Recommendation or Recommended Mitigation Measure: The final EIR should evaluate how the city will accommodate the increased water burden between groundwater, purchases from SEWD and WID, and the City's existing water right permit 21176.
ENVIRONMENTAL DATA
CEQA requires that information developed in environmental impact reports and negative declarations be incorporated into a database which may be used to make subsequent or supplemental environmental determinations (Pub. Resources Code,§ 21003, subd. (e).) Accordingly, please report any special-status species and natural communities detected during Project surveys to the California Natural Diversity Database (CNDDB). The CNN DB field survey form can be found at the following link: https://www.wildlife.ca.gov/Data/ CNDDB/Submitting-Data . The completed form can be submitted online or mailed electronically to CNDDB at the following email address: CNDDB@wildlife .ca.gov .
FILING FEES
The Project, as proposed, would have an impact on fish and/or wildlife, and assessment of filing fees is necessary. Fees are payable upon filing of the Notice of Determination by the Lead Agency and serve to help defray the cost of environmental review by CDFW.
Payment of the fee is required in order for the underlying project approval to be operative, vested, and final. (Cal. Code Regs, tit. 14, § 753.5; Fish & G. Code, § 711.4; Pub.
Resources Code, § 21089.)
CONCLUSION
Pursuant to Public Resources Code § 21092 and § 21092.2, CDFW requests written notification of proposed actions and pending decisions regarding the proposed project.
Written notifications shall be directed to: California Department of Fish and Wildlife North Central Region, 1701 Nimbus Road, Rancho Cordova , CA 95670 or emailed to [email protected].
CDFW appreciates the opportunity to comment on the DEIR for the Le Baron Ranch to assist City of Stockton in identifying and mitigating Project impacts on biological resources.
CDFW personnel are available for consultation regarding biological resources and strategies to minimize and/or mitigate impacts. Questions regarding this letter or further coordination should be directed to Zach Kearns, Environmental Scientist at (916) 358-1134 or [email protected].
Sincerely, r-:DocuSigned by:
L~:eOA~!t~
Morgan Kilgour, PhD
Regional Manager
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Docusign Envelope ID: 27AFBEB5-9AC4-4A94-9F26-20B920179DFC LeBaron Ranch
September 26, 2024
ec: Tanya Sheya, Environmental Program Manager
Billie Wilson, Senior Environmental Scientist (Supervisory) Zach Kearns, Environmental Scientist
Department of Fish and Wildlife
Office of Planning and Research, State Clearinghouse, Sacramento EXHIBIT 1
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Response to Letter A: California Department of Fish and Wildlife Response A-1: This comment serves as an introduction to the comment letter. No further response is necessary.
Response A-2: This comment describes the California Department of Fish and Wildlife (CDFW) regulatory role. No further response is necessary.
Response A-3: This comment correctly summarizes the proposed Project description. No further response is necessary.
Response A-4: See Responses A-5 through A-7 for detailed responses regarding the Project’s potentiallysignificant impacts related to biological resources which are described in the body of the comment letter.
Response A-5: Crotch bumble bee (Bombus crotchii) is discussed on page 3.4-13 and in Impact 3.4-1 on pages 3.4-28 and 3.4-29 of Section 3.4, Biological Resources, of the Draft EIR. As shown in Table 3.4-3, appropriate habitat for this species is not present. This determination is based on the field surveys completed by Principal Biologist Steve McMurtry on April 22, 2022, and May 15, 2023. The methodology of these surveys is summarized on page 3.4-
3. Additionally, as discussed on page 3.4-28, field surveys and habitat evaluations for the entire Project site were performed on April 22, 2022, and May 15, 2023. No special-status invertebrates were observed within the Project site during field surveys and none are expected to be affected by the proposed Project based on the lack of appropriate habitat.
As discussed on page 3.4-29, while crotch bumbles are documented within the nine-quad region for the Project site, they are not documented on the Project site. The habitat present on the Project site is not ideal natural habitat for this species and none are believed to be present. Further, the nearest California Natural Diversity Database (CNDDB) occurrence of this species is over 20 miles southwest of the Project site. As such, the determination for this species is accurate.
Response A-6: Impacts associated with bird mortality are discussed in Impact 3.4-3 on pages 3.4-31 and
3.4-32 of Section 3.4, Biological Resources, of the Draft EIR. As discussed, there are eight (8) special-status birds that are documented in the CNDDB within the nine (9)-quadrangle area for the Project site according to the CNDDB, including: Burrowing owl (Athene cunicularia), California black rail (Laterallus jamaicensis coturniculus), Least Bell's vireo (Vireo bellii pusillus), Song sparrow (Modesto Population) (Melospiza melodia), Swainson’s hawk (Buteo swainsoni), Tricolored blackbird (Agelaius tricolor), White-tailed kite (Elanus leucurus), and Yellow-headed blackbird (Xanthocephalus xanthocephalus). All of these bird species, except for Least bell’s vireo, are covered species under the San Joaquin County Multi-Species Habitat Conservation and Open Space Plan (SJMSCP).
In summary, powerlines and trees located in the region represent potentially suitable nesting habitat for a variety of special-status birds. Additionally, the agricultural land EXHIBIT 1
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represents potentially suitable nesting habitat for some ground-nesting birds. The CNDDB currently contains records for Swainson's hawk, burrowing owl, and tricolored blackbird in the vicinity of the Project site. In addition to the species described above, common raptors, may nest in or adjacent to the Project site. Further, indirect impacts related to bird collision with glass windows and bird mortality associated with domestic pets could occur.
Additionally, new sources of noise and light during the construction and operational phases of the project could adversely affect nesters if they located adjacent to the Project site in any given year. While avian mortality due to window collisions is a real phenomenon, CEQA-level assessments of this risk are typically limited to developments with an especially high percentage of clear and/ or reflective glazing (glass, windows) on exterior facades, and/ or other specific elements deemed likely to result in a high rate of collisions.
Glazing on the proposed residential windows would be minimal. The glazing included in the Project consists entirely of windows for the residential units, all of which are isolated from each other at regular intervals versus being grouped/conjoined to form larger contiguous window panels, and each is further divided into smaller areas. The elevations also feature forms of architectural relief (overhangs, spatially offset adjacent faces) as well as varied (opaque) materials and colors, all of which would break up the exterior visually ( i.e., create “visual noise”), and increase the likelihood that birds would perceive the building overall as a solid surface.
Overall, by current architectural/design standards, the project provides minimal risk of bird collisions. The number of birds that would collide with the building over time is virtually impossible to estimate, and thus speculative. In any event, these impacts are unlikely to be significant at a regional or even local scale. In particular, bird strikes (to the degree that such occur, if at all) are more likely to involve common (and not specialstatus) species given their relative abundance in the area and local conditions. The impact related to bird collisions would be less than significant, and no mitigation is required.
Further, the proposed Project would eliminate the agricultural areas on the Project site, which serve as potential foraging habitat for birds throughout the year. Mitigation Measure 3.4-1 requires participation in the SJMSCP. As part of the SJMSCP, SJCOG requires preconstruction surveys for projects that initiate grading activities during the avian breeding season (March 1 – August 31). When active nests are identified, the biologists develop buffer zones around the active nests as deemed appropriate until the young have fledged. SJCOG also uses the fees to purchase habitat as compensation for the loss of foraging habitat. These ITMMs are included in Mitigation Measures 3.4-2 through 3.4-4. Implementation of the proposed Project, with the Mitigation Measures
3.4-1 through 3.4-4, would ensure that potential impacts to special status birds are reduced to a less than significant level.
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Response A-7: Impacts associated with water supplies available to serve the Project are discussed in Impact 3.14-5 on pages 3.14-27 and 3.14-28 of Section 3.14, Utilities and Service Systems, of the Draft EIR. Additionally, a Water Supply Assessment (WSA) was completed for the Project (see Appendix G of the Draft EIR). As discussed, the total projected water supplies determined to be available for the proposed Project during normal, single dry, and multiple dry years during a 20-year projection will meet the projected water demand associated with the Proposed Project, in addition to existing and planned future uses, including, but not limited to, agriculture and industrial uses. Future purchasing plans for water supplies to serve the City of Stockton would be determined and analyzed by the City. Impacts related to water supplies were determined to be less than significant.
Further, impacts related to groundwater recharge are discussed in Impact 3.9-2 on page
3.9-25 of Section 3.9, Hydrology and Water Quality, of the Draft EIR. As described, potable water at the Project site would be provided by the City of Stockton Municipal Utilities Department (COSMUD), which relies on purchased water from the Calaveras, Stanislaus, and Mokelumne Rivers; surface water from the San Joaquin Delta; and groundwater.
According to the WSA prepared by COSMUD for the Project, sufficient water supplies exist to meet the Project’s build-out water demand as well as all existing and reasonably foreseeable water demands. Additionally, the WSA concludes that the existing near-term and long-term reliable supplies of surface water supplies and indigenous groundwater supplies can deliver a sustainable reliable water supply to meet existing and foreseeable water demands without impacting environmental values and/or impacting the current stabilization of the groundwater basin underlying the City of Stockton Metropolitan Area.
Response A-8: Any species or communities detected during the Project surveys will be reported to the CNDDB.
Response A-9: The Project applicant will pay the applicable filing fees upon filing the Notice of Determination for the Project.
Response A-10: The City will provide the CDFW with any written notification of proposed actions and pending decisions regarding the proposed Project.
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B-1
B-2
Docusign Envelope ID: 578D34D4-AF4A-48B9-9880--83630BB92C56
STATE OF CALIFORNIA - CALIFORNIA NATURAL RESOURCES AGENCY CENTRAL VALLEY FLOOD PROTECTION BOARD 3310 El Camino Ave., ste. 170 SACRAM ENTO, CA 9582 1
(9 16) 57 4-0609
September 25, 2024
Nicole Moore
Contract Planner
City of Stockton
345 N. El Dorado Street
Stockton, CA 95202
nicole. moore. [email protected]
Subject: Comments for the Draft Environmental Impact Report, LeBaron Ranch Project, SCH# 2023070657, San Joaquin County
Dear Nicole Moore,
The Central Valley Flood Protection Board (Board) appreciates the opportunity to comment on the Draft Environmental Impact Report (DEIR) for the proposed LeBaron Ranch Project (proposed project).
The proposed project involves constructing a new residential development. The proposed project is located southeast of Pixley Slough and northwest of Bear Creek. Pixley Slough and Bear Creek are regulated streams and federally regulated channels within the Board's permitting authority, therefore an encroachment permit may be required. Board permit information is available on the Permitting at the Central Valley Flood Protection Board website.
While the proposed project does not anticipate construction within Pixley Slough nor Bear Creek, any activities that modifies Board regulated streams or elements of the State Plan of Flood Control within the watershed may require review and approval by the Central Valley Flood Protection Board. This includes activities that introduce encroachments, increase peak flow rates, or alter flow velocities, potentially altering channel conveyance capacity and sediment transport patterns and causing negative downstream impacts. For any such activities, compliance with California Code of Regulations Title 23, Division 1 (Central Valley Flood Protection Board) and Part 4 of Division 5 of the California Water Code would be necessary.
Responsibility of the Central Valley Flood Protection Board The Board is the State's regulatory agency responsible for enforcing appropriate standards for the construction, maintenance, and operation of the flood control system that protects life, property, and habitat in California's Central Valley. The Board serves as the State coordinator between local flood management agencies and the federal government, with the goal of providing the highest level of flood protection possible to California's Central Valley.
The Board operates under authorities as described in California Water Code (Water Code), which requires the Board to oversee future modifications or additions to facilities of the State Plan of Flood Control (SPFC). In addition, pursuant to assurances provided to the United States EXHIBIT 1
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Docusign Envelope ID: 578D34D4-AF4A-48B9-9880-83630BB92C56 City of Stockton
September 25, 2024
Army Corps of Engineers (USAGE) by the Board on behalf of the State, the USAGE Operation and Maintenance Manuals, Code of Federal Regulations, Title 33, Section 208.10, and United States Code, Title 33, Section 408, the Board is responsible for the operation and maintenance of the SPFC facilities. The USA CE requires the Board to serve as the lead non-Federal sponsor for projects to improve or alter facilities of the SPFC pursuant to Code of Federal Regulations, Title 33, Section 408. The State's objectives include fulfilling the USACE's expectations pursuant to the assurances provided to the USAGE.
Encroachment Permit
Per California Code of Regulations, Title 23, Waters, Division 1 (Title 23), Section 6, approval by the Board is required for all proposed work or uses, including the alteration of levees within any area for which there is an Adopted Plan of Flood Control within the Board's jurisdiction. In addition , Board approval is required for all proposed encroachments within a floodway , on adjacent levees, and within any Regulated Stream identified in Title 23, Table 8.1. Specifically, Board jurisdiction includes the levee section, the waterward area between project levees, a minimum 10-foot-wide strip adjacent to the landward levee toe, the area within 30 feet from the top of bank(s) of Regulated Streams, and inside Board's Designated Floodways. Activities outside of these limits which could adversely affect Federal-State flood control facilities, as determined by Board staff, are also under the Board's jurisdiction. Permits may also be required for existing unpermitted encroachments or where it is necessary to establish the conditions normally imposed by permitting, including where responsibility for the encroachment has not been clearly established or ownership or uses have been changed.
Federal permits, including USAGE Section 404 and Section 10 regulatory permits and Section 408 Permission, in conjunction with a Board permit, may be required for the proposed project. In addition to federal permits, state and local agency permits, certification, or approvals may also be required. State approvals may include, but are not limited to, California Department of Fish and Wildlife's Lake and Streamed Alteration Agreement and Central Valley Regional Water Quality Control Board's Section 401 Water Quality Certification and/or Waste Discharge Requirement. The Applicant must obtain all authorizations that the proposed project may require.
Flood Impacts Analysis
Pursuant to Section 15 of Title 23, the Board may deny an encroachment permit if the proposed project could:
• Jeopardize directly or indirectly the physical integrity of levees or other works • Obstruct, divert, redirect, or raise the surface level of design floods or flows, or the lesser flows for which protection is provided
• Cause significant adverse changes in water velocity or flow regimen • Impair the inspection of floodways or project works
• Interfere with the maintenance of floodways or project works • Interfere with the ability to engage in flood fighting , patrolling, or other flood emergency activities
• Increase the damaging effects of flood flows
• Be injurious to, or interfere with, the successful execution, functioning, or operation of any adopted plan of flood control
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Docusign Envelope ID: 578D34D4-AF4A-48B9-9880-83630BB92C56 City of Stockton
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• Adversely affect the State Plan of Flood Control, as defined in the California Water Code The Board, as a Responsible Agency under the California Environmental Quality Act (CEQA), will review and consider the environmental effects of the proposed project identified in the DEIR, and will reach its own conclusions on whether and how to approve the project involved (14 CCR 15096, subd. (a)). This includes direct impacts to facilities under construction, as well as indirect impacts from the proposed project to surrounding facilities.
Closing
The potential risks to public safety, including increased flood risks, need to be considered when developing proposed projects that seek to modify flood control works or the hydrology of the water ways. Board staff is available to discuss any questions you have regarding the above comments. Please contact Jordan Robbins at (916) 524-3454, or via email at [email protected] .gov if you have any questions.
Sincerely,
Jamie Silva
Environmental Program Manager
cc: Office of Planning and Research
[email protected]
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Response to Letter B: Central Valley Flood Protection Board Response B-1: This comment serves as an introduction to the comment letter. See responses to comments B-4 and B-5 below for details. No further response is necessary.
Response B-2: This comment describes the Centra Valley Flood Protection Board regulatory role. No further response is necessary.
Response B-3: As discussed on pages 3.4-34 and 3.4-35 of Section 3.4, Biological Resources, of the Draft EIR, development of the proposed Project would include construction of a new storm basin near Eight Mile Road, and two (2) options for connecting to offsite drainage facilities are being considered and evaluated. Option One would connect to a new outfall structure to the north of the basin and pump storm water into the Woodbridge Irrigation District drainage ditch that is located south of, and parallel to Eight Mile Road. Option Two is construction of a force main to Pixley Slough to an existing outfall structure. The force main would be located south of, and parallel Eight Mile Road. Should Option Two be required, no encroachment into Pixley Slough would be required. Should Option One be required, an encroachment permit would be required.
The Project site does not contain jurisdictional wetland habitat. The irrigation ditches are manmade agricultural irrigation facilities that are not jurisdictional. Water flows are controlled by the irrigation district that owns the facilities. There are no other aquatic features. Section 404, Section 401, or Section 408 permissions, or a Lake and Streambed Alteration Agreement, would not be required.
Additionally, as noted on page 3.9-8 of Section 3.9, Hydrology and Water Quality, Because the City of Stockton participates in the National Flood Insurance Program, it must require development permits to ensure that construction materials and methods will mitigate future flood damage, and to prevent encroachment of development within floodways.
Pursuant to Chapter 15.44, Flood Damage Prevention, of the City’s Municipal Code, new construction and substantial improvements of residential structures are also required to “have the lowest habitable floor (including the basement if it is, or easily could be ‘habitable’) elevated to or above the base flood level.” Non-residential structures must have their utility systems above the BFE or be of flood-proof construction.
Response B-4: This comment is noted. See Response B-3 regarding encroachment of development. No encroachment permit is required for the Project; as such, this comment does not apply.
Response B-5: This comment serves as a conclusion to the comment letter. No further response is necessary.
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SAN ,JO AO U IN - CO UNT YGreotness grows here.
Environmental Health Department
Jasjit Kang, REHS, Director
Muniappa Naidu, REHS, Assistant Director
PROGRAM COORDINATORS
Jeff Carruesco, REHS, RDI
Willy Ng , REHS
Steven Shih, REHS
Elena Manzo, REHS
Natalia Subbotnikova, REHS
September 19, 2024
To: City of Stockton Planning Department
From:
Attention: Nicole Moore ~
Aaron Gooderham (209) 616-3062
RE:
Senior Registered Environmental Health Specialist
LeBaron Ranch, Draft Environmental Impact Report, SU-2400146 LeBaron Ranch Project Site
The San Joaquin County Environmental Health Department (EHD) is supportive of this project in regards to the provision of full public services. The San Joaquin County Environmental Health Department (EHD) recommends the following conditions as a part of developing this project:
1) Destroy the abandoned well located on the north-east corner of APN 08405008 under permit and inspection by the Environmental Health Department as required by San Joaquin County Development Title, Section 9-601 .020(e).
2) Any geotechnical drilling shall be conducted under permit and inspection by The Environmental Health Department (San Joaquin County Development Title, Section 9- 601.01 0(b) and 9-601.020(i)).
3) Before any hazardous materials/waste can be stored or used onsite, the owner/operator must report the use or storage of these hazardous materials to the California Environmental Reporting System (GERS) at cers.calepa.ca.gov/ and comply with the laws and regulations for the programs listed below (based on quantity of hazardous material in some cases). The applicant may contact the Program Coordinator of the CUPA program, Elena Manzo (209) 953-7699, with any questions.
a) Any amount but not limited to the following hazardous waste; hazardous material spills, used oil, used oil filters, used oil-contaminated absorbenUdebris, waste antifreeze, used batteries or other universal waste, etc. - Hazardous Waste Program (Health &Safety Code (HSC) Sections 25404 & 25180 et sec.)
b) Onsite treatment of hazardous waste - Hazardous Waste Treatment Tiered Permitting Program (HSC Sections 25404 & 25200 et sec. & California Code of Regulations (CCR), Title 22, Section 67450.1 et sec.)
c) Reportable quantities of hazardous materials-reportable quantities are 55 gallons or more of liquids, 500 pounds for solids, or 200 cubic feet for compressed gases, with some exceptions. Carbon dioxide is a regulated substance and is required to be reported as a hazardous material if storing 1,200 cubic feet (137 pounds) or more onsite in San Joaquin County - Hazardous Materials Business Plan Program (HSC Sections 25508 & 25500 et sec.)
1868 E. Hazelton Avenue I Stockton, California 95205 I T 209 468-3420 I F 209 464-0138 I www.sjgov.org/ehd EXHIBIT 1
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LeBaron Ranch Draft Environmental Impact Report, SU-2400146 LeBaron Ranch Project Site
September 19, 2024
d) Any amount of hazardous material stored in an Underground Storage Tank - Underground Storage Tank Program (HSC Sections 25286 & 25280 et sec.) i) If an underground storage tank (UST) system will be installed , a permit is required to be submitted to, and approved by, the San Joaquin County Environmental Health Department (EHD) before any UST installation work can begin. ii) Additionally, an EHD UST permit to operate is required once the approved UST system is installed.
e) Storage of at least 1,320 gallons of petroleum aboveground or any amount of petroleum stored below grade in a vault -Aboveground Petroleum Storage Program (HSC Sections 25270.6 & 25270 et sec.)
i) Spill Prevention, Countermeasures and Control (SPCC) Plan requirement f) Threshold quantities of regulated substances stored onsite - California Accidental Release Prevention (CalARP) Program (Title 19, Section 2735.4 & HSC Section 25531 et sec.)
i) Risk Management Plan requirement for covered processes 1868 E. Hazelton Avenue I Stockton, California 95205 I T 209 468-3420 I F 209 464-0138 I www.sjgov.org/ehd EXHIBIT 1
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Response to Letter C: San Joaquin County Environmental Health Department Response C-1: This comment serves as an introduction to the comment letter. No further response is necessary.
Response C-2: This comment is noted. There are no abandoned wells within the Project site.
Nevertheless, it is the City’s policy to require any wells to be abandoned shall be abandoned/destroyed under permit and inspection by the EHD (San Joaquin County Development Title, Section 9-1110.3 & 9-1110.4). This is an existing regulation that is in place and there is not a need for a measure requiring this existing requirement.
Response C-3: This comment is noted. A final geotechnical evaluation of soils at a design-level would be prepared for the Project. The geotechnical evaluation would be prepared in accordance with the standards and requirements outlined in the California Building Code (CBC), Title 24, Part 2, Chapter 16, Chapter 17, and Chapter 18, which addresses structural design, tests and inspections, and soils and foundation standards. Implementation of requirement would ensure that all on-site fill soils are properly compacted and comply with the applicable safety requirements established by the CBC to reduce risks associated with unstable soils and excavations and fills, and that any issues associated with unstable soils are addressed at the design level. This work will be performed at a design level, and it is not known at this time if drilling would be necessary, or if a less sampling method would be appropriate. Nevertheless, it is the City’s policy to require any geotechnical drilling to be conducted under permit and inspection by The Environmental Health Department (San Joaquin County Development Title, Section 9-1115.3 and 9-1115.6). This is an existing regulation that is in place and there is not a need for a measure requiring this existing requirement.
Response C-4: This comment is noted. As discussed in Section 3.8, Hazards and Hazardous Materials, the operational phase would occur after construction is completed and business operations commence on a day-to-day basis. The Project proposes to construct a primarily residential development comprised of up to 1,411 residential units, parks/open space, and a school site within the Development Area, as well as circulation and infrastructure improvements.
The Project does not propose uses that would involve the use or storage of hazardous substances other than limited quantities of hazardous materials such as solvents, fertilizers, pesticides, and other materials used for regular household maintenance of buildings and landscaping. The quantities of these materials would not typically be at an amount that would pose a significant hazard to the public or the environment. While the risk of exposure to hazardous materials cannot be eliminated, measures can be implemented to reduce risk to acceptable levels. Adherence to existing regulations would ensure compliance with safety standards related to the use and storage of hazardous materials, and the safety procedures mandated by applicable federal, State, and local laws and regulations would ensure that risks resulting from the routine transportation, use, storage, or disposal of hazardous materials during the operational phase of the proposed Project would be less than significant.
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D-1
Balancing Communit) and Commerce
44 N. SAN JOAQUIN STREET SUITE 374
September 27, 2024
Nicole Moore
City of Stockton
345 N. El Dorado Street
Stockton, CA 95202
Via email: [email protected]
STOCKTON, CA 95202
SUBJECT: Comments on Notice of Availability of a Draft EIR LeBaron Ranch Project, State Clearinghouse Number 2023070657 Dear Ms. Moore:
209-468-3198
Thank you for sending San Joaquin LAFCo the Notice of Availability for the Draft Environmental Impact Report for the Le Baron Ranch Project. San Joaquin LAFCo appreciates the opportunity to review and comment on the Draft EIR pursuant to the California Environmental Quality Act {Pub.
Res. Code§ 21000 et seq .: "CEQA") and the State CEQA Guidelines (14 C.C.R. § 15000 set seq.).
LAFCo staff has reviewed this document and offers the following comments.
LAFCo is an independent, regulatory agency with discretion to approve, wholly, partially or conditionally, or disapprove, changes of organization or reorganizations. In accordance with the Cortese-Knox-Hertzberg Local Government Reorganization Act of 2000 ("CKH Act"), LAFCo is required to consider various factors when evaluating a proposal, including, but not limited to, impacts to agricultural and open space lands, the provision of municipal services and infrastructure to the project site, timely and available supply of water, fair share of regional housing, consistency with regional plans, and other factors.
The factors relating to boundary changes are contained in Government Code {"GC" ) §56668.
Including an assessment of these factors in the County's environmental document will facilitate LAFCo' s review and the LAFCo process. Deficiencies in the environmental document as required by LAFCo may result in the need for additional CEQA compliance work.
As a Responsible Agency pursuant to the CEQA, LAFCo would like to rely on the County's EIR in consideration of any local agency boundary change required for the project. Given that LAFCo's approvals will be a fundamental part of the entitlements required for this project, the EIR should specifically address the following:
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2.0 Project Description
1. Page 2.0-12: "Annexation" section appears unfinished as last sentence ends in ellipses without a conclusion.
2. Page 2.0-13: San Joaquin LAFCo is listed as an agency whose approval is required for annexation. Please add that LAFCo is also the approving authority for the detachment from Lincoln Rural Fire Protection District. Lincoln Rural Fire Protection District currently contracts with the City of Stockton for services, so the service provider will remain the same and has capacity for services in this area.
3. Page 2.0-13: Under "City of Stockton," revise "Approval of Annexation and Authorization to Submit Annexation ll:equest to San Joaquin LAFCo" to add "and Submit Detachment Request for Lincoln Fire District."
4. Annexation Timing: The Final EIR should discuss the timing of annexation relative to timing of the proposed development plans. Typically, LAFCOs organization/reorganization processes will be required after project approvals and prior to map recordation. In the case of a phased map, all approvals should occur prior to recordation of the first phase of the map so as not to create island territory issues.
3.10 Land Use, Population and Housing
5. Annexation of Rights of Way: Per San Joaquin LAFCo's standards for annexation, "LAFCo will require cities to an.nex streets where adjacent lands that are in the city will generate additional traffic or where the annexation will isolate sections of county road. Cities shall include all contiguous public roads that can be included without fragmenting governmental responsibility by alternating city and county road jurisdiction over short section of the same roadway." Any annexation of the subject property should include surrounding roadways and rights of way to avoid the creation of islands and/or illogical boundaries pursuant to Section 56668 of the CKH Act.
The proposed Right-of-Way Annexation Area includes Eight Mile Road along the northern boundary of the project site. Please clarify whether other contiguous roadways are within the City sphere/City maintained mileage system. To this end, it would be useful if the EIR included an exhibit showing the annexation areas, including right-of-way annexation, and what is to be maintained by the City versus the County. All of Marlette Road, Eight Mile Road, West Lane, and Lower Sacramento Road contiguous to the project site should be annexed to the City, where not already within the City limits. In addition, all rights of way stranded in the creation of the unincorporated island to the south should be considered for annexation to the City in coordination with the County Public Works Department.
6. Evaluate Difference in Density and Population of Existing Versus Proposed Uses: While the project area was evaluated in the 2020 City of Stockton Sphere of Influence (SOI)
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Plan/Municipal Service Review (MSR), and the City was projected to meet all water demands, sewer demands, stormwater provisions, police services, and fire services within its SOI, it is unclear whether that evaluation is still relevant or needs to be updated. The proposed project's "reorganization" of land uses described in the Draft EIR includes modification of the acreages of various General Plan land use designations that were used for the 2020 MSR, which could result in greater density and population than evaluated in the MSR and General Plan EIR. The Land Use, Population and Housing chapter should include an analysis of density and population changes between existing and proposed land use quantities (preferably in tabular format), which should in turn be addressed in the Public Services and Utilities chapters (3.12 and 3.14).
7. 2020 City of Stockton Sphere of Influence (SOI) Plan/Municipal Service Review (MSR): In addition, the 2020 MSR states on page 2-25 that the "balance of the area north of City limit, south of Eight Mile Road," which includes the project site and several other properties, is "expected to accommodate up to 1,380 new single-family homes, 1,200 new multi-family homes, and 39,000 square feet of new commercial and office development." The proposed project includes up 1,217 new single-family residential units, or 88 percent of the planned single-family homes evaluated in the MSR, even though much of the remaining territory which encompasses an area larger than the project site is planned for single-family development in the 2040 General Plan Land Use Map. An update to the 2020 MSR is likely needed and will be required prior to LAFCo approval of the annexation. This issue should be addressed in the EIR as LAFCo would like to rely on the County's EIR in consideration of any local agency boundary change required for the project.
8. Impact 3.10-2: Conflicts with Land Use Plans and Policies: The Draft EIR concludes that Impact 3.10-2 is less than significant. Although LAFCo has expressed support for annexation of the property as noted in the Draft EIR, the project will nonetheless result in the creation of an island territory inconsistent with the CKH Act Section 56668(f). In addition, CKH Act Section 56377 states that "Development or use of land for other than open-space uses shall be guided away from existing prime agricultural lands in openspace use toward areas containing nonprime agricultural lands, unless that action would not promote the planned, orderly, efficient development of an area." The conversion of farmlands of importance is in itself a significant and unavoidable impact per Impact 3.2-
1. The development of the proposed project, although planned in the City's General Plan and included in the City's SOI, was presumably contingent upon the orderly development of the territories within the SOI in such a manner that would not create island territories (e.g., in the project area, from south to north). LAFCo therefore recommends that this impact be considered significant and unavoidable, and if the project is approved, findings of overriding consideration made, which could include the infeasibility of annexation of areas to the south, the right to farm ordinances within the City and County, and the farmland mitigation programs in place, among other socioeconomic justifications. This approach provides the transparency that CEQA requires for public informational purposes, noting the significance of inconsistency with specific policies in place to prevent
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the creation of islands and loss of important farmlands and allowing the public the opportunity to consider any findings of overriding consideration.
9. Map of City boundaries and Spheres of Influence: It would be useful if this chapter included a map showing the project site in relation to the City boundaries and Spheres of Influence so that the creation island territories can be clearly seen .
3.12 Public Services and Recreation and 3.14 Utilities and Service Systems
10. Evaluate Difference in Density and Population of Existing Versus Proposed Uses Vis-a-vis the Provision of Services: See item 6 above. Once the analysis is updated to define any differences between existing and proposed populations and densities, these data should be used to update the analyses in the Public Service and Utilities chapters. LAFCo will rely on these analyses in the annexation application request.
Thank you for the opportunity to comment on the LeBaron Ranch Draft EIR. Please contact the LAFCo office if you have any questions.
Sincerely,
'--->f{\1·~·\....A
ghtower
~
~ Executive Officer
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Response to Letter D: San Joaquin County LAFCO
Response D-1: This comment serves as an introduction to the comment letter and discusses LAFCO’s regulatory responsibility. See Responses D-2 through D-9.
Response D-2: The error on page 2.0-12 of Chapter 2.0, Project Description, of the Draft EIR has been corrected to remove the incomplete sentence. See Chapter 3.0, Revisions, of this Final EIR.
The requested text additions have been added to page 2.0-13 of Chapter 2.0, Project Description. See Chapter 3.0, Revisions, of this Final EIR.
As discussed in Chapter 2.0, Project Description, of the Draft EIR, the Project would establish a logical phasing plan designed to ensure that each phase of development would include necessary public improvements that are required to meet City standards, both onsite and offsite. Internal Phases will basically commence from the eastern portion of the Development Area and move west, allowing infrastructure to be advanced to an upcoming phase. The Project approvals would occur prior to recordation of the first phase of the tentative map so as not to create island territory issues.
Response D-3: As shown in Table 2.0-1 on page 2.0-2 of Chapter 2.0, Project Description, of the Draft EIR, the proposed annexation area includes 13.7 acres of right-of-way. Figure 2.0-3 illustrates the Assessor Parcel Numbers and extent of the proposed annexation area. As shown, Eight Mile Road and Marlette Road are within the Project site (or Annexation Area). The roadways which would be annexed as part of the Project would be maintained by the City.
Lower Sacramento Road, the adjacent west roadway, would not be annexed as part of the Project as the extent of this roadway adjacent to the Project site is within the City limits.
It is also noted that a new figure depicting the annexation area has been added to Chapter
2.0, Project Description, of the Draft EIR in order to address this comment. See Chapter
3.0, Revisions, of this Final EIR for the new figure.
Response D-4: A comparison of the proposed Project population with the population allowed under the existing General Plan is discussed in Impact 3.10-3. As discussed, according to the Department of Finance population estimates for the year 2023, the population in Stockton is 319,731 people. The proposed Project would include the development of approximately 236.6-acres of land which will include: residential, parks, open space, public facilities, and public roadway right-of-way land uses. The proposed Project establishes a site for a 12.0-acre K-8 school to be developed by Lodi Unified School District (LUSD). The development of a K-8 school at this site is the discretionary decision of the LUSD, and while the proposed Project has planned for a school at this location, it will be determined by LUSD later through their decision-making process. If the LUSD decides to not pursue building a school at this site, then the site would be developed with 79 single family residential units. Construction of homes in this location would increase the number EXHIBIT 1
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of units by 79 units when compared to the proposed Project with the school site. The total combined residential units would increase from 1,332 under the proposed Project to 1,411 units under this variation (i.e., no school). Using the most recent Department of Finance data (2023) for the average number of persons residing in a dwelling unit in the City of Stockton (3.13 persons per household), the Project could result in 4,169 to 4,416 residents.
The proposed Project would not result in direct population growth beyond the City’s capacity identified in the General Plan; rather, it would result in a reduction of the total number of units anticipated under the General Plan by approximately 662 to 741 units.
The net population reduction associated with the reduction of units under the proposed Project (compared to the capacity assumed for the Project site under the General Plan) is anticipated to be 2,072 to 2,319 persons.
Response D-5: The City of Stockton Municipal Service Review (MSR) (2020) includes Figure 2-7, 10-Year Planning Horizon Annexation Areas, which shows where annexations within the City’s current Sphere of Influence (SOI) would contribute to addressing demand over the 10- year horizon (i.e., prior to 2030). Any areas that aren’t completely developed by 2030 are assumed to be built out by the end of the 20-year horizon. One of the areas identified in Figure 2-7 identified the following area: “Balance of area north of City limit, south of Eight Mile Road: According to the 2040 General Plan EIR, this area is expected to accommodate up to 1,380 new single-family homes, 1,200 new multifamily homes, and 39,000 square feet of new commercial and office development.”
As shown in Table 2.0-3 of the Draft EIR, the Project includes up to 1,217 single-family residential units, or 88 percent of the single-family residential units assumed for the “Balance of area north of City limit, south of Eight Mile Road” identified in the MSR. It is noted that this percentage would decrease slightly if the proposed school site is built.
Additionally, the Project includes up to 194 multi-family residential units, or 16 percent of the multi-family residential units assumed for the “Balance of area north of City limit, south of Eight Mile Road” identified in the MSR.
The Project would be developed in six phases. Assuming the Project is approved in 2025, the first house in phase one will be ready to sell in 2027. The entire Project will take between seven and ten years to buildout, resulting in full buildout estimated between 2034 to 2037.
Ultimately, as noted in Section 3.10, Land Use, Population and Housing of the Draft EIR, LAFCo will determine whether the proposed annexation would first require an update to the City of Stockton Sphere of Influence Plan/Municipal Service Review (2020) to approve the annexation. This LAFCo policy was not specifically adopted to avoid or mitigate an environmental effect, rather it is intended to ensure orderly and logical reorganization to local jurisdiction boundaries, including annexations. The proposed Project is generally consistent with LAFCo policies adopted to address environmental impacts. Section 3.2, Agricultural Resources, addresses impacts related to conversion of agricultural land and EXHIBIT 1
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includes all feasible mitigation measures to reduce impacts to prime farmland.
Nevertheless, annexation and subsequent urban development of the Project site will have a significant and unavoidable impact on prime farmland. This topic was analyzed as part of the City’s General Plan Draft EIR, and ultimately the City approved land use designations that would allow for the conversion of the prime farmland to an urban use.
Response D-6: As described in Impact 3.10-2 of the Draft EIR, the pre-planning process for the proposed Project included meetings with Jim Glaser, former Executive Officer of the San Joaquin LAFCo, and JD Hightower, current Executive Officer of the San Joaquin LAFCo, to discuss the proposed annexation. Per LAFCo’s recommendation, the Project applicant consulted with and reviewed information related to properties south of the proposed Project, which would become an island of unincorporated territory upon annexation of the proposed Project site, to evaluate the potential annexation of the southern sites to the City as part of the proposed Project. The ownerships of the parcels to the south of the Project site were not in a position to join in the proposed annexation proposed by the Project. The primary reasons were either the properties were not under contract with a developer and/or Williamson Act contracts are on several properties and no non-renewals to cancel the Williamson Act contracts have been filed. Jim Glaser and the Project applicant had several phone calls to further discuss the proposed annexation. It was concluded that a reasonable effort had been made to include the island in the annexation, but the status of those properties at this time did not make sense to join the annexation.
As noted in Policy LAFCO Change of Organization Policies and Procedures (Including Annexations and reorganizations) (As Amended 12/14/12), LAFCo may nevertheless approve an annexation that creates an island where it finds that the application of this policy would be detrimental to the orderly development of the community and that a reasonable effort has been made to include the island in the annexation but that inclusion is not feasible at this time.
With respect to farmland, a significant and unavoidable impact is identified in Section 3.2, Agricultural Resources, of the Draft EIR. Findings of overriding considerations have been made for this impact.
Ultimately, as noted in Section 3.10, Land Use, Population and Housing of the Draft EIR, the LAFCo Change of Organization Policies and Procedures (Including Annexations and Reorganizations) was not specifically adopted to avoid or mitigate an environmental effect, rather it is intended to ensure orderly and logical reorganization to local jurisdiction boundaries, including annexations. The proposed Project is generally consistent with LAFCo policies adopted to address environmental impacts. Section 3.2, Agricultural Resources, addresses impacts related to conversion of agricultural land and includes all feasible mitigation measures to reduce impacts to prime farmland.
Nevertheless, annexation and subsequent urban development of the Project site will have a significant and unavoidable impact on prime farmland. This topic was analyzed as part of the City’s General Plan Draft EIR, and ultimately the City approved land use designations that would allow for the conversion of the prime farmland to an urban use.
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Response D-7: A new figure depicting the annexation area has been added to Chapter 2.0, Project Description, of the Draft EIR. See Chapter 3.0, Revisions, of this Final EIR for the new figure.
Response D-8: See Response D-4.
Response D-9: This comment serves as a conclusion to the comment letter. No further response is necessary.
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■ San Joaquin Valley - AIR POLLUTION CONTROL DISTRICT
September 25, 2024
Nicole Moore
City of Stockton
345 North El Dorado Street
Stockton, CA 95202
HEALTHY Al R LIVING™
Project: Draft Environmental Impact Report for the LeBaron Ranch Project District CEQA Reference No: 20240963
Dear Ms. Moore:
The San Joaquin Valley Air Pollution Control District (District) has reviewed the Draft Environmental Impact Report (DEi R) from the City of Stockton (City) for the above project. Per the DEIR , the project consists of 1,217 single-family homes and 194 high density residential units, for a total residential unit count of 1,411 units and 30.7 acres of parkland and open space (Project). The Project is bounded on the north by Eight Mile Road , to the east by West Lane , and to the west by Lower Sacramento Road (APNs 084-050-06, -07, -08, -14, -27, and -28).
The District offers the following comments at this time regarding the Project:
1) Construction Emissions
The District recommends, to further reduce impacts from construction-related diesel exhaust emissions, the Project should utilize the cleanest available off-road construction equipment.
2) Voluntary Emission Reduction Agreement
Per the DEIR, Table 3.3-10 (Operational Project Generated Emissions - Mitigated) demonstrates Project operational emissions are expected to exceed the District's significance thresholds. Therefore, the District recommends the DEIR be revised to include a Voluntary Emission Reduction Agreement (VERA) for this Project.
A VERA is a mitigation measure by which the project proponent provides pound-forpound mitigation of emissions increases through a process that develops, funds, and implements emission reduction projects, with the District serving a role of administrator of the emissions reduction projects and verifier of the successful mitigation effort. To implement a VERA, the project proponent and the District enter Northern Region
4800 Enterprise Way
Modesto, CA 95356-8718
Tel: (209) 557-6400 FAX: (209) 557-6475
Samir Sheikh
Executive Director/Air Pollution Control Officer
Central Region (Main Office)
1990 E. Gettysburg Avenue
Fresno, CA 93726-0244
Tel: (559) 230-6000 FAX: (559) 230-606 1
www.valleyair.org www.healthyairliving.com
Southern Region
34946 flyover Court
Bakersfield, CA 93308-9725
Tel: (661) 392-5500 FAX: (661) 392-5585
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into a contractual agreement in which the project proponent agrees to mitigate project specific emissions by providing funds for the District's incentives programs.
The funds are disbursed by the District in the form of grants for projects that achieve emission reductions. Thus, project-related impacts on air quality can be mitigated.
Types of emission reduction projects that have been funded in the past include electrification of stationary internal combustion engines (such as agricultural irrigation pumps), replacing old heavy-duty trucks with new, cleaner, more efficient heavy-duty trucks, and replacement of agricultural equipment with the latest generation technologies.
In implementing a VERA, the District verifies the actual emission reductions that have been achieved as a result of completed grant contracts, monitors the emission reduction projects, and ensures the enforceability of achieved reductions. After the project is mitigated, the District certifies to the Lead Agency that the mitigation is completed, providing the Lead Agency with an enforceable mitigation measure demonstrating that project-related emissions have been mitigated. To assist the Lead Agency and project proponent in ensuring that the environmental document is compliant with CEQA, the District recommends the environmental document includes an assessment of the feasibility of implementing a VERA. 3) Health Risk Screening/Assessment
Although the DEIR includes a discussion on sensitive receptors and sources of Toxic Air Contaminants (TACs), the DEIR did not assess the potential air quality impacts from the Project to nearby sensitive receptors. Additionally, there are residential units surrounding the project area. The Project may have the potential to impact sensitive receptors (residences, businesses, hospitals, day-care facilities, health care facilities, etc.). Therefore, the District recommends that the City evaluate the risk associated with the Project for sensitive receptors in the area and mitigate any potentially significant risk to help limit exposure of sensitive receptors to emissions.
To determine potential health impacts on surrounding receptors (residences, businesses, hospitals, day-care facilities, health care facilities, etc.) a Prioritization and/or a Health Risk Assessment (HRA) should be performed for the Project. These health risk determinations should quantify and characterize potential TACs identified by the Office of Environmental Health Hazard Assessment/California Air Resources Board (OEHHA/CARB) that pose a present or potential hazard to human health.
Health risk analyses should include all potential air emissions from the project, which include emissions from construction of the project, including multi-year construction, as well as ongoing operational activities of the project. Note, two common sources of TACs can be attributed to diesel exhaust emitted from heavy-duty off-road earth moving equipment during construction, and from ongoing operation of heavy-duty on-road trucks.
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Prioritization (Screening Health Risk Assessment):
A "Prioritization" is the recommended method for a conservative screening-level health risk assessment. The Prioritization should be performed using the California Air Pollution Control Officers Association's (CAPCOA) methodology. Please contact the District for assistance with performing a Prioritization analysis.
The District recommends that a more refined analysis, in the form of an HRA, be performed for any project resulting in a Prioritization score of 10 or greater. This is because the prioritization results are a conservative health risk representation, while the detailed HRA provides a more accurate health risk evaluation .
Health Risk Assessment:
Prior to performing an HRA, it is strongly recommended that land use agencies/ project proponents develop and submit for District review a health risk modeling protocol that outlines the sources and methodologies that will be used to perform the HRA.
A development project would be considered to have a potentially significant health risk if the HRA demonstrates that the health impacts would exceed the District's established risk thresholds, which can be found here:
https://ww2.valleyair.org/permitting/cega/.
A project with a significant health risk would trigger all feasible mitigation measures.
The District strongly recommends that development projects that result in a significant health risk not be approved by the land use agency.
The District is available to review HRA protocols and analyses. For HRA submittals please provide the following information electronically to the District for review:
• HRA (AERMOD) modeling files
• HARP2 files
• Summary of emissions source locations, emissions rates, and emission factor calculations and methodologies.
For assistance , please contact the District's Technical Services Department by:
• E-Mailing inquiries to: [email protected]
• Calling (559) 230-5900
4) Ambient Air Quality Analysis
Per the DEi R, Table 3.3-10 (Operational Project Generated Emissions - Mitigated) demonstrates the Project is expected to exceed 100 pounds per day of emissions.
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performed. An AAQA uses air dispersion modeling to determine if emission increase from a project will cause or contribute to a violation of State or National Ambient Air Quality Standards. An acceptable analysis would include emissions from both project-specific permitted and non-permitted equipment and activities.
The District recommends consultation with District staff to determine the appropriate model and input data to use in the analysis.
Specific information for assessing significance, including screening tools and modeling guidance, is available on line at the District's website :
https://ww2. va lie ya ir .o rg/perm itting/cega/.
5) Clean Lawn and Garden Equipment in the Community
Since the Project consists of residential development, gas-powered residential lawn and garden equipment have the potential to result in an increase of NOx and PM2.5 emissions. Utilizing electric lawn care equipment can provide residents with immediate economic, environmental, and health benefits. The District recommends the Project proponent consider the District's Clean Green Yard Machines (CGYM) program which provides incentive funding for replacement of existing gas powered lawn and garden equipment. More information on the District CGYM program and funding can be found at: https://ww2.valleyair.org/grants/zero-emissionlandscaping-eguipment-voucher-program/. 6) District Rules and Regulations
The District issues permits for many types of air pollution sources, and regulates some activities that do not require permits. A project subject to District rules and regulations would reduce its impacts on air quality through compliance with the District's regulatory framework. In general, a regulation is a collection of individual rules, each of which deals with a specific topic. As an example, Regulation II (Permits) includes District Rule 2010 (Permits Required), Rule 2201 (New and Modified Stationary Source Review), Rule 2520 (Federally Mandated Operating Permits), and several other rules pertaining to District permitting requirements and processes.
The list of rules below is neither exhaustive nor exclusive. Current District rules can be found online at: https://ww2.valleyair.org/rules-and-planning/current-district-rulesand-regulations. To identify other District rules or regulations that apply to future projects, or to obtain information about District permit requirements, the project proponents are strongly encouraged to contact the District's Small Business Assistance (SBA) Office at (209) 557-6446.
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6a) District Rules 2010 and 2201 -Air Quality Permitting for Stationary Sources
Stationary Source emissions include any building, structure, facility, or installation which emits or may emit any affected pollutant directly or as a fugitive emission. District Rule 2010 (Permits Required) requires operators of emission sources to obtain an Authority to Construct (ATC) and Permit to Operate (PTO) from the District. District Rule 2201 (New and Modified Stationary Source Review) requires that new and modified stationary sources of emissions mitigate their emissions using Best Available Control Technology (BACT).
This Project may be subject to District Rule 2010 (Permits Required) and Rule 2201 (New and Modified Stationary Source Review) and may require District permits. Prior to construction, the Project proponent should submit to the District an application for an ATC. For further information or assistance, the project proponent may contact the District's SBA Office at (209) 557-6446. 6b) District Rule 9510 - Indirect Source Review (ISR)
The Project is subject to District Rule 9510 because it will receive a projectlevel discretionary approval from a public agency and will equal or exceed 50 residential units.
The purpose of District Rule 9510 is to reduce the growth in both NOx and PM emissions associated with development and transportation projects from mobile and area sources; specifically, the emissions associated with the construction and subsequent operation of development projects. The ISR Rule requires developers to mitigate their NOx and PM emissions by incorporating clean air design elements into their projects. Should the proposed development project clean air design elements be insufficient to meet the required emission reductions, developers must pay a fee that ultimately funds incentive projects to achieve off-site emissions reductions.
Per Section 5.0 of the ISR Rule, an Air Impact Assessment (AIA) application is required to be submitted no later than applying for project-level approval from a public agency. As of the date of this letter, the District has not received an AIA application for this Project. Please inform the project proponent to immediately submit an AIA application to the District to comply with District Rule 9510 so that proper mitigation and clean air design under ISR can be incorporated into the Project's design. One AIA application should be submitted for the entire Project.
Information about how to comply with District Rule 9510 can be found online at:
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The AIA application form can be found online at:
https://ww2.valleyair.org/permitting/indirect-source-review-rule-overview/formsand-applications/ District staff is available to provide assistance and can be reached by phone at (559) 230-5900 or by email at [email protected].
6c) District Rule 4002 (National Emissions Standards for Hazardous Air Pollutants)
The Project will be subject to District Rule 4002 since the Project will include demolition and removal of existing structures. To protect the public from uncontrolled emissions of asbestos, this rule requires a thorough inspection for asbestos to be conducted before any regulated facility is demolished or renovated. Any asbestos present must be handled in accordance with established work practice standards and disposal requirements.
Information on how to comply with District Rule 4002 can be found online at:
https://ww2.valleyair.org/compliance/demolition-renovation/. 6d) District Rule 4601 (Architectural Coatings)
The Project will be subject to District Rule 4601 since it is expected to utilize architectural coatings. Architectural coatings are paints, varnishes, sealers, or stains that are applied to structures, portable buildings, pavements or curbs.
The purpose of this rule is to limit VOC emissions from architectural coatings.
In addition, this rule specifies architectural coatings storage, cleanup and labeling requirements. Additional information on how to comply with District Rule 4601 requirements can be found online at:
https://ww2.valleyair.org/media/tkgjeusd/rule-4601 .pdf 6e) District Regulation VIII (Fugitive PM10 Prohibitions) The project proponent may be required to submit a Construction Notification Form or submit and receive approval of a Dust Control Plan prior to commencing any earthmoving activities as described in Regulation VIII, specifically Rule 8021 - Construction, Demolition, Excavation, Extraction, and Other Earthmoving Activities.
Should the project result in at least 1-acre in size , the project proponent shall provide written notification to the District at least 48 hours prior to the project proponents intent to commence any earthmoving activities pursuant to District Rule 8021 (Construction, Demolition, Excavation, Extraction, and Other Earthmoving Activities). Also, should the project result in the disturbance of 5- acres or more, or will include moving, depositing, or relocating more than 2,500 EXHIBIT 1
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cubic yards per day of bulk materials, the project proponent shall submit to the District a Dust Control Plan pursuant to District Rule 8021 (Construction, Demolition, Excavation, Extraction, and Other Earthmoving Activities). For additional information regarding the written notification or Dust Control Plan requirements, please contact District Compliance staff at (559) 230-5950.
The application for both the Construction Notification and Dust Control Plan can be found online at: https://ww2.valleyair.org/media/fm3jrbsg/dcp-form.docx Information about District Regulation VIII can be found online at:
https://ww2.valleyair.org/dustcontrol
6f) District Rule 4901 - Wood Burning Fireplaces and Heaters The purpose of this rule is to limit emissions of carbon monoxide and particulate matter from wood burning fireplaces, wood burning heaters, and outdoor wood burning devices. This rule establishes limitations on the installation of new wood burning fireplaces and wood burning heaters.
Specifically, at elevations below 3,000 feet in areas with natural gas service, no person shall install a wood burning fireplace, low mass fireplace, masonry heater, or wood burning heater.
Information about District Rule 4901 can be found online at:
https://ww2.valleyair.org/compliance/residential-wood-smoke-reductionprogram/ 6g) Other District Rules and Regulations
The Project may also be subject to the following District rules: Rule 4102 (Nuisance) and Rule 4641 (Cutback, Slow Cure, and Emulsified Asphalt, Paving and Maintenance Operations).
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7) District Comment Letter
The District recommends that a copy of the District's comments be provided to the Project proponent.
If you have any questions or require further information, please contact Dylan Casares by e-mail at [email protected] or by phone at (559) 230-6574.
Sincerely,
Tom Jordan
Director of Policy and Government Affairs
For: Mark Montelongo
Program Manager
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Response to Letter E: San Joaquin Valley Air Pollution Control District Response E-1: This comment is noted, as this comment provides an introductory statement, introducing the comment letter and summarizing the Project details. No further response to this comment is warranted.
Response E-2: As described in Table 3.3-12 of Section 3.3, Air Quality, of the Draft EIR, the proposed Project would not generate construction-related emissions that would exceed the San Joaquin Valley Air Pollution Control District (SJVAPCD) thresholds for constructiongenerated emissions. Therefore, mitigation to reduce construction-related criteria pollutant emissions would not be required. Nevertheless, regardless of emission quantities, the SJVAPCD requires construction-related control measures in accordance with their rules and regulations. Implementation of these control measures, as provided on pages 3.3-37 and 3.3-38 of the Draft EIR (incorporated as mitigation measures), would further reduce proposed Project construction related emissions to the extent possible.
Response E-3: This comment is noted. Mitigation Measure 3.3-4 has been added to the errata, to reflect this comment. Mitigation Measure 3.3-4 of the FEIR requires the City to educate the Project applicant(s) on the benefits of a VERA, and requires the Project applicant(s) to enter into a VERA with the SJVAPCD, if emissions reductions associated with mandatory compliance with SJVAPCD’s Rule 9510 are not sufficient to reduce emissions to below the applicable SJVAPCD thresholds of significance for operation ROG. If conditions warrant participation in a VERA, the VERA shall demonstrate a reduction in emissions that reduces the ROG operational emissions to below the applicable threshold, through a process that funds and implements emissions reduction projects within the SJVAB. The types of emission reduction projects that could be funded include replacing old heavy-duty trucks with cleaner, more efficient heavy-duty trucks, for example. If a VERA is found to be required, and the applicant elects to enter into one, the project applicant shall engage in a discussion with SJVAPCD prior to the adoption of the VERA to ensure that feasible mitigation has been identified to reduce emissions to a less-than-significant level.
It is noted that Rule 9510 is a regulation that is imposed by the SJVAPCD to collect fees for emissions that exceed the threshold of significance established by the SJVAPCD after all calculated onsite and offsite mitigation, from construction and operation of the building/end user, can be calculated and is applied. The proposed Project is subject to the SJVAPCD Rule 9510 (Indirect Source Review [ISR] rule), which could result in substantial mitigation of emissions beyond what is reflected in the modeling outputs provided in the EIR. The reductions are accomplished by the incorporation of measures into individual projects and/or by the payment of an Indirect Source Rule fee for any required reductions that have not been accomplished through Project mitigation commitments. The actual calculations will be accomplished by the SJVAPCD and project applicants through the regulatory permitting process as the Project (i.e., or portions of the Project) are brought forward for approval under Rule 9510. The Project applicant would be required to pay the ISR fee to the SJVAPCD at that time. Ultimately, the SJVAPCD utilizes the fees to fund offsite projects that reduce emissions to at, or below, the thresholds of significance EXHIBIT 1
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established by the SJVAPCD. The performance-based metric for each individual case, is actual emissions compared to the threshold. No further response to this comment is warranted.
Response E-4: The proposed Project is primarily a residential project which will provide up to 1,411 units (assuming the school site is developed with single-family residential units), which also includes parks, trails, and open space. The proposed Project is not a Project that would be considered to have potential to generate significant levels of TACs. That is, overall, the risk of the Project to generate TACs which would exceed the SJVAPCD’s TAC thresholds is negligible.
Moreover, as described on pages 3.3-41 of the Draft EIR, residences are proposed as part of the Project, which are considered traditional sensitive receptors. However, no residences would be located within 500 feet of a freeway, urban road with 100,000 vehicles/day or more, or a rural road with 50,000 vehicles/day or more. Additionally, under CEQA, an EIR need not analyze the impacts of the existing environment on the Project.
In conclusion, there are virtually no residual TAC emissions and corresponding elevated cancer risk anticipated after Project construction. The proposed Project is not anticipated to generate any notable long-term, operational sources of TAC emissions because the proposed Project would only include residential uses and public open space. The Project would not include heavy industrial uses or other land uses typically associated with stationary sources of TACs.
It should be noted that the mobile vehicles generated by the Project during operation would generate ultrafine particles (UFPs) through vehicle emissions, braking, and tire wear. Like PM in general, (though generating even higher risk per unit than larger particle sizes) UFPs are notable for their potential to generate chronic risks associated with cardiovascular disease, potential long-term loss of long-function, and cancer. According to a recent study prepared for the European Geosciences Union, UFPs vary widely as a proportion of PM overall, depending on location; specifically, the PM0.1 to PM2.5 ratio analyzed in approximately 39 cities in the United States varied from approximately 1% to 16%.1 These factors vary so widely because the sources of PM0.1 vary substantially from city to city. For example, cities that are located close to substantial sources of natural gas combustion have higher PM0.1 to PM2.5 ratios, since almost all the PM emitted by natural gas combustion is in the PM0.1 size fraction, whereas this is only true for less than half of the PM emitted by gasoline and diesel fuel combustion. Taken together, these facts support the potential importance of natural gas combustion for ambient PM0.1 concentrations.
1 Venecek, M. A., Yu, X., and Kleeman, M. J.: Predicted ultrafine particulate matter source contribution across the continental United States during summertime air pollution events, Atmos. Chem. Phys., 19, 9399–9412, https://doi.org/10.5194/acp-19-9399-2019, 2019.
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The city analyzed in the study with the greatest similarity to the City of Stockton (i.e. where the Project is located) was the City of Bakersfield, given its similarity in location within the Central Valley region. The ratio of PM0.1 to PM2.5 for Bakersfield was found to be approximately 11 percent. Absent data specific to the City of Stockton, this data is presumed to be the best available data and reasonable for use in estimating PM0.1 levels in this case. Therefore, given the Project’s estimated 3.5 tons per year of PM2.5 (see Table
3.3-10), the total PM0.1 generated by the Project is estimated to be approximately 0.39 tons per year (780 lbs/year). This is equivalent to 2.14 lbs/day of PM0.1. While there is not specifically a quantitative threshold of significance established by the SJVAPCD for PM0.1, the quantity estimated is considered small relative to thresholds established for other particulate matter. From an incremental health perspective, this level of UFPs generated by the Project would not be substantial. As such, the Project would not result in substantial UFP emissions that may affect nearby receptors.
Response E-5: The proposed Project would not exceed 100 pounds per day of emissions, contrary to the commentor’s claim. See Appendix B (i.e. CalEEMod output) of the Draft EIR for further detail. Also see the errata changes made to Section 3.0 of this FEIR, for additional detail.
Therefore, an AAQA would not be required.
Response E-6: The Project proponent will consider utilizing the District’s Clean Green Yard Machines program, which provides incentive funding for replacement of existing as powered lawn and garden equipment. However, it should be noted that, nevertheless, any mandatory requirements in this regard would not be feasible. For a mitigation measure to be feasible, it must be able to be meaningfully monitored and enforced. Utilizing green yard machines would occur during the Project operation by the future residents of the Project; however, for this measure to be a feasible mitigation measure, the City would be required to police the choice of individual project residents indefinitely. The City itself does not have the means do monitor and enforce such activities. Instead, the mitigation measures included within the EIR are based on regulatory and other state requirements, which are enforceable at the state level, as well as other measures that can be monitored and enforced. It should be noted, however, that Mitigation Measure 3.3-5 has been added to the errata, which requires the Project applicant(s) to consider the Air District’s Clean Green Yard Machines (CGYM) program, which provides incentive funding for replacement of existing gas powered lawn and garden equipment.
Response E-7: The proposed Project will comply with all applicable SJVAPCD rules and regulations, including those cited by the commentor (as applicable).
Response E-8: The proposed Project will comply with all applicable SJVAPCD rules and regulations, including those cited by the commentor (as applicable), including Rule 9510.
Response E-9: The commentor identifies that SJVAPCD Rule 4002 may be applicable to the proposed Project. The proposed Project will comply with all applicable SJVAPCD rules and regulations, including those cited by the commentor (as applicable).
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Response E-10: The proposed Project will comply with all applicable SJVAPCD rules and regulations, including those cited by the commentor (as applicable).
Response E-11: The proposed Project will comply with all applicable SJVAPCD rules and regulations, including those cited by the commentor (as applicable).
Response E-12: The proposed Project will comply with all applicable SJVAPCD rules and regulations, including those cited by the commentor (as applicable).
Response E-13: The proposed Project will comply with all applicable SJVAPCD rules and regulations, including those cited by the commentor (as applicable).
Response E-14: A copy of the SJVAPCD’s comments will be provided to the Project proponent.
Response E-15: The commentor provides their contact information. No response to this comment is warranted.
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F-1
F-2
September 30, 2024
Nicole Moore, Contract Planner
Stockton Community Development Deptment.
Via e-mail
[email protected]
Re: Comments on the Draft Environmental Impact Report for the LeBaron Ranch Project Ms. Moore et al:
The Sierra Club submits the following comments on the Draft Environmental Impact Report (DEIR) for the LeBaron Ranch Project.
Please ensure that all future digital notices regarding this and every other discretionary project that are pending with the City are sent to Eric Parfrey, Sierra Club, at [email protected].
The 230-acre project proposes 1,217 single family residential units with lot sizes that would range from 3,375 to 6,000 square feet (typical "suburban sprawl" densities), plus a token 194 high density residential units, for a total residential unit count of 1,411 units . The subdivision would house an additional 4,400 residents.
The density of subdivision is not consistent with the City of Stockton's Housing Action Plan under review, which includes the following statements:
Stockton should prioritize infill housing and produce more small, attached, housing units to encourage sustainable homeownership at all income levels. Building condos and townhomes could ease the shortage of for-sale homes and complement the construction 1 EXHIBIT 1
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of market rate and below market rate single-family homes and apartments for a more diverse range of housing options.
The DEIR Must be Augmented with New Analysis and Recirculated In general, we are appalled that this DEIR substantially understates, and fails to fully analyze, the severity and extent of significant project-related effects on air quality, greenhouse gas ("GHG") emissions, public health, transportation , among other issues. The environmental documentation for the Project is thus inadequate as an informational document and violates the minimum standards of adequacy under the California Environmental Quality Act ("CEQA"), Public Resources Code§ 21000 et seq., and the CEQA "Guidelines," California Code of Regulations, title 14, § 15000 et seq. Moreover, the DEIR identifies virtually no substantial mitigation measures to reduce the Project's impacts, even though such measures are readily available, feasible , and commonly required.
We will be watching carefully to ensure that the City requires additional analysis and mitigation before this project can move forward.
We believe the subdivision design should be re-worked and that additional work to reduce GHG emissions must be completed through the recirculation of a revised DEIR before the City may proceed. We will strenuously object to any attempt to add significant new analysis and information in the Final EIR at the last minute.
The DEIR's Analysis of the GHG Impacts is Insufficient and the Conclusion that Impacts are Less Than Significant is Unsupported.
The DEIR asserts that the greenhouse gas (GHG) emissions impacts from the Project would be less than significant despite the fact that GHG emissions were quantified and are substantial.
The DEIR asserts that because Air District does not have an adopted threshold that has been updated, a simple consistency assessment with relevant plans is sufficient to reach a conclusion of less than significant and ignore the 16,118 metric tons of Project-generated GHG emissions released on an annual basis into the San Joaquin Valley air basin. (Emissions are expressed in annual metric tons of CO2 equivalent units of measure (i.e., MT CO2e), based on the global warming potential of the individual pollutants). An additional 3,643 tons would be generated during construction. See DEIR at 3.7-27.
2 EXHIBIT 1
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This conclusory approach does not work. Protect the Historic Amador Waterways v. Amador Water Agency (2004) 116 Cal. App. 4th 1099, 1109 ("in preparing an EIR, the agency must consider and resolve every fair argument that can be made about the possible significant environmental effects of a project, irrespective of whether an established threshold of significance has been met with respect to any given effect") dictates that the lead agency can't simply turn away from the volume of GHG emissions generated by the Project. The Project generates substantial GHG emissions, is not in conformance with the City of Stockton Climate Action Plan, and the DEIR makes no attempt to establish a threshold of significance against which the project can be measured. The lead agency's responsibility here cannot be ignored.
By ignoring that the Project's emissions are significant, the DEIR fails to adopt even the most routine mitigation measures to reduce GHG emissions and contribute the Project's "fair share" of what will be required to achieve long-term climate goals for the State. Since 2010, it has become clear from a scientific perspective that any additional GHG emissions will contribute to a serious and growing climate crisis.1 Recognizing this reality, in 2018 Governor Brown signed Executive Order 55-18 calling for the state to achieve carbon neutrality as soon as possible and no later than 2045. 2 Given these facts on the ground, the EIR should establish a net zero threshold for new emissions . See e.g., CARB 2017 Scoping Plan at 101 ("Achieving no net additional increase in GHG emissions, resulting in no contribution to GHG impacts, is an appropriate overall objective for new development.")3 Not only does the EIR neglect to reference EO 55-18, it also fails to explain why this project should not be judged by a significance threshold requiring no net increase in GHG emissions, since that is the standard necessary to comply with the State's climate change plans and policies.
As the Supreme Court found in Center for Biological Diversity v. California Dept. of Fish & Wildlife (2015) 62 Cal.4th 204 ("Newhall Ranch"), new projects-such as this Project-may require a greater level of emission reduction because "[d]esigning new buildings and infrastructure for maximum energy efficiency and renewable energy use is likely to be easier, 1 Summary for Policymakers (SPM) presents key findings of the Working Group I (WGI) contribution to the Intergovernmental Panel on Climate Change (IPCC):
https://www.ipcc.ch/report/ar6/wg1/downloads/report/lPCC_AR6_WGI_SPM.pdf 2 Executive Order to Achieve Carbon Neutrality: https://www.ca.gov/archive/gov39/wp content/uploads/2018/09/9.10.18-Executive-Order pdf
3 California's 2017 Climate Change Scoping Plan:
https://ww2. a rb. ca.gov /sites/defau lt/fil es/classic/cc/scoping pla n/scopi ng_plan _ 2017. pdf? utm_rnedium=email&utm_source=govdelivery
3 EXHIBIT 1
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and is more likely to occur, than achieving the same savings by retrofitting of older structures and systems." Newhall Ranch, 62 Cal.4th at 226.
The Project Fails to Meet the GHG Reduction Target in the Stockton CAP Meanwhile, the DEIR asserts that the Project "is not inconsistent" with the sustainability measures included with the City of Stockton Climate Action Plan (CAP). The CAP includes community and municipal GHG reduction targets, and includes a clearly stated GHG reduction target. Specifically, the CAP states: "the City now proposes approximately 10% below 2005 levels as its GHG reduction goal which would be consistent with the level of reductions needed at the state level to meet the AB 32 goal, compared to statewide 2005 levels ." See City of Stockton CAP4 at ES-7.
To comply with CEQA's dictates and the City of Stockton CAP, the EIR must include an analysis of the project's per capita GHG emissions and whether it is achieving a 10% reduction from the City's 2005 baseline. If not, the DEIR must be revised and recirculated to conclude the Project is not in conformance with the CAP and therefore has significant GHG impacts.
In fact, the DEIR states unequivocally that "As shown in the following tables (Table 3.7-3 and Table 3.7-4), the annual GHG emissions associated with the proposed Project would be approximately 16,118 MT CO2e under the unmitigated scenario, and 16,103 MT CO2e under the mitigated scenario (i.e. with implementation of the mitigation measures provided in Section
3.3: Air Quality of the Draft EIR)." This reduction amounts to a miniscule 103 MT CO2, or a reduction of less than 1 %.
Qualitative Analysis of GHG is Not Supported by Factual Evidence With regard to the qualitative analysis on GHG impacts, the DEIR incorrectly and without supportive evidence asserts the Project would not be inconsistent with the 2022 CARS Scoping Plan. Regardless, the unconvincing conclusion of consistency is based on no substantial evidence.
For example, the CARS VMT Reduction policies state:
4 City of Stockton Climate Action Plan (2014):
https://cms3.revize.com/revize/stockton/Documents/Business/Economic%20Development/Contracts%20&%20Purch asing/BidFlash/Administration%20Services/PUR%2024-030/Climate_Action_Plan_August_2014.pdf 4 EXHIBIT 1
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cont’d
Reduce or eliminate minimum parking standards
Implement Complete Streets policies and investments, consistent with general plan circulation element requirements
Increase access to public transit by increasing density of development near transit, improving transit service by increasing service frequency, creating bus priority lanes, reducing or eliminating fares, microtransit, etc.
Increase public access to clean mobility options by planning for and investing in electric shuttles, bike share, car share, and walking
Implement parking transportation demand pricing strategies The DEi R's inadequate "consistency" response states, with no factual support:
No Conflict. Although this goal is not applicable to an individual residential development project, the Project is implementing neighborhood design improvements such as pedestrian network improvements and traffic calming measures. Furthermore, the proposed Project would enable walkable development. See DEIR at 3.7-28.
The DEIR then offers the following weak justification for the assertion that the GHG impacts are less than significant, again without citing any substantial evidence:
"The proposed Project would be consistent with relevant plans, policies, and regulations associated with GHGs, notably the most recent version of the CAR B's Scoping Plan, the SJCOG's 2022 RTP/SCS, and the City of Stockton Climate Action Plan. This would ensure that the proposed Project would be consistent with, and would not impair, the State's carbon neutrality standard by year 2045 as established under AB 1279. The State is making progress toward reducing GHG emissions in key sectors such as transportation, industry, and electricity. Since the Project would be consistent with State GHG Plans , it would not impede the State's goals of reducing GHG emissions 40 percent below 1990 levels by 2030, and of achieving carbon neutrality by 2045. The proposed Project would make a reasonable fair share contribution to the State's GHG reduction goals, by implementing a wide array of Project features that would substantially reduce GHG emissions and therefore, the proposed Project's GHG emissions would be considered to have a less than significant impact." See DEIR at 3.7- 35 5
EXHIBIT 1
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F-6
cont’d
F-7
But these conclusory statements provide no evidence showing how a project that adds tens of thousands of tons of GHG emissions every year could be consistent with the goal of reducing GHG emissions 40 percent below 1990 levels by 2030. Moreover, reliance on vague "project features" to support a less-than significant determination is problematic because, unless these features are detailed and clarified as required mitigation, there is no guarantee their implementation will be successful and cannot be considered enforceable mitigation pursuant to CEQA requirement.
The EIR Must Incorporate Additional Feasible Mitigation Measures Because the project's mitigation measures fail to even come close to meeting a 10% reduction In GHG, numerous additional measures recommended by the San Joaquin Valley Air Pollution Control District and other regulatory agencies must be incorporated into the project. Some of these additional feasible mitigation measures, include, but are not limited to:
(1) clean fleet and clean construction equipment requirements (2) extensive use of on-site solar photovoltaic panels
(3) installation of electric vehicle charging infrastructure (4) Installation of clean residential heating devices such as certified wood burning residential fireplaces and wood stoves, natural gas fireplace inserts, or electric heat pumps. (5) encourages the siting of development projects with increased densities in order to reduce vehicle miles traveled (VMT) emissions and improve walkability and transit ridership in the area (6) locates development projects with high density near transit, which could promote the use of transit by people traveling to or from the project site. The use of transit could result in a mode shift and therefore could reduce VMT. The project should, at a minimum, include the following design features:
• A transit station/stop with high-quality, high-frequency bus service located within a 5- 10 minute walk (or roughly¼ mile from stop to edge of development), and/or • A rail station located within a 20 minute walk (or roughly½ mile from station to edge of development)
6 EXHIBIT 1
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• Fast, frequent, and reliable transit service connecting to a high percentage of regional destinations
• Neighborhood designed for walking and cycling encourages development projects to incorporate a greater percentage of smaller units into the design to allow a greater number of families to be accommodated on infill and transit-oriented development sites within a given building footprint and height limit. (7) promote the use of subsidized/discounted daily or monthly public transit passes. The project may also provide free transfers between all shuttles and transit to participants. These passes can be partially or wholly subsidized by the employer, school, or development. (8) utilize the following design elements to increase pedestrian access and connectivity:
• Provide continuous sidewalks separated from the roadway by landscaping and on-street parking.
• Provide on and off-site pedestrian facility improvements such as trails linking them to designated pedestrian commuting routes and/or on-site overpasses and wider sidewalks.
• Link cul-de-sacs and dead-end streets to encourage pedestrian and bicycle travel. • Provide traffic reduction modifications to project roads, such as: narrower streets, speed platforms, bulb-outs and intersection modifications designed to reduce vehicle speeds and to encourage pedestrian and bicycle travel.
• Provide pedestrian access between bus service and major transportation points and to destination points within the project.
(9) create local "light" vehicle networks , such as NEV networks. NEVs are classified in the California Vehicle Code as a "low speed vehicle". They are electric powered and must conform to applicable federal automobile safety standards. NEVs offer an alternative to traditional vehicle trips and can legally be used on roadways with speed limits of 35 MPH or less (unless specifically restricted). They are ideal for short trips up to 30 miles in length. To create an NEV network, the project will need to implement the necessary infrastructure, including NEV parking, 7 EXHIBIT 1
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cont’d
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charging facilities, striping, signage, and educational tools. NEV routes can be implemented throughout the project and can double as bicycle routes.5 The City must require this project developer to incorporate these and all other feasible mitigation measures to reduce GHG emissions and VMT.
The Subdivision Must be Redesigned and Reconfigured to Become as Efficient as Possible and to Meet GHG Reduction Goals
In our judgement, perhaps the most effective measures that could be implemented which could also significantly reduce GHG emissions are:
• improve pedestrian and bicycle links within and outside the project site, and • require the developer to contribute financially to link the project site with high frequency fixed route transit service,
Regarding the first point, as currently designed the layout of the subdivision map does not appear to comply with these specific General Plan policies:
LU-6.4C. Reduce Vehicle Miles Traveled (VMT) per household by planning new housing in closest proximity to employment centers, improving and funding public transportation and ridesharing, and facilitating more direct routes for pedestrians and bicyclists.
TR-3.2. Require new development and transportation projects to reduce travel demand and greenhouse gas emissions , support electric vehicle charging, and accommodate multi passenger autonomous vehicle travel as much as feasible.
TR-2.2A. Require major new development to incorporate and fund design features to promote safe and comfortable access to transit, such as a circulation network that facilitates efficient and connected bus travel, clear pedestrian and bicycle routes connecting origins and destinations to transit stops sheltered bus stops park-and-ride facilities and highly visible transit information and maps. (emphasis added)
5 See San Joaquin Valley Air Pollution Control District, Emission Reduction Clean Air Measures, https://VWl/2.valleyair.org/media/obOpweru/clean-air-measures.pdf. 8 EXHIBIT 1
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cont’d
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For example, the proposed subdivision map (Figs. 2.0-8-A, B) appears to feature numerous separate portions of the site that are accessed by rectangular roads that do not appear to be connected with pedestrian and bike facilities . This is critical without which local residents would not be able to connect with the "wellness" and other sidewalks and bike ways in a direct fashion, but would have to meander around on local streets. Please clarify the rationale for this outdated design.
All cul-de-sac type access roads must be reconfigured to allow pedestrian and bike trails to encourage direct access to the wellness and green bike paths.
In addition, the developer should be required to provide a "Safe Route to Schools" plan that specifies how school children may directly walk, bike, use electric scooters or skate boards, to the new LUSD K-8 school (if it is built), as well as to the McNair High School (and under construction City of Stockton library) located south of the project site on West Lane.
The EIR Must Require the Applicant to Link the Project Site with High Frequency Fixed Transit Service
The DEIR includes an existing Transportation Demand Management Mitigation Measure 3.13-1 which states:
The Project applicant shall work with the City of Stockton to implement feasible Transportation Demand Management (TOM) strategies, which would decrease the VMT generated by the Project. Specific potential TOM strategies include, but are not limited to, the following:
Provide public transit service, including improving San Joaquin Rapid Transit District (RTD) transit service connecting workers with existing and future residential developments;
Implement a fair value commuting program or other pricing of vehicle travel and parking; ...
Please clarify the details for "a fair value commuting program or other pricing of vehicle travel and parking." Presumably, this would have to be a citywide program, which we are dubious would ever be approved by our Council. Please don't include a measure in this list if it is not a politically viable measure that could be implemented in the short term. 9 EXHIBIT 1
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cont’d
The requirement in Mitigation Measure 3.13-1 to "Provide public transit service, including improving San Joaquin Rapid Transit District (RTD) transit service ... " is vague and unenforceable. The measure must be re-written to be much more specific and enforceable as a legal condition of approval. We propose much more specific wording below. If there is an issue of a legal CEQA nexus, the condition may require a separate development or contractual agreement between the developer, the City, and RTD.
This measure is critical because, as the DEIR notes, there is currently no fixed route transit service to the project site. The site is served by a "deviated fixed-route service" that does not directly allow residents of the new community board RTD Hopper buses. The DEIR states that:
"Metro Hopper is a deviated fixed-route service for areas within the Stockton city limits.
SJRTD operates 12 Hopper routes ... SJRTD operates County Hopper Route 93 along West Lane along the eastern edge of the Project site. This route travels between the Stockton Downtown Transit Center and the Lodi Transit Station. The route operates eight (8) times a day in the northbound direction, and 10 times a day in the southbound direction." DEIR at 3.13-6.
A "deviated fixed-route service" does not allow deviation from a very limited number of established stops, with only a deviation of one mile from the fixed route service which requires reservations two days in advance for all Hopper deviations. Hoppers will deviate up to two times per trip.
The current established stop for the Hopper 93 bus that is nearest the project site is at Mc Nair High School, south of the project on West Lane. The bus does not currently stop between McNair High School and the downtown Lodi transit center. The City should require this project to contribute the costs of providing one additional fixed stop along the Hopper route that would serve the new subdivision of 4,400 residents.
The above vague, unenforceable mitigation measure should be re-written as follows :
"The developer shall be required to contribute to the costs of providing one additional fixed stop on West Lane along the Hopper 93 route that would serve the new subdivision. The developer shall be responsible for funding the construction of a transit stop, plus any additional infrastructure that would be required to serve the new subdivision with transit service. In addition, the developer shall negotiate with San Joaquin Rapid Transit District to determine if 10 EXHIBIT 1
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F-9
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F-10
there are additional costs required to construct and serve this new stop, e.g., the cost of adding one new bus along the route. If there are additional costs, the developer shall be required to pay a fair share of those additional costs."
This or similar text would be in place of the existing measure: "Provide public transit service, including improving San Joaquin Rapid Transit District (RTD) transit service connecting workers with existing and future residential developments."
Transportation Impacts are Significant and More Mitigation Must be Required The subdivision would generate vehicle miles traveled (VMT) in excess of "significant standards." As shown in Table 3.13-1, under Baseline Year conditions, the proposed Project would generate 20.10 home-based VMT per resident, or a total of 35,749 vehicle miles traveled. (Conveniently, the table does not disclose this latter calculation but only states a citywide difference. This should be rectified in the Final EIR.) The text notes that "This would be 35 percent above the significance threshold . As a result, the Project is considered to have a significant impact on VMT. Under Cumulative Year conditions, the Project would generate 17.54 home-based VMT per resident. This would be 18 percent above the significance threshold. As a result, the Project is considered to have a significant impact on VMT." DEIR at 3-13.18
This amount of new traffic would have very dramatic impacts to local air quality. The DEIR states
As shown in Table 3.3-9 and Table 3.3-10, the proposed Project's operational criteria pollutant would exceed the applicable SJVAPCD thresholds of significance for ROG, even after implementation of mitigation measures (see Mitigation Measures 3.3-1 through 3.3-3, below). Therefore, the Project's criteria pollutant emissions would be considered to have a significant and unavoidable impact. Further the analysis of criteria air pollutants is inherently cumulative and impacts also would be cumulatively considerable.
The DEIR notes the obvious impacts of approving another low and medium density subdivision far from the major employment areas oft e City: a huge increase in VMT. The DEIR blames this increase not on this and other low density projects approved in in the wrong place , but on 11 EXHIBIT 1
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the "land use imbalance in the rest of the City and greater San Joaquin County geographic area." Rather than try to reduce this huge increase in VMT (and GHG and AQ impacts), the DEIR authors throw up their hands and blame poor regional planning that occurred decades ago.
However, the precise effectiveness of specific TOM strategies can be difficult to accurately measure due to several external factors such as types of tenants, employee responses to strategies, and changes to technology. Additionally. it is noted that with the current planned growth and development in the City of Stockton, the City's jobs-housing ratio is expected to increase in 2040, and city-wide home-based work VMT per worker is projected to increase. TOM strategies alone cannot eliminate VMT increases caused by land use imbalance in the rest of the City and greater San Joaquin County geographic ~
Based on the status of the City of Stockton's TIAG, even with the implementation of Mitigation Measure 3.13-1, the impact would remain significant and unavoidable when compared to the City of Stockton's VMT goal of reducing average home-based work VMT per worker from 18.56 miles to 15.66 miles. (emphasis added) DEIR at 3.13-21 The pathetic response to these very real issues underscore how important it is for the City to recirculate this EIR and present a new DEIR with more effective mitigation measures.
Potential Impacts to Some Endangered Species Have Not been Studied or Mitigated The DEIR fails to adequately analyze or mitigate potentially significant impacts to some listed species, such as the threatened Swainson's hawk, burrowing owl, and tricolored blackbird. The DEi R simply repeats the old refrain that coverage of the project under the San Joaquin County Multi-Species Habitat Conservation Plan (SJMSHCP) will automatically reduce any impacts to a less than significant level. This is unacceptable. The project applicant should have performed field surveys for these critical bird species, as was done for other sensitive species and disclosed the status of the land in the SJMSCP. (Maybe surveys were performed and hawks or other species were seen, but the DEIR is silent on this.) 12 EXHIBIT 1
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The DEIR notes that:
"The CNDDB currently contains records for Swainson's hawk, burrowing owl, and tricolored blackbird in the vicinity of the Project site. In addition to the species described above, common raptors, may nest in or adjacent to the Project site. New sources of noise and light during the construction and operational phases of the project could adversely affect nesters if they located adjacent to the Project site in any given year.
Additionally, the proposed Project would eliminate the agricultural areas on the Project site, which serve as potential foraging habitat for birds throughout the year." Then , the DEIR concludes that "Mitigation Measure 3.4-1 requires participation in the SJMSCP ... Mitigation Measure 3.4-1, would ensure that potential impacts to special status birds are reduced to a less than significant level." DEIR at 3-4.32 \Ne must remind you that the City of Stockton is the lead agency for complying with the California Environmental Quality Act (CEQA) for this project, not the SJCOG. In the event the SJCOG does not accept this project for SJMSCP coverage , the biological mitigation measures should explicitly require the developer to perform the protocol surveys now to determine the absence or presence of these bird species and implement the standard mitigation required by the agencies before any grading occurs.
Conclusion
\Ne will be watching carefully to ensure that the City requires additional analysis and mitigation before this project can move forward.
\Ne repeat that we believe the subdivision design should be re-worked and that additional work to reduce GHG emissions must be completed through the recirculation of a revised DEIR before the City may proceed. We will strenuously object to any attempt to add significant new analysis and information in the Final EIR at the last minute.
13 EXHIBIT 1
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Sincerely,
s/s Margo Praus, Chair,
Eric Parfrey, member
Mary Elizabeth M.S., R.E.H.S., Conservation Chair
Delta-Sierra Group, Sierra Club
cc: Robert Swanson, California Attorney General's Office Stanley Armstrong, California Air Resources Board
Patia Siong and Harout Sagherian, San Joaquin Valley Air Pollution Control District
Heather Minner and Winter King , Shute, Mihaly, & Weinberger Aaron Isherwood and Joya Manjur, Sierra Club Environmental Law Program Stockton City Council
Stockton Planning Commission
SJCOG
14 EXHIBIT 1
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Response to Letter F: Sierra Club, Delta-Sierra Group
Response F-1: Any future digital notices regarding this and every discretionary project that are pending with the City will be sent to Eric Parfrey at the Sierra Club.
Response F-2: The City’s Housing Element Update is required by state law and outlines the City’s housing policies, demographics, and housing capacity sites necessary to fulfill the City’s Regional Housing Needs Allocation (RHNA). The Housing Action Plan (HAP), separate from the City’s Housing Element, is an original planning document that creates a user manual to encourage housing development of all types in Stockton and will serve as a strategic plan to identify housing priority sites and outline recommendations for further action. It is a “toolkit” to encourage housing production, both affordable and market-rate.
While the Project does not include infill housing or small, attached housing units, the Project, the City’s HAP does not prohibit development such as the Project.
The proposed Project is generally consistent with the City’s land use vision for the Project site as set forth in the City’s General Plan. As noted on page 2.0-3 of Chapter 2.0, Project Description, of the Draft EIR, the Envision Stockton 2040 General Plan Land Use Map (Figure 2.0-5) designates the Project site as Low Density Residential, Medium Density Residential, High Density Residential, Institutional, and Parks and Recreation. Table 2.0-2 provides an existing land use summary of the Development Area per the 2040 Stockton General Plan. It is noted that the proposed Project would require a City of Stockton General Plan Amendment to the Land Use Element to change land uses on the Project site. However, changes to the General Plan Land Use Map are largely a reorganization of the precise locations for each land use within the boundary of the Project site as opposed to land use changes. Figures 2.0-6-A and 2.0-6-B illustrate the proposed Stockton General Plan land uses with and without the school site.
Table 2.0-4 summarizes the existing and proposed land use designations. As shown in Table 2.0-4 on page 2.0-10, the proposed Project would result in a 48.4-acre decrease in Low Density Residential uses, a 49.7-acre increase in Medium Density Residential uses, and a decrease of 9.9-acres of High Density Residential uses. As such, by substantially increasing the amount of Medium Density Residential units on the Project site, the proposed Project would increase the amount and range of smaller lot sizes, when compared to the City’s land use vision for the Project site as set forth in the City’s General Plan.
Response F-3: The commenter’s letter is fully addressed in this Final EIR. For detailed responses regarding the air quality, greenhouse gas (GHG), transportation, public health, and other issues raised by the commenter, see Responses F-4 through F-11. Minor changes and clarifications have been made to the Draft EIR text in response to two comment letters received, including letter F. However, the revisions herein do not result in new significant environmental impacts, do not constitute significant new information, nor do they alter the conclusions of the environmental analysis that would warrant recirculation of the Draft EIR pursuant to State CEQA Guidelines Section 15088.5. The Draft EIR is adequate EXHIBIT 1
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as an informational document and includes mitigation measures for potentially significant impacts that aim to reduce impacts to the extent feasible.
Response F-4: As stated on page 3.7-25 of the Draft EIR, the vast majority of individual projects do not generate sufficient GHG emissions to create a project-specific impact through a direct influence to climate change; therefore, the issue of climate change typically involves an analysis of whether a project’s contribution towards an impact is cumulatively considerable. “Cumulatively considerable” means that the incremental effects of an individual project are significant when viewed in connection with the effects of past projects, other current projects, and probable future projects (CEQA Guidelines, Section 15355).
For individual proposed projects, the significance of GHG emissions may be evaluated based on locally adopted quantitative thresholds, or consistency with a regional GHG reduction plan (such as a Climate Action Plan). The City of Stockton does have a formal GHG emissions reduction plan, in the form of the City of Stockton Climate Action Plan (CAP) (2014). However, it should be noted that this CAP is not considered a Qualified GHG Reduction Plan.
The Supreme Court’s decision in Center for Biological Diversity v. California Dept. of Fish & Wildlife (2015) 62 Cal.4th 204 (“Newhall Ranch”) determined that comparative analysis of GHG emissions could be applicable based on local or regional data of the project location. However, the court did not specify in detail what kind of comparative (quantitative) analysis would be considered adequate. An alternative way to satisfy the greenhouse gas requirements is to rely on a locally qualified CAP if it is adequately supported.
More recently, in the Golden Door Properties, LLF v. County of San Diego (“Golden Door”) case, the court indicated that, in order for a use of a quantitative threshold for GHGs to be applicable, the quantitative threshold must to be adopted by the City via resolution, ordinance, or regulation, needs to undergo include a public review process, and must to be supported by substantial evidence. Although the City of Stockton CAP included a GHG efficiency metric target for year 2020, the City of Stockton has not adopted a quantitative threshold for GHGs for years beyond year 2020 that satisfy these requirements.
Therefore, the use of a quantitative threshold to analyze GHGs is not appropriate for the Project.
Rather, the analysis approach utilized is an analysis of the Project’s consistency applicable GHG-related plans, policies, and regulations, which represents an appropriate approach to analyzing the potential for the Project to generate significant impacts related to GHGs.
This approach was taken in Section 3.7: Greenhouse Gases, Climate Change, and Energy, of the Draft EIR, and is consistent with current case law (including the Newhall Ranch and Golden Door cases). To that end, additional errata text has been added to Table 3.7-7 (now Table 3.7-8), to provide further clarification.
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Overall, the analysis provided in Section 3.7: Greenhouse Gases, Climate Change, and Energy, of the Draft EIR provides a qualitative assessment of the Project’s compliance with the applicable plans, policies, and regulations for the purposes of reducing greenhouse gas emissions. This analysis determined that the proposed Project would be consistent with relevant plans, policies, and regulations associated with GHGs, notably the most recent version of the CARB’s Scoping Plan, and the SJCOG’s 2022 RTP/SCS. Consistency with the City of Stockton Climate Action Plan is provided for information purposes only.
This would ensure that the proposed Project would be consistent with, and would not impair, the State’s carbon neutrality standard by year 2045 as established under AB 1279.
Separately, disclosure of the Project’s estimated construction and operation-related GHG emissions are provided for the purposes of disclosure. This approach does not ignore the volume of GHG emissions generated by the project; instead, the Project’s emissions are disclosed and the Project is evaluated based on its consistency with the applicable plans, policies, and regulations that are in place and have been designed to ensure that the Project would not generate significant GHG emissions.
Moreover, with the included analysis of the Project’s consistency with the 2022 Scoping Plan, the Draft EIR addresses whether the project is consistent with AB 1279, since the 2022 Scoping Plan has been designed consistent with the requirements of AB 1279, including the requirement to achieving carbon neutrality as soon as possible, but no later than 2045, and maintaining net negative GHG emissions thereafter, as well as to ensure that California reduces GHG emissions to 85 percent below 1990 levels by 2045. As provided in the Draft EIR, the Project would be consistent with the 2022 Scoping Plan, and would thereby be consistent with the requirements of AB 1279. No further response to this comment is warranted.
Response F-5: Table 3.3-7 (now Table 3.7-8 within the errata) in Section 3.7 of the Draft EIR provides an analysis of the consistency of the proposed Project with the GHG reduction measures contained within the City’s CAP, for informational purposes. To that end, additional errata text has been added to Table 3.7-7 (now Table 3.7-8 within the errata).
Moreover, as described in Response F-4, the Supreme Court’s decision in Center for Biological Diversity v. California Dept. of Fish & Wildlife (2015) 62 Cal.4th 204 (“Newhall Ranch”) determined that comparative analysis of GHG emissions could be applicable based on local or regional data of the project location. However, the court did not specify in detail what kind of comparative (quantitative) analysis would be considered adequate.
An alternative way to satisfy the greenhouse gas requirements is to rely on a locally qualified CAP if it is adequately supported. More recently, in the Golden Door Properties, LLF v. County of San Diego (“Golden Door”) case, the court indicated that, in order for a use of a quantitative threshold for GHGs to be applicable, the quantitative threshold must be adopted by the City via resolution, ordinance, or regulation, needs to undergo include a public review process, and must to be supported by substantial evidence. Although the City of Stockton Climate Action Plan (2014) includes a year 2020 quantitative threshold for GHGs, which did undergo such a process, it only applies to year 2020, which has EXHIBIT 1
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already come and gone. The City of Stockton has not adopted a quantitative threshold for any relevant future years for GHGs that satisfy these requirements. Therefore, the use of a quantitative threshold to analyze GHGs is not appropriate for the Project (it should be noted that errata text has been added within the local setting, under the “City of Stockton Climate Action Plan” header, to further describe why this is the case).
Rather, the analysis approach utilized is an analysis of the Project’s consistency with the applicable GHG-related plans, policies, and regulations, which represents an appropriate approach to analyzing the potential for the Project to generate significant impacts related to GHGs. This approach was taken in Section 3.7, Greenhouse Gases, Climate Change, and Energy, of the Draft EIR, and is consistent with current case law (including the Newhall Ranch and Golden Door cases).
Overall, the analysis provided in Section 3.7, Greenhouse Gases, Climate Change, and Energy, of the Draft EIR provides a qualitative assessment of the Project’s compliance with the applicable plans, policies, and regulations for the purposes of reducing greenhouse gas emissions. This analysis determined that the proposed Project would be consistent with relevant plans, policies, and regulations associated with GHGs, notably the most recent version of the California Air Resources Board (CARB) Scoping Plan, the San Joaquin Council of Governments (SJCOG) 2022 Regional Transportation Plan/Sustainable Communities Strategy (RTP/SCS), and the City of Stockton CAP. This would ensure that the proposed Project would be consistent with, and would not impair, the State’s carbon neutrality standard by year 2045 as established under AB 1279. Separately, disclosure of the Project’s estimated construction and operation-related GHG emissions are provided for the purposes of disclosure. This approach does not ignore the volume of GHG emissions generated by the project; instead, the Project’s emissions are disclosed and the Project is evaluated based on its consistency with the applicable plans, policies, and regulations that are in place and have been designed to ensure that the Project would not generate significant GHG emissions. Additional errata text has also been added to Section
3.7: Greenhouse Gases, Climate Change, and Energy, of the Draft EIR, including a new table summarizing the statewide GHG reduction strategies that apply to the Project, to provide additional disclosure.
Moreover, with the included analysis of the Project’s consistency with the 2022 Scoping Plan, the Draft EIR addresses whether the project is consistent with future statewide GHG reduction targets, including AB 1279, since the 2022 Scoping Plan has been designed consistent with the requirements of AB 1279, including the requirement to achieving carbon neutrality as soon as possible, but no later than 2045, and maintaining net negative GHG emissions thereafter, as well as to ensure that California reduces GHG emissions to 85 percent below 1990 levels by 2045. As provided in the Draft EIR, the Project would be consistent with the 2022 Scoping Plan, and would thereby be consistent with the requirements of future statewide GHG reduction targets, including AB 1279.
Response F-6: As stated on page 3.7-25 of the Draft EIR, the vast majority of individual projects do not generate sufficient GHG emissions to create a project-specific impact through a direct EXHIBIT 1
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influence to climate change; therefore, the issue of climate change typically involves an analysis of whether a project’s contribution towards an impact is cumulatively considerable. “Cumulatively considerable” means that the incremental effects of an individual project are significant when viewed in connection with the effects of past projects, other current projects, and probable future projects (CEQA Guidelines, Section 15355).
Overall, the analysis provided in Section 3.7, Greenhouse Gases, Climate Change, and Energy, of the Draft EIR provides a factually based and appropriate assessment of the Project’s compliance with the applicable plans, policies, and regulations for the purposes of reducing greenhouse gas emissions, to evaluate whether Project implementation would or would not generate GHGs that have a significant impact on the environment.
Ultimately, statewide policies are largely responsible for ensuring that the state achieves its long-term GHG emissions goals. This analysis determined that the proposed Project would be consistent with relevant plans, policies, and regulations associated with GHGs, notably the most recent version of the CARB’s Scoping Plan, and the SJCOG’s 2022 RTP/SCS, thus ensuring that the Project would not generate GHGs that have a significant impact on the environment.
For example, Table 3.7-5 (now Table 3.7-6, within the errata) demonstrates that the Project would be consistent with the 2022 Scoping Plan, since it would not conflict with the applicable 2022 Scoping Plan policies included within the plan, in order to ensure consistency with the AB 1279 GHG reduction targets of achieving carbon neutrality by 2045, and reducing anthropogenic emissions to 85 percent below 1990 levels by 2045.
The proposed Project’s operational emissions would be further reduced as regulations are implemented by the CARB and other State agencies to comply with the statewide GHG reduction targets. Many of these regulations are already identified in the 2022 Scoping Plan. Similarly, Table 3.7-6 (now Table 3.7-7 within the errata) demonstrates how the Project would not conflict with SJCOG’s 2022 RTP/SCS. Furthermore, Table 3.7- 7 (now Table 3.7-8, within the errata) describes how the Project would not conflict with the Stockton Climate Action Plan.
This would ensure that the proposed Project would be consistent with, and would not impair, the State’s carbon neutrality standard by year 2045 as established under AB 1279.
Separately, disclosure of the Project’s estimated construction and operation-related GHG emissions are provided for the purposes of disclosure. This approach does not ignore the volume of GHG emissions generated by the project; instead, the Project’s emissions are disclosed and the Project is evaluated based on its consistency with the applicable plans, policies, and regulations that are in place and have been designed to ensure that the Project would not generate significant GHG emissions.
It is also noted that the Project includes development of bicycle and pedestrian facilities throughout the Project site. For example, the proposed Project will provide both standard sidewalks, and as part of specific project roadways, enhanced sidewalks (also referred to as “wellness walks”) throughout the development, along with bike lanes along the major EXHIBIT 1
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arterials that the proposed Project fronts to offer additional bicycling and walking facilities for all of Stockton’s residents. Class IV bikeways (separated bikeways) will be provided along the major arterials that border the Project site; which includes Lower Sacramento Road, West Lane and Eight Mile Road. The Eight Mile Road cross section shows both a Class IV bikeway on Eight Mile Road and a Class I bike path between the proposed Project and the Woodbridge Irrigation Ditch (see Figure 2.0-9 illustrating bikeways in the green area of the roadway cross section). The Eight Mile Road cross section shows both a Class IV bikeway and Class I bike path. The Class I path is in the green area and Class IV is to the left of the sidewalk. The illustration shows a raised curb/divider next to right turn lane. Further, Mitigation Measure 3.13-1 requires the applicant to work with the City of Stockton to implement feasible Transportation Demand Management (TDM) strategies, which would decrease the VMT generated by the Project As noted on page 3.13-6 of Section 3.13 of the Draft EIR, SJRTD operates County Hopper Route 93 along West Lane along the eastern edge of the Project site. This route travels between the Stockton Downtown Transit Center and the Lodi Transit Station. The route operates eight (8) times a day in the northbound direction, and 10 times a day in the southbound direction.
The commenter’s suggestion to reduce parking standards is a City planning and policy measure and would not be effective for the proposed project. This is because such a measure is ineffective in locations where unrestricted street parking or other offsite parking is available nearby and has adequate capacity to accommodate project-related vehicle parking demand, which is the case for the area around the proposed Project. 2 Further, according to the LeBaron Ranch VMT Assessment (WK Shijo Consulting, LLC, 2023) parking pricing strategies are typically recommended for commercial projects, not residential projects such as the proposed Project.
3 This is, in part, because, when
limiting parking supply, a best practice is to do so at sites that are located near high quality alternative modes of travel (such as a rail station, frequent bus line, or in a higher density area with multiple walkable locations nearby).4 However, there would not be sufficient high quality nearby alternative modes of transportation would be available to serve the proposed Project, should parking pricing strategies be implemented. For limiting residential parking supply, the GHG Handbook notes, “This measure is ineffective in locations where unrestricted street parking or other offsite parking is available nearby and has adequate capacity to accommodate project-related vehicle parking demand.”
2 Refer to Measure T-15: Limit Residential Parking Supply, in CAPCOA’s GHG Handbook. Available at:
https://www.caleemod.com/handbook/index.html
3 Refer to Measure T-24: Implement Market Price Public Parking, in CAPCOA’s GHG Handbook. Available at:
https://www.caleemod.com/handbook/index.html
4 Refer to Measure T-15: Limit Residential Parking Supply, in CAPCOA’s GHG Handbook. Available at:
https://www.caleemod.com/handbook/index.html
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As noted above, the Project would implement Complete Streets, consistent with existing City policies and standards. See Figures 2.09-a through 2.0-9d of the Draft EIR for the street cross sections.
Mitigation Measure 3.13-1 requires coordination with public transit agencies regarding transit service connecting workers with existing and future residential developments, and also requires coordination with SJRTD regarding the potential for increasing service on Hopper Route 93. As such, this measure aims to increase access to public transit, as suggested by the commenter.
Response F-7: Mitigation measures for GHG impacts are not required or appropriate, since the proposed Project would have a ‘less than significant’ impact associated with GHG impacts (as provided in Section 3.7, Greenhouse Gases, Climate Change, and Energy of the Draft EIR).
As described under Comment Response F-4, for individual proposed projects, the significance of GHG emissions may be evaluated based on locally adopted quantitative thresholds, or consistency with a regional GHG reduction plan (such as a Climate Action Plan). The City of Stockton does have a formal GHG emissions reduction plan, in the form of the City of Stockton CAP (2014). The Supreme Court’s decision in Center for Biological Diversity v. California Dept. of Fish & Wildlife (2015) 62 Cal.4th 204 (“Newhall Ranch”) determined that comparative analysis of GHG emissions could be applicable based on local or regional data of the project location. However, the court did not specify in detail what kind of comparative (quantitative) analysis would be considered adequate.
Moreover, the City of Stockton CAP is not considered a Qualified GHG Reduction Plan, for the purposes of CEQA. An alternative way to satisfy the greenhouse gas requirements is to rely on a locally qualified CAP if it is adequately supported. More recently, in the Golden Door Properties, LLF v. County of San Diego (“Golden Door”) case, the court indicated that, in order for a use of a quantitative threshold for GHGs to be applicable, the quantitative threshold must to be adopted by the City via resolution, ordinance, or regulation, needs to undergo include a public review process, and must to be supported by substantial evidence. Although the City of Stockton CAP did include an efficiency target for year 2020, it did not include any efficiency targets for years after year 2020, and year 2020 has come and gone. Therefore, the City of Stockton has not adopted a quantitative threshold for GHGs that satisfy these requirements. Therefore, the use of a quantitative threshold to analyze GHGs is not appropriate for the Project.
Rather, the analysis approach utilized is an analysis of the Project’s consistency with the applicable GHG-related plans, policies, and regulations, which represents an appropriate approach to analyzing the potential for the Project to generate significant impacts related to GHGs. This approach was taken in Section 3.7, Greenhouse Gases, Climate Change, and Energy, of the Draft EIR, and is consistent with current case law (including the Newhall Ranch and Golden Door cases).
Overall, the analysis provided in Section 3.7, Greenhouse Gases, Climate Change, and Energy, of the Draft EIR provides a qualitative assessment of the Project’s compliance with the applicable plans, policies, and regulations for the purposes of reducing greenhouse EXHIBIT 1
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gas emissions. This analysis determined that the proposed Project would be consistent with relevant plans, policies, and regulations associated with GHGs, notably the most recent version of the CARB’s Scoping Plan, and the SJCOG’s 2022 RTP/SCS. This would ensure that the proposed Project would be consistent with, and would not impair, the State’s carbon neutrality standard by year 2045 as established under AB 1279.
Separately, disclosure of the Project’s estimated construction and operation-related GHG emissions are provided for the purposes of disclosure. Therefore, neither a specific quantitative reduction in GHG emissions associated with the Project, nor implementation of mitigation measures for GHG emissions, are required. Additional errata text has been added throughout 3.7, Greenhouse Gases, Climate Change, and Energy of the Draft EIR, where appropriate, to describe this in further detail. No further response to this comment is warranted.
Response F-8: While this comment is noted, this comment does not relate to CEQA. The proposed Project is required to be consistent with the General Plan, including the General Plan actions cited by the commentor. A General Plan policy consistency analysis is provided in Table 3.10-3 of Section 3.10 of the Draft EIR. As noted in Response F-6 and further described in various responses in Table 3.10-3, the Project includes development of bicycle and pedestrian facilities throughout the Project site which provide clear pedestrian and bicycle routes connecting the Project site to adjacent off-site developments.
The proposed onsite improvements would satisfy the City’s Complete Streets standards.
The Project includes an extension of the west-east trending Marlette Road that will provide several access points to the proposed development, and connect to West Lane and Lower Sacramento Road. West Lane and Lower Sacramento Road are the main arterial roadways providing access to the Development Area. The proposed Project includes annexation of right-of-way along Eight Mile Road, which will be improved to City of Stockton standards; however, access to the proposed development will not occur from Eight Mile Road, thus eliminating any conflicts with the flow of traffic on Eight Mile Road.
Project traffic will be directed to Marlette Road, except for one direct access point to West Lane, and then directed east or west along Marlette Road to West Lane and Lower Sacramento Road. These proposed improvements, as well as the proposed “wellness walk”, could be used by school-aged residents to get to and from nearby schools (including McNair High School).
Nothing cited by the commentor provides sufficient evidence that the Project would not comply with the General Plan policies cited by the commentor, or any other General Plan policies. Therefore, redesign and/or reconfiguration of the Project site is not warranted.
See Responses F-6 and F-9 regarding VMT reduction and transit.
Response F-9: Public transit is an important component of measures to vehicle miles traveled (VMT).
However, public transit is only one facet of a broader overall approach to reducing VMT.
To reduce VMT, it is important to consider and apply a broad and flexible range of EXHIBIT 1
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measures, selecting measures most effective to the individual site and set of users. As noted in Reponses F-6 and F-8, the Project includes development of bicycle and pedestrian facilities throughout the Project site in order to encourage non-automobile methods of travel and, thus, reduce VMT.
Mitigation Measure 3.13-1 as presented in the Draft EIR provides for consideration of a broader range of measures to reduce VMT. Because of the need to consider a broad range of measures, the overall structure of Mitigation Measure 3.13-1 has been retained in the EIR. Mitigation Measure 3.13-1 includes the following specific transportation demand management (TDM) strategy: “Implement a fair value commuting program or other pricing of vehicle travel and parking”. Further consideration was given to the feasibility of vehicle travel and parking pricing strategies. As noted by the commenter, this would have to be a citywide program, which is not under the control of the applicant.
Further, according to the LeBaron Ranch VMT Assessment (WK Shijo Consulting, LLC, 2023) parking pricing strategies are typically recommended for commercial projects, not residential projects such as the proposed Project.
5 Based on this further
consideration, this strategy was determined to be not feasible. Because of this, as suggested by the commenter, this strategy has been deleted from Mitigation Measure
3.13-1. Additionally, language has been included in the analysis in Section 3.13 to clarify Mitigation Measure 3.13-1; refer to Section 3.0 of this Final EIR.
The commenter provides specific language for re-writing Mitigation Measure 3.13-1. The language provided by the commenter is related to Hopper Route 93, which is operated by San Joaquin Regional Transit District (RTD). The commenter states Mitigation Measure
3.13-1 should be re-written to require the developer to contribute to the costs of one additional fixed stop on West Lane, plus additional infrastructure, and require the developer to negotiate with San Joaquin RTD to determine additional costs for the new stop, including the cost of one new bus.
Compliance with the measure, as proposed by the commenter would require the cooperation and active participation of San Joaquin RTD. This would include requiring San Joaquin RTD to: (1) agree to an additional stop on West Lane, (2) identify specific infrastructure needed for the additional stop, and (3) specify the type of vehicle that would be needed to serve the additional stop. San Joaquin RTD funding would also be required.
While the City, as the lead agency, has the authority to require some actions by the developer, the City does not have the authority to require another agency (in this case the San Joaquin RTD) to mitigate Project impacts. The City can encourage and support additional public transit serving the Project site, and provide infrastructure for a new bus stop. But the City cannot require San Joaquin RTD to add a bus stop. Because compliance with the measure as proposed by the commenter would require the cooperation and 5 Refer to Measure T-24: Implement Market Price Public Parking, in CAPCOA’s GHG Handbook. Available at:
https://www.caleemod.com/handbook/index.html
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active participation of San Joaquin RTD, the measure as proposed by the commenter is considered infeasible.
In response to the commenter, Mitigation Measure 3.13-1 has been modified to specifically address increasing service on Hopper Route 93. See Chapter 3.0, Revisions, of this Final EIR for the change in strike through and underline format.
Response F-10: The commenter refers to a calculated change of 35,749 VMT, and notes the table does not present the calculated change. In making this comment, it appears the commenter is referring to Table 3.13-2 in Section 3.13 of the Draft EIR. Table 3.13-2 does not present the amount of change in VMT because the applicable significance threshold is based on whether the Project would result in an increase in VMT. The significance threshold is not based on the quantity of the change in VMT, but that the proposed Project would generate 15 percent below the average VMT per resident in the City.
While the quantity of change in VMT does not affect the significance of the impact, the following revised version of Table 3.13-2 shows the quantity of change referred to by the commenter, for better clarity. See Chapter 3.0, Revisions, of this Final EIR for the change in strike through and underline format.
TABLE 3.13-2: VMT ANALYSIS – CITYWIDE TOTAL VMT
SCENARIO NO PROJECT WITH PROJECT
PROJECTRELATED
CHANGE
WITH PROJECT
VMT GREATER
THAN NO
PROJECT VMT?
Baseline Year Before Mitigation 5,184,549 5,220,298 35,749 Yes Baseline Year With Mitigation - 5,215,729 31,180 Yes
Cumulative Year Before Mitigation 6,597,410 6,636,505 39,095 Yes Cumulative Year With Mitigation - 6,632,517 35,107 Yes
As cited by the commenter, the Draft EIR discloses the impact of the Project on reactive organic gas (ROG) emissions and presents mitigation measures to reduce the impact. As described in the Draft EIR, even with implementation of the mitigation measures, the impact of the Project on ROG emissions would be significant and unavoidable.
The commenter states, “The DEIR blames this increase not on this and other low density projects approved in in (sic) the wrong place, but on ‘land use imbalance in the rest of the City and greater San Joaquin County geographic area.’ Rather than try to reduce this huge increase in VMT (and GHG and AQ impacts), the DEIR authors throw up their hands and blame poor regional planning that occurred decades ago.” The Draft EIR is an informational document to disclose the potential environmental impacts of the Project for decision-makers. The Draft EIR fully discloses impacts of the Project on VMT and air quality, describes the sources of the impacts, and presents feasible mitigation measures. In those cases where an impact is project-related, the Draft EIR discloses the impact. In those cases where an effect is not due to the Project, the Draft EIR explains the source of the effect.
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As cited by the commenter, the Draft EIR discloses that the impact of the Project on VMT would be significant and unavoidable. The commenter refers to Mitigation Measure 3.13- 1 as a “pathetic response”. The Draft EIR fully discloses the impact of the Project on VMT and presents feasible mitigation measures and project design features to reduce the significance of the impact. See Response F-9 regarding the feasibility of various TDM measures. The quantitative assessment presented in the Draft EIR objectively concludes that, even with implementation of the mitigation measures and project design features, the impact would be significant and unavoidable.
It is noted that text additions and clarifications have been made to Section 3.13 of the Draft EIR. See Chapter 3.0, Revisions, of this Final EIR.
Response F-11: Swainson’s hawk, burrowing owl, and tricolored blackbird are discussed on pages 3.4-15,
3.4-16, 3.4-31, and 3.4-32 of Section 3.4, Biological Resource, of the Draft EIR.
Additionally, as discussed on page 3.4-3 of the Draft EIR, field surveys were conducted by Principal Biologist Steve McMurtry on April 22, 2022, and May 15, 2023. The site reconnaissance surveys served several purposes. First, they served as reconnaissance of the site to establish the existing conditions of the site and to verify information gathered in the pre-field investigation. This included identification of the habitat types, hydrologic features, topography, soil characteristics, and vegetation. The field investigations followed the Protocols for Surveying and Evaluating Impacts to Special Status Native Plant Populations and Natural Communities (CDFW 2009). Habitat was recorded. Visibility during each survey was excellent. Swainson’s hawk, burrowing owl, and tricolored blackbird were not observed during the surveys.
Additionally, as noted on pages 3.4-31 and 3.4-32 of the Draft EIR, Powerlines and trees located in the region represent potentially suitable nesting habitat for a variety of specialstatus birds. Additionally, the agricultural land represents potentially suitable nesting habitat for some ground-nesting birds. In general, most nesting occurs from late February and early March through late July and early August, depending on various environmental conditions. As noted by the commenter, and as stated in the Draft EIR, the CNDDB currently contains records for Swainson's hawk, burrowing owl, and tricolored blackbird in the vicinity of the Project site. In addition to the species described above, common raptors, may nest in or adjacent to the Project site.
These three bird species are all covered species under the San Joaquin County MultiSpecies Habitat Conservation Plan (SJMSCP). Mitigation Measure 3.4-1 requires the applicant to seek coverage under the SJMSCP, which would involve compensation for habitat impacts on covered species through implementation of incidental take and minimization measures (ITMMs) and payment of fees for conversion of lands that may provide habitat for covered special status species. These fees are used to preserve and/or create habitat in preserves to be managed in perpetuity. Additionally, as part of the SJMSCP, SJCOG requires preconstruction surveys for projects that initiate grading activities during the avian breeding season (March 1 – August 31). When active nests are EXHIBIT 1
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identified, the biologists develop buffer zones around the active nests as deemed appropriate until the young have fledged.
Project applicants have four options to receive Coverage, with approval by SJCOG, Inc.:
1. Pay the appropriate fee. A fee is assessed depending on which of the four habitats the project lies within.
2. Dedicate habitat lands as conservation easement or fee title.
3. Purchase mitigation bank credits from a mitigation bank approved by SJMSCP.
4. Propose an alternative mitigation plan, consistent with the goals of the SJMSCP and equivalent in biological value.
There is no reason to believe that the Project would not receive coverage under the SJMSCP under at least one of these options. Further, the California Department of Fish and Wildlife submitted a Draft EIR comment letter (Letter A in this chapter); their letter did not indicate that additional mitigation for this species should be provided.
Response F-12: For detailed responses to the commenter’s concerns provided in this comment, please see Responses F-1 through F-11.
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REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-1 This section includes minor edits and changes to the Draft EIR. These modifications resulted from responses to comments received during the public review period for the Draft EIR, as well as City staff-initiated edits to clarify the details of the project.
Revisions herein do not result in new significant environmental impacts, do not constitute significant new information, nor do they alter the conclusions of the environmental analysis that would warrant recirculation of the Draft EIR pursuant to State CEQA Guidelines Section 15088.5.
Other minor changes to various sections of the Draft EIR are also shown below. These changes are provided in revision marks with underline for new text and strike out for deleted text.
3.1 REVISIONS TO THE DRAFT EIR
0.0 EXECUTIVE SUMMARY
The following changes were made to pages ES-3 and ES-4 of Chapter ES of the Draft EIR:
TABLE ES-1: COMPARISON SUMMARY OF ALTERNATIVES TO THE PROPOSED PROJECT
ENVIRONMENTAL ISSUE
NO PROJECT
(NO BUILD)
ALTERNATIVE
REDUCED
DENSITY
ALTERNATIVE
AGRICULTURE PROTECTION
ALTERNATIVE
Aesthetics and Visual Resources Less (Best) Slightly Less (3rd Best) Less (2nd Best) Agricultural Resources Less (Best) Equal (3rd Best) Less (2nd Best) Air Quality Less (Best) Less (2nd Best) Equal (3rd Best) Biological Resources Less (Best) Equal (3rd Best) Less (2nd Best) Cultural and Tribal Resources Less (Best) Equal (3rd Best) Less (2nd Best) Geology and Soils Less (Best) Slightly Less (2nd Best) Equal (3rd Best) Greenhouse Gases, Climate Change and Energy Less (Best) Less (2nd Best) Equal (3rd Best) Hazards and Hazardous Materials Less (Best) Equal (2nd 3rd Best) Equal Slightly Less (2nd Best) Hydrology and Water Quality Less (Best) Slightly Less (3rd Best) Less (2nd Best) Land Use and Population Less (Best) Less (2nd Best) Equal (3rd Best) Noise Less (Best) Slightly Less (2nd Best) Equal (3rd Best) Public Services and Recreation Less (Best) Equal (2nd Best) Equal (3rd Best) Transportation and Circulation Less (Best) Slightly Less (2nd Best) Equal (3rd Best) Utilities Less (Best) Less (2nd Best) Equal (3rd Best)
GREATER = GREATER IMPACT THAN THAT OF THE PROPOSED PROJECT LESS = LESS IMPACT THAN THAT OF THE PROPOSED PROJECT
EQUAL = NO SUBSTANTIAL CHANGE IN IMPACT FROM THAT OF THE PROPOSED PROJECT As shown in the table, the No Project (No Build) Alternative is the environmentally superior alternative. However, as required by CEQA, when the No Project (No Build) Alternative is the environmentally superior alternative, the environmentally superior alternative among the others must be identified. Therefore, the Reduced Density Alternative and Agriculture Protection Alternative both rank higher than the proposed Project. The Reduced Density Alternative would have equal impacts in five areas, slightly less impacts in five areas, and less impacts in nine areas.
The Agriculture Protection Alternative would have equal impacts in nine eight areas, slightly less impacts in one area, and less impacts in five areas. Therefore, the Reduced Density Alternative would be the next environmentally superior alternative. It is noted that neither the Agriculture Protection Alternative nor the Reduced Density Alternative fully meet all of the Project objectives.
See Section 5.4 below for a comparative evaluation of the objectives for each alternative.
The following changes were made to pages ES-5 through ES-12 of Chapter ES of the Draft EIR:
- - I
EXHIBIT 1
1061
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-2 6BTABLE ES-2: PROJECT IMPACTS AND PROPOSED MITIGATION MEASURES
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
AESTHETICS AND VISUAL RESOURCES
Impact 3.1-1: Project implementation may result
in substantial adverse effects on scenic vistas
and resources or substantial degradation of
visual character
SU None feasible. SU
Impact 3.1-2: Project implementation would not
substantially damage scenic resources within a
State Scenic Highway
NI None required. --
Impact 3.1-3: Project implementation may result
in light and glare impacts
LS None required. --
AGRICULTURAL RESOURCES
Impact 3.2-1: The proposed Project would result
in the conversion of Farmlands, including Prime
Farmland and Farmland of Statewide
Importance, as shown on the maps prepared
pursuant to the Farmland Mapping and
Monitoring Program of the California Resources
Agency, to non-agricultural uses
PS Mitigation Measure 3.2-1: Prior to the conversion of Important Farmland on the Project site, the Project applicant shall participate in the City’s Agricultural Lands Mitigation Program, under which developers of the property shall contribute agricultural mitigation land or shall pay the Agricultural Land Mitigation Fee to the City. on a 1:1 basis for each acre of land converted. The Agricultural Land Mitigation Program provides that agricultural mitigation lands shall be dedicated to a qualifying management entity such as the Central Valley Farmland Trust. The fees shall be collected by the City, held in a dedicated account, and then expended by the City to acquire agricultural mitigation land or pay for the monitoring and administrative costs of the program. The fees may also be transferred to a qualifying entity for the same purpose. Payment in the in the City’s Agricultural Lands Mitigation Program would be feasible or effective mitigation for conversion of agricultural land.
Participation Alternatively, participation in the San Joaquin County Multi-Species Habitat Conservation and Open Space Plan (SJMSCP) that results in agricultural land mitigation may also be considered as the functional equivalent of mitigation for the loss of Important Farmland. The SJMSCP requires the payment of a per-acre fee for loss of wildlife habitat, which in San Joaquin County is largely integral with agricultural use. One important use of the fees is the acquisition of conservation easements over agricultural land that are intended to preserve the agricultural use of these lands in order to maintain their biological habitat values.
SU
-
I I
EXHIBIT 1
1062
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-3
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
Impact 3.2-2: The proposed Project would
conflict with existing zoning for agricultural use,
or Williamson Act contracts
PS None feasible. SU
Impact 3.2-3: The proposed Project may involve
other changes in the existing environment
which, due to their location or nature, could
result in conversion of Farmland, to nonagricultural use LS None required. --
AIR QUALITY
Impact 3.3-1: Project operation has the potential
to result in a cumulatively considerable net
increase of any criteria pollutant for which the
Project region is in non-attainment, or conflict or
obstruct implementation of the District’s air
quality plan
PS Mitigation Measure 3.3-1: The project Project applicant(s) shall comply with SJVAPCD Rule 4101, which prohibits emissions of visible air contaminants to the atmosphere and applies to any source operation that emits or may emit air contaminants. Specifically, the project applicant(s), during Project operation, shall not discharge into the atmosphere any air contaminant, other than uncombined water vapor, for a period or periods aggregating more that (3) minutes in any one (1) hour which is: a) As dark or darker in shade as that designated as No. 1 on the Ringelmann Chart, as published by the United States Bureau of Mines; b) Of such opacity as to obscure an observer's view to a degree equal to or greater than the smoke described in Section 5.1 of this rule.
Mitigation Measure 3.3-2: The project Project applicant(s) shall comply with SJVAPCD Rule 4601, during Project construction and operation, which limits project has agreed to abide by morelimits stringent VOC emissions requirementsfrom architectural coatings.
This rule specifies Emissions of volatile organic compounds from architectural coatings by specifying storage, clean up and labeling requirements. Specific VOC limits for architectural coatings are provided within the Air District’s website, located at:
https://ww2.valleyair.org/rules-and-planning/current-district-rules-and-regulations/ (The project has agreed to abide by more stringent VOC emissions requirements.) Mitigation Measure 3.3-3: The project Project applicant(s) shall utilize low-VOC paints, equivalent to 10 g/L of ROG, if commercially available.
Mitigation Measure 3.3-4: The City shall educate the Project applicant(s) on the benefits of a VERA. The Project applicant(s) shall consult with the City regarding the results of SJVAPCD’s Rule 9510 process, prior the building permit stage. If emissions reductions SU
EXHIBIT 1
1063
3.0 REVISIONS
3.0-4 Final Environmental Impact Report – LeBaron Ranch
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
associated with mandatory compliance with SJVAPCD’s Rule 9510 are not sufficient to reduce emissions to below the applicable SJVAPCD thresholds of significance for operational ROG, the project applicant shall enter into a VERA with the SJVAPCD, to reduce emissions to below the applicable thresholds of significance, after taking into account any emissions reductions associated with mandatory compliance with SJVAPCD’s Rule 9510. If conditions warrant participation in a VERA, the VERA shall demonstrate a reduction in emissions that meets SJVAPCD’s ROG operational emissions threshold through a process that funds and implements emissions reduction projects within the SJVAB. The types of emission reduction projects that could be funded include replacing old heavy-duty trucks with cleaner, more efficient heavy-duty trucks, for example. If a VERA is found to be required, the project applicant shall engage in a discussion with SJVAPCD prior to the adoption of the VERA to ensure that feasible mitigation has been identified to reduce emissions to a less-than-significant level.
Mitigation Measure 3.3-5: The Project applicant(s) shall provide information regarding the Air District’s Clean Green Yard Machines (CGYM) program, which provides incentive funding for the replacement of existing gas powered lawn and garden equipment, to the home-buyers at time of sale of the housing units by the applicant. More information on the District CGYM program and funding can be found at:
https://ww2.valleyair.org/grants/zero-emission-landscaping-equipment-voucherprogram/.
Impact 3.3-2: Proposed Project construction
activities would not result in a cumulatively
considerable net increase of any criteria
pollutant for which the Project region is in nonattainment, or conflict or obstruct implementation of the District’s air quality plan
PS Mitigation Measure 3.3-64: Prior to the issuance of a Grading Permit for each phase of the Project, the Project Proponent shall prepare and submit a Dust Control Plan that meets all of the applicable requirements of APCD Rule 8021, Section 6.3, for the review and approval of the APCD Air Pollution Control Officer.
Mitigation Measure 3.3-75: During all construction activities, the Project Proponent shall implement dust control measures, as required by APCD Rules 8011-8081, to limit Visible Dust Emissions to 20% opacity or less. Dust control measures shall include application of water or chemical dust suppressants to unpaved roads and graded areas, covering or stabilization of transported bulk materials, prevention of carryout or trackout of soil materials to public roads, limiting the area subject to soil disturbance, construction of wind barriers, access restrictions to inactive sites as required by the applicable rules.
Mitigation Measure 3.3-86: During all construction activities, the Project proponent shall LS
EXHIBIT 1
1064
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-5
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
implement the following dust control practices identified in Tables 6-2 and 6-3 of the GAMAQI (2002).
a. All disturbed areas, including storage piles, which are not being actively utilized for construction purposes, shall be effectively stabilized of dust emissions using water, chemical stabilizer/suppressant, or vegetative ground cover. b. All on-site unpaved roads and off-site unpaved access roads shall be effectively stabilized of dust emissions using water or chemical stabilizer/suppressant. c. All land clearing, grubbing, scraping, excavation, land leveling, grading, cut and fill, and demolition activities shall control fugitive dust emissions by application of water or by presoaking.
d. When materials are transported off-site, all material shall be covered, effectively wetted to limit visible dust emissions, or at least six inches of freeboard space from the top of the container shall be maintained.
e. All operations shall limit or expeditiously remove the accumulation of mud or dirt from adjacent public streets at least once every 24 hours when operations are occurring. The use of dry rotary brushes is expressly prohibited except where preceded or accompanied by sufficient wetting to limit the visible dust emissions.
Use of blower devices is expressly forbidden.
f. Following the addition of materials to, or the removal of materials from, the surface of outdoor storage piles, said piles shall be effectively stabilized of fugitive dust emissions utilizing sufficient water or chemical stabilizer/suppressant. g. Limit traffic speeds on unpaved roads to 5 mph.
h. Install sandbags or other erosion control measures to prevent silt runoff to public roadways from sites with a slope greater than one percent.
Mitigation Measure 3.3-97: Asphalt paving shall be applied in accordance with APCD Rule 4641, the purpose of which is to limit VOC emissions by restricting the application and manufacturing of certain types of asphalt for paving and maintenance operations.
This rule applies to the manufacture and use of cutback asphalt, slow cure asphalt and emulsified asphalt for paving and maintenance operations. The Project Applicant shall coordinate with the APCD, prior to Project asphalt paving activities, to ensure all Project asphalt paving would comply with this rule. The Project Applicant shall provide the City of Stockton with evidence of consultation with the APCD, including confirmation of compliance with APCD Rule 4641.
EXHIBIT 1
1065
3.0 REVISIONS
3.0-6 Final Environmental Impact Report – LeBaron Ranch
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
Impact 3.3-3: The proposed Project would not
generate carbon monoxide hotspot impacts
LS None required. --
Impact 3.3-4: The proposed Project has the
potential for public exposure to toxic air
contaminants
LS None required. --
Impact 3.3-5: The proposed Project would not
cause exposure to other emissions (such as
those leading to odors) adversely affecting a
substantial number of people
LS None required. --
BIOLOGICAL RESOURCES
Impact 3.4-1: The proposed Project would not
have a direct or indirect effect on special-status
invertebrate species
LS None required. --
Impact 3.4-2: The proposed Project has the
potential to have direct or indirect effects on
special-status reptile and amphibian species
PS Mitigation Measure 3.4-1: Prior to commencement of any grading activities, the Project proponent shall seek coverage under the San Joaquin County Multi-Species Habitat Conservation Plan (SJMSCP) to mitigate for habitat impacts to covered special status species. Coverage involves compensation for habitat impacts on covered species through implementation of incidental take and minimization measures (ITMMs) and payment of fees for conversion of lands that may provide habitat for covered special status species.
These fees are used to preserve and/or create habitat in preserves to be managed in perpetuity. Obtaining coverage for a Project includes incidental take authorization (permits) under the Endangered Species Act Section 10(a), California Fish and Game Code Section 2081, and the Migratory Bird Treaty Act (MBTA). Coverage under the SJMSCP would fully mitigate all habitat impacts on covered special-status species.
Mitigation Measure 3.4-2: Prior to the commencement of grading activities or other ground disturbing activities on the Project site, the Project applicant shall arrange for a qualified biologist to conduct a preconstruction survey for Swainson’s hawks. If no hawks or hawk nests are detected, then construction activities may commence. If Swainson’s hawks or occupied nests are discovered, then the following shall be implemented:
• During the nesting season (February 15 through August 31) and Swainson’s hawks are nesting in or near the Project site, a construction setback of 250 feet of the nest tree (as measured from under the nest) would be required until nesting is LS
EXHIBIT 1
1066
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-7
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
complete.
This requirement is consistent with the incidental take and minimization measures (ITMMs) outlined in the SJMSCP. Implementation of this requirement shall occur prior to grading or site clearing activities. SJCOG shall be responsible for monitoring and a qualified biologist shall conduct surveys as required.
Mitigation Measure 3.4-3: Prior to the commencement of grading activities or other ground disturbing activities on the Project site, the Project applicant shall arrange for a qualified biologist to conduct a preconstruction survey for burrowing owls. If no owls or owl nests are detected, then construction activities may commence. If burrowing owls or occupied nests are discovered, then the following shall be implemented:
• During the nesting season (February 1 and August 31) and burrowing owls are present on-site, a 250-foot construction setback from the natal burrow would be required until nesting is complete.
• Outside the nesting season (September 1 and January 31) burrowing owls occupying the Project site should be evicted from the Project site by passive relocation as described in the California Department of Fish and Game’s Staff Report on Burrowing Owls (Oct., 1995)
These requirements are consistent with the incidental take and minimization measures (ITMMs) outlined in the SJMSCP. Implementation of this requirement shall occur prior to grading or site clearing activities. SJCOG shall be responsible for monitoring and a qualified biologist shall conduct surveys and relocate owls as required.
Mitigation Measure 3.4-4: Prior to the commencement of grading activities or other ground disturbing activities on the Project site, the Project applicant shall arrange for a qualified biologist to conduct a preconstruction survey for tricolored blackbird. If no tricolored blackbird or tricolored blackbird nests are detected, then construction activities may commence. If tricolored blackbird or occupied nests are discovered, then the following shall be implemented:
• A setback of 500 feet from colonial nesting areas shall be established and maintained during the nesting season for the period encompassing nest building EXHIBIT 1
1067
3.0 REVISIONS
3.0-8 Final Environmental Impact Report – LeBaron Ranch
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
and continuing until fledglings leave nests. This setback applies whenever construction or other ground-disturbing activities must begin during the nesting season in the presence of nests which are known to be occupied. Setbacks shall be marked by brightly colored temporary fencing.
This requirement is consistent with the incidental take and minimization measures (ITMMs) outlined in the SJMSCP. Implementation of this requirement shall occur prior to grading or site clearing activities. SJCOG shall be responsible for monitoring and a qualified biologist shall conduct surveys as required.
Impact 3.4-3: The proposed Project has the
potential to have direct or indirect effects on
special-status bird species
PS Implement Mitigation Measure 3.4-1. LS
Impact 3.4-4: The proposed Project has the
potential to result in direct or indirect effects on
special-status mammal species.
PS Implement Mitigation Measure 3.4-1. LS
Impact 3.4-5: The proposed Project would not
result in direct or indirect effects on candidate,
sensitive, or special-status plant species
LS None required. --
Impact 3.4-6: The proposed Project would not
result in direct or indirect effects on candidate,
sensitive, or special-status fish species
LS None required. --
Impact 3.4-7: The proposed Project would not
affect protected wetlands and jurisdictional
waters
LS None required. --
Impact 3.4-8: The proposed Project would not
result in adverse effects on riparian habitat or a
sensitive natural community
LS None required. --
Impact 3.4-9: The proposed Project would not
result in interference with the movement of
native fish or wildlife species or with established
wildlife corridors, or impede the use of native
wildlife nursery sites
LS None required. --
Impact 3.4-10: The proposed Project would not
conflict with an adopted Habitat Conservation
Plan
LS None required. --
EXHIBIT 1
1068
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-9
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
Impact 3.4-11: The proposed Project has the
potential to conflict with local policies or
ordinances protecting biological resources, such
as a tree preservation policy or ordinance
PS Mitigation Measure 3.4-52: If removal of any oak tree on the project site is required, the project applicant or contractor shall hire a certified arborist shall to survey the oak trees proposed for removal to determine if they are Heritage Trees as defined in Stockton Municipal Code Chapter 16.130. The survey shall occur prior to site disturbance. The arborist report with its findings shall be submitted to the City’s Community Development Department. If Heritage Trees are determined to exist on the property, removal of any such tree shall require a permit to be issued by the City in accordance with Stockton Municipal Code Chapter 16.130. The permittee shall comply with all permit conditions, including tree replacement at specified ratios.
LS
CULTURAL AND TRIBAL RESOURCES
Impact 3.5-1: Project implementation would not
cause a substantial adverse change to a
significant historical resource, as defined in
CEQA Guidelines §15064.5
LS None required. --
Impact 3.5-2: Project implementation has the
potential to cause a substantial adverse change
to a significant archaeological resource, as
defined in CEQA Guidelines §15064.5, or a
significant tribal cultural resource, as defined in
Public Resources Code §21074
PS Mitigation Measure 3.5-1: Prior to any ground-disturbing activities on the Project site, the Developer shall retain a qualified archaeologist and native American monitor shall to conduct pre-construction worker cultural resources sensitivity training. The training session shall focus on the recognition of the types of historical and cultural, including Native American, resources that could be encountered;, procedures to be followed if resources are found, including who to contact and appropriate avoidance measures until the find(s) can be properly evaluated,; and pertinent laws protecting these resources.
Training shall be scheduled at the discretion of the Project applicant in consultation with the City. The Developer shall be responsible for ensuring that all workers requiring training are in attendance. Those in attendance shall be recorded, with records maintained on-site. Any new workers that were not part of the initial training shall be required to undergo a new training session.
Mitigation Measure 3.5-2: If any cultural resources, including prehistoric or historic artifacts, or other indications of archaeological resources, are found during grading and construction activities during any phase of the Project, all work shall be halted immediately within a 200-foot radius of the discovery until an archaeologist meeting the Secretary of the Interior's Professional Qualifications Standards in prehistoric or historical archaeology, as appropriate, has evaluated the find(s).
LS
EXHIBIT 1
1069
3.0 REVISIONS
3.0-10 Final Environmental Impact Report – LeBaron Ranch
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
Work shall not continue at the discovery site until the archaeologist conducts sufficient research and data collection to make a determination that the resource is either 1) not cultural in origin; or 2) not potentially significant or eligible for listing on the NRHP or CRHR; or 3) not a significant Public Trust Resource.
If Native American resources are identified, a Native American monitor, following the Guidelines for Monitors/Consultants of Native American Cultural, Religious, and Burial Sites established by the Native American Heritage Commission, may also be required and, if required, shall be retained at the Project applicant’s expense.
If the discovery proves to be significant under CEQA and cannot be avoided by the Project, additional work such as data recovery excavation may be warranted to mitigate any significant impacts. Mitigation could include avoidance, preservation in place, or the scientific removal, analysis, reporting, and curation of any recovered cultural materials.
Construction shall not resume in the area until appropriate protection and preservation measures are in place and have been approved by the Community Development Director or designee, and the qualified archaeologist states in writing that the proposed construction activities would not significantly damage any archaeological or tribal cultural resources.
Impact 3.5-3: Project implementation has the
potential to disturb human remains, including
those interred outside of formal cemeteries
LS None required. --
GEOLOGY AND SOILS
Impact 3.6-1: The proposed Project would not
directly or indirectly cause potential substantial
adverse effects, including the risk of loss, injury,
or death involving: rupture of a known
earthquake fault, strong seismic ground shaking,
seismic related ground failure, or landslides
LS None required. --
Impact 3.6-2: Implementation and construction
of the proposed Project may result in substantial
soil erosion or the loss of topsoil
LS None required. --
Impact 3.6-3: The proposed Project has the
potential to be located on a geologic unit or soil
LS None required. --
EXHIBIT 1
1070
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-11
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
that is unstable, or that would become unstable
as a result of Project implementation, and
potentially result in landslide, lateral spreading,
subsidence, liquefaction or collapse
Impact 3.6-4: The proposed Project has the
potential for expansive soils to create substantial
risks to life or property
LS None required. --
Impact 3.6-5: The proposed Project has the
potential to directly or indirectly destroy a
unique geological feature or paleontological
resource
PS Mitigation Measure 3.6-1: If any paleontological resources are found during grading and construction activities of the Project, all work shall be halted immediately within a 200- foot radius of the discovery, the City of Stockton Community Development Director shall be notified, and a professional vertebrate paleontologist (as defined by the Society for Vertebrate Paleontology) shall be contacted immediately to evaluate the finduntil a qualified paleontologist has evaluated the find. The paleontologist shall have the authority to stop or divert construction, as necessary. Documentation and treatment of the discovery shall occur in accordance with Society of Vertebrate Paleontology standards.
Work shall not continue at the discovery site until the professional vertebrate paleontologist evaluates the find pursuant to the CEQA Guidelines and makes a determination regarding the significance of the resource and identifies recommendations for conservation of the resource, including, but not limited to, preserving in place or relocating on the Project site, if feasible, or collecting the resource to the extent feasible and documenting the find with the University of California Museum of Paleontology.
LS
GREENHOUSE GASES, CLIMATE CHANGE AND ENERGY
Impact 3.7-1: Project implementation would not
generate greenhouse gas emissions, either
directly or indirectly, that may have a significant
impact on the environment and would not
conflict with an applicable plan, policy, or
regulation adopted for the purpose of reducing
the emissions of greenhouse gases
LS None required. --
EXHIBIT 1
1071
3.0 REVISIONS
3.0-12 Final Environmental Impact Report – LeBaron Ranch
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
Impact 3.7-2: Project implementation would not
result in the inefficient, wasteful, or unnecessary
use of energy resources, and would not conflict
with or obstruct a state or local plan for
renewable energy or energy efficiency
LS None required. --
HAZARDS AND HAZARDOUS MATERIALS
Impact 3.8-1: Project implementation has the
potential to create a significant hazard through
the routine transport, use, or disposal of
hazardous materials or through the reasonably
foreseeable upset and accident conditions
involving the release of hazardous materials into
the environment
PS Mitigation Measure 3.8-1: Prior to initiating construction or grading activities, the construction contractor shall be provided with project-specific training regarding the identification and handling of hazardous materials and agency notification procedures.
In the event that contaminated soils hazardous materials are encountered during construction, the Project applicant shall prepare and implement a Soils Management Plan (SMP) to provide guidance for the proper handling, onsite management, and disposal of impacted soil that might be encountered during construction activities shall be submitted and approved by the San Joaquin County Department of Environmental Health. The SMP shall establish management practices for handling of contaminated soils and other hazardous materials, including fuels, paints, cleaners, solvents, etc., during construction. The SMP would include, but is not limited to, an outline of how Project construction crews would identify, handle, and dispose of potentially contaminated soil; the qualifications of the appropriately trained professionals that would monitor soil conditions and conduct soil sampling during construction; laboratory testing; anticipated field screening methods and appropriate regulatory limits to be applied to determine proper handling and disposal; and requirements for documenting and reporting incidents of encountered contaminants, such as documenting locations of occurrence, sampling results, and reporting actions taken to dispose of contaminated materials. In the event that potentially contaminated soils were encountered within the footprint of construction, soils would be tested and stockpiled. The SMP shall be submitted to the San Joaquin County Department of Environmental Health for review and approval. The approved SMP shall be posted and maintained onsite during construction activities and all construction personnel shall acknowledge that they have reviewed and understand the plan.
Mitigation Measure 3.8-2: Prior to initiation of any ground disturbance activities, a soil sampling and analysis workplan shall be submitted to the San Joaquin County Department of Environmental Health for approval. The sampling and analysis plan shall LS
EXHIBIT 1
1072
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-13
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
meet the requirements of the Department of Toxic Substances Control Interim Guidance for Sampling Agricultural Properties (2008), and the County Department of Environmental Resources Recommended Soil and Groundwater Sampling for Underground Tank Investigations (2013). evenly Evenly distributed soil samples shall be conducted throughout the Development Area for analysis of pesticides and heavy metals.
The samples shall be submitted for laboratory analysis of pesticides and heavy metals per DTSC and EPA protocols. The results of the soil sampling shall be submitted to the City of Stockton for review. If elevated levels of pesticides or heavy metals are detected during the laboratory analysis of the soils, a soil cleanup and remediation plan shall be prepared and implemented prior to the commencement of grading activities.
If the sampling results indicate the presence of agrichemicals that exceed commercial screening levels, a removal action workplan shall be prepared in coordination with San Joaquin County Environmental Health Department. The removal action workplan shall include a detailed engineering plan for conducting the removal action, a description of the onsite contamination, the goals to be achieved by the removal action, and any alternative removal options that were considered and rejected and the basis for that rejection. A no further action letter shall be issued by San Joaquin County Environmental Health Department upon completion of the removal action. The removal action shall be deemed complete when the confirmation samples exhibit concentrations below the commercial screening levels, which will be established by the agencies.
Impact 3.8-2: Project implementation has the
potential to emit hazardous emissions or handle
hazardous or acutely hazardous materials,
substances, or waste within one-quarter mile of
an existing or proposed school
LS None required. --
Impact 3.8-3: Project implementation has the
potential to result in impacts from being included
on a list of hazardous materials sites compiled
pursuant to Government Code Section 65962.5
NI None required. --
Impact 3.8-4: Project implementation has the
potential to result in a safety hazard for people
residing or working on the Project site as a result
of public airport or public use airport
LS None required. --
EXHIBIT 1
1073
3.0 REVISIONS
3.0-14 Final Environmental Impact Report – LeBaron Ranch
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
Impact 3.8-5: Project implementation has the
potential to impair implementation of or
physically interfere with an adopted emergency
response plan or emergency evacuation plan
LS None required. --
Impact 3.8-6: Project implementation has the
potential to expose people or structures to a risk
of loss, injury or death from wildland fires
LS None required. --
HYDROLOGY AND WATER QUALITY
Impact 3.9-1: The proposed Project has the
potential to violate water quality standards or
waste discharge requirements or otherwise
substantially degrade surface or ground water
quality
LS None required. --
Impact 3.9-2: The proposed Project has the
potential to substantially deplete groundwater
supplies or interfere substantially with
groundwater recharge such that the Project may
impede sustainable groundwater management of
the basin
LS None required. --
Impact 3.9-3: The proposed Project would not
alter the existing drainage pattern of the site or
area, including the alteration of the course of a
river or through the addition of impervious
surfaces, in a manner which would result in
substantial erosion, siltation, surface runoff,
flooding, or polluted runoff
LS None required. --
Impact 3.9-4: The proposed Project has the
potential to, in a flood hazard, tsunami, or seiche
zones, risk release of pollutants due to Project
inundation
PS Mitigation Measure 3.9-1: All residential and non-residential structures within the Project site shall meet the urban level of flood protection, as required by the State of California Central Valley Flood Protection Act of 2008 (Senate Bill 5). Finished floor elevations of proposed residential structures shall be elevated to or above the prescribed 200-year floodplain elevation, or proposed nonresidential structures shall be floodproofed, consistent with the City of Stockton’s Criteria for Development in 200-year Floodplains and City of Stockton Municipal Code. Code compliance shall be documented in materials prepared by licensed professionals and submitted to the Community LS
EXHIBIT 1
1074
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-15
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
t----------------'-r----11 -------'-r--11 Development Director -------1 prior to issuance of grading permits. I EXHIBIT 1
1075
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-16 The following changes were made to pages ES-16 through ES-18 of Chapter ES of the Draft EIR:
EXHIBIT 1
1076
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-17
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
TRANSPORTATION AND CIRCULATION
Impact 3.13-1: Project implementation would
conflict with or be inconsistent with CEQA
Guidelines Section 15064.3, subdivision (b).
PS Mitigation Measure 3.13-1: The Project applicant shall work with the City of Stockton to implement feasible Transportation Demand Management (TDM) strategies, which would decrease the VMT generated by the Project. Specific potential TDM strategies include, but are not limited to, the following:
• Provide Coordinate with public transit serviceagencies, including improving San Joaquin Rapid Transit District (RTD) regarding transit service connecting workers with existing and future residential developments;
• Coordinate with San Joaquin RTD regarding the potential for increasing service on Hopper Route 93;
• Implement a fair value commuting program or other pricing of vehicle travel and parking;
• TDM coordinator for large employers, such as the LUSD, should the school site be developed;
• Provide carpool and/or vanpool incentive programs;
• Provide on-site lockers and showers for workers who take alternative transportation, such as those employed by the LUSD, should the school site be developed;
• Promote walking and bicycling for employees who live and/or work in the area through the preparation of an Active Transportation Plan; • Incentivize the use of alternative travel modes for travel within the project site through shared use of e-bikes and e-scooters;
• Allow flexible work hours and schedule classes to reduce arrivals/departures during peak hours; and
• Employer coordination to SJCOG’s DIBs program for workers.
The TDM Plan shall be submitted to the City for review, and the effectiveness of the TDM Plan shall be evaluated, monitored, and revised, if necessary. The TDM Plan shall include the TDM strategies which will be implemented during the lifetime of the proposed Project and shall outline the anticipated effectiveness of the strategies to achieve the home-based work VMT per worker target identified in the City’s TIAG. The effectiveness of the TDM Plan may be monitored through annual surveys to determine employee travel mode split and travel distance for home-based work trips, and/or the implementation of technology to determine the amount of traffic generated by and home-based work miles SU
-
-
I I
EXHIBIT 1
1077
3.0 REVISIONS
3.0-18 Final Environmental Impact Report – LeBaron Ranch
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
traveled by employees, which shall be determined in coordination with the City and included as part of the TDM Plan. Monitoring of the effectiveness of the TDM Plan shall be mandatory at least for first three year after implementation of the TDMs to see how well the TDM Plan is performing, and to add new TDMs, if some measures become feasible later.
Impact 3.13-2: Project implementation would
not conflict with a program, plan, ordinance or
policy addressing the circulation system,
including transit, roadway, bicycle, and
pedestrian facilities
LS None required. --
Impact 3.13-3: Project implementation would
not substantially increase hazards due to a
geometric design feature (e.g., sharp curves or
dangerous intersections) or incompatible uses
(e.g., farm equipment).
LS None required. --
Impact 3.13-4: Project implementation would
not result in inadequate emergency access
LS None required. --
Impact 3.13-5: Project implementation would
not cause impacts due to construction.
LS None required. --
UTILITIES AND SERVICE SYSTEMS
Impact 3.14-1: The proposed Project would not
exceed wastewater treatment requirements of
the applicable Regional Water Quality Control
Board
LS None required. --
Impact 3.14-2: The proposed Project would not
result in a determination by the wastewater
treatment and/or collection provider which
serves or may serve the Project that is does not
have adequate capacity to serve the Project’s
projected demand in addition to the provider’s
existing commitments
PS Mitigation Measure 3.14-1: Prior to occupancy of any building that would require wastewater treatment services, the Project proponent shall secure from the City of Stockton Municipal Utilities Department with a request for utility service adequate wastewater treatment capacity/allocation.
LS
Impact 3.14-3: The proposed Project would not
require or result in the construction of new
wastewater treatment or collection facilities or
LS None required. --
EXHIBIT 1
1078
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-19
ENVIRONMENTAL IMPACT
LEVEL OF
SIGNIFICANCE
WITHOUT
MITIGATION
MITIGATION MEASURE
RESULTING
LEVEL OF
SIGNIFICANCE
expansion of existing facilities, the construction
of which could cause significant environmental
effects
Impact 3.14-4: The proposed Project would not
require construction of new water treatment
facilities or expansion of existing facilities, the
construction of which could cause significant
environmental effects
LS None required. --
Impact 3.14-5: The proposed Project would not
have insufficient water supplies available to
serve the Project from existing entitlements and
resources
LS None required. --
Impact 3.14-6: The proposed Project would not
require or result in the construction of new
storm water drainage facilities or expansion of
existing facilities, the construction of which
could cause significant environmental effects
PS Mitigation Measure 3.14-2: Prior to the issuance of a building or grading permit, the project applicant shall submit a drainage plan to the City of Stockton for review and approval. The plan shall include an engineered Storm Water Quality Control Criteria Plan (SWQCCP) that demonstrates attainment of pre-project runoff requirements prior to release at the Bear Creek outfall. The plan shall describe the volume reduction measures and treatment controls, which may include, but not limited to vegetated swale, infiltration basin, rain garden, or bioretention, consistent with the Federal Clean Water Act, the City’s Stormwater Quality Control Criteria Plan, the adopted municipal stormwater National Pollutant Discharge Elimination System (NPDES) permit and the City's corresponding Stormwater Management PlanCity of Stockton requirements.
LS
EXHIBIT 1
1079
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-20
1.0 INTRODUCTION
No changes were made to Chapter 1.0 of the Draft EIR.
2.0 PROJECT DESCRIPTION
The following changes were made to page 2.0-12 of Chapter 2.0 of the Draft EIR:
ANNEXATION
The proposed Project includes an Annexation of 12 APNs totaling 306.03 acres. This includes the Development Area (six parcels totaling 236.30 acres), Non-development Area (six parcels totaling
56.03 acres), and the remaining Right-of-Way Annexation Area (13.7 acres of existing County rightof-way). The annexation will also include detachment from the Lincoln Fire District. Figure 2.0-10 shows the proposed annexation area. Non-development area includes lands that will be…..
The following changes were made to pages 2.0-13 and 2.0-14 of Chapter 2.0 of the Draft EIR:
CITY OF STOCKTON
The City of Stockton will be the Lead Agency for the proposed Project, pursuant to the State Guidelines for Implementation of CEQA, Section 15050. Actions that would be required from the City include, but are not limited to the following:
• Certification of the EIR;
• Adoption of the Mitigation Monitoring and Reporting Program; • Adoption of the Findings and Statement of Overriding Considerations; • Adoption of General Plan Amendment (Land Use Map);
• Adoption of an Ordinance for City of Stockton Pre-Zoning; • Approval of a Detachment Agreement from the Lincoln Fire District; • Approval of a Planned Unit Residential Development (PURD) Permit; • Approval of Vesting Tentative map;
• Approval of Annexation and Authorization to submit Annexation request and Submit Detachment Request for Lincoln Fire District to San Joaquin LAFCo; • Approval of future Final Maps;
• Approval of future Improvement Plans;
• Approval of future Grading Plans;
• Approval of Building Permits;
• Issuance of grading, encroachment, and building permits; and • City review and approval of Project utility plans.
OTHER GOVERNMENTAL AGENCY APPROVALS
The following agencies are considered “Responsible Agencies” and will need to rely on this EIR to issue permits or approve certain aspects of the proposed Project. A "Responsible Agency" is any public agency, other than the lead agency, which has the responsibility for approving the project EXHIBIT 1
1080
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-21 where more than one public agency is involved. Other governmental agencies that may require approval include, but are not limited to, the following:
• California Department of Fish and Wildlife (CDFW) – should a 1600 Streambed Alteration Agreement, or 401/404 Permit be required;
• Central Valley Flood Protection Board (CVFPB) – should offsite work impact Pixley Slough (which is not anticipated);
• Central Valley Regional Water Quality Control Board (CVRWQCB) – Storm Water Pollution Prevention Plan (SWPPP) approval pursuant to the Clean Water Act; • CVRWQCB – Water quality certification pursuant to Section 401 of the Clean Water Act;
• San Joaquin County Flood Control and Water Conservation District; • Native American Heritage Commission (NAHC);
• San Joaquin Local Agency Formation Commission (LAFCo) – Annexation to the City of Stockton and detachment from the Lincoln Rural Fire Protection District; • San Joaquin Valley Air Pollution Control District (SJVAPCD) – Construction-related permits;
• San Joaquin Valley Air Pollution Control District (SJVAPCD) – Authority to Construct, Permit to Operate for stationary sources of air pollution • Stockton Fire Department – Plan check of the site plan and roadway improvements for adequate emergency vehicle access and fire flow capabilities; • San Joaquin Council of Governments (SJCOG) – Issuance of incidental take permit under the San Joaquin Multi-Species Habitat Conservation and Open Space Plan (SJMSCP).;
• United States Army Corps. Of Engineers (USACE) – Permitting of federal jurisdictional areas pursuant to Section 404 of the Clean Water Act.;
• Woodbridge Irrigation District.
A new figure, Figure 2.0-10 (Proposed Annexation) was added to page 2.0-45 of Chapter 2.0 of the Draft EIR:
EXHIBIT 1
1081
3.0 REVISIONS
3.0-22 Final Environmental Impact Report – LeBaron Ranch _________ .._ ___ , ElGlilMILE,RD----------•'J'-----------,----------------~- GHT•M l!E•R □ - 1
I ____ _. I
I
~ l El< I I
E SCOOOI , ________ j
C
a:
"'
~ ROYAL OAKS DR
C •a
OaJ..Y> •
m
...
\ PONCE OE LE N AV O
•
LEGEND
L::1 Stockton City Limits - Public Schools
C Project Site Parks
N
A
IJlOO 2.000
--US Feet
S!,:"(:kton Fl'e
Depar1menl
Sta: )11f13
@ Go ooin
Ela SC/I
STOCKTON LEBARON RANCH
Figure 2.0-10. Proposed Annexation
EXHIBIT 1
1082
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-23
3.1 AESTHETICS AND VISUAL RESOURCES
The following changes were made to page 3.1-10 of Section 3.1 of the Draft EIR:
Nevertheless, the loss of the visual appearance of the existing agricultural land on the site would alter the visual character of the Project site in perpetuity. Compliance with the requirements within the General Plan and Zoning Code would reduce visual impacts to the greatest extent feasible; however, the proposed Project would permanently convert the agricultural uses to urbanized uses.
This is considered a significant and unavoidable impact. As discussed in Section 3.2, Agricultural Resources, while the proposed Project would contribute fees toward the purchase of conservation easements on agricultural lands through the San Joaquin County Multi-Species Habitat Conservation and Open Space Plan (as required by Mitigation Measure 3.2-1), those fees and conservation easements would not result in the creation of new farmland to offset the loss that would occur with Project implementation. The only way to mitigate this impact would be to prohibit the development of urban uses on the Project site; no additional mitigation is available.
CEQA does not require that the project be changed in order to avoid an impact. . There is no additional feasible mitigation available that would reduce this impact to a less than significant level.
Overriding considerations for this significant and unavoidable impact would be provided in the Findings and Statement of Overriding Considerations for the Project.
3.2 AGRICULTURAL RESOURCES
The following changes were made to pages 3.2-13 and 3.2-14 of Section 3.2 of the Draft EIR:
The Envision Stockton 2040 General Plan EIR anticipated development of the Project site as part of the overall evaluation of the buildout of the City. The General Plan EIR addressed the conversion and loss of Important Farmland that would result from the build out of the General Plan (General Plan Draft EIR, pp. 4.2-10 through 4.2-12). The General Plan EIR determined that impacts would be significant and unavoidable. According to the General Plan EIR, although the General Plan includes policies and actions that would reduce and partially offset the conversion of farmland, it designates approximately 16,160 acres of farmlands of concern under CEQA for non-agricultural uses. Because these farmland areas are located near existing urbanized areas, they may not be viable for agricultural operations due to conflicts with nearby urbanized areas. The General Plan includes policies and actions that aim to concentrate growth and protect agricultural lands outside of the city from conversion to non-agricultural use. The General Plan EIR does not identify any mitigation measures to reduce this impact. The As stated in the General Plan EIR, the only way to mitigate this impact would be to prohibit any development on farmland of concern. CEQA does not require that the project be changed in order to avoid an impact, and no additional mitigation is available, resulting in a significant and unavoidable impact.
While the proposed Project would contribute fees toward the purchase of conservation easements on agricultural lands through the SJMSCP (as required by Mitigation Measure 3.2-1), those fees and conservation easements would not result in the creation of new farmland to offset the loss that would occur with Project implementation. Implementation of the Project would result in a net loss of farmland, even with implementation of mitigation. As such, consistent with the conclusion of the General Plan EIR, the loss of Important Farmland would be a significant and unavoidable impact relative to this topic.
EXHIBIT 1
1083
3.0 REVISIONS
3.0-24 Final Environmental Impact Report – LeBaron Ranch
MITIGATION MEASURE(S)
Mitigation Measure 3.2-1: Prior to the conversion of Important Farmland on the Project site, the Project applicant shall participate in the City’s Agricultural Lands Mitigation Program, under which developers of the property shall contribute agricultural mitigation land or shall pay the Agricultural Land Mitigation Fee to the City. on a 1:1 basis for each acre of land converted. The Agricultural Land Mitigation Program provides that agricultural mitigation lands shall be dedicated to a qualifying management entity such as the Central Valley Farmland Trust. The fees shall be collected by the City, held in a dedicated account, and then expended by the City to acquire agricultural mitigation land or pay for the monitoring and administrative costs of the program. The fees may also be transferred to a qualifying entity for the same purpose. Payment in the in the City’s Agricultural Lands Mitigation Program would be feasible or effective mitigation for conversion of agricultural land.
Participation Alternatively, participation in the San Joaquin County Multi-Species Habitat Conservation and Open Space Plan (SJMSCP) that results in agricultural land mitigation may also be considered as the functional equivalent of mitigation for the loss of Important Farmland. The SJMSCP requires the payment of a per-acre fee for loss of wildlife habitat, which in San Joaquin County is largely integral with agricultural use. One important use of the fees is the acquisition of conservation easements over agricultural land that are intended to preserve the agricultural use of these lands in order to maintain their biological habitat values.
3.3 AIR QUALITY
The following changes were made to pages 3.3-26 and 3.3-27 of Section 3.3 of the Draft EIR:
District Rules 2010 and 2201 - Air Quality Permitting for Stationary Sources Stationary Source emissions include any building, structure, facility, or installation which emits or may emit any affected pollutant directly or as a fugitive emission. District Rule 2010 (Permits Required) requires operators of emission sources to obtain an Authority to Construct (ATC) and Permit to Operate (PTO) from the District. District Rule 2201 (New and Modified Stationary Source Review) requires that new and modified stationary sources of emissions mitigate their emissions using Best Available Control Technology (BACT).
District Rule 4002 (National Emissions Standards for Hazardous Air Pollutants) The Project would be subject to District Rule 4002, since the Project will include demolition and removal of existing structures. To protect the public from uncontrolled emissions of asbestos, this rule requires a thorough inspection for asbestos to be conducted before any regulated facility is demolished or renovated. Any asbestos present must be handled in accordance with established work practice standards and disposal requirements.
District Rule 4601 (Architectural Coatings)
The Project would be subject to District Rule 4601 since it is expected to utilize architectural coatings. Architectural coatings are paints, varnishes, sealers, or stains that are applied to structures, portable buildings, pavements or curbs. The purpose of this rule is to limit VOC emissions from architectural coatings. In addition, this rule specifies architectural coatings storage, cleanup and labeling requirements.
EXHIBIT 1
1084
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-25 The following changes were made to pages 3.3-31 through 3.3-34 of Section 3.3 of the Draft EIR:
The Project’s operational ROG emissions are primarily from the Project’s mobile vehicle emissions.
However, a substantial portion of the ROG emissions are also from area sources, which include offgassing from architectural coatings, off-gassing from consumer products, and the usage of landscape equipment. The only feasible mitigation to reduce the Project’s operational emissions are to reduce the ROG content off-gassed from architectural coatings (by using architectural coatings that have fewer ROG emissions) and by utilizing landscaping equipment with fewer or no ROG emissions. There is no feasible mitigation to reduce mobile vehicle ROG emissions, or to reduce the amount of ROG off-gassing from consumer products, as these are not activities that the Project applicant would have the ability to feasibly influence.
Since operational ROG emissions were found to above the applicable SJVAPCD threshold, all potentially feasible mitigation measures were considered to reduce this to below the threshold. An assessment of potential transportation-related measures included in the California Air Pollution Control Officer’s Association (CAPCOA) GHG Handbook, entitled "Handbook for Analyzing Greenhouse Gas Emission Reductions, Assessing Climate Vulnerabilities, and Advancing Health and Equity”,
1 is presented in detail in Appendix F of this EIR (i.e. the Traffic Analysis). As described in Appendix F, Mitigation measures to reduce the impact of the LeBaron Ranch Project on VMT were considered in compliance with the City of Stockton Traffic Impact Analysis Guidelines. The guidelines note:
“A list of mitigation measures applicable for consideration at the project-site level can be found in the Handbook for Analyzing Greenhouse Gas Emission Reductions, Assessing Climate Vulnerabilities, and Advancing Health and Equity (GHG Handbook).” The assessment includes the feasibility and applicability of GHG Handbook measures for the proposed Project. Measures considered for the Project are those included in the GHG Handbook in the Transportation category. These measures, such as carshare programs and community-based travel planning, were considered as potential mitigation measures, but are not recommended. As described in further detail in Appendix F, such measures are not feasible for the project, since these systems require a geographic scale larger than an individual development project. 2 Additionally, the
GHG Handbook presents measures which are not applicable to residential land use projects. These are measures which are primarily applicable to employment-generating uses, such as increased job density, ridesharing programs, and subsidized transit programs.3 Measures were also considered, but are not feasible because they are not within the authority of the applicant or the City of Stockton. For example, the San Joaquin Regional Transit District (RTD) provides limited public transit service to the Project site. The County Hopper Route 93 operates weekdays along West Lane, with eight northbound trips per day and ten southbound trips per day.
County Hopper service is a deviated fixed route type of service. The GHG Handbook presents 1 See: CAPCOA. 2024. Handbook for Analyzing Greenhouse Gas Emission Reductions, Assessing Climate Vulnerabilities, and Advancing Health and Equity. Available at:
https://www.caleemod.com/handbook/index.html
2 Refer to Appendix F and Section 3.13: Transportation and Circulation of this EIR, for further detail. 3 Refer to Appendix F and Section 3.13: Transportation and Circulation of this EIR, for further detail.
EXHIBIT 1
1085
3.0 REVISIONS
3.0-26 Final Environmental Impact Report – LeBaron Ranch measures which are related to the structure of the community-level public transit system. While these measures have the potential to reduce VMT, the RTD has authority to implement the measures. Implementation of the measures, including development of a transit-oriented development, increased transit service frequency, provide bus rapid transit, or reduce transit fares, is not within the authority of the applicant or the City of Stockton.
The GHG Handbook presents measures which are considered not applicable to, or not feasible for, the LeBaron Ranch Project site. These measures were considered as potential mitigation measures, but are not recommended. The Project includes 194 high density multiple-family dwelling units.
Current residential development in the vicinity of the Project site is predominantly composed of relatively lower density single family dwelling units. The General Plan travel demand model, used to estimate VMT for the Project, already includes relatively lower VMT per unit generated by the Project multiple family dwelling units.
The GHG Handbook includes a measure that involves affordable and below market rate housing, noting, “Multifamily residential units must be permanently dedicated as affordable for lower income families.” The Project includes a mix of housing types: low-density single family dwelling units, medium-density single family dwelling units, and high-density multiple-family dwelling units.
The Project does not include units that are deed restricted as “affordable units”. Affordability by design, both for purchase and rent, will be created with some of the product within the medium density and high-density designations.
The GHG Handbook includes three measures that involves parking supply and parking cost, including limiting residential parking supply, unbundling residential parking costs from property cost, and implement market price public parking (on-street). For limiting residential parking supply, the GHG Handbook notes, “This measure is ineffective in locations where unrestricted street parking or other offsite parking is available nearby and has adequate capacity to accommodate project-related vehicle parking demand.” Unrestricted street parking is available in the vicinity of the Project site, and is expected to be available in the future. Implementation of unbundling residential parking costs from property cost, would appear to require modification of Stockton Municipal Code section 16.64.040, Number of parking spaces required. In the description of implementing market price public parking, the GHG Handbook notes, “This measure will price all on-street parking in a given community, with a focus on parking near central business districts, employment centers, and retail centers.” The Project is composed of residential land use, rather than central business districts, employment centers and retail centers. Therefore, these parkingrelated mitigation measures are not feasible for the Project.
The GHG Handbook includes a measure related to the density and connectivity of streets. the Project as proposed includes a relatively high density of street intersections within the Project site.
The number of connections to surrounding arterial roadways (i.e., Eight Mile Road, West Lane, and Lower Sacramento Road), however, are constrained by existing adopted precise road plans for each of these roadways. As a result, the measure is considered not feasible for the Project.
Separately, with regard to potential energy measures, it should be noted that none of the energyrelated measures in the GHG Handbook would be anticipated to reduce operational ROG emissions, which are the only operational emissions that are above the SJVAPCD operational thresholds for criteria pollutants. This is because ROG emissions are not generated by energy usage. Therefore, there are no additional feasible energy-related mitigation measures to reduce operational ROG emissions, beyond Mitigation Measures 3.3-1 through 3.3-3.
EXHIBIT 1
1086
REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-27 With regard to the potential for a Voluntary Emissions Reduction Agreement (VERA) measure, Mitigation Measure 3.3-4 requires the City to educate applicants on the benefits of a VERA, and requires the project applicant(s) to consult with the City regarding the results of SJVAPCD’s Rule 9510 process, prior the building permit stage. If emissions reductions associated with mandatory compliance with SJVAPCD’s Rule 9510 are not sufficient to reduce emissions to below the applicable SJVAPCD thresholds of significance for operational ROG, the project applicant is required under Mitigation Measure 3.3-4 to enter into a VERA with the SJVAPCD, to reduce emissions to below the applicable thresholds of significance, after taking into account any emissions reductions associated with mandatory compliance with SJVAPCD’s Rule 9510.
With implementation of the available feasible mitigation measures (Mitigation Measures 3.3-1 through 3.3-43, as provided below), the proposed Project’s emissions would be reduced as shown in Table 3.3-10, below. It should be noted that Table 3.3-10 does not account for further potential reductions associated with the possibility of a VERA agreement; Table 3.3-10 also not account for further reductions in operational emissions that would occur due to implementation of Mitigation Measure 3.13-1, which requires the Project applicant to implement feasible TDM (i.e. VMT reduction) strategies.
4 TABLE 3.3-10: OPERATIONAL PROJECT GENERATED EMISSIONS (TONS PER YEAR) - MITIGATED POLLUTANT CO NOX ROG SOX PM10 PM2.5
THRESHOLD 100 10 10 27 15 15
EMISSIONS
MOBILE 54.1 7.1 7.7 0.1 12.7 3.3
AREA 0 0 5.2 0 0 0
ENERGY 0.8 1.8 0.1 <0.1 0.1 0.1
WATER 0 0 0 0 0 0
WASTE 0 0 0 0 0 0
TOTAL
EMISSIONS
54.9 8.8 13.0 0.2 12.8 3.5
EXCEEDS
THRESHOLD?
N N Y N N N
SOURCES: CALEEMOD (V.2022.1)
As shown in Table 3.3-10, above, the Project’s ROG emissions could be reduced from approximately
14.3 to 13.0 tons per year, with the implementation of Mitigation Measures 3.3-1 through 3.3-3.
However, this would not be sufficient to ensure a reduction of ROGs to below the applicable Air District criteria pollutant threshold of 10 tons per year.
Separately, the SJVAPCD has developed daily mass emissions screening criteria for ROG, NOX, CO, SOX, PM10, and PM2.5 to determine whether project emissions would result in a violation of an AAQS. Because the NAAQS and CAAQS are concentration-based standards, Project emissions were evaluated using the SJVAPCD mass emissions screening approach, which provides a preliminary assessment to determine whether a project would contribute to a violation of an AAQS. The screening is conducted by evaluating daily Project emissions against a 100 pound per day threshold 4 This is because the exact operational emissions reductions associated with Mitigation Measure 3.13-1 depend on the actual VMT reductions applied, which cannot be known at this time.
EXHIBIT 1
1087
3.0 REVISIONS
3.0-28 Final Environmental Impact Report – LeBaron Ranch for each criteria air pollutant. The following table (Table 3.3-11) provides the proposed Project’s mitigated operational emissions in pounds per day in comparison to these screening thresholds. As shown in Table 3.3-11, the proposed Project’s mitigated operational emissions would not exceed any of the daily mass screening criteria thresholds.
TABLE 3.3-11: OPERATIONAL PROJECT GENERATED EMISSIONS (POUNDS PER DAY) - MITIGATED POLLUTANT CO NOX ROG SOX PM10 PM2.5
THRESHOLD
(POUNDS/DAY)
100 100 100 100 100 100
EMISSIONS –
TOTAL PROJECT
48.5 15.5 35.4 0.2 11.2 3.5
EXCEEDS THRESHOLD? N N N N N N
SOURCES: CALEEMOD (V.2022.1)
NOTE: EMISSIONS ONLY INCLUDE THOSE EMISSIONS THAT ARE CONSIDERED “ON-SITE”, PER SJVAPCD GUIDANCE. THIS EXCLUDES “MOBILE” EMISSIONS, EXCEPT FOR APPROXIMATELY 15% OF MOBILE EMISSIONS THAT ARE ESTIMATED TO BE ON-SITE.
Overall, since the Project’s ROG emissions in terms of tons per year would be above the applicable Air district criteria pollutant threshold of 10 tons per yearTherefore, this impact would be considered significant and unavoidable.
The following changes were made to page 3.3-36 of Section 3.3 of the Draft EIR:
The estimated background health incidences of mean ozone annual health effects across the San Joaquin Valley are shown in Table 3.3-1112.
5 ,
6 The background health incidences provide an
estimate of the average number of people over a given population that suffer from some adverse health effect over a given period. For example, the background health incidence in the San Joaquin Valley for total asthma-related emergency room visits for adults is 11,039 per year; this represents approximately 0.3% of the population as experiencing such incidents in a given year.
The following changes were made to page 3.3-37 of Section 3.3 of the Draft EIR:
Furthermore, as shown in Table 3.3-1112, health-related incidences associated with ozone are relatively low in the San Joaquin Valley.
The following changes were made to pages 3.3-39 and 3.3-42 of Section 3.3 of the Draft EIR:
MITIGATION MEASURES
Mitigation Measure 3.3-1: The project Project applicant(s) shall comply with SJVAPCD Rule 4101, which prohibits emissions of visible air contaminants to the atmosphere and applies to any source operation that emits or may emit air contaminants. Specifically, the project applicant(s), during 5 As provided for the San Joaquin Valley for Year 2025, as prepared by Ramboll U.S. Consulting Inc. in their Analysis of Potential Health Effects of Criteria Air Pollutant Emission Impacts, North Manteca Annexation #1 Project, March 2023.
6 Note: Although the Ramboll U.S. Consulting Inc. analysis for was prepared for a different project, the background health incidence rates are not project-specific. Rather, they are for the San Joaquin Valley as a whole for year 2025, and therefore are also provide a representative data snapshot for this project.
EXHIBIT 1
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REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-29 Project operation, shall not discharge into the atmosphere any air contaminant, other than uncombined water vapor, for a period or periods aggregating more that (3) minutes in any one (1) hour which is: a) As dark or darker in shade as that designated as No. 1 on the Ringelmann Chart, as published by the United States Bureau of Mines; b) Of such opacity as to obscure an observer's view to a degree equal to or greater than the smoke described in Section 5.1 of this rule.
Mitigation Measure 3.3-2: The project Project applicant(s) shall comply with SJVAPCD Rule 4601, during Project construction and operation, which limits project has agreed to abide by morelimits stringent VOC emissions requirementsfrom architectural coatings. This rule specifies Emissions of volatile organic compounds from architectural coatings by specifying storage, clean up and labeling requirements. Specific VOC limits for architectural coatings are provided within the Air District’s website, located at: https://ww2.valleyair.org/rules-and-planning/current-district-rules-andregulations/ (The project has agreed to abide by more stringent VOC emissions requirements.) Mitigation Measure 3.3-3: The project Project applicant(s) shall utilize low-VOC paints, equivalent to 10 g/L of ROG, if commercially available.
Mitigation Measure 3.3-4: The City shall educate the Project applicant(s) on the benefits of a VERA.
The Project applicant(s) shall consult with the City regarding the results of SJVAPCD’s Rule 9510 process, prior the building permit stage. If emissions reductions associated with mandatory compliance with SJVAPCD’s Rule 9510 are not sufficient to reduce emissions to below the applicable SJVAPCD thresholds of significance for operational ROG, the project applicant shall enter into a VERA with the SJVAPCD, to reduce emissions to below the applicable thresholds of significance, after taking into account any emissions reductions associated with mandatory compliance with SJVAPCD’s Rule 9510. If conditions warrant participation in a VERA, the VERA shall demonstrate a reduction in emissions that meets SJVAPCD’s ROG operational emissions threshold through a process that funds and implements emissions reduction projects within the SJVAB. The types of emission reduction projects that could be funded include replacing old heavy-duty trucks with cleaner, more efficient heavy-duty trucks, for example. If a VERA is found to be required, the project applicant shall engage in a discussion with SJVAPCD prior to the adoption of the VERA to ensure that feasible mitigation has been identified to reduce emissions to a less-than-significant level.
Mitigation Measure 3.3-5: The Project applicant(s) shall provide information regarding tconsider the Air District’s Clean Green Yard Machines (CGYM) program, which provides incentive funding for the replacement of existing gas powered lawn and garden equipment, to the home-buyers at time of sale of the housing units by the applicant. More information on the District CGYM program and funding can be found at: https://ww2.valleyair.org/grants/zero-emission-landscaping-equipmentvoucher-program/.
Impact 3.3-2: Proposed Project construction activities would not result in a cumulatively considerable net increase of any criteria pollutant for which the Project region is in non-attainment, or conflict or obstruct implementation of the District’s air quality plan. (Less than Significant with Mitigation)
Emissions from construction activities represent temporary impacts that are typically short in duration, depending on the size, phasing, and type of project. Air quality impacts can nevertheless be acute during construction periods, resulting in significant localized impacts to air quality.
Construction-related activities would result in Project-generated emissions from demolition, site EXHIBIT 1
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3.0-30 Final Environmental Impact Report – LeBaron Ranch preparation, grading, paving, building construction, and architectural coatings. CalEEModTM (v.2022.1) was used to estimate construction emissions for the proposed Project. Table 3.3-1213, below, provides the construction criteria pollutant emissions associated with implementation of the proposed Project.
TABLE 3.3-1213: MAXIMUM CONSTRUCTION PROJECT GENERATED EMISSIONS (TONS PER YEAR) POLLUTANT CO NOX ROG SOX PM10 PM2.5
THRESHOLD 100 10 10 27 15 15
EMISSIONS 4.9 3.1 8.5 <0.1 1.4 0.6
EXCEEDS
THRESHOLD?
N N N N N N
SOURCES: CALEEMOD (V.2022.1)
If the proposed Project’s emissions will exceed the SJVAPCD’s threshold of significance for construction-generated emissions, the proposed Project will have a significant impact on air quality and conflict with the Clean Air Plan and all feasible mitigation are required to be implemented to reduce emissions. As shown in Table 3.3-1213, Project maximum construction emissions would not exceed the SJVAPCD thresholds of significance. Nevertheless, regardless of emission quantities, the SJVAPCD requires construction related mitigation in accordance with their rules and regulations.
Nevertheless, implementation of the Mitigation Measure 3.3-4 5 through 3.3-7 8 (see below), would further reduce proposed Project construction related emissions to the extent possible.
CONCLUSION
The proposed Project would comply with pre-existing requisite federal, State, SJVAPCD, and other local regulations and requirements, as well as implement the mitigation measures provided by the SJVAPCD for construction-related PM10 emissions, including those provided in Mitigation Measure
3.3-4 6 through 3.3-79. Therefore, the Project’s criteria pollutant emissions would be considered to have a less than significant impact and the Project would not impede or conflict with the Clean Air Plan.
MITIGATION MEASURE(S)
Mitigation Measure 3.3-64: Prior to the issuance of a Grading Permit for each phase of the Project, the Project Proponent shall prepare and submit a Dust Control Plan that meets all the applicable requirements of APCD Rule 8021, Section 6.3, for the review and approval of the APCD Air Pollution Control Officer.
Mitigation Measure 3.3-57: During all construction activities, the Project Proponent shall implement dust control measures, as required by APCD Rules 8011-8081, to limit Visible Dust Emissions to 20% opacity or less. Dust control measures shall include application of water or chemical dust suppressants to unpaved roads and graded areas, covering or stabilization of transported bulk materials, prevention of carryout or trackout of soil materials to public roads, limiting the area subject to soil disturbance, construction of wind barriers, access restrictions to inactive sites as required by the applicable rules.
Mitigation Measure 3.3-68: During all construction activities, the Project proponent shall implement the following dust control practices identified in Tables 6-2 and 6-3 of the GAMAQI (2002). a. All disturbed areas, including storage piles, which are not being actively utilized for EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-31 construction purposes, shall be effectively stabilized of dust emissions using water, chemical stabilizer/suppressant, or vegetative ground cover. b. All on-site unpaved roads and off-site unpaved access roads shall be effectively stabilized of dust emissions using water or chemical stabilizer/suppressant. c. All land clearing, grubbing, scraping, excavation, land leveling, grading, cut and fill, and demolition activities shall control fugitive dust emissions by application of water or by presoaking.
d. When materials are transported off-site, all material shall be covered, effectively wetted to limit visible dust emissions, or at least six inches of freeboard space from the top of the container shall be maintained.
e. All operations shall limit or expeditiously remove the accumulation of mud or dirt from adjacent public streets at least once every 24 hours when operations are occurring. The use of dry rotary brushes is expressly prohibited except where preceded or accompanied by sufficient wetting to limit the visible dust emissions. Use of blower devices is expressly forbidden.
f. Following the addition of materials to, or the removal of materials from, the surface of outdoor storage piles, said piles shall be effectively stabilized of fugitive dust emissions utilizing sufficient water or chemical stabilizer/suppressant. g. Limit traffic speeds on unpaved roads to 5 mph.
h. Install sandbags or other erosion control measures to prevent silt runoff to public roadways from sites with a slope greater than one percent.
Mitigation Measure 3.3-79: Asphalt paving shall be applied in accordance with APCD Rule 4641, the purpose of which is to limit VOC emissions by restricting the application and manufacturing of certain types of asphalt for paving and maintenance operations. This rule applies to the manufacture and use of cutback asphalt, slow cure asphalt and emulsified asphalt for paving and maintenance operations. The Project Applicant shall coordinate with the APCD, prior to Project asphalt paving activities, to ensure all Project asphalt paving would comply with this rule. The Project Applicant shall provide the City of Stockton with evidence of consultation with the APCD, including confirmation of compliance with APCD Rule 4641.
The following changes were made to page 3.3-44 of Section 3.3 of the Draft EIR:
Table 3.3-13 14 provides the California Air Resources Board minimum separation recommendations on siting sensitive land uses.
TABLE 3.3-1314: CARB MINIMUM SEPARATION RECOMMENDATIONS ON SITING SENSITIVE LAND USES
SOURCE CATEGORY ADVISORY RECOMMENDATIONS
Freeways and HighTraffic Roads • Avoid siting new sensitive land uses within 500 feet of a freeway, urban roads with 100,000 vehicles/day, or rural roads with 50,000 vehicles/day.
Distribution Centers
• Avoid siting new sensitive land uses within 1,000 feet of a distribution center (that accommodates more than 100 trucks per day, more than 40 trucks with operating transport refrigeration units (TRUs) per day, or where TRU unit operations exceed 300 hours per week).
• Take into account the configuration of existing distribution centers and avoid locating residences and other new sensitive land uses near entry and exit points.
Rail Yards
• Avoid siting new sensitive land uses within 1,000 feet of a major service and maintenance rail yard.
• Within one mile of a rail yard, consider possible siting limitations and mitigation EXHIBIT 1
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3.0-32 Final Environmental Impact Report – LeBaron Ranch
SOURCE CATEGORY ADVISORY RECOMMENDATIONS
approaches.
Ports
• Avoid siting of new sensitive land uses immediately downwind of ports in the most heavily impacted zones. Consult local air districts or the CARB on the status of pending analyses of health risks.
Refineries
• Avoid siting new sensitive land uses immediately downwind of petroleum refineries.
Consult with local air districts and other local agencies to determine an appropriate separation.
Chrome Platers • Avoid siting new sensitive land uses within 1,000 feet of a chrome plater.
Dry Cleaners Using
Perchloro- ethylene
• Avoid siting new sensitive land uses within 300 feet of any dry cleaning operation. For operations with two or more machines, provide 500 feet. For operations with 3 or more machines, consult with the local air district.
• Do not site new sensitive land uses in the same building with perc dry cleaning operations.
Gasoline Dispensing
Facilities
• Avoid siting new sensitive land uses within 300 feet of a large gas station (defined as a facility with a throughput of 3.6 million gallons per year or greater). A 50-foot separation is recommended for typical gas dispensing facilities.
SOURCES: AIR QUALITY AND LAND USE HANDBOOK: A COMMUNITY HEALTH PERSPECTIVE” (CARB 2005) The following changes were made to pages 3.3-45 and 3.3-46 of Section 3.3 of the Draft EIR:
Residences are proposed as part of the Project, which are considered traditional sensitive receptors. However, no residences would be located within 500 feet of a freeway, urban road with 100,000 vehicles/day or more, or a rural road with 50,000 vehicles/day or more. Additionally, under CEQA, an EIR need not analyze the impacts of the existing environment on the Project.
With regard to nearby sensitive receptors, although the Project does not include substantial sources of TACs, there would be some TACs during the Project’s construction and operational phases.
Specifically, Virtually no residual TAC emissions and corresponding cancer risk are anticipated after Project construction. The proposed Project is not anticipated to generate long-term, operational sources of TAC emissions because the proposed Project would only include residential land uses and public open space. The Project would not include heavy industrial uses or other land uses typically associated with stationary sources of TACs. during the Project’s operational phase, the Project would generate some heavy-duty trucks, which are an emitter of diesel particulate matter (DPM). In particular, DPM is emitted from on-site heavy-duty truck vehicle circulation and idling, and off-site mobile travel. Additionally, during Project operation, DPM would be generated by heavy-duty off-road construction vehicles. The SJVAPCD has established a screening calculator entitled the “Prioritization Calculator”. An estimate of DPM emissions generated by the proposed project was calculated. Specifically, during Project operation, heavy-duty trucks would generate DPM from on-site mobile and idling emissions, and off-site mobile emissions 0.25 miles from the Project site, in accordance with the California Office of Environmental Health Hazard Assessment (OEHHA) guidance, as recommended by the SJVAPCD. The estimate of DPM emissions were based on the data provided in the Traffic Analysis for the proposed project, and with diesel particulate matter mobile emission rates from CARB’s EMFAC2021 database, and from standard heavy-duty truck idling emission rates from CARB. Additionally, construction-related off-road construction vehicle emissions data was provided by CalEEMod.
The results of the screening analysis show that the cancer and non-cancer risks associated with the proposed Project, inclusive of both construction and operational-related sources, are below the SJVAPCD screening thresholds contained within their Prioritization Calculator. Specifically, the EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-33 Prioritization Calculator estimates that the prioritization score associated with total cancer risk from proposed project operational and construction-related DPM (combined) would be approximately
9.31, below the SJVAPCD threshold of 10 that would require development of air toxics Health Risk Assessment (HRA) that includes air dispersion modeling.7 Additionally, non-cancer (i.e. chronic and acute risks) associated with project DPM would also be well below the applicable thresholds for the Maximally Exposed Individual (i.e. greater than or equal to the Hazard Index level of 1). Therefore, the complex air dispersion modeling using software such as AERMOD is not required. See Appendix B for further detail.
Separately,
iIt should be noted that the mobile vehicles generated by the Project during operation would generate UFPs through vehicle emissions, braking, and tire wear. Like PM in general, (though generating even higher risk per unit than larger particle sizes) UFPs are notable for their potential to generate chronic risks associated with cardiovascular disease, potential long-term loss of longfunction, and cancer. According to a recent study prepared for the European Geosciences Union, UFPs vary widely as a proportion of PM overall, depending on location; specifically, the PM0.1 to PM2.5 ratio analyzed in approximately 39 cities in the United States varied from approximately 1% to 16%.8 These factors vary so widely because the sources of PM0.1 vary substantially from city to city.
For example, cities that are located close to substantial sources of natural gas combustion have higher PM0.1 to PM2.5 ratios, since almost all the PM emitted by natural gas combustion is in the PM0.1 size fraction, whereas this is only true for less than half of the PM emitted by gasoline and diesel fuel combustion. Taken together, these facts support the potential importance of natural gas combustion for ambient PM0.1 concentrations.
3.4 BIOLOGICAL RESOURCES
The following changes were made to page 3.4-3 of Section 3.4 of the Draft EIR:
Field Surveys
The Project site was subject to a field surveys by Principal Biologist Steve McMurtry on April 22, 2022, and May 15, 2023. The site reconnaissance surveys served several purposes. First, they served as reconnaissance of the site to establish the existing conditions of the site and to verify information gathered in the pre-field investigation. This included identification of the habitat types, hydrologic features, topography, soil characteristics, and vegetation. The field investigations followed the Protocols for Surveying and Evaluating Impacts to Special Status Native Plant Populations and Natural Communities (CDFW 2009). Habitat was recorded. Visibility during each survey was excellent.
The following changes were made to page 3.4-29 of Section 3.4 of the Draft EIR:
Other Insects: There are two other insects that are not formally listed, special-status species, but are included in the CNDDB search results. These include crotch bumble bee (Bombus crotchii) and 7 Sensitive receptors were assumed to be within the 0-100 meter distance range from the Project site, which represents the most conservative distance assumption.
8 Venecek, M. A., Yu, X., and Kleeman, M. J.: Predicted ultrafine particulate matter source contribution across the continental United States during summertime air pollution events, Atmos. Chem. Phys., 19, 9399– 9412, https://doi.org/10.5194/acp-19-9399-2019, 2019.
EXHIBIT 1
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3.0-34 Final Environmental Impact Report – LeBaron Ranch American bumble bee (Bombus pensylvanicus). Neither species are covered by the San Joaquin County Multi-Species Habitat Conservation and Open Space Plan (“Plan” or “SJMSCP”). It is noted that the crotch bumble is a candidate species for listing under the State Endangered Species Act.
While these species are documented within the nine (9)-quad region for the Project site, they are not documented on the Project site. As shown in Table 3.4-3, appropriate habitat for crotch bumble bee (Bombus crotchii) and American bumble bee (Bombus pensylvanicus) is not present. This determination is based on the field surveys completed by Principal Biologist Steve McMurtry on April 22, 2022, and May 15, 2023. No special-status invertebrates were observed within the Project site during field surveys and none are expected to be affected by the proposed Project based on the lack of appropriate habitat. The habitat present on the Project site is not ideal natural habitat for these species and none are believed to be present. Further, the nearest CNDDB occurrence of crotch bumble bee is over 20 miles southwest of the Project site. The nearest CNDDB occurrence of American bumble bee is approximately 4.1 miles or further north of the Project site. The habitat present on the Project site is not ideal natural habitat for these species and none are believed to be present.
Conclusion: The Project site is located within the jurisdiction of the San Joaquin County MultiSpecies Habitat Conservation and Open Space Plan (“Plan” or “SJMSCP”) and is located within the Central Zone of the SJMSCP. Within the Central Zone, the Project site is located in the Category C/Pay Zone B. The Category C/Pay Zone B includes parcels containing habitat types classified as Agricultural Habitat Lands which are not otherwise exempt. Applicants pay mitigation fees on a peracre basis, as established by the JPA, according to the measures needed to mitigate impacts to the various habitat and biological resources. The project applicant would be required to seek coverage under the SJMSCP and would be subject to the Category C/Pay Zone B fees in order to mitigate for any habitat impacts. Coverage involves compensation for habitat impacts on covered species through payment of development fees for conversion of lands that may provide habitat for covered special status species. These fees are used to preserve and/or create habitat in preserves to be managed in perpetuity. In addition, coverage includes incidental take avoidance and minimization measures for species that could be affected as a result of the proposed project. The valley elderberry longhorn beetle, longhorn fairy shrimp, vernal pool fairy shrimp, and midvalley fairy shrimp are covered species under the SJMCP.
The following changes were made to page 3.4-32 of Section 3.4 of the Draft EIR:
Analysis: Powerlines and trees located in the region represent potentially suitable nesting habitat for a variety of special-status birds. Additionally, the agricultural land represents potentially suitable nesting habitat for some ground-nesting birds. In general, most nesting occurs from late February and early March through late July and early August, depending on various environmental conditions. The CNDDB currently contains records for Swainson's hawk, burrowing owl, and tricolored blackbird in the vicinity of the Project site. In addition to the species described above, common raptors, may nest in or adjacent to the Project site. Further, indirect impacts related to bird collision with glass windows and bird mortality associated with domestic pets could occur.
While avian mortality due to window collisions is a real phenomenon, CEQA-level assessments of this risk are typically limited to developments with an especially high percentage of clear and/ or reflective glazing (glass, windows) on exterior facades, and/ or other specific elements deemed likely to result in a high rate of collisions.
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Final Environmental Impact Report – LeBaron Ranch 3.0-35 Glazing on the proposed residential windows would be minimal. The glazing included in the Project consists entirely of windows for the residential units, all of which are isolated from each other at regular intervals versus being grouped/conjoined to form larger contiguous window panels, and each is further divided into smaller areas. The elevations also feature forms of architectural relief (overhangs, spatially offset adjacent faces) as well as varied (opaque) materials and colors, all of which would break up the exterior visually (i.e., create “visual noise”), and increase the likelihood that birds would perceive the building overall as a solid surface.
Overall, by current architectural/design standards, the project provides minimal risk of bird collisions. The number of birds that would collide with the building over time is virtually impossible to estimate, and thus speculative. In any event, these impacts are unlikely to be significant at a regional or even local scale. In particular, bird strikes (to the degree that such occur, if at all) are more likely to involve common (and not special-status) species given their relative abundance in the area and local conditions. The impact related to bird collisions would be less than significant, and no mitigation is required.
New sources of noise and light during the construction and operational phases of the project could adversely affect nesters if they located adjacent to the Project site in any given year. Additionally, the proposed Project would eliminate the agricultural areas on the Project site, which serve as potential foraging habitat for birds throughout the year. Mitigation Measure 3.4-1 requires participation in the SJMSCP. As part of the SJMSCP, SJCOG requires preconstruction surveys for projects that initiate grading activities during the avian breeding season (March 1 – August 31).
When active nests are identified, the biologists develop buffer zones around the active nests as deemed appropriate until the young have fledged. SJCOG also uses the fees to purchase habitat as compensation for the loss of foraging habitat. These ITMMs are included in Mitigation Measures
3.4-2 through 3.4-4. These mitigation measures provide more details about what SJMSCP already requires (i.e., ITMMs) under Mitigation Measure 3.4-1. Implementation of the proposed Project, with the Mitigation Measures 3.4-1 through 3.4-4, would ensure that potential impacts to special status birds are reduced to a less than significant level.
MITIGATION MEASURE(S)
Implement Mitigation Measure 3.4-1.
Mitigation Measure 3.4-2: Prior to the commencement of grading activities or other ground disturbing activities on the Project site, the Project applicant shall arrange for a qualified biologist to conduct a preconstruction survey for Swainson’s hawks. If no hawks or hawk nests are detected, then construction activities may commence. If Swainson’s hawks or occupied nests are discovered, then the following shall be implemented:
• During the nesting season (February 15 through August 31) and Swainson’s hawks are nesting in or near the Project site, a construction setback of 250 feet of the nest tree (as measured from under the nest) would be required until nesting is complete.
This requirement is consistent with the incidental take and minimization measures (ITMMs) outlined in the SJMSCP. Implementation of this requirement shall occur prior to grading or site clearing activities. SJCOG shall be responsible for monitoring and a qualified biologist shall conduct surveys as required.
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3.0-36 Final Environmental Impact Report – LeBaron Ranch Mitigation Measure 3.4-3: Prior to the commencement of grading activities or other ground disturbing activities on the Project site, the Project applicant shall arrange for a qualified biologist to conduct a preconstruction survey for burrowing owls. If no owls or owl nests are detected, then construction activities may commence. If burrowing owls or occupied nests are discovered, then the following shall be implemented:
• During the nesting season (February 1 and August 31) and burrowing owls are present onsite, a 250-foot construction setback from the natal burrow would be required until nesting is complete.
• Outside the nesting season (September 1 and January 31) burrowing owls occupying the Project site should be evicted from the Project site by passive relocation as described in the California Department of Fish and Game’s Staff Report on Burrowing Owls (Oct., 1995) These requirements are consistent with the incidental take and minimization measures (ITMMs) outlined in the SJMSCP. Implementation of this requirement shall occur prior to grading or site clearing activities. SJCOG shall be responsible for monitoring and a qualified biologist shall conduct surveys and relocate owls as required.
Mitigation Measure 3.4-4: Prior to the commencement of grading activities or other ground disturbing activities on the Project site, the Project applicant shall arrange for a qualified biologist to conduct a preconstruction survey for tricolored blackbird. If no tricolored blackbird or tricolored blackbird nests are detected, then construction activities may commence. If tricolored blackbird or occupied nests are discovered, then the following shall be implemented:
• A setback of 500 feet from colonial nesting areas shall be established and maintained during the nesting season for the period encompassing nest building and continuing until fledglings leave nests. This setback applies whenever construction or other grounddisturbing activities must begin during the nesting season in the presence of nests which are known to be occupied. Setbacks shall be marked by brightly colored temporary fencing.
This requirement is consistent with the incidental take and minimization measures (ITMMs) outlined in the SJMSCP. Implementation of this requirement shall occur prior to grading or site clearing activities. SJCOG shall be responsible for monitoring and a qualified biologist shall conduct surveys as required.
The following changes were made to page 3.4-38 of Section 3.4 of the Draft EIR:
The following mitigation measures would require compliance with the Stockton Municipal Code for removal and replacement of Heritage Oak Trees. With the implementation of the following mitigation measures, the proposed Project would have a less than significant impact relative to this topic.
MITIGATION MEASURE(S)
Mitigation Measure 3.4-52: If removal of any oak tree on the project site is required, the project applicant or contractor shall hire a certified arborist shall to survey the oak trees proposed for removal to determine if they are Heritage Trees as defined in Stockton Municipal Code Chapter
16.130. The survey shall occur prior to site disturbance. The arborist report with its findings shall be submitted to the City’s Community Development Department. If Heritage Trees are determined to EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-37 exist on the property, removal of any such tree shall require a permit to be issued by the City in accordance with Stockton Municipal Code Chapter 16.130. The permittee shall comply with all permit conditions, including tree replacement at specified ratios.
3.5 CULTURAL AND TRIBAL RESOURCES
The following changes were made to pages 3.5-12 through 3.5-14 of Section 3.5 of the Draft EIR:
Impact 3.5-2: Project implementation has the potential to cause a substantial adverse change to a significant archaeological resource, as defined in CEQA Guidelines §15064.5, or a significant tribal cultural resource, as defined in Public Resources Code §21074 (Less than Significant with Mitigation)
The Project site is located in an area known to have archaeological, cultural, and tribal cultural resources. As noted above, a CHRIS search was requested from the CCIC, which included the Project site and a 0.25-mile radius. According to the CCIC CHRIS results, no cultural resources have been reported within the Project site; however, several resources have been found within the 0.25-mile search radius. A letter was sent to the NAHC requesting a records search of the Sacred Lands files for the Project site, as well as a list of Native American tribes that may have knowledge of cultural resources in the Project site. On August 24, 2023, the NAHC responded indicating that results were negative for Sacred Lands. The NAHC provided a list of individuals and groups to contact regarding potential cultural resources within the Project site. Letters were sent to the groups and individuals listed on July 29, 2023, in compliance with AB 52 and SB 18 tribal consultation requirements; refer to Appendix D for tribal consultation communications. The consultation letters provided information regarding the proposed Project and contact information for the Project Planner. Under AB 52, Native American tribes have 30 days to respond and request further project information and formal consultation. No tribal organizations responded requesting formal consultation with the City.
Although no archeological resources or Native American tribal cultural resources are known to occur within the Project site, as with most projects in the region that involve ground-disturbing activities, there is the potential for discovery of previously unknown archaeological resources and/or tribal cultural resources. Implementation of Mitigation Measures 3.5-1 through 3.5-2 would ensure that the potential impact to archaeological and tribal cultural resources is less than significant.
MITIGATION MEASURE(S)
Mitigation Measure 3.5-1: Prior to any ground-disturbing activities on the Project site, the Developer shall retain a qualified archaeologist and native American monitor shall to conduct preconstruction worker cultural resources sensitivity training. The training session shall focus on the recognition of the types of historical and cultural, including Native American, resources that could be encountered;, procedures to be followed if resources are found, including who to contact and appropriate avoidance measures until the find(s) can be properly evaluated,; and pertinent laws protecting these resources. Training shall be scheduled at the discretion of the Project applicant in consultation with the City. The Developer shall be responsible for ensuring that all workers requiring training are in attendance. Those in attendance shall be recorded, with records maintained on-site. - I
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3.0-38 Final Environmental Impact Report – LeBaron Ranch Any new workers that were not part of the initial training shall be required to undergo a new training session.
Mitigation Measure 3.5-2: If any cultural resources, including prehistoric or historic artifacts, or other indications of archaeological resources, are found during grading and construction activities during any phase of the Project, all work shall be halted immediately within a 200-foot radius of the discovery until an archaeologist meeting the Secretary of the Interior's Professional Qualifications Standards in prehistoric or historical archaeology, as appropriate, has evaluated the find(s).
Work shall not continue at the discovery site until the archaeologist conducts sufficient research and data collection to make a determination that the resource is either 1) not cultural in origin; or 2) not potentially significant or eligible for listing on the NRHP or CRHR; or 3) not a significant Public Trust Resource.
If Native American resources are identified, a Native American monitor, following the Guidelines for Monitors/Consultants of Native American Cultural, Religious, and Burial Sites established by the Native American Heritage Commission, may also be required and, if required, shall be retained at the Project applicant’s expense.
If the discovery proves to be significant under CEQA and cannot be avoided by the Project, additional work such as data recovery excavation may be warranted to mitigate any significant impacts.
Mitigation could include avoidance, preservation in place, or the scientific removal, analysis, reporting, and curation of any recovered cultural materials. Construction shall not resume in the area until appropriate protection and preservation measures are in place and have been approved by the Community Development Director or designee, and the qualified archaeologist states in writing that the proposed construction activities would not significantly damage any archaeological or tribal cultural resources.
Impact 3.5-3: Project implementation has the potential to disturb human remains, including those interred outside of formal cemeteries (Less than Significant)
Indications suggest that humans have occupied San Joaquin County for over 10,000 years and it is not always possible to predict where human remains may occur outside of formal burials.
Therefore, excavation and construction activities, regardless of depth, may yield human remains that may not be interred in marked, formal burials.
Under CEQA, human remains are protected under the definition of archaeological materials as being “any evidence of human activity.” Public Resources Code Section 5097 has specific stop-work and notification procedures to follow in the event that human remains are inadvertently discovered during Project implementation. Additionally, Section 16.36.050 of the Stockton Municipal Code requires construction activities to cease in the event human remains are discovered during construction, and the County Coroner and Director must be notified immediately in compliance with CEQA Guidelines 15064.5(d). A qualified archaeologist shall be contacted to evaluate the situation. If the human remains are of Native American origin, the Coroner shall notify the Native American Heritage Commission within 24 hours of this identification. The Native American Heritage Commission will identify the most likely descendent of the Native American to inspect the site and provide recommendations for the proper treatment of the remains and associated grave goods. If a most likely descendant cannot be identified or fails to make a recommendation, or the landowner EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-39 rejects the recommendations of the most likely descendant, and the mediation by the Native American Heritage Commission fails to provide measures acceptable to the landowner, then the landowner shall rebury the remains and associated grave goods with appropriate dignity on the property in a location not subject to further subsurface disturbance.
3.6 GEOLOGY AND SOILS
The following changes were made to pages 3.6-15 and 3.6-16 of Section 3.6 of the Draft EIR:
The Project site is relatively flat; therefore, the potential for a landslide in the Project site is nonexistent. Some limited potential for slope instability risk could arise during grading and construction activities, where slopes could be over-steepened. However, this risk is mitigated by adhering to relevant California Building Code requirements, which includes requirements for building design and construction. Additionally, according to the CGS Information Warehouse: Regulatory Maps, the site is not located within a Landslide and Liquefication Zone. As a result, the probability of landslides causing substantial adverse effects on people or structures is less than significant.
The following changes were made to page 3.6-17 of Section 3.6 of the Draft EIR:
Overall, compliance with applicable State and City requirements, including but not limited to the NPDES Stormwater Program and the City’s Grading and Erosion Control Ordinance, would ensure that the proposed Project would have a less-than-significant impact relative to this topic.
The following changes were made to page 3.6-20 of Section 3.6 of the Draft EIR:
MITIGATION MEASURE(S)
Mitigation Measure 3.6-1: If any paleontological resources are found during grading and construction activities of the Project, all work shall be halted immediately within a 200-foot radius of the discovery, the City of Stockton Community Development Director shall be notified, and a professional vertebrate paleontologist (as defined by the Society for Vertebrate Paleontology) shall be contacted immediately to evaluate the finduntil a qualified paleontologist has evaluated the find.
The paleontologist shall have the authority to stop or divert construction, as necessary.
Documentation and treatment of the discovery shall occur in accordance with Society of Vertebrate Paleontology standards.
Work shall not continue at the discovery site until the professional vertebrate paleontologist evaluates the find pursuant to the CEQA Guidelines and makes a determination regarding the significance of the resource and identifies recommendations for conservation of the resource, including, but not limited to, preserving in place or relocating on the Project site, if feasible, or collecting the resource to the extent feasible and documenting the find with the University of California Museum of Paleontology.
3.7 GREENHOUSE GASES, CLIMATE CHANGE, AND ENERGY
The following changes were made to pages 3.7-24 and 3.7-25 of Section 3.7 of the Draft EIR:
EXHIBIT 1
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3.0-40 Final Environmental Impact Report – LeBaron Ranch City of Stockton Climate Action Plan
The City of Stockton Climate Action Plan (2014) sets forth a strategy to reduce communitygenerated GHG emissions, consistent with statewide GHG reduction efforts. As a condition for approval of the 2035 General Plan, the City of Stockton entered into a Settlement Agreement with the Sierra Club and the California Attorney General’s Office in October 2008. The Settlement Agreement was enacted to ensure future growth outlined in the City of Stockton 2035 General Plan addresses GHG emissions in a meaningful and constructive manner. The City of Stockton Climate Action Plan (CAP) outlines a framework to feasibly reduce community GHG emissions in a manner that is supportive of AB 32 and is consistent with the Settlement Agreement and 2035 General Plan policy. The CAP is considered functionally equivalent to a GHG Reduction Plan, given that both refer to a document that quantifies and reduces GHG emissions within a particular jurisdiction.
A “Qualified GHG Reduction Plan” under CEQA refers to a plan that meets specific criteria for reducing greenhouse gas (GHG) emissions. This plan is intended to be used as a tool for evaluating the environmental impacts of proposed projects and plans under CEQA.
A Qualified GHG Reduction Plan must:
1. Quantify existing and projected GHG emissions.
2. Develop a level of cumulative GHG emissions that, based on substantial evidence, would not be considered significant for CEQA purposes.
3. Specify measures and standards that would ensure the level of GHG emissions is achieved.
4. Include monitoring to track progress in achieving the GHG reduction goals.
The plan must also comply with CEQA Guidelines Section 15183.5, which outlines the requirements for Qualified GHG Reduction Plans. These plans are intended to be used for both project-level and plan-level analyses under CEQA. Based on these criteria, the City of Stockton Climate Action Plan is not considered a “Qualified GHG Reduction Plan”, since it does not include a level of cumulative GHG emissions that, based on substantial evidence, would not be considered significant for CEQA purposes, consistent with the latest case law.
Specifically, the City of Stockton Climate Action Plan includes community and municipal GHG reduction targets. The City of Stockton Climate Action Plan states: “…the City now proposes approximately 10% below 2005 levels [by year 2020] as its GHG reduction goal which would be consistent with the level of reductions needed at the state level to meet the AB 32 goal, compared to statewide 2005 levels.” See City of Stockton Climate Action Plan page ES-7. However, this threshold is not meant for usage as a CEQA threshold. Moreover, it should be noted that year 2020 has already come and gone. Therefore, this emissions target is no longer relevant. Furthermore, it is not appropriate to translate this target into requirements for an individual project, since there is no clear mechanism to do so.
Separately, the City of Stockton Climate Action Plan states that “This plan, if fully implemented, would result in a 20% reduction in per capita GHG emission from 2005 to 2020. Compared to the statewide effort needed to meet AB 32, for the land use sector (e.g. excluding heavy industrial sources, marine transportation, etc., which are not included in Stockton’s local inventory), the state would need to reduce per capita GHG emissions from the land use sector from 10.0 MT/person in EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-41 1990 to approximately 7.4 MT/person in 2020. Implementation of the CAP would result in reducing Stockton’s emissions from approximately 8.5 MT/person in 2005 to 6.8 MT/person in 2020, which is slightly less than the state goal in 2020 (see data in Appendix E)”. However, subsequently, the Golden Door Properties, LLC v. County of San Diego case held that the use of a quantitative threshold (like the efficiency threshold described above), which has historically been used for EIRs throughout California, must be adopted by the City via a resolution, ordinance or regulation based on a public review process, and supported by substantial evidence. However, such a quantitative threshold as included with the City of Stockton Climate Action Plan has never been specifically adopted as a threshold by the City via a resolution, ordinance, or regulation. Moreover, this efficiency threshold also relates only to year 2020, which has already come and gone. Therefore, overall, the usage of a per capita efficiency metric, such as the one included within the City of Stockton Climate Action Plan, is also not relevant or appropriate in a CEQA context.
The following changes were made to page 3.7-25 of the Draft EIR:
The vast majority of individual projects do not generate sufficient GHG emissions to create a project-specific impact through a direct influence to climate change; therefore, the issue of climate change typically involves an analysis of whether a project’s contribution towards an impact is cumulatively considerable. “Cumulatively considerable” means that the incremental effects of an individual project are significant when viewed in connection with the effects of past projects, other current projects, and probable future projects (CEQA Guidelines, Section 15355).
For individual proposed projects, the significance of GHG emissions may be evaluated based on locally adopted quantitative thresholds, or consistency with a regional GHG reduction plan (such as a Climate Action Plan). The City of Stockton does have a formal GHG emissions reduction plan, in the form of the City of Stockton Climate Action Plan (2014). However, the City of Stockton Climate Action Plan only provided analysis of the Project’s emissions and established an emissions target for year 2020, which has come and gone. Moreover, the Stockton Climate Action Plan is not considered a ”Qualified GHG Reduction Plan. Therefore, analysis of the Project’s consistency with the Stockton Climate Action Plan is provided for informational purposes only.
In addition, the Project is also assessed based on its consistency with CARB’s adopted Scoping Plans, including the Project’s compliance with relevant Scoping Plan measures, as well as the latest RTP/SCS for the region within which the Project is located within (i.e., the San Joaquin Council of Governments (SJCOG) 2022 RTP/SCS). It should be noted that the Scoping Plan is consistent with the AB 1279 GHG reduction targets of achieving carbon neutrality by 2045, and reducing anthropogenic emissions to 85 percent below 1990 levels by 2045. Therefore, consistency with the CARB’s most recent Scoping Plan would also demonstrate consistency with the carbon neutrality requirements encapsulated by AB 1279. FurthermoreSeparately, the Project is evaluated for its consistency with the City of Stockton Climate Action Plan (CAP), which was adopted in 2014, for informational purposes only.
The following changes were made to pages 3.7-26 through 3.7-35 of Section 3.7 of the Draft EIR:
EXHIBIT 1
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3.0-42 Final Environmental Impact Report – LeBaron Ranch Impact 3.7-1: Project implementation would not generate greenhouse gas emissions, either directly or indirectly, that may have a significant impact on the environment and would not conflict with an applicable plan, policy, or regulation adopted for the purpose of reducing the emissions of greenhouse gases (Less than Significant)
Emissions of GHGs contributing to global climate change are attributable in large part to human activities associated with the industrial/manufacturing, utility, transportation, residential, and agricultural sectors. Therefore, the cumulative global emissions of GHGs contributing to global climate change can be attributed to every nation, region, and city, and virtually every individual on Earth. A project’s GHG emissions are at a micro-scale relative to global emissions, but could result in a cumulatively considerable incremental contribution to a significant cumulative macro-scale impact. Implementation of the Project would contribute to increases of GHG emissions that are associated with global climate change. Estimated GHG emissions attributable to Project development would be primarily associated with increases of CO2 and other GHG pollutants, such as methane (CH4) and nitrous oxide (N2O), from mobile sources and utility usage.
Several statewide GHG reduction strategies apply to the Project either directly or indirectly. A summary of these strategies is provided in Table 3.7-2, below.
TABLE 3.7-2: SUMMARY OF STATEWIDE GHG REDUCTION STRATEGIES THAT APPLY TO THE PROJECT
PROJECT COMPONENT
APPLICABLE
LAWS/REGULATIONS
GREENHOUSE GAS REDUCTION MEASURES REQUIRED FOR PROJECT
BUILDING COMPONENTS / FACILITY OPERATIONS
Roofs/Ceilings/ Insulation CAL Green Code (Title
24, Part 11) California
Energy Code
(Title 24, Part 6)
The Project must comply with efficiency standards regarding roofing, ceilings, and insulation. For example:
Roofs/Ceilings: New construction must reduce roof heat island effects per CALGreen Code Section 106.11.2, which requires use of roofing materials having a minimum aged solar reflectance, thermal emittance complying with Sections A5.106.11.2.2 and A5.106.11.2.3, or a minimum aged Solar Reflectance Index as specified in Table A5.106.11.2.2 or A5.106.11.2.3. Roofing materials must also meet solar reflectance and thermal emittance standards contained in Title 20 Standards.
Roof/Ceiling Insulation: Requirements for the installation of roofing and ceiling insulation (see Title 24, Part 6 Compliance Manual at Section 3.2.2).
Flooring CALGreen Code The Project must comply with efficiency standards regarding flooring materials. For example, for 80% of floor area receiving “resilient flooring,” the flooring must meet applicable installation and material requirements contained in CALGreen Code Section 5.504.4.6.
Window and Doors California Energy
Code
The Project must comply with fenestration efficiency requirements.
For example, the choice of windows, glazed doors, and any skylights for the Project must conform to energy consumption requirements affecting size, orientation, and types of fenestration products used (see Title 24, Part 6 Compliance Manual, Section 3.3).
Building Walls/ Insulation CALGreen Code
California Energy
The Project must comply with efficiency requirements for building EXHIBIT 1
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Code walls and insulation.
Exterior Walls: Must meet requirements in the current edition of the California Energy Code and comply with Section A5.106.7.1 or A5.106.7.2 of CALGreen for wall surfaces, as well as Section 5.407.1, which requires weather-resistant exterior wall and foundation envelope as required by California Building Code Section 1403.2.
Construction must also meet requirements contained in Title 24, Part 6, which vary by material of the exterior walls (see Title 24, Part 6 Compliance Manual, Part 3.2.3).
Demising (Interior) Walls: Mandatory insulation requirements for demising walls (which separate conditioned from non-conditions space) differ by the type of wall material used (Title 24, Part 6 Compliance Manual Part 3.2.4).
Door Insulation: Mandatory requirements for air infiltration rates to improve insulation efficiency; they differ according to the type of door (Title 24, Part 6 Compliance Manual Part 3.2.5).
Flooring Insulation: Mandatory requirements for insulation that depend on the material and location of the flooring (Title 24, Part 6 Compliance Manual Part 3.2.6).
Finish Materials CALGreen The Project must comply with pollutant control requirements for finish materials. For example, materials including adhesives, sealants, caulks, paints and coatings, carpet systems, and composite wood products must meet requirements in CALGreen to ensure pollutant control (CALGreen Section 5.504.4).
Wet Appliances
(Toilets/Faucets/Urinal,
Dishwasher/Clothes
Washer, Spa and
Pool/Water Heater)
CALGreen, California
Energy Code,
Appliance Efficiency
Regulations (Title 20
Standards)
Wet appliances associated with the Project must meet various efficiency requirements. For example:
Pool: Use associated with the Project is subject to appliance efficiency requirements for service water heating systems and equipment and spa and pool heating systems and equipment (Title 24, Part 6, Sections 110.3, 110.4, 110.5; Title 20 Standards, Sections 1605.1(g), 1605.3(g); see also California Energy Code).
Toilets/Faucets/Urinals: Use associated with the Project is subject to new maximum rates for toilets, urinals, and faucets effective January 1, 2016 (Title 20 Standards, Sections 1605.1(h),(i) 1065.3(h),(i)):
◼ Showerheads maximum flow rate 2.5 gallons per minute
(gpm) at 80 pounds per square inch (psi)
◼ Wash fountains 2.2 x (rim space in inches/20) gpm at 60 psi ◼ Metering faucets 0.25 gallons per cycle
◼ Lavatory faucets and aerators 1.2 gpm at 60 psi
◼ Kitchen faucets and aerators 1.8 gpm with optional
temporary flow of 2.2 gpm at 60 psi
◼ Public lavatory faucets 0.5 gpm at 60 psi
EXHIBIT 1
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PROJECT COMPONENT
APPLICABLE
LAWS/REGULATIONS
GREENHOUSE GAS REDUCTION MEASURES REQUIRED FOR PROJECT
◼ Trough-type urinals 16 inches length
◼ Wall mounted urinals 0.125 gallons per flush
◼ Other urinals 0.5 gallons per flush
Water Heaters: Use associated with the Project is subject to appliance efficiency requirements for water heaters (Title 20 Standards, Sections 1605.1(f), 1605.3(f)).
Dishwasher/Clothes Washer: Use associated with the Project is subject to appliance efficiency requirements for dishwashers and clothes washers (Title 20 Standards, Sections 1605.1(o),(p),(q), 1605.3(o),(p),(q)).
Dry Appliances
(Refrigerator/Freezer,
Heater/Air Conditioner,
Clothes Dryer)
Title 20 Standards
CALGreen Code
Dry appliances associated with the Project must meet various efficiency requirements. For example:
Refrigerator/Freezer: Use associated with the Project is subject to appliance efficiency requirements for refrigerators and freezers (Title 20 Standards, Sections 1605.1(a), 1605.3(a)).
Heater/Air Conditioner: Use associated with the Project is subject to appliance efficiency requirements for heaters and air conditioners (Title 20 Standards, Sections 1605.1(b),(c),(d),(e), 1605.3(b),(c),(d),(e) as applicable).
Clothes Dryer: Use associated with the Project is subject to appliance efficiency requirements for clothes dryers (Title 20 Standards, Section 1605.1(q)).
CALGreen Code Installations of heating, ventilation, and air conditioning; refrigeration and fire suppression equipment must comply with CALGreen Sections
5.508.1.1 and 508.1.2, which prohibits CFCs, halons, and certain HCFCs and HFCs.
Lighting Title 20 Standards Lighting associated with the Project are subject to energy efficiency requirements contained in Title 20 Standards.
General Lighting: Indoor and outdoor lighting associated with the Project must comply with applicable appliance efficiency regulations (Title 20 Standards, Sections 1605.1(j),(k),(n), 1605.3(j),(k),(n)).
Emergency Lighting and Self-Contained Lighting: Project must also comply with applicable appliance efficiency regulations (Title 20 Standards, Sections 1605.1(l), 1605.3(l)). Emergency Lighting and SelfContained Lighting: Project must also comply with applicable appliance efficiency regulations (Title 20 Standards, Sections 1605.1(l), 1605.3(l)).
Traffic Signal Lighting: For any necessary Project improvements involving traffic lighting, traffic signal modules and traffic signal lamps will need to comply with applicable appliance efficiency regulations (Title 20 Standards, Sections 1605.1(m), 1605.3(m)).
California Energy Lighting associated with the Project will also be subject to energy efficiency requirements contained in Title 24, Part 6, which contains EXHIBIT 1
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GREENHOUSE GAS REDUCTION MEASURES REQUIRED FOR PROJECT
Code energy standards for non-residential indoor lighting and outdoor lighting (see Title 24 Part 6 Compliance Manual, at Sections 5, 6).
Mandatory lighting controls for indoor lighting include, for example, regulations for automatic shut-off, automatic daytime controls, demand responsive controls, and certificates of installation (Title 24 Part 6 Compliance Manual at Section 5).
Regulations for outdoor lighting include, for example, creation of lighting zones, lighting power requirements, a hardscape lighting power allowance, requirements for outdoor incandescent and luminaire lighting, and lighting control functionality (Title 24 Part 6 Compliance Manual Section 6).
AB 1109 Lighting associated with the Project will be subject to energy efficiency requirements adopted pursuant to AB 1109.
Enacted in 2007, AB 1109 required the CEC to adopt minimum energy efficiency standards for general purpose lighting to reduce electricity consumption 25% for indoor commercial lighting.
Bicycle and Vehicle
Parking
CALGreen Code The Project will be required to provide compliant bicycle parking, fuelefficient vehicle parking, and electric vehicle (EV) charging spaces (CALGreen Code Sections 5.106.4, 5.106.5.1, 5.106.5.3).
California Energy
Code
The Project is subject to parking requirements contained in Title 24, Part 6. For example, parking capacity is to meet but not exceed minimum local zoning requirements, and the Project should employ approved strategies to reduce parking capacity (Title 24, Part 6, Section 106.6).
Landscaping CALGreen Code CALGreen requires and has further voluntary provisions for the following:
◼ A water budget for landscape irrigation use
◼ For new water service, separate meters or submeters must be installed for indoor and outdoor potable water use for landscaped areas of 1,000 to 5,000 square feet
◼ Provide water-efficient landscape design that reduces use of potable water beyond initial requirements for plant installation and establishment
Model Water
Efficient Landscaping
Ordinance
The model ordinance promotes efficient landscaping in new developments and establishes an outdoor water budget for new and renovated landscaped areas that are 500 square feet or larger (CCR, Title 23, Division 2, Chapter 2.7).
Refrigerants CARB Management
of High GWP
Refrigerants for
Stationary Sources
Any refrigerants associated with the Project would be subject to CARB standards. CARB’s Regulation for the Management of High GWP Refrigerants for Stationary Sources reduces emissions of high-GWP refrigerants from leaky stationary, non-residential refrigeration equipment; reduces emissions resulting from the installation and servicing of stationary refrigeration and air conditioning appliances using high-GWP refrigerants; and requires verification GHG emission EXHIBIT 1
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PROJECT COMPONENT
APPLICABLE
LAWS/REGULATIONS
GREENHOUSE GAS REDUCTION MEASURES REQUIRED FOR PROJECT
reductions (CCR, Title 17, Division 3, Chapter 1, Subchapter 10, Article 4, Subarticle 5.1, Section 95380 et seq.).
Consumer Products CARB High GWP
GHGs in Consumer
Products
All consumer products associated with the Project will be subject to CARB standards. CARB’s consumer products regulations set VOC limits for numerous categories of consumer products, and limits the reactivity of the ingredients used in numerous categories of aerosol coating products (CCR, Title 17, Division 3, Chapter 1, Subchapter 8.5).
CONSTRUCTION
Use of Off-Road Diesel
Engines, Vehicles, and
Equipment
CARB In-Use Off-Road
Diesel Vehicle
Regulation
Any relevant vehicle or machine use associated with the Project will be subject to CARB standards.
The CARB In-Use-Off-Road Diesel Vehicle Regulation applies to certain off-road diesel engines, vehicles, or equipment greater than 25 horsepower. The regulation imposes limits on idling, requires a written idling policy, and requires a disclosure when selling vehicles; requires all vehicles to be reported to CARB (using the Diesel Off-Road Online Reporting System) and labeled; restricts the adding of older vehicles into fleets starting on January 1, 2014; and requires fleets to reduce their emissions by retiring, replacing, or repowering older engines, or installing Verified Diesel Emission Control Strategies (i.e., exhaust retrofits).
The requirements and compliance dates of the Off-Road Regulation vary by fleet size, as defined by the regulation.
Greening New
Construction
CALGreen Code All new construction, including the Project, must comply with CALGreen, as discussed in more detail throughout this table. Adoption of the mandatory CALGreen standards for construction has been essential for improving the overall environmental performance of new buildings; it also sets voluntary targets for builders to exceed the mandatory requirements.
Construction Waste CALGreen Code The Project would be subject to CALGreen requirements for construction waste reduction, disposal, and recycling, such as a requirement to recycle and/or salvage for reuse a minimum of 50% of the non-hazardous construction waste in accordance with Section
5.408.1.1, 5.408.1.2, or 5.408.1.3, or meet a local construction and demolition waste management ordinance, whichever is more stringent.
SOLID WASTE
Solid Waste Management Landfill Methane
Control Measure
Waste associated with the Project would be disposed of per state requirements for landfills, material recovery facilities, and transfer stations. Per the statewide GHG emissions inventory, the largest emissions from waste management sectors come from landfills and are in the form of methane (CH4).
In 2010, CARB adopted a regulation that reduces emissions from CH4 in landfills, primarily by requiring owners and operators of certain uncontrolled municipal solid waste landfills to install gas collection and control systems, and requires existing and newly installed gas and control systems to operate in an optimal manner. The regulation allows local air districts to voluntarily enter into a memorandum of understanding with CARB to implement and enforce the regulation EXHIBIT 1
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and to assess fees to cover costs of implementation.
Mandatory
Commercial Recycling
(AB 341)
AB 341 will require the Project, if it generates 4 cubic yards or more of commercial solid waste per week, to arrange for recycling services using one of the following: self-haul, subscribe to a hauler, arrange for pickup of recyclable materials, or subscribe to a recycling service that may include mixed waste processing that yields diversion results comparable to source separation.
The Project will also be subject to local commercial solid waste recycling programs required to be implemented by each jurisdiction under AB 341.
CALGreen Code The Project will be subject to CALGreen requirements to provide areas that serve the entire building and are identified for depositing, storing, and collecting nonhazardous materials for recycling (CALGreen Code Section 5.410.1).
ENERGY USE
Renewable Energy California RPS (SB X1-
2, SB 350, SB 100,
and SB 1020)
Energy providers associated with the Project will be required to comply with the RPS set by SB X1 2, SB 350, and SB 100.
SB X1 2 required investor-owned utilities, publicly owned utilities, and electric service providers to increase purchases of renewable energy such that at least 33% of retail sales are procured from renewable energy resources by December 31, 2020. In the interim, each entity was required to procure an average of 20% of renewable energy for the period of January 1, 2011 through December 31, 2013; and were required to procure an average of 25% by December 31, 2016, and 33% by 2020.
SB 350 requires retail sellers and publicly owned utilities to procure 50% of their electricity from eligible renewable energy resources by 2030.
SB 100 increased the standards set forth in SB 350 establishing that 44% of the total electricity sold to retail customers in California per year by December 31, 2024, 52% by December 31, 2027, and 60% by December 31, 2030, be secured from qualifying renewable energy sources. SB 100 states that it is the policy of the state that eligible renewable energy resources and zero-carbon resources supply 100% of the retail sales of electricity to California by 2045.
SB 1020 built on the standards set forth in SB 100, establishing that 90% of the retail sales of electricity must be carbon free by 2035, 95% must be carbon free by 2040, and, as stated in SB 100, 100% must be carbon free by 2045.
Million Solar Roofs
Program (SB1)
As part of Governor Schwarzenegger’s Million Solar Roofs Program, California set a goal to install 3,000 megawatts of new solar capacity through 2016. The Million Solar Roofs Program is a ratepayer-financed incentive program aimed at transforming the market for rooftop solar systems by driving down costs over time.
California Solar Multifamily properties qualify for rebates of up to $800,000 on solar EXHIBIT 1
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PROJECT COMPONENT
APPLICABLE
LAWS/REGULATIONS
GREENHOUSE GAS REDUCTION MEASURES REQUIRED FOR PROJECT
Initiative-Thermal
Program
water heating systems and eligible solar pool heating systems qualify for rebates of up to $500,000. Funding for the California Solar Initiative –Thermal program comes from ratepayers of Pacific Gas & Electric, SCE, Southern California Gas Company, and San Diego Gas & Electric. The rebate program is overseen by the CPUC as part of the California Solar Initiative.
VEHICULAR/MOBILE SOURCES
General SB 375 and RTP/SCS The Project complies with, and is subject to, the San Joaquin Council of Governments RTP/SCS adopted in 2022, as shown in Table 3.7-7 below.
Fuel Low Carbon Fuel
Standard (LCFS)/ EO
S-01-07
Auto trips associated with the Project will be subject to the Low Carbon Fuel Standard (EO S-01-07), which required a 10% or greater reduction in the average fuel carbon intensity by 2020 with a 2010 baseline for transportation fuels in California regulated by CARB. The program establishes a strong framework to promote the low carbon fuel adoption necessary to achieve the Governor’s 2030 and 2050 GHG goals.
Automotive Refrigerants CARB Regulation for
Small Containers of
Automotive
Refrigerant
Vehicles associated with the Project will be subject to CARB’s Regulation for Small Containers of Automotive Refrigerant (CCR, Title 17, Division 3, Chapter 1, Subchapter 10, Article 4, Subarticle 5, Section 95360 et seq.). The regulation applies to the sale, use, and disposal of small containers of automotive refrigerant with a GWP greater than 150. The regulation achieves emission reductions through implementation of four requirements: use of a self-sealing valve on the container, improved labeling instructions, a deposit and recycling program for small containers, and an education program that emphasizes best practices for vehicle recharging. This regulation went into effect on January 1, 2010, with a 1-year sell-through period for containers manufactured before January 1, 2010. The target recycle rate was initially set at 90%, and rose to 95% beginning January 1, 2012.
Light-Duty Vehicles AB 1493 (or the
Pavley Standard)
Cars that drive to and from the Project will be subject to AB 1493, which directed CARB to adopt a regulation requiring the maximum feasible and cost-effective reduction of GHG emissions from new passenger vehicles. Pursuant to AB 1493, CARB adopted regulations that established a declining fleet average standard for CO2, CH4, N2O, and HFCs (air conditioner refrigerants) in new passenger vehicles and light-duty trucks beginning with the 2009 model year and phased-in through the 2016 model year. These standards were divided into those applicable to lighter and those applicable to heavier portions of the passenger vehicle fleet.
The regulations will reduce “upstream” smog-forming emissions from refining, marketing, and distribution of fuel.
Advanced Clean Car
and ZEV Programs
Cars that drive to and from the Project will be subject to the Advanced Clean Car and ZEV Programs. In January 2012, CARB approved a new emissions-control program for model years 2017 through 2025. The program combines the control of smog, soot, and global warming gases and requirements for greater numbers of zero-emission vehicles (ZEVs) into a single package of standards called Advanced Clean Cars.
By 2025, new automobiles will emit 34% less global warming gases EXHIBIT 1
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and 75% less smog-forming emissions.
The ZEV Program will act as the focused technology of the Advanced Clean Cars Program by requiring manufacturers to produce increasing numbers of ZEVs and plug-in hybrid EVs in the 2018–2025 model years.
The Advanced Clean Cars II (ACC II) regulation builds on the Advanced Clean Cars (ACC) rule adopted in 2012. ACC II decreases emissions by increasing EV sales via two programs. First, the under the ZEV program, original equipment manufacturers (OEMs) must increase sales of ZEV vehicles from 35 percent in 2026 to 100 percent in 2035.
Second, ACC II further strengthened the LEV program discussed above, with more stringent emission standards beginning with model year 2025.
Tire Inflation
Regulation
Cars that drive to and from the Project will be subject to the CARB Tire Inflation Regulation, which took effect on September 1, 2010, and applies to vehicles with a gross vehicle weight rating of 10,000 pounds or less. Under this regulation, automotive service providers must, inter alia, check and inflate each vehicle’s tires to the recommended tire pressure rating, with air or nitrogen, as appropriate, at the time of performing any automotive maintenance or repair service, to keep a copy of the service invoice for a minimum of 3 years, and to make the vehicle service invoice available to the CARB or its authorized representative upon request.
EPA and NHTSA GHG
and CAFÉ standards.
Mobile sources that travel to and from the Project site would be subject to EPA and NHTSA GHG and CAFE standards for passenger cars, light-duty trucks, and medium-duty passenger vehicles (75 FR 25324–25728 and 77 FR 62624–63200).
Medium-and Heavy-Duty
Vehicles
CARB In-Use On-Road
Heavy-Duty Diesel
Vehicles Regulation
(Truck and Bus
Regulation)
Any heavy-duty trucks associated with the Project will be subject to CARB standards. The regulation requires diesel trucks and buses that operate in California to be upgraded to reduce emissions. Newer heavier trucks and buses must meet PM filter requirements. Lighter and older heavier trucks must be replaced starting January 1, 2015. By January 1, 2023, nearly all trucks and buses will need to have 2010 model year engines or equivalent. The regulation applies to nearly all privately and federally owned diesel fueled trucks and buses and to privately and publicly owned school buses with a gross vehicle weight rating greater than 14,000 pounds.
To further reduce emissions, the Advanced Clean Truck Act (ACT) requires original equipment manufacturers of medium- and heavyduty vehicles to sell ZEVs or near-zero-emissions vehicles (NZEVs) such as plug-in electric hybrids as an increasing percentage of their annual sales from 2024 to 2035. The ACT includes a cap-and-trade system, capping the number of fossil fuel vehicles sold by stipulating annual sales percentage requirements. Manufacturers can comply with the ACT by generating compliance credits through the sale of ZEVs or NZEVs or through the trading of compliance credits.
CARB In-Use Off-Road
Diesel Vehicle
Any relevant vehicle or machine use associated with the Project will be subject to CARB standards.
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APPLICABLE
LAWS/REGULATIONS
GREENHOUSE GAS REDUCTION MEASURES REQUIRED FOR PROJECT
Regulation The CARB In-Use-Off-Road Diesel Vehicle Regulation applies to certain off-road diesel engines, vehicles, or equipment greater than 25 horsepower. The regulations impose limits on idling, require a written idling policy, and require a disclosure when selling vehicles; require all vehicles to be reported to CARB (using the Diesel Off-Road Online Reporting System) and labeled; restricted the adding of older vehicles into fleets starting on January 1, 2014; and require fleets to reduce their emissions by retiring, replacing, or repowering older engines, or installing Verified Diesel Emission Control Strategies (i.e., exhaust retrofits).
The requirements and compliance dates of the Off-Road regulation vary by fleet size, as defined by the regulation.
Heavy-Duty Vehicle
GHG Emission
Reduction Regulation
Any relevant vehicle or machine use associated with the Project will be subject to CARB standards. The CARB Heavy-Duty Vehicle GHG Emission Reduction Regulation applies to heavy-duty tractors that pull 53-foot or longer box-type trailers (CCR, Title 17, Division 3, Chapter 1, Subchapter 10, Article 4, Subarticle 1, Section 95300 et seq.). Fuel efficiency is improved through improvements in tractor and trailer aerodynamics and the use of low rolling resistance tires.
EPH and NHTSA GHG
and CAFÉ standards.
Mobile sources that travel to and from the Project site would be subject to EPA and NHTSA GHG and CAFE standards for medium-and heavy-duty vehicles (76 FR 57106–57513).
WATER USE
Water Use Efficiency Emergency State
Water Board
Regulations
Water use associated with the Project will be subject to emergency regulations. On May 18, 2016, partially in response to EO B-27-16, the State Water Board adopted emergency water use regulations (CCR, title 23, Section 864.5 and amended and re-adopted Sections 863, 864, 865, and 866). The regulation directs the State Water Board, Department of Water Resources, and CPUC to implement rates and pricing structures to incentivize water conservation, and calls upon water suppliers, homeowner’s associations, California businesses, landlords and tenants, and wholesale water agencies to take stronger conservation measures.
SB X7-7 Water provided to the Project will be affected by SB X7-7’s requirements for water suppliers. SB X7-7, or the Water Conservation Act of 2009, requires all water suppliers to increase water use efficiency. It also requires, among other things, that the Department of Water Resources, in consultation with other state agencies, develop a single standardized water use reporting form, which would be used by both urban and agricultural water agencies.
CALGreen Code The Project is subject to CALGreen’s water efficiency standards, including a required 20% mandatory reduction in indoor water use (CALGreen Code, Division 4.3).
California RPS Electricity usage associated with Project water and wastewater The Project’s short-term construction-related and long-term operational GHG emissions were estimated using the California Emission Estimator Model (CalEEMod)TM (v.2022.1). CalEEMod is a EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-51 statewide model designed to provide a uniform platform for government agencies, land use planners, and environmental professionals to quantify GHG emissions from land use projects. The model quantifies direct GHG emissions from construction and operation (including vehicle use), as well as indirect GHG emissions, such as GHG emissions from energy use, solid waste disposal, vegetation planting and/or removal, and water use. Emissions are expressed in annual metric tons of CO2 equivalent units of measure (i.e., MT CO2e), based on the global warming potential of the individual pollutants.
SHORT-TERM CONSTRUCTION GHG EMISSIONS
The Project’s short-term construction-related and long-term operational GHG emissions were estimated using the California Emission Estimator Model (CalEEMod)TM (v.2022.1). CalEEMod is a statewide model designed to provide a uniform platform for government agencies, land use planners, and environmental professionals to quantify GHG emissions from land use projects. The model quantifies direct GHG emissions from construction and operation (including vehicle use), as well as indirect GHG emissions, such as GHG emissions from energy use, solid waste disposal, vegetation planting and/or removal, and water use. Emissions are expressed in annual metric tons of CO2 equivalent units of measure (i.e., MT CO2e), based on the global warming potential of the individual pollutants.
Estimated maximum GHG emissions associated with construction of the proposed Project are summarized in Table 3.7-23. These emissions include all worker vehicle, vendor vehicle, hauler vehicle, and off-road construction vehicle GHG emissions. For the purposes of this analysis, based on input from the Project applicant, the proposed Project is assumed to commence construction in 2025 and finish in 2028. See Appendix B for further detail.
TABLE 3.7-23: TOTAL CONSTRUCTION GHG EMISSIONS (MT CO2E/YEAR) YEAR BIO- CO2 NON-BIO- CO2 TOTAL CO2 CH4 N2O CO2E
2025 0 1,074 1,074 0.03 0.06 1,093
2026 0 1,353 1,353 0.03 0.10 1,385
2027 0 1,111 1,111 0.03 0.08 1,137
2028 0 28.0 28.0 <0.01 <0.01 28.2
Total 0 3,566 3,566 0.09 0.24 3,643
SOURCES: CALEEMOD (V.2022.1)
As presented in the table, short-term construction emissions of GHGs are estimated to be a total of approximately 3,643 MT CO2e.
OPERATIONAL GHG EMISSIONS
The operational GHG emissions estimate for the proposed Project includes on-site area, energy, mobile, waste, and water emissions. Estimated GHG emissions associated with operation of the proposed Project are summarized in Table 3.7-34, below. It should be noted that CalEEMod does not account for Governor Newsom’s Zero-Emission by 2035 Executive Order (N-79-20), which requires that all new cars and passenger trucks sold in California be zero-emission vehicles by 2035; CalEEMod also does not account for the new CARB rules related to truck electrification (e.g.
Advanced Clean Trucks Regulation). This is anticipated to substantially reduce the operational emissions associated with vehicles (i.e., mobile emissions) over time. The operational emissions EXHIBIT 1
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3.0-52 Final Environmental Impact Report – LeBaron Ranch results provided in Table 3.7-3 4 are likely an overestimate for mobile emissions, given the state’s ongoing effort to increase electric vehicles and trucks. As shown in the following tables (Table 3.7-3 4 and Table 3.7-45), the annual GHG emissions associated with the proposed Project would be approximately 16,118 MT CO2e under the unmitigated scenario, and 16,103 MT CO2e under the mitigated scenario (i.e. with implementation of the mitigation measures provided in Section 3.3: Air Quality of the Draft EIR).
It should be noted that the mitigated emissions in Table 3.7-5 do not account for Mitigation Measure 3.13-1 (see Section 3.13: Transportation and Circulation), since the exact TDM measures that would be implemented are not known at this time; therefore, mitigated GHG emissions are anticipated to be even lower than those as shown in Table 3.7-5. Moreover, it should also be noted that the emissions results in Table 3.7-5 also do not account for potential additional sustainability measures that may be incorporated into the proposed Project, such as increased energy efficiency standards that may apply by the time the proposed Project is developed, beyond what was modeled (such as more stringent, future Title 24 building envelope energy efficiency standards), as well as solar power that would be required to be included on-site (also under the Title 24 standards) and emissions reductions associated electric vehicle charging infrastructure (as also required under the Title 24 standards). Therefore, the GHG emissions results provided in Table 3.7-5 provide a highly conservative estimate of Project-related mitigated GHG emissions.
TABLE 3.7-34: OPERATIONAL GHG EMISSIONS AT BUILDOUT (METRIC TONS/YEAR) - UNMITIGATED BIO- CO2 NON-BIO- CO2 TOTAL CO2 CH4 N2O CO2E
Area 0 17.5 17.5 <0.01 <0.01 17.5
Energy 0 3,075 3,075 0.35 0.02 3,091
Mobile 0 12,728 12,728 0.58 0.64 12,950
Waste 0 0 0 0 0 0
Water 0 56.7 56.7 0.01 <0.01 57.3
Refrig. 0 0 0 0 3.06 3.06
Total 0 15,877 15,877 0.94 0.66 16,118
SOURCES: CALEEMOD (V.2022.1)
TABLE 3.7-45: OPERATIONAL GHG EMISSIONS AT BUILDOUT (METRIC TONS/YEAR) - MITIGATED BIO- CO2 NON-BIO- CO2 TOTAL CO2 CH4 N2O CO2E
Area 0 0 0 0 0 0
Energy 0 3,076 3,076 0.35 0.02 3,092
Mobile 0 12,728 12,728 0.58 0.64 12,950
Waste 0 0 0 0 0 0
Water 0 56.7 56.7 0.01 <0.01 57.3
Refrig. 0 0 0 0 3.06 3.06
Total 0 15,862 15,862 0.94 0.66 16,103
SOURCES: CALEEMOD (V.2022.1)
Based on the highly conservative estimate of 16,103 MT CO2e at Project buildout, and based on the estimated 4,169 to 4,416 residents that are anticipated to be generated by the proposed Project (as provided in Section 3.10: Land Use, Population, and Housing), per capita GHG emissions associated with the proposed Project would be approximately 3.86 MT CO2e per capita. Although year 2020 EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-53 has come and gone, and a per capita GHG emissions target is no longer relevant for individual CEQA projects,9it should be noted that this value compares favorably with the Stockon CAP’s per capita goals of to 6.8 MT/person in 2020.
CONSISTENCY WITH 2022 SCOPING PLAN
In accordance with AB 32, the CARB developed the first Scoping Plan in 2008 to outline the State’s strategy to achieve 1990 level emissions by year 2020. In May 2014, the CARB released and adopted the First Update to the Climate Change Scoping Plan to identify the next steps in reaching AB 32 goals and evaluate the progress that has been made between 2000 and 2012. A newer version of the Scoping Plan was then adopted by the CARB in December 2017 (entitled California’s 2017 Climate Change Scoping Plan). Lastly, the most recent version of the Scoping Plan was adopted by the CARB in November 2022 (entitled Final 2022 Scoping Plan for Achieving Carbon Neutrality), which was designed consistent with the long-term GHG reduction targets embedded in AB 1279.
Since adoption of the 2008 Scoping Plan and the subsequent updates in 2014, 2017, and 2022, State agencies have adopted programs identified in the plan, and the Legislature has passed additional legislation to achieve the GHG reduction targets. Statewide strategies to reduce GHG emissions include the Low Carbon Fuel Standard, California Appliance Energy Efficiency regulations, California Building Standards (e.g., CALGreen and the 2022 Building and Energy Efficiency Standards), zero carbon electricity by 2045, and changes in the corporate average fuel economy standards (e.g., Pavley I and California Advanced Clean Cars)).
The CARB’s 2022 Scoping Plan (the latest version of the Scoping Plan) provides policies that are considered needed to meet the State’s mid-term and long-term GHG emissions reduction targets.
Specifically, the CARB’s Final 2022 Scoping Plan identifies that it “…lays out the sector-by-sector roadmap for California, the world’s fifth largest economy, to achieve carbon neutrality by 2045 or earlier…”. The Scoping Plan addresses recent legislation and direction from Governor Newsom, by extending and expanding upon the earlier Scoping Plans with a target of reducing anthropogenic emissions to 85 percent below 1990 levels by 2045, and adding carbon neutrality as a science-based guide and touchstone for California’s climate work. The Scoping Plan is therefore consistent with the AB 1279 GHG reduction targets of achieving carbon neutrality by 2045, and reducing anthropogenic emissions to 85 percent below 1990 levels by 2045. The Project’s consistency with the applicable 2022 Scoping Plan policies is discussed in Table 3.7-56, below.
TABLE 3.7-56: PROJECT CONSISTENCY WITH THE 2022 SCOPING PLAN TABLE 1 OF APPENDIX D OF THE SCOPING PLAN
POLICY PROJECT CONSISTENCY
Transportation Electrification
Convert local government fleets to ZEVs and provide
EV charging at public sites
No Conflict. This goal is not applicable to an
individual residential development project.
Create a jurisdiction-specific ZEV ecosystem to support deployment of ZEVs statewide (such as building
standards that exceed state building codes, permit
streamlining, infrastructure siting, consumer
9 Refer to the Golden Door Properties, LLC v. County of San Diego case.
EXHIBIT 1
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3.0 REVISIONS
3.0-54 Final Environmental Impact Report – LeBaron Ranch education, preferential parking policies, and ZEV
readiness plans)
VMT Reduction
Reduce or eliminate minimum parking standards
No Conflict. Although this goal is not applicable to
an individual residential development project, the
Project is implementing neighborhood design
improvements such as pedestrian network
improvements and traffic calming measures.
Furthermore, the proposed Project would enable
walkable development.
Implement Complete Streets policies and investments,
consistent with general plan circulation element
requirements
Increase access to public transit by increasing density of development near transit, improving transit service
by increasing service frequency, creating bus priority
lanes, reducing or eliminating fares, microtransit, etc.
Increase public access to clean mobility options by
planning for and investing in electric shuttles, bike
share, car share, and walking
Implement parking pricing or transportation demand
management pricing strategies
Amend zoning or development codes to enable mixeduse, walkable, transit-oriented, and compact infill development (such as increasing the allowable density
of a neighborhood)
Preserve natural and working lands by implementing
land use policies that guide development toward infill
areas and do not convert “greenfield” land to urban
uses (e.g., green belts, strategic conservation
easements)
Building Decarbonization
Adopt all-electric new construction reach codes for
residential and commercial uses
No Conflict. Although this goal is not applicable to
an individual residential development project, the
Project would be consistent with the applicable
Title 24 Building Envelope Energy Efficiency
Standards, which ensure highly energy efficient
development. Additionally, the proposed Project
would utilize electricity from PG&E, which has been
increasing its overall supply of renewable energy as
part of its overall energy portfolio, consistent with
the State’s Renewable Portfolio Standard. More
detail is provided under Impact 3.7-2, below.
Adopt policies and incentive programs to implement
energy efficiency retrofits for existing buildings, such as weatherization, lighting upgrades, and replacing
energy-intensive appliances and equipment with more
efficient systems (such as Energy Star-rated equipment
and equipment controllers)
Adopt policies and incentive programs to electrify all
appliances and equipment in existing buildings such as
appliance rebates, existing building reach codes, or
time of sale electrification ordinances
Facilitate deployment of renewable energy production
and distribution and energy storage on privately
owned land uses (e.g., permit streamlining,
information sharing)
Deploy renewable energy production and energy
storage directly in new public projects and on existing public facilities (e.g., solar photovoltaic systems on
rooftops of municipal buildings and on canopies in
public parking lots, battery storage systems in
municipal buildings)
TABLE 3 OF APPENDIX D OF THE SCOPING PLAN
POLICY PROJECT CONSISTENCY
EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-55 Transportation Electrification
Provides EV charging infrastructure that, at minimum,
meets the most ambitious voluntary standard in the
California Green Building Standards Code at the time of project approval
No Conflict. The Project would provide electric
conduit to the Project garage area(s), to provide for
the addition of electric charging equipment.
Although the EV charging is not anticipated to meet
the most ambitious voluntary standard in the
California Green Building Standards Code at the
time of project approval, the Project would be
ready for installation of such EV charging stations in
the future.
VMT Reduction
Is located on infill sites that are surrounded by existing urban uses and reuses or redevelops previously
undeveloped or underutilized land that is presently
served by existing utilities and essential public services (e.g., transit, streets, water, sewer)
No Conflict. The Project is surrounded by existing
residential development to the west. Additionally,
the Project redevelops previously undeveloped land
that is presently served by existing utilities and
essential public services.
Does not result in the loss or conversion of natural and working lands
Conflict. Development of the proposed Project
would result in the permanent conversion of 23.12
acres of Prime Farmland, 217.79 acres of Farmland
of Statewide Importance, and 7.51 acres of
Farmland of Local Importance to non-agricultural
use. However, the Project would implement
Mitigation Measure 3.2-1, which requires the
Project applicant to participate in the City’s
Agricultural Lands Mitigation Program, under which
developers of the property are required to
contribute agricultural mitigation land or to pay the
Agricultural Land Mitigation Fee to the City.
Nevertheless, the Project could still lead to a net
loss or conversion of natural and working lands.
Consists of transit-supportive densities (minimum of 20 residential dwelling units per acre), or
Is in proximity to existing transit stops (within a half mile), or
Satisfies more detailed and stringent criteria specified in the region’s SCS
No Conflict. The proposed Project’s High Density
Residential land uses inside the downtown core
and inside the greater downtown would exceed 20
units per acre, consistent with this policy. Refer to
Chapter 2.0: Project Description, for further detail.
Moreover, the proposed Project would not disrupt
an existing transit facility or service, and would not
interfere with the implementation of future transit
service that may be within ½ mile.
Reduces parking requirements by: Eliminating parking
requirements or including maximum allowable parking
ratios (i.e., the ratio of parking spaces to residential units or square feet); or Providing residential parking supply at a ratio of less than one parking space per
dwelling unit; or
For multifamily residential development, requiring
parking costs to be unbundled from costs to rent or
own a residential unit.
Conflict. The proposed Project would not reduce
parking requirements consistent with this policy, or
require parking costs to be unbundled from costs to
rent or own a residential unit, for multifamily
development.
EXHIBIT 1
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3.0-56 Final Environmental Impact Report – LeBaron Ranch At least 20 percent of units included are affordable to lower-income residents
Conflict. Development of the proposed Project is
not anticipated to result in at least 20 percent of
units included to be affordable to lower-income
residents.
Building Decarbonization
Uses all-electric appliances without any natural gas
connections and does not use propane or other fossil
fuels for space heating, water heating, or indoor
cooking
No Conflict. The Project is all-electric. That is,
natural gas would not be used for appliances, nor
does the Project use propane or other fossil fuels
for space heating, water heating, or indoor
cooking.1
SOURCE: 2022 SCOPING PLAN, TABLE 1 AND TABLE 3, APPENDIX D NOTE: CORRESPONDENCE WITH TREVOR SMITH, LAZARES COMPANIES ON MAY 20, 2025.
It should be noted that, in reference to Table 3 of Appendix D of the Scoping Plan, as stated on page 23 and 24 of Appendix D of the Scoping Plan:
“Lead agencies may determine, with adequate additional supporting evidence that projects that incorporate some, but not all, of the key project attributes [within Table 3 of Appendix D] are consistent with the State’s climate goals.” The proposed Project implements several of the key project attributes that are consistent with the State’s climate goals, specifically relating to transportation electrification and building decarbonization (refer to the policy analysis for Table 3 of Appendix D of the Scoping Plan, in Table 3.7-6, above). Therefore, based on this, as well as additional evidence provided throughout this analysis, the proposed Project is considered consistent with the State’s climate goals, Moreover, it should be noted that the Project includes Mitigation Measure 3.13-1, which implementation of feasible Transportation Demand Management (TDM) strategies, which would decrease the VMT generated by the Project (refer to Section 3.13: Transportation and Circulation, of this EIR, for further detail).
The proposed Project’s operational emissions would be reduced as regulations are implemented by the CARB and other State agencies to comply with the statewide GHG reduction targets. Many of these regulations are already identified in the 2022 Scoping Plan. These statewide actions are anticipated to reduce operational GHG emissions even further below those identified in Table
3.7-23, Table 3.7-34, and Table 3.7-45. For example, the proposed Project’s transportation emissions would be expected to decline as vehicle efficiency standards are implemented beyond the Advanced Clean Cars II program and the Low Carbon Fuel Standard is strengthened.
Furthermore, CalEEMod does not account for Governor Newsom’s Zero-Emission by 2035 Executive Order (N-79-20) or CARB’s subsequent regulations, which requires that all new cars and passenger trucks sold in California be zero-emission vehicles by 2035. This is anticipated to substantially reduce the operational emissions associated with passenger vehicles (i.e. mobile emissions) further, over time.
The proposed Project would also benefit from the electrification of the vehicle fleet that would occur by the assumed Project buildout year and over the life of the Project. Based on estimates provided by the CEC, 5 million zero-emission electric vehicles will be needed by 2030 to meet the State’s goal of reducing GHG emissions by 40% below 1990 levels, and 8 million zero emission vehicles are anticipated to be needed by 2030 to meet the requirements embedded in Executive EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-57 Order N-79-20.10 Therefore, it can be reasonably projected that a substantial reduction in GHGs associated with the electrification of the vehicle fleet by Project operational year would occur, beyond what has been modeled within this EIR.
Separately, Tthe proposed Project would be required to comply with the latest (i.e. 2022) version of the Title 24 standards, which are more stringent than the 2019 Title 24 standards that are modeled in CalEEMod.11 Therefore, proposed Project emissions would continue to decline beyond the buildout year due to regulations that would indirectly affect Project emissions. Moreover, the Title 24 standards are anticipated to be revised again in the latter half of year 2025, with even stricter energy efficiency and renewable energy requirements for new development, which help to ensure that new development is consistent with the State’s GHG reduction goals, consistent with the Scoping Plan.12 These improvements to the Title 24 standards will be reflected in per capita GHG emission reductions at the Project buildout.
Overall, the proposed Project would not conflict with the 2022 Scoping Plan. The proposed Project would be developed according to the latest State and federal regulatory requirements, including those associated with operational building energy efficiency. Therefore, the Project would be considered consistent with the 2022 Scoping Plan. Based on this, recognizing the CARB as an authoritative substantial evidence source in evaluating post-2020 GHG impacts, since the proposed Project would be consistent with the CARB’s 2022 Scoping Plan, buildout of the proposed Project would not interfere with the main programs the CARB has identified to support its conclusions that the State is on a trajectory to meet the 2045 GHG target. Overall, the proposed Project would not impede the 2022 Scoping Plan and would help the State to progress towards this target.
CONSISTENCY WITH SJCOG’S 2022 RTP/SCS
The SJCOG’s 2022 RTP/SCS includes eight policies with corresponding implementation strategies for conserving energy, maximizing mobility and accessibility, increasing safety and security, preserving the transportation system, supporting economic development, promoting interagency cooperation and public participation, maximizing cost effectiveness, and improving quality of life for residents.
These strategies include similar measures to the 2022 Scoping Plan, such as supporting energy and water efficiency. The Project’s consistency with the applicable 2022 RTP/SCS strategies is discussed in Table 3.7-67, below.
10 See Assembly Bill 2127 Electric Vehicle Charging Infrastructure Assessment: Analyzing Charging Needs to Support Zero-Emission Vehicles in 2030. Available at:
https://www.energy.ca.gov/publications/2020/assembly-bill-2127-electric-vehicle-charging-infrastructureassessment-analyzing 11 Since the latest version of CalEEMod (v.2022.1) only accounts for the energy efficiency requirements associated with the 2019 version of Title 24, and since there is no well-established methodology for quantifying the reductions in energy consumption associated with the 2022 version of Title 24 over the 2019 version of Title 24, the CalEEMod modeling does not account for the energy efficiency improvements that would be associated with the 2022 (or future, more stringent) versions of Title 24. 12 See: https://www.energy.ca.gov/programs-and-topics/programs/building-energy-efficiencystandards/2025-building-energy-efficiency EXHIBIT 1
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3.0-58 Final Environmental Impact Report – LeBaron Ranch TABLE 3.7-67: PROJECT CONSISTENCY WITH THE SJCOG’S 2022 RTP/SCS
POLICY PROJECT CONSISTENCY
Enhance the Environment
for Existing and Future
Generations and Conserve
Energy
No Conflict. The Project would utilize electricity provided by Pacific Gas & Electric (PG&E) which is required to meet the future year renewable portfolio performance standards. In addition, future development associated with Project implementation would be required to meet the applicable requirements of the 2022 (or more current) Title 24 Building Energy Efficiency Standards.
Maximize Mobility and
Accessibility
No Conflict. The Project would support EV-ready charging spaces, consistent with the requirements of the latest version of the Title 24 Building Energy Efficiency Standards. In addition, although this Project is not a transportation improvement project, the Project is located in a city where regional transit improvements are planned. Moreover, the proposed Project would include many project features that improve mobility and accessibility, including providing pedestrian network improvements.
Increase Safety and
Security
No Conflict. The Project would be developed using the latest State and local requirements relating to safety and security. Development of the Project site would include other uses to support and complement the proposed residential development include public utility infrastructure, public and private roadways, curb/gutters/sidewalks, other pedestrian facilities, private parking, street lighting, and street signage, which would enhance the safety and security of the site and it surroundings, by connecting to existing development.
Preserve the Efficiency of
the Existing Transportation
System
Not applicable. This is not a transportation improvement project and is therefore not applicable. The Project would not interfere with the efficiency of any existing transportation system.
Support Economic Vitality No Conflict. The proposed Project would create local jobs, including construction jobs during the construction phase as well as home-based businesses during the Project’s operational phase, as well as provide new consumers for local businesses, thereby supporting economic vitality.
Promote Interagency
Coordination and Public
Participation for
Transportation DecisionMaking and Planning
Efforts
Not applicable. This is not a transportation planning or improvement project and is therefore not applicable.
Maximize the Cost
Effectiveness
No Conflict. The proposed Project would be developed based on market demand.
Improve the Quality of Life
for Residents
No Conflict. The proposed Project would provide additional residences, thereby improving the quality of life for the local community.
SOURCE: SJCOG 2022 RTP/SCS
As shown in Table 3.7-67, above, the Project would not conflict with any of the GHG emissions reduction strategies contained in the SJCOG’s 2022 RTP/SCS. Therefore, the Project would be considered to be consistent with SJCOG’s 2022 RTP/SCS.
CONSISTENCY WITH THE SJVAPCD REQUIREMENTS
The proposed Project would be required to comply with all applicable SJVAPCD (i.e., Air District) Rules and regulations. For example, Regulations and rules that may apply to the proposed Project could include Regulation VIII provides fugitive PM10 dust prohibitions; Rule 8021 provides rules for PM10 dust prohibition associated with construction, demolition activities, excavation, extraction, and other earthmoving activities; Rule 4601 provides rules to limit VOC emissions for architectural coatings. Moreover, the proposed Project would be required to comply with SJVAPCD Rule 9510, as described in further detail below. In sum, the proposed Project would comply with all applicable EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-59 SJVAPCD Rules and regulations and as to such rules and regulations, impacts are less than significant.
SJVAPCD’S RULE 9510
In accordance with the SJVAPCD’s Rule 9510, an Air Impact Assessment (AIA) is required to be prepared for the proposed Project based on the applicability and exemption criteria of the rule.13 The rule includes general mitigation requirements for construction and/or operational emissions.
Per the general mitigation requirements of Rule 9510, the Project would be required to reduce the Project’s operational baseline NOx emissions 33.3%, and the Project’s operational baseline PM10 emissions 50%, over a period of ten years as quantified in the approved AIA. Although the purpose of Rule 9510 is to reduce NOx and PM10 emissions, rather than GHG emissions, it should be noted that these reductions are enforced through on- and off-site measures, many of which would also reduce GHG emissions.
These off-site emission reductions have the ancillary benefit of reducing GHG emissions, beyond what has been modeled herein. For example, for off-site mitigation that would occur due to the replacement of older, higher-emitting agricultural tractors with new latest-tier tractors, the greenhouse gas intensity of the new latest-tier tractors compared to older, higher-emitting tractors by approximately 33-80%, according to the U.S EPA, by increasing the fuel economy of tractor trailers from approximately 5-6 mpg to 8-9 mpg in 2027.14 Although such reductions in GHGs will be attributed to the proposed Project through the Rule 9510 ISR, these reductions are not reflected in the Project GHG modeling estimates included herein, except that the modeling estimates do reflect that fact that the Project does not include any open-hearth fireplaces. It is notable, however, that the GHG reductions are projected to be substantial and are in alignment with the goals of the 2022 Scoping Plan.
EXECUTIVE ORDER S-3-05
The Executive Order S-3-05 2050 target has not been codified by legislation. However, studies have shown that, in order to meet the 2050 target, aggressive pursuit of technologies in the transportation and energy sectors, including electrification and the decarbonization of fuel, will be required. Because of the technological shifts required and the unknown parameters of the regulatory framework in 2050, quantitatively analyzing the project’s impacts further relative to the 2050 goal is speculative for purposes of CEQA.15
The CARB recognizes that AB 32 establishes an emissions reduction trajectory that will allow California to achieve the more stringent 2050 target: “These [greenhouse gas emission reduction] 13 Available at: https://www.valleyair.org/rules/currntrules/r9510-a.pdf. Accessed: March 2025. 14 See page 677 of the Greenhouse Gas Emissions and Fuel Efficiency Standards for Medium- and Heavy-Duty Engines and Vehicles – Phase 2 (Response to Comments for Joint Rulemaking) for detail:
https://www.nhtsa.gov/sites/nhtsa.gov/files/phase2-hd-fuel-efficiency-ghg-response-to-comments.pdf 15 California Air Resources Board (CARB). 2014. First Update to the Climate Change Scoping Plan. Website:
http://www.arb.ca.gov/cc/scopingplan/document/updatedscopingplan2013.htm. Accessed March 2023September 11, 2023.
EXHIBIT 1
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3.0-60 Final Environmental Impact Report – LeBaron Ranch measures also put the State on a path to meet the long-term 2050 goal of reducing California’s GHG emissions to 80 percent below 1990 levels. This trajectory is consistent with the reductions that are needed globally to stabilize the climate.” In addition, the CARB’s First Update to the Scoping Plan “lays the foundation for establishing a broad framework for continued emission reductions beyond 2020, on the path to 80 percent below 1990 levels by 2050,” and many of the emission reduction strategies recommended by the CARB would serve to reduce the proposed project’s post-2020 emissions level to the extent applicable by law:
• Energy Sector: Continued improvements in California’s appliance and building energy efficiency programs and initiatives, such as the State’s zero net energy building goals, would serve to reduce the proposed project’s emissions level. Additionally, further additions to California’s renewable resource portfolio would favorably influence the project’s emissions level.
• Transportation Sector: Anticipated deployment of improved vehicle efficiency, zeroemission technologies, lower carbon fuels, and improvement of existing transportation systems all will serve to reduce the project’s emissions level. • Water Sector: The project’s emissions level will be reduced as a result of further utilization of water conservation technologies.
• Waste Management Sector: Plans to further improve recycling, reuse and reduction of solid waste will beneficially reduce the project’s emissions level.
In his January 2015 inaugural address, Governor Brown expressed a commitment to achieve “three ambitious goals” that he wanted to see accomplished by 2030 to reduce the State’s GHG emissions:
• Increasing the State’s Renewable Portfolio Standard from 33 percent in 2020 to 50 percent in 2030;
• Cutting the petroleum use in cars and trucks in half; and • Doubling the efficiency of existing buildings and making heating fuels cleaner.
These expressions of executive branch policy may be manifested in adopted legislative or regulatory action through the State agencies and departments responsible for achieving the State’s environmental policy objectives, particularly those relating to global climate change.16 Further, studies show that the State’s existing and proposed regulatory framework will allow the State to reduce its GHG emissions level to 40 percent below 1990 levels by 2030, and to 80 percent below 1990 levels by 2050. Even though these studies did not provide an exact regulatory and technological roadmap to achieve the 2030 and 2050 goals, they demonstrated that various combinations of policies could allow the Statewide emissions level to remain very low through 2050, suggesting that the combination of new technologies and other regulations not analyzed in the studies could allow the State to meet the 2050 target.17 16 Brown, Edmund G. Jr. 2015. Press Release: California Establishes Most Ambitious Greenhouse Gas Goal in North America. April 29.
Website: https://www.gov.ca.gov/news.php?id=18938. Accessed February 2, 2021. 17 Energy and Environmental Economics, 2015. Pathways to Deep Carbonization in the United States.
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Final Environmental Impact Report – LeBaron Ranch 3.0-61 Given the proportional contribution of mobile source-related GHG emissions to the State’s inventory, recent studies also show that relatively new trends—such as the increasing importance of web-based shopping, the emergence of different driving patterns, and the increasing effect of web-based applications on transportation choices—are beginning to substantially influence transportation choices and the energy used by transportation modes. These factors have changed the direction of transportation trends in recent years and will require the creation of new models to effectively analyze future transportation patterns and the corresponding effect on GHG emissions.
For the reasons described above, the proposed project’s post-2020 emissions trajectory is expected to follow a declining trend, consistent with the 2030 and 2050 targets.
CONSISTENCY WITH THE CITY OF STOCKTON CLIMATE ACTION PLAN18 The proposed Project would be consistent with the relevant GHG reduction measures associated with the City of Stockton Climate Action Plan (CAP), published in 2014. Table 3.3-78, below, provides an analysis of the consistency of the proposed Project with the GHG reduction measures contained within the CAP. As shown, the proposed Project would be consistent with all applicable GHG reduction measures that would be applicable to the proposed Project.19 TABLE 3.7-78: PROJECT CONSISTENCY WITH THE CITY OF STOCKTON CLIMATE ACTION PLAN
GHG REDUCTION MEASURE PROJECT CONSISTENCY
DRP-1: Development
Review Process – 29%
Reduction for Discretionary
Project
Not Applicable. The Project does not need to demonstrate a 29% reduction in GHG emissions, per this measure, since this efficiency target no longer applies. Specifically, this target was included in the CAP originally, since it was part of the normal review process for projects, at the time. Refer to the description of this measure’s applicability on page 3-11 of the CAP. However, the SJVAPCD no longer recommends this approach to analyzing GHGs (i.e compared to an efficiency target). Refer to the Newhall Ranch and Golden Door cases.20,21
content/uploads/2015/11/US_Deep_Decarbonization_Technical_Report_Exec_Summary.pdf. Accessed June 8, 2022.
18 This analysis of consistency with the Stockton CAP is provided for informational purposes only. 19 It should be noted that, subsequent to adoption of the CAP, the Golden Door Properties, LLC v. County of San Diego case held that the use of a quantitative threshold (like the year 2020 efficiency threshold included within the Stockton Climate Action Plan), which has historically been used for EIRs throughout California, must be adopted by the City via a resolution, ordinance or regulation based on a public review process, and supported by substantial evidence. However, a quantitative threshold beyond year 2020 has never been specifically adopted as a threshold by the City via a resolution, ordinance, or regulation. Therefore, overall, the usage of a per capita efficiency metric, such as the one included within the City of Stockton Climate Action Plan, is also not relevant or appropriate in a CEQA context. 20 The Supreme Court’s decision in Center for Biological Diversity v. California Dept. of Fish & Wildlife (2015) 62 Cal.4th 204 (“Newhall Ranch”) determined that comparative analysis of GHG emissions could be applicable based on local or regional data of the project location. However, the court did not specify in detail what kind of comparative (quantitative) analysis would be considered adequate. An alternative way to satisfy the greenhouse gas requirements is to rely on a locally qualified CAP if it is adequately supported.
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Energy-1: Green Building
Ordinance
No Conflict. The Project would exceed the 2008 Title 24 of the California Code of Regulations Standards, since the most recent version of the Title 24 Standards is much more stringent. Simply meeting the current Title 24 Standards would result in significant energy and GHG savings for the City because the state has regularly updated the Title 24 requirements since 2005 and plans to continue to update the Title 24 standards periodically in the future. Therefore, the proposed Project would not conflict with this GHG reduction measure.
Energy-2: Outdoor Lighting
Upgrades for Existing
Development
Not applicable. The proposed Project is a new development; therefore, GHG reduction measures associated with existing development would not apply.
Energy-3: Energy Efficiency
Incentives and Programs to
Promote Retrofits for Existing
Residential Buildings
Not applicable. The proposed Project is a new development; therefore, GHG reduction measures associated with existing development would not apply.
Energy-4: Energy Efficiency
Programs to Promote Retrofits
for Existing Non‐ Residential
Buildings
Not applicable. The proposed Project is a new development; therefore, GHG reduction measures associated with existing development would not apply. Moreover, the proposed Project does not include non-residential development.
Energy‐5: Solar‐Powered
Parking
No Conflict. The Project would be consistent with the current Title 24 Standards associated with solar PV, as applicable. Therefore, the proposed Project would not conflict with this GHG reduction measure.
Energy-6: Residential and
Non-residential Rooftop Solar
No Conflict. The Project would be consistent with the current Title 24 Standards associated with solar PV, which would require that approximately 30% of residential electricity requirements are met by rooftop solar. Specifically, based on the 2022 version of the Title 24 standards, although the exact percentage of electricity generated by the PV system can vary based on factors such as the climate zone, conditioned floor area, and possible plug loads of the building, the goal is to offset the electrical consumption of the proposed building, assuming a natural gas furnace, water heater, stove, and clothes dryer. Therefore, the proposed Project would not conflict with this GHG reduction measure.
Trans-1: Land
Use/Transportation System
Design Integration
No Conflict. The Project would increase density in the City of Stockton, thereby facilitating additional land use and existing transportation integration. That is, the development of the Project would increase use of existing roadways that have been designed to accommodate additional traffic, such as that as would be generated by the proposed Project.
Overall, the Project land uses have been previously planned for and integrate appropriately with the existing transportation system Therefore, the proposed Project would not conflict with this GHG reduction measure.
Trans-2: Parking Policies Not applicable. This GHG reduction measure would apply to the downtown area, which the Project is not in. Therefore, this GHG reduction measure would not apply to the proposed Project.
Trans-3: Transit System
Support
No Conflict. The Project would not hinder the development of the City’s transit system. Furthermore, the increased residential density of the area that would occur with development of the proposed Project would 21 More recently, in the Golden Door Properties, LLF v. County of San Diego (“Golden Door”) case, the court indicated that, in order for a use of a quantitative threshold for GHGs to be applicable, the quantitative threshold must to be adopted by the City via resolution, ordinance, or regulation, needs to undergo include a public review process, and must to be supported by substantial evidence. The City of Stockton has not adopted a quantitative threshold for GHGs beyond the year 2020 that satisfy these requirements, for future years. Therefore, the use of a quantitative threshold to analyze GHGs is not appropriate for the Project.
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incentivize further development of local transit options, beyond which would be anticipated to occur without development of the proposed Project, simply due to the increased residential development in an area that is currently not developed. Further, Mitigation Measure 3.13-1 requires coordination with public transit agencies regarding transit service connecting workers with existing and future residential developments, and also requires coordination with SJRTD regarding the potential for increasing service on Hopper Route 93. As such, this measure aims to increase access to public transit. Therefore, the proposed Project would not conflict with this GHG reduction measure.
Trans-4: Efficient Goods
Movement
Not applicable. This GHG reduction measure would apply to the City’s rail lines. Therefore, this GHG reduction measure would not apply to the proposed Project.
Trans-5: Reduce Barriers for
Non‐Motorized Travel
No Conflict. The Project would connect the City’s existing transportation system, via pedestrian walkways (including sidewalks) and bicycle facilities, and connect with the existing system. Therefore, the proposed Project would not conflict with this GHG reduction measure.
Trans‐6: Transit System
Improvements
No Conflict. This GHG reduction measure would apply to the City’s transit system. Nevertheless, the proposed Project would be accessible via the City’s existing transit system. Existing bus stops are located south of the Project site, at West Lane and Morado Lane, as well as Royal Oaks Drive and Lower Sacramento Road. Furthermore, Additional bus stops may be added closer to the Project site in the future. Therefore, the proposed Project would not conflict with this GHG reduction measure.
Trans‐7: Safe Routes to School No Conflict. The Project would connect the City’s existing transportation system, via pedestrian walkways (including sidewalks). Therefore, the proposed Project would not conflict with this GHG reduction measure.
Trans‐8: Transportation
Demand Management and
Additional Safe Routes to
School
No Conflict. The Project would connect the City’s existing Safe Routes to School. Moreover, the Project would reduce VMTs through implementation of Mitigation Measure 3.13-1, which requires the Project applicant to work with the City of Stockton to implement feasible Transportation Demand Management (TDM) strategies, which would decrease the VMT generated by the Project. See Mitigation Measure 3.13- 1, for further detail. Therefore, the proposed Project would not conflict with this GHG reduction measure.
Waste‐1: Increased Waste
Diversion
No Conflict. The Project would be consistent with the State’s 75% waste diversion goal as required by AB 341. It should be noted that AB 341 has been superseded by California’s SB 1383, which sets a more stringent goal of diverting 75% of the waste stream from landfills by 2025 and includes enforcement mechanisms, such as monetary fines, for non-compliance.
The Project would be required to comply with SB 1383, and since AB 341 has come and gone, the Project would not conflict with requirements associated with AB 341., as the local waste haulers are required by State law to implement this measure. Therefore, the proposed Project would not conflict with this GHG reduction measure.
Water‐1: Comply with Senate
Bill X7‐7
No Conflict. The Project would be consistent with the State’s statewide goal of a 20% reduction in urban per capita use, as required by Senate Bill X7-7. Senate Bill X7-7 is a California state law that requires the state to reduce urban water consumption by 20% by the year 2020. Since the year 2020 has come and gone, the Project would not conflict with this law.
Therefore, the proposed Project would not conflict with this GHG reduction measure.
Water‐2: Promotion of
Water‐Efficiency for Existing
Development
Not applicable. This GHG reduction measure would apply only to existing development. The proposed Project does not contain any existing development; rather, it includes new development. Therefore, this GHG reduction measure would not apply to the proposed Project.
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Wastewater‐1: Energy
Efficiency Improvements at
the Regional Wastewater
Treatment Plant
No Conflict. The Project would not conflict with the City’s goal of reducing energy usage as the Regional Wastewater Treatment Plant. The Project is not anticipated to be a large generate of wastewater demand, since it is a commercial and industrial project. Additionally, the Project would not hinder energy efficiency improvements or other upgrades at the Regional Wastewater Treatment Plant. Therefore, the proposed Project would not conflict with this GHG reduction measure.
Urban Forestry‐1: Urban Tree
Planting Programs
No Conflict. The Project would include landscaping trees that would not conflict with this GHG reduction measure.
High GWP GHG‐1: Residential
Responsible Appliance
Disposal Programs
No Conflict. The Project is a new development that would install new energy-efficient refrigerators and freezers. Therefore, the proposed Project would not conflict with the goal of replacing existing inefficient sources of high global warming potential (GWP) appliances. Therefore, the proposed Project would not conflict with this GHG reduction measure.
Off‐Road‐1: Electric‐Powered
Construction Equipment
No Conflict. The Project would not conflict with the City’s goal of increasing the percentage of construction equipment that is electric powered.
Therefore, the proposed Project would not conflict with this GHG reduction measure.
Off‐Road‐2: Reduced Idling
Times for Construction
Equipment
No Conflict. The Project would be consistent with the CARB’s Airborne Toxic Control Measure to Limit Diesel‐Fueled Commercial Motor Vehicle Idling currently limits diesel‐fueled commercial motor vehicle idling time to 5 minutes. Therefore, the proposed Project would not conflict with this GHG reduction measure.
Off‐Road‐3: Electric
Landscaping Equipment
No Conflict. The Project would not conflict with the City’s goal of 15% of the City’s landscaping equipment to be electric or battery powered.
Therefore, the proposed Project would not conflict with this GHG reduction measure.
SOURCE: CITY OF STOCKTON CLIMATE ACTION PLAN, 2014
CONCLUSION
The proposed Project would be consistent with relevant plans, policies, and regulations associated with GHGs, notably the most recent version of the CARB’s Scoping Plan, and the SJCOG’s 2022 RTP/SCS, and the City of Stockton Climate Action Plan. This would ensure that the proposed Project would be consistent with, and would not impair, the State’s carbon neutrality standard by year 2045 as established under AB 1279. The State is making progress toward reducing GHG emissions in key sectors such as transportation, industry, and electricity. Since the Project would be consistent with State GHG Plans, it would not impede the State’s goals of reducing GHG emissions 40 percent below 1990 levels by 2030, and of achieving carbon neutrality by 2045. The proposed Project would make a reasonable fair share contribution to the State’s GHG reduction goals, by implementing a wide array of Project features that would substantially reduce GHG emissions and therefore, the proposed Project’s GHG emissions would be considered to have a less than significant impact.
The following changes were made to pages 3.7-35 through 3.7-39 of Section 3.7 of the Draft EIR:
ELECTRICITY AND NATURAL GAS
Operation. Electricity and natural gas used by the proposed Project during operation would be used primarily to generate energy for Project buildings, as well as for outdoor parking lot lighting. As shown in further detail in the CalEEMod modeling outputs provided in Appendix B, “Energy” is one of the categories that was modeled for GHG emissions. As also shown in the CalEEMod modeling outputs as provided in Appendix B, the proposed Project is anticipated to consume approximately EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-65 11,238,093 kWh of electricity per year and approximately 9,693,520 kBTU per of natural gas per year. Moreover, this is likely a conservative estimate, given that the CalEEMod model does not account for the latest version of Title 24. Furthermore, this also does not account for the vast majority of the Project’s energy efficiency commitments, which would likely drive down the energy usage much further than identified herein.
The proposed Project’s buildings would be designed and constructed in accordance with the City’s latest adopted energy efficiency standards, which are based on the State’s Title 24 Energy Efficiency Standards for Residential Buildings and Green Building Code Standards. These standards include minimum energy efficiency requirements related to building envelope, mechanical systems (e.g., heating, ventilation, and air conditioning [HVAC] and water heating systems), and indoor and outdoor lighting, are widely regarded as the some of the most advanced and stringent building energy efficiency standards in the country. In addition, the on-site solar PV system would meet the State legal requirements. As such, the design of the proposed project would facilitate the future commitment to renewable energy resources. Therefore, building energy consumption would not be considered wasteful, inefficient, or unnecessary.
Additionally, the proposed Project is anticipated to implement renewable energy features. In particular, the proposed Project would be required to implement on-site solar, consistent with the most recent (2022) Title 24 standards. The 2022 Title 24 standards require single-family homes and low-rise multi-family projects to install solar photovoltaic (PV) systems and be “battery-ready”, by installing either a subpanel or a split-bus main panel with four backed-up circuits.22 This is a requirement as part of the 2022 Title 24 standards. However, it should be noted that additional onsite solar PV could be installed, especially in the case that stricter Title 24 standards come into effect prior to portions of Project development.
Separately, Tthe 2022 Title 24 standard requires that the number of electric vehicle (EV) charging spaces depends on the building type and total number of parking spaces on-site. Similarly, such requirements would be anticipated to further reduce energy consumption beyond what is modeled herein.
Construction. Temporary electric power for as-necessary lighting and electronic equipment, such as computers inside temporary construction trailers, and water for dust control would be provided by PG&E. The electricity used for such activities would be temporary, would be substantially less than that required for Project operation, and would therefore have a negligible contribution to the Project’s overall energy consumption. Natural gas is not anticipated to be required during construction of the Project.
Fuels used for construction would primarily consist of diesel and gasoline, which are discussed below under the “on-road and off-road vehicles” subsections. Any minor amounts of natural gas that may be consumed as a result of Project construction would be substantially less than that required for Project operation and would have a negligible contribution to the Project’s overall energy consumption.
ON-ROAD VEHICLES (OPERATION)
The proposed Project would generate vehicle trips (i.e., passenger vehicles for employees and heavy-duty trucks for hauling) during its operational phase. Compliance with applicable State laws and regulations would limit idling and a part of a comprehensive regulatory framework that is 22 See: https://calsolarinc.com/news/title-24-california/ EXHIBIT 1
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3.0-66 Final Environmental Impact Report – LeBaron Ranch implemented by the CARB. A description of Project operational on-road mobile energy usage is provided below.
According to the Traffic Study prepared for the proposed Project (WK Shijo Consulting, 2023), and as described in more detail in Section 3.13 of this EIR, the proposed Project would increase total vehicle trips by approximately 12,784 new daily trips. In order to calculate operational on-road vehicle energy usage, De Novo Planning Group used fleet mix data from the CalEEMod (v.2022.1) output for the proposed Project, and Year 2025 gasoline and diesel MPG (miles per gallon) factors for individual vehicle classes as provided by EMFAC2021, to derive weighted average gasoline and diesel MPG factors for the vehicle fleet as a whole. Based on these calculations, as provided in Appendix B, upon full buildout, the proposed Project would generate operational vehicle trips that would use a total of approximately 2,334 gallons of gasoline and 5,395 gallons of diesel per day, or 851,728 gallons of gasoline and 1,969,247 gallons of diesel per year. Additionally, the Project would generate operational vehicle trips that require electricity for electric vehicles, which is dependent on the number of electric vehicles within the vehicle fleet at the time of Project operation.
Over the lifetime of the Project, the fuel efficiency of the vehicles being used by the Project is expected to increase. As such, the amount of petroleum consumed as a result of vehicular trips to and from the Project site during operation would decrease over time. Numerous regulations are in place that require and encourage increased fuel efficiency. For example, CARB has adopted a new approach to passenger vehicles by combining the control of smog-causing pollutants and GHG emissions into a single coordinated package of standards. The new approach also includes efforts to support and accelerate the numbers of plug-in hybrids and ZEVs in California. The Project would be required to comply with CARB’s Airborne Toxics Control Measure, which restricts heavy-duty diesel vehicle idling time to 5 minutes, which would minimize fuel consumption. Operation of the Project is expected to use decreasing amounts of petroleum over time due to advances in fuel economy.
The Project would provide a bike-friendly, pedestrian-friendly development and facilitate ridesharing and carpooling to reduce VMT. The Project also would encourage EVs by providing EV chargers, in compliance with CalGreen standards.
In summary, although Project implementation would result in an increase in petroleum use during construction and operation, over time vehicles would use less petroleum due to advances in fuel economy. Additionally, the Project would include features that would encourage electric and zeroemissions technology, and reduced VMT through sidewalks. Given these considerations, petroleum consumption associated with the Project would not be considered inefficient or wasteful, and impacts would be less than significant.
ON-ROAD VEHICLES (CONSTRUCTION)
The proposed Project would also generate on-road vehicle trips during Project construction (from construction workers and vendors travelling to and from the Project site). De Novo Planning Group estimated the vehicle fuel consumed during these trips based on the assumed construction schedule, vehicle trip lengths and number of workers per construction phase as provided by CalEEMod, and Year 2023 gasoline and diesel MPG factors provided by EMFAC2021 (year 2023 factors were used to represent a conservative analysis, as the energy efficiency of construction activities is anticipated to improve over time). For the sake of simplicity and to be conservative, it was assumed that all construction worker light duty passenger cars and truck trips use gasoline as a fuel source, and all medium and heavy-duty vendor trucks use diesel fuel. Table 3.7-89, below, EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-67 describes gasoline and diesel fuel consumed during each construction phase (in aggregate). As shown, the vast majority of on-road mobile vehicle fuel used during the construction of the proposed Project would occur during the building construction phase. See Appendix B of this EIR for a detailed accounting of construction on-road vehicle fuel usage estimates.
TABLE 3.7-89: ON-ROAD MOBILE FUEL USAGE BY PROJECT CONSTRUCTION ACTIVITIES – BY PHASE
CONSTRUCTION PHASE TOTAL GALLONS OF GASOLINE FUEL(B) TOTAL GALLONS OF DIESEL FUEL(B) Site Preparation 495 0
Grading 550 0
Building Construction 7,944 4,805
Paving 687 0
Architectural Coatings 5,314 0
Total 14,990 4,805
NOTE:
(A) PROVIDED BY CALEEMOD OUTPUT.(B)SEE APPENDIX B OF THIS EIR FOR FURTHER DETAIL SOURCE: CALEEMOD (V.2022.1); EMFAC2021.
OFF-ROAD EQUIPMENT (CONSTRUCTION)
Off-road construction equipment would use diesel fuel during the construction phase of the proposed Project. A non-exhaustive list of off-road constructive equipment expected to be used during the construction phase of the proposed Project includes: forklifts, generator sets, tractors, excavators, and dozers. Based on the total amount of CO2 emissions expected to be generated by the proposed Project (as provided by the CalEEMod output), and standard conversion factors (as provided by the U.S. Energy Information Administration), the proposed Project would use a total of approximately 103,905 gallons of diesel fuel for off-road construction equipment. Detailed calculations are provided in Appendix B of this EIR.
State laws and regulations would limit idling from both on-road and off-road diesel-powered equipment and are part of a comprehensive regulatory framework that is implemented by the CARB. Additionally, as a practical matter, it is reasonable to assume that the overall construction schedule and process would be designed to be as efficient as feasible in order to avoid excess monetary costs. For example, equipment and fuel are not typically used wastefully due to the added expense associated with renting the equipment, maintaining it, and fueling it. Therefore, the opportunities for further future efficiency gains during construction are limited. For the foregoing reasons, it is anticipated that the construction phase of the project would not result in wasteful, inefficient, and unnecessary consumption of energy.
CONCLUSION
The proposed Project would use energy resources for the operation of Project buildings (natural gas and electricity), outdoor lighting (electricity), on-road vehicle trips (e.g. gasoline and diesel fuel) generated by the proposed Project, and off-road and on-road construction activities associated with the proposed Project (e.g. diesel fuel). Each of these activities would require the use of energy resources. The proposed Project would be responsible for conserving energy, including through the mitigation measures provided throughout this EIR, as well as through the implementation of statewide and local measures. The proposed Project would be responsible for conserving energy, to the extent feasible.
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3.0-68 Final Environmental Impact Report – LeBaron Ranch The proposed Project would comply with all applicable federal, State, and local regulations regulating energy usage. For example, PG&E, the electric and natural gas provider to the proposed Project, is responsible for the mix of energy resources used to provide electricity for its customers, and it is in the process of implementing the statewide RPS to increase the proportion of renewable energy (e.g. solar and wind) within its energy portfolio. PG&E has achieved at least a 33% mix of renewable energy resources in 2020 and is on track to achieve 60% mix of renewable energy by 2030. Moreover, the Project intends to supply 100 percent of its electricity demand from renewable sources associated with a combination of onsite generation and direct source renewable purchased energywould supply a notable portion of its on-site energy via rooftop solar PV, consistent with the latest Title 24 energy efficiency standards. Specifically, the Project applicant has entered into direct source renewable purchase contracts sufficient to supply these needs. Other statewide measures, including those intended to improve the energy efficiency of the statewide passenger and heavyduty truck vehicle fleet (e.g. the Pavley Bill and the Low Carbon Fuel Standard), would improve vehicle fuel economies, thereby conserving gasoline and diesel fuel. These energy savings would continue to accrue over time. Furthermore, the proposed Project would implement Mitigation Measures 3.13-1, which requires the Project applicant to implement feasible TDM (i.e. VMT reduction) strategies. Mitigation Measure 3.3-4 could also reduce Project-related GHG emissions, if a VERA is required. Moreover, the proposed Project would comply with the City’s Sustainability Action PlanClimate Action Plan GHG reduction measures (as applicable), and General Plan goals, objectives and policies related to energy conservation that are relevant to this analysis, and also be consistent with the State’s 2022 Scoping Plan and SJCOG’s 2022 RTP/SCS.
The proposed Project would comply with all existing energy standards and would not be expected to result in significant adverse impacts on energy resources. For these reasons, the proposed Project would not cause an inefficient, wasteful, or unnecessary use of energy resources nor cause a significant impact on any of the energy-related thresholds as described by the CEQA Guidelines.
This is a less than significant impact.
3.8 HAZARDS AND HAZARDOUS MATERIALS
The following changes were made to page 3.8-14 of Section 3.8 of the Draft EIR:
ACTIONS: SAFETY ELEMENT
• SAF-2.2A. Require new development to provide adequate access for emergency vehicles and evacuation routes, including by designing roadway systems to provide multiple escape routes in the event of a levee failure. SAF-2.6A. Restrict transport of hazardous materials within the city to routes that have been designated for such transport.
The following changes were made to pages 3.8-17 through 3.8-19 of Section 3.8 of the Draft EIR:
Contractors would be required to comply with CalEPA’s Unified Program; regulated activities would be managed by San Joaquin County Department of Environmental Health, the designated Certified Unified Program Agency for San Joaquin County, in accordance with the regulations included in the Unified Program (e.g., hazardous materials release response plans and inventories, California hazardous material management plans and inventories). The use, storage, transport, and disposal of construction-related hazardous materials would be required to conform to existing laws and regulations. Compliance with applicable laws and regulations governing the use, storage, EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-69 transportation, and disposal of hazardous materials would ensure all potentially hazardous materials are used and handled in an appropriate manner and would minimize the potential for safety impacts. For example, all spills or leakage of petroleum products during construction activities are required to be immediately contained, the hazardous material identified, and the material remediated in compliance with applicable State and local regulations for the cleanup and disposal of that contaminant. All contaminated waste would be required to be collected and disposed of at an appropriately licensed disposal or treatment facility.
Future construction activities could expose construction workers to accidental conditions as a result of existing potential contamination in on-site soils related to historical use of the Project site.
Additionally, iIf hazardous materials are discovered during Project construction activities, a Soils Management Plan (SMP) would be submitted and approved by the San Joaquin County Department of Environmental Health, as required by Mitigation Measure 3.8-1. The SMP would establish management practices for handling contaminated soils and other hazardous materials, including fuels, paints, cleaners, solvents, etc., during construction. Such compliance would reduce the potential for accidental release of hazardous materials during construction of the proposed Project.
As a result, it would lessen the risk of exposure of construction workers and the public to accidental release of hazardous materials, as well as the demand for incident emergency response.
The Project site consists of the Development Area (236.3 acres), Non-development Area (56.03 acres), and Right-of-Way Annexation Area (13.7 acres). The Development Area is predominantly comprised of agricultural and undeveloped uses. The Project proposes to construct a primarily residential development comprised of up to 1,411 residential units, parks/open space, and a school site within the Development Area, as well as circulation and infrastructure improvements. Future development within the Development Area would involve the conversion of active agricultural land into residential, public facility, and/or open space uses. Site grading, excavation for utilities, trenching, backfilling, and the construction of proposed structures could result in the exposure of construction workers and the general public to hazardous materials, such as pesticides and herbicides. Like most agricultural and farming operations in the Central Valley, agricultural practices in the area have used agricultural chemicals including pesticides and herbicides as a standard practice. Although no contaminated soils have been identified on the Project site or the vicinity above applicable levels, residual concentrations of pesticides may be present in soil because of historic agricultural application and storage. Continuous spraying of crops over many years can potentially result in a residual buildup of pesticides, in farm soils. Of highest concern relative to agrichemicals are chlorinated herbicides, organophosphate pesticides, and organochlorine pesticides (OCPs), such as such as Mecoprop (MCPP), Dinoseb, chlordane, dichlorodiphenyltrichloroethane (DDT), and dichloro-diphenyl-dichloroethylene (DDE).
Mitigation Measure 3.8-2 requires evenly distributed soil samples to be conducted within the Development Area for analysis of pesticides and heavy metals prior to initiation of any ground disturbance activities. If elevated levels of pesticides or heavy metals are detected during the laboratory analysis of the soils, the Project applicant would be required to prepare and implement a soil cleanup and remediation plan prior to the commencement of grading activities.
Implementation of Mitigation Measure 3.8-2 would ensure that redevelopment of the active agricultural land would not result in accidental release of or exposure to hazardous materials.
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OPERATIONAL PHASE IMPACTS
The operational phase would occur after construction is completed and business operations commence on a day-to-day basis. As previously noted, the Project proposes to construct a primarily residential development comprised of up to 1,411 residential units, parks/open space, and a school site within the Development Area, as well as circulation and infrastructure improvements. The Project does not propose uses that would involve the use or storage of hazardous substances other than limited quantities of hazardous materials such as solvents, fertilizers, pesticides, and other materials used for regular household maintenance of buildings and landscaping. The quantities of these materials would not typically be at an amount that would pose a significant hazard to the public or the environment. While the risk of exposure to hazardous materials cannot be eliminated, measures can be implemented to reduce risk to acceptable levels. Adherence to existing regulations would ensure compliance with safety standards related to the use and storage of hazardous materials, and the safety procedures mandated by applicable federal, State, and local laws and regulations would ensure that risks resulting from the routine transportation, use, storage, or disposal of hazardous materials during the operational phase of the proposed Project would be less than significant.
CONCLUSION
Overall, consistency with federal, State, and local laws and regulations related to hazardous materials discussed above and implementation of Mitigation Measures 3.8-1 through 3.8-2 would reduce potential impacts that could occur due to the routine transport, use, or disposal of hazardous materials or through the reasonably foreseeable upset and accident conditions involving the release of hazardous materials into the environment associated with construction activities within the Project site to a less than significant level.
MITIGATION MEASURE(S)
Mitigation Measure 3.8-1: Prior to initiating construction or grading activities, the construction contractor shall be provided with project-specific training regarding the identification and handling of hazardous materials and agency notification procedures. In the event that contaminated soils hazardous materials are encountered during construction, the Project applicant shall prepare and implement a Soils Management Plan (SMP) to provide guidance for the proper handling, onsite management, and disposal of impacted soil that might be encountered during construction activities shall be submitted and approved by the San Joaquin County Department of Environmental Health.
The SMP shall establish management practices for handling of contaminated soils and other hazardous materials, including fuels, paints, cleaners, solvents, etc., during construction. The SMP would include, but is not limited to, an outline of how Project construction crews would identify, handle, and dispose of potentially contaminated soil; the qualifications of the appropriately trained professionals that would monitor soil conditions and conduct soil sampling during construction; laboratory testing; anticipated field screening methods and appropriate regulatory limits to be applied to determine proper handling and disposal; and requirements for documenting and reporting incidents of encountered contaminants, such as documenting locations of occurrence, sampling results, and reporting actions taken to dispose of contaminated materials. In the event that potentially contaminated soils were encountered within the footprint of construction, soils would be tested and stockpiled. The SMP shall be submitted to the San Joaquin County Department of Environmental Health for review and approval. The approved SMP shall be posted and EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-71 maintained onsite during construction activities and all construction personnel shall acknowledge that they have reviewed and understand the plan.
Mitigation Measure 3.8-2: Prior to initiation of any ground disturbance activities, a soil sampling and analysis workplan shall be submitted to the San Joaquin County Department of Environmental Health for approval. The sampling and analysis plan shall meet the requirements of the Department of Toxic Substances Control Interim Guidance for Sampling Agricultural Properties (2008), and the County Department of Environmental Resources Recommended Soil and Groundwater Sampling for Underground Tank Investigations (2013). evenly Evenly distributed soil samples shall be conducted throughout the Development Area for analysis of pesticides and heavy metals. The samples shall be submitted for laboratory analysis of pesticides and heavy metals per DTSC and EPA protocols. The results of the soil sampling shall be submitted to the City of Stockton for review. If elevated levels of pesticides or heavy metals are detected during the laboratory analysis of the soils, a soil cleanup and remediation plan shall be prepared and implemented prior to the commencement of grading activities.
If the sampling results indicate the presence of agrichemicals that exceed commercial screening levels, a removal action workplan shall be prepared in coordination with San Joaquin County Environmental Health Department. The removal action workplan shall include a detailed engineering plan for conducting the removal action, a description of the onsite contamination, the goals to be achieved by the removal action, and any alternative removal options that were considered and rejected and the basis for that rejection. A no further action letter shall be issued by San Joaquin County Environmental Health Department upon completion of the removal action. The removal action shall be deemed complete when the confirmation samples exhibit concentrations below the commercial screening levels, which will be established by the agencies.
The following changes were made to pages 3.8-21 and 3.8-22 of Section 3.8 of the Draft EIR:
In San Joaquin County, all major roads are available for evacuation, depending on the location and type of emergency that arises. Primary evacuation routes within the Project site area would include Eight Mile Road, West Lane, and Lower Sacramento Road. The Project would not interfere with any emergency response plan or emergency evaluation plan, as the Project does not include any actions that would impair or physically interfere with the San Joaquin County EOP, San Joaquin County Hazardous Materials Area Plan, and the Stockton EOP. As previously stated, the Project proposes to construct a primarily residential development comprised of up to 1,411 residential units, parks/open space, and a school site within the Development Area, as well as circulation and infrastructure improvements that would result in increased connectivity of the area. Residential streets within the Development Area would be constructed according to City standards and would provide adequate access for emergency vehicles and connect to exiting major roads. Other improvements to circulation include an extension of the west-east trending Marlette Road, which would provide access to the proposed development and connect to West Lane and Lower Sacramento Road. Access to the proposed Project would not occur from Eight Mile Road, thus eliminating any conflicts with the flow of traffic on Eight Mile Road. The proposed Project includes an annexation of right-of-way along Eight Mile Road, which would be improved to City of Stockton standards.
The City of Stockton General Plan EIR concluded that development anticipated under the Envision Stockton 2040 General Plan would result in less than significant impacts relative to impacting or EXHIBIT 1
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3.0-72 Final Environmental Impact Report – LeBaron Ranch physically interfering with an adopted emergency response plan or emergency evacuation plan. As discussed in Section 3.10, Land Use, Population and Housing, while the proposed Project would result in population growth relative to existing conditions, it would not result in direct population growth beyond the City’s capacity identified in the General Plan; rather, the Project would result in a reduction of the total number of units anticipated under the General Plan by approximately 662 to 741 units. Overall, the proposed Project is not anticipated to exceed the planned growth (directly or indirectly) in the area beyond what is anticipated in the City’s General Plan or regional growth projections. As such, population growth associated with the Project is not anticipated to result in significant impacts or interfere with an adopted emergency response plan or emergency evacuation plan.
Future uses on the Project site will have access to the County resources that establish protocols for safe use, handling, and transport of hazardous materials. Construction activities are not expected to result in any unknown significant road closures, traffic detours, or congestion that could hinder the emergency vehicle access or evacuation in the event of an emergency. Additionally, the proposed Project would require review and approval by the City’s law enforcement and fire personnel to ensure that adequate emergency ingress and egress is provided throughout the site that would not interfere or impair evacuation plans. Therefore, impacts related to the potential for the project to impair implementation of emergency response plans would be less than significant impact.
Impact 3.8-56: Project implementation has the potential to expose people or structures to a risk of loss, injury, or death from wildland fires (Less than Significant)
3.9 HYDROLOGY AND WATER QUALITY
The following change was made to page 3.9-29 of Section 3.9 of the Draft EIR:
Mitigation Measure 3.9-1: All residential and non-residential structures within the Project site shall meet the urban level of flood protection, as required by the State of California Central Valley Flood Protection Act of 2008 (Senate Bill 5). Finished floor elevations of proposed residential structures shall be elevated to or above the prescribed 200-year floodplain elevation, or proposed nonresidential structures shall be floodproofed, consistent with the City of Stockton’s Criteria for Development in 200-year Floodplains and City of Stockton Municipal Code. Code compliance shall be documented in materials prepared by licensed professionals and submitted to the Community Development Director prior to issuance of grading permits.
3.10 LAND USE, POPULATION AND HOUSING
The following change was made to pages 3.10-26 and 3.10-27 of Section 3.12 of the Draft EIR:
1. Plan for Services: The Draft EIR assesses service capacity and demands for these services in Sections 3.12, Public Services and Recreation, and 3.14, Utilities. There are not any service deficiencies noted by the City of Stockton, or contained within this EIR that are anticipated to occur after installation of infrastructure and payment of fees. See Section 3.12, Public Services and Recreation, for more information. The annexation will also include detachment from the Lincoln Fire District. The proposed annexation area is within the Stockton Water Service Area boundary and the Wastewater Service Area boundary as defined by LAFCo and the City. It is also noted that a City Services Plan would be required and prepared for the Project to ensure EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-73 services are available. The Services Plan would be submitted with the LAFCo annexation application for the Project.
The following change was made to pages 3.10-29 of Section 3.12 of the Draft EIR:
o Service Requirements: As stated in this policy procedure, “an annexation shall not be approved merely to facilitate the delivery of one or a few services to the determent of the delivery of a larger number of services or service more basic to public health and welfare.” The proposed annexation is not requested in order to facilitate the delivery of one or a few services to the determent of the delivery of a larger number of services, or service more basic to public health and welfare. As stated further in Section 3.12 (Public Services and Recreation) and Section 3.14 (Utilities), the City has adequate service capacity to serve the proposed Project without reducing the adequacy of services elsewhere. See Section 3.12 (Public Services and Recreation) for more information. The annexation will also include detachment from the Lincoln Fire District. Therefore, the proposed annexation is consistent with this policy.
3.11 NOISE
No changes were made to Section 3.11 of the Draft EIR.
3.12 PUBLIC SERVICES AND RECREATION
The following changes were made to pages 3.12-16 and 3.12-17 of Section 3.12 of the Draft EIR:
The Project proposes the development of approximately 306 acres and includes a Development Area of 236.3 acres, Non-development Area of 56.0 acres, and Right-of-Way Annexation Area of
13.7 acres. The Development Area is predominantly comprised of agricultural and undeveloped uses. The Non-development area consists of agricultural land, one (1) existing residential home in the northwestern portion, a commercial use (single building), and a church. The Right-of-Way Annexation Area includes Eight Mile Road, forming the northern border of the Project site. The proposed Project would include the development of approximately 236.3-acres of land which will include: 1,332 to 1,411 residential units, parks, open space, public facilities, and public roadway right-of-way land uses. Using the most recent Department of Finance data (2023) for the average number of persons residing in a dwelling unit in the City of Stockton (3.13 persons per household), the Project could result in 4,169 to 4,416 residents. The proposed Project would not result in direct population growth beyond the City’s capacity identified in the General Plan; rather, it would result in a reduction of the total number of units anticipated under the General Plan by approximately 662 to 741 units. The net population reduction associated with the reduction of units under the proposed Project (compared to the capacity assumed for the Project site under the General Plan) is anticipated to be 2,072 to 2,319 persons.
The following changes were made to page 3.12-20 of Section 3.12 of the Draft EIR:
As identified in Table 3.13-5, the Project would result in a net increase of approximately 697 to 738 school-aged children in the LUSD. As described in Chapter 2.0, Project Description, the Project includes the potential development of a school site. The potential adverse physical environmental impacts associated with the proposed school have been addressed within this EIR. It is noted that EXHIBIT 1
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3.0-74 Final Environmental Impact Report – LeBaron Ranch LUSD will do a separate environmental study to determine the precise impacts of developing and operating this school site, if it decides to construct one in project area. Additionally, the LUSD collects impact fees from new developments under the provisions of SB 50. The Project would be subject to payment of school impact fees in accordance with Senate Bill 50 (SB 50). Pursuant to Government Code Section 65995(3)(h), payment of statutory fees is deemed to be full and complete mitigation of impacts of any legislative or adjudicative act, or both, involving, but not limited to, the planning, use or development of real property…” Developer fees collected by LUSD pursuant to SB 50 are used for the provision of additional and reconstructed or modernized school facilities. The Project Applicant would be required to pay all statutory fees in place at the time and demonstrate proof of payment to the City. With payment of the fees, the impact of the proposed Project on the need for additional school facilities is less than significant.
3.13 TRANSPORTATION AND CIRCULATION
The following changes were made to pages 3.13-18 and 3.13-19 of Section 3.13 of the Draft EIR:
TABLE 3.13-2: VMT ANALYSIS – CITYWIDE TOTAL VMT
SCENARIO NO PROJECT WITH PROJECT
PROJECTRELATED CHANGE
WITH PROJECT
VMT GREATER
THAN NO
PROJECT VMT?
Baseline Year Before Mitigation 5,184,549 5,220,298 35,749 Yes Baseline Year With Mitigation -- 5,215,729 31,180 Yes
Cumulative Year Before Mitigation 6,597,410 6,636,505 39,095 Yes Cumulative Year With Mitigation -- 6,632,517 35,107 Yes SOURCE: WK SHIJO CONSULTING, LLC, 2023.
An assessment of potential measures included in the GHG Handbook is presented in detail in Appendix F of this EIR. The assessment includes the feasibility and applicability of GHG Handbook measures for the proposed Project. Measures considered for the Project are those included in the GHG Handbook in the Transportation category. The GHG Handbook presents measures which are considered feasible at a community size level, but are considered not feasible at an individual project size level. These measures, including carshare programs and community-based travel planning, were considered as potential mitigation measures, but are not recommended. The GHG Handbook presents measures which are not applicable to residential land use projects. These are measures which are primarily applicable to employment-generating uses, such as increased job density, ridesharing programs, and subsidized transit programs.
Measures were also considered, but are not feasible because they are not within the authority of the applicant or the City of Stockton. As discussed above, currently, the San Joaquin Regional Transit District (RTD) provides limited public transit service to the Project site. The County Hopper Route 93 operates weekdays along West Lane, with eight northbound trips per day and ten southbound trips per day. County Hopper service is a deviated fixed route type of service. The GHG Handbook presents measures which are related to the structure of the community-level public transit system. While these measures have the potential to reduce VMT, the RTD has authority to implement the measures. Implementation of the measures, including development of a transitoriented development, increased transit service frequency, provide bus rapid transit, or reduce transit fares, is not within the authority of the applicant or the City of Stockton.
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Final Environmental Impact Report – LeBaron Ranch 3.0-75 The GHG Handbook presents measures which are considered not applicable to, or not feasible for, the LeBaron Ranch Project site. The GHG Handbook presents measures which are considered not applicable to, or not feasible for, the Project site. These measures were considered as potential mitigation measures, but are not recommended. The Project includes 194 high density multiplefamily dwelling units. Current residential development in the vicinity of the Project site is predominantly composed of relatively lower density single family dwelling units. The General Plan travel demand model, used to estimate VMT for the Project, already includes relatively lower VMT per unit generated by the Project multiple family dwelling units. Therefore, the measure to provide increased residential density is already incorporated into the VMT levels presented in Table 3.13-2, and is not considered applicable as a mitigation measure.
The GHG Handbook includes a measure that involves affordable and below market rate housing, noting, “Multifamily residential units must be permanently dedicated as affordable for lower income families.” The Project includes a mix of housing types: low-density single family dwelling units, medium-density single family dwelling units, and high-density multiple-family dwelling units.
The Project does not include units that are deed restricted as “affordable units”. Affordability by design, both for purchase and rent, will be created with some of the product within the medium density and high-density designations.
The GHG Handbook includes three measures that involves parking supply and parking cost, including limiting residential parking supply, unbundling residential parking costs from property cost, and implement market price public parking (on-street). For limiting residential parking supply, the GHG Handbook notes, “This measure is ineffective in locations where unrestricted street parking or other offsite parking is available nearby and has adequate capacity to accommodate project-related vehicle parking demand.” Unrestricted street parking is available in the vicinity of the Project site, and is expected to be available in the future. Implementation of unbundling residential parking costs from property cost, would appear to require modification of Stockton Municipal Code section 16.64.040, Number of parking spaces required. In the description of implementing market price public parking, the GHG Handbook notes, “This measure will price all on-street parking in a given community, with a focus on parking near central business districts, employment centers, and retail centers.” The Project is composed of residential land use, rather than central business districts, employment centers and retail centers. Therefore, these parkingrelated mitigation measures are not feasible for the Project.
The GHG Handbook includes a measure related to the density and connectivity of streets. the Project as proposed includes a relatively high density of street intersections within the Project site.
The number of connections to surrounding arterial roadways (i.e., Eight Mile Road, West Lane, and Lower Sacramento Road), however, are constrained by existing adopted precise road plans for each of these roadways. As a result, the measure is considered not feasible for the Project.
The following changes were made to pages 3.13-21 through 3.13-23 of Section 3.13 of the Draft EIR:
Based on estimates presented in the GHG Handbook, implementation of the Project Design Features recommended above could result in a maximum reduction in VMT of 4.9 percent. It would be reasonable to expect implementation of the measures to result in a reduction somewhat less than 4.9 percent. As a result, implementation of the recommended Project Design Features would not reduce the Project impact on VMT to a less than significant level.
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3.0-76 Final Environmental Impact Report – LeBaron Ranch Mitigation Measure 3.13-1, which requires travel demand management (TDM) strategies, would be required if the school within the project site is constructed. While the VMT reduction measures described immediately above are oriented towards residential land uses, Mitigation Measure 3.13-1 is oriented towards employment-generating uses. Implementation of Mitigation Measure 3.13-1 is feasible because it is within the applicant’s purview to implement and has been found effective in previous academic studies. However, the precise effectiveness of specific TDM strategies can be difficult to accurately measure due to several external factors such as types of tenants, employee responses to strategies, and changes to technology. Additionally, it is noted that with the current planned growth and development in the City of Stockton, the City’s jobs-housing ratio is expected to increase in 2040, and city-wide home-based work VMT per worker is projected to increase. TDM strategies alone cannot eliminate VMT increases caused by land use imbalance in the rest of the City and greater San Joaquin County geographic area.
Within the City of Stockton and San Joaquin County, there is no requirement to prepare a TDM plan for residential uses. Additionally, specific vehicle trip reduction targets or monitoring of the effectiveness of the Project-specific TDM Plan are not required by San Joaquin County as of January 2024.
The City of Stockton adopted their Transportation Impact Analysis Guidelines (TIAG) in May 2023 which includes strategies that are intended to reduce vehicular travel to meet the requirements of SB 743. The TIAG includes provisions for TDM strategies to reduce the amount of vehicle traffic generated by new employment development by creating measures, strategies, incentives, and policies to shift employees from driving alone and have these employees be aware of and look into the ability of using other travel modes including carpooling, transit (bus and commuter tail), cycling, and walking. In addition, employees who initially arrive in a vehicle would also be encouraged to use alternative travel modes (walking and bicycling). It is possible that the Project would result in schools employees, should the LUSD develop the proposed school site.
As part of this on-going effort to reduce VMT and associated greenhouse gas emissions in the City and region, a TDM Plan will be developed based on California Air Pollution Control Officers Association (CAPCOA) strategies that evaluate any project against mode split targets and other elements outlined by the City of Stockton. The required TDM plan for the Project will be submitted to the City for review and approval.
To monitor the effectiveness of the TDM Plan, there are several viable options that may be required by the City of Stockton as part of the TIAG, including annual surveys to determine employee travel mode split and travel distance for home-based work trips, and/or the implementation of technology to determine the amount of traffic generated by and home-based work miles traveled by employees.
As part of Mitigation Measure 3:13-1, the proposed Project would be required to monitor and evaluate the effectiveness of the Project’s TDM Plan and provide the results to the City of Stockton.
Based on the results of the evaluation, modifications to the TDM Plan may be required by the City to improve effectiveness toward achieving the home-based work VMT per worker target identified in the City’s TIAG.
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Final Environmental Impact Report – LeBaron Ranch 3.0-77 Based on the status of the City of Stockton’s TIAG, even with the implementation of Mitigation Measure 3.13-1, the impact would remain significant and unavoidable when compared to the City of Stockton’s VMT goal of reducing average home-based work VMT per worker from 18.56 miles to
15.66 miles.
Other strategies to reduce VMT were considered but were deemed infeasible. Further consideration was given to the feasibility of vehicle travel and parking pricing strategies. However, this would have to be a citywide program, which is not under the control of the applicant. For example, reducing parking standards is a City planning and policy measure and cannot be implemented by an individual Project. Additionally, according to the LeBaron Ranch VMT Assessment (WK Shijo Consulting, LLC, 2023) parking pricing strategies are typically recommended for commercial projects, not residential projects such as the proposed Project.23 This is, in part, because, when limiting parking supply, a best practice is to do so at sites that are located near high quality alternative modes of travel (such as a rail station, frequent bus line, or in a higher density area with multiple walkable locations nearby).24 However, there would not be sufficient high quality nearby alternative modes of transportation would be available to serve the proposed Project, should parking pricing strategies be implemented.
MITIGATION MEASURE(S)
Mitigation Measure 3.13-1: The Project applicant shall work with the City of Stockton to implement feasible Transportation Demand Management (TDM) strategies, which would decrease the VMT generated by the Project. Specific potential TDM strategies include, but are not limited to, the following:
• Provide Coordinate with public transit serviceagencies, including improving San Joaquin Rapid Transit District (RTD) regarding transit service connecting workers with existing and future residential developments;
• Coordinate with San Joaquin RTD regarding the potential for increasing service on Hopper Route 93;
• Implement a fair value commuting program or other pricing of vehicle travel and parking; • TDM coordinator for large employers, such as the LUSD, should the school site be developed;
• Provide carpool and/or vanpool incentive programs;
• Provide on-site lockers and showers for workers who take alternative transportation, such as those employed by the LUSD, should the school site be developed; • Promote walking and bicycling for employees who live and/or work in the area through the preparation of an Active Transportation Plan;
• Incentivize the use of alternative travel modes for travel within the project site through shared use of e-bikes and e-scooters;
23 Refer to Measure T-24: Implement Market Price Public Parking, in CAPCOA’s GHG Handbook. Available at:
https://www.caleemod.com/handbook/index.html
24 Refer to Measure T-15: Limit Residential Parking Supply, in CAPCOA’s GHG Handbook. Available at:
https://www.caleemod.com/handbook/index.html
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3.0-78 Final Environmental Impact Report – LeBaron Ranch • Allow flexible work hours and schedule classes to reduce arrivals/departures during peak hours; and
• Employer coordination to SJCOG’s DIBs program for workers.
The TDM Plan shall be submitted to the City for review, and the effectiveness of the TDM Plan shall be evaluated, monitored, and revised, if necessary. The TDM Plan shall include the TDM strategies which will be implemented during the lifetime of the proposed Project and shall outline the anticipated effectiveness of the strategies to achieve the home-based work VMT per worker target identified in the City’s TIAG. The effectiveness of the TDM Plan may be monitored through annual surveys to determine employee travel mode split and travel distance for home-based work trips, and/or the implementation of technology to determine the amount of traffic generated by and home-based work miles traveled by employees, which shall be determined in coordination with the City and included as part of the TDM Plan. Monitoring of the effectiveness of the TDM Plan shall be mandatory at least for first three year after implementation of the TDMs to see how well the TDM Plan is performing, and to add new TDMs, if some measures become feasible later.
The following changes were made to page 3.13-24 of Section 3.13 of the Draft EIR:
One intersection and one roadway corridor identified with high numbers of accidents are within the Project site vicinity. The intersection of West Lane and Hammer Lane is listed as a location with a high number of bicycle accidents. The Hammer Lane corridor is listed as a street corridor with a high number of pedestrian accidents. The proposed Project is expected to result in project-related traffic through the intersection and along the street corridor.
However, as shown in Table 11 and Table 18 in Appendix F, the Project would not result in a change in LOS at the intersection of West Lane and Hammer Lane. With implementation of the Project, the intersection would continue to operate at LOS D, which is considered acceptable by the City of Stockton. As a result, the Project would not result in a significant change to the vehicle mix or speed of traffic that is not compatible with the design of existing or planned facility design.
The following changes were made to page 3.13-25 of Section 3.13 of the Draft EIR:
The Project would be developed in six (6) phases. A portion of the Central Park would be developed in Phase 1. The sequence of phasing would generally be from the future Marlette Road, to the north, toward Eight Mile Road. During construction, there may be periods of active construction in one (1) or more areas of the Project site, depending on the location of each phase and the individual timelines for Project components. Most of the construction activity would occur on the Project site. Construction management plans are prepared by the construction manager once the Project has entered the construction phase, or by the Project civil engineer. The plans will be reviewed by the City of Stockton. The plans will ensure construction activities do not result in unacceptable effects on safety and traffic operations, and do not adversely affect emergency service providers. Therefore, this impact would be less than significant.
3.14 UTILITIES AND SERVICE SYSTEMS
The following changes were made to page 3.14-8 of Section 3.14 of the Draft EIR:
The RWCF provides secondary and tertiary treatment of municipal wastewater from throughout the City. The remainder of the City is served by on-site septic systems, or lie outside the urban service EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-79 area. The RWCF processes an average of 33 million gallons per day (mgd) and has capacity to treat 55 million gallons of sewage per day. The treated wastewater is discharged into the San Joaquin River. Additionally, the RWCF sewer treatment plant is undergoing the Modifications Project to modernize the facility, and to accommodate growth initially through 2035 with the ability to expand through 2045 and beyond. The Modification Project includes changing the sewer treatment to an activated sludge process to meet the State’s standards and replaces equipment and processes that are 40 to 70 years old. The Modification Project was initiated to increase the reliability of the liquid and solids treatment processes, improve reliability in treating existing and projected flows, reduce energy costs and provide reliable renewable energy alternatives, and reduce nitrate plus nitrite concentrations in the final effluent to comply with the RWCF NPDES permit.25 The following changes were made to page 3.14-10 of Section 3.14 of the Draft EIR:
Mitigation Measure 3.14-1: Prior to occupancy of any building that would require wastewater treatment services, the Project proponent shall secure from the City of Stockton Municipal Utilities Department with a request for utility service adequate wastewater treatment capacity/allocation.
The following changes were made to page 3.14-11 of Section 3.14 of the Draft EIR:
New wastewater collection and conveyance infrastructure needed for the proposed Project will require trenching/excavation of earth, and placement of pipe within the trenches at specific locations, elevations, and gradients, consistent with the City of Stockton Municipal Code Chapter
13.08, Sewer Use. The applicant will refine the wastewater collection/conveyance infrastructure design through the development of improvements plans which undergo a review by the Public Works Department to ensure consistency with the City’s engineering standards. This improvement plan process will include full engineering design (i.e. location, depth, slope, etc.) of all conveyance infrastructure as well as a review of new sewer pump stations and new force mains if needed.
Ultimately, the sanitary sewer collection system will be an underground collection system installed as per the City of Stockton standards and specifications. Sanitary sewer disposal and treatment will be to the RWCF.
The following changes were made to page 3.14-13 of Section 3.14 of the Draft EIR:
The New Hogan Reservoir has a water storage capacity of 317,000 AF. It receives its water supply primarily from rain runoff fed by the Calaveras River. The United States Army Corps of Engineers operates the dam and determines flood control releases when the New Hogan Project is in flood control mode. SEWD is the Watermaster and determines New Hogan releases for irrigation and municipal use for itself and Calaveras County Water District (CACWD) during non-flood control periods. The total annual supply available for both SEWD and CACWD is approximately 84,100 AFY in normal water years. The contract also provides that any water not used by CACWD can be used by SEWD. At the current level of CACWD use, the SEWD can rely on about 83,000 AFY of supply from the New Hogan Project in normal water years under safe yield operation. However, if CACWD exercises its percentage entitlement (43.5 percent), the available supply from this source would be reduced.
25 City of Stockton, Draft Supplement to City of Stockton Regional Wastewater Control Facility Modifications Project Environmental Impact Report. February 2022.
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3.0-80 Final Environmental Impact Report – LeBaron Ranch The New Melones Reservoir has a water storage capacity of 2.4 million AF and is a part of the Central Valley Project (CVP). It receives water primarily from rain and snowmelt runoff and is fed by the Stanislaus River. Pursuant to a December 1983 contract with USBR, SEWD and Central San Joaquin Water Conservation District (CSJWCD) are entitled to up to 155,000 AF of water annually.
SEWD is allocated up to 75,000 AFY. Water allocation amounts are based on the March-September water forecast and the February end of month storage in the New Melones Reservoir each year, to be used for municipal, industrial, or agricultural use. This water is subject to cutbacks based on the USBR’s overall CVP operations.
The startup and operation of the DWTP in 2012 has provided the COSMUD with a new and reliable source of surface water under Water Right Permit 21176 for current and future use within its service area. In addition, COSMUD will continue to rely on SEWD supplies for a portion of its water supply portfolio provided under the Second Amended Contract (expires in 2035), particularly as development continues in South Stockton. Second Amended Contract Section 3 Renewal:
Continued Service entitles COSMUD continued service delivery under then current or mutuallyagreeable terms.
The following changes were made to page 3.14-18 of Section 3.14 of the Draft EIR:
WATER SUPPLY AND DEMAND COMPARISON
Based on the analysis described above, the City’s existing and projected potable water supplies are sufficient to meet the City’s existing and projected future potable water demands, including those future water demands associated with the Project, to the year 2040 under all hydrologic conditions.
The City’s 2008 contract with WID includes a provision for increase in water supply as WID-served agricultural lands in the northern part of the City are annexed to the City for municipal and industrial use. Under this contract, an additional 6,500 AFY of WID supply will become available to COSMUD at a rate of 3.0 AFY per acre annexed. WID supply may potentially increase from 6,500 AFY to 13,000 AFY by 2030.
Concurrent with the preparation of this UWMP, the City prepared a Water Master Plan Update to identify projects that improve the reliability of its existing water supplies. Although these projects do not provide additional water supplies, they enhance reliability of the City’s water supplies. The Water Master Plan Update recommended the following projects, which have been included in the City’s budget for implementation:
• Groundwater Study: A comprehensive groundwater supply study was recommended to investigate existing facility conditions, capacity, and water quality/regulatory trends. The outcome of the study would identify recommendations for rehabilitation of wells in North Stockton and South Stockton, including identifying appropriate wellhead treatment (at each location or centralized at a reservoir site).
• Groundwater Storage Bank Study: A groundwater storage bank/recharge basins study was recommended to address future supply reliability by expanding/augmenting its conjunctive use portfolio, allowing for the flexibility of banking unused available surface water supply in the groundwater basin for use at a later time.
The following changes were made to page 3.14-28 of Section 3.14 of the Draft EIR:
EXHIBIT 1
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Final Environmental Impact Report – LeBaron Ranch 3.0-81 As shown in Table 3.14-4, projected future water demands presented in the 2020 UWMP used landuse based water demand projections developed for the City’s 2021 Water Master Plan Update.
Water demand projections were based on the anticipated growth within the COSMUD water service area as defined by Envision Stockton 2040 General Plan; the Project, which is consistent with the 2040 General Plan, is included in these projections. The proposed Project would not result in direct population growth beyond the City’s capacity identified in the General Plan; rather, it would result in a reduction of the total number of units anticipated under the General Plan by approximately 662 to 741 units. The net population reduction associated with the reduction of units under the proposed Project (compared to the capacity assumed for the Project site under the General Plan) is anticipated to be 2,072 to 2,319 persons. Projected water demands for 2045 are assumed to be the same as projected water demands in 2040 since the development of future planned developments beyond 2040 is not defined in the Envision Stockton 2040 General Plan.
The following changes were made to pages 3.14-40 and 3.14-41 of Section 3.14 of the Draft EIR:
According to the City of Stockton and San Joaquin County Stormwater Quality Control Criteria Plan (SWQCCP), the Project would be considered both a Priority Project and a PLU Project, as the Project includes a residential subdivision of 10 housing units or more (Priority Project) and contains land uses with at least 10 developed dwelling units per acre (PLU Project). Priority projects are required to prepare and submit a Project Stormwater Quality Control Plan with the initial building permit submittal, that demonstrates the Project incorporates site design measures, landscape features, and engineered treatment facilities (typically bioretention facilities) that will minimize imperviousness, retain or detain stormwater, slow runoff rates, and reduce pollutants in postdevelopment runoff. In particular, the Project Stormwater Quality Control Plan would specify BMPs required to be implemented by the Project and design specifications for selected BMPs. The Project Stormwater Quality Control Plan must be submitted for review and approval by the City of Stockton Department of Municipal Utilities, consistent with the requirements in the City’s Municipal Code Chapter 13.20.
The proposed Project includes development of a new storm drainage system to serve the proposed uses as described above. The potential environmental effects resulting from construction of the storm drainage system are analyzed throughout this Draft EIR, and in some cases, there are potentially significant impacts associated with construction of this infrastructure. Where impacts are identified for each environmental topic, mitigation measures are developed to avoid, minimize, or compensate for the impact to the extent practicable. All mitigation measures presented throughout this EIR will be implemented to reduce impacts to the extent practicable. There will not be any significant impacts beyond what is disclosed in the other chapters of this document. In addition to the other mitigation measures presented throughout this document, the following mitigation measure is intended to ensure that the drainage system is designed and constructed to meet the City’s performance standards. With the implementation of mitigation measures presented throughout this EIR, and the following mitigation measure, impacts would be less than significant.
MITIGATION MEASURE
Mitigation Measure 3.14-2: Prior to the issuance of a building or grading permit, the project applicant shall submit a drainage plan to the City of Stockton for review and approval. The plan shall include an engineered Storm Water Quality Control Criteria Plan (SWQCCP) that demonstrates attainment of pre-project runoff requirements prior to release at the Bear Creek outfall. The plan EXHIBIT 1
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3.0 REVISIONS
3.0-82 Final Environmental Impact Report – LeBaron Ranch shall describe the volume reduction measures and treatment controls, which may include, but not limited to vegetated swale, infiltration basin, rain garden, or bioretention, consistent with the Federal Clean Water Act, the City’s Stormwater Quality Control Criteria Plan, the adopted municipal stormwater National Pollutant Discharge Elimination System (NPDES) permit and the City's corresponding Stormwater Management PlanCity of Stockton requirements.
4.0 OTHER CEQA-REQUIRED TOPICS
The following changes were made to pages 4.0-28 and 4.0-29 of Chapter 4.0 of the Draft EIR:
The Development Area is bordered on the north by Eight Mile Road, on the east by West Lane, on the west by agricultural land, a residential home, a church and commercial building along Lower Sacramento Road, and on the south by Marlette Road, a partially paved frontage road. The Development Area is predominantly comprised of agricultural and undeveloped uses; sheds and associated agricultural equipment exist in the center portion of the site. Additionally, two (2) dirt/gravel roadways bisect the Development Area, including one roadway extending north to south from Eight Mile Road to the southern boundary at Marlette Road, and another extending east to west from West Lane connecting to the dirt/gravel roadway in the center of the Development Area.
Irrigation canals, operated by the Woodbridge Irrigation District, run along the northern, eastern, and southern borders of the Development Area, separating existing agricultural uses from the respective roadways.
The Project site is adjacent to the City of Stockton’s northern city limits, within the City of Stockton SOI (as defined in the Envision Stockton 2040 General Plan), and within the City of Stockton Urban Services Boundary. The Project site is primarily bounded by lands within the County of San Joaquin (County) to the north and south. Lands within the City of Stockton are located to the east and west.
North and south of the Project site are existing agricultural lands, to the east of the site are existing are existing agricultural lands that were recently incorporated into the City of Stockton and will be developed with residential and commercial uses as part of the approved Tra Vigne development project. West of the Project site is an existing residential neighborhood. The proposed Project would require a City of Stockton General Plan Amendment to the Land Use Element to change land uses on the Project site. Changes to the General Plan Land Use Map are largely a reorganization of the precise locations for each land use within the boundary of the Project site as opposed to land use changes. The proposed Project would not result in direct population growth beyond the City’s capacity identified in the General Plan; rather, it would result in a reduction of the total number of units anticipated under the General Plan by approximately 662 to 741 units. The net population reduction associated with the reduction of units under the proposed Project (compared to the capacity assumed for the Project site under the General Plan) is anticipated to be 2,072 to 2,319 persons. The Project would result in an extension of developed uses within an area of the City that currently has development uses and is planned for urban development by the City’s General Plan.
The Project would provide roadways and pedestrian pathways to connect the Project site to the existing circulation system and to allow access to and from the site.
Buildout of the Project would require the extension of off-site and on-site roadway, potable water, wastewater, and storm drainage infrastructure to the undeveloped and underdeveloped portions of the Project site. However, as noted in Section 3.15, Utilities, wastewater generated by the proposed Project could be accommodated by the existing wastewater treatment facilities. Additionally, the City has adequate water supply to meet the water demand from buildout of the Project and the EXHIBIT 1
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REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-83 landfill that would serve the Project has adequate capacity to manage the solid waste generated as a result of the Project. Furthermore, buildout of the Project would not generate or contribute runoff water that would exceed the capacity of the stormwater drainage system. The existing development to the west of the Project site includes residential uses. The land to the east and south of the Project site is also designated for residential uses. Growth inducement to the undeveloped agricultural land to the north of the Project site would not occur as that land is designated as Agricultural General (A/G), with land along the Pixley Slough designated Resource Conservation (OS/RC). The proposed Project would not oversize or extend infrastructure to that area, and would not induce growth beyond that anticipated under the City’s General Plan.
Given the historical and current population, housing, and employment trends, growth in the City, as well as the entire state, is inevitable. The primary factors that account for population growth are natural increase and net migration. The average annual birth rate for California is expected to be 20 births per 1,000 population. Additionally, California is expected to attract more than one third of the country’s immigrants. Other factors that affect growth include the cost of housing, the location of jobs, the economy, the climate, and transportation. While these factors would likely result in growth in Stockton during the planning period of the General Plan, growth will continue to occur based primarily on the demand of the housing market and demand for new commercial, industrial, and other non-residential uses. Using the most recent Department of Finance data (2023) for the average number of persons residing in a dwelling unit in the City of Stockton (3.13 persons per household), the Project could result in 4,169 to 4,416 residents. Based on the growth projected to occur in the City’s General Plan Planning Area, which, as discussed above, the net population reduction associated with the reduction of units under the proposed Project (compared to the capacity assumed for the Project site under the General Plan) is anticipated to be 2,072 to 2,319 persons, the proposed Project would not induce a substantial amount of growth that has not been adequately planned. Overall, cumulative growth would not displace substantial numbers of people or housing or exceed planned levels of growth.
The Project would result in an increase in employment opportunities by creating full-time job positions at the school site. The Project would also generate short-term construction employment opportunities, but these opportunities would not result in substantial population growth in the project region. The increase in population could also induce indirect job inducement. As discussed above, the population growth of the Project is anticipated by the General Plan. The General Plan land use map provides a mixture of housing, shopping, public, and employment opportunities, so that as the number of residents increase, they do not have to pressure adjacent communities to provide new commercial and employment opportunities. Therefore, the proposed Project would not result in significant growth inducing impacts.
5.0 ALTERNATIVES TO THE PROPOSED PROJECT
The following changes were made to page 5.0-12 of Chapter 5.0 of the Draft EIR:
Development of the proposed Project would result in the permanent conversion of 23.12 acres of Prime Farmland, 217.79 acres of Farmland of Statewide Importance, and 7.51 acres of Farmland of Local Importance to non-agricultural use. Because the size of the Development Area and Project site under this alternative would be equal to the Project, the amount of Farmland converted would be equal to the Project. Overall, the Reduced Density Alternative would have equal similar impacts on agricultural resources when compared to the proposed Project.
EXHIBIT 1
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3.0 REVISIONS
3.0-84 Final Environmental Impact Report – LeBaron Ranch The following changes were made to page 5.0-13 of Chapter 5.0 of the Draft EIR:
The size of the Development Area and Project site would be equal to the Project under this alternative. As such, the same amount of habitat conversion would result, and the same mitigation measures would be required for this alternative. As such, the Reduced Density Alternative would result in similar equal impacts to biological resources when compared to the proposed Project.
Cultural and Tribal Resources
As discussed previously, a CHRIS search and a field assessment conducted as part of the Cultural Resource Assessment found no evidence of cultural resources in the Project site. As such, the Project site does not contain historical resources, archeological resources, or tribal cultural resources. Additionally, no human remains have been documented on or near the Project site. Any previously unknown cultural or tribal cultural resources which may be discovered during development of the proposed Project would be required to be preserved, either through preservation in place, excavation, documentation, curation, data recovery, or other appropriate measures. With implementation of the mitigation measures provided in Section 3.5, the proposed Project is not anticipated to considerably contribute to a significant reduction in cultural resources in the region.
The size of the Development Area and Project site would be equal to the Project under this alternative. As such, the same amount of land conversion would result. This would result in an equal potential to disturb or destroy cultural, historic, and archaeological resources, as well as paleontological resources. The same mitigation measures required for the proposed Project would be required for this alternative. Overall, the Reduced Density Alternative would result in an similar equal potential for impacts to cultural resources.
The following changes were made to page 5.0-15 of Chapter 5.0 of the Draft EIR:
Under the Reduced Density Alternative, the type of urban uses would not change when compared to the proposed Project, but the amount of development would be reduced by 25 percent. This alternative would still use the hazardous materials identified under the proposed Project. As such, this alternative would have similarequal impacts from hazards and hazardous materials impacts when compared to the proposed Project.
The following changes were made to page 5.0-17 of Chapter 5.0 of the Draft EIR:
The VMT would likely decrease due to the reduction in units. The other impacts would be similar equal to the Project. Overall, the Reduced Density Alternative would result in slightly reduced traffic related impacts when compared to the proposed Project.
The following changes were made to page 5.0-19 of Chapter 5.0 of the Draft EIR:
Uses in the Agriculture Protection Alternative would be required to adhere to the same mitigation measures as the proposed Project. The Agriculture Protection Alternative would result in similarequal impacts related to air quality when compared to the proposed Project and the significant and unavoidable air quality impact would remain under this alternative.
The following changes were made to page 5.0-20 of Chapter 5.0 of the Draft EIR:
EXHIBIT 1
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REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-85 Under the Agriculture Protection Alternative, the amount of developed area would be reduced by 25 percent compared to the Project, but the structural square footage that would be subject to hazardous geological conditions would be similarequal to the Project. Both the proposed Project and the Agriculture Protection Alternative would not result in potentially significant impacts related to geology and soils and both would require mitigation. As such, the Agriculture Protection Alternative would result in similarequal geology and soils impacts when compared to the proposed Project.
The following changes were made to page 5.0-21 of Chapter 5.0 of the Draft EIR:
Under the Agriculture Protection Alternative, the Project site would be developed with the same number of residential units as the proposed Project, but the amount of developed area would be decreased by 25 percent. All uses in the Agriculture Protection Alternative would be required to adhere to the same mitigation measure as the proposed Project. The similar equal amount of development would result in a corresponding similar equal level of GHG emissions when compared to the proposed Project. As such, the GHG emissions impact would have similar equal impacts when compared to the proposed Project.
Hazards and Hazardous Materials
For the most part, potential impacts associated with new and future development would be confined to commercial and industrial areas and would not involve the use of hazardous substances in large quantities or that would be particularly hazardous. Incidents, if any, would typically be site specific and would involve accidental spills or inadvertent releases. Associated health and safety risks would generally be limited to those individuals using the materials or to persons in the immediate vicinity of the materials and would not combine with similar effects elsewhere (i.e., construction workers), as hazard-related impacts tend to be site-specific and Project-specific.
The Project site is not associated with any existing hazardous materials spills; however, after agricultural operations cease, and development is anticipated to occur, the applicant or future project proponent would be required to hire a qualified consultant to perform site-specific soil sampling to determine if chemicals of potential concern associated with the historical agricultural uses at the Project site are present in shallow soil at concentrations that would pose a threat to human health. Overall, consistency with federal, State, and local laws and regulations related to the handling of hazardous materials discussed above and implementation of Mitigation Measures 3.8-1 through 3.8-3 would reduce potential impacts that could occur due to the routine transport, use, or disposal of hazardous materials or through the reasonably foreseeable upset and accident conditions involving the release of hazardous materials into the environment associated with construction activities within the Project site to a less than significant level.
Under the Agriculture Protection Alternative, the type of urban uses would not change when compared to the proposed Project, but the amount of developed area would be reduced by 25 percent. The reduction in development area would result in a slight reduction in construction related impacts because the amount of potentially contaminated soils that would be disturbed would be reduced compared to the Project. This alternative would use the same types and quantities of hazardous materials identified under the proposed Project. As such, this alternative would have slightly reducedequal impacts from hazards and hazardous materials impacts when compared to the proposed Project.
EXHIBIT 1
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3.0 REVISIONS
3.0-86 Final Environmental Impact Report – LeBaron Ranch The following changes were made to pages 5.0-22 and 5.0-23 of Chapter 5.0 of the Draft EIR:
The Agriculture Protection Alternative would result in an equal amount of residential units uses compared to the Project; therefore, the noise impacts associated with vehicular and operational activities of the proposed Project would be equal under this alternative. Although the eastern portion of the Development Area would not be developed under this alternative, there are few noise sensitive receptors near the eastern portion of the site. All noise issues would be mitigated, as appropriate, through noise attenuation and best management practices under both the proposed Project and the Agriculture Protection Alternative. Therefore, under this alternative, noise impacts are similarequal when compared to the proposed Project.
Public Services and Recreation
Development of the proposed Project will require payment of all applicable fees and assessments required to fund its fair share of public services. This funding would assist in the development of facilities to meet the City’s standards. The proposed Project would have a less than significant impact to fire, police, schools, and recreational facilities.
Under this alternative, the proposed Project would be developed with the same components as described in the Project Description, but the density of the residential areas would be increased to maintain the number of residential units proposed while also reducing the development footprint.
Both the proposed Project and the Agriculture Protection Alternative would result in less-thansignificant impacts to public services. As such, impacts to public services under this alternative would be similarequal to the proposed Project.
Transportation and Circulation
As shown in Table 3.13-1 in Section 3.13, under Baseline Year conditions, the proposed Project would generate 20.10 home-based VMT per resident. This would be 35 percent above the significance threshold. As a result, the Project is considered to have a significant impact on VMT.
Under Cumulative Year conditions, the Project would generate 17.54 home-based VMT per resident. This would be 18 percent above the significance threshold. As a result, the Project is considered to have a significant impact on VMT. All other transportation related impacts were determined to be less than significant.
The VMT would be similar the Project. As such, the significant and unavoidable VMT impact would remain under this alternative. The other impacts would be like the Project. Overall, the Reduced Density Alternative would result in similarequal traffic related impacts when compared to the proposed Project.
The following changes were made to pages 5.0-24 and 5.0-25 of Chapter 5.0 of the Draft EIR:
This alternative would have similarequal wastewater treatment demand, similarequal water demand, similarequal solid waste generated, and similarequal storm water runoff when compared to the proposed Project. As such, this alternative would have similarequal impacts when compared to the proposed Project.
ENVIRONMENTALLY SUPERIOR ALTERNATIVE
CEQA requires that an environmentally superior alternative be identified among the alternatives that are analyzed in the EIR. If the No Project (No Build) Alternative is the environmentally superior EXHIBIT 1
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REVISIONS 3.0
Final Environmental Impact Report – LeBaron Ranch 3.0-87 alternative, an EIR must also identify an environmentally superior alternative among the other alternatives (CEQA Guidelines Section 15126.6(e)(2)). The environmentally superior alternative is that alternative with the least adverse environmental impacts when compared to the proposed Project.
Table 5.0-2 presents a comparison of the alternative Project impacts with those of the proposed Project.
TABLE 5.0-2: COMPARISON OF ALTERNATIVE PROJECT IMPACTS TO THE PROPOSED PROJECT
ENVIRONMENTAL ISSUE
NO PROJECT
(NO BUILD)
ALTERNATIVE
REDUCED
DENSITY
ALTERNATIVE
AGRICULTURE
PROTECTION
ALTERNATIVE
Aesthetics and Visual Resources Less (Best) Slightly Less (3rd Best) Less (2nd Best) Agricultural Resources Less (Best) Equal (3rd Best) Less (2nd Best) Air Quality Less (Best) Less (2nd Best) Equal (3rd Best) Biological Resources Less (Best) Equal (3rd Best) Less (2nd Best) Cultural and Tribal Resources Less (Best) Equal (3rd Best) Less (2nd Best) Geology and Soils Less (Best) Slightly Less (2nd Best) Equal (3rd Best) Greenhouse Gases, Climate Change and Energy Less (Best) Less (2nd Best) Equal (3rd Best) Hazards and Hazardous Materials Less (Best) Equal (2nd 3rd Best) Equal Slightly Less (2nd Best)
Hydrology and Water Quality Less (Best) Slightly Less (3rd Best) Less (2nd Best) Land Use and Population Less (Best) Less (2nd Best) Equal (3rd Best) Noise Less (Best) Slightly Less (2nd Best) Equal (3rd Best) Public Services and Recreation Less (Best) Equal (2nd Best) Equal (3rd Best) Transportation and Circulation Less (Best) Slightly Less (2nd Best) Equal (3rd Best) Utilities Less (Best) Less (2nd Best) Equal (3rd Best)
GREATER = GREATER IMPACT THAN THAT OF THE PROPOSED PROJECT LESS = LESS IMPACT THAN THAT OF THE PROPOSED PROJECT
EQUAL = NO SUBSTANTIAL CHANGE IN IMPACT FROM THAT OF THE PROPOSED PROJECT As shown in the table, the No Project (No Build) Alternative is the environmentally superior alternative. However, as required by CEQA, when the No Project (No Build) Alternative is the environmentally superior alternative, the environmentally superior alternative among the others must be identified. Therefore, the Reduced Density Alternative and Agriculture Protection Alternative both rank higher than the proposed Project. The Reduced Density Alternative would have equal impacts in five (5) areas, slightly less impacts in five (5) areas, and less impacts in nine (9) areas. The Agriculture Protection Alternative would have equal impacts in nine eight (89) areas, slightly less impacts in one (1) area, and less impacts in five (5) areas. Therefore, the Reduced Density Alternative would be the next environmentally superior alternative. It is noted that neither the Agriculture Protection Alternative nor the Reduced Density Alternative fully meet all the Project objectives. See Section 5.4 below for a comparative evaluation of the objectives for each alternative.
6.0 REPORT PREPARERS
No changes were made to Chapter 6.0 of the Draft EIR.
7.0 REFERENCES
No changes were made to Chapter 7.0 of the Draft EIR.
- - I -- -
EXHIBIT 1
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3.0 REVISIONS
3.0-88 Final Environmental Impact Report – LeBaron Ranch This Page Intentionally Left Blank.
EXHIBIT 1
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This document is the Final Mitigation Monitoring and Reporting Program (FMMRP) for the LeBaron Ranch Project (Project). This FMMRP has been prepared pursuant to Section 21081.6 of the California Public Resources Code, which requires public agencies to “adopt a reporting and monitoring program for the changes made to the project or conditions of project approval, adopted in order to mitigate or avoid significant effects on the environment.” A FMMRP is required for the proposed Project because the EIR has identified significant adverse impacts, and measures have been identified to mitigate those impacts.
The numbering of the individual mitigation measures follows the numbering sequence as found in the Draft EIR.
4.1 MITIGATION MONITORING AND REPORTING PROGRAM
The FMMRP, as outlined in the following table, describes mitigation timing, monitoring responsibilities, and compliance verification responsibility for all mitigation measures identified in this Final EIR.
The City of Stockton will be the primary agency responsible for implementing the mitigation measures and will continue to monitor mitigation measures that are required to be implemented during the operation of the Project.
The FMMRP is presented in tabular form on the following pages. The components of the FMMRP are described briefly below:
• Mitigation Measures: The mitigation measures are taken from the Draft EIR in the same order that they appear in that document.
• Mitigation Timing: Identifies at which stage of the project mitigation must be completed. • Monitoring Responsibility: Identifies the agency that is responsible for mitigation monitoring.
• Compliance Verification: This is a space that is available for the monitor to date and initial when the monitoring or mitigation implementation took place.
EXHIBIT 1
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TABLE 4.0-1: MITIGATION MONITORING AND REPORTING PROGRAM
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
AGRICULTURAL RESOURCES
Impact 3.2-1: The proposed
Project would result in the
conversion of Farmlands,
including Prime Farmland and
Farmland of Statewide
Importance, as shown on the
maps prepared pursuant to the
Farmland Mapping and
Monitoring Program of the
California Resources Agency, to
non-agricultural uses
Mitigation Measure 3.2-1: Prior to the conversion of Important Farmland on the Project site, the Project applicant shall participate in the City’s Agricultural Lands Mitigation Program, under which developers of the property shall contribute agricultural mitigation land or shall pay the Agricultural Land Mitigation Fee to the City on a 1:1 basis for each acre of land converted. The Agricultural Land Mitigation Program provides that agricultural mitigation lands shall be dedicated to a qualifying management entity such as the Central Valley Farmland Trust. The fees shall be collected by the City, held in a dedicated account, and then expended by the City to acquire agricultural mitigation land or pay for the monitoring and administrative costs of the program. The fees may also be transferred to a qualifying entity for the same purpose. Payment in the in the City’s Agricultural Lands Mitigation Program would be feasible or effective mitigation for conversion of agricultural land.
Alternatively, participation in the San Joaquin County Multi-Species Habitat Conservation and Open Space Plan (SJMSCP) that results in agricultural land mitigation may also be considered as the functional equivalent of mitigation for the loss of Important Farmland. The SJMSCP requires the payment of a per-acre fee for loss of wildlife habitat, which in San Joaquin County is largely integral with agricultural use. One important use of the fees is the acquisition of conservation easements over agricultural land that are intended to preserve the agricultural use of these lands in order to maintain their biological habitat values.
City of Stockton
Community
Development
Department
San Joaquin
Council of
Governments
Prior to the
conversion of
Important
Farmland on the
Project site
AIR QUALITY
Impact 3.3-1: Project operation
has the potential to result in a
cumulatively considerable net
increase of any criteria pollutant
for which the Project region is in
non-attainment, or conflict or
obstruct implementation of the
District’s air quality plan
Mitigation Measure 3.3-1: The Project applicant(s) shall comply with SJVAPCD Rule 4101, which prohibits emissions of visible air contaminants to the atmosphere and applies to any source operation that emits or may emit air contaminants. Specifically, the project applicant(s), during Project operation, shall not discharge into the atmosphere any air contaminant, other than uncombined water vapor, for a period or periods aggregating more that (3) minutes in any one (1) hour which is: a) As dark or darker in shade as that designated as No. 1 on the Ringelmann Chart, as published by the United States Bureau of Mines; b) Of such opacity as to obscure an observer's view to a degree equal to or greater than the smoke described in Section 5.1 of this rule.
City of Stockton
Community
Development
Department
Prior to the
issuance of the
first building
permit
EXHIBIT 1
1150
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
Mitigation Measure 3.3-2: The Project applicant(s) shall comply with SJVAPCD Rule 4601, during Project construction and operation, which limits VOC emissions from architectural coatings. This rule specifies architectural coatings storage, clean up and labeling requirements. Specific VOC limits for architectural coatings are provided within the Air District’s website, located at: https://ww2.valleyair.org/rules-and-planning/current-district-rules-andregulations/ Mitigation Measure 3.3-3: The Project applicant(s) shall utilize low-VOC paints, equivalent to 10 g/L of ROG, if commercially available.
Mitigation Measure 3.3-4: The City shall educate the Project applicant(s) on the benefits of a VERA. The Project applicant(s) shall consult with the City regarding the results of SJVAPCD’s Rule 9510 process, prior the building permit stage. If emissions reductions associated with mandatory compliance with SJVAPCD’s Rule 9510 are not sufficient to reduce emissions to below the applicable SJVAPCD thresholds of significance for operational ROG, the project applicant shall enter into a VERA with the SJVAPCD, to reduce emissions to below the applicable thresholds of significance, after taking into account any emissions reductions associated with mandatory compliance with SJVAPCD’s Rule 9510. If conditions warrant participation in a VERA, the VERA shall demonstrate a reduction in emissions that meets SJVAPCD’s ROG operational emissions threshold through a process that funds and implements emissions reduction projects within the SJVAB. The types of emission reduction projects that could be funded include replacing old heavyduty trucks with cleaner, more efficient heavy-duty trucks, for example. If a VERA is found to be required, the project applicant shall engage in a discussion with SJVAPCD prior to the adoption of the VERA to ensure that feasible mitigation has been identified to reduce emissions to a less-thansignificant level.
Mitigation Measure 3.3-5: The Project applicant(s) shall provide information regarding the Air District’s Clean Green Yard Machines (CGYM) program, which provides incentive funding for the replacement of existing gas powered lawn and garden equipment, to the home-buyers at time of sale of the housing units by the applicant. More information on the District CGYM program and funding can be found at:
City of Stockton
Community
Development
Department
City of Stockton
Community
Development
Department
City of Stockton
Community
Development
Department
City of Stockton
Community
Development
Department
Prior to the
issuance of the
first building
permit
Prior to the
issuance of the
first building
permit
Prior to the
issuance of the
first building
permit
Prior to
operation of the
Project
EXHIBIT 1
1151
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
https://ww2.valleyair.org/grants/zero-emission-landscaping-equipmentvoucher-program/.
Impact 3.3-2: Proposed Project
construction activities would not
result in a cumulatively
considerable net increase of any
criteria pollutant for which the
Project region is in nonattainment, or conflict or
obstruct implementation of the
District’s air quality plan
Mitigation Measure 3.3-6: Prior to the issuance of a Grading Permit for each phase of the Project, the Project Proponent shall prepare and submit a Dust Control Plan that meets all of the applicable requirements of APCD Rule 8021, Section 6.3, for the review and approval of the APCD Air Pollution Control Officer.
Mitigation Measure 3.3-7: During all construction activities, the Project Proponent shall implement dust control measures, as required by APCD Rules 8011-8081, to limit Visible Dust Emissions to 20% opacity or less. Dust control measures shall include application of water or chemical dust suppressants to unpaved roads and graded areas, covering or stabilization of transported bulk materials, prevention of carryout or trackout of soil materials to public roads, limiting the area subject to soil disturbance, construction of wind barriers, access restrictions to inactive sites as required by the applicable rules.
Mitigation Measure 3.3-8: During all construction activities, the Project proponent shall implement the following dust control practices identified in Tables 6-2 and 6-3 of the GAMAQI (2002).
a. All disturbed areas, including storage piles, which are not being actively utilized for construction purposes, shall be effectively stabilized of dust emissions using water, chemical
stabilizer/suppressant, or vegetative ground cover.
b. All on-site unpaved roads and off-site unpaved access roads shall be effectively stabilized of dust emissions using water or chemical stabilizer/suppressant.
c. All land clearing, grubbing, scraping, excavation, land leveling, grading, cut and fill, and demolition activities shall control fugitive dust emissions by application of water or by presoaking. d. When materials are transported off-site, all material shall be covered, effectively wetted to limit visible dust emissions, or at least six inches of freeboard space from the top of the container shall be maintained. e. All operations shall limit or expeditiously remove the accumulation of mud or dirt from adjacent public streets at least once every 24 hours when operations are occurring. The use of dry rotary brushes is City of Stockton
Community
Development
Department/
APCD Air
Pollution
Control Officer
City of Stockton
Community
Development
Department
City of Stockton
Community
Development
Department
Prior to the
issuance of a
Grading Permit
for each phase of
the Project
During all
construction
activities
During all
construction
activities
EXHIBIT 1
1152
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
expressly prohibited except where preceded or accompanied by sufficient wetting to limit the visible dust emissions. Use of blower devices is expressly forbidden.
f. Following the addition of materials to, or the removal of materials from, the surface of outdoor storage piles, said piles shall be effectively stabilized of fugitive dust emissions utilizing sufficient water or chemical stabilizer/suppressant.
g. Limit traffic speeds on unpaved roads to 5 mph.
h. Install sandbags or other erosion control measures to prevent silt runoff to public roadways from sites with a slope greater than one percent.
Mitigation Measure 3.3-9: Asphalt paving shall be applied in accordance with APCD Rule 4641, the purpose of which is to limit VOC emissions by restricting the application and manufacturing of certain types of asphalt for paving and maintenance operations. This rule applies to the manufacture and use of cutback asphalt, slow cure asphalt and emulsified asphalt for paving and maintenance operations. The Project Applicant shall coordinate with the APCD, prior to Project asphalt paving activities, to ensure all Project asphalt paving would comply with this rule. The Project Applicant shall provide the City of Stockton with evidence of consultation with the APCD, including confirmation of compliance with APCD Rule 4641.
City of Stockton
Community
Development
Department/
APCD
During all
construction
activities
BIOLOGICAL RESOURCES
Impact 3.4-2: The proposed
Project has the potential to have
direct or indirect effects on
special-status reptile and
amphibian species
Mitigation Measure 3.4-1: Prior to commencement of any grading activities, the Project proponent shall seek coverage under the San Joaquin County Multi-Species Habitat Conservation Plan (SJMSCP) to mitigate for habitat impacts to covered special status species. Coverage involves compensation for habitat impacts on covered species through implementation of incidental take and minimization measures (ITMMs) and payment of fees for conversion of lands that may provide habitat for covered special status species. These fees are used to preserve and/or create habitat in preserves to be managed in perpetuity. Obtaining coverage for a Project includes incidental take authorization (permits) under the Endangered Species Act Section 10(a), California Fish and Game Code Section 2081, and the Migratory Bird Treaty Act (MBTA). Coverage under the SJMSCP would fully mitigate all habitat impacts on covered special-status species.
Mitigation Measure 3.4-2: Prior to the commencement of grading activities or other ground disturbing activities on the Project site, the Project applicant City of Stockton
Community
Development
Department
San Joaquin
Council of
Governments
City of Stockton
Community
Prior to
commencement
of any grading
activities
Prior to the
commencement
EXHIBIT 1
1153
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
shall arrange for a qualified biologist to conduct a preconstruction survey for Swainson’s hawks. If no hawks or hawk nests are detected, then construction activities may commence. If Swainson’s hawks or occupied nests are discovered, then the following shall be implemented:
• During the nesting season (February 15 through August 31) and Swainson’s hawks are nesting in or near the Project site, a construction setback of 250 feet of the nest tree (as measured from under the nest) would be required until nesting is complete.
This requirement is consistent with the incidental take and minimization measures (ITMMs) outlined in the SJMSCP. Implementation of this requirement shall occur prior to grading or site clearing activities. SJCOG shall be responsible for monitoring and a qualified biologist shall conduct surveys as required.
Mitigation Measure 3.4-3: Prior to the commencement of grading activities or other ground disturbing activities on the Project site, the Project applicant shall arrange for a qualified biologist to conduct a preconstruction survey for burrowing owls. If no owls or owl nests are detected, then construction activities may commence. If burrowing owls or occupied nests are discovered, then the following shall be implemented:
• During the nesting season (February 1 and August 31) and burrowing owls are present on-site, a 250-foot construction setback from the natal burrow would be required until nesting is complete. • Outside the nesting season (September 1 and January 31) burrowing owls occupying the Project site should be evicted from the Project site by passive relocation as described in the California Department of Fish and Game’s Staff Report on Burrowing Owls (Oct., 1995) These requirements are consistent with the incidental take and minimization measures (ITMMs) outlined in the SJMSCP. Implementation of this requirement shall occur prior to grading or site clearing activities. SJCOG shall be responsible for monitoring and a qualified biologist shall conduct surveys and relocate owls as required.
Mitigation Measure 3.4-4: Prior to the commencement of grading activities or other ground disturbing activities on the Project site, the Project applicant shall arrange for a qualified biologist to conduct a preconstruction survey for Development
Department
San Joaquin
Council of
Governments
City of Stockton
Community
Development
Department
San Joaquin
Council of
Governments
City of Stockton
Community
Development
of grading
activities or other
ground
disturbing
activities on the
Project site
Prior to the
commencement
of grading
activities or other
ground
disturbing
activities on the
Project site
Prior to the
commencement
of grading
EXHIBIT 1
1154
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
tricolored blackbird. If no tricolored blackbird or tricolored blackbird nests are detected, then construction activities may commence. If tricolored blackbird or occupied nests are discovered, then the following shall be implemented:
• A setback of 500 feet from colonial nesting areas shall be established and maintained during the nesting season for the period encompassing nest building and continuing until fledglings leave nests. This setback applies whenever construction or other grounddisturbing activities must begin during the nesting season in the presence of nests which are known to be occupied. Setbacks shall be marked by brightly colored temporary fencing.
This requirement is consistent with the incidental take and minimization measures (ITMMs) outlined in the SJMSCP. Implementation of this requirement shall occur prior to grading or site clearing activities. SJCOG shall be responsible for monitoring and a qualified biologist shall conduct surveys as required.
Department
San Joaquin
Council of
Governments
activities or other
ground
disturbing
activities on the
Project site
Impact 3.4-3: The proposed
Project has the potential to have
direct or indirect effects on
special-status bird species
Implement Mitigation Measure 3.4-1. See Mitigation
Measure 3.4-1
See Mitigation
Measure 3.4-1
Impact 3.4-4: The proposed
Project has the potential to result
in direct or indirect effects on
special-status mammal species.
Implement Mitigation Measure 3.4-1. See Mitigation
Measure 3.4-1
See Mitigation
Measure 3.4-1
Impact 3.4-11: The proposed
Project has the potential to
conflict with local policies or
ordinances protecting biological
resources, such as a tree
preservation policy or ordinance
Mitigation Measure 3.4-5: If removal of any oak tree on the project site is required, the project applicant or contractor shall hire a certified arborist to survey the oak trees proposed for removal to determine if they are Heritage Trees as defined in Stockton Municipal Code Chapter 16.130. The survey shall occur prior to site disturbance. The arborist report with its findings shall be submitted to the City’s Community Development Department. If Heritage Trees are determined to exist on the property, removal of any such tree shall require a permit to be issued by the City in accordance with Stockton Municipal Code Chapter 16.130. The permittee shall comply with all permit conditions, including tree replacement at specified ratios.
City of Stockton
Community
Development
Department
If removal of any
oak tree on the
project site is
required
CULTURAL AND TRIBAL RESOURCES
Impact 3.5-2: Project
implementation has the potential
Mitigation Measure 3.5-1: Prior to any ground-disturbing activities on the Project site, the Developer shall retain a qualified archaeologist and native City of Stockton
Community
Prior to any
ground
EXHIBIT 1
1155
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
to cause a substantial adverse
change to a significant
archaeological resource, as
defined in CEQA Guidelines
§15064.5, or a significant tribal
cultural resource, as defined in
Public Resources Code §21074
American monitor to conduct pre-construction worker cultural resources sensitivity training. The training session shall focus on the recognition of the types of historical and cultural, including Native American, resources that could be encountered; procedures to be followed if resources are found, including who to contact and appropriate avoidance measures until the find(s) can be properly evaluated; and pertinent laws protecting these resources. Training shall be scheduled at the discretion of the Project applicant in consultation with the City. The Developer shall be responsible for ensuring that all workers requiring training are in attendance. Those in attendance shall be recorded, with records maintained on-site. Any new workers that were not part of the initial training shall be required to undergo a new training session.
Mitigation Measure 3.5-2: If any cultural resources, including prehistoric or historic artifacts, or other indications of archaeological resources, are found during grading and construction activities during any phase of the Project, all work shall be halted immediately within a 200-foot radius of the discovery until an archaeologist meeting the Secretary of the Interior's Professional Qualifications Standards in prehistoric or historical archaeology, as appropriate, has evaluated the find(s).
Work shall not continue at the discovery site until the archaeologist conducts sufficient research and data collection to make a determination that the resource is either 1) not cultural in origin; or 2) not potentially significant or eligible for listing on the NRHP or CRHR; or 3) not a significant Public Trust Resource.
If Native American resources are identified, a Native American monitor, following the Guidelines for Monitors/Consultants of Native American Cultural, Religious, and Burial Sites established by the Native American Heritage Commission, may also be required and, if required, shall be retained at the Project applicant’s expense.
If the discovery proves to be significant under CEQA and cannot be avoided by the Project, additional work such as data recovery excavation may be warranted to mitigate any significant impacts. Mitigation could include avoidance, preservation in place, or the scientific removal, analysis, reporting, and curation of any recovered cultural materials. Construction shall not resume in the area until appropriate protection and preservation measures are in place and have been approved by the Community Development
Department,
qualified
archaeologist,
and Native
American
monitor
City of Stockton
Community
Development
Department,
qualified
archaeologist
disturbance
activities
If any cultural
resources,
including
prehistoric or
historic artifacts,
or other
indications of
archaeological
resources, are
found during
grading and
construction
activities during
any phase of the
Project
EXHIBIT 1
1156
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
Development Director or designee, and the qualified archaeologist states in writing that the proposed construction activities would not significantly damage any archaeological or tribal cultural resources.
GEOLOGY AND SOILS
Impact 3.6-5: The proposed
Project has the potential to
directly or indirectly destroy a
unique geological feature or
paleontological resource
Mitigation Measure 3.6-1: If any paleontological resources are found during grading and construction activities of the Project, all work shall be halted immediately within a 200-foot radius of the discovery, the City of Stockton Community Development Director shall be notified, and a professional vertebrate paleontologist (as defined by the Society for Vertebrate Paleontology) shall be contacted immediately to evaluate the find.
The paleontologist shall have the authority to stop or divert construction, as necessary. Documentation and treatment of the discovery shall occur in accordance with Society of Vertebrate Paleontology standards.
Work shall not continue at the discovery site until the professional vertebrate paleontologist evaluates the find pursuant to the CEQA Guidelines and makes a determination regarding the significance of the resource and identifies recommendations for conservation of the resource, including, but not limited to, preserving in place or relocating on the Project site, if feasible, or collecting the resource to the extent feasible and documenting the find with the University of California Museum of Paleontology.
City of Stockton
Community
Development
Department,
qualified
paleontologist
If any
paleontological
resources are
found during
grading and
construction
activities of the
Project
HAZARDS AND HAZARDOUS MATERIALS
Impact 3.8-1: Project
implementation has the potential
to create a significant hazard
through the routine transport,
use, or disposal of hazardous
materials or through the
reasonably foreseeable upset
and accident conditions
involving the release of
hazardous materials into the
environment
Mitigation Measure 3.8-1: Prior to initiating construction or grading activities, the construction contractor shall be provided with project-specific training regarding the identification and handling of hazardous materials and agency notification procedures. In the event that contaminated soils are encountered during construction, the Project applicant shall prepare and implement a Soils Management Plan (SMP) to provide guidance for the proper handling, onsite management, and disposal of impacted soil that might be encountered during construction activities. The SMP shall establish management practices for handling of contaminated soils and other hazardous materials during construction. The SMP would include, but is not limited to, an outline of how Project construction crews would identify, handle, and dispose of potentially contaminated soil; the qualifications of the appropriately trained professionals that would monitor soil conditions and conduct soil sampling during construction; laboratory testing; anticipated field screening methods and appropriate regulatory limits to be applied to determine proper handling and disposal; and requirements for documenting San Joaquin
County
Department of
Environmental
Health
Prior to initiating
construction or
grading activities
EXHIBIT 1
1157
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
and reporting incidents of encountered contaminants, such as documenting locations of occurrence, sampling results, and reporting actions taken to dispose of contaminated materials. In the event that potentially contaminated soils were encountered within the footprint of construction, soils would be tested and stockpiled. The SMP shall be submitted to the San Joaquin County Department of Environmental Health for review and approval. The approved SMP shall be posted and maintained onsite during construction activities and all construction personnel shall acknowledge that they have reviewed and understand the plan.
Mitigation Measure 3.8-2: Prior to initiation of any ground disturbance activities, a soil sampling and analysis workplan shall be submitted to the San Joaquin County Department of Environmental Health for approval. The sampling and analysis plan shall meet the requirements of the Department of Toxic Substances Control Interim Guidance for Sampling Agricultural Properties (2008), and the County Department of Environmental Resources Recommended Soil and Groundwater Sampling for Underground Tank Investigations (2013). Evenly distributed soil samples shall be conducted throughout the Development Area for analysis of pesticides and heavy metals. The samples shall be submitted for laboratory analysis of pesticides and heavy metals per DTSC and EPA protocols. The results of the soil sampling shall be submitted to the City of Stockton for review.
If the sampling results indicate the presence of agrichemicals that exceed commercial screening levels, a removal action workplan shall be prepared in coordination with San Joaquin County Environmental Health Department.
The removal action workplan shall include a detailed engineering plan for conducting the removal action, a description of the onsite contamination, the goals to be achieved by the removal action, and any alternative removal options that were considered and rejected and the basis for that rejection. A no further action letter shall be issued by San Joaquin County Environmental Health Department upon completion of the removal action. The removal action shall be deemed complete when the confirmation samples exhibit concentrations below the commercial screening levels, which will be established by the agencies.
City of Stockton
Community
Development
Department
Prior to initiation
of any ground
disturbance
activities
EXHIBIT 1
1158
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
HYDROLOGY AND WATER QUALITY
Impact 3.9-4: The proposed
Project has the potential to, in a
flood hazard, tsunami, or seiche
zones, risk release of pollutants
due to Project inundation
Mitigation Measure 3.9-1: All residential and non-residential structures within the Project site shall meet the urban level of flood protection, as required by the State of California Central Valley Flood Protection Act of 2008 (Senate Bill 5). Finished floor elevations of proposed residential structures shall be elevated to or above the prescribed 200-year floodplain elevation, or proposed nonresidential structures shall be floodproofed, consistent with the City of Stockton’s Criteria for Development in 200-year Floodplains and City of Stockton Municipal Code. Code compliance shall be documented in materials prepared by licensed professionals and submitted to the Community Development Director prior to issuance of grading permits.
City of Stockton
Community
Development
Director
Prior to issuance
of grading
permits
NOISE
Impact 3.11-1: The proposed
Project has the potential to
generate a substantial temporary
or permanent increase in
ambient noise levels in the
vicinity of the Project in excess of
standards established in the local
general plan or noise ordinance,
or applicable standards of other
agencies
Mitigation Measure 3.11-1: To reduce potential construction noise impacts during Project construction, the following multi-part mitigation measure shall be implemented for the Project:
• All construction equipment powered by internal combustion engines shall be properly muffled and maintained.
• Quiet construction equipment, particularly air compressors, shall be selected whenever possible.
• All stationery noise-generating construction equipment such as generators or air compressors shall be located as far as is practical from existing residences. In addition, the Project contractor shall place such stationary construction equipment so that emitted noise is directed away from sensitive receptors nearest the Project site. • Unnecessary idling of internal combustion engines shall be prohibited.
• The construction contractor shall, to the maximum extent practical, locate on-site equipment staging areas so as to maximize the distance between construction-related noise sources and noisesensitive receptors nearest the Project site during all Project construction.
• Construction shall be limited to 7:00 a.m. to 10:00 p.m. • Staging areas on the Project site shall be located in areas that maximize, to the extent feasible, the distance between staging activity and sensitive receptors.
These requirements shall be noted on the Project improvement plans as part City of Stockton
Building and
Life Safety
Division
Prior to the
approval of
Project
improvement
plans
EXHIBIT 1
1159
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
of the submittal for grading or building permit, whichever shall occur first, to the City of Stockton Building and Life Safety Division.
TRANSPORTATION AND CIRCULATION
Impact 3.13-1: Project
implementation would conflict
with or be inconsistent with
CEQA Guidelines Section
15064.3, subdivision (b).
Mitigation Measure 3.13-1: The Project applicant shall work with the City of Stockton to implement feasible Transportation Demand Management (TDM) strategies, which would decrease the VMT generated by the Project.
Specific potential TDM strategies include, but are not limited to, the following:
• Coordinate with public transit agencies, including improving San Joaquin Rapid Transit District (RTD) regarding transit service connecting workers with existing and future residential developments;
• Coordinate with San Joaquin RTD regarding the potential for increasing service on Hopper Route 93;
• TDM coordinator for large employers, such as the LUSD, should the school site be developed;
• Provide carpool and/or vanpool incentive programs;
• Provide on-site lockers and showers for workers who take alternative transportation, such as those employed by the LUSD, should the school site be developed;
• Promote walking and bicycling for employees who live and/or work in the area through the preparation of an Active Transportation Plan; • Incentivize the use of alternative travel modes for travel within the project site through shared use of e-bikes and e-scooters; • Allow flexible work hours and schedule classes to reduce arrivals/departures during peak hours; and
• Employer coordination to SJCOG’s DIBs program for workers.
The TDM Plan shall be submitted to the City for review, and the effectiveness of the TDM Plan shall be evaluated, monitored, and revised, if necessary. The TDM Plan shall include the TDM strategies which will be implemented during the lifetime of the proposed Project and shall outline the anticipated effectiveness of the strategies to achieve the home-based work VMT per worker target identified in the City’s TIAG. The effectiveness of the TDM Plan may be monitored through annual surveys to determine employee travel mode split and travel distance for home-based work trips, and/or the implementation of technology to determine the amount of traffic generated by and home-based work miles traveled by employees, which shall be City of Stockton
Community
Development
Department
San Joaquin
RTD
Prior to
certificates of
occupancy/verifi
cation of TDM
programs/
ongoing annual
monitoring
EXHIBIT 1
1160
ENVIRONMENTAL IMPACT MITIGATION MEASURE
MONITORING
RESPONSIBILITY
TIMING
VERIFICATION
(DATE/INITIALS)
determined in coordination with the City and included as part of the TDM Plan. Monitoring of the effectiveness of the TDM Plan shall be mandatory at least for first three year after implementation of the TDMs to see how well the TDM Plan is performing, and to add new TDMs, if some measures become feasible later.
UTILITIES AND SERVICE SYSTEMS
Impact 3.14-2: The proposed
Project would not result in a
determination by the
wastewater treatment and/or
collection provider which serves
or may serve the Project that is
does not have adequate capacity
to serve the Project’s projected
demand in addition to the
provider’s existing commitments
Mitigation Measure 3.14-1: Prior to occupancy of any building that would require wastewater treatment services, the Project proponent shall secure from the City of Stockton Municipal Utilities Department with a request for utility service adequate wastewater treatment capacity/allocation.
City of Stockton
Community
Development
Department
Prior to
occupancy of any
building that
would require
wastewater
treatment
services
Impact 3.14-6: The proposed
Project would not require or
result in the construction of new
storm water drainage facilities or
expansion of existing facilities,
the construction of which could
cause significant environmental
effects
Mitigation Measure 3.14-2: Prior to the issuance of a building or grading permit, the project applicant shall submit a drainage plan to the City of Stockton for review and approval. The plan shall include an engineered Storm Water Quality Control Criteria Plan (SWQCCP) that demonstrates attainment of pre-project runoff requirements prior to release at the Bear Creek outfall.
The plan shall describe the volume reduction measures and treatment controls, which may include, but not limited to vegetated swale, infiltration basin, rain garden, or bioretention, consistent with the Federal Clean Water Act, the City’s Stormwater Quality Control Criteria Plan, the adopted municipal stormwater National Pollutant Discharge Elimination System (NPDES) permit and the City's corresponding Stormwater Management Plan.
City of Stockton
Community
Development
Department
Prior to the
issuance of a
building or
grading permit
EXHIBIT 1
1161
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EXHIBIT 1
1162
APPENDIX B
Air Quality, Greenhouse Gas, and Energy Appendices
EXHIBIT 1
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City of Stockton - Lebaron Ranch v3 Detailed Report
Table of Contents
1. Basic Project Information
1.1. Basic Project Information
1.2. Land Use Types
1.3. User-Selected Emission Reduction Measures by Emissions Sector
2. Emissions Summary
2.1. Construction Emissions Compared Against Thresholds
2.2. Construction Emissions by Year, Unmitigated
2.3. Construction Emissions by Year, Mitigated
2.4. Operations Emissions Compared Against Thresholds
2.5. Operations Emissions by Sector, Unmitigated
2.6. Operations Emissions by Sector, Mitigated
3. Construction Emissions Details
3.1. Site Preparation (2025) - Unmitigated
3.2. Site Preparation (2025) - Mitigated
EXHIBIT 1
1164
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3.3. Grading (2025) - Unmitigated
3.4. Grading (2025) - Mitigated
3.5. Building Construction (2025) - Unmitigated
3.6. Building Construction (2025) - Mitigated
3.7. Building Construction (2026) - Unmitigated
3.8. Building Construction (2026) - Mitigated
3.9. Building Construction (2027) - Unmitigated
3.10. Building Construction (2027) - Mitigated
3.11. Paving (2027) - Unmitigated
3.12. Paving (2027) - Mitigated
3.13. Paving (2028) - Unmitigated
3.14. Paving (2028) - Mitigated
3.15. Architectural Coating (2027) - Unmitigated
3.16. Architectural Coating (2027) - Mitigated
4. Operations Emissions Details
4.1. Mobile Emissions by Land Use
4.1.1. Unmitigated
EXHIBIT 1
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4.1.2. Mitigated
4.2. Energy
4.2.1. Electricity Emissions By Land Use - Unmitigated
4.2.2. Electricity Emissions By Land Use - Mitigated
4.2.3. Natural Gas Emissions By Land Use - Unmitigated
4.2.4. Natural Gas Emissions By Land Use - Mitigated
4.3. Area Emissions by Source
4.3.1. Unmitigated
4.3.2. Mitigated
4.4. Water Emissions by Land Use
4.4.1. Unmitigated
4.4.2. Mitigated
4.5. Waste Emissions by Land Use
4.5.1. Unmitigated
4.5.2. Mitigated
4.6. Refrigerant Emissions by Land Use
4.6.1. Unmitigated
EXHIBIT 1
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4.6.2. Mitigated
4.7. Offroad Emissions By Equipment Type
4.7.1. Unmitigated
4.7.2. Mitigated
4.8. Stationary Emissions By Equipment Type
4.8.1. Unmitigated
4.8.2. Mitigated
4.9. User Defined Emissions By Equipment Type
4.9.1. Unmitigated
4.9.2. Mitigated
4.10. Soil Carbon Accumulation By Vegetation Type
4.10.1. Soil Carbon Accumulation By Vegetation Type - Unmitigated
4.10.2. Above and Belowground Carbon Accumulation by Land Use Type - Unmitigated
4.10.3. Avoided and Sequestered Emissions by Species - Unmitigated
4.10.4. Soil Carbon Accumulation By Vegetation Type - Mitigated
4.10.5. Above and Belowground Carbon Accumulation by Land Use Type - Mitigated
4.10.6. Avoided and Sequestered Emissions by Species - Mitigated EXHIBIT 1
1167
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5. Activity Data
5.1. Construction Schedule
5.2. Off-Road Equipment
5.2.1. Unmitigated
5.2.2. Mitigated
5.3. Construction Vehicles
5.3.1. Unmitigated
5.3.2. Mitigated
5.4. Vehicles
5.4.1. Construction Vehicle Control Strategies
5.5. Architectural Coatings
5.6. Dust Mitigation
5.6.1. Construction Earthmoving Activities
5.6.2. Construction Earthmoving Control Strategies
5.7. Construction Paving
5.8. Construction Electricity Consumption and Emissions Factors
5.9. Operational Mobile Sources
EXHIBIT 1
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5.9.1. Unmitigated
5.9.2. Mitigated
5.10. Operational Area Sources
5.10.1. Hearths
5.10.1.1. Unmitigated
5.10.1.2. Mitigated
5.10.2. Architectural Coatings
5.10.3. Landscape Equipment
5.10.4. Landscape Equipment - Mitigated
5.11. Operational Energy Consumption
5.11.1. Unmitigated
5.11.2. Mitigated
5.12. Operational Water and Wastewater Consumption
5.12.1. Unmitigated
5.12.2. Mitigated
5.13. Operational Waste Generation
5.13.1. Unmitigated
EXHIBIT 1
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5.13.2. Mitigated
5.14. Operational Refrigeration and Air Conditioning Equipment
5.14.1. Unmitigated
5.14.2. Mitigated
5.15. Operational Off-Road Equipment
5.15.1. Unmitigated
5.15.2. Mitigated
5.16. Stationary Sources
5.16.1. Emergency Generators and Fire Pumps
5.16.2. Process Boilers
5.17. User Defined
5.18. Vegetation
5.18.1. Land Use Change
5.18.1.1. Unmitigated
5.18.1.2. Mitigated
5.18.1. Biomass Cover Type
5.18.1.1. Unmitigated
EXHIBIT 1
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5.18.1.2. Mitigated
5.18.2. Sequestration
5.18.2.1. Unmitigated
5.18.2.2. Mitigated
6. Climate Risk Detailed Report
6.1. Climate Risk Summary
6.2. Initial Climate Risk Scores
6.3. Adjusted Climate Risk Scores
6.4. Climate Risk Reduction Measures
7. Health and Equity Details
7.1. CalEnviroScreen 4.0 Scores
7.2. Healthy Places Index Scores
7.3. Overall Health & Equity Scores
7.4. Health & Equity Measures
7.5. Evaluation Scorecard
7.6. Health & Equity Custom Measures
8. User Changes to Default Data
EXHIBIT 1
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1. Basic Project Information
1.1. Basic Project Information
Data Field Value
Project Name City of Stockton - Lebaron Ranch v3
Construction Start Date 1/1/2025
Operational Year 2028
Lead Agency —
Land Use Scale Project/site
Analysis Level for Defaults County
Windspeed (m/s) 3.40
Precipitation (days) 0.40
Location 38.05434444439149, -121.30877263887623
County San Joaquin
City Unincorporated
Air District San Joaquin Valley APCD
Air Basin San Joaquin Valley
TAZ 2149
EDFZ 4
Electric Utility Pacific Gas & Electric Company
Gas Utility Pacific Gas & Electric
App Version 2022.1.1.21
1.2. Land Use Types
Land Use Subtype Size Unit Lot Acreage Building Area (sq ft) Landscape Area (sq ft)
Special Landscape
Area (sq ft)
Population Description
EXHIBIT 1
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Single Family
Housing
1,217 Dwelling Unit 192 2,373,150 14,254,547 0.00 3,931 Low Density Residential
Apartments Low
Rise
194 Dwelling Unit 9.50 205,640 0.00 0.00 627 High Density Residential
City Park 30.7 Acre 30.7 0.00 0.00 0.00 — Park and Open Space Areas
Other Asphalt
Surfaces
4.50 Acre 4.50 0.00 0.00 0.00 — Storm Basin
1.3. User-Selected Emission Reduction Measures by Emissions Sector Sector # Measure Title
Area Sources LL-1 Replace Gas Powered Landscape Equipment with Zero-Emission Landscape Equipment
Area Sources AS-2 Use Low-VOC Paints
2. Emissions Summary
2.1. Construction Emissions Compared Against Thresholds Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Un/Mit. TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 4.40 166 29.7 46.7 0.06 1.23 9.37 10.6 1.14 3.69 4.83 — 12,817 12,817 0.43 0.88 31.6 13,114 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 4.02 166 31.7 40.2 0.06 1.37 19.8 21.2 1.26 10.1 11.4 — 12,228 12,228 0.34 0.90 0.82 12,504 Average
Daily
(Max)
— — — — — — — — — — — — — — — — — —
-------------------
EXHIBIT 1
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Unmit. 2.84 46.4 17.0 26.6 0.04 0.62 7.11 7.73 0.57 2.83 3.40 — 8,172 8,172 0.21 0.61 8.72 8,367 Annual
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 0.52 8.46 3.09 4.86 0.01 0.11 1.30 1.41 0.10 0.52 0.62 — 1,353 1,353 0.03 0.10 1.44 1,385
2.2. Construction Emissions by Year, Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Year TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily -
Summer
(Max)
— — — — — — — — — — — — — — — — — —
2025 4.19 3.68 29.7 45.0 0.06 1.23 9.37 10.6 1.14 3.69 4.83 — 12,013 12,013 0.43 0.85 31.6 12,310 2026 3.96 3.47 16.4 42.5 0.05 0.44 6.01 6.44 0.41 1.46 1.86 — 11,824 11,824 0.28 0.84 28.3 12,109 2027 4.40 166 16.6 46.7 0.06 0.42 6.98 7.39 0.39 1.68 2.07 — 12,817 12,817 0.29 0.88 28.4 13,114 Daily -
Winter
(Max)
— — — — — — — — — — — — — — — — — —
2025 4.01 3.47 31.7 38.8 0.06 1.37 19.8 21.2 1.26 10.1 11.4 — 11,502 11,502 0.32 0.85 0.82 11,765 2026 3.81 3.30 17.1 36.8 0.05 0.44 6.01 6.44 0.41 1.46 1.86 — 11,324 11,324 0.31 0.85 0.73 11,587 2027 4.02 166 17.4 40.2 0.06 0.42 6.98 7.39 0.39 1.68 2.07 — 12,228 12,228 0.34 0.90 0.74 12,504 2028 0.87 0.85 6.67 10.4 0.01 0.26 0.13 0.38 0.24 0.03 0.26 — 1,630 1,630 0.06 0.02 0.01 1,636 Average
Daily
— — — — — — — — — — — — — — — — — —
2025 2.84 2.44 17.0 25.1 0.04 0.62 7.11 7.73 0.57 2.83 3.40 — 6,488 6,488 0.20 0.35 5.35 6,602 2026 2.71 2.36 12.0 26.6 0.04 0.31 4.29 4.60 0.29 1.04 1.33 — 8,172 8,172 0.21 0.61 8.72 8,367 2027 2.20 46.4 10.2 22.6 0.03 0.27 3.55 3.83 0.25 0.86 1.11 — 6,712 6,712 0.17 0.48 6.33 6,865 2028 0.09 0.09 0.69 1.08 < 0.005 0.03 0.01 0.04 0.02 < 0.005 0.03 — 169 169 0.01 < 0.005 0.02 170 Annual — — — — — — — — — — — — — — — — — —
2025 0.52 0.44 3.09 4.57 0.01 0.11 1.30 1.41 0.10 0.52 0.62 — 1,074 1,074 0.03 0.06 0.89 1,093 -------------------
EXHIBIT 1
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2026 0.50 0.43 2.19 4.86 0.01 0.06 0.78 0.84 0.05 0.19 0.24 — 1,353 1,353 0.03 0.10 1.44 1,385 2027 0.40 8.46 1.85 4.12 0.01 0.05 0.65 0.70 0.05 0.16 0.20 — 1,111 1,111 0.03 0.08 1.05 1,137 2028 0.02 0.02 0.13 0.20 < 0.005 < 0.005 < 0.005 0.01 < 0.005 < 0.005 0.01 — 28.0 28.0 < 0.005 < 0.005 < 0.005 28.2
2.3. Construction Emissions by Year, Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Year TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily -
Summer
(Max)
— — — — — — — — — — — — — — — — — —
2025 4.19 3.68 29.7 45.0 0.06 1.23 9.37 10.6 1.14 3.69 4.83 — 12,013 12,013 0.43 0.85 31.6 12,310 2026 3.96 3.47 16.4 42.5 0.05 0.44 6.01 6.44 0.41 1.46 1.86 — 11,824 11,824 0.28 0.84 28.3 12,109 2027 4.40 166 16.6 46.7 0.06 0.42 6.98 7.39 0.39 1.68 2.07 — 12,817 12,817 0.29 0.88 28.4 13,114 Daily -
Winter
(Max)
— — — — — — — — — — — — — — — — — —
2025 4.01 3.47 31.7 38.8 0.06 1.37 19.8 21.2 1.26 10.1 11.4 — 11,502 11,502 0.32 0.85 0.82 11,765 2026 3.81 3.30 17.1 36.8 0.05 0.44 6.01 6.44 0.41 1.46 1.86 — 11,324 11,324 0.31 0.85 0.73 11,587 2027 4.02 166 17.4 40.2 0.06 0.42 6.98 7.39 0.39 1.68 2.07 — 12,228 12,228 0.34 0.90 0.74 12,504 2028 0.87 0.85 6.67 10.4 0.01 0.26 0.13 0.38 0.24 0.03 0.26 — 1,630 1,630 0.06 0.02 0.01 1,636 Average
Daily
— — — — — — — — — — — — — — — — — —
2025 2.84 2.44 17.0 25.1 0.04 0.62 7.11 7.73 0.57 2.83 3.40 — 6,488 6,488 0.20 0.35 5.35 6,602 2026 2.71 2.36 12.0 26.6 0.04 0.31 4.29 4.60 0.29 1.04 1.33 — 8,172 8,172 0.21 0.61 8.72 8,367 2027 2.20 46.4 10.2 22.6 0.03 0.27 3.55 3.83 0.25 0.86 1.11 — 6,712 6,712 0.17 0.48 6.33 6,865 2028 0.09 0.09 0.69 1.08 < 0.005 0.03 0.01 0.04 0.02 < 0.005 0.03 — 169 169 0.01 < 0.005 0.02 170 Annual — — — — — — — — — — — — — — — — — —
2025 0.52 0.44 3.09 4.57 0.01 0.11 1.30 1.41 0.10 0.52 0.62 — 1,074 1,074 0.03 0.06 0.89 1,093 2026 0.50 0.43 2.19 4.86 0.01 0.06 0.78 0.84 0.05 0.19 0.24 — 1,353 1,353 0.03 0.10 1.44 1,385 -------------------
EXHIBIT 1
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2027 0.40 8.46 1.85 4.12 0.01 0.05 0.65 0.70 0.05 0.16 0.20 — 1,111 1,111 0.03 0.08 1.05 1,137 2028 0.02 0.02 0.13 0.20 < 0.005 < 0.005 < 0.005 0.01 < 0.005 < 0.005 0.01 — 28.0 28.0 < 0.005 < 0.005 < 0.005 28.2
2.4. Operations Emissions Compared Against Thresholds
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Un/Mit. TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 57.4 85.3 46.1 420 0.86 1.45 69.0 70.5 1.40 17.6 19.0 — 100,457 100,457 5.44 3.85 252 101,992 Mit. 50.1 74.8 45.3 340 0.86 1.41 69.0 70.4 1.37 17.6 18.9 — 100,264 100,264 5.44 3.85 252 101,799 %
Reduced
13% 12% 2% 19% < 0.5% 3% — < 0.5% 2% — < 0.5% — < 0.5% < 0.5% < 0.5% < 0.5% — < 0.5% Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 46.5 74.6 50.8 304 0.80 1.41 69.0 70.4 1.37 17.6 18.9 — 94,437 94,437 5.91 4.15 24.5 95,847 Mit. 46.5 71.1 50.8 304 0.80 1.41 69.0 70.4 1.37 17.6 18.9 — 94,437 94,437 5.91 4.15 24.5 95,847 %
Reduced
— 5% — — — — — — — — — — — — — — — —
Average
Daily
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 50.2 78.2 48.8 340 0.82 1.43 69.0 70.4 1.39 17.5 18.9 — 95,899 95,899 5.68 4.01 119 97,356 Mit. 46.6 71.2 48.4 301 0.82 1.41 69.0 70.4 1.37 17.5 18.9 — 95,805 95,805 5.68 4.01 119 97,261 %
Reduced
7% 9% 1% 12% < 0.5% 1% — < 0.5% 1% — < 0.5% — < 0.5% < 0.5% < 0.5% — — < 0.5% Annual
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 9.16 14.3 8.90 62.1 0.15 0.26 12.6 12.9 0.25 3.20 3.46 — 15,877 15,877 0.94 0.66 19.7 16,118 Mit. 8.50 13.0 8.84 54.9 0.15 0.26 12.6 12.8 0.25 3.20 3.45 — 15,862 15,862 0.94 0.66 19.7 16,103 -------------------
EXHIBIT 1
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%
Reduced
7% 9% 1% 12% < 0.5% 1% — < 0.5% 1% — < 0.5% — < 0.5% < 0.5% < 0.5% < 0.5% — < 0.5%
2.5. Operations Emissions by Sector, Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Sector TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Mobile 48.9 45.7 35.6 335 0.80 0.63 69.0 69.6 0.59 17.6 18.1 — 81,329 81,329 3.27 3.69 233 82,745 Area 7.37 39.0 0.76 80.2 < 0.005 0.04 — 0.04 0.03 — 0.03 — 214 214 0.01 < 0.005 — 215 Energy 1.13 0.57 9.68 4.12 0.06 0.78 — 0.78 0.78 — 0.78 — 18,571 18,571 2.10 0.15 — 18,668 Water — — — — — — — — — — — — 342 342 0.06 0.01 — 346
Waste — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Refrig. — — — — — — — — — — — — — — — — 18.5 18.5
Total 57.4 85.3 46.1 420 0.86 1.45 69.0 70.5 1.40 17.6 19.0 — 100,457 100,457 5.44 3.85 252 101,992 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Mobile 45.4 42.0 41.1 300 0.74 0.63 69.0 69.6 0.59 17.6 18.1 — 75,524 75,524 3.75 4.00 6.05 76,815 Area — 32.0 — — — — — — — — — — — — — — — —
Energy 1.13 0.57 9.68 4.12 0.06 0.78 — 0.78 0.78 — 0.78 — 18,571 18,571 2.10 0.15 — 18,668 Water — — — — — — — — — — — — 342 342 0.06 0.01 — 346
Waste — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Refrig. — — — — — — — — — — — — — — — — 18.5 18.5
Total 46.5 74.6 50.8 304 0.80 1.41 69.0 70.4 1.37 17.6 18.9 — 94,437 94,437 5.91 4.15 24.5 95,847 Average
Daily
— — — — — — — — — — — — — — — — — —
Mobile 45.4 42.1 38.7 296 0.75 0.63 69.0 69.6 0.59 17.5 18.1 — 76,880 76,880 3.52 3.86 101 78,218 -------------------
EXHIBIT 1
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Area 3.63 35.5 0.37 39.5 < 0.005 0.02 — 0.02 0.01 — 0.01 — 106 106 < 0.005 < 0.005 — 106 Energy 1.13 0.57 9.68 4.12 0.06 0.78 — 0.78 0.78 — 0.78 — 18,571 18,571 2.10 0.15 — 18,668 Water — — — — — — — — — — — — 342 342 0.06 0.01 — 346
Waste — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Refrig. — — — — — — — — — — — — — — — — 18.5 18.5
Total 50.2 78.2 48.8 340 0.82 1.43 69.0 70.4 1.39 17.5 18.9 — 95,899 95,899 5.68 4.01 119 97,356 Annual — — — — — — — — — — — — — — — — — —
Mobile 8.29 7.69 7.07 54.1 0.14 0.11 12.6 12.7 0.11 3.20 3.31 — 12,728 12,728 0.58 0.64 16.7 12,950 Area 0.66 6.48 0.07 7.22 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 17.5 17.5 < 0.005 < 0.005 — 17.5 Energy 0.21 0.10 1.77 0.75 0.01 0.14 — 0.14 0.14 — 0.14 — 3,075 3,075 0.35 0.02 — 3,091 Water — — — — — — — — — — — — 56.7 56.7 0.01 < 0.005 — 57.3 Waste — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Refrig. — — — — — — — — — — — — — — — — 3.06 3.06
Total 9.16 14.3 8.90 62.1 0.15 0.26 12.6 12.9 0.25 3.20 3.46 — 15,877 15,877 0.94 0.66 19.7 16,118
2.6. Operations Emissions by Sector, Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Sector TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Mobile 48.9 45.7 35.6 335 0.80 0.63 69.0 69.6 0.59 17.6 18.1 — 81,329 81,329 3.27 3.69 233 82,745 Area — 28.5 — — — — — — — — — — — — — — — —
Energy 1.13 0.57 9.68 4.12 0.06 0.78 — 0.78 0.78 — 0.78 — 18,593 18,593 2.11 0.15 — 18,689 Water — — — — — — — — — — — — 342 342 0.06 0.01 — 346
Waste — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Refrig. — — — — — — — — — — — — — — — — 18.5 18.5
Total 50.1 74.8 45.3 340 0.86 1.41 69.0 70.4 1.37 17.6 18.9 — 100,264 100,264 5.44 3.85 252 101,799 -------------------
EXHIBIT 1
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Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Mobile 45.4 42.0 41.1 300 0.74 0.63 69.0 69.6 0.59 17.6 18.1 — 75,524 75,524 3.75 4.00 6.05 76,815 Area — 28.5 — — — — — — — — — — — — — — — —
Energy 1.13 0.57 9.68 4.12 0.06 0.78 — 0.78 0.78 — 0.78 — 18,571 18,571 2.10 0.15 — 18,668 Water — — — — — — — — — — — — 342 342 0.06 0.01 — 346
Waste — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Refrig. — — — — — — — — — — — — — — — — 18.5 18.5
Total 46.5 71.1 50.8 304 0.80 1.41 69.0 70.4 1.37 17.6 18.9 — 94,437 94,437 5.91 4.15 24.5 95,847 Average
Daily
— — — — — — — — — — — — — — — — — —
Mobile 45.4 42.1 38.7 296 0.75 0.63 69.0 69.6 0.59 17.5 18.1 — 76,880 76,880 3.52 3.86 101 78,218 Area — 28.5 — — — — — — — — — — — — — — — —
Energy 1.13 0.57 9.68 4.12 0.06 0.78 — 0.78 0.78 — 0.78 — 18,582 18,582 2.11 0.15 — 18,678 Water — — — — — — — — — — — — 342 342 0.06 0.01 — 346
Waste — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Refrig. — — — — — — — — — — — — — — — — 18.5 18.5
Total 46.6 71.2 48.4 301 0.82 1.41 69.0 70.4 1.37 17.5 18.9 — 95,805 95,805 5.68 4.01 119 97,261 Annual — — — — — — — — — — — — — — — — — —
Mobile 8.29 7.69 7.07 54.1 0.14 0.11 12.6 12.7 0.11 3.20 3.31 — 12,728 12,728 0.58 0.64 16.7 12,950 Area — 5.20 — — — — — — — — — — — — — — — —
Energy 0.21 0.10 1.77 0.75 0.01 0.14 — 0.14 0.14 — 0.14 — 3,076 3,076 0.35 0.02 — 3,092 Water — — — — — — — — — — — — 56.7 56.7 0.01 < 0.005 — 57.3 Waste — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Refrig. — — — — — — — — — — — — — — — — 3.06 3.06
Total 8.50 13.0 8.84 54.9 0.15 0.26 12.6 12.8 0.25 3.20 3.45 — 15,862 15,862 0.94 0.66 19.7 16,103 EXHIBIT 1
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3. Construction Emissions Details
3.1. Site Preparation (2025) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
3.94 3.31 31.6 30.2 0.05 1.37 — 1.37 1.26 — 1.26 — 5,295 5,295 0.21 0.04 — 5,314 Dust
From
Material
Movement
— — — — — — 19.7 19.7 — 10.1 10.1 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.65 0.54 5.20 4.96 0.01 0.22 — 0.22 0.21 — 0.21 — 870 870 0.04 0.01 — 873 Dust
From
Material
Movement
— — — — — — 3.23 3.23 — 1.66 1.66 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.12 0.10 0.95 0.91 < 0.005 0.04 — 0.04 0.04 — 0.04 — 144 144 0.01 < 0.005 — 145 -------------------
EXHIBIT 1
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Dust
From
Material
Movement
— — — — — — 0.59 0.59 — 0.30 0.30 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.07 0.07 0.07 0.72 0.00 0.00 0.15 0.15 0.00 0.03 0.03 — 146 146 < 0.005 0.01 0.02 148 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.01 0.01 0.01 0.12 0.00 0.00 0.02 0.02 0.00 0.01 0.01 — 24.6 24.6 < 0.005 < 0.005 0.04 25.0 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.02 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 4.08 4.08 < 0.005 < 0.005 0.01 4.14 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.2. Site Preparation (2025) - Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e -------------------
Onsite — — — — — — — — — — — — — — — — — —
EXHIBIT 1
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Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
3.94 3.31 31.6 30.2 0.05 1.37 — 1.37 1.26 — 1.26 — 5,295 5,295 0.21 0.04 — 5,314 Dust
From
Material
Movement
— — — — — — 19.7 19.7 — 10.1 10.1 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.65 0.54 5.20 4.96 0.01 0.22 — 0.22 0.21 — 0.21 — 870 870 0.04 0.01 — 873 Dust
From
Material
Movement
— — — — — — 3.23 3.23 — 1.66 1.66 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.12 0.10 0.95 0.91 < 0.005 0.04 — 0.04 0.04 — 0.04 — 144 144 0.01 < 0.005 — 145 Dust
From
Material
Movement
— — — — — — 0.59 0.59 — 0.30 0.30 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
EXHIBIT 1
1182
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 20 / 86
Daily, — — — — — — — — — — — — — — — — — —
Summer
(Max)
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.07 0.07 0.07 0.72 0.00 0.00 0.15 0.15 0.00 0.03 0.03 — 146 146 < 0.005 0.01 0.02 148 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.01 0.01 0.01 0.12 0.00 0.00 0.02 0.02 0.00 0.01 0.01 — 24.6 24.6 < 0.005 < 0.005 0.04 25.0 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.02 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 4.08 4.08 < 0.005 < 0.005 0.01 4.14 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.3. Grading (2025) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
3.80 3.20 29.7 28.3 0.06 1.23 — 1.23 1.14 — 1.14 — 6,599 6,599 0.27 0.05 — 6,622 -------------------
EXHIBIT 1
1183
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 21 / 86
Dust — — — — — — 9.20 9.20 — 3.65 3.65 — — — — — — —
From
Material
Movement
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
3.80 3.20 29.7 28.3 0.06 1.23 — 1.23 1.14 — 1.14 — 6,599 6,599 0.27 0.05 — 6,622 Dust
From
Material
Movement
— — — — — — 9.20 9.20 — 3.65 3.65 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.63 0.53 4.88 4.65 0.01 0.20 — 0.20 0.19 — 0.19 — 1,085 1,085 0.04 0.01 — 1,088 Dust
From
Material
Movement
— — — — — — 1.51 1.51 — 0.60 0.60 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.11 0.10 0.89 0.85 < 0.005 0.04 — 0.04 0.03 — 0.03 — 180 180 0.01 < 0.005 — 180 Dust
From
Material
Movement
— — — — — — 0.28 0.28 — 0.11 0.11 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 EXHIBIT 1
1184
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 22 / 86
Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.09 0.08 0.06 1.04 0.00 0.00 0.17 0.17 0.00 0.04 0.04 — 185 185 0.01 0.01 0.69 188 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.08 0.08 0.08 0.83 0.00 0.00 0.17 0.17 0.00 0.04 0.04 — 167 167 < 0.005 0.01 0.02 169 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.01 0.01 0.01 0.14 0.00 0.00 0.03 0.03 0.00 0.01 0.01 — 28.2 28.2 < 0.005 < 0.005 0.05 28.6 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.03 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 — 4.66 4.66 < 0.005 < 0.005 0.01 4.73 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.4. Grading (2025) - Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
------------------- — — — — — — — — — — — — — — — — — — EXHIBIT 1
1185
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 23 / 86
Off-Road
Equipment
3.80 3.20 29.7 28.3 0.06 1.23 — 1.23 1.14 — 1.14 — 6,599 6,599 0.27 0.05 — 6,622 Dust
From
Material
Movement
— — — — — — 9.20 9.20 — 3.65 3.65 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
3.80 3.20 29.7 28.3 0.06 1.23 — 1.23 1.14 — 1.14 — 6,599 6,599 0.27 0.05 — 6,622 Dust
From
Material
Movement
— — — — — — 9.20 9.20 — 3.65 3.65 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.63 0.53 4.88 4.65 0.01 0.20 — 0.20 0.19 — 0.19 — 1,085 1,085 0.04 0.01 — 1,088 Dust
From
Material
Movement
— — — — — — 1.51 1.51 — 0.60 0.60 — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.11 0.10 0.89 0.85 < 0.005 0.04 — 0.04 0.03 — 0.03 — 180 180 0.01 < 0.005 — 180 Dust
From
Material
Movement
— — — — — — 0.28 0.28 — 0.11 0.11 — — — — — — —
EXHIBIT 1
1186
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 24 / 86
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.09 0.08 0.06 1.04 0.00 0.00 0.17 0.17 0.00 0.04 0.04 — 185 185 0.01 0.01 0.69 188 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.08 0.08 0.08 0.83 0.00 0.00 0.17 0.17 0.00 0.04 0.04 — 167 167 < 0.005 0.01 0.02 169 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.01 0.01 0.01 0.14 0.00 0.00 0.03 0.03 0.00 0.01 0.01 — 28.2 28.2 < 0.005 < 0.005 0.05 28.6 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.03 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 — 4.66 4.66 < 0.005 < 0.005 0.01 4.73 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.5. Building Construction (2025) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e -------------------
Onsite — — — — — — — — — — — — — — — — — —
EXHIBIT 1
1187
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 25 / 86
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
1.35 1.13 10.4 13.0 0.02 0.43 — 0.43 0.40 — 0.40 — 2,398 2,398 0.10 0.02 — 2,406 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
1.35 1.13 10.4 13.0 0.02 0.43 — 0.43 0.40 — 0.40 — 2,398 2,398 0.10 0.02 — 2,406 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.52 0.43 4.03 5.03 0.01 0.17 — 0.17 0.15 — 0.15 — 924 924 0.04 0.01 — 928 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.09 0.08 0.73 0.92 < 0.005 0.03 — 0.03 0.03 — 0.03 — 153 153 0.01 < 0.005 — 154 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Worker 2.62 2.42 1.63 30.1 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 5,345 5,345 0.25 0.20 19.9 5,432 Vendor 0.23 0.14 5.31 1.81 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,270 4,270 0.08 0.63 11.7 4,473 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 EXHIBIT 1
1188
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 26 / 86
Daily, — — — — — — — — — — — — — — — — — —
Winter
(Max)
Worker 2.44 2.21 2.18 23.9 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 4,830 4,830 0.14 0.20 0.52 4,894 Vendor 0.21 0.13 5.66 1.84 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,274 4,274 0.08 0.63 0.30 4,465 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.94 0.86 0.70 9.44 0.00 0.00 1.87 1.87 0.00 0.44 0.44 — 1,909 1,909 0.05 0.08 3.31 1,936 Vendor 0.09 0.05 2.13 0.71 0.01 0.02 0.44 0.47 0.02 0.12 0.15 — 1,647 1,647 0.03 0.24 1.95 1,722 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker 0.17 0.16 0.13 1.72 0.00 0.00 0.34 0.34 0.00 0.08 0.08 — 316 316 0.01 0.01 0.55 321 Vendor 0.02 0.01 0.39 0.13 < 0.005 < 0.005 0.08 0.09 < 0.005 0.02 0.03 — 273 273 0.01 0.04 0.32 285 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.6. Building Construction (2025) - Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
1.35 1.13 10.4 13.0 0.02 0.43 — 0.43 0.40 — 0.40 — 2,398 2,398 0.10 0.02 — 2,406 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
-------------------
EXHIBIT 1
1189
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 27 / 86
Off-Road
Equipment
1.35 1.13 10.4 13.0 0.02 0.43 — 0.43 0.40 — 0.40 — 2,398 2,398 0.10 0.02 — 2,406 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.52 0.43 4.03 5.03 0.01 0.17 — 0.17 0.15 — 0.15 — 924 924 0.04 0.01 — 928 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.09 0.08 0.73 0.92 < 0.005 0.03 — 0.03 0.03 — 0.03 — 153 153 0.01 < 0.005 — 154 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Worker 2.62 2.42 1.63 30.1 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 5,345 5,345 0.25 0.20 19.9 5,432 Vendor 0.23 0.14 5.31 1.81 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,270 4,270 0.08 0.63 11.7 4,473 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 2.44 2.21 2.18 23.9 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 4,830 4,830 0.14 0.20 0.52 4,894 Vendor 0.21 0.13 5.66 1.84 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,274 4,274 0.08 0.63 0.30 4,465 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.94 0.86 0.70 9.44 0.00 0.00 1.87 1.87 0.00 0.44 0.44 — 1,909 1,909 0.05 0.08 3.31 1,936 Vendor 0.09 0.05 2.13 0.71 0.01 0.02 0.44 0.47 0.02 0.12 0.15 — 1,647 1,647 0.03 0.24 1.95 1,722 EXHIBIT 1
1190
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 28 / 86
Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker 0.17 0.16 0.13 1.72 0.00 0.00 0.34 0.34 0.00 0.08 0.08 — 316 316 0.01 0.01 0.55 321 Vendor 0.02 0.01 0.39 0.13 < 0.005 < 0.005 0.08 0.09 < 0.005 0.02 0.03 — 273 273 0.01 0.04 0.32 285 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.7. Building Construction (2026) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
1.28 1.07 9.85 13.0 0.02 0.38 — 0.38 0.35 — 0.35 — 2,397 2,397 0.10 0.02 — 2,405 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
1.28 1.07 9.85 13.0 0.02 0.38 — 0.38 0.35 — 0.35 — 2,397 2,397 0.10 0.02 — 2,405 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.91 0.77 7.04 9.26 0.02 0.27 — 0.27 0.25 — 0.25 — 1,712 1,712 0.07 0.01 — 1,718 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
-------------------
EXHIBIT 1
1191
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 29 / 86
Off-Road
Equipment
0.17 0.14 1.28 1.69 < 0.005 0.05 — 0.05 0.05 — 0.05 — 283 283 0.01 < 0.005 — 284 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Worker 2.45 2.26 1.46 27.8 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 5,233 5,233 0.10 0.19 18.0 5,310 Vendor 0.22 0.13 5.08 1.71 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,193 4,193 0.08 0.63 10.3 4,394 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 2.31 2.10 1.83 22.0 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 4,730 4,730 0.13 0.20 0.47 4,794 Vendor 0.21 0.13 5.41 1.77 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,197 4,197 0.08 0.63 0.27 4,388 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 1.64 1.50 1.17 16.1 0.00 0.00 3.47 3.47 0.00 0.81 0.81 — 3,463 3,463 0.08 0.14 5.54 3,514 Vendor 0.16 0.10 3.78 1.24 0.02 0.04 0.82 0.87 0.04 0.23 0.27 — 2,996 2,996 0.06 0.45 3.18 3,135 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker 0.30 0.27 0.21 2.94 0.00 0.00 0.63 0.63 0.00 0.15 0.15 — 573 573 0.01 0.02 0.92 582 Vendor 0.03 0.02 0.69 0.23 < 0.005 0.01 0.15 0.16 0.01 0.04 0.05 — 496 496 0.01 0.07 0.53 519 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.8. Building Construction (2026) - Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e -------------------
EXHIBIT 1
1192
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 30 / 86
Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
1.28 1.07 9.85 13.0 0.02 0.38 — 0.38 0.35 — 0.35 — 2,397 2,397 0.10 0.02 — 2,405 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
1.28 1.07 9.85 13.0 0.02 0.38 — 0.38 0.35 — 0.35 — 2,397 2,397 0.10 0.02 — 2,405 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.91 0.77 7.04 9.26 0.02 0.27 — 0.27 0.25 — 0.25 — 1,712 1,712 0.07 0.01 — 1,718 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.17 0.14 1.28 1.69 < 0.005 0.05 — 0.05 0.05 — 0.05 — 283 283 0.01 < 0.005 — 284 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Worker 2.45 2.26 1.46 27.8 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 5,233 5,233 0.10 0.19 18.0 5,310 Vendor 0.22 0.13 5.08 1.71 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,193 4,193 0.08 0.63 10.3 4,394 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 EXHIBIT 1
1193
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 31 / 86
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 2.31 2.10 1.83 22.0 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 4,730 4,730 0.13 0.20 0.47 4,794 Vendor 0.21 0.13 5.41 1.77 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,197 4,197 0.08 0.63 0.27 4,388 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 1.64 1.50 1.17 16.1 0.00 0.00 3.47 3.47 0.00 0.81 0.81 — 3,463 3,463 0.08 0.14 5.54 3,514 Vendor 0.16 0.10 3.78 1.24 0.02 0.04 0.82 0.87 0.04 0.23 0.27 — 2,996 2,996 0.06 0.45 3.18 3,135 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker 0.30 0.27 0.21 2.94 0.00 0.00 0.63 0.63 0.00 0.15 0.15 — 573 573 0.01 0.02 0.92 582 Vendor 0.03 0.02 0.69 0.23 < 0.005 0.01 0.15 0.16 0.01 0.04 0.05 — 496 496 0.01 0.07 0.53 519 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.9. Building Construction (2027) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
1.23 1.03 9.39 12.9 0.02 0.34 — 0.34 0.31 — 0.31 — 2,397 2,397 0.10 0.02 — 2,405 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
-------------------
EXHIBIT 1
1194
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 32 / 86
Off-Road
Equipment
1.23 1.03 9.39 12.9 0.02 0.34 — 0.34 0.31 — 0.31 — 2,397 2,397 0.10 0.02 — 2,405 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.67 0.56 5.11 7.04 0.01 0.18 — 0.18 0.17 — 0.17 — 1,304 1,304 0.05 0.01 — 1,309 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.12 0.10 0.93 1.28 < 0.005 0.03 — 0.03 0.03 — 0.03 — 216 216 0.01 < 0.005 — 217 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Worker 2.34 2.15 1.28 25.9 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 5,150 5,150 0.09 0.19 16.2 5,225 Vendor 0.22 0.13 4.85 1.64 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,106 4,106 0.08 0.63 9.04 4,305 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 2.04 1.98 1.66 20.4 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 4,657 4,657 0.13 0.20 0.42 4,720 Vendor 0.21 0.13 5.18 1.70 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,109 4,109 0.08 0.63 0.23 4,300 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 1.11 1.08 0.80 11.4 0.00 0.00 2.64 2.64 0.00 0.62 0.62 — 2,597 2,597 0.06 0.11 3.79 2,635 Vendor 0.12 0.07 2.76 0.90 0.02 0.03 0.63 0.66 0.03 0.17 0.21 — 2,234 2,234 0.04 0.34 2.12 2,340 EXHIBIT 1
1195
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Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker 0.20 0.20 0.15 2.08 0.00 0.00 0.48 0.48 0.00 0.11 0.11 — 430 430 0.01 0.02 0.63 436 Vendor 0.02 0.01 0.50 0.17 < 0.005 0.01 0.11 0.12 0.01 0.03 0.04 — 370 370 0.01 0.06 0.35 387 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.10. Building Construction (2027) - Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
1.23 1.03 9.39 12.9 0.02 0.34 — 0.34 0.31 — 0.31 — 2,397 2,397 0.10 0.02 — 2,405 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
1.23 1.03 9.39 12.9 0.02 0.34 — 0.34 0.31 — 0.31 — 2,397 2,397 0.10 0.02 — 2,405 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.67 0.56 5.11 7.04 0.01 0.18 — 0.18 0.17 — 0.17 — 1,304 1,304 0.05 0.01 — 1,309 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
-------------------
EXHIBIT 1
1196
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 34 / 86
Off-Road
Equipment
0.12 0.10 0.93 1.28 < 0.005 0.03 — 0.03 0.03 — 0.03 — 216 216 0.01 < 0.005 — 217 Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Worker 2.34 2.15 1.28 25.9 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 5,150 5,150 0.09 0.19 16.2 5,225 Vendor 0.22 0.13 4.85 1.64 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,106 4,106 0.08 0.63 9.04 4,305 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 2.04 1.98 1.66 20.4 0.00 0.00 4.85 4.85 0.00 1.14 1.14 — 4,657 4,657 0.13 0.20 0.42 4,720 Vendor 0.21 0.13 5.18 1.70 0.03 0.06 1.15 1.21 0.06 0.32 0.38 — 4,109 4,109 0.08 0.63 0.23 4,300 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 1.11 1.08 0.80 11.4 0.00 0.00 2.64 2.64 0.00 0.62 0.62 — 2,597 2,597 0.06 0.11 3.79 2,635 Vendor 0.12 0.07 2.76 0.90 0.02 0.03 0.63 0.66 0.03 0.17 0.21 — 2,234 2,234 0.04 0.34 2.12 2,340 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker 0.20 0.20 0.15 2.08 0.00 0.00 0.48 0.48 0.00 0.11 0.11 — 430 430 0.01 0.02 0.63 436 Vendor 0.02 0.01 0.50 0.17 < 0.005 0.01 0.11 0.12 0.01 0.03 0.04 — 370 370 0.01 0.06 0.35 387 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.11. Paving (2027) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e -------------------
EXHIBIT 1
1197
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 35 / 86
Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.88 0.74 6.94 9.95 0.01 0.30 — 0.30 0.27 — 0.27 — 1,511 1,511 0.06 0.01 — 1,516 Paving — 0.12 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.15 0.13 1.18 1.69 < 0.005 0.05 — 0.05 0.05 — 0.05 — 257 257 0.01 < 0.005 — 258 Paving — 0.02 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.03 0.02 0.22 0.31 < 0.005 0.01 — 0.01 0.01 — 0.01 — 42.6 42.6 < 0.005 < 0.005 — 42.7 Paving — < 0.005 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.05 0.05 0.04 0.53 0.00 0.00 0.13 0.13 0.00 0.03 0.03 — 121 121 < 0.005 0.01 0.01 123 EXHIBIT 1
1198
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 36 / 86
Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.01 0.01 0.01 0.09 0.00 0.00 0.02 0.02 0.00 0.01 0.01 — 21.1 21.1 < 0.005 < 0.005 0.03 21.4 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.02 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 3.49 3.49 < 0.005 < 0.005 0.01 3.54 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.12. Paving (2027) - Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.88 0.74 6.94 9.95 0.01 0.30 — 0.30 0.27 — 0.27 — 1,511 1,511 0.06 0.01 — 1,516 Paving — 0.12 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
-------------------
EXHIBIT 1
1199
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 37 / 86
Off-Road 0.15 0.13 1.18 1.69 < 0.005 0.05 — 0.05 0.05 — 0.05 — 257 257 0.01 < 0.005 — 258 Equipment
Paving — 0.02 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.03 0.02 0.22 0.31 < 0.005 0.01 — 0.01 0.01 — 0.01 — 42.6 42.6 < 0.005 < 0.005 — 42.7 Paving — < 0.005 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.05 0.05 0.04 0.53 0.00 0.00 0.13 0.13 0.00 0.03 0.03 — 121 121 < 0.005 0.01 0.01 123 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.01 0.01 0.01 0.09 0.00 0.00 0.02 0.02 0.00 0.01 0.01 — 21.1 21.1 < 0.005 < 0.005 0.03 21.4 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.02 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 3.49 3.49 < 0.005 < 0.005 0.01 3.54 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 EXHIBIT 1
1200
City of Stockton - Lebaron Ranch v3 Detailed Report, 12/11/2023 38 / 86
3.13. Paving (2028) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.82 0.69 6.63 9.91 0.01 0.26 — 0.26 0.24 — 0.24 — 1,511 1,511 0.06 0.01 — 1,516 Paving — 0.12 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.08 0.07 0.69 1.03 < 0.005 0.03 — 0.03 0.02 — 0.02 — 157 157 0.01 < 0.005 — 157 Paving — 0.01 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.02 0.01 0.13 0.19 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 25.9 25.9 < 0.005 < 0.005 — 26.0 Paving — < 0.005 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
-------------------
EXHIBIT 1
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Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.05 0.04 0.04 0.49 0.00 0.00 0.13 0.13 0.00 0.03 0.03 — 119 119 < 0.005 0.01 0.01 120 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.01 < 0.005 < 0.005 0.05 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 — 12.6 12.6 < 0.005 < 0.005 0.02 12.8 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.01 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 2.09 2.09 < 0.005 < 0.005 < 0.005 2.12 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.14. Paving (2028) - Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.82 0.69 6.63 9.91 0.01 0.26 — 0.26 0.24 — 0.24 — 1,511 1,511 0.06 0.01 — 1,516 Paving — 0.12 — — — — — — — — — — — — — — — —
-------------------
EXHIBIT 1
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Onsite 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 truck
Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.08 0.07 0.69 1.03 < 0.005 0.03 — 0.03 0.02 — 0.02 — 157 157 0.01 < 0.005 — 157 Paving — 0.01 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.02 0.01 0.13 0.19 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 25.9 25.9 < 0.005 < 0.005 — 26.0 Paving — < 0.005 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.05 0.04 0.04 0.49 0.00 0.00 0.13 0.13 0.00 0.03 0.03 — 119 119 < 0.005 0.01 0.01 120 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.01 < 0.005 < 0.005 0.05 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 — 12.6 12.6 < 0.005 < 0.005 0.02 12.8 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.01 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 2.09 2.09 < 0.005 < 0.005 < 0.005 2.12 EXHIBIT 1
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Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.15. Architectural Coating (2027) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.14 0.11 0.83 1.13 < 0.005 0.02 — 0.02 0.02 — 0.02 — 134 134 0.01 < 0.005 — 134 Architect
ural
Coatings
— 162 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.14 0.11 0.83 1.13 < 0.005 0.02 — 0.02 0.02 — 0.02 — 134 134 0.01 < 0.005 — 134 Architect
ural
Coatings
— 162 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.04 0.03 0.23 0.31 < 0.005 0.01 — 0.01 < 0.005 — < 0.005 — 36.6 36.6 < 0.005 < 0.005 — 36.7 -------------------
EXHIBIT 1
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Architect — 44.4 — — — — — — — — — — — — — — — —
ural
Coatings
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.01 0.01 0.04 0.06 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 6.06 6.06 < 0.005 < 0.005 — 6.08 Architect
ural
Coatings
— 8.10 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.47 0.43 0.26 5.17 0.00 0.00 0.97 0.97 0.00 0.23 0.23 — 1,030 1,030 0.02 0.04 3.23 1,045 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.41 0.40 0.33 4.07 0.00 0.00 0.97 0.97 0.00 0.23 0.23 — 931 931 0.03 0.04 0.08 944 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.11 0.11 0.08 1.15 0.00 0.00 0.27 0.27 0.00 0.06 0.06 — 262 262 0.01 0.01 0.38 265 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
EXHIBIT 1
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Worker 0.02 0.02 0.01 0.21 0.00 0.00 0.05 0.05 0.00 0.01 0.01 — 43.3 43.3 < 0.005 < 0.005 0.06 43.9 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
3.16. Architectural Coating (2027) - Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.14 0.11 0.83 1.13 < 0.005 0.02 — 0.02 0.02 — 0.02 — 134 134 0.01 < 0.005 — 134 Architect
ural
Coatings
— 162 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.14 0.11 0.83 1.13 < 0.005 0.02 — 0.02 0.02 — 0.02 — 134 134 0.01 < 0.005 — 134 Architect
ural
Coatings
— 162 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.04 0.03 0.23 0.31 < 0.005 0.01 — 0.01 < 0.005 — < 0.005 — 36.6 36.6 < 0.005 < 0.005 — 36.7 -------------------
EXHIBIT 1
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Architect
Coatings
— 44.4 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
0.01 0.01 0.04 0.06 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 6.06 6.06 < 0.005 < 0.005 — 6.08 Architect
ural
Coatings
— 8.10 — — — — — — — — — — — — — — — —
Onsite
truck
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.47 0.43 0.26 5.17 0.00 0.00 0.97 0.97 0.00 0.23 0.23 — 1,030 1,030 0.02 0.04 3.23 1,045 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.41 0.40 0.33 4.07 0.00 0.00 0.97 0.97 0.00 0.23 0.23 — 931 931 0.03 0.04 0.08 944 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.11 0.11 0.08 1.15 0.00 0.00 0.27 0.27 0.00 0.06 0.06 — 262 262 0.01 0.01 0.38 265 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker 0.02 0.02 0.01 0.21 0.00 0.00 0.05 0.05 0.00 0.01 0.01 — 43.3 43.3 < 0.005 < 0.005 0.06 43.9 EXHIBIT 1
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Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00
4. Operations Emissions Details
4.1. Mobile Emissions by Land Use
4.1.1. Unmitigated
Mobile source emissions results are presented in Sections 2.6. No further detailed breakdown of emissions is available.
4.1.2. Mitigated
Mobile source emissions results are presented in Sections 2.5. No further detailed breakdown of emissions is available.
4.2. Energy
4.2.1. Electricity Emissions By Land Use - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 5,799 5,799 0.94 0.11 — 5,856
Apartme
nts
Low Rise
— — — — — — — — — — — — 482 482 0.08 0.01 — 487
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 6,280 6,280 1.02 0.12 — 6,343 EXHIBIT 1
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Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 5,799 5,799 0.94 0.11 — 5,856
Apartme
nts
Low Rise
— — — — — — — — — — — — 482 482 0.08 0.01 — 487
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 6,280 6,280 1.02 0.12 — 6,343 Annual — — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 960 960 0.16 0.02 — 970
Apartme
nts
Low Rise
— — — — — — — — — — — — 79.8 79.8 0.01 < 0.005 — 80.6
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 1,040 1,040 0.17 0.02 — 1,050
4.2.2. Electricity Emissions By Land Use - Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
EXHIBIT 1
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Single
Family
Housing
— — — — — — — — — — — — 5,817 5,817 0.94 0.11 — 5,875
Apartme
nts
Low Rise
— — — — — — — — — — — — 485 485 0.08 0.01 — 490
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 6,302 6,302 1.02 0.12 — 6,364 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 5,799 5,799 0.94 0.11 — 5,856
Apartme
nts
Low Rise
— — — — — — — — — — — — 482 482 0.08 0.01 — 487
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 6,280 6,280 1.02 0.12 — 6,343 Annual — — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 962 962 0.16 0.02 — 971
Apartme
nts
Low Rise
— — — — — — — — — — — — 80.0 80.0 0.01 < 0.005 — 80.8
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 EXHIBIT 1
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Other — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Asphalt
Surfaces
Total — — — — — — — — — — — — 1,042 1,042 0.17 0.02 — 1,052
4.2.3. Natural Gas Emissions By Land Use - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
1.05 0.52 8.94 3.80 0.06 0.72 — 0.72 0.72 — 0.72 — 11,346 11,346 1.00 0.02 — 11,377 Apartme
nts
Low Rise
0.09 0.04 0.74 0.32 < 0.005 0.06 — 0.06 0.06 — 0.06 — 945 945 0.08 < 0.005 — 948 City Park 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Total 1.13 0.57 9.68 4.12 0.06 0.78 — 0.78 0.78 — 0.78 — 12,291 12,291 1.09 0.02 — 12,325 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
1.05 0.52 8.94 3.80 0.06 0.72 — 0.72 0.72 — 0.72 — 11,346 11,346 1.00 0.02 — 11,377 Apartme
nts
Low Rise
0.09 0.04 0.74 0.32 < 0.005 0.06 — 0.06 0.06 — 0.06 — 945 945 0.08 < 0.005 — 948 City Park 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 EXHIBIT 1
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Other 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Asphalt
Surfaces
Total 1.13 0.57 9.68 4.12 0.06 0.78 — 0.78 0.78 — 0.78 — 12,291 12,291 1.09 0.02 — 12,325 Annual — — — — — — — — — — — — — — — — — —
Single
Family
Housing
0.19 0.10 1.63 0.69 0.01 0.13 — 0.13 0.13 — 0.13 — 1,878 1,878 0.17 < 0.005 — 1,884 Apartme
nts
Low Rise
0.02 0.01 0.14 0.06 < 0.005 0.01 — 0.01 0.01 — 0.01 — 156 156 0.01 < 0.005 — 157 City Park 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Total 0.21 0.10 1.77 0.75 0.01 0.14 — 0.14 0.14 — 0.14 — 2,035 2,035 0.18 < 0.005 — 2,041
4.2.4. Natural Gas Emissions By Land Use - Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
1.05 0.52 8.94 3.80 0.06 0.72 — 0.72 0.72 — 0.72 — 11,346 11,346 1.00 0.02 — 11,377 Apartme
nts
Low Rise
0.09 0.04 0.74 0.32 < 0.005 0.06 — 0.06 0.06 — 0.06 — 945 945 0.08 < 0.005 — 948 City Park 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 EXHIBIT 1
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Total 1.13 0.57 9.68 4.12 0.06 0.78 — 0.78 0.78 — 0.78 — 12,291 12,291 1.09 0.02 — 12,325 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
1.05 0.52 8.94 3.80 0.06 0.72 — 0.72 0.72 — 0.72 — 11,346 11,346 1.00 0.02 — 11,377 Apartme
nts
Low Rise
0.09 0.04 0.74 0.32 < 0.005 0.06 — 0.06 0.06 — 0.06 — 945 945 0.08 < 0.005 — 948 City Park 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Total 1.13 0.57 9.68 4.12 0.06 0.78 — 0.78 0.78 — 0.78 — 12,291 12,291 1.09 0.02 — 12,325 Annual — — — — — — — — — — — — — — — — — —
Single
Family
Housing
0.19 0.10 1.63 0.69 0.01 0.13 — 0.13 0.13 — 0.13 — 1,878 1,878 0.17 < 0.005 — 1,884 Apartme
nts
Low Rise
0.02 0.01 0.14 0.06 < 0.005 0.01 — 0.01 0.01 — 0.01 — 156 156 0.01 < 0.005 — 157 City Park 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Total 0.21 0.10 1.77 0.75 0.01 0.14 — 0.14 0.14 — 0.14 — 2,035 2,035 0.18 < 0.005 — 2,041
4.3. Area Emissions by Source
4.3.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Source TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e -------------------
EXHIBIT 1
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Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Consum
er
Products
— 27.6 — — — — — — — — — — — — — — — —
Architect
ural
Coatings
— 4.44 — — — — — — — — — — — — — — — —
Landsca
pe
Equipme
nt
7.37 6.98 0.76 80.2 < 0.005 0.04 — 0.04 0.03 — 0.03 — 214 214 0.01 < 0.005 — 215 Total 7.37 39.0 0.76 80.2 < 0.005 0.04 — 0.04 0.03 — 0.03 — 214 214 0.01 < 0.005 — 215 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Consum
er
Products
— 27.6 — — — — — — — — — — — — — — — —
Architect
ural
Coatings
— 4.44 — — — — — — — — — — — — — — — —
Total — 32.0 — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Consum
er
Products
— 5.04 — — — — — — — — — — — — — — — —
Architect
ural
Coatings
— 0.81 — — — — — — — — — — — — — — — —
Landsca
pe
Equipme
nt
0.66 0.63 0.07 7.22 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 17.5 17.5 < 0.005 < 0.005 — 17.5 Total 0.66 6.48 0.07 7.22 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 17.5 17.5 < 0.005 < 0.005 — 17.5 EXHIBIT 1
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4.3.2. Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Source TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Consum
er
Products
— 27.6 — — — — — — — — — — — — — — — —
Architect
ural
Coatings
— 0.90 — — — — — — — — — — — — — — — —
Total — 28.5 — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Consum
er
Products
— 27.6 — — — — — — — — — — — — — — — —
Architect
ural
Coatings
— 0.90 — — — — — — — — — — — — — — — —
Total — 28.5 — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Consum
er
Products
— 5.04 — — — — — — — — — — — — — — — —
Architect
ural
Coatings
— 0.16 — — — — — — — — — — — — — — — —
Total — 5.20 — — — — — — — — — — — — — — — —
-------------------
EXHIBIT 1
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4.4. Water Emissions by Land Use
4.4.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 328 328 0.05 0.01 — 331
Apartme
nts
Low Rise
— — — — — — — — — — — — 14.4 14.4 < 0.005 < 0.005 — 14.5 City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 342 342 0.06 0.01 — 346
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 328 328 0.05 0.01 — 331
Apartme
nts
Low Rise
— — — — — — — — — — — — 14.4 14.4 < 0.005 < 0.005 — 14.5 City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 342 342 0.06 0.01 — 346
EXHIBIT 1
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Annual — — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 54.3 54.3 0.01 < 0.005 — 54.9
Apartme
nts
Low Rise
— — — — — — — — — — — — 2.38 2.38 < 0.005 < 0.005 — 2.40 City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 56.7 56.7 0.01 < 0.005 — 57.3
4.4.2. Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 328 328 0.05 0.01 — 331
Apartme
nts
Low Rise
— — — — — — — — — — — — 14.4 14.4 < 0.005 < 0.005 — 14.5 City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 342 342 0.06 0.01 — 346
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
EXHIBIT 1
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Single
Family
Housing
— — — — — — — — — — — — 328 328 0.05 0.01 — 331
Apartme
nts
Low Rise
— — — — — — — — — — — — 14.4 14.4 < 0.005 < 0.005 — 14.5 City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 342 342 0.06 0.01 — 346
Annual — — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 54.3 54.3 0.01 < 0.005 — 54.9
Apartme
nts
Low Rise
— — — — — — — — — — — — 2.38 2.38 < 0.005 < 0.005 — 2.40 City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 56.7 56.7 0.01 < 0.005 — 57.3
4.5. Waste Emissions by Land Use
4.5.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
EXHIBIT 1
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Single
Family
Housing
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Apartme
nts
Low Rise
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Apartme
nts
Low Rise
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Annual — — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Apartme
nts
Low Rise
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 EXHIBIT 1
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Other — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Asphalt
Surfaces
Total — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
4.5.2. Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Apartme
nts
Low Rise
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Apartme
nts
Low Rise
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 EXHIBIT 1
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Other — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Asphalt
Surfaces
Total — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Annual — — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Apartme
nts
Low Rise
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
City Park — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
4.6. Refrigerant Emissions by Land Use
4.6.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — — — — — 17.0 17.0
Apartme
nts
Low Rise
— — — — — — — — — — — — — — — — 1.47 1.47
City Park — — — — — — — — — — — — — — — — 0.00 0.00
EXHIBIT 1
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Total — — — — — — — — — — — — — — — — 18.5 18.5
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — — — — — 17.0 17.0
Apartme
nts
Low Rise
— — — — — — — — — — — — — — — — 1.47 1.47
City Park — — — — — — — — — — — — — — — — 0.00 0.00
Total — — — — — — — — — — — — — — — — 18.5 18.5
Annual — — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — — — — — 2.81 2.81
Apartme
nts
Low Rise
— — — — — — — — — — — — — — — — 0.24 0.24
City Park — — — — — — — — — — — — — — — — 0.00 0.00
Total — — — — — — — — — — — — — — — — 3.06 3.06
4.6.2. Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — — — — — 17.0 17.0
EXHIBIT 1
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Apartme — — — — — — — — — — — — — — — — 1.47 1.47
nts
City Park — — — — — — — — — — — — — — — — 0.00 0.00
Total — — — — — — — — — — — — — — — — 18.5 18.5
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — — — — — 17.0 17.0
Apartme
nts
Low Rise
— — — — — — — — — — — — — — — — 1.47 1.47
City Park — — — — — — — — — — — — — — — — 0.00 0.00
Total — — — — — — — — — — — — — — — — 18.5 18.5
Annual — — — — — — — — — — — — — — — — — —
Single
Family
Housing
— — — — — — — — — — — — — — — — 2.81 2.81
Apartme
nts
Low Rise
— — — — — — — — — — — — — — — — 0.24 0.24
City Park — — — — — — — — — — — — — — — — 0.00 0.00
Total — — — — — — — — — — — — — — — — 3.06 3.06
4.7. Offroad Emissions By Equipment Type
4.7.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Equipme
nt
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e EXHIBIT 1
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Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
4.7.2. Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Equipme
nt
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
4.8. Stationary Emissions By Equipment Type
4.8.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) EXHIBIT 1
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Equipme
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
4.8.2. Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Equipme
nt
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
4.9. User Defined Emissions By Equipment Type
EXHIBIT 1
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4.9.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Equipme
nt
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
4.9.2. Mitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Equipme
nt
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
EXHIBIT 1
1226
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4.10. Soil Carbon Accumulation By Vegetation Type
4.10.1. Soil Carbon Accumulation By Vegetation Type - Unmitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Vegetatio
n
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
4.10.2. Above and Belowground Carbon Accumulation by Land Use Type - Unmitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
EXHIBIT 1
1227
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4.10.3. Avoided and Sequestered Emissions by Species - Unmitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Species TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Avoided — — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Sequest
ered
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Remove
d
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
— — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Avoided — — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Sequest
ered
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Remove
d
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
— — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Avoided — — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
-------------------
EXHIBIT 1
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Sequest — — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Remove
d
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
— — — — — — — — — — — — — — — — — — —
4.10.4. Soil Carbon Accumulation By Vegetation Type - Mitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Vegetatio
n
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
4.10.5. Above and Belowground Carbon Accumulation by Land Use Type - Mitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
EXHIBIT 1
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Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
4.10.6. Avoided and Sequestered Emissions by Species - Mitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Species TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Avoided — — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Sequest
ered
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Remove
d
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
— — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Avoided — — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Sequest
ered
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
-------------------
EXHIBIT 1
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Remove — — — — — — — — — — — — — — — — — —
d
Subtotal — — — — — — — — — — — — — — — — — —
— — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Avoided — — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Sequest
ered
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Remove
d
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
— — — — — — — — — — — — — — — — — — —
5. Activity Data
5.1. Construction Schedule
Phase Name Phase Type Start Date End Date Days Per Week Work Days per Phase Phase Description Site Preparation Site Preparation 1/1/2025 3/25/2025 5.00 60.0 — Grading Grading 3/26/2025 6/17/2025 5.00 60.0 —
Building Construction Building Construction 6/18/2025 10/5/2027 5.00 600 — Paving Paving 10/6/2027 2/22/2028 5.00 100 —
Architectural Coating Architectural Coating 5/19/2027 10/5/2027 5.00 100 —
5.2. Off-Road Equipment
5.2.1. Unmitigated
EXHIBIT 1
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Phase Name Equipment Type Fuel Type Engine Tier Number per Day Hours Per Day Horsepower Load Factor Site Preparation Rubber Tired Dozers Diesel Average 3.00 8.00 367 0.40 Site Preparation Tractors/Loaders/Backh
oes
Diesel Average 4.00 8.00 84.0 0.37
Grading Graders Diesel Average 1.00 8.00 148 0.41
Grading Excavators Diesel Average 2.00 8.00 36.0 0.38
Grading Tractors/Loaders/Backh
oes
Diesel Average 2.00 8.00 84.0 0.37
Grading Scrapers Diesel Average 2.00 8.00 423 0.48
Grading Rubber Tired Dozers Diesel Average 1.00 8.00 367 0.40 Building Construction Forklifts Diesel Average 3.00 8.00 82.0 0.20 Building Construction Generator Sets Diesel Average 1.00 8.00 14.0 0.74 Building Construction Cranes Diesel Average 1.00 7.00 367 0.29 Building Construction Welders Diesel Average 1.00 8.00 46.0 0.45 Building Construction Tractors/Loaders/Backh
oes
Diesel Average 3.00 7.00 84.0 0.37
Paving Pavers Diesel Average 2.00 8.00 81.0 0.42
Paving Paving Equipment Diesel Average 2.00 8.00 89.0 0.36 Paving Rollers Diesel Average 2.00 8.00 36.0 0.38
Architectural Coating Air Compressors Diesel Average 1.00 6.00 37.0 0.48
5.2.2. Mitigated
Phase Name Equipment Type Fuel Type Engine Tier Number per Day Hours Per Day Horsepower Load Factor Site Preparation Rubber Tired Dozers Diesel Average 3.00 8.00 367 0.40 Site Preparation Tractors/Loaders/Backh
oes
Diesel Average 4.00 8.00 84.0 0.37
Grading Graders Diesel Average 1.00 8.00 148 0.41
Grading Excavators Diesel Average 2.00 8.00 36.0 0.38
EXHIBIT 1
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Grading Tractors/Loaders/Backh Diesel Average 2.00 8.00 84.0 0.37 Grading Scrapers Diesel Average 2.00 8.00 423 0.48
Grading Rubber Tired Dozers Diesel Average 1.00 8.00 367 0.40 Building Construction Forklifts Diesel Average 3.00 8.00 82.0 0.20 Building Construction Generator Sets Diesel Average 1.00 8.00 14.0 0.74 Building Construction Cranes Diesel Average 1.00 7.00 367 0.29 Building Construction Welders Diesel Average 1.00 8.00 46.0 0.45 Building Construction Tractors/Loaders/Backh
oes
Diesel Average 3.00 7.00 84.0 0.37
Paving Pavers Diesel Average 2.00 8.00 81.0 0.42
Paving Paving Equipment Diesel Average 2.00 8.00 89.0 0.36 Paving Rollers Diesel Average 2.00 8.00 36.0 0.38
Architectural Coating Air Compressors Diesel Average 1.00 6.00 37.0 0.48
5.3. Construction Vehicles
5.3.1. Unmitigated
Phase Name Trip Type One-Way Trips per Day Miles per Trip Vehicle Mix Site Preparation — — — —
Site Preparation Worker 17.5 11.9 LDA,LDT1,LDT2
Site Preparation Vendor — 9.10 HHDT,MHDT
Site Preparation Hauling 0.00 20.0 HHDT
Site Preparation Onsite truck — — HHDT
Grading — — — —
Grading Worker 20.0 11.9 LDA,LDT1,LDT2
Grading Vendor — 9.10 HHDT,MHDT
Grading Hauling 0.00 20.0 HHDT
Grading Onsite truck — — HHDT
EXHIBIT 1
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Building Construction — — — —
Building Construction Worker 578 11.9 LDA,LDT1,LDT2
Building Construction Vendor 151 9.10 HHDT,MHDT
Building Construction Hauling 0.00 20.0 HHDT
Building Construction Onsite truck — — HHDT
Paving — — — —
Paving Worker 15.0 11.9 LDA,LDT1,LDT2
Paving Vendor — 9.10 HHDT,MHDT
Paving Hauling 0.00 20.0 HHDT
Paving Onsite truck — — HHDT
Architectural Coating — — — —
Architectural Coating Worker 116 11.9 LDA,LDT1,LDT2
Architectural Coating Vendor — 9.10 HHDT,MHDT
Architectural Coating Hauling 0.00 20.0 HHDT
Architectural Coating Onsite truck — — HHDT
5.3.2. Mitigated
Phase Name Trip Type One-Way Trips per Day Miles per Trip Vehicle Mix Site Preparation — — — —
Site Preparation Worker 17.5 11.9 LDA,LDT1,LDT2
Site Preparation Vendor — 9.10 HHDT,MHDT
Site Preparation Hauling 0.00 20.0 HHDT
Site Preparation Onsite truck — — HHDT
Grading — — — —
Grading Worker 20.0 11.9 LDA,LDT1,LDT2
Grading Vendor — 9.10 HHDT,MHDT
Grading Hauling 0.00 20.0 HHDT
EXHIBIT 1
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Grading Onsite truck — — HHDT
Building Construction — — — —
Building Construction Worker 578 11.9 LDA,LDT1,LDT2
Building Construction Vendor 151 9.10 HHDT,MHDT
Building Construction Hauling 0.00 20.0 HHDT
Building Construction Onsite truck — — HHDT
Paving — — — —
Paving Worker 15.0 11.9 LDA,LDT1,LDT2
Paving Vendor — 9.10 HHDT,MHDT
Paving Hauling 0.00 20.0 HHDT
Paving Onsite truck — — HHDT
Architectural Coating — — — —
Architectural Coating Worker 116 11.9 LDA,LDT1,LDT2
Architectural Coating Vendor — 9.10 HHDT,MHDT
Architectural Coating Hauling 0.00 20.0 HHDT
Architectural Coating Onsite truck — — HHDT
5.4. Vehicles
5.4.1. Construction Vehicle Control Strategies
Non-applicable. No control strategies activated by user.
5.5. Architectural Coatings
Phase Name Residential Interior Area Coated
(sq ft)
Residential Exterior Area Coated
(sq ft)
Non-Residential Interior Area
Coated (sq ft)
Non-Residential Exterior Area
Coated (sq ft)
Parking Area Coated (sq ft)
Architectural Coating 5,222,050 1,740,683 0.00 0.00 11,761
5.6. Dust Mitigation
EXHIBIT 1
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5.6.1. Construction Earthmoving Activities
Phase Name Material Imported (Cubic Yards) Material Exported (Cubic Yards) Acres Graded (acres) Material Demolished (sq. ft.) Acres Paved (acres) Site Preparation 0.00 0.00 90.0 0.00 —
Grading 0.00 0.00 180 0.00 —
Paving 0.00 0.00 0.00 0.00 17.9
5.6.2. Construction Earthmoving Control Strategies
Non-applicable. No control strategies activated by user.
5.7. Construction Paving
Land Use Area Paved (acres) % Asphalt
Single Family Housing 13.4 0%
Apartments Low Rise — 0%
City Park 0.00 0%
Other Asphalt Surfaces 4.50 100%
5.8. Construction Electricity Consumption and Emissions Factors kWh per Year and Emission Factor (lb/MWh)
Year kWh per Year CO2 CH4 N2O
2025 0.00 204 0.03 < 0.005
2026 0.00 204 0.03 < 0.005
2027 0.00 204 0.03 < 0.005
2028 0.00 204 0.03 < 0.005
5.9. Operational Mobile Sources
5.9.1. Unmitigated
EXHIBIT 1
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Land Use Type Trips/Weekday Trips/Saturday Trips/Sunday Trips/Year VMT/Weekday VMT/Saturday VMT/Sunday VMT/Year Total all Land Uses 12,784 12,784 12,784 4,666,160 96,884 96,884 96,884 35,362,835
5.9.2. Mitigated
Land Use Type Trips/Weekday Trips/Saturday Trips/Sunday Trips/Year VMT/Weekday VMT/Saturday VMT/Sunday VMT/Year Total all Land Uses 12,784 12,784 12,784 4,666,160 96,884 96,884 96,884 35,362,835
5.10. Operational Area Sources
5.10.1. Hearths
5.10.1.1. Unmitigated
5.10.1.2. Mitigated
5.10.2. Architectural Coatings
Residential Interior Area Coated (sq ft) Residential Exterior Area Coated (sq ft) Non-Residential Interior Area Coated (sq ft)
Non-Residential Exterior Area Coated
(sq ft)
Parking Area Coated (sq ft)
5222049.75 1,740,683 0.00 0.00 11,761
5.10.3. Landscape Equipment
Season Unit Value
Snow Days day/yr 0.00
Summer Days day/yr 180
5.10.4. Landscape Equipment - Mitigated
Season Unit Value
Snow Days day/yr 0.00
EXHIBIT 1
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Summer Days day/yr 180
5.11. Operational Energy Consumption
5.11.1. Unmitigated
Electricity (kWh/yr) and CO2 and CH4 and N2O and Natural Gas (kBTU/yr) Land Use Electricity (kWh/yr) CO2 CH4 N2O Natural Gas (kBTU/yr) Single Family Housing 10,375,788 204 0.0330 0.0040 35,402,561 Apartments Low Rise 862,305 204 0.0330 0.0040 2,948,632 City Park 0.00 204 0.0330 0.0040 0.00
Other Asphalt Surfaces 0.00 204 0.0330 0.0040 0.00
5.11.2. Mitigated
Electricity (kWh/yr) and CO2 and CH4 and N2O and Natural Gas (kBTU/yr) Land Use Electricity (kWh/yr) CO2 CH4 N2O Natural Gas (kBTU/yr) Single Family Housing 10,375,788 204 0.0330 0.0040 35,402,561 Apartments Low Rise 862,305 204 0.0330 0.0040 2,948,632 City Park 0.00 204 0.0330 0.0040 0.00
Other Asphalt Surfaces 0.00 204 0.0330 0.0040 0.00
5.12. Operational Water and Wastewater Consumption
5.12.1. Unmitigated
Land Use Indoor Water (gal/year) Outdoor Water (gal/year) Single Family Housing 49,499,984 244,539,302
Apartments Low Rise 7,890,712 0.00
City Park 0.00 0.00
EXHIBIT 1
1238
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Other Asphalt Surfaces 0.00 0.00
5.12.2. Mitigated
Land Use Indoor Water (gal/year) Outdoor Water (gal/year) Single Family Housing 49,499,984 244,539,302
Apartments Low Rise 7,890,712 0.00
City Park 0.00 0.00
Other Asphalt Surfaces 0.00 0.00
5.13. Operational Waste Generation
5.13.1. Unmitigated
Land Use Waste (ton/year) Cogeneration (kWh/year)
Single Family Housing 1,076 —
Apartments Low Rise 144 —
City Park 2.64 —
Other Asphalt Surfaces 0.00 —
5.13.2. Mitigated
Land Use Waste (ton/year) Cogeneration (kWh/year)
Single Family Housing 1,076 —
Apartments Low Rise 144 —
City Park 2.64 —
Other Asphalt Surfaces 0.00 —
5.14. Operational Refrigeration and Air Conditioning Equipment EXHIBIT 1
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5.14.1. Unmitigated
Land Use Type Equipment Type Refrigerant GWP Quantity (kg) Operations Leak Rate Service Leak Rate Times Serviced Single Family Housing Average room A/C &
Other residential A/C
and heat pumps
R-410A 2,088 < 0.005 2.50 2.50 10.0
Single Family Housing Household refrigerators
and/or freezers
R-134a 1,430 0.12 0.60 0.00 1.00
Apartments Low Rise Average room A/C &
Other residential A/C
and heat pumps
R-410A 2,088 < 0.005 2.50 2.50 10.0
Apartments Low Rise Household refrigerators
and/or freezers
R-134a 1,430 0.12 0.60 0.00 1.00
City Park Other commercial A/C
and heat pumps
R-410A 2,088 < 0.005 4.00 4.00 18.0
City Park Stand-alone retail
refrigerators and
freezers
R-134a 1,430 0.04 1.00 0.00 1.00
5.14.2. Mitigated
Land Use Type Equipment Type Refrigerant GWP Quantity (kg) Operations Leak Rate Service Leak Rate Times Serviced Single Family Housing Average room A/C &
Other residential A/C
and heat pumps
R-410A 2,088 < 0.005 2.50 2.50 10.0
Single Family Housing Household refrigerators
and/or freezers
R-134a 1,430 0.12 0.60 0.00 1.00
Apartments Low Rise Average room A/C &
Other residential A/C
and heat pumps
R-410A 2,088 < 0.005 2.50 2.50 10.0
Apartments Low Rise Household refrigerators
and/or freezers
R-134a 1,430 0.12 0.60 0.00 1.00
City Park Other commercial A/C
and heat pumps
R-410A 2,088 < 0.005 4.00 4.00 18.0
EXHIBIT 1
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City Park Stand-alone retail
refrigerators and
freezers
R-134a 1,430 0.04 1.00 0.00 1.00
5.15. Operational Off-Road Equipment
5.15.1. Unmitigated
Equipment Type Fuel Type Engine Tier Number per Day Hours Per Day Horsepower Load Factor
5.15.2. Mitigated
Equipment Type Fuel Type Engine Tier Number per Day Hours Per Day Horsepower Load Factor
5.16. Stationary Sources
5.16.1. Emergency Generators and Fire Pumps
Equipment Type Fuel Type Number per Day Hours per Day Hours per Year Horsepower Load Factor
5.16.2. Process Boilers
Equipment Type Fuel Type Number Boiler Rating (MMBtu/hr) Daily Heat Input (MMBtu/day) Annual Heat Input (MMBtu/yr)
5.17. User Defined
Equipment Type Fuel Type
5.18. Vegetation
5.18.1. Land Use Change
EXHIBIT 1
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5.18.1.1. Unmitigated
Vegetation Land Use Type Vegetation Soil Type Initial Acres Final Acres
5.18.1.2. Mitigated
Vegetation Land Use Type Vegetation Soil Type Initial Acres Final Acres
5.18.1. Biomass Cover Type
5.18.1.1. Unmitigated
Biomass Cover Type Initial Acres Final Acres
5.18.1.2. Mitigated
Biomass Cover Type Initial Acres Final Acres
5.18.2. Sequestration
5.18.2.1. Unmitigated
Tree Type Number Electricity Saved (kWh/year) Natural Gas Saved (btu/year)
5.18.2.2. Mitigated
Tree Type Number Electricity Saved (kWh/year) Natural Gas Saved (btu/year)
6. Climate Risk Detailed Report
6.1. Climate Risk Summary
EXHIBIT 1
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Cal-Adapt midcentury 2040–2059 average projections for four hazards are reported below for your project location. These are under Representation Concentration Pathway (RCP) 8.5 which assumes GHG emissions will continue to rise strongly through 2050 and then plateau around 2100.
Climate Hazard Result for Project Location Unit
Temperature and Extreme Heat 24.1 annual days of extreme heat Extreme Precipitation 2.50 annual days with precipitation above 20 mm Sea Level Rise — meters of inundation depth
Wildfire 0.00 annual hectares burned
Temperature and Extreme Heat data are for grid cell in which your project are located. The projection is based on the 98th historical percentile of daily maximum/minimum temperatures from observed historical data (32 climate model ensemble from Cal-Adapt, 2040–2059 average under RCP 8.5). Each grid cell is 6 kilometers (km) by 6 km, or 3.7 miles (mi) by 3.7 mi.
Extreme Precipitation data are for the grid cell in which your project are located. The threshold of 20 mm is equivalent to about ¾ an inch of rain, which would be light to moderate rainfall if received over a full day or heavy rain if received over a period of 2 to 4 hours. Each grid cell is 6 kilometers (km) by 6 km, or 3.7 miles (mi) by 3.7 mi.
Sea Level Rise data are for the grid cell in which your project are located. The projections are from Radke et al. (2017), as reported in Cal-Adapt (Radke et al., 2017, CEC-500-2017-008), and consider inundation location and depth for the San Francisco Bay, the Sacramento-San Joaquin River Delta and California coast resulting different increments of sea level rise coupled with extreme storm events.
Users may select from four scenarios to view the range in potential inundation depth for the grid cell. The four scenarios are: No rise, 0.5 meter, 1.0 meter, 1.41 meters Wildfire data are for the grid cell in which your project are located. The projections are from UC Davis, as reported in Cal-Adapt (2040–2059 average under RCP 8.5), and consider historical data of climate, vegetation, population density, and large (> 400 ha) fire history. Users may select from four model simulations to view the range in potential wildfire probabilities for the grid cell. The four simulations make different assumptions about expected rainfall and temperature are: Warmer/drier (HadGEM2-ES), Cooler/wetter (CNRM-CM5), Average conditions (CanESM2), Range of different rainfall and temperature possibilities (MIROC5). Each grid cell is 6 kilometers (km) by 6 km, or 3.7 miles (mi) by 3.7 mi.
6.2. Initial Climate Risk Scores
Climate Hazard Exposure Score Sensitivity Score Adaptive Capacity Score Vulnerability Score Temperature and Extreme Heat 2 0 0 N/A
Extreme Precipitation N/A N/A N/A N/A
Sea Level Rise N/A N/A N/A N/A
Wildfire N/A N/A N/A N/A
Flooding 0 0 0 N/A
Drought 0 0 0 N/A
Snowpack Reduction N/A N/A N/A N/A
Air Quality Degradation 0 0 0 N/A
The sensitivity score reflects the extent to which a project would be adversely affected by exposure to a climate hazard. Exposure is rated on a scale of 1 to 5, with a score of 5 representing the greatest exposure.
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The adaptive capacity of a project refers to its ability to manage and reduce vulnerabilities from projected climate hazards. Adaptive capacity is rated on a scale of 1 to 5, with a score of 5 representing the greatest ability to adapt.
The overall vulnerability scores are calculated based on the potential impacts and adaptive capacity assessments for each hazard. Scores do not include implementation of climate risk reduction measures.
6.3. Adjusted Climate Risk Scores
Climate Hazard Exposure Score Sensitivity Score Adaptive Capacity Score Vulnerability Score Temperature and Extreme Heat 2 1 1 3
Extreme Precipitation N/A N/A N/A N/A
Sea Level Rise N/A N/A N/A N/A
Wildfire N/A N/A N/A N/A
Flooding 1 1 1 2
Drought 1 1 1 2
Snowpack Reduction N/A N/A N/A N/A
Air Quality Degradation 1 1 1 2
The sensitivity score reflects the extent to which a project would be adversely affected by exposure to a climate hazard. Exposure is rated on a scale of 1 to 5, with a score of 5 representing the greatest exposure.
The adaptive capacity of a project refers to its ability to manage and reduce vulnerabilities from projected climate hazards. Adaptive capacity is rated on a scale of 1 to 5, with a score of 5 representing the greatest ability to adapt.
The overall vulnerability scores are calculated based on the potential impacts and adaptive capacity assessments for each hazard. Scores include implementation of climate risk reduction measures.
6.4. Climate Risk Reduction Measures
7. Health and Equity Details
7.1. CalEnviroScreen 4.0 Scores
The maximum CalEnviroScreen score is 100. A high score (i.e., greater than 50) reflects a higher pollution burden compared to other census tracts in the state.
Indicator Result for Project Census Tract
Exposure Indicators —
AQ-Ozone 47.0
AQ-PM 50.1
AQ-DPM 33.9
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Drinking Water 99.8
Lead Risk Housing 28.5
Pesticides 87.0
Toxic Releases 21.8
Traffic 31.7
Effect Indicators —
CleanUp Sites 4.12
Groundwater 52.4
Haz Waste Facilities/Generators 54.6
Impaired Water Bodies 66.7
Solid Waste 75.7
Sensitive Population —
Asthma 50.8
Cardio-vascular 77.7
Low Birth Weights 86.8
Socioeconomic Factor Indicators —
Education 68.8
Housing 12.0
Linguistic 61.9
Poverty 52.5
Unemployment 40.6
7.2. Healthy Places Index Scores
The maximum Health Places Index score is 100. A high score (i.e., greater than 50) reflects healthier community conditions compared to other census tracts in the state.
Indicator Result for Project Census Tract
Economic —
Above Poverty 58.77069165
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Employed 40.16424997
Median HI 63.15924548
Education—
Bachelor's or higher 36.40446555
High school enrollment 20.46708585
Preschool enrollment 39.62530476
Transportation—
Auto Access 84.51174131
Active commuting 29.75747466
Social—
2-parent households 95.8937508
Voting 58.07776209
Neighborhood—
Alcohol availability 93.60964969
Park access 27.678686
Retail density 8.700115488
Supermarket access 17.15642243
Tree canopy 58.29590658
Housing—
Homeownership 88.78480688
Housing habitability 96.44552804
Low-inc homeowner severe housing cost burden 77.08199666 Low-inc renter severe housing cost burden 96.70216861
Uncrowded housing 52.3675093
Health Outcomes—
Insured adults 47.32452201
Arthritis 82.7
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Asthma ER Admissions 57.7
High Blood Pressure 39.5
Cancer (excluding skin) 82.6
Asthma 76.7
Coronary Heart Disease 87.2
Chronic Obstructive Pulmonary Disease 81.8
Diagnosed Diabetes 55.5
Life Expectancy at Birth 57.0
Cognitively Disabled 28.0
Physically Disabled 26.6
Heart Attack ER Admissions 42.9
Mental Health Not Good 61.1
Chronic Kidney Disease 85.5
Obesity 74.1
Pedestrian Injuries 84.5
Physical Health Not Good 65.0
Stroke 75.8
Health Risk Behaviors—
Binge Drinking 89.9
Current Smoker 51.2
No Leisure Time for Physical Activity 32.7
Climate Change Exposures—
Wildfire Risk 0.0
SLR Inundation Area 0.0
Children 50.1
Elderly 24.7
English Speaking 36.6
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Foreign-born 63.8
Outdoor Workers 62.2
Climate Change Adaptive Capacity —
Impervious Surface Cover 76.9
Traffic Density 44.9
Traffic Access 0.0
Other Indices —
Hardship 50.9
Other Decision Support —
2016 Voting 35.4
7.3. Overall Health & Equity Scores
Metric Result for Project Census Tract
CalEnviroScreen 4.0 Score for Project Location (a) 72.0 Healthy Places Index Score for Project Location (b) 56.0 Project Located in a Designated Disadvantaged Community (Senate Bill 535) No Project Located in a Low-Income Community (Assembly Bill 1550) No Project Located in a Community Air Protection Program Community (Assembly Bill 617) No a: The maximum CalEnviroScreen score is 100. A high score (i.e., greater than 50) reflects a higher pollution burden compared to other census tracts in the state. b: The maximum Health Places Index score is 100. A high score (i.e., greater than 50) reflects healthier community conditions compared to other census tracts in the state.
7.4. Health & Equity Measures
No Health & Equity Measures selected.
7.5. Evaluation Scorecard
Health & Equity Evaluation Scorecard not completed.
7.6. Health & Equity Custom Measures
No Health & Equity Custom Measures created.
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8. User Changes to Default Data
Screen Justification
Land Use Land uses consistent with the land uses provided in Table 2.0-3 of the Draft EIR Chapter 2.0: Project Description. For the purposes of modeling: LDR and MDR assumed to be all single-family (total of 1,217 units, 191.6 acres), consistent with the Project Description; HDR assumed to be all Apartments Low Rise (194 units, 9.5 acres); Park area = 12.2 acres of parks and recreation plus 18.5 acres of open space and rights of way a= 30-.7 acres; Asphalt surfaces assumed for remainder of Development area = 4.5 acres. Total acreage = 236.3 total development area.
Construction: Construction Phases No demolition. Construction schedule adjusted to reflect assumed buildout schedule of 2028. Start date for construction assumed to be beginning of 2025, based on current information. Architectual coating phase assumed to overlap with tail end of building construction phase.
Operations: Hearths No hearths or wood stoves.
Operations: Consumer Products Revised General Category consumer products emissions factor to reflect CARB adjustments applied to their Consumer and Commercial Product Survey Emission data, made after the 2008 consumer products emissions factor. Adjustment made to reflect average adjustment factor. See for further detail:
https://ww2.arb.ca.gov/our-work/programs/consumer-products-program/consumer-products-emissions-inv
0.0000107
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Source: EMFAC2021 (v1.0.1) Emissions Inventory
Region Type: County
Region: San Joaquin
Calendar Year: 2023, 2025
Season: Annual
Vehicle Classification: EMFAC202x Categories
Units: miles/day for CVMT and EVMT, trips/day for Trips, kWh/day for Energy Consumption, tons/day for Emissions, 1000 gallons/day for Fuel Consumption Region Calendar Year Vehicle Category Model Year Speed Fuel Population Total VMT Trips Fuel Consumption MPG San Joaquin 2023 All Other Buses Aggregate Aggregate Diesel 63.39460475 3393.93922 564.2119822 0.391421545 8.670803 San Joaquin 2023 LDA Aggregate Aggregate Gasoline 246367.0682 9973102.47 1138235.391 349.3216614 28.54991 San Joaquin 2023 LDA Aggregate Aggregate Diesel 705.734891 23139.8254 3023.214022 0.543997543 42.53664 San Joaquin 2023 LDT1 Aggregate Aggregate Gasoline 22016.87719 727225.714 95173.38769 30.52486616 23.82404 San Joaquin 2023 LDT1 Aggregate Aggregate Diesel 6.309776167 72.3140659 18.53577151 0.002954101 24.47922 San Joaquin 2023 LDT2 Aggregate Aggregate Gasoline 99986.64004 4006976.31 463638.6569 174.3583341 22.98127 San Joaquin 2023 LDT2 Aggregate Aggregate Diesel 269.0353638 11767.7731 1277.639106 0.369317903 31.86353 San Joaquin 2023 LHD1 Aggregate Aggregate Gasoline 9831.305478 343356.563 146471.803 37.0137846 9.276451 San Joaquin 2023 LHD1 Aggregate Aggregate Diesel 8858.793592 311287.78 111432.479 19.67413691 15.82218 San Joaquin 2023 LHD2 Aggregate Aggregate Gasoline 1172.202392 40932.8123 17464.06906 4.90823024 8.339628 San Joaquin 2023 LHD2 Aggregate Aggregate Diesel 3130.564849 115648.086 39378.56755 8.863291415 13.04798 San Joaquin 2023 MCY Aggregate Aggregate Gasoline 12111.77426 65765.9483 24223.54852 1.643730409 40.01018 San Joaquin 2023 MDV Aggregate Aggregate Gasoline 94539.47242 3309649.73 427287.8869 178.486066 18.5429 San Joaquin 2023 MDV Aggregate Aggregate Diesel 1386.649679 54072.4946 6485.715736 2.267270858 23.84916 San Joaquin 2023 MH Aggregate Aggregate Gasoline 1507.494843 13134.1796 150.8097841 2.977418428 4.411264 San Joaquin 2023 MH Aggregate Aggregate Diesel 642.7961913 5646.6428 64.27961913 0.600452961 9.403972 San Joaquin 2023 Motor Coach Aggregate Aggregate Diesel 17.50069597 2493.47591 402.1659934 0.455354651 5.475899 San Joaquin 2023 OBUS Aggregate Aggregate Gasoline 184.2186442 8143.5346 3685.846633 1.733278965 4.69834 San Joaquin 2023 PTO Aggregate Aggregate Diesel 0 19769.5175 0 4.013121008 4.92622 San Joaquin 2023 SBUS Aggregate Aggregate Gasoline 127.6658449 7011.40481 510.6633795 0.69096273 10.1473 San Joaquin 2023 SBUS Aggregate Aggregate Diesel 488.0661519 10999.7571 7067.197879 1.346323697 8.170217 San Joaquin 2023 T6 CAIRP Class 4 Aggregate Aggregate Diesel 10.21525791 684.779876 234.7466267 0.077405114 8.846701 San Joaquin 2023 T6 CAIRP Class 5 Aggregate Aggregate Diesel 13.70885779 939.491781 315.0295519 0.106056052 8.858446 San Joaquin 2023 T6 CAIRP Class 6 Aggregate Aggregate Diesel 43.24157557 2453.39435 993.6914066 0.273109788 8.98318 San Joaquin 2023 T6 CAIRP Class 7 Aggregate Aggregate Diesel 74.64743229 15398.8197 1715.397994 1.609252898 9.568925 MHD San Joaquin 2023 T6 Instate Delivery Class 4 Aggregate Aggregate Diesel 243.75384 8276.65194 3478.367297 1.005561316 8.230877 8.579141 San Joaquin 2023 T6 Instate Delivery Class 5 Aggregate Aggregate Diesel 156.2432876 5383.85911 2229.591714 0.657027122 8.194272 San Joaquin 2023 T6 Instate Delivery Class 6 Aggregate Aggregate Diesel 682.6025228 23363.9411 9740.738001 2.839033489 8.229541 San Joaquin 2023 T6 Instate Delivery Class 7 Aggregate Aggregate Diesel 122.4768589 6703.21055 1747.744776 0.802391793 8.354037 San Joaquin 2023 T6 Instate Other Class 4 Aggregate Aggregate Diesel 449.8451938 18399.4289 5200.21044 2.166542487 8.492531 San Joaquin 2023 T6 Instate Other Class 5 Aggregate Aggregate Diesel 1174.570894 51943.6226 13578.03953 6.096265009 8.520565 San Joaquin 2023 T6 Instate Other Class 6 Aggregate Aggregate Diesel 912.5417949 38573.6428 10548.98315 4.50612298 8.560273 San Joaquin 2023 T6 Instate Other Class 7 Aggregate Aggregate Diesel 553.092214 25667.2012 6393.745994 2.950154535 8.70029 San Joaquin 2023 T6 Instate Tractor Class 6 Aggregate Aggregate Diesel 10.69132111 510.925844 123.591672 0.060247854 8.480399 San Joaquin 2023 T6 Instate Tractor Class 7 Aggregate Aggregate Diesel 696.5366058 42802.4924 8051.963163 4.748833943 9.013264 San Joaquin 2023 T6 OOS Class 4 Aggregate Aggregate Diesel 5.905142679 392.334655 135.7001788 0.044317954 8.852725 San Joaquin 2023 T6 OOS Class 5 Aggregate Aggregate Diesel 7.890998517 538.212595 181.3351459 0.060737656 8.861267 San Joaquin 2023 T6 OOS Class 6 Aggregate Aggregate Diesel 24.97157764 1406.36491 573.8468541 0.156409596 8.991551 San Joaquin 2023 T6 OOS Class 7 Aggregate Aggregate Diesel 40.57354344 10226.0217 932.3800283 1.062980063 9.620144 San Joaquin 2023 T6 Public Class 4 Aggregate Aggregate Diesel 32.09216486 1056.60486 164.6328057 0.140824099 7.503012 San Joaquin 2023 T6 Public Class 5 Aggregate Aggregate Diesel 76.27568061 2776.64108 391.2942415 0.361173048 7.687841 San Joaquin 2023 T6 Public Class 6 Aggregate Aggregate Diesel 126.4582156 4446.297 648.7306462 0.576020372 7.718993 San Joaquin 2023 T6 Public Class 7 Aggregate Aggregate Diesel 152.7305258 6768.06936 783.5075973 0.883776286 7.658125 San Joaquin 2023 T6 Utility Class 5 Aggregate Aggregate Diesel 33.47606031 1364.93307 428.493572 0.154770907 8.819055 San Joaquin 2023 T6 Utility Class 6 Aggregate Aggregate Diesel 6.356456131 257.430851 81.36263848 0.029104667 8.845002 San Joaquin 2023 T6 Utility Class 7 Aggregate Aggregate Diesel 7.230830053 358.500092 92.55462468 0.040337535 8.887506 San Joaquin 2023 T6TS Aggregate Aggregate Gasoline 560.525111 27400.6685 11214.98642 5.873758607 4.664929 San Joaquin 2023 T7 CAIRP Class 8 Aggregate Aggregate Diesel 1500.771839 308143.872 34487.73687 51.00604804 6.04132 HHD San Joaquin 2023 T7 NNOOS Class 8 Aggregate Aggregate Diesel 1343.474448 364734.036 30873.04281 59.83110996 6.09606 5.596459 San Joaquin 2023 T7 NOOS Class 8 Aggregate Aggregate Diesel 562.3598205 132501.396 12923.02868 21.97566159 6.029461 San Joaquin 2023 T7 Other Port Class 8 Aggregate Aggregate Diesel 28.6781176 5381.65764 469.174004 0.90785985 5.927851 San Joaquin 2023 T7 POAK Class 8 Aggregate Aggregate Diesel 131.1211785 13188.0173 2145.142481 2.26470624 5.823279 San Joaquin 2023 T7 POLA Class 8 Aggregate Aggregate Diesel 139.588006 18353.09 2283.659779 3.154875131 5.817374 San Joaquin 2023 T7 Public Class 8 Aggregate Aggregate Diesel 387.066761 16533.9411 1985.652484 3.205449572 5.158072 San Joaquin 2023 T7 Single Concrete/Transit Mix Class 8 Aggregate Aggregate Diesel 118.1878034 8595.90453 1113.329108 1.467125303 5.859012 San Joaquin 2023 T7 Single Dump Class 8 Aggregate Aggregate Diesel 486.5561857 30707.0394 4583.359269 5.327318734 5.76407 San Joaquin 2023 T7 Single Other Class 8 Aggregate Aggregate Diesel 1040.735731 57042.4876 9803.730584 9.736964144 5.858344 San Joaquin 2023 T7 SWCV Class 8 Aggregate Aggregate Diesel 175.044521 11346.9523 805.2047965 4.507153801 2.517543 San Joaquin 2023 T7 Tractor Class 8 Aggregate Aggregate Diesel 2638.276559 211937.817 38334.1584 34.91925222 6.069369 San Joaquin 2023 T7 Utility Class 8 Aggregate Aggregate Diesel 23.22093261 1080.67322 297.2279374 0.186573576 5.792209 San Joaquin 2023 T7IS Aggregate Aggregate Gasoline 2.419215607 60.0081934 48.40366587 0.018776223 3.195967 San Joaquin 2023 UBUS Aggregate Aggregate Gasoline 49.369827 3719.55506 197.479308 0.791708132 4.698139 San Joaquin 2023 UBUS Aggregate Aggregate Diesel 78.33872382 5427.523 313.3548953 0.602229331 9.012386 San Joaquin 2025 All Other Buses Aggregate Aggregate Diesel 67.92171408 3454.27959 604.5032553 0.395338932 8.737514 San Joaquin 2025 LDA Aggregate Aggregate Gasoline 247812.193 10065418.7 1143376.643 340.6379829 29.54873 San Joaquin 2025 LDA Aggregate Aggregate Diesel 620.8563183 19917.7375 2643.071074 0.459921869 43.30678 San Joaquin 2025 LDT1 Aggregate Aggregate Gasoline 20969.62889 704503.526 90823.61908 28.55436416 24.67236 San Joaquin 2025 LDT1 Aggregate Aggregate Diesel 5.057977491 54.7985719 14.33247387 0.002232746 24.54313 San Joaquin 2025 LDT2 Aggregate Aggregate Gasoline 105887.2734 4297523.94 491668.9279 179.0193905 24.00591 San Joaquin 2025 LDT2 Aggregate Aggregate Diesel 305.5941154 13558.4186 1463.961841 0.410704288 33.01261 San Joaquin 2025 LHD1 Aggregate Aggregate Gasoline 9450.489324 335570.018 140798.2097 34.90157426 9.614753 San Joaquin 2025 LHD1 Aggregate Aggregate Diesel 8447.684296 292201.982 106261.2413 18.38163512 15.89641 San Joaquin 2025 LHD2 Aggregate Aggregate Gasoline 1129.168714 39496.2437 16822.93138 4.600897482 8.584465 San Joaquin 2025 LHD2 Aggregate Aggregate Diesel 3098.911716 112092.227 38980.41096 8.493201579 13.19788 San Joaquin 2025 MCY Aggregate Aggregate Gasoline 12009.69999 64631.0827 24019.39998 1.598967718 40.42051 San Joaquin 2025 MDV Aggregate Aggregate Gasoline 92446.53152 3253692.9 417141.1232 169.0306745 19.24913 San Joaquin 2025 MDV Aggregate Aggregate Diesel 1393.091492 51951.9772 6420.977754 2.139013823 24.28782 San Joaquin 2025 MH Aggregate Aggregate Gasoline 1345.73466 11738.0981 134.6272954 2.660033836 4.412763 San Joaquin 2025 MH Aggregate Aggregate Diesel 631.6240768 5453.24118 63.16240768 0.580283559 9.397546 San Joaquin 2025 Motor Coach Aggregate Aggregate Diesel 18.80772922 2514.51501 432.2016174 0.452917647 5.551815 San Joaquin 2025 OBUS Aggregate Aggregate Gasoline 170.8324994 7309.03024 3418.016649 1.52248184 4.800734 EXHIBIT 1
1250
San Joaquin 2025 PTO Aggregate Aggregate Diesel 0 20105.4227 0 3.98427046 5.046199 San Joaquin 2025 SBUS Aggregate Aggregate Gasoline 131.6189784 7271.29468 526.4759134 0.71341232 10.19228 San Joaquin 2025 SBUS Aggregate Aggregate Diesel 490.2787139 10849.6548 7099.235777 1.320741795 8.214819 MHD San Joaquin 2025 T6 CAIRP Class 4 Aggregate Aggregate Diesel 10.57610418 697.742444 243.038874 0.077548733 8.997471 8.711536 San Joaquin 2025 T6 CAIRP Class 5 Aggregate Aggregate Diesel 14.00551629 958.755772 321.8467643 0.106617779 8.992457 San Joaquin 2025 T6 CAIRP Class 6 Aggregate Aggregate Diesel 47.29566683 2488.35531 1086.854424 0.272426579 9.13404 San Joaquin 2025 T6 CAIRP Class 7 Aggregate Aggregate Diesel 78.11014265 15772.0773 1794.971078 1.605687139 9.822634 San Joaquin 2025 T6 Instate Delivery Class 4 Aggregate Aggregate Diesel 252.424868 8475.97193 3602.102866 1.019116289 8.316982 San Joaquin 2025 T6 Instate Delivery Class 5 Aggregate Aggregate Diesel 162.4907366 5516.89416 2318.742812 0.666350411 8.279269 San Joaquin 2025 T6 Instate Delivery Class 6 Aggregate Aggregate Diesel 708.1406495 23932.0747 10105.16707 2.87788442 8.315857 San Joaquin 2025 T6 Instate Delivery Class 7 Aggregate Aggregate Diesel 127.2799027 6929.15534 1816.284212 0.825964977 8.389164 San Joaquin 2025 T6 Instate Other Class 4 Aggregate Aggregate Diesel 457.3843802 18839.146 5287.363435 2.200026822 8.563144 San Joaquin 2025 T6 Instate Other Class 5 Aggregate Aggregate Diesel 1233.945904 53254.2945 14264.41465 6.208167542 8.578102 San Joaquin 2025 T6 Instate Other Class 6 Aggregate Aggregate Diesel 939.5521797 39531.7219 10861.2232 4.582174014 8.627285 San Joaquin 2025 T6 Instate Other Class 7 Aggregate Aggregate Diesel 601.2468734 26326.7381 6950.413857 3.002944814 8.766974 San Joaquin 2025 T6 Instate Tractor Class 6 Aggregate Aggregate Diesel 11.09411194 521.271565 128.2479341 0.060836197 8.568444 San Joaquin 2025 T6 Instate Tractor Class 7 Aggregate Aggregate Diesel 742.8431118 44239.5012 8587.266373 4.878765067 9.067766 San Joaquin 2025 T6 OOS Class 4 Aggregate Aggregate Diesel 6.191325924 405.515484 142.2766697 0.044545776 9.103343 San Joaquin 2025 T6 OOS Class 5 Aggregate Aggregate Diesel 8.158025029 556.294323 187.4714152 0.061223253 9.086324 San Joaquin 2025 T6 OOS Class 6 Aggregate Aggregate Diesel 27.75525515 1453.61298 637.8157633 0.156720574 9.275189 San Joaquin 2025 T6 OOS Class 7 Aggregate Aggregate Diesel 42.05361037 10569.5739 966.3919663 1.066856767 9.90721 San Joaquin 2025 T6 Public Class 4 Aggregate Aggregate Diesel 30.96340517 1050.77782 158.8422685 0.137051326 7.667039 San Joaquin 2025 T6 Public Class 5 Aggregate Aggregate Diesel 77.40598482 2785.90976 397.0927021 0.357713881 7.788095 San Joaquin 2025 T6 Public Class 6 Aggregate Aggregate Diesel 124.4648645 4446.56253 638.5047549 0.566454177 7.849819 San Joaquin 2025 T6 Public Class 7 Aggregate Aggregate Diesel 148.2002736 6742.4666 760.2674038 0.856702113 7.870258 San Joaquin 2025 T6 Utility Class 5 Aggregate Aggregate Diesel 33.80713566 1371.26265 432.7313364 0.154052822 8.90125 San Joaquin 2025 T6 Utility Class 6 Aggregate Aggregate Diesel 6.404694197 258.753793 81.98008572 0.028984726 8.927246 San Joaquin 2025 T6 Utility Class 7 Aggregate Aggregate Diesel 7.233394318 359.399463 92.58744727 0.039964166 8.993043 San Joaquin 2025 T6TS Aggregate Aggregate Gasoline 531.0756316 27321.54 10625.76124 5.695995374 4.796623 HHD San Joaquin 2025 T7 CAIRP Class 8 Aggregate Aggregate Diesel 1559.383676 317454.145 35834.63687 51.17555421 6.203238 5.689878 San Joaquin 2025 T7 NNOOS Class 8 Aggregate Aggregate Diesel 1399.986354 379791.503 32171.68641 59.50406302 6.382615 San Joaquin 2025 T7 NOOS Class 8 Aggregate Aggregate Diesel 592.9033383 137971.507 13624.91871 22.13949036 6.231919 San Joaquin 2025 T7 Other Port Class 8 Aggregate Aggregate Diesel 31.09466321 5773.39367 508.7086901 0.965450648 5.979999 San Joaquin 2025 T7 POAK Class 8 Aggregate Aggregate Diesel 137.4284865 13680.6366 2248.330039 2.333991731 5.861476 San Joaquin 2025 T7 POLA Class 8 Aggregate Aggregate Diesel 157.478818 19849.822 2576.353462 3.419583803 5.804748 San Joaquin 2025 T7 Public Class 8 Aggregate Aggregate Diesel 386.4284577 16615.451 1982.377988 3.157962941 5.261446 San Joaquin 2025 T7 Single Concrete/Transit Mix Class 8 Aggregate Aggregate Diesel 121.0999578 8533.43151 1140.761603 1.428680336 5.972947 San Joaquin 2025 T7 Single Dump Class 8 Aggregate Aggregate Diesel 518.3758674 30855.2217 4883.100671 5.328325632 5.790791 San Joaquin 2025 T7 Single Other Class 8 Aggregate Aggregate Diesel 1163.187559 58572.1124 10957.22681 9.897066107 5.918129 San Joaquin 2025 T7 SWCV Class 8 Aggregate Aggregate Diesel 167.5568448 10862.3368 770.7614863 4.227120943 2.569677 San Joaquin 2025 T7 Tractor Class 8 Aggregate Aggregate Diesel 2947.082282 219605.844 42821.10556 35.73125002 6.146044 San Joaquin 2025 T7 Utility Class 8 Aggregate Aggregate Diesel 24.5522509 1096.54573 314.2688115 0.187591616 5.845388 San Joaquin 2025 T7IS Aggregate Aggregate Gasoline 1.372290651 54.2951776 27.45679134 0.014900233 3.643915 San Joaquin 2025 UBUS Aggregate Aggregate Gasoline 50.67993554 3818.16315 202.7197421 0.812722391 4.697992 San Joaquin 2025 UBUS Aggregate Aggregate Diesel 73.34639924 4977.17265 293.3855969 0.526331001 9.456355 EXHIBIT 1
1251
On-road Mobile (Operational) Energy Usage
Unmitigated: