Agenda packet — Carpinteria City Council, March 28, 2022 (part 7 of 10)

Code, § 2050 et seq.) or the Native Plant Protection Act (NPPA; Fish & Game Code, § 1900 et seq.), CDFW recommends the Project proponent obtain appropriate authorization under the Fish and Game Code.

Project Location: The Project would extend from the eastern end of Carpinteria Avenue, in the City of Carpinteria, to Rincon Beach County Park, in unincorporated Santa Barbara County. The Carpinteria Bluffs Nature Preserve lies to the east of the Project and the Project is bordered by the Rincon Bluffs Preserve.

Project Description/Objectives: The proposed Project includes the construction of a paved 16-foot-wide trail (10-foot-wide path with 3-foot-wide paved shoulder along both sides); an approximately 2,800-feet-long, a clear-span bridge over the Union Pacific Railroad alignment; parking facilities; fencing; signage; and a storm drainage collection system, with new drain outlets to the ocean. The bridge would be approximately 160-feet-long, with a width of between 14-feet and 16-feet.

COMMENTS AND RECOMMENDATIONS
CDFW offers the following comments and recommendations to assist the City in adequately identifying and/or mitigating the Project’s significant, or potentially significant, direct and indirect impacts on fish and wildlife (biological) resources.

Specific Comments
1) Crotch Bumble Bee. Potential for Crotch bumble bee (Bombus crotchii) within the Project vicinity. Project ground disturbing activities may result in crushing or filling of active bee colonies, causing the death or injury of adults, eggs, and larvae. The Project may remove bee habitat by eliminating vegetation that may support essential foraging habitat. Impacts to Crotch’s bumble bee could result from ground disturbing activities. Project disturbance activities could result in mortality or injury to hibernating bees, as well as temporary or longterm loss of suitable foraging habitats. Construction during the breeding season of bees could result in the incidental loss of breeding success or otherwise lead to nest abandonment.
a) CDFW recommends that measures be taken, primarily, to avoid Project impacts to Crotch bumble bee. On June 12, 2019, the California Fish and Game Commission accepted a petition to list the crotch bumble bee as endangered under the California Endangered Species Act (“CESA”), determining the listing “may be warranted” and advancing the species to the candidacy stage of the CESA listing process. b) CDFW recommends, within one year prior to vegetation removal and/or grading, a qualified entomologist familiar with the species behavior and life history should conduct surveys to determine the presence/absence of Crotch’s bumble bee.

Surveys should be conducted during flying season when the species is most likely to be detected above ground, between March 1 to September 1 (Thorp et al. 1983).

Survey results including negative findings should be submitted to CDFW prior to initiation of Project activities. If “take” or adverse impacts to Crotch’s bumble bee cannot be avoided either during Project activities or over the life of the Project, the City must consult CDFW to determine if a CESA incidental take permit is required (pursuant to Fish & Game Code, § 2080 et seq.).

Nick Bobroff
City of Carpinteria
Nov. 30, 2020

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2) California Endangered Species Act (CESA). A review of CNDDB indicates several occurrences within two miles of the Project vicinity of light-footed Ridgway’s rail (Rallus obsoletus levipes), a CESA-listed and Fully-Protected species (Fish and G. Code § 3511) that is also listed under the federal Endangered Species Act. A review of CNDDB indicates several occurrences within two miles of the Project vicinity of Belding’s savannah sparrow (Passerculus sandwichensis beldingi), a CESA-listed species. Project related activities may adversely impact potential habitat for this species. CDFW considers adverse impacts to a species protected by CESA to be significant without mitigation under CEQA. As to CESA, take of any endangered, threatened, candidate species, or State-listed rare plant species that results from the Project is prohibited, except as authorized by state law (Fish and Game Code, §§ 2080, 2085; Cal. Code Regs., tit. 14, §786.9). Consequently, if the Project, Project construction, or any Project-related activity during the life of the Project will result in take of a species designated as endangered or threatened, or a candidate for listing under CESA, CDFW recommends that the Project proponent seek appropriate take authorization under CESA prior to implementing the Project. Appropriate authorization from CDFW may include an Incidental Take Permit (ITP) or a consistency determination in certain circumstances, among other options [Fish & Game Code, §§ 2080.1, 2081, subds. (b) and (c)]. Early consultation is encouraged, as significant modification to a Project and mitigation measures may be required in order to obtain a CESA Permit. Revisions to the Fish and Game Code, effective January 1998, may require that CDFW issue a separate CEQA document for the issuance of an ITP unless the Project CEQA document addresses all Project impacts to CESA-listed species and specifies a mitigation monitoring and reporting program that will meet the requirements of an ITP. For these reasons, biological mitigation monitoring and reporting proposals should be of sufficient detail and resolution to satisfy the requirements for a CESA ITP.

CDFW cannot authorize the take of any fully protected species as defined by State law.

State fully protected species may not be taken or possessed at any time and no licenses or permits may be issued for its take except for collecting those species for necessary scientific research and relocation of the bird species for protection of livestock (Fish & G. Code, §§ 3511, 4700, 5050, 5515). Take of any species designated as fully protected under the Fish and Game Code is prohibited. CDFW recognizes that light-footed Ridgway’s rail is documented to occur in the vicinity of the project area. CDFW recommends the City fully avoid all impacts to light-footed Ridgway’s rail occupied habitat. 3) Human-Wildlife Interface. Due to the location of the Project site within coastal bluff and beach environment, CDFW recommends the lead agency evaluate the use of this trail and its potential impacts to wildlife in the adjacent open space settings. 4) Biological Baseline Assessment. A CNDDB review indicates the occurrence of several special status insect, reptile, mammal, and plant species including Coulter's saltbush (Atriplex coulteri), globose dune beetle (Coelus globosus), western snowy plover (Charadrius alexandrinus nivosus), Northern California legless lizard (Anniella pulchra), white-veined monardella (Monardella hypoleuca ssp. hypoleuca),Townsend's big-eared bat (Corynorhinus townsendii), southern tarplant (Centromadia parryi ssp. australis), and monarch - California overwintering population (Danaus plexippus pop. 1) within the Project vicinity. The majority of the Project site is open space. Undisturbed land may provide suitable habitat for special status or regionally and locally unique species. CDFW recommends providing a complete assessment and impact analysis of the flora and fauna within and adjacent to the Project area, with emphasis upon identifying endangered,

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City of Carpinteria
Nov. 30, 2020

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threatened, sensitive, regionally and locally unique species, and sensitive habitats. Impact analysis will aid in determining any alternative trail designs that could reduce impacts to any special status species detected, as well as assess direct, indirect, and cumulative biological impacts. CDFW recommends avoiding any sensitive natural communities found on or adjacent to the Project. CDFW also considers impacts to Species of Special Concern a significant direct and cumulative adverse effect without implementing appropriate avoidance and/or mitigation measures. The DEIR should include the following information:
a) Information on the regional setting that is critical to an assessment of environmental impacts, with special emphasis on resources that are rare or unique to the region [CEQA Guidelines, § 15125(c)]. The DEIR should include measures to fully avoid and otherwise protect Sensitive Natural Communities from Project-related impacts.

Project implementation may result in impacts to rare or endangered plants or plant communities that have been recorded adjacent to the Project vicinity. CDFW considers these communities as threatened habitats having both regional and local significance. Plant communities, alliances, and associations with a state-wide ranking of S1, S2, S3 and S4 should be considered sensitive and declining at the local and regional level. These ranks can be obtained by visiting https://www.wildlife.ca.gov/Data/VegCAMP/NaturalCommunities#sensitive%20natural%20communities; b) A thorough, recent, floristic-based assessment of special status plants and natural communities, following CDFW's Protocols for Surveying and Evaluating Impacts to Special Status Native Plant Populations and Natural Communities (see https://nrm.dfg.ca.gov/FileHandler.ashx?DocumentID=18959&inline); c) Floristic, alliance- and/or association-based mapping and vegetation impact assessments conducted at the Project site and within the neighboring vicinity. The Manual of California Vegetation, second edition, should also be used to inform this mapping and assessment (Sawyer, 2008). Adjoining habitat areas should be included in this assessment where site activities could lead to direct or indirect impacts offsite. Habitat mapping at the alliance level will help establish baseline vegetation conditions;
d) A complete, recent, assessment of the biological resources associated with each habitat type on site and within adjacent areas that could also be affected by the Project. CDFW’s CNDDB in Sacramento should be contacted to obtain current information on any previously reported sensitive species and habitat. CDFW recommends that CNDDB Field Survey Forms be completed and submitted to CNDDB to document survey results. Online forms can be obtained and submitted at http://www.dfg.ca.gov/biogeodata/cnddb/submitting_data_to_cnddb.asp; e) A complete, recent, assessment of rare, threatened, and endangered, and other sensitive species on site and within the area of potential effect, including California Species of Special Concern and California Fully Protected Species (Fish & Game Code, §§ 3511, 4700, 5050 and 5515). Species to be addressed should include all those which meet the CEQA definition of endangered, rare or threatened species (CEQA Guidelines, § 15380). Seasonal variations in use of the Project area should also be addressed. Focused species-specific surveys, conducted at the appropriate time of year and time of day when the sensitive species are active or otherwise

Nick Bobroff
City of Carpinteria
Nov. 30, 2020

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identifiable, are required. Acceptable species-specific survey procedures should be developed in consultation with CDFW and the USFWS; and, f) A recent, wildlife and rare plant survey. CDFW generally considers biological field assessments for wildlife to be valid for a one-year period, and assessments for rare plants may be considered valid for a period of up to three years. Some aspects of the proposed Project may warrant periodic updated surveys for certain sensitive taxa, particularly if build out could occur over a protracted time frame, or in phases. 5) Biological Direct, Indirect, and Cumulative Impacts. Due to the proximity of the Project site to undeveloped land and open space just north of the Project site, it is essential to understand how these open spaces and the biological diversity within them may be impacted by Project activities. This should aid in identifying specific mitigation or avoidance measures necessary to offset those impacts. CDFW recommends providing a thorough discussion of direct, indirect, and cumulative impacts expected to adversely affect biological resources, with specific measures to offset such impacts. The following should be addressed in the DEIR:
a) A discussion regarding indirect Project impacts on biological resources, including resources in nearby public lands, open space, adjacent natural habitats, riparian ecosystems, and any designated and/or proposed or existing reserve lands (e.g., preserve lands associated with a Natural Community Conservation Plan (NCCP, Fish & Game Code, § 2800 et. seq.). Impacts on, and maintenance of, wildlife corridor/movement areas, including access to undisturbed habitats in adjacent areas, should be fully evaluated in the DEIR;
b) A discussion of potential adverse impacts from lighting, noise, temporary and permanent human activity, and exotic species and identification of any mitigation measures;
c) A discussion on Project-related changes on drainage patterns and downstream of the Project site; the volume, velocity, and frequency of existing and post-Project surface flows; polluted runoff; soil erosion and/or sedimentation in streams and water bodies; and, post-Project fate of runoff from the Project site. The discussion should also address the proximity of the extraction activities to the water table, whether dewatering would be necessary and the potential resulting impacts on the habitat (if any) supported by the groundwater. Mitigation measures proposed to alleviate such Project impacts should be included;
d) An analysis of impacts from land use designations and zoning located nearby or adjacent to natural areas that may inadvertently contribute to wildlife-human interactions. A discussion of possible conflicts and mitigation measures to reduce these conflicts should be included in the DEIR; and,
e) A cumulative effects analysis, as described under CEQA Guidelines, section 15130.

General and specific plans, as well as past, present, and anticipated future projects, should be analyzed relative to their impacts on similar plant communities and wildlife habitats.
6) Nesting Birds. Project activities may impact nesting birds. Project activities occurring during the breeding season of nesting birds could result in the incidental loss of fertile eggs, or

Nick Bobroff
City of Carpinteria
Nov. 30, 2020

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nestlings, or otherwise lead to nest abandonment in trees directly adjacent to the Project boundary. The Project could also lead to the loss of foraging habitat for sensitive bird species.
a) CDFW recommends that measures be taken, primarily, to avoid Project impacts to nesting birds. Migratory nongame native bird species are protected by international treaty under the Federal Migratory Bird Treaty Act (MBTA) of 1918 (Code of Federal Regulations, Title 50, § 10.13). Sections 3503, 3503.5, and 3513 of the California Fish and Game Code prohibit take of all birds and their active nests including raptors and other migratory nongame birds (as listed under the Federal MBTA). b) Proposed Project activities including (but not limited to) staging and disturbances to native and nonnative vegetation, structures, and substrates should occur outside of the avian breeding season which generally runs from February 15 through August 31 (as early as January 1 for some raptors) to avoid take of birds or their eggs. If avoidance of the avian breeding season is not feasible, CDFW recommends surveys by a qualified biologist with experience in conducting breeding bird surveys to detect protected native birds occurring in suitable nesting habitat that is to be disturbed and (as access to adjacent areas allows) any other such habitat within 300-feet of the disturbance area (within 500-feet for raptors). Project personnel, including all contractors working on site, should be instructed on the sensitivity of the area.

Reductions in the nest buffer distance may be appropriate depending on the avian species involved, ambient levels of human activity, screening vegetation, or possibly other factors.

General Comments
7) Project Description and Alternatives. To enable CDFW to adequately review and comment on the proposed Project from the standpoint of the protection of plants, fish, and wildlife, we recommend the following information be included in the DEIR:
a) A complete discussion of the purpose and need for, and description of, the proposed Project, including all staging areas and access routes to the construction and staging areas; and,
b) A range of feasible alternatives to Project component location and design features to ensure that alternatives to the proposed Project are fully considered and evaluated. The alternatives should avoid or otherwise minimize direct and indirect impacts to sensitive biological resources and wildlife movement areas.
8) Wetlands Resources. CDFW, as described in Fish and Game Code section 703(a), is guided by the Fish and Game Commission’s policies. The Wetlands Resources policy (http://www.fgc.ca.gov/policy/) of the Fish and Game Commission “…seek[s] to provide for the protection, preservation, restoration, enhancement and expansion of wetland habitat in California. Further, it is the policy of the Fish and Game Commission to strongly discourage development in or conversion of wetlands. It opposes, consistent with its legal authority, any development or conversion that would result in a reduction of wetland acreage or wetland habitat values. To that end, the Commission opposes wetland development proposals unless, at a minimum, project mitigation assures there will be ‘no net loss’ of either wetland

Nick Bobroff
City of Carpinteria
Nov. 30, 2020

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habitat values or acreage. The Commission strongly prefers mitigation which would achieve expansion of wetland acreage and enhancement of wetland habitat values.” a) The Wetlands Resources policy provides a framework for maintaining wetland resources and establishes mitigation guidance. CDFW encourages avoidance of wetland resources as a primary mitigation measure and discourages the development or type conversion of wetlands to uplands. CDFW encourages activities that would avoid the reduction of wetland acreage, function, or habitat values. Once avoidance and minimization measures have been exhausted, the Project must include mitigation measures to assure a “no net loss” of either wetland habitat values, or acreage, for unavoidable impacts to wetland resources. Conversions include, but are not limited to, conversion to subsurface drains, placement of fill or building of structures within the wetland, and channelization or removal of materials from the streambed. All wetlands and watercourses, whether ephemeral, intermittent, or perennial, should be retained and provided with substantial setbacks, which preserve the riparian and aquatic values and functions for the benefit to on-site and off-site wildlife populations. CDFW recommends mitigation measures to compensate for unavoidable impacts be included in the DEIR and these measures should compensate for the loss of function and value.
b) The Fish and Game Commission’s Water policy guides CDFW on the quantity and quality of the waters of this state that should be apportioned and maintained respectively so as to produce and sustain maximum numbers of fish and wildlife; to provide maximum protection and enhancement of fish and wildlife and their habitat; encourage and support programs to maintain or restore a high quality of the waters of this state; prevent the degradation thereof caused by pollution and contamination; and, endeavor to keep as much water as possible open and accessible to the public for the use and enjoyment of fish and wildlife. CDFW recommends avoidance of water practices and structures that use excessive amounts of water, and minimization of impacts that negatively affect water quality, to the extent feasible (Fish & Game Code, § 5650). 9) Compensatory Mitigation. The DEIR should include mitigation measures for adverse Projectrelated impacts to sensitive plants, animals, and habitats. Mitigation measures should emphasize avoidance and reduction of Project impacts. For unavoidable impacts, on-site habitat restoration or enhancement should be discussed in detail. If on-site mitigation is not feasible or would not be biologically viable and therefore not adequately mitigate the loss of biological functions and values, off-site mitigation through habitat creation and/or acquisition and preservation in perpetuity should be addressed. Areas proposed as mitigation lands should be protected in perpetuity with a conservation easement, financial assurance and dedicated to a qualified entity for long-term management and monitoring. Under Government Code, section 65967, the lead agency must exercise due diligence in reviewing the qualifications of a governmental entity, special district, or nonprofit organization to effectively manage and steward land, water, or natural resources on mitigation lands it approves.
10) Long-term Management of Mitigation Lands. For proposed preservation and/or restoration, the DEIR should include measures to protect the targeted habitat values from direct and indirect negative impacts in perpetuity. The objective should be to offset the Project-induced qualitative and quantitative losses of wildlife habitat values. Issues that should be addressed include (but are not limited to) restrictions on access, proposed land dedications, monitoring and management programs, control of illegal dumping, water pollution, and increased

Nick Bobroff
City of Carpinteria
Nov. 30, 2020

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human intrusion. An appropriate non-wasting endowment should be set aside to provide for long-term management of mitigation lands.
11) Translocation/Salvage of Plants and Animal Species. Translocation and transplantation is the process of moving an individual from the Project site and permanently moving it to a new location. CDFW generally does not support the use of, translocation or transplantation as the primary mitigation strategy for unavoidable impacts to rare, threatened, or endangered plant or animal species. Studies have shown that these efforts are experimental and the outcome unreliable. CDFW has found that permanent preservation and management of habitat capable of supporting these species is often a more effective long-term strategy for conserving sensitive plants and animals and their habitats. 12) Moving out of Harm’s Way. The proposed Project is anticipated to result in clearing of habitats that support many species of indigenous wildlife. To avoid direct mortality, we recommend that a qualified biological monitor approved by CDFW be on-site prior to and during ground and habitat disturbing activities to move out of harm’s way special status species or other wildlife of low mobility that would be injured or killed by grubbing or Projectrelated construction activities. It should be noted that the temporary relocation of on-site wildlife does not constitute effective mitigation for the purposes of offsetting Project impacts associated with habitat loss. If the Project requires species to be removed, disturbed, or otherwise handled, we recommend that the DEIR clearly identify that the designated entity should obtain all appropriate state and federal permits.

CONCLUSION
CDFW appreciates the opportunity to comment on the NOP to assist the City of Carpinteria in identifying and mitigating Project impacts on biological resources. If you have any questions or comments regarding this letter, please contact Kelly Schmoker, Senior Environmental Scientist, at (626) 335-9092 or by email at [email protected].

Sincerely,
Erinn Wilson-Olgin
Environmental Program Manager I
Ec: CDFW
Steve Gibson, Los Alamitos – [email protected] Sarah Rains, Los Alamitos – [email protected] Susan Howell, San Diego – [email protected]
CEQA Program Coordinator, Sacramento – [email protected]

State Clearinghouse, Sacramento – [email protected]

Nick Bobroff
City of Carpinteria
Nov. 30, 2020

Page 9 of 9 ends

References
Sawyer, J. O., Keeler-Wolf, T., and Evens J.M. 2008. A manual of California Vegetation, 2nd ed.

ISBN 978-0-943460-49-9.

Thorp, Robbin W., Horning Jr, Donald S., and Dunning, Lorry L. 1983. Bumble Bees and Cuckoo Bumble Bees of California. Bulletin of the California Insect Survey 23.

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Rob and Christi Hudson
6180 Via Real #98
Carpinteria, CA 93013
To: Nick Bobroff
Contact Person for the Carpinteria/Rincon Multi-Use Trail Project Carpinteria City Hall
November 24, 2020
Dear Mr. Bobroff,
My husband, Rob, and I have lived in Carpinteria since 2007, and currently live in the Vista de Santa Barbara Mobile Home Park directly across from the Bluffs. We love our town and cherish the open spaces that we are privileged to enjoy! We fully support the idea of finishing a trail connection between Rincon Beach and the Carpinteria Coastal Trail. We love to ride our bikes on and around the Bluffs and frequently use both sections of the existing trail. Having a completed trail would be a great asset to many people.

We attended the virtual meeting held on November 17 in which the plan for the new trail section was discussed in preparation for an upcoming Environmental Impact Report, and we have a few questions, concerns, and requests.

First, we are concerned that the current plan involves the removal of so much dirt and land. Perhaps we are joining the conversation about this new trail segment too late, but have all other possible routes truly been considered and evaluated? Is the purpose of this segment to provide a practical and efficient completion of the trail, using existing corridors and structures, and being less invasive into natural habitat, or is it to provide a scenic experience for the hiker or biker? We, personally, would be willing to sacrifice a great view as we ride along a short segment of the trail, if it meant that we could preserve a larger portion of the Bluffs undisturbed.

As I am sure you are aware, our Bluffs are a repository of many rapidly vanishing native species. If there is truly no other route option other than the one that is being presented, we request that every precaution be taken to evaluate and protect the plant and animal species that would be impacted by the location of the new trail and the digging and construction that would it would involve.

A Certificated California Botanist is needed to evaluate any plant species that would be impacted. A scientist with this certification would have specialized knowledge of plants and biomes that are specific to the Bluffs, and be able to determine if any lasting harm to a native plant species might be a result of this project. In the same manner, a biologist with specific training in the animal life of California habitats, especially coastal habitats, should be included in the upcoming EIR.

We are also concerned about the use of the Rincon Beach parking lot as a part of the new trail segment. This parking lot is extremely busy on almost every day of the year! This part of the proposal did not seem to be well thought-out, or perhaps was just not very clear. Will there be a way to separate and protect trail users from beach users and cars in the entire parking lot area extending down towards Bates Road? We certainly recognize that there are numerous details, opinions, and desires to be taken into consideration as you move forward. We thank you in advance for using caution and care for the native species of plants and animals that live in the Bluffs as you make decisions regarding the completion of the Carpinteria/ Rincon Multi-Use Trail.

Sincerely,
Christi and Rob Hudson

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November 25, 2020
Nick Bobroff
City of Carpinteria
Community Development Department
5775 Carpinteria Avenue
Carpinteria, CA 93013
Re: Santa Barbara County Air Pollution Control District Response to Notice of Preparation of a Draft Environmental Impact Report for Rincon Trail Project, 19-2015-CUP/CDP Dear Nick Bobroff:

The Santa Barbara County Air Pollution Control District (District) appreciates the opportunity to provide comments on the Notice of Preparation (NOP) of a Draft Environmental Impact Report (EIR) for the Rincon Trail Project. The applicant proposes to construct and operate a multi-use trail approximately 2,800 feet long and 16 feet wide with a 160 feet long bridge over the railroad tracks. Grading is estimated at 104,000 cubic yards (CY) of cut, 10,300 CY of fill, and 94,100 CY of export. It is anticipated that construction of the proposed project would commence in March 2022 and reach completion by March 2024, for a total construction window of approximately two years. The project site is located at the end of Carpinteria Avenue in the City of Carpinteria and Rincon Beach County Park in the County of Santa Barbara.

District staff reviewed the NOP of a Draft EIR and concurs that air quality impacts should be addressed in the EIR. The District’s guidance document, entitled Scope and Content of Air Quality Sections in Environmental Documents (updated June 2017), is available online at www.ourair.org/land-use. This document should be referenced for general guidance in assessing air quality impacts in the Draft EIR.

The EIR should evaluate the following potential impacts related to the Rincon Trail Project:

1. Construction Impacts. The proposed project will involve air quality impacts associated with heavy equipment use for earth-moving activities and bridge construction, as well as truck trips associated with the export of soils, equipment and materials delivery, and employee commute.

Common earthwork equipment, such as dozer, excavator, dump truck, roller, skid steer, and tractor, will be used for trail construction, v-trench construction, and installation of fencing. Two cranes will be required for the installation of the prefabricated bridge. The bridge foundation will be constructed using deep piles. The EIR should include a description and quantification of potential air quality impacts, including criteria pollutant emissions and greenhouse gas emissions, associated with construction activities for the proposed project. The District’s June, 2017 Scope and Content document, Section 6, presents recommended mitigation measures for fugitive dust and equipment exhaust emissions associated with construction projects. Construction mitigation measures should be enforced as conditions of approval for the project. The Draft EIR should NOP of Draft EIR for the Rincon Trail Project, 19-2015-CUP/CDP November 25, 2020

Page 2 of 3 ends

include a Mitigation Monitoring and Reporting Plan that explicitly states the required mitigation and establishes a mechanism for enforcement.

In addition, please be advised that the project will be subject to the following regulatory requirements:

1. All portable diesel-fired construction engines rated at 50 bhp or greater must have either statewide Portable Equipment Registration Program (PERP) certificates or District permits prior to grading/building permit issuance. Construction engines with PERP certificates are exempt from the District permit, provided they will be on-site for less than 12 months. If a District permit is required, proof of receipt of the District permits shall be submitted by the applicant to planning staff. The District permit process can take several months. To avoid delay, the applicant is encouraged to submit their Authority to Construct permit application to the District as soon as possible, see www.ourair.org/permit-applications to download the necessary permit application(s).

2. Two engine cranes are subject to CARB’s In-Use Off-Road Diesel-Fueled Fleets Regulation. For more information on applicable requirements of the Off-Road Regulation, please visit the following website: www.arb.ca.gov/msprog/ordiesel/ordiesel.htm. In addition, the upper engine on a crane must have either a statewide Portable Equipment Registration Program (PERP) certificates or District permits prior to grading/building permit issuance. Two engine cranes are eligible for registration in PERP provided they will be on-site for less than 12 months.

3. The application of architectural coatings, such as paints, primers, and sealers that are applied to buildings or stationary structures, shall comply with District Rule 323.1, Architectural Coatings that places limits on the VOC-content of coating products.

4. Asphalt paving activities shall comply with District Rule 329, Cutback and Emulsified Asphalt Paving Materials.

5. Construction/demolition activities are subject to District Rule 345, Control of Fugitive Dust from Construction and Demolition Activities. This rule establishes limits on the generation of visible fugitive dust emissions at demolition and construction sites, includes measures for minimizing fugitive dust from on-site activities, and from trucks moving on- and off-site. Please see www.ourair.org/wp-content/uploads/rule345.pdf. Activities subject to Rule 345 are also subject to Rule 302 (Visible Emissions) and Rule 303 (Nuisance).

6. If the project area to be disturbed: a) is located in a geographic ultramafic rock unit; b) has naturally-occurring asbestos, serpentine, or ultramafic rock as determined by the owner/operator; or c) is discovered by the owner/operator, a registered geologist, or the Air Pollution Control Officer to have naturally-occurring asbestos, serpentine, or ultramafic rock after the start of any construction or grading; then appropriate abatement measures must be undertaken pursuant to the requirements of the Air Resources Board Air Toxic Control Measure (ATCM) for Construction, Grading, Quarrying and Surface Mining Operations (see www.arb.ca.gov/toxics/asbestos/asbestos.htm).

NOP of Draft EIR for the Rincon Trail Project, 19-2015-CUP/CDP November 25, 2020

Page 3 of 3 ends

7. At all times, idling of heavy-duty diesel trucks should be minimized; auxiliary power units should be used whenever possible. State law requires that:
x Drivers of diesel-fueled commercial vehicles shall not idle the vehicle’s primary diesel engine for greater than 5 minutes at any location.
x Drivers of diesel-fueled commercial vehicles shall not idle a diesel-fueled auxiliary power system (APS) for more than 5 minutes to power a heater, air conditioner, or any ancillary equipment on the vehicle. Trucks with 2007 or newer model year engines must meet additional requirements (verified clean APS label required). x See www.arb.ca.gov/noidle for more information.

In addition, the District recommends that the following best practices be applied to the project as appropriate:

1. To reduce the potential for violations of District Rule 345 (Control of Fugitive Dust from Construction and Demolition Activities), Rule 302 (Visible Emissions), and Rule 303 (Nuisance), standard dust mitigations (Attachment A) are recommended for all construction and/or grading activities. The name and telephone number of an on-site contact person must be provided to the District prior to grading/building permit issuance.

2. The State of California considers particulate matter emitted by diesel engines carcinogenic.

Therefore, during project grading, construction, and hauling, construction contracts must specify that contractors shall adhere to the requirements listed in Attachment B to reduce emissions of particulate matter (as well as of ozone precursors) from diesel equipment. Recommended measures shall be implemented to the maximum extent feasible. Prior to grading/building permit issuance and/or map recordation, all requirements shall be shown as conditions of approval on grading/building plans, and/or on a separate sheet to be recorded with the map.

Conditions shall be adhered to throughout all grading and construction periods. The contractor shall retain the Certificate of Compliance for CARB’s In-Use Regulation for Off-Road Diesel Vehicles onsite and have it available for inspection.

We hope you find our comments useful. We look forward to reviewing the Draft EIR. Please contact me at 961-8873 or by e-mail at [email protected] if you have questions.

Sincerely,
Desmond Ho
Air Quality Specialist
Planning Division
Attachments: Fugitive Dust Control Measures
Diesel Particulate and NOx Emission Measures
cc: Planning Chron File
Sincerely,

ATTACHMENT A

FUGITIVE DUST CONTROL MEASURES
These measures are required for all projects involving earthmoving activities regardless of the project size or duration. Projects are expected to manage fugitive dust emissions such that emissions do not exceed APCD’s visible emissions limit (APCD Rule 302), create a public nuisance (APCD Rule 303), and are in compliance with the APCD’s requirements and standards for visible dust (APCD Rule 345). x During construction, use water trucks or sprinkler systems to keep all areas of vehicle movement damp enough to prevent dust from leaving the site and from exceeding the APCD’s limit of 20% opacity for greater than 3 minutes in any 60 minute period. At a minimum, this should include wetting down such areas in the late morning and after work is completed for the day. Increased watering frequency should be required when sustained wind speed exceeds 15 mph. Reclaimed water should be used whenever possible.

However, reclaimed water should not be used in or around crops for human consumption. x Onsite vehicle speeds shall be no greater than 15 miles per hour when traveling on unpaved surfaces. x Install and operate a track-out prevention device where vehicles enter and exit unpaved roads onto paved streets. The track-out prevention device can include any device or combination of devices that are effective at preventing track out of dirt such as gravel pads, pipe-grid track-out control devices, rumble strips, or wheel-washing systems.
x If importation, exportation, and stockpiling of fill material is involved, soil stockpiled for more than one day shall be covered, kept moist, or treated with soil binders to prevent dust generation. Trucks transporting fill material to and from the site shall be tarped from the point of origin. x Minimize the amount of disturbed area. After clearing, grading, earthmoving, or excavation is completed, treat the disturbed area by watering, OR using roll-compaction, OR revegetating, OR by spreading soil binders until the area is paved or otherwise developed so that dust generation will not occur. All roadways, driveways, sidewalks etc. to be paved should be completed as soon as possible. x Schedule clearing, grading, earthmoving, and excavation activities during periods of low wind speed to the extent feasible. During periods of high winds (>25 mph) clearing, grading, earthmoving, and excavation operations shall be minimized to prevent fugitive dust created by onsite operations from becoming a nuisance or hazard.
x The contractor or builder shall designate a person or persons to monitor and document the dust control program requirements to ensure any fugitive dust emissions do not result in a nuisance and to enhance the implementation of the mitigation measures as necessary to prevent transport of dust offsite. Their duties shall include holiday and weekend periods when work may not be in progress. The name and telephone number of such persons shall be provided to the Air Pollution Control District prior to grading/building permit issuance and/or map clearance.

PLAN REQUIREMENTS: All requirements shall be shown on grading and building plans and/or as a separate information sheet listing the conditions of approval to be recorded with the map. Timing: Requirements shall be shown on plans prior to grading/building permit issuance and/or recorded with the map during map recordation.

Conditions shall be adhered to throughout all grading and construction periods.

ATTACHMENT B

DIESEL PARTICULATE AND NOX EMISSION REDUCTION MEASURES
Particulate emissions from diesel exhaust are classified as carcinogenic by the state of California. The following is a list of regulatory requirements and control strategies that should be implemented to the maximum extent feasible.

The following measures are required by state law:
x All portable diesel-powered construction equipment greater than 50 brake horsepower (bhp) shall be registered with the state’s portable equipment registration program OR shall obtain an APCD permit. x Fleet owners of diesel-powered mobile construction equipment greater than 25 hp are subject to the California Air Resource Board (CARB) In-Use Off-Road Diesel-Fueled Fleets Regulation (Title 13, California Code of Regulations (CCR), §2449), the purpose of which is to reduce oxides of nitrogen (NOx), diesel particulate matter (DPM), and other criteria pollutant emissions from in-use off-road diesel-fueled vehicles. Off-road heavy-duty trucks shall comply with the State OffRoad Regulation. For more information, see www.arb.ca.gov/msprog/ordiesel/ordiesel.htm. x Fleet owners of diesel-fueled heavy-duty trucks and buses are subject to CARB’s On-Road Heavy-Duty Diesel Vehicles (InUse) Regulation (Title 13, CCR, §2025), the purpose of which is to reduce DPM, NOx and other criteria pollutants from inuse (on-road) diesel-fueled vehicles. For more information, see www.arb.ca.gov/msprog/onrdiesel/onrdiesel.htm. x All commercial off-road and on-road diesel vehicles are subject, respectively, to Title 13, CCR, §2449(d)(3) and §2485, limiting engine idling time. Off-road vehicles subject to the State Off-Road Regulation are limited to idling no more than five minutes. Idling of heavy-duty diesel trucks during loading and unloading shall be limited to five minutes, unless the truck engine meets the optional low-NOx idling emission standard, the truck is labeled with a clean-idle sticker, and it is not operating within 100 feet of a restricted area.

The following measures are recommended:
x Diesel equipment meeting the CARB Tier 3 or higher emission standards for off-road heavy-duty diesel engines should be used to the maximum extent feasible.
x On-road heavy-duty equipment with model year 2010 engines or newer should be used to the maximum extent feasible. x Diesel powered equipment should be replaced by electric equipment whenever feasible. Electric auxiliary power units should be used to the maximum extent feasible.
x Equipment/vehicles using alternative fuels, such as compressed natural gas (CNG), liquefied natural gas (LNG), propane or biodiesel, should be used on-site where feasible.
x Catalytic converters shall be installed on gasoline-powered equipment, if feasible. x All construction equipment shall be maintained in tune per the manufacturer’s specifications. x The engine size of construction equipment shall be the minimum practical size. x The number of construction equipment operating simultaneously shall be minimized through efficient management practices to ensure that the smallest practical number is operating at any one time. x Construction worker trips should be minimized by requiring carpooling and by providing for lunch onsite. x Construction truck trips should be scheduled during non-peak hours to reduce peak hour emissions whenever feasible. x Proposed truck routes should minimize to the extent feasible impacts to residential communities and sensitive receptors.
x Construction staging areas should be located away from sensitive receptors such that exhaust and other construction emissions do not enter the fresh air intakes to buildings, air conditioners, and windows.

PLAN REQUIREMENTS AND TIMING: Prior to grading/building permit issuance and/or map recordation, all requirements shall be shown as conditions of approval on grading/building plans, and/or on a separate sheet to be recorded with the map. Conditions shall be adhered to throughout all grading and construction periods. The contractor shall retain the Certificate of Compliance for CARB’s In-Use Regulation for Off-Road Diesel Vehicles onsite and have it available for inspection.

MONITORING: The Lead Agency shall ensure measures are on project plans and/or recorded with maps. The Lead Agency staff shall ensure compliance onsite. APCD inspectors will respond to nuisance complaints.
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VENTURA COUNTY

AIR POLLUTION CONTROL DISTRICT
Memorandum
TO: Nick Bobroff, Principal Planner
DATE: November 24, 2020
FROM: Nicole Collazo, Air Quality Specialist
SUBJECT: Comment Letter on Notice of Preparation of EIR for the Carpinteria Rincon Multi-Use Trail Project
Air Pollution Control District (APCD) staff has reviewed the subject Notice of Preparation (NOP) of a draft environmental impact report (EIR), which will identify any potential environmental impacts, for the construction and operation of the project mentioned above.

The Lead Agency for the project is the City of Carpinteria.

GENERAL COMMENTS
The project lies within the jurisdiction of Santa Barbara County and the Santa Barbara County Air Pollution Control District (SBCAPCD). However, due to the construction operations occurring immediately adjacent to a residential community within Ventura County, it is suggested that emission reduction measures and fugitive dust control measures are recommended for construction operations occurring on the eastern end of the construction site to avoid dust-driven or odor-driven violations from complaints within Ventura County.

A reference document such as the Ventura County Air Quality Assessment Guidelines (AQAG), or SBCAPCD’s guidelines for emission reduction measures for construction emissions are encouraged. We note that the AQAG has not been updated since 2003, serves as a guidance document, and greater reduction measures can be recommended for construction mitigation, including using newer, cleaner diesel Tier 3 or Tier 4 off-road engines and/or using on-road construction vehicles of year 2010 model or greater. These reduction measures can serve as a standard condition of approval for discretionary permit with Lead Agency in the case there are many sensitive receptors in the vicinity and/or if construction is expected to occur over several months. The diesel particulate matter (DPM) emissions from diesel-powered construction and grading equipment is a considered a toxic 2 air contaminant by the EPA and accounts for 70-80% of the overall cancer risk from mobile source emissions (CARB 2005 Land Use Handbook, MATES IV Study, respectively).

Thank you for the opportunity to comment on the project NOP. If you have any questions, you may reach me at [email protected].

Ventura County Resource Management Agency – Planning Division ~ 800 S. Victoria Avenue ~ Ventura, CA 93009-1740 November 6, 2020
Anthony Ciuffetelli
Ventura County Planning Division
Sent via email: [email protected]
Subject: Request for Comment on Carpinteria Rincon Multi-Use Trail Project RMA Reference #19-012-1
Dear Mr. Ciuffetelli,
Ventura County Cultural Heritage Board (CHB) Staff are in receipt of the Notice of Preparation (NOP) of an Environmental Impact Report (EIR) for the above-referenced projects. Thank you for the opportunity to review and comment on the proposed telecommunications tower. We have researched the subject site, as well as property within the vicinity, and found the following:
No listed or known historic resources eligible for listing are located on or near the subject site;
Areas in the vicinity of the subject site do exhibit a low potential to contain paleontological resources;
Areas in the vicinity of the subject site exhibits a high likelihood of containing archaeological resources (very sensitive).

A previous survey of the northern half of Ventura County indicated that “year-round settlements of Native Americans are located in areas of moderate winter climate, perennial water, and major plant communities for sustenance. […] Areas rich in natural resources, especially foods and implement materials, were sites of seasonal camp and food preparation sites.”1 We understand the subject area for the proposed project is located in the vicinity of natural waterways, including the Pacific Ocean and Rincon Creek.

Due to the aforementioned historical practices, combined with the project site’s proximity to these features, these activities could result in the subject area having a high sensitivity for tribal cultural resources. Therefore, it is recommended that outreach be conducted with relevant Native American tribes pursuant to federal and State law. 1 James, Susanne M., The North Half of Ventura County: Scenic, Biological and Cultural Resources, April 1986.

Comment Letter
November 6, 2020

Page 2 of 3 ends

Ventura County Resource Management Agency – Planning Division ~ 800 S. Victoria Avenue ~ Ventura, CA 93009-1740 Due to the potential paleontological and archaeological sensitivity of the subject site, implementation of the project could encounter previously undiscovered or unrecorded paleontological and archaeological sites, materials, and resources. Ground-disturbing activities have the potential to damage or destroy previously undiscovered or unrecorded paleontological and archaeological resources. Therefore, the following measures are recommended to reduce impacts to paleontological resources to the greatest extent feasible:
¾ The Applicant should retain a paleontological consultant or professional geologist to monitor all subsurface grading, trenching, or construction activities on the subject site;
¾ If any paleontological remains are uncovered during ground disturbance or construction activities, the Applicant should:
a. Cease operations and ensure the preservation of the area in which the discovery was made;
b. Notify the Lead Agency immediately;
c. Obtain the services of a qualified paleontological consultant or professional geologist to assess the find and provide a report that assesses the resources and sets forth recommendations on the proper disposition of the site;
d. Provide the paleontological report to the Lead Agency; e. Obtain the Lead Agency’s written concurrence with the recommended disposition of the site before resuming development; and f. Implement the agreed upon recommendations.

Additionally, based on the subject site’s high degree of sensitivity related to archeological resources, the following measures are recommended to reduce impacts to archaeological resources to the greatest extent feasible. Moreover, it is recommended that outreach be conducted with relevant Native American tribes to determine if known tribal cultural resources are present in the subject site area.
¾ The Applicant should retain a Native American monitor to monitor all subsurface grading, trenching, or construction activities on the subject site; ¾ If any archaeological or historical artifacts are uncovered during ground disturbance or construction activities, the Applicant should:
a. Cease operations and ensure the preservation of the area in which the discovery was made;
b. Notify the Lead Agency immediately;
c. Obtain the services of a qualified archaeologist who shall assess the find and provide recommendations on the proper disposition of the site in a written report format;
d. Provide the report to the Lead Agency;
Comment Letter
November 6, 2020

Page 3 of 3 ends

Ventura County Resource Management Agency – Planning Division ~ 800 S. Victoria Avenue ~ Ventura, CA 93009-1740 e. Obtain the Lead Agency’s written concurrence with the recommended disposition of the site before resuming development; and f. Implement the agreed upon recommendations.
¾ Consistent with Section 7050.5 of the California Health and Safety Code, if any human burial remains are encountered during ground disturbance or construction activities, the Applicant should:
a. Cease operations and ensure the preservation of the area in which the discovery was made;
b. Immediately notify the County Coroner and the Lead Agency; c. Obtain the services of a qualified archaeologist and, if necessary, Native American Monitor(s), who shall assess the find and provide recommendations on the proper disposition of the site in a written report format;
d. Provide the report to the Lead Agency;
e. Obtain the Lead Agency’s written concurrence with the recommended disposition of the site before resuming development; and f. Implement the agreed upon recommendations.

Thank you again for the opportunity to comment on the proposed project. If you require anything further or have questions regarding our findings, please do not hesitate to contact Dillan Murray at (805) 654-5042 or at [email protected].

Sincerely,
Dillan Murray
Cultural Heritage Program Planner
CC: Denice Thomas, Planning Programs Manager, Ventura County Planning Division Case File

WATERSHED PROTECTION

WATERSHED PLANNING AND PERMITS DIVISION
800 South Victoria Avenue, Ventura, California 93009
Sergio Vargas, Deputy Director – (805) 650-4077

M E M O R A N D U M
DATE: November 13, 2020
TO: Anthony Ciuffetelli RMA Case Planner
County of Ventura
FROM: Alex Hill, Engineer II – Advanced Planning Section SUBJECT: RMA19-012 Carpinteria Rincon Trail
Zone 4
Watershed Protection Project Number: WC2019-0081
Pursuant to your request dated October 30, 2020, this office has reviewed the submitted materials and provides the following comments.

PROJECT LOCATION:

The proposed Carpinteria Rincon Trail would extend from the eastern end of Carpinteria Avenue in the City of Carpinteria to the western end of Rincon Beach County Park and the Ventura County Line in Santa Barbara County.

PROJECT DESCRIPTION:

Watershed Protection previously provided a “No Comment” response on 11/6/2019 and the following comments provide context for that rationale. The proposed Carpinteria Rincon Trail would extend from the eastern end of Carpinteria Avenue, in the City of Carpinteria, to Rincon Beach County Park, in Santa Barbara County. The proposed shared-use trail would be 16-feet wide (10- foot wide path with 3-foot wide paved shoulder along both sides) and approximately 2,800-feet long and would include a clear-span bridge over the UPRR alignment. The bridge would be approximately 160-feet-long, with a width of between 14-feet and 16- feet (clear width, measured inside the bridge rails).

Earthwork for the trail construction would involve 104,000 cubic yards of cut, 10,300 cubic yards of which would be used for fill on-site and 94,100 cubic yards would be exported off-site. A storm drainage collection system is proposed, with new drain outlets to the ocean. The new, shared-use trail would provide a strategic addition to Carpinteria's Coastal Vista Trail that upon completion, would connect Padaro Lane to the west and Rincon Beach County Park to the east. In addition to providing critical improvements in public safety, the completion of this trail segment would provide improved public coastal access and recreational opportunities, and enhancement of non-vehicular travel alternatives to the region’s significant coastal resources.

RMA19-012 Carpinteria Rincon Trail
November 13, 2020

Page 2 of 2 ends

WATERSHED PROTECTION DISTRICT COMMENTS:

The following comments are intended to provide context for the application review process, and they require no further action.

Flood Control Facilities / Watercourses – Ventura County Watershed Protection District

1. The project is located to the West of Highway 101 within Santa Barbara and Ventura Counties. There are no proposed direct connections to any Ventura County Watershed Protection District Jurisdictional redline channel. Project drainage will be conveyed to three (3) existing and three (3) proposed storm drains that will discharge into the Pacific Ocean, therefore there is no impact to WP facilities.

Hydraulic Hazards – FEMA

2. The project site is in a location identified by the Federal Emergency Management Agency (FEMA) as an area of minimal flood hazard Zone X unshaded. This is evidenced on FEMA Map Panel 06083C1438H effective September 28, 2018. The proposed development is therefore, deemed to be Less than Significant for Hydraulic Hazards - FEMA.

If you have any questions, please feel free to contact me by email at [email protected] or by phone at (805) 654-3795.

END OF TEXT

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Wells Not Abandoned to Current Division Requirements as Prescribed by Law & Projected to be Built Over or Have Future Access Impeded dŚĞǁĞůůƐůŝƐƚĞĚďĞůŽǁĂƌĞŶŽƚĂďĂŶĚŽŶĞĚ ƚŽĐƵƌƌĞŶƚŝǀŝƐŝŽŶ ƌĞƋƵŝƌĞŵĞŶƚƐĂƐƉƌĞƐĐƌŝďĞĚďǇůĂǁ͕ĂŶĚ ďĂƐĞĚƵƉŽŶŝŶĨŽƌŵĂƚŝŽŶƉƌŽǀŝĚĞĚ͕ĂƌĞƉƌŽũĞĐƚĞĚ ƚŽďĞďƵŝůƚŽǀĞƌŽƌŚĂǀĞ ĨƵƚƵƌĞĂĐĐĞƐƐ ŝŵƉĞĚĞĚ͘The Division expects these wells to be reabandoned in compliance with current California law, prior to development activities.
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04083048
47 1 Dr. R. W.

Hill
Based on current well location and the currently planned trail location this well is projected to have the multi-use trail constructed over it.

Based on well records:

1. There is no record of an oil/gas zone plug (CCR § 1723.1)

2. There is no record of a freshwater plug (CCR § 1723.2)

3. There is no record of a casing shoe plug (CCR § 1723.3)

4. There is no record of a surface plug (CCR § 1723.5)

Page 5 ends

Appendix B
Air Quality and Greenhouse Gas Emissions Calculations

Table of Contents
Annual 2
Summer 36
Winter 65
CarbonSequstrationCalculation_20170127 94

1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Parking Lot 6.15 1000sqft 0.14 6,150.00 0
City Park 1.40 Acre 1.40 60,984.00 0

1.2 Other Project CharacteristicsUrbanizationClimate Zone Urban8
Wind Speed (m/s) Precipitation Freq (Days) 2.7 37

1.3 User Entered Comments & Non-Default Data1.0 Project CharacteristicsUtility Company Southern California Edison Operational Year 2024
CO2 Intensity (lb/MWhr)
702.44 0.029 CH4 Intensity
(lb/MWhr)
N2O Intensity 0.006(lb/MWhr)
Carpinteria Rincon Trail
Santa Barbara-South of Santa Ynez Range County, Annual
CalEEMod Version: CalEEMod.2016.3.2 Page 1 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual Project Characteristics -
Land Use - Construction Phase - Based on project description.Off-road Equipment - CalEEmod defaults.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Trips and VMT - CalEEMod defaults. Odd trips were rounded up to account for whole round trips.On-road Fugitive Dust - CalEEMod defaults.Grading - Based on City provided data.Architectural Coating - CalEEMod defaults.

Vehicle Trips - For maintenance, assumption of one trip per week.Energy Use - No energy use.Water And Wastewater - CalEEMod defaults.Solid Waste - CalEEMod defaults.Land Use Change - Sequestration - Construction Off-road Equipment Mitigation - In accordance with SBCAPCD Rule 345.Operational Off-Road Equipment - NA Table Name Column Name Default Value New Value
tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstructionPhase NumDays 2.00 32.00tblConstructionPhase NumDays 4.00 224.00tblConstructionPhase NumDays 200.00 96.00 CalEEMod Version: CalEEMod.2016.3.2 Page 2 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual tblConstructionPhase NumDays 200.00 10.00
tblConstructionPhase NumDays 10.00 32.00tblConstructionPhase NumDays 10.00 20.00 tblEnergyUse LightingElect 0.35 0.00
tblGrading MaterialExported 0.00 94,100.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 0.00 1.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 0.00 1.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 0.00 1.00tblOffRoadEquipment PhaseName Grading tblOffRoadEquipment PhaseName Trail ConstructiontblOffRoadEquipment PhaseName PavingtblOffRoadEquipment UsageHours 6.00 8.00 tblTripsAndVMT HaulingTripNumber 11,763.00 11,764.00tblTripsAndVMT VendorTripNumber 11.00 12.00tblTripsAndVMT VendorTripNumber 11.00 12.00tblTripsAndVMT WorkerTripNumber 5.00 6.00 CalEEMod Version: CalEEMod.2016.3.2 Page 3 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

2.0 Emissions Summary
tblVehicleTrips ST_TR 22.75 1.43tblVehicleTrips SU_TR 16.74 0.00tblVehicleTrips WD_TR 1.89 0.00 CalEEMod Version: CalEEMod.2016.3.2 Page 4 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

2.1 Overall Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year tons/yr MT/yr
2022 0.1415 2.4975 1.0291 5.3600e003 0.2978 0.0523 0.3501 0.0862 0.0482 0.1344 0.0000 522.4596 522.4596 0.0842 0.0000 524.56352023 0.0706 0.8524 0.5333 1.9500e003 0.1980 0.0253 0.2233 0.0355 0.0234 0.0589 0.0000 182.6620 182.6620 0.0359 0.0000 183.5604 Maximum 0.1415 2.4975 1.0291 5.3600e003 0.2978 0.0523 0.3501 0.0862 0.0482 0.1344 0.0000 522.4596 522.4596 0.0842 0.0000 524.5635 Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year tons/yr MT/yr
2022 0.1415 2.4975 1.0291 5.3600e003 0.1899 0.0523 0.2421 0.0539 0.0482 0.1021 0.0000 522.4594 522.4594 0.0842 0.0000 524.56332023 0.0706 0.8524 0.5333 1.9500e003 0.1411 0.0253 0.1664 0.0292 0.0234 0.0526 0.0000 182.6619 182.6619 0.0359 0.0000 183.5603 Maximum 0.1415 2.4975 1.0291 5.3600e003 0.1899 0.0523 0.2421 0.0539 0.0482 0.1021 0.0000 522.4594 522.4594 0.0842 0.0000 524.5633 Mitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction

0.00 0.00 0.00 0.00 33.24 0.00 28.75 31.72 0.00 19.97 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2016.3.2 Page 5 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Area 1.1900e003 0.0000 7.0000e- 005 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 1.3000e- 004 1.3000e- 004 0.0000 0.0000 1.4000e- 004 Energy 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Mobile 7.0000e005 2.4000e- 004 6.6000e- 004 0.0000 1.7000e- 004 0.0000 1.8000e- 004 5.0000e- 005 0.0000 5.0000e- 005 0.0000 0.1656 0.1656 1.0000e- 005 0.0000 0.1658 Waste 0.0000 0.0000 0.0000 0.0000 0.0249 0.0000 0.0249 1.2400e003 0.0000 0.0558 Water 0.0000 0.0000 0.0000 0.0000 0.0000 1.8602 1.8602 8.0000e005 2.0000e- 005 1.8669 Total 1.2600e003 2.4000e- 004 7.3000e- 004 0.0000 1.7000e- 004 0.0000 1.8000e- 004 5.0000e- 005 0.0000 5.0000e- 005 0.0249 2.0259 2.0508 1.3300e- 003 2.0000e- 005 2.0886 Unmitigated Operational
Quarter Start Date End Date Maximum Unmitigated ROG + NOX (tons/quarter) Maximum Mitigated ROG + NOX (tons/quarter) 1 3-1-2022 5-31-2022 0.6833 0.68332 6-1-2022 8-31-2022 0.8283 0.82833 9-1-2022 11-30-2022 0.8209 0.82094 12-1-2022 2-28-2023 0.6781 0.67815 3-1-2023 5-31-2023 0.2380 0.23806 6-1-2023 8-31-2023 0.2616 0.26167 9-1-2023 9-30-2023 0.0200 0.0200 Highest 0.8283 0.8283
CalEEMod Version: CalEEMod.2016.3.2 Page 6 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Area 1.1900e003 0.0000 7.0000e- 005 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 1.3000e- 004 1.3000e- 004 0.0000 0.0000 1.4000e- 004 Energy 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Mobile 7.0000e005 2.4000e- 004 6.6000e- 004 0.0000 1.7000e- 004 0.0000 1.8000e- 004 5.0000e- 005 0.0000 5.0000e- 005 0.0000 0.1656 0.1656 1.0000e- 005 0.0000 0.1658 Waste 0.0000 0.0000 0.0000 0.0000 0.0249 0.0000 0.0249 1.2400e003 0.0000 0.0558 Water 0.0000 0.0000 0.0000 0.0000 0.0000 1.8602 1.8602 8.0000e005 2.0000e- 005 1.8669 Total 1.2600e003 2.4000e- 004 7.3000e- 004 0.0000 1.7000e- 004 0.0000 1.8000e- 004 5.0000e- 005 0.0000 5.0000e- 005 0.0249 2.0259 2.0508 1.3300e- 003 2.0000e- 005 2.0886 Mitigated Operational3.0 Construction DetailConstruction Phase ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2016.3.2 Page 7 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Site Preparation Site Preparation 3/1/2022 4/13/2022 5 322 Grading Grading 4/14/2022 2/21/2023 5 2243 Trail Construction Building Construction 2/22/2023 7/5/2023 5 964 Bridge Construction Building Construction 7/6/2023 7/19/2023 5 105 Paving Paving 7/20/2023 9/1/2023 5 326 Architectural Coating Architectural Coating 9/2/2023 9/29/2023 5 20 OffRoad Equipment
Residential Indoor: 0; Residential Outdoor: 0; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area: 369 (Architectural Coating – sqft)Acres of Grading (Site Preparation Phase): 16 Acres of Grading (Grading Phase): 182
Acres of Paving: 0.14
CalEEMod Version: CalEEMod.2016.3.2 Page 8 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor Site Preparation Graders 1 8.00 187 0.41Site Preparation Rubber Tired Dozers 1 7.00 247 0.40Site Preparation Tractors/Loaders/Backhoes 1 8.00 97 0.37Grading Crawler Tractors 1 7.00 212 0.43Grading Graders 1 6.00 187 0.41Grading Rubber Tired Dozers 0 6.00 247 0.40Grading Tractors/Loaders/Backhoes 1 7.00 97 0.37Trail Construction Cranes 0 6.00 231 0.29Trail Construction Crawler Tractors 1 7.00 212 0.43Trail Construction Forklifts 0 6.00 89 0.20Trail Construction Generator Sets 0 8.00 84 0.74Trail Construction Tractors/Loaders/Backhoes 1 6.00 97 0.37Trail Construction Welders 0 8.00 46 0.45Bridge Construction Cranes 1 8.00 231 0.29Bridge Construction Forklifts 0 6.00 89 0.20Bridge Construction Generator Sets 0 8.00 84 0.74Bridge Construction Tractors/Loaders/Backhoes 1 6.00 97 0.37Bridge Construction Welders 3 8.00 46 0.45Paving Cement and Mortar Mixers 0 6.00 9 0.56Paving Crawler Tractors 1 8.00 212 0.43Paving Pavers 0 6.00 130 0.42Paving Paving Equipment 1 8.00 132 0.36Paving Rollers 0 7.00 80 0.38Paving Tractors/Loaders/Backhoes 0 8.00 97 0.37Architectural Coating Air Compressors 1 6.00 78 0.48 Trips and VMT
CalEEMod Version: CalEEMod.2016.3.2 Page 9 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.0928 0.0000 0.0928 0.0473 0.0000 0.0473 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0210 0.2340 0.1135 2.8000e004 9.9600e- 003 9.9600e- 003 9.1600e- 003 9.1600e- 003 0.0000 24.1844 24.1844 7.8200e- 003 0.0000 24.3800 Total 0.0210 0.2340 0.1135 2.8000e004 0.0928 9.9600e- 003 0.1028 0.0473 9.1600e- 003 0.0564 0.0000 24.1844 24.1844 7.8200e- 003 0.0000 24.3800 Unmitigated Construction On-Site3.1 Mitigation Measures ConstructionWater Exposed AreaReduce Vehicle Speed on Unpaved Roads Phase Name Offroad Equipment
Count
Worker Trip
Number
Vendor Trip
Number
Hauling Trip
Number
Worker Trip
Length
Vendor Trip
Length
Hauling Trip
Length
Worker Vehicle
Class
Vendor
Vehicle Class
Hauling
Vehicle Class
Site Preparation 3 8.00 0.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTGrading 3 8.00 0.00 11,764.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTTrail Construction 2 28.00 12.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTBridge Construction 5 28.00 12.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTPaving 2 6.00 0.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 6.00 0.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2016.3.2 Page 10 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 3.5000e004 2.8000e- 004 2.5000e- 003 1.0000e- 005 7.9000e- 004 0.0000 8.0000e- 004 2.1000e- 004 0.0000 2.1000e- 004 0.0000 0.6015 0.6015 2.0000e- 005 0.0000 0.6019 Total 3.5000e004 2.8000e- 004 2.5000e- 003 1.0000e- 005 7.9000e- 004 0.0000 8.0000e- 004 2.1000e- 004 0.0000 2.1000e- 004 0.0000 0.6015 0.6015 2.0000e- 005 0.0000 0.6019 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.0418 0.0000 0.0418 0.0213 0.0000 0.0213 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0210 0.2340 0.1135 2.8000e004 9.9600e- 003 9.9600e- 003 9.1600e- 003 9.1600e- 003 0.0000 24.1844 24.1844 7.8200e- 003 0.0000 24.3800 Total 0.0210 0.2340 0.1135 2.8000e004 0.0418 9.9600e- 003 0.0517 0.0213 9.1600e- 003 0.0304 0.0000 24.1844 24.1844 7.8200e- 003 0.0000 24.3800 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 11 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 3.5000e004 2.8000e- 004 2.5000e- 003 1.0000e- 005 7.9000e- 004 0.0000 8.0000e- 004 2.1000e- 004 0.0000 2.1000e- 004 0.0000 0.6015 0.6015 2.0000e- 005 0.0000 0.6019 Total 3.5000e004 2.8000e- 004 2.5000e- 003 1.0000e- 005 7.9000e- 004 0.0000 8.0000e- 004 2.1000e- 004 0.0000 2.1000e- 004 0.0000 0.6015 0.6015 2.0000e- 005 0.0000 0.6019 Mitigated Construction Off-Site3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.1035 0.0000 0.1035 0.0115 0.0000 0.0115 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0828 0.9973 0.4932 1.3600e003 0.0377 0.0377 0.0346 0.0346 0.0000 119.4881 119.4881 0.0386 0.0000 120.4543 Total 0.0828 0.9973 0.4932 1.3600e003 0.1035 0.0377 0.1411 0.0115 0.0346 0.0461 0.0000 119.4881 119.4881 0.0386 0.0000 120.4543 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 12 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0352 1.2643 0.4053 3.6700e003 0.0962 4.6100e- 003 0.1008 0.0260 4.4100e- 003 0.0304 0.0000 374.6704 374.6704 0.0376 0.0000 375.6097 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 2.0700e003 1.6100e- 003 0.0146 4.0000e- 005 4.6200e- 003 3.0000e- 005 4.6500e- 003 1.2300e- 003 3.0000e- 005 1.2500e- 003 0.0000 3.5151 3.5151 1.0000e- 004 0.0000 3.5176 Total 0.0373 1.2659 0.4199 3.7100e003 0.1008 4.6400e- 003 0.1054 0.0272 4.4400e- 003 0.0317 0.0000 378.1855 378.1855 0.0377 0.0000 379.1273 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.0466 0.0000 0.0466 5.1600e003 0.0000 5.1600e- 003 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0828 0.9973 0.4932 1.3600e003 0.0377 0.0377 0.0346 0.0346 0.0000 119.4880 119.4880 0.0386 0.0000 120.4541 Total 0.0828 0.9973 0.4932 1.3600e003 0.0466 0.0377 0.0842 5.1600e- 003 0.0346 0.0398 0.0000 119.4880 119.4880 0.0386 0.0000 120.4541 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 13 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0352 1.2643 0.4053 3.6700e003 0.0962 4.6100e- 003 0.1008 0.0260 4.4100e- 003 0.0304 0.0000 374.6704 374.6704 0.0376 0.0000 375.6097 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 2.0700e003 1.6100e- 003 0.0146 4.0000e- 005 4.6200e- 003 3.0000e- 005 4.6500e- 003 1.2300e- 003 3.0000e- 005 1.2500e- 003 0.0000 3.5151 3.5151 1.0000e- 004 0.0000 3.5176 Total 0.0373 1.2659 0.4199 3.7100e003 0.1008 4.6400e- 003 0.1054 0.0272 4.4400e- 003 0.0317 0.0000 378.1855 378.1855 0.0377 0.0000 379.1273 Mitigated Construction Off-Site3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.1035 0.0000 0.1035 0.0115 0.0000 0.0115 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0150 0.1724 0.0959 2.7000e004 6.5400e- 003 6.5400e- 003 6.0100e- 003 6.0100e- 003 0.0000 23.6305 23.6305 7.6400e- 003 0.0000 23.8216 Total 0.0150 0.1724 0.0959 2.7000e004 0.1035 6.5400e- 003 0.1100 0.0115 6.0100e- 003 0.0175 0.0000 23.6305 23.6305 7.6400e- 003 0.0000 23.8216 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 14 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 5.1300e003 0.1882 0.0751 7.0000e- 004 0.0798 4.6000e- 004 0.0803 0.0201 4.4000e- 004 0.0205 0.0000 72.2054 72.2054 7.4400e- 003 0.0000 72.3913 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 3.8000e004 2.9000e- 004 2.6400e- 003 1.0000e- 005 9.1000e- 004 1.0000e- 005 9.2000e- 004 2.4000e- 004 1.0000e- 005 2.5000e- 004 0.0000 0.6695 0.6695 2.0000e- 005 0.0000 0.6700 Total 5.5100e003 0.1885 0.0777 7.1000e- 004 0.0807 4.7000e- 004 0.0812 0.0203 4.5000e- 004 0.0208 0.0000 72.8749 72.8749 7.4600e- 003 0.0000 73.0613 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.0466 0.0000 0.0466 5.1600e003 0.0000 5.1600e- 003 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0150 0.1724 0.0959 2.7000e004 6.5400e- 003 6.5400e- 003 6.0100e- 003 6.0100e- 003 0.0000 23.6305 23.6305 7.6400e- 003 0.0000 23.8215 Total 0.0150 0.1724 0.0959 2.7000e004 0.0466 6.5400e- 003 0.0531 5.1600e- 003 6.0100e- 003 0.0112 0.0000 23.6305 23.6305 7.6400e- 003 0.0000 23.8215 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 15 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 5.1300e003 0.1882 0.0751 7.0000e- 004 0.0798 4.6000e- 004 0.0803 0.0201 4.4000e- 004 0.0205 0.0000 72.2054 72.2054 7.4400e- 003 0.0000 72.3913 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 3.8000e004 2.9000e- 004 2.6400e- 003 1.0000e- 005 9.1000e- 004 1.0000e- 005 9.2000e- 004 2.4000e- 004 1.0000e- 005 2.5000e- 004 0.0000 0.6695 0.6695 2.0000e- 005 0.0000 0.6700 Total 5.5100e003 0.1885 0.0777 7.1000e- 004 0.0807 4.7000e- 004 0.0812 0.0203 4.5000e- 004 0.0208 0.0000 72.8749 72.8749 7.4600e- 003 0.0000 73.0613 Mitigated Construction Off-Site3.4 Trail Construction - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.0241 0.2705 0.1746 4.4000e004 0.0111 0.0111 0.0102 0.0102 0.0000 38.7406 38.7406 0.0125 0.0000 39.0538 Total 0.0241 0.2705 0.1746 4.4000e004 0.0111 0.0111 0.0102 0.0102 0.0000 38.7406 38.7406 0.0125 0.0000 39.0538 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 16 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.4 Trail Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 1.3700e003 0.0462 0.0165 1.3000e- 004 3.3500e- 003 7.0000e- 005 3.4200e- 003 9.7000e- 004 7.0000e- 005 1.0400e- 003 0.0000 12.9763 12.9763 9.9000e- 004 0.0000 13.0009 Worker 3.4800e003 2.6000e- 003 0.0239 7.0000e- 005 8.3000e- 003 5.0000e- 005 8.3500e- 003 2.2100e- 003 5.0000e- 005 2.2500e- 003 0.0000 6.0798 6.0798 1.6000e- 004 0.0000 6.0839 Total 4.8500e003 0.0488 0.0405 2.0000e- 004 0.0117 1.2000e- 004 0.0118 3.1800e- 003 1.2000e- 004 3.2900e- 003 0.0000 19.0561 19.0561 1.1500e- 003 0.0000 19.0848 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.0241 0.2705 0.1746 4.4000e004 0.0111 0.0111 0.0102 0.0102 0.0000 38.7405 38.7405 0.0125 0.0000 39.0538 Total 0.0241 0.2705 0.1746 4.4000e004 0.0111 0.0111 0.0102 0.0102 0.0000 38.7405 38.7405 0.0125 0.0000 39.0538 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 17 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.4 Trail Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 1.3700e003 0.0462 0.0165 1.3000e- 004 3.3500e- 003 7.0000e- 005 3.4200e- 003 9.7000e- 004 7.0000e- 005 1.0400e- 003 0.0000 12.9763 12.9763 9.9000e- 004 0.0000 13.0009 Worker 3.4800e003 2.6000e- 003 0.0239 7.0000e- 005 8.3000e- 003 5.0000e- 005 8.3500e- 003 2.2100e- 003 5.0000e- 005 2.2500e- 003 0.0000 6.0798 6.0798 1.6000e- 004 0.0000 6.0839 Total 4.8500e003 0.0488 0.0405 2.0000e- 004 0.0117 1.2000e- 004 0.0118 3.1800e- 003 1.2000e- 004 3.2900e- 003 0.0000 19.0561 19.0561 1.1500e- 003 0.0000 19.0848 Mitigated Construction Off-Site3.5 Bridge Construction - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 6.1400e003 0.0461 0.0427 8.0000e- 005 1.9100e- 003 1.9100e- 003 1.8200e- 003 1.8200e- 003 0.0000 6.3840 6.3840 1.4600e- 003 0.0000 6.4205 Total 6.1400e003 0.0461 0.0427 8.0000e- 005 1.9100e- 003 1.9100e- 003 1.8200e- 003 1.8200e- 003 0.0000 6.3840 6.3840 1.4600e- 003 0.0000 6.4205 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 18 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.5 Bridge Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 1.4000e004 4.8100e- 003 1.7200e- 003 1.0000e- 005 3.5000e- 004 1.0000e- 005 3.6000e- 004 1.0000e- 004 1.0000e- 005 1.1000e- 004 0.0000 1.3517 1.3517 1.0000e- 004 0.0000 1.3543 Worker 3.6000e004 2.7000e- 004 2.4900e- 003 1.0000e- 005 8.6000e- 004 1.0000e- 005 8.7000e- 004 2.3000e- 004 0.0000 2.3000e- 004 0.0000 0.6333 0.6333 2.0000e- 005 0.0000 0.6337 Total 5.0000e004 5.0800e- 003 4.2100e- 003 2.0000e- 005 1.2100e- 003 2.0000e- 005 1.2300e- 003 3.3000e- 004 1.0000e- 005 3.4000e- 004 0.0000 1.9850 1.9850 1.2000e- 004 0.0000 1.9880 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 6.1400e003 0.0461 0.0427 8.0000e- 005 1.9100e- 003 1.9100e- 003 1.8200e- 003 1.8200e- 003 0.0000 6.3840 6.3840 1.4600e- 003 0.0000 6.4205 Total 6.1400e003 0.0461 0.0427 8.0000e- 005 1.9100e- 003 1.9100e- 003 1.8200e- 003 1.8200e- 003 0.0000 6.3840 6.3840 1.4600e- 003 0.0000 6.4205 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 19 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.5 Bridge Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 1.4000e004 4.8100e- 003 1.7200e- 003 1.0000e- 005 3.5000e- 004 1.0000e- 005 3.6000e- 004 1.0000e- 004 1.0000e- 005 1.1000e- 004 0.0000 1.3517 1.3517 1.0000e- 004 0.0000 1.3543 Worker 3.6000e004 2.7000e- 004 2.4900e- 003 1.0000e- 005 8.6000e- 004 1.0000e- 005 8.7000e- 004 2.3000e- 004 0.0000 2.3000e- 004 0.0000 0.6333 0.6333 2.0000e- 005 0.0000 0.6337 Total 5.0000e004 5.0800e- 003 4.2100e- 003 2.0000e- 005 1.2100e- 003 2.0000e- 005 1.2300e- 003 3.3000e- 004 1.0000e- 005 3.4000e- 004 0.0000 1.9850 1.9850 1.2000e- 004 0.0000 1.9880 Mitigated Construction Off-Site3.6 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 9.8400e003 0.1076 0.0768 1.9000e- 004 4.4300e- 003 4.4300e- 003 4.0700e- 003 4.0700e- 003 0.0000 16.7320 16.7320 5.4100e- 003 0.0000 16.8672 Paving 1.8000e004 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0100 0.1076 0.0768 1.9000e004 4.4300e- 003 4.4300e- 003 4.0700e- 003 4.0700e- 003 0.0000 16.7320 16.7320 5.4100e- 003 0.0000 16.8672 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 20 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.6 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 2.5000e004 1.9000e- 004 1.7100e- 003 0.0000 5.9000e- 004 0.0000 6.0000e- 004 1.6000e- 004 0.0000 1.6000e- 004 0.0000 0.4343 0.4343 1.0000e- 005 0.0000 0.4346 Total 2.5000e004 1.9000e- 004 1.7100e- 003 0.0000 5.9000e- 004 0.0000 6.0000e- 004 1.6000e- 004 0.0000 1.6000e- 004 0.0000 0.4343 0.4343 1.0000e- 005 0.0000 0.4346 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 9.8400e003 0.1076 0.0768 1.9000e- 004 4.4300e- 003 4.4300e- 003 4.0700e- 003 4.0700e- 003 0.0000 16.7319 16.7319 5.4100e- 003 0.0000 16.8672 Paving 1.8000e004 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0100 0.1076 0.0768 1.9000e004 4.4300e- 003 4.4300e- 003 4.0700e- 003 4.0700e- 003 0.0000 16.7319 16.7319 5.4100e- 003 0.0000 16.8672 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 21 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.6 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 2.5000e004 1.9000e- 004 1.7100e- 003 0.0000 5.9000e- 004 0.0000 6.0000e- 004 1.6000e- 004 0.0000 1.6000e- 004 0.0000 0.4343 0.4343 1.0000e- 005 0.0000 0.4346 Total 2.5000e004 1.9000e- 004 1.7100e- 003 0.0000 5.9000e- 004 0.0000 6.0000e- 004 1.6000e- 004 0.0000 1.6000e- 004 0.0000 0.4343 0.4343 1.0000e- 005 0.0000 0.4346 Mitigated Construction Off-Site3.7 Architectural Coating - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Archit. Coating 2.1400e003 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 1.9200e003 0.0130 0.0181 3.0000e- 005 7.1000e- 004 7.1000e- 004 7.1000e- 004 7.1000e- 004 0.0000 2.5533 2.5533 1.5000e- 004 0.0000 2.5571 Total 4.0600e003 0.0130 0.0181 3.0000e- 005 7.1000e- 004 7.1000e- 004 7.1000e- 004 7.1000e- 004 0.0000 2.5533 2.5533 1.5000e- 004 0.0000 2.5571 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 22 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

3.7 Architectural Coating - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 1.6000e004 1.2000e- 004 1.0700e- 003 0.0000 3.7000e- 004 0.0000 3.7000e- 004 1.0000e- 004 0.0000 1.0000e- 004 0.0000 0.2714 0.2714 1.0000e- 005 0.0000 0.2716 Total 1.6000e004 1.2000e- 004 1.0700e- 003 0.0000 3.7000e- 004 0.0000 3.7000e- 004 1.0000e- 004 0.0000 1.0000e- 004 0.0000 0.2714 0.2714 1.0000e- 005 0.0000 0.2716 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Archit. Coating 2.1400e003 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 1.9200e003 0.0130 0.0181 3.0000e- 005 7.1000e- 004 7.1000e- 004 7.1000e- 004 7.1000e- 004 0.0000 2.5533 2.5533 1.5000e- 004 0.0000 2.5571 Total 4.0600e003 0.0130 0.0181 3.0000e- 005 7.1000e- 004 7.1000e- 004 7.1000e- 004 7.1000e- 004 0.0000 2.5533 2.5533 1.5000e- 004 0.0000 2.5571 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 23 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

4.0 Operational Detail - Mobile

4.1 Mitigation Measures Mobile3.7 Architectural Coating - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 1.6000e004 1.2000e- 004 1.0700e- 003 0.0000 3.7000e- 004 0.0000 3.7000e- 004 1.0000e- 004 0.0000 1.0000e- 004 0.0000 0.2714 0.2714 1.0000e- 005 0.0000 0.2716 Total 1.6000e004 1.2000e- 004 1.0700e- 003 0.0000 3.7000e- 004 0.0000 3.7000e- 004 1.0000e- 004 0.0000 1.0000e- 004 0.0000 0.2714 0.2714 1.0000e- 005 0.0000 0.2716 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 24 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 7.0000e005 2.4000e- 004 6.6000e- 004 0.0000 1.7000e- 004 0.0000 1.8000e- 004 5.0000e- 005 0.0000 5.0000e- 005 0.0000 0.1656 0.1656 1.0000e- 005 0.0000 0.1658 Unmitigated 7.0000e005 2.4000e- 004 6.6000e- 004 0.0000 1.7000e- 004 0.0000 1.8000e- 004 5.0000e- 005 0.0000 5.0000e- 005 0.0000 0.1656 0.1656 1.0000e- 005 0.0000 0.1658

4.2 Trip Summary Information4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
City Park 0.00 2.00 0.00 459 459
Parking Lot 0.00 0.00 0.00
Total 0.00 2.00 0.00 459 459
Miles Trip % Trip Purpose %
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C H-O or C-NW Primary Diverted Pass-by City Park 6.60 5.50 6.40 33.00 48.00 19.00 66 28 6
Parking Lot 6.60 5.50 6.40 0.00 0.00 0.00 0 0 0

4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH City Park 0.572071 0.027190 0.206810 0.117824 0.018361 0.005136 0.017629 0.020081 0.002790 0.002084 0.006580 0.002569 0.000873 Parking Lot 0.572071 0.027190 0.206810 0.117824 0.018361 0.005136 0.017629 0.020081 0.002790 0.002084 0.006580 0.002569 0.000873 CalEEMod Version: CalEEMod.2016.3.2 Page 25 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

5.0 Energy Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Electricity
Mitigated

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Electricity
Unmitigated

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 NaturalGas
Mitigated

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 NaturalGasUnmitigated

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000

5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2016.3.2 Page 26 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr tons/yr MT/yr
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Parking Lot 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Unmitigated
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr tons/yr MT/yr
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Parking Lot 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 27 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

6.1 Mitigation Measures Area

6.0 Area Detail5.3 Energy by Land Use - Electricity
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
City Park 0 0.0000 0.0000 0.0000 0.0000
Parking Lot 0 0.0000 0.0000 0.0000 0.0000
Total 0.0000 0.0000 0.0000 0.0000
Unmitigated
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
City Park 0 0.0000 0.0000 0.0000 0.0000
Parking Lot 0 0.0000 0.0000 0.0000 0.0000
Total 0.0000 0.0000 0.0000 0.0000
Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 28 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 1.1900e003 0.0000 7.0000e- 005 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 1.3000e- 004 1.3000e- 004 0.0000 0.0000 1.4000e- 004 Unmitigated 1.1900e003 0.0000 7.0000e- 005 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 1.3000e- 004 1.3000e- 004 0.0000 0.0000 1.4000e- 004

6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory tons/yr MT/yr
Architectural
Coating

2.1000e004 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Consumer
Products

9.7000e004 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Landscaping 1.0000e005 0.0000 7.0000e- 005 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 1.3000e- 004 1.3000e- 004 0.0000 0.0000 1.4000e- 004 Total 1.1900e003 0.0000 7.0000e- 005 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 1.3000e- 004 1.3000e- 004 0.0000 0.0000 1.4000e- 004 Unmitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 29 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

7.1 Mitigation Measures Water

7.0 Water Detail

2.1000e004 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Consumer
Products

9.7000e004 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Landscaping 1.0000e005 0.0000 7.0000e- 005 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 1.3000e- 004 1.3000e- 004 0.0000 0.0000 1.4000e- 004 Total 1.1900e003 0.0000 7.0000e- 005 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 1.3000e- 004 1.3000e- 004 0.0000 0.0000 1.4000e- 004 Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 30 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual Total CO2 CH4 N2O CO2e
Category MT/yr
Mitigated 1.8602 8.0000e005 2.0000e- 005 1.8669
Unmitigated 1.8602 8.0000e005 2.0000e- 005 1.8669

7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
City Park 0 /

1.66807

1.8602 8.0000e005 2.0000e- 005 1.8669
Parking Lot 0 / 0 0.0000 0.0000 0.0000 0.0000
Total 1.8602 8.0000e005 2.0000e- 005 1.8669
Unmitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 31 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

8.1 Mitigation Measures Waste

7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
City Park 0 /

1.66807

1.8602 8.0000e005 2.0000e- 005 1.8669
Parking Lot 0 / 0 0.0000 0.0000 0.0000 0.0000
Total 1.8602 8.0000e005 2.0000e- 005 1.8669
Mitigated

8.0 Waste Detail
Total CO2 CH4 N2O CO2e
MT/yr
Mitigated 0.0249 1.2400e003 0.0000 0.0558
Unmitigated 0.0249 1.2400e003 0.0000 0.0558
Category/Year
CalEEMod Version: CalEEMod.2016.3.2 Page 32 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

8.2 Waste by Land Use
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
City Park 0.12 0.0249 1.2400e003 0.0000 0.0558
Parking Lot 0 0.0000 0.0000 0.0000 0.0000
Total 0.0249 1.2400e003 0.0000 0.0558
Unmitigated
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
City Park 0.12 0.0249 1.2400e003 0.0000 0.0558
Parking Lot 0 0.0000 0.0000 0.0000 0.0000
Total 0.0249 1.2400e003 0.0000 0.0558
Mitigated

9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type CalEEMod Version: CalEEMod.2016.3.2 Page 33 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

11.0 Vegetation

10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2016.3.2 Page 34 of 34 Date: 12/15/2020 2:27 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Annual

1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Parking Lot 6.15 1000sqft 0.14 6,150.00 0
City Park 1.40 Acre 1.40 60,984.00 0

1.2 Other Project CharacteristicsUrbanizationClimate Zone Urban8
Wind Speed (m/s) Precipitation Freq (Days) 2.7 37

1.3 User Entered Comments & Non-Default Data1.0 Project CharacteristicsUtility Company Southern California Edison Operational Year 2024
CO2 Intensity (lb/MWhr)
702.44 0.029 CH4 Intensity
(lb/MWhr)
N2O Intensity 0.006(lb/MWhr)
Carpinteria Rincon Trail
Santa Barbara-South of Santa Ynez Range County, Summer
CalEEMod Version: CalEEMod.2016.3.2 Page 1 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer Project Characteristics -
Land Use - Construction Phase - Based on project description.Off-road Equipment - CalEEmod defaults.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Trips and VMT - CalEEMod defaults. Odd trips were rounded up to account for whole round trips.On-road Fugitive Dust - CalEEMod defaults.Grading - Based on City provided data.Architectural Coating - CalEEMod defaults.

Vehicle Trips - For maintenance, assumption of one trip per week.Energy Use - No energy use.Water And Wastewater - CalEEMod defaults.Solid Waste - CalEEMod defaults.Land Use Change - Sequestration - Construction Off-road Equipment Mitigation - In accordance with SBCAPCD Rule 345.Operational Off-Road Equipment - NA Table Name Column Name Default Value New Value
tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstructionPhase NumDays 2.00 32.00tblConstructionPhase NumDays 4.00 224.00tblConstructionPhase NumDays 200.00 96.00 CalEEMod Version: CalEEMod.2016.3.2 Page 2 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer tblConstructionPhase NumDays 200.00 10.00
tblConstructionPhase NumDays 10.00 32.00tblConstructionPhase NumDays 10.00 20.00 tblEnergyUse LightingElect 0.35 0.00
tblGrading MaterialExported 0.00 94,100.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 0.00 1.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 0.00 1.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 0.00 1.00tblOffRoadEquipment PhaseName Grading tblOffRoadEquipment PhaseName Trail ConstructiontblOffRoadEquipment PhaseName PavingtblOffRoadEquipment UsageHours 6.00 8.00 tblTripsAndVMT HaulingTripNumber 11,763.00 11,764.00tblTripsAndVMT VendorTripNumber 11.00 12.00tblTripsAndVMT VendorTripNumber 11.00 12.00tblTripsAndVMT WorkerTripNumber 5.00 6.00 CalEEMod Version: CalEEMod.2016.3.2 Page 3 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

2.0 Emissions Summary
tblVehicleTrips ST_TR 22.75 1.43tblVehicleTrips SU_TR 16.74 0.00tblVehicleTrips WD_TR 1.89 0.00 CalEEMod Version: CalEEMod.2016.3.2 Page 4 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

2.1 Overall Construction (Maximum Daily Emission)
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2022 1.3337 23.9289 9.6900 0.0545 5.8501 0.6228 6.4729 2.9671 0.5730 3.5401 0.0000 5,894.174 1 5,894.174
1 0.8960 0.0000 5,916.574
8 2023 1.3266 19.3246 9.3649 0.0533 5.3957 0.3841 5.7738 1.2267 0.3667 1.5755 0.0000 5,776.919 7 5,776.919
7 0.8964 0.0000 5,799.329
6 Maximum 1.3337 23.9289 9.6900 0.0545 5.8501 0.6228 6.4729 2.9671 0.5730 3.5401 0.0000 5,894.174 1 5,894.174
1 0.8964 0.0000 5,916.574
8 Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2022 1.3337 23.9289 9.6900 0.0545 2.6603 0.6228 3.2832 1.3426 0.5730 1.9156 0.0000 5,894.174 1 5,894.174
1 0.8960 0.0000 5,916.574
8 2023 1.3266 19.3246 9.3649 0.0533 4.8877 0.3841 5.2658 1.1704 0.3667 1.5192 0.0000 5,776.919 7 5,776.919
7 0.8964 0.0000 5,799.329
6 Maximum 1.3337 23.9289 9.6900 0.0545 4.8877 0.6228 5.2658 1.3426 0.5730 1.9156 0.0000 5,894.174 1 5,894.174
1 0.8964 0.0000 5,916.574
8 Mitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction

0.00 0.00 0.00 0.00 32.88 0.00 30.19 40.08 0.00 32.86 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2016.3.2 Page 5 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 6.5600e003 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003 Energy 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Mobile 2.7600e003 9.0100e- 003 0.0243 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 7.1577 7.1577 3.4000e- 004 7.1662 Total 9.3200e003 9.0200e- 003 0.0251 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 7.1593 7.1593 3.4000e- 004 0.0000 7.1680 Unmitigated Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 6.5600e003 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003 Energy 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Mobile 2.7600e003 9.0100e- 003 0.0243 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 7.1577 7.1577 3.4000e- 004 7.1662 Total 9.3200e003 9.0200e- 003 0.0251 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 7.1593 7.1593 3.4000e- 004 0.0000 7.1680 Mitigated Operational
CalEEMod Version: CalEEMod.2016.3.2 Page 6 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Site Preparation Site Preparation 3/1/2022 4/13/2022 5 322 Grading Grading 4/14/2022 2/21/2023 5 2243 Trail Construction Building Construction 2/22/2023 7/5/2023 5 964 Bridge Construction Building Construction 7/6/2023 7/19/2023 5 105 Paving Paving 7/20/2023 9/1/2023 5 326 Architectural Coating Architectural Coating 9/2/2023 9/29/2023 5 20 OffRoad Equipment
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Residential Indoor: 0; Residential Outdoor: 0; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area: 369 (Architectural Coating – sqft)Acres of Grading (Site Preparation Phase): 16 Acres of Grading (Grading Phase): 182Acres of Paving: 0.14 CalEEMod Version: CalEEMod.2016.3.2 Page 7 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor Site Preparation Graders 1 8.00 187 0.41Site Preparation Rubber Tired Dozers 1 7.00 247 0.40Site Preparation Tractors/Loaders/Backhoes 1 8.00 97 0.37Grading Crawler Tractors 1 7.00 212 0.43Grading Graders 1 6.00 187 0.41Grading Rubber Tired Dozers 0 6.00 247 0.40Grading Tractors/Loaders/Backhoes 1 7.00 97 0.37Trail Construction Cranes 0 6.00 231 0.29Trail Construction Crawler Tractors 1 7.00 212 0.43Trail Construction Forklifts 0 6.00 89 0.20Trail Construction Generator Sets 0 8.00 84 0.74Trail Construction Tractors/Loaders/Backhoes 1 6.00 97 0.37Trail Construction Welders 0 8.00 46 0.45Bridge Construction Cranes 1 8.00 231 0.29Bridge Construction Forklifts 0 6.00 89 0.20Bridge Construction Generator Sets 0 8.00 84 0.74Bridge Construction Tractors/Loaders/Backhoes 1 6.00 97 0.37Bridge Construction Welders 3 8.00 46 0.45Paving Cement and Mortar Mixers 0 6.00 9 0.56Paving Crawler Tractors 1 8.00 212 0.43Paving Pavers 0 6.00 130 0.42Paving Paving Equipment 1 8.00 132 0.36Paving Rollers 0 7.00 80 0.38Paving Tractors/Loaders/Backhoes 0 8.00 97 0.37Architectural Coating Air Compressors 1 6.00 78 0.48 Trips and VMT
CalEEMod Version: CalEEMod.2016.3.2 Page 8 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 5.7996 0.0000 5.7996 2.9537 0.0000 2.9537 0.0000 0.0000 Off-Road 1.3122 14.6277 7.0939 0.0172 0.6225 0.6225 0.5727 0.5727 1,666.173 8 1,666.173
8 0.5389 1,679.645
7 Total 1.3122 14.6277 7.0939 0.0172 5.7996 0.6225 6.4221 2.9537 0.5727 3.5264 1,666.173 8 1,666.173
8 0.5389 1,679.645
7 Unmitigated Construction On-Site3.1 Mitigation Measures ConstructionWater Exposed AreaReduce Vehicle Speed on Unpaved Roads Phase Name Offroad Equipment
Count
Worker Trip
Number
Vendor Trip
Number
Hauling Trip
Number
Worker Trip
Length
Vendor Trip
Length
Hauling Trip
Length
Worker Vehicle
Class
Vendor
Vehicle Class
Hauling
Vehicle Class
Site Preparation 3 8.00 0.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTGrading 3 8.00 0.00 11,764.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTTrail Construction 2 28.00 12.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTBridge Construction 5 28.00 12.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTPaving 2 6.00 0.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 6.00 0.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2016.3.2 Page 9 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0216 0.0154 0.1548 4.3000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 42.3628 42.3628 1.2000e- 003 42.3929 Total 0.0216 0.0154 0.1548 4.3000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 42.3628 42.3628 1.2000e- 003 42.3929 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 2.6098 0.0000 2.6098 1.3292 0.0000 1.3292 0.0000 0.0000 Off-Road 1.3122 14.6277 7.0939 0.0172 0.6225 0.6225 0.5727 0.5727 0.0000 1,666.173 8 1,666.173
8 0.5389 1,679.645
7 Total 1.3122 14.6277 7.0939 0.0172 2.6098 0.6225 3.2323 1.3292 0.5727 1.9019 0.0000 1,666.173 8 1,666.173
8 0.5389 1,679.645
7 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 10 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0216 0.0154 0.1548 4.3000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 42.3628 42.3628 1.2000e- 003 42.3929 Total 0.0216 0.0154 0.1548 4.3000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 42.3628 42.3628 1.2000e- 003 42.3929 Mitigated Construction Off-Site3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.9237 0.0000 0.9237 0.1024 0.0000 0.1024 0.0000 0.0000 Off-Road 0.8858 10.6663 5.2750 0.0146 0.4026 0.4026 0.3704 0.3704 1,408.696 6 1,408.696
6 0.4556 1,420.086
6 Total 0.8858 10.6663 5.2750 0.0146 0.9237 0.4026 1.3263 0.1024 0.3704 0.4729 1,408.696 6 1,408.696
6 0.4556 1,420.086
6 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 11 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.3727 13.2472 4.2603 0.0395 1.0497 0.0488 1.0984 0.2833 0.0467 0.3299 4,443.114 7 4,443.114
7 0.4392 4,454.095
4 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0216 0.0154 0.1548 4.3000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 42.3628 42.3628 1.2000e- 003 42.3929 Total 0.3943 13.2627 4.4151 0.0400 1.1002 0.0491 1.1493 0.2967 0.0470 0.3436 4,485.477 5 4,485.477
5 0.4404 4,496.488
2 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.4157 0.0000 0.4157 0.0461 0.0000 0.0461 0.0000 0.0000 Off-Road 0.8858 10.6663 5.2750 0.0146 0.4026 0.4026 0.3704 0.3704 0.0000 1,408.696 6 1,408.696
6 0.4556 1,420.086
6 Total 0.8858 10.6663 5.2750 0.0146 0.4157 0.4026 0.8183 0.0461 0.3704 0.4165 0.0000 1,408.696 6 1,408.696
6 0.4556 1,420.086
6 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 12 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.3727 13.2472 4.2603 0.0395 1.0497 0.0488 1.0984 0.2833 0.0467 0.3299 4,443.114 7 4,443.114
7 0.4392 4,454.095
4 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0216 0.0154 0.1548 4.3000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 42.3628 42.3628 1.2000e- 003 42.3929 Total 0.3943 13.2627 4.4151 0.0400 1.1002 0.0491 1.1493 0.2967 0.0470 0.3436 4,485.477 5 4,485.477
5 0.4404 4,496.488
2 Mitigated Construction Off-Site3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.9237 0.0000 0.9237 0.1024 0.0000 0.1024 0.0000 0.0000 Off-Road 0.8087 9.3175 5.1851 0.0145 0.3533 0.3533 0.3250 0.3250 1,408.008 6 1,408.008
6 0.4554 1,419.393
0 Total 0.8087 9.3175 5.1851 0.0145 0.9237 0.3533 1.2770 0.1024 0.3250 0.4275 1,408.008 6 1,408.008
6 0.4554 1,419.393
0 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 13 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.2745 9.9933 4.0031 0.0383 4.4215 0.0246 4.4461 1.1109 0.0235 1.1344 4,328.131 8 4,328.131
8 0.4399 4,339.130
4 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0201 0.0138 0.1414 4.1000e004 0.0505 2.9000e- 004 0.0508 0.0134 2.7000e- 004 0.0137 40.7793 40.7793 1.0700e- 003 40.8062 Total 0.2946 10.0071 4.1446 0.0387 4.4720 0.0249 4.4969 1.1243 0.0238 1.1481 4,368.911 1 4,368.911
1 0.4410 4,379.936
6 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.4157 0.0000 0.4157 0.0461 0.0000 0.0461 0.0000 0.0000 Off-Road 0.8087 9.3175 5.1851 0.0145 0.3533 0.3533 0.3250 0.3250 0.0000 1,408.008 6 1,408.008
6 0.4554 1,419.393
0 Total 0.8087 9.3175 5.1851 0.0145 0.4157 0.3533 0.7690 0.0461 0.3250 0.3711 0.0000 1,408.008 6 1,408.008
6 0.4554 1,419.393
0 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 14 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.2745 9.9933 4.0031 0.0383 4.4215 0.0246 4.4461 1.1109 0.0235 1.1344 4,328.131 8 4,328.131
8 0.4399 4,339.130
4 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0201 0.0138 0.1414 4.1000e004 0.0505 2.9000e- 004 0.0508 0.0134 2.7000e- 004 0.0137 40.7793 40.7793 1.0700e- 003 40.8062 Total 0.2946 10.0071 4.1446 0.0387 4.4720 0.0249 4.4969 1.1243 0.0238 1.1481 4,368.911 1 4,368.911
1 0.4410 4,379.936
6 Mitigated Construction Off-Site3.4 Trail Construction - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.5022 5.6358 3.6367 9.1900e003 0.2308 0.2308 0.2123 0.2123 889.6701 889.6701 0.2877 896.8636 Total 0.5022 5.6358 3.6367 9.1900e003 0.2308 0.2308 0.2123 0.2123 889.6701 889.6701 0.2877 896.8636 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 15 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.4 Trail Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0278 0.9535 0.3281 2.7500e003 0.0711 1.5000e- 003 0.0726 0.0204 1.4300e- 003 0.0219 301.0654 301.0654 0.0222 301.6204 Worker 0.0705 0.0484 0.4950 1.4300e003 0.1768 1.0300e- 003 0.1779 0.0469 9.5000e- 004 0.0479 142.7277 142.7277 3.7600e- 003 142.8216 Total 0.0983 1.0019 0.8232 4.1800e003 0.2479 2.5300e- 003 0.2504 0.0674 2.3800e- 003 0.0697 443.7930 443.7930 0.0260 444.4420 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.5022 5.6358 3.6367 9.1900e003 0.2308 0.2308 0.2123 0.2123 0.0000 889.6701 889.6701 0.2877 896.8636 Total 0.5022 5.6358 3.6367 9.1900e003 0.2308 0.2308 0.2123 0.2123 0.0000 889.6701 889.6701 0.2877 896.8636 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 16 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.4 Trail Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0278 0.9535 0.3281 2.7500e003 0.0711 1.5000e- 003 0.0726 0.0204 1.4300e- 003 0.0219 301.0654 301.0654 0.0222 301.6204 Worker 0.0705 0.0484 0.4950 1.4300e003 0.1768 1.0300e- 003 0.1779 0.0469 9.5000e- 004 0.0479 142.7277 142.7277 3.7600e- 003 142.8216 Total 0.0983 1.0019 0.8232 4.1800e003 0.2479 2.5300e- 003 0.2504 0.0674 2.3800e- 003 0.0697 443.7930 443.7930 0.0260 444.4420 Mitigated Construction Off-Site3.5 Bridge Construction - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.2283 9.2289 8.5417 0.0158 0.3816 0.3816 0.3643 0.3643 1,407.434 8 1,407.434
8 0.3218 1,415.479
6 Total 1.2283 9.2289 8.5417 0.0158 0.3816 0.3816 0.3643 0.3643 1,407.434 8 1,407.434
8 0.3218 1,415.479
6 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 17 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.5 Bridge Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0278 0.9535 0.3281 2.7500e003 0.0711 1.5000e- 003 0.0726 0.0204 1.4300e- 003 0.0219 301.0654 301.0654 0.0222 301.6204 Worker 0.0705 0.0484 0.4950 1.4300e003 0.1768 1.0300e- 003 0.1779 0.0469 9.5000e- 004 0.0479 142.7277 142.7277 3.7600e- 003 142.8216 Total 0.0983 1.0019 0.8232 4.1800e003 0.2479 2.5300e- 003 0.2504 0.0674 2.3800e- 003 0.0697 443.7930 443.7930 0.0260 444.4420 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.2283 9.2289 8.5417 0.0158 0.3816 0.3816 0.3643 0.3643 0.0000 1,407.434 8 1,407.434
8 0.3218 1,415.479
6 Total 1.2283 9.2289 8.5417 0.0158 0.3816 0.3816 0.3643 0.3643 0.0000 1,407.434 8 1,407.434
8 0.3218 1,415.479
6 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 18 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.5 Bridge Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0278 0.9535 0.3281 2.7500e003 0.0711 1.5000e- 003 0.0726 0.0204 1.4300e- 003 0.0219 301.0654 301.0654 0.0222 301.6204 Worker 0.0705 0.0484 0.4950 1.4300e003 0.1768 1.0300e- 003 0.1779 0.0469 9.5000e- 004 0.0479 142.7277 142.7277 3.7600e- 003 142.8216 Total 0.0983 1.0019 0.8232 4.1800e003 0.2479 2.5300e- 003 0.2504 0.0674 2.3800e- 003 0.0697 443.7930 443.7930 0.0260 444.4420 Mitigated Construction Off-Site3.6 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.6149 6.7275 4.8004 0.0119 0.2767 0.2767 0.2546 0.2546 1,152.738 8 1,152.738
8 0.3728 1,162.059
3 Paving 0.0115 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.6263 6.7275 4.8004 0.0119 0.2767 0.2767 0.2546 0.2546 1,152.738 8 1,152.738
8 0.3728 1,162.059
3 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 19 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.6 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0151 0.0104 0.1061 3.1000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 30.5845 30.5845 8.0000e- 004 30.6046 Total 0.0151 0.0104 0.1061 3.1000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 30.5845 30.5845 8.0000e- 004 30.6046 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.6149 6.7275 4.8004 0.0119 0.2767 0.2767 0.2546 0.2546 0.0000 1,152.738 8 1,152.738
8 0.3728 1,162.059
3 Paving 0.0115 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.6263 6.7275 4.8004 0.0119 0.2767 0.2767 0.2546 0.2546 0.0000 1,152.738 8 1,152.738
8 0.3728 1,162.059
3 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 20 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.6 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0151 0.0104 0.1061 3.1000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 30.5845 30.5845 8.0000e- 004 30.6046 Total 0.0151 0.0104 0.1061 3.1000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 30.5845 30.5845 8.0000e- 004 30.6046 Mitigated Construction Off-Site3.7 Architectural Coating - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 0.2138 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.1917 1.3030 1.8111 2.9700e003 0.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690 Total 0.4055 1.3030 1.8111 2.9700e003 0.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 21 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

3.7 Architectural Coating - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0151 0.0104 0.1061 3.1000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 30.5845 30.5845 8.0000e- 004 30.6046 Total 0.0151 0.0104 0.1061 3.1000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 30.5845 30.5845 8.0000e- 004 30.6046 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 0.2138 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.1917 1.3030 1.8111 2.9700e003 0.0708 0.0708 0.0708 0.0708 0.0000 281.4481 281.4481 0.0168 281.8690 Total 0.4055 1.3030 1.8111 2.9700e003 0.0708 0.0708 0.0708 0.0708 0.0000 281.4481 281.4481 0.0168 281.8690 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 22 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

4.0 Operational Detail - Mobile

4.1 Mitigation Measures Mobile3.7 Architectural Coating - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0151 0.0104 0.1061 3.1000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 30.5845 30.5845 8.0000e- 004 30.6046 Total 0.0151 0.0104 0.1061 3.1000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 30.5845 30.5845 8.0000e- 004 30.6046 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 23 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 2.7600e003 9.0100e- 003 0.0243 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 7.1577 7.1577 3.4000e- 004 7.1662 Unmitigated 2.7600e003 9.0100e- 003 0.0243 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 7.1577 7.1577 3.4000e- 004 7.1662

4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH City Park 0.572071 0.027190 0.206810 0.117824 0.018361 0.005136 0.017629 0.020081 0.002790 0.002084 0.006580 0.002569 0.000873 Parking Lot 0.572071 0.027190 0.206810 0.117824 0.018361 0.005136 0.017629 0.020081 0.002790 0.002084 0.006580 0.002569 0.000873 CalEEMod Version: CalEEMod.2016.3.2 Page 24 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

5.0 Energy Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
NaturalGas
Mitigated

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 NaturalGasUnmitigated

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000

5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2016.3.2 Page 25 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

6.1 Mitigation Measures Area

6.0 Area Detail5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Parking Lot 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Unmitigated
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Parking Lot 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 26 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 6.5600e003 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003 Unmitigated 6.5600e003 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003

6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating

1.1700e003 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products

5.3200e003 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Landscaping 7.0000e005 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003 Total 6.5600e003 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003 Unmitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 27 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

8.1 Mitigation Measures Waste

7.1 Mitigation Measures Water7.0 Water Detail8.0 Waste Detail

1.1700e003 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products

9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type

10.0 Stationary Equipment
Fire Pumps and Emergency Generators
CalEEMod Version: CalEEMod.2016.3.2 Page 28 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

11.0 Vegetation
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2016.3.2 Page 29 of 29 Date: 12/15/2020 2:28 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Summer

1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Parking Lot 6.15 1000sqft 0.14 6,150.00 0
City Park 1.40 Acre 1.40 60,984.00 0

1.2 Other Project CharacteristicsUrbanizationClimate Zone Urban8
Wind Speed (m/s) Precipitation Freq (Days) 2.7 37

1.3 User Entered Comments & Non-Default Data1.0 Project CharacteristicsUtility Company Southern California Edison Operational Year 2024
CO2 Intensity (lb/MWhr)
702.44 0.029 CH4 Intensity
(lb/MWhr)
N2O Intensity 0.006(lb/MWhr)
Carpinteria Rincon Trail
Santa Barbara-South of Santa Ynez Range County, Winter
CalEEMod Version: CalEEMod.2016.3.2 Page 1 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter Project Characteristics -
Land Use - Construction Phase - Based on project description.Off-road Equipment - CalEEmod defaults.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Off-road Equipment - Based on modeling from the Supplemental MND.Trips and VMT - CalEEMod defaults. Odd trips were rounded up to account for whole round trips.On-road Fugitive Dust - CalEEMod defaults.Grading - Based on City provided data.Architectural Coating - CalEEMod defaults.

Vehicle Trips - For maintenance, assumption of one trip per week.Energy Use - No energy use.Water And Wastewater - CalEEMod defaults.Solid Waste - CalEEMod defaults.Land Use Change - Sequestration - Construction Off-road Equipment Mitigation - In accordance with SBCAPCD Rule 345.Operational Off-Road Equipment - NA Table Name Column Name Default Value New Value
tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstructionPhase NumDays 2.00 32.00tblConstructionPhase NumDays 4.00 224.00tblConstructionPhase NumDays 200.00 96.00 CalEEMod Version: CalEEMod.2016.3.2 Page 2 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter tblConstructionPhase NumDays 200.00 10.00
tblConstructionPhase NumDays 10.00 32.00tblConstructionPhase NumDays 10.00 20.00 tblEnergyUse LightingElect 0.35 0.00
tblGrading MaterialExported 0.00 94,100.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 0.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 0.00 1.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 0.00 1.00tblOffRoadEquipment OffRoadEquipmentUnitAmount 0.00 1.00tblOffRoadEquipment PhaseName Grading tblOffRoadEquipment PhaseName Trail ConstructiontblOffRoadEquipment PhaseName PavingtblOffRoadEquipment UsageHours 6.00 8.00 tblTripsAndVMT HaulingTripNumber 11,763.00 11,764.00tblTripsAndVMT VendorTripNumber 11.00 12.00tblTripsAndVMT VendorTripNumber 11.00 12.00tblTripsAndVMT WorkerTripNumber 5.00 6.00 CalEEMod Version: CalEEMod.2016.3.2 Page 3 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

2.0 Emissions Summary
tblVehicleTrips ST_TR 22.75 1.43tblVehicleTrips SU_TR 16.74 0.00tblVehicleTrips WD_TR 1.89 0.00 CalEEMod Version: CalEEMod.2016.3.2 Page 4 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

2.1 Overall Construction (Maximum Daily Emission)
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2022 1.3366 23.9918 9.8705 0.0540 5.8501 0.6228 6.4729 2.9671 0.5730 3.5401 0.0000 5,831.371 5 5,831.371
5 0.9046 0.0000 5,853.986
3 2023 1.3377 19.3520 9.4630 0.0527 5.3957 0.3842 5.7744 1.2267 0.3667 1.5761 0.0000 5,714.503 8 5,714.503
8 0.9038 0.0000 5,737.099
6 Maximum 1.3377 23.9918 9.8705 0.0540 5.8501 0.6228 6.4729 2.9671 0.5730 3.5401 0.0000 5,831.371 5 5,831.371
5 0.9046 0.0000 5,853.986
3 Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2022 1.3366 23.9918 9.8705 0.0540 2.6603 0.6228 3.2832 1.3426 0.5730 1.9156 0.0000 5,831.371 5 5,831.371
5 0.9046 0.0000 5,853.986
3 2023 1.3377 19.3520 9.4630 0.0527 4.8877 0.3842 5.2664 1.1704 0.3667 1.5198 0.0000 5,714.503 8 5,714.503
8 0.9038 0.0000 5,737.099
6 Maximum 1.3377 23.9918 9.8705 0.0540 4.8877 0.6228 5.2664 1.3426 0.5730 1.9156 0.0000 5,831.371 5 5,831.371
5 0.9046 0.0000 5,853.986
3 Mitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction

0.00 0.00 0.00 0.00 32.88 0.00 30.19 40.08 0.00 32.85 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2016.3.2 Page 5 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 6.5600e003 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003 Energy 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Mobile 2.7000e003 9.2800e- 003 0.0263 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 6.9924 6.9924 3.5000e- 004 7.0013 Total 9.2600e003 9.2900e- 003 0.0270 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 6.9941 6.9941 3.5000e- 004 0.0000 7.0030 Unmitigated Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 6.5600e003 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003 Energy 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Mobile 2.7000e003 9.2800e- 003 0.0263 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 6.9924 6.9924 3.5000e- 004 7.0013 Total 9.2600e003 9.2900e- 003 0.0270 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 6.9941 6.9941 3.5000e- 004 0.0000 7.0030 Mitigated Operational
CalEEMod Version: CalEEMod.2016.3.2 Page 6 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Residential Indoor: 0; Residential Outdoor: 0; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area: 369 (Architectural Coating – sqft)Acres of Grading (Site Preparation Phase): 16 Acres of Grading (Grading Phase): 182Acres of Paving: 0.14 CalEEMod Version: CalEEMod.2016.3.2 Page 7 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor Site Preparation Graders 1 8.00 187 0.41Site Preparation Rubber Tired Dozers 1 7.00 247 0.40Site Preparation Tractors/Loaders/Backhoes 1 8.00 97 0.37Grading Crawler Tractors 1 7.00 212 0.43Grading Graders 1 6.00 187 0.41Grading Rubber Tired Dozers 0 6.00 247 0.40Grading Tractors/Loaders/Backhoes 1 7.00 97 0.37Trail Construction Cranes 0 6.00 231 0.29Trail Construction Crawler Tractors 1 7.00 212 0.43Trail Construction Forklifts 0 6.00 89 0.20Trail Construction Generator Sets 0 8.00 84 0.74Trail Construction Tractors/Loaders/Backhoes 1 6.00 97 0.37Trail Construction Welders 0 8.00 46 0.45Bridge Construction Cranes 1 8.00 231 0.29Bridge Construction Forklifts 0 6.00 89 0.20Bridge Construction Generator Sets 0 8.00 84 0.74Bridge Construction Tractors/Loaders/Backhoes 1 6.00 97 0.37Bridge Construction Welders 3 8.00 46 0.45Paving Cement and Mortar Mixers 0 6.00 9 0.56Paving Crawler Tractors 1 8.00 212 0.43Paving Pavers 0 6.00 130 0.42Paving Paving Equipment 1 8.00 132 0.36Paving Rollers 0 7.00 80 0.38Paving Tractors/Loaders/Backhoes 0 8.00 97 0.37Architectural Coating Air Compressors 1 6.00 78 0.48 Trips and VMT
CalEEMod Version: CalEEMod.2016.3.2 Page 8 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 5.7996 0.0000 5.7996 2.9537 0.0000 2.9537 0.0000 0.0000 Off-Road 1.3122 14.6277 7.0939 0.0172 0.6225 0.6225 0.5727 0.5727 1,666.173 8 1,666.173
8 0.5389 1,679.645
7 Total 1.3122 14.6277 7.0939 0.0172 5.7996 0.6225 6.4221 2.9537 0.5727 3.5264 1,666.173 8 1,666.173
8 0.5389 1,679.645
7 Unmitigated Construction On-Site3.1 Mitigation Measures ConstructionWater Exposed AreaReduce Vehicle Speed on Unpaved Roads Phase Name Offroad Equipment
Count
Worker Trip
Number
Vendor Trip
Number
Hauling Trip
Number
Worker Trip
Length
Vendor Trip
Length
Hauling Trip
Length
Worker Vehicle
Class
Vendor
Vehicle Class
Hauling
Vehicle Class
Site Preparation 3 8.00 0.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTGrading 3 8.00 0.00 11,764.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTTrail Construction 2 28.00 12.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTBridge Construction 5 28.00 12.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDTPaving 2 6.00 0.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 6.00 0.00 0.00 8.30 6.40 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2016.3.2 Page 9 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0244 0.0177 0.1600 4.2000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 41.3836 41.3836 1.2000e- 003 41.4136 Total 0.0244 0.0177 0.1600 4.2000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 41.3836 41.3836 1.2000e- 003 41.4136 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 2.6098 0.0000 2.6098 1.3292 0.0000 1.3292 0.0000 0.0000 Off-Road 1.3122 14.6277 7.0939 0.0172 0.6225 0.6225 0.5727 0.5727 0.0000 1,666.173 8 1,666.173
8 0.5389 1,679.645
7 Total 1.3122 14.6277 7.0939 0.0172 2.6098 0.6225 3.2323 1.3292 0.5727 1.9019 0.0000 1,666.173 8 1,666.173
8 0.5389 1,679.645
7 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 10 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0244 0.0177 0.1600 4.2000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 41.3836 41.3836 1.2000e- 003 41.4136 Total 0.0244 0.0177 0.1600 4.2000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 41.3836 41.3836 1.2000e- 003 41.4136 Mitigated Construction Off-Site3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.9237 0.0000 0.9237 0.1024 0.0000 0.1024 0.0000 0.0000 Off-Road 0.8858 10.6663 5.2750 0.0146 0.4026 0.4026 0.3704 0.3704 1,408.696 6 1,408.696
6 0.4556 1,420.086
6 Total 0.8858 10.6663 5.2750 0.0146 0.9237 0.4026 1.3263 0.1024 0.3704 0.4729 1,408.696 6 1,408.696
6 0.4556 1,420.086
6 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 11 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.3823 13.3079 4.4355 0.0390 1.0497 0.0501 1.0998 0.2833 0.0479 0.3312 4,381.291 3 4,381.291
3 0.4478 4,392.486
0 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0244 0.0177 0.1600 4.2000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 41.3836 41.3836 1.2000e- 003 41.4136 Total 0.4067 13.3255 4.5955 0.0394 1.1002 0.0504 1.1506 0.2967 0.0482 0.3449 4,422.674 9 4,422.674
9 0.4490 4,433.899
6 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.4157 0.0000 0.4157 0.0461 0.0000 0.0461 0.0000 0.0000 Off-Road 0.8858 10.6663 5.2750 0.0146 0.4026 0.4026 0.3704 0.3704 0.0000 1,408.696 6 1,408.696
6 0.4556 1,420.086
6 Total 0.8858 10.6663 5.2750 0.0146 0.4157 0.4026 0.8183 0.0461 0.3704 0.4165 0.0000 1,408.696 6 1,408.696
6 0.4556 1,420.086
6 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 12 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.3823 13.3079 4.4355 0.0390 1.0497 0.0501 1.0998 0.2833 0.0479 0.3312 4,381.291 3 4,381.291
3 0.4478 4,392.486
0 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0244 0.0177 0.1600 4.2000e004 0.0505 3.0000e- 004 0.0508 0.0134 2.8000e- 004 0.0137 41.3836 41.3836 1.2000e- 003 41.4136 Total 0.4067 13.3255 4.5955 0.0394 1.1002 0.0504 1.1506 0.2967 0.0482 0.3449 4,422.674 9 4,422.674
9 0.4490 4,433.899
6 Mitigated Construction Off-Site3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.9237 0.0000 0.9237 0.1024 0.0000 0.1024 0.0000 0.0000 Off-Road 0.8087 9.3175 5.1851 0.0145 0.3533 0.3533 0.3250 0.3250 1,408.008 6 1,408.008
6 0.4554 1,419.393
0 Total 0.8087 9.3175 5.1851 0.0145 0.9237 0.3533 1.2770 0.1024 0.3250 0.4275 1,408.008 6 1,408.008
6 0.4554 1,419.393
0 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 13 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.2812 10.0187 4.1321 0.0378 4.4215 0.0252 4.4467 1.1109 0.0241 1.1350 4,266.658 1 4,266.658
1 0.4474 4,277.842
7 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0228 0.0158 0.1458 4.0000e004 0.0505 2.9000e- 004 0.0508 0.0134 2.7000e- 004 0.0137 39.8372 39.8372 1.0700e- 003 39.8639 Total 0.3041 10.0345 4.2779 0.0382 4.4720 0.0255 4.4975 1.1243 0.0244 1.1487 4,306.495 2 4,306.495
2 0.4485 4,317.706
6 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 0.4157 0.0000 0.4157 0.0461 0.0000 0.0461 0.0000 0.0000 Off-Road 0.8087 9.3175 5.1851 0.0145 0.3533 0.3533 0.3250 0.3250 0.0000 1,408.008 6 1,408.008
6 0.4554 1,419.393
0 Total 0.8087 9.3175 5.1851 0.0145 0.4157 0.3533 0.7690 0.0461 0.3250 0.3711 0.0000 1,408.008 6 1,408.008
6 0.4554 1,419.393
0 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 14 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.2812 10.0187 4.1321 0.0378 4.4215 0.0252 4.4467 1.1109 0.0241 1.1350 4,266.658 1 4,266.658
1 0.4474 4,277.842
7 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0228 0.0158 0.1458 4.0000e004 0.0505 2.9000e- 004 0.0508 0.0134 2.7000e- 004 0.0137 39.8372 39.8372 1.0700e- 003 39.8639 Total 0.3041 10.0345 4.2779 0.0382 4.4720 0.0255 4.4975 1.1243 0.0244 1.1487 4,306.495 2 4,306.495
2 0.4485 4,317.706
6 Mitigated Construction Off-Site3.4 Trail Construction - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.5022 5.6358 3.6367 9.1900e003 0.2308 0.2308 0.2123 0.2123 889.6701 889.6701 0.2877 896.8636 Total 0.5022 5.6358 3.6367 9.1900e003 0.2308 0.2308 0.2123 0.2123 889.6701 889.6701 0.2877 896.8636 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 15 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.4 Trail Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0295 0.9485 0.3583 2.6800e003 0.0711 1.5700e- 003 0.0726 0.0204 1.5000e- 003 0.0219 293.7724 293.7724 0.0232 294.3511 Worker 0.0799 0.0553 0.5104 1.4000e003 0.1768 1.0300e- 003 0.1779 0.0469 9.5000e- 004 0.0479 139.4301 139.4301 3.7400e- 003 139.5237 Total 0.1094 1.0038 0.8687 4.0800e003 0.2479 2.6000e- 003 0.2505 0.0674 2.4500e- 003 0.0698 433.2025 433.2025 0.0269 433.8748 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.5022 5.6358 3.6367 9.1900e003 0.2308 0.2308 0.2123 0.2123 0.0000 889.6701 889.6701 0.2877 896.8636 Total 0.5022 5.6358 3.6367 9.1900e003 0.2308 0.2308 0.2123 0.2123 0.0000 889.6701 889.6701 0.2877 896.8636 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 16 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.4 Trail Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0295 0.9485 0.3583 2.6800e003 0.0711 1.5700e- 003 0.0726 0.0204 1.5000e- 003 0.0219 293.7724 293.7724 0.0232 294.3511 Worker 0.0799 0.0553 0.5104 1.4000e003 0.1768 1.0300e- 003 0.1779 0.0469 9.5000e- 004 0.0479 139.4301 139.4301 3.7400e- 003 139.5237 Total 0.1094 1.0038 0.8687 4.0800e003 0.2479 2.6000e- 003 0.2505 0.0674 2.4500e- 003 0.0698 433.2025 433.2025 0.0269 433.8748 Mitigated Construction Off-Site3.5 Bridge Construction - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.2283 9.2289 8.5417 0.0158 0.3816 0.3816 0.3643 0.3643 1,407.434 8 1,407.434
8 0.3218 1,415.479
6 Total 1.2283 9.2289 8.5417 0.0158 0.3816 0.3816 0.3643 0.3643 1,407.434 8 1,407.434
8 0.3218 1,415.479
6 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 17 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.5 Bridge Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0295 0.9485 0.3583 2.6800e003 0.0711 1.5700e- 003 0.0726 0.0204 1.5000e- 003 0.0219 293.7724 293.7724 0.0232 294.3511 Worker 0.0799 0.0553 0.5104 1.4000e003 0.1768 1.0300e- 003 0.1779 0.0469 9.5000e- 004 0.0479 139.4301 139.4301 3.7400e- 003 139.5237 Total 0.1094 1.0038 0.8687 4.0800e003 0.2479 2.6000e- 003 0.2505 0.0674 2.4500e- 003 0.0698 433.2025 433.2025 0.0269 433.8748 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.2283 9.2289 8.5417 0.0158 0.3816 0.3816 0.3643 0.3643 0.0000 1,407.434 8 1,407.434
8 0.3218 1,415.479
6 Total 1.2283 9.2289 8.5417 0.0158 0.3816 0.3816 0.3643 0.3643 0.0000 1,407.434 8 1,407.434
8 0.3218 1,415.479
6 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 18 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.5 Bridge Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0295 0.9485 0.3583 2.6800e003 0.0711 1.5700e- 003 0.0726 0.0204 1.5000e- 003 0.0219 293.7724 293.7724 0.0232 294.3511 Worker 0.0799 0.0553 0.5104 1.4000e003 0.1768 1.0300e- 003 0.1779 0.0469 9.5000e- 004 0.0479 139.4301 139.4301 3.7400e- 003 139.5237 Total 0.1094 1.0038 0.8687 4.0800e003 0.2479 2.6000e- 003 0.2505 0.0674 2.4500e- 003 0.0698 433.2025 433.2025 0.0269 433.8748 Mitigated Construction Off-Site3.6 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.6149 6.7275 4.8004 0.0119 0.2767 0.2767 0.2546 0.2546 1,152.738 8 1,152.738
8 0.3728 1,162.059
3 Paving 0.0115 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.6263 6.7275 4.8004 0.0119 0.2767 0.2767 0.2546 0.2546 1,152.738 8 1,152.738
8 0.3728 1,162.059
3 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 19 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.6 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0171 0.0119 0.1094 3.0000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 29.8779 29.8779 8.0000e- 004 29.8979 Total 0.0171 0.0119 0.1094 3.0000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 29.8779 29.8779 8.0000e- 004 29.8979 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.6149 6.7275 4.8004 0.0119 0.2767 0.2767 0.2546 0.2546 0.0000 1,152.738 8 1,152.738
8 0.3728 1,162.059
3 Paving 0.0115 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.6263 6.7275 4.8004 0.0119 0.2767 0.2767 0.2546 0.2546 0.0000 1,152.738 8 1,152.738
8 0.3728 1,162.059
3 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 20 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.6 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0171 0.0119 0.1094 3.0000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 29.8779 29.8779 8.0000e- 004 29.8979 Total 0.0171 0.0119 0.1094 3.0000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 29.8779 29.8779 8.0000e- 004 29.8979 Mitigated Construction Off-Site3.7 Architectural Coating - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 0.2138 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.1917 1.3030 1.8111 2.9700e003 0.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690 Total 0.4055 1.3030 1.8111 2.9700e003 0.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 21 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

3.7 Architectural Coating - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0171 0.0119 0.1094 3.0000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 29.8779 29.8779 8.0000e- 004 29.8979 Total 0.0171 0.0119 0.1094 3.0000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 29.8779 29.8779 8.0000e- 004 29.8979 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 0.2138 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.1917 1.3030 1.8111 2.9700e003 0.0708 0.0708 0.0708 0.0708 0.0000 281.4481 281.4481 0.0168 281.8690 Total 0.4055 1.3030 1.8111 2.9700e003 0.0708 0.0708 0.0708 0.0708 0.0000 281.4481 281.4481 0.0168 281.8690 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 22 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

4.0 Operational Detail - Mobile

4.1 Mitigation Measures Mobile3.7 Architectural Coating - 2023 ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0171 0.0119 0.1094 3.0000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 29.8779 29.8779 8.0000e- 004 29.8979 Total 0.0171 0.0119 0.1094 3.0000e004 0.0379 2.2000e- 004 0.0381 0.0101 2.0000e- 004 0.0103 29.8779 29.8779 8.0000e- 004 29.8979 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2016.3.2 Page 23 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 2.7000e003 9.2800e- 003 0.0263 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 6.9924 6.9924 3.5000e- 004 7.0013 Unmitigated 2.7000e003 9.2800e- 003 0.0263 7.0000e- 005 6.8400e- 003 6.0000e- 005 6.9000e- 003 1.8300e- 003 6.0000e- 005 1.8900e- 003 6.9924 6.9924 3.5000e- 004 7.0013

4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH City Park 0.572071 0.027190 0.206810 0.117824 0.018361 0.005136 0.017629 0.020081 0.002790 0.002084 0.006580 0.002569 0.000873 Parking Lot 0.572071 0.027190 0.206810 0.117824 0.018361 0.005136 0.017629 0.020081 0.002790 0.002084 0.006580 0.002569 0.000873 CalEEMod Version: CalEEMod.2016.3.2 Page 24 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

5.0 Energy Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
NaturalGas
Mitigated

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 NaturalGasUnmitigated

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000

5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2016.3.2 Page 25 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

6.1 Mitigation Measures Area

6.0 Area Detail5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Parking Lot 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Unmitigated
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Parking Lot 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Mitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 26 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 6.5600e003 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003 Unmitigated 6.5600e003 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003

1.1700e003 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products

5.3200e003 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Landscaping 7.0000e005 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003 Total 6.5600e003 1.0000e- 005 7.7000e- 004 0.0000 0.0000 0.0000 0.0000 0.0000 1.6500e- 003 1.6500e- 003 0.0000 1.7600e- 003 Unmitigated
CalEEMod Version: CalEEMod.2016.3.2 Page 27 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

8.1 Mitigation Measures Waste

7.1 Mitigation Measures Water7.0 Water Detail8.0 Waste Detail

1.1700e003 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products

9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type

10.0 Stationary Equipment
Fire Pumps and Emergency Generators
CalEEMod Version: CalEEMod.2016.3.2 Page 28 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter

11.0 Vegetation
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2016.3.2 Page 29 of 29 Date: 12/15/2020 2:29 PM Carpinteria Rincon Trail - Santa Barbara-South of Santa Ynez Range County, Winter Summary:

Carbon Loss
Project Vegetation Land Use
Vegetation Land
Use Category
Subtype Net Loss
Loss of
Sequestered CO2
(acres) (MT CO2)
Forest Land Scrub 10.70 153.01
Total 153.01
Carbon Gain
Project Vegetation Land Use
Vegetation Land
Use Category
Subtype Net Loss
Loss of
Sequestered CO2
(acres) (MT CO2)
Forest Land Scrub 11.45 163.74
Total 163.74
Total CO2E emissions released (loss) (MT) 153.01
CO2E sequestered from Net New Vegetation (gain) (MT) 163.74 Total CO2E Released (loss - gain) (MT) -10.73
Amortized Net Change of CO2E over 30 years (MT/year) -0.36 Future planting of trees within the project site will sequester CO2 and is considered to result in a onetime carbon-stock change. Trees sequester CO2 while they are actively growing.

Vegetation
Land Use Change - Net Sequestered Carbon
The project's changes in land use results in changes in CO2 sequestration from the atmosphere which would not have been captured had there been no land-type change.

Project Name
Equation:

Where:

Vegetation Land Use Type
Vegetation Land Use
Subtype
Biogenic CO2
Emissions
(MT CO2/Acre)
Cropland Cropland 6.2
Forest Land Scrub 14.3
Forest Land Trees 111
Grassland Grassland 4.31
Wetlands Wetlands 0
Others Others 0
Notes:

Reference:

CalEEMod Users Guide, Appendix A Calculation Details (Section 11 Vegetation, pages 50-52) Vegetation
Sequestered CO2 (MT CO2) = Σf (SeqCO2 )f x (area)f - Σi (SeqCO2 )i x (area)i I = index for initial land use type
Based on values indicated in IPCC Guidelines for National Greenhouse Gas Inventories (IPCC Guidelines). Available online at http://www.ipccnggip.iges.or.jp/public/2006gl/ Project Name
The mass of sequestered CO2 per unit area (MT CO2/acre) is dependent on the specific land use type. The program uses default CO2 sequestration values from the California Climate Action Registry for each land use that will be preserved or created:

A development which changes land use type results in changes in CO2 sequestration from the atmosphere which would not have been captured had there been no land-type change.

Land Use Change - Loss of Sequestered Carbon
SeqCO2 = mass of sequestered CO2 per unit area (MT CO2/acre) area = area of land for specific land use type (acre)
Default CalEEMod Factors
f = index for final land use type
Project Name
Calculations:

Project Vegetation Land Use
Vegetation Land
Use Category
Vegetation
Land Use
Category
Subtype Initial Acres Final Acres Net Loss
Biogenic CO2
Emissions
Sequestered
CO2
(acres) (acres) (acres) (MT CO2/Acre) (MT CO2)
Non-Native Woodland Forest Land Scrub 10.70 0.00 10.70 14.3 153.01 Total 10.70 0.00 10.70 153.01
Notes:

Wetlands
This category includes areas of peat extraction and land that is covered or saturated by water for all or part of the year (e.g., peatlands) and that does not fall into the Forest Land, Cropland, Grassland or Settlements categories. It includes reservoirs as a managed sub-division and natural rivers and lakes as unmanaged sub-divisions.

Vegetation Type
The user must specify area of land in acres for specific final and initial land use types. These area changes include not only the area of land that will be converted to buildings, but also areas disrupted by the construction of utility corridors, water tank sites, and associated borrow and grading areas. Areas temporarily disturbed that will eventually recover to become vegetated will not be counted as vegetation removed as there is no net change in vegetation or land use.

This assumption facilitates the calculation as a yearly growth rate and CO2 removal rate does not have to be calculated. As long as the disturbed land will indeed return to its original state, this assumption is valid for time periods over 20 years.

The default annual CO2 is calculated by multiplying total biomass (MT dry matter/acre) from IPCC data by the carbon fraction in plant material (0.47), then using the ratio of molecular weights (44/12) to convert from MT of carbon (C) to MT of carbon dioxide (CO2).

Forest Land
This category includes all land with woody vegetation consistent with thresholds used to define Forest Land in the national greenhouse gas inventory. It also includes systems with a vegetation structure that currently fall below, but in situ could potentially reach the threshold values used by a country to define the Forest Land category.

Area
Cropland
This category includes cropped land, including rice fields, and agro-forestry systems where the vegetation structure falls below the thresholds used for the Forest Land category.

Vegetation types are defined by IPCC as follows:

Grassland
This category includes rangelands and pasture land that are not considered Cropland. It also includes systems with woody vegetation and other non-grass vegetation such as herbs and brushes that fall below the threshold values used in the Forest Land category. The category also includes all grassland from wild lands to recreational areas as well as agricultural and silvi-pastural systems, consistent with national definitions.

Equation:

Where:

Reference:

CalEEMod Users Guide, Appendix A Calculation Details (Section 11 Vegetation, pages 50-52) Project Name
Vegetation
Land Use Change - Sequestered Carbon
A development which changes land use type results in changes in CO2 sequestration from the atmosphere which would not have been captured had there been no land-type change.

Sequestered CO2 (MT CO2) = Σf (SeqCO2 )f x (area)f - Σi (SeqCO2 )i x (area)i SeqCO2 = mass of sequestered CO2 per unit area (MT CO2/acre) area = area of land for specific land use type (acre)
f = index for final land use type
I = index for initial land use type
Default CalEEMod Factors
The mass of sequestered CO2 per unit area (MT CO2/acre) is dependent on the specific land use type. The program uses default CO2 sequestration values from the California Climate Action Registry for each land use that will be preserved or created:

Based on values indicated in IPCC Guidelines for National Greenhouse Gas Inventories (IPCC Guidelines). Available online at http://www.ipccnggip.iges.or.jp/public/2006gl/ Project Name
Calculations:

Project Vegetation Land Use
Vegetation Land
Use Category
Vegetation
Land Use
Category
Subtype Initial Acres Final Acres Net Loss
Biogenic CO2
Emissions
Sequestered
CO2
(acres) (acres) (acres) (MT CO2/Acre) (MT CO2)
Non-Native Woodland Forest Land Scrub 11.45 0.00 11.45 14.3 163.74 Total 11.45 0.00 11.45 163.74
Notes:

The user must specify area of land in acres for specific final and initial land use types. These area changes include not only the area of land that will be converted to buildings, but also areas disrupted by the construction of utility corridors, water tank sites, and associated borrow and grading areas. Areas temporarily disturbed that will eventually recover to become vegetated will not be counted as vegetation removed as there is no net change in vegetation or land use.

Vegetation Type
Vegetation types are defined by IPCC as follows:

Cropland
This category includes cropped land, including rice fields, and agro-forestry systems where the vegetation structure falls below the thresholds used for the Forest Land category.

Area
Appendix C1
Plant and Wildlife Compendium

APPENDIX C1

PLANT AND WILDLIFE SPECIES COMPENDIUM
11032
C1-1 March 2021
Plant Species
Eudicots – Vascular Species
ADOXACEAE—MUSKROOT FAMILY
Sambucus nigra ssp. caerulea—blue elderberry
AIZOACEAE—FIG-MARIGOLD FAMILY
* Carpobrotus chilensis—sea fig
* Carpobrotus edulis—hottentot fig
* Mesembryanthemum crystallinum—common iceplant
* Tetragonia tetragonoides—New Zealand spinach
AMARANTHACEAE—AMARANTH FAMILY
* Amaranthus albus—prostrate pigweed
Amaranthus blitoides—mat amaranth
ANACARDIACEAE—SUMAC OR CASHEW FAMILY
Rhus integrifolia—lemonade berry
* Schinus terebinthifolius—Brazilian peppertree
APIACEAE—CARROT FAMILY
Apiastrum angustifolium—mock parsley
* Conium maculatum—poison hemlock
* Foeniculum vulgare—fennel
ASTERACEAE—SUNFLOWER FAMILY
Ambrosia psilostachya—western ragweed
Artemisia californica—California sagebrush
Baccharis pilularis—coyote brush
Baccharis salicifolia—mulefat
Brickellia californica—California brickellbush
* Carduus pycnocephalus—Italian plumeless thistle
* Centaurea melitensis—Maltese star-thistle
Corethrogyne filaginifolia—sand-aster
* Delairea odorata—Cape-ivy
Encelia californica—California brittle bush
* Erigeron bonariensis—asthmaweed
Erigeron canadensis—Canadian horseweed
* Erigeron sumatrensis—asthmaweed
Eriophyllum confertiflorum—golden-yarrow
Hazardia squarrosa—sawtooth golden bush
APPENDIX C1

PLANT AND WILDLIFE SPECIES COMPENDIUM
11032
C1-2 March 2021
* Helminthotheca echioides—bristly oxtongue
Heterotheca grandiflora—telegraphweed
Heterotheca sessiliflora—sessileflower false goldenaster Isocoma menziesii—Menzies’s golden bush
* Lactuca serriola—prickly lettuce
Malacothrix saxatilis var. saxatilis—cliff malacothrix
Pseudognaphalium beneolens—Wright's cudweed
Pseudognaphalium biolettii—two-color rabbit-tobacco
Pseudognaphalium californicum—ladies' tobacco
* Pseudognaphalium luteoalbum—Jersey cudweed
Pseudognaphalium ramosissimum—pink cudweed
* Silybum marianum—blessed milkthistle
* Sonchus asper—spiny sowthistle
* Sonchus oleraceus—common sowthistle
Venegasia carpesioides—canyon sunflower
BORAGINACEAE—BORAGE FAMILY
Amsinckia menziesii—Menzies' fiddleneck
Eriodictyon crassifolium—thick leaf yerba santa
Eucrypta chrysanthemifolia—spotted hideseed
Phacelia ramosissima var. austrolitoralis—south coast branching phacelia BRASSICACEAE—MUSTARD FAMILY
* Brassica nigra—black mustard
* Brassica rapa—field mustard
* Brassica tournefortii—Tournefort's mustard
* Cakile maritima—European searocket
* Capsella bursa-pastoris—shepherd's purse
Descurainia pinnata—western tansymustard
* Hirschfeldia incana—shortpod mustard
Lepidium nitidum—shining pepperweed
* Lobularia maritima—sweet alyssum
* Raphanus sativus—cultivated radish
* Sisymbrium irio—London rocket
* Sisymbrium orientale—Indian hedgemustard
CACTACEAE—CACTUS FAMILY
Opuntia littoralis—coast prickly pear
CARYOPHYLLACEAE—PINK FAMILY
* Spergularia bocconi—Boccone's sandspurry
APPENDIX C1

PLANT AND WILDLIFE SPECIES COMPENDIUM
11032
C1-3 March 2021
CHENOPODIACEAE—GOOSEFOOT FAMILY
Atriplex lentiformis—quailbush
* Atriplex semibaccata—Australian saltbush
* Bassia hyssopifolia—fivehorn smotherweed
* Chenopodium album—lambsquarters
* Chenopodium murale—nettleleaf goosefoot
* Salsola tragus—prickly Russian thistle
Suaeda taxifolia—woolly seablite
CONVOLVULACEAE—MORNING-GLORY FAMILY
Calystegia macrostegia ssp. cyclostegia—island false bindweed * Convolvulus arvensis—field bindweed
EUPHORBIACEAE—SPURGE FAMILY
Croton californicus—California croton
Croton setiger—dove weed
* Euphorbia peplus—petty spurge
* Ricinus communis—castorbean
FABACEAE—LEGUME FAMILY
Acmispon americanus—Spanish clover
Acmispon glaber—deer weed
* Medicago polymorpha—burclover
* Melilotus indicus—annual yellow sweetclover
* Melilotus officinalis—sweetclover
FAGACEAE—OAK FAMILY
Quercus agrifolia—coast live oak
GERANIACEAE—GERANIUM FAMILY
* Erodium botrys—longbeak stork's bill
* Erodium cicutarium—redstem stork's bill
* Erodium moschatum—musky stork's bill
LAMIACEAE—MINT FAMILY
* Marrubium vulgare—horehound
Stachys bullata—California hedgenettle
MALVACEAE—MALLOW FAMILY
* Malva nicaeensis—bull mallow
* Malva parviflora—cheeseweed mallow
APPENDIX C1

PLANT AND WILDLIFE SPECIES COMPENDIUM
11032
C1-4 March 2021
MYRSINACEAE—MYRSINE FAMILY
* Lysimachia arvensis—scarlet pimpernel
MYRTACEAE—MYRTLE FAMILY
* Eucalyptus camaldulensis—river redgum
NYCTAGINACEAE—FOUR O'CLOCK FAMILY
Mirabilis laevis var. crassifolia—California four o'clock ONAGRACEAE—EVENING PRIMROSE FAMILY
Camissoniopsis bistorta—southern suncup
OXALIDACEAE—OXALIS FAMILY
* Oxalis pes-caprae—Bermuda buttercup
PHRYMACEAE—LOPSEED FAMILY
Diplacus aurantiacus—bush monkeyflower
PLANTAGINACEAE—PLANTAIN FAMILY
Plantago erecta—dwarf plantain
* Plantago lanceolata—narrowleaf plantain
PLATANACEAE—PLANE TREE, SYCAMORE FAMILY
Platanus racemosa—California sycamore
PLUMBAGINACEAE—LEADWORT FAMILY
* Limonium perezii—Perez's sea lavender
POLYGONACEAE—BUCKWHEAT FAMILY
Eriogonum parvifolium—seacliff buckwheat
* Polygonum aviculare—prostrate knotweed
RHAMNACEAE—BUCKTHORN FAMILY
Rhamnus crocea—redberry buckthorn
SALICACEAE—WILLOW FAMILY
Salix laevigata—red willow
Salix lasiolepis—arroyo willow
SCROPHULARIACEAE—FIGWORT FAMILY
* Myoporum laetum—myoporum
Scrophularia californica—California figwort
APPENDIX C1

PLANT AND WILDLIFE SPECIES COMPENDIUM
11032
C1-5 March 2021
SOLANACEAE—NIGHTSHADE FAMILY
Datura wrightii—sacred thorn-apple
* Nicotiana glauca—tree tobacco
Solanum americanum—American black nightshade
Solanum douglasii—greenspot nightshade
Solanum xanti—chaparral nightshade
TROPAEOLACEAE—NASTURTIUM FAMILY
* Tropaeolum majus—nasturtium
URTICACEAE—NETTLE FAMILY
* Urtica urens—dwarf nettle
VERBENACEAE—VERVAIN FAMILY
Verbena lasiostachys—western vervain
Gymnosperms and Gnetophytes – Vascular Species
ARAUCARIACEAE— ARAUCARIANS FAMILY
Araucaria heterophylla—Norfolk Island pine
CUPRESSACEAE—CYPRESS FAMILY
Hesperocyparis macrocarpa—Monterey cypress
PINACEAE—PINE FAMILY
Pinus sp.—Pine tree
Monocots – Vascular Species
ASPHODELACEAE—ASPHODEL FAMILY
* Asphodelus fistulosus—onionweed
POACEAE—GRASS FAMILY
* Avena barbata—slender oat
* Brachypodium distachyon—purple false brome
* Bromus diandrus—ripgut brome
* Bromus hordeaceus—soft brome
* Bromus madritensis—compact brome
* Cortaderia jubata—purple pampas grass
* Cynodon dactylon—Bermudagrass
* Ehrharta calycina—perennial veldtgrass
Elymus condensatus—giant wild rye
APPENDIX C1

PLANT AND WILDLIFE SPECIES COMPENDIUM
11032
C1-6 March 2021
* Festuca myuros—rat-tail fescue
* Festuca perennis—perennial rye grass
* Hordeum murinum—mouse barley
* Lamarckia aurea—goldentop grass
Melica imperfecta—smallflower melicgrass
* Pennisetum setaceum—fountain grass
* Pennisetum villosum—feathertop
* Poa annua—annual bluegrass
* Polypogon monspeliensis—annual rabbitsfoot grass
* Schismus arabicus—Arabian schismus
* Stipa miliacea—no common name
* signifies introduced (non-native) species
APPENDIX C1

PLANT AND WILDLIFE SPECIES COMPENDIUM
11032
C1-7 March 2021
Wildlife Species
Birds
AEGITHALIDAE—LONG-TAILED TITS AND BUSHTITS
Psaltriparus minimus—bushtit
CARDINALIDAE—CARDINALS AND ALLIES
Pheucticus melanocephalus—black-headed grosbeak
FALCONIDAE—CARACARAS AND FALCONS
Falco peregrinus anatum—American peregrine falcon
Falco sparverius—American kestrel
FRINGILLIDAE—FRINGILLINE AND CARDUELINE FINCHES AND ALLIES Haemorhous mexicanus—house finch
Spinus psaltria—lesser goldfinch
TYRANNIDAE—TYRANT FLYCATCHERS
Sayornis nigricans—black phoebe
Sayornis saya—Say’s phoebe
ACCIPITRIDAE—HAWKS, KITES, EAGLES AND ALLIES
Buteo jamaicensis—red-tailed hawk
TROCHILIDAE—HUMMINGBIRDS
Calypte anna—Anna's hummingbird
CORVIDAE—CROWS AND JAYS
Corvus brachyrhynchos—American crow
CATHARTIDAE—NEW WORLD VULTURES
Cathartes aura—turkey vulture
SYLVIIDAE—SYLVIID WARBLERS
Polioptila caerulea—blue-gray gnatcatcher
COLUMBIDAE—PIGEONS AND DOVES
Zenaida macroura—mourning dove
* Streptopelia decaocto—Eurasian collared-dove
CUCULIDAE—CUCKOOS, ROADRUNNERS AND ANIS
Geococcyx californianus—greater roadrunner
APPENDIX C1

PLANT AND WILDLIFE SPECIES COMPENDIUM
11032
C1-8 March 2021
MIMIDAE—MOCKINGBIRDS AND THRASHERS
Toxostoma redivivum—California thrasher
PASSERIDAE—OLD WORLD SPARROWS
* Passer domesticus—house sparrow
POLIOPTILIDAE—GNATCATCHERS
Polioptila caerulea—blue-gray gnatcatcher
STURNIDAE—STARLINGS
* Sturnus vulgaris—European starling
HIRUNDINIDAE—SWALLOWS
Hirundo rustica—barn swallow
LARIDAE—GULLS, TERNS AND SKIMMERS
Larus occidentalis—western gull
TROGLODYTIDAE—WRENS
Thryomanes bewickii—Bewick's wren
TIMALIIDAE—BABBLERS
Chamaea fasciata—wrentit
PASSERELLIDAE—NEW WORLD SPARROWS
Melospiza melodia—song sparrow
Melozone crissalis—California towhee
Zonotrichia leucophrys—white-crowned sparrow
Invertebrates
LYCAENIDAE—BLUES, HAIRSTREAKS AND COPPERS
Brephidium exile—western pygmy-blue
PIERIDAE—WHITES AND SULFURS
Pieris rapae—cabbage white
Mammals
LEPORIDAE—HARES AND RABBITS
Sylvilagus bachmani—brush rabbit
APPENDIX C1

PLANT AND WILDLIFE SPECIES COMPENDIUM
11032
C1-9 March 2021
SCIURIDAE—SQUIRRELS
Spermophilus (Otospermophilus) beecheyi—California ground squirrel CRICETIDAE—RATS, MICE AND VOLES
Neotoma sp.—woodrat
Reptiles
PHRYNOSOMATIDAE—IGUANID LIZARDS
Sceloporus occidentalis—western fence lizard
Uta stansburiana—common side-blotched lizard
* signifies introduced (non-native) species
APPENDIX C1

PLANT AND WILDLIFE SPECIES COMPENDIUM
11032
C1-10 March 2021

INTENTIONALLY LEFT BLANK
Appendix C2
Plant and Wildlife Species Not Expected to
Occur within the Biological Study Area

APPENDIX C2

PLANT AND WILDLIFE SPECIES NOT EXPECTED TO OCCUR WITHIN THE BIOLOGICAL SURVEY AREA 11032
C2-1 March 2021
Special-Status Plant Species Not Expected to Occur within the Biological Survey Area Scientific Name
Common
Name
Regulatory
Status1 Habitat Requirements
Potential to Occur within
the BSA
Arenaria
paludicola
marsh
sandwort
FE/SE/1B.1 Marshes and swamps
(freshwater or
brackish); sandy,
openings/perennial
stoloniferous
herb/May–Aug/10–
560
Not expected to occur.

Suitable marsh or swamp
habitat is not present.

Astragalus
pycnostachyus
var.
lanosissimus
Ventura marsh
milk-vetch
FE/SE/1B.1 Coastal dunes, Coastal
scrub, Marshes and
swamps (edges, coastal
salt or
brackish)/perennial
herb/(June)Aug–
Oct/3–115
Not expected to occur.

While suitable coastal
scrub habitat is present,
this species rarely occurs
on sandy bluffs as
compared to within coastal
salt marsh margins or
coastal dunes (CDFW
2020). There is only one
occurrence in the region2
which is considered
possibly extirpated (CDFW
2020).

Calochortus
fimbriatus
late-flowered
mariposa lily
None/None/1B.3 Chaparral, Cismontane
woodland, Riparian
woodland; often
serpentinite/perennial
bulbiferous herb/June–
Aug/902–6,250
Not expected to occur. The
site is outside of the
species’ known elevation
range. Additionally, suitable
habitat is not present.

Calochortus
palmeri var.
palmeri
Palmer's
mariposa lily
None/None/1B.2 Chaparral, Lower
montane coniferous
forest, Meadows and
seeps; mesic/perennial
bulbiferous herb/Apr–
July/2,325–7,840
Not expected to occur. The
site is outside of the
species’ known elevation
range. Additionally, suitable
habitat is not present.

Chloropyron
maritimum ssp.
maritimum
salt marsh
bird's-beak
FE/SE/1B.2 Coastal dunes,
Marshes and swamps
(coastal salt)/annual
herb
(hemiparasitic)/May–
Oct(Nov)/0–100
Not expected to occur.

Suitable dune, marsh, or
swamp habitat is not
present.

Delphinium
umbraculorum
umbrella
larkspur
None/None/1B.3 Chaparral, Cismontane
woodland/perennial
herb/Apr–June/1,310–
5,245
Not expected to occur. The
site is outside of the
species’ known elevation
range. Additionally, suitable
habitat is not present.

APPENDIX C2

PLANT AND WILDLIFE SPECIES NOT EXPECTED TO OCCUR WITHIN THE BIOLOGICAL SURVEY AREA 11032
C2-2 March 2021
Special-Status Plant Species Not Expected to Occur within the Biological Survey Area Scientific Name
Common
Name
Regulatory
Status1 Habitat Requirements
Potential to Occur within
the BSA
Fritillaria
ojaiensis
Ojai fritillary None/None/1B.2 Broadleafed upland
forest (mesic),
Chaparral, Cismontane
woodland, Lower
montane coniferous
forest; rocky/perennial
bulbiferous herb/Feb–
May/738–3,270
Not expected to occur. The
site is outside of the
species’ known elevation
range. Additionally, suitable
habitat is not present.

Lasthenia
glabrata ssp.
coulteri
Coulter's
goldfields
None/None/1B.1 Marshes and swamps
(coastal salt), Playas,
Vernal pools/annual
herb/Feb–June/3–
4,000
Not expected to occur.

Suitable vernal pool, playa,
marsh, or swamp habitat is
not present.

Layia
heterotricha
pale-yellow
layia
None/None/1B.1 Cismontane woodland,
Coastal scrub, Pinyon
and juniper woodland,
Valley and foothill
grassland; alkaline or
clay/annual herb/Mar–
June/984–5,590
Not expected to occur. The
site is outside of the
species’ known elevation
range. Additionally, only
marginally suitable habitat
is present.

Monardella
hypoleuca ssp.
hypoleuca
white-veined
monardella
None/None/1B.3 Chaparral, Cismontane
woodland/perennial
herb/(Apr)May–
Aug(Sep–Dec)/164–
5,000
Not expected to occur. No
suitable chaparral or
woodland habitat present.

Although this species is
mapped along Rincon
Creek all the way to the
ocean just behind the
project site, it is associated
with the riparian habitat of
the creek which is not
present on site (CDFW
2020).

Nasturtium
gambelii
Gambel's
water cress
FE/ST/1B.1 Marshes and swamps
(freshwater or
brackish)/perennial
rhizomatous herb/Apr–
Oct/16–1,080
Not expected to occur.

Suitable marsh or swamp
habitat is not present.

Navarretia
fossalis
spreading
navarretia
FT/None/1B.1 Chenopod scrub,
Marshes and swamps
(assorted shallow
freshwater), Playas,
Vernal pools/annual
herb/Apr–June/98–
2,145
Not expected to occur.

Although chenopod scrub
habitat is present, vernal
pools are absent within the
project site. This species is
not known to occur within
the region2 (CDFW 2020).

APPENDIX C2

PLANT AND WILDLIFE SPECIES NOT EXPECTED TO OCCUR WITHIN THE BIOLOGICAL SURVEY AREA 11032
C2-3 March 2021
Special-Status Plant Species Not Expected to Occur within the Biological Survey Area Scientific Name
Common
Name
Regulatory
Status1 Habitat Requirements
Potential to Occur within
the BSA
Navarretia
ojaiensis
Ojai navarretia None/None/1B.1 Chaparral (openings),
Coastal scrub
(openings), Valley and
foothill
grassland/annual
herb/May–July/902–
2,030
Not expected to occur. The
site is outside of the
species’ known elevation
range.

Navarretia
peninsularis
Baja
navarretia
None/None/1B.2 Chaparral (openings),
Lower montane
coniferous forest,
Meadows and seeps,
Pinyon and juniper
woodland;
mesic/annual
herb/(May)June–
Aug/4,920–7,545
Not expected to occur. The
site is outside of the
species’ known elevation
range. Additionally, suitable
habitat is not present.

Nolina
cismontana
chaparral
nolina
None/None/1B.2 Chaparral, Coastal
scrub; sandstone or
gabbro/perennial
evergreen
shrub/(Mar)May–
July/459–4,180
Not expected to occur. The
site is outside of the
species’ known elevation
range.

Orcuttia
californica
California
Orcutt grass
FE/SE/1B.1 Vernal pools/annual
herb/Apr–Aug/49–
2,165
Not expected to occur.

Suitable vernal pool habitat
is absent within the project
site. Additionally, this
species is not known to
occur within the region2
(CDFW 2020).

Sagittaria
sanfordii
Sanford's
arrowhead
None/None/1B.2 Marshes and swamps
(assorted shallow
freshwater)/perennial
rhizomatous herb
(emergent)/May–
Oct(Nov)/0–2,130
Not expected to occur.

Suitable marsh or swamp
habitat is not present.

Additionally, the only one
occurrence in the region2 is
considered extirpated
(CDFW 2020).

APPENDIX C2

PLANT AND WILDLIFE SPECIES NOT EXPECTED TO OCCUR WITHIN THE BIOLOGICAL SURVEY AREA 11032
C2-4 March 2021
Special-Status Plant Species Not Expected to Occur within the Biological Survey Area Scientific Name
Common
Name
Regulatory
Status1 Habitat Requirements
Potential to Occur within
the BSA
Sidalcea
neomexicana
salt spring
checkerbloom
None/None/2B.2 Chaparral, Coastal
scrub, Lower montane
coniferous forest,
Mojavean desert scrub,
Playas; alkaline,
mesic/perennial
herb/Mar–June/49–
5,015
Low potential to occur.

Suitable coastal scrub
habitat is present, however
mesic habitats such as
springs or marshes are
absent. The only
occurrence in the region2
was last confirmed in 1962
and is located in Oak View
(CDFW 2020). This species
was not detected during
2018 or 2019 specialstatus plant species
surveys.

Streptanthus
campestris
southern
jewelflower
None/None/1B.3 Chaparral, Lower
montane coniferous
forest, Pinyon and
juniper woodland;
rocky/perennial
herb/(Apr)May–
July/2,950–7,545
Not expected to occur. The
site is outside of the
species’ known elevation
range. Additionally, suitable
habitat is not present.

Thelypteris
puberula var.
sonorensis
Sonoran
maiden fern
None/None/2B.2 Meadows and seeps
(seeps and
streams)/perennial
rhizomatous herb/Jan–
Sep/164–2,000
Not expected to occur.

Suitable meadow or seep
habitat is not present.
1Status Legend:

FE: Federally listed as endangered
SE: State listed as endangered
CRPR 1A: Plants presumed extinct in California
CRPR 1B: Plants rare, threatened, or endangered in California and elsewhere CRPR 2A: Plants rare, threatened, or endangered in California but common elsewhere CRPR 2B: Plants rare, threatened, or endangered in California but more common elsewhere CRPR 3: Plants about which more information is needed – a review list CRPR 4: Plants of limited distribution – a watch list
.1 Seriously endangered in California (over 80% of occurrences threatened/high degree and immediacy of threat) .2 Fairly endangered in California (20% to 80% of occurrences threatened) .3 Not very endangered in California (less than 20% of occurrences threatened or no current threats known). 2Region: “Region” refers to species recorded in the USGS 7.5-minute White Ledge Peak quadrangle, as well as the surrounding coastal quadrangles including Carpinteria, Pitas Point, Ventura, and Matilija (CDFW 2020; CNPS 2020).

CDFW (California Department of Fish and Wildlife). 2020. Rarefind 5: Commercial version. Online database.

California Natural Diversity Database. CDFW, Biogeographic Data Branch. Accessed December 2020. http://www.dfg.ca.gov/biogeodata/cnddb/mapsanddata.asp.

APPENDIX C2

PLANT AND WILDLIFE SPECIES NOT EXPECTED TO OCCUR WITHIN THE BIOLOGICAL SURVEY AREA 11032
C2-5 March 2021
CNPS (California Native Plant Society). 2020. Inventory of Rare and Endangered Plants (online edition, v8-03

0.39). Sacramento, California: California Native Plant Society. Accessed December 6, 2020 at www.rareplants.cnps.org.

Special-Status Wildlife Species Not Expected to Occur within the Biological Survey Area Scientific Name
Common
Name
Regulatory
Status1 Habitat Requirements
Potential to Occur within
the BSA
Amphibians
Anaxyrus
californicus
arroyo toad FE/SSC Semi-arid areas near washes,
sandy riverbanks, riparian
areas, palm oasis, Joshua
tree, mixed chaparral and
sagebrush; stream channels
for breeding (typically third
order); adjacent stream
terraces and uplands for
foraging and wintering
Not expected to occur. No
suitable wash, riparian, or
chaparral habitat present.

Rana boylii foothill yellowlegged frog
None/SSC,
SE
Rocky streams and rivers with
open banks in forest,
chaparral, and woodland
Not expected to occur. No
suitable stream, river,
forest, or chaparral habitat
present.

Rana draytonii California redlegged frog
FT/SSC Lowland streams, wetlands,
riparian woodlands, livestock
ponds; dense, shrubby or
emergent vegetation
associated with deep, still or
slow-moving water; uses
adjacent uplands
Not expected to occur. No
suitable stream, wetland,
woodland, or pond habitat
present.

Taricha torosa
(Monterey Co.
south only)
California
newt
None/SSC Wet forests, oak forests,
chaparral, and rolling
grassland
Not expected to occur. No
suitable forest, chaparral,
or grassland habitat
present.

Reptiles
Actinemys
marmorata
northwestern
pond turtle
None/SSC Slow-moving permanent or
intermittent streams, ponds,
small lakes, and reservoirs
with emergent basking sites;
adjacent uplands used for
nesting and during winter
Not expected to occur. No
suitable stream, pond, or
lake habitat present.

Thamnophis
hammondii
two-striped
gartersnake
None/SSC Streams, creeks, pools,
streams with rocky beds,
ponds, lakes, vernal pools
Not expected to occur. No
suitable stream, creek, or
pool habitat present.

APPENDIX C2

PLANT AND WILDLIFE SPECIES NOT EXPECTED TO OCCUR WITHIN THE BIOLOGICAL SURVEY AREA 11032
C2-6 March 2021
Special-Status Wildlife Species Not Expected to Occur within the Biological Survey Area Scientific Name
Common
Name
Regulatory
Status1 Habitat Requirements
Potential to Occur within
the BSA
Birds
Agelaius tricolor
(nesting colony)
tricolored
blackbird

BCC/SSC,
ST
Nests near freshwater,
emergent wetland with
cattails or tules, but also in
Himalayan blackberrry;
forages in grasslands,
woodland, and agriculture
Not expected to occur. No
suitable freshwater
wetland habitat present.

Athene
cunicularia
(burrow sites &
some wintering
sites)
burrowing owl BCC/SSC Nests and forages in
grassland, open scrub, and
agriculture, particularly with
ground squirrel burrows
Not expected to occur. No
suitable open scrub,
grassland, or agricultural
habitat present.

Brachyramphus
marmoratus
(nesting)
marbled
murrelet
FT/SE Nests in old-growth coastal
forests, forages in subtidal
and pelagic habitats
Not expected to occur. No
suitable old-growth forest
habitat present.

Charadrius
alexandrinus
nivosus
(nesting)
western snowy
plover
FT,

BCC/SSC
On coasts nests on sandy
marine and estuarine shores;
in the interior nests on sandy,
barren or sparsely vegetated
flats near saline or alkaline
lakes, reservoirs, and ponds
Not expected to occur. No
suitable marine/estuarine
sandy shore, flat, lake,
pond, or reservoir habitat
present.

Empidonax
traillii extimus
(nesting)
southwestern
willow
flycatcher
FE/SE Nests in dense riparian
habitats along streams,
reservoirs, or wetlands; uses
variety of riparian and
shrubland habitats during
migration
Not expected to occur. No
suitable riparian or
wetland habitat present.

Falco peregrinus
anatum
(nesting)
American
peregrine
falcon
FDL,

BCC/FP,
SDL
Nests on cliffs, buildings, and
bridges; forages in wetlands,
riparian, meadows, croplands,
especially where waterfowl
are present
Not expected to nest.

Suitable cliff nesting
habitat is present,
however the slopes and
cliffs within the project
area are subject to a high
amount of human
disturbance with walking
trails and popular
paragliding sites. This
species has been known
to nest along the south
coast, with former nest
sites including Gaviota
Pass; San Onofre Canyon
near Gaviota; Las Flores
APPENDIX C2

PLANT AND WILDLIFE SPECIES NOT EXPECTED TO OCCUR WITHIN THE BIOLOGICAL SURVEY AREA 11032
C2-7 March 2021
Special-Status Wildlife Species Not Expected to Occur within the Biological Survey Area Scientific Name
Common
Name
Regulatory
Status1 Habitat Requirements
Potential to Occur within
the BSA
Canyon; upper Mission
Canyon, Santa Barbara;
and Santa Monica Canyon
behind Carpinteria
(Lehman 2020).

Gymnogyps
californianus
California
condor
FE/FP, SE Nests in rock formations,
deep caves, and occasionally
in cavities in giant sequoia
trees (Sequoiadendron
giganteus); forages in
relatively open habitats where
large animal carcasses can
be detected
Not expected to occur.

This species is not known
to occur in coastal Santa
Barbara County in recent
history, and since the last
resident pair in the County
in the early 1980s, this
species is largely
restricted to the rural
interior of the County
primarily within the San
Rafael Wilderness and in
Sierra Madre. (Lehman
2020).

Passerculus
sandwichensis
beldingi
Belding's
savannah
sparrow
None/SE Nests and forages in coastal
saltmarsh dominated by
pickleweed (Salicornia spp.)
Not expected to occur. No
suitable saltmarsh habitat
present.

Polioptila
californica
californica
coastal
California
gnatcatcher
FT/SSC Nests and forages in various
sage scrub communities,
often dominated by California
sagebrush and buckwheat;
generally avoids nesting in
areas with a slope of greater
than 40%; majority of nesting
at less than 1,000 feet above
mean sea level
Not expected to occur.

While coastal scrub
habitat is present, this
species is only known
from one occurrence in
the region2 which was last
observed in 1906 near
Ventura (CDFW 2020).

Rallus obsoletus
levipes
Ridgway’s rail FE/SE, FP Coastal wetlands, brackish
areas, coastal saline
emergent wetlands
Not expected to occur. No
suitable wetland present.

Setophaga
petechia
(nesting)
yellow warbler BCC/SSC Nests and forages in riparian
and oak woodlands, montane
chaparral, open ponderosa
pine, and mixed-conifer
habitats
Not expected to occur. No
suitable riparian,
woodland, forest, or
chaparral habitat present.

APPENDIX C2

PLANT AND WILDLIFE SPECIES NOT EXPECTED TO OCCUR WITHIN THE BIOLOGICAL SURVEY AREA 11032
C2-8 March 2021
Special-Status Wildlife Species Not Expected to Occur within the Biological Survey Area Scientific Name
Common
Name
Regulatory
Status1 Habitat Requirements
Potential to Occur within
the BSA
Sternula
antillarum
browni (nesting
colony)
California
least tern
FE/FP, SE Forages in shallow estuaries
and lagoons; nests on sandy
beaches or exposed tidal flats
Not expected to occur. No
suitable estuary or lagoon
foraging habitat, or
suitable beach nesting
habitat present.

Vireo bellii
pusillus
(nesting)
least Bell's
vireo
FE/SE Nests and forages in low,
dense riparian thickets along
water or along dry parts of
intermittent streams; forages
in riparian and adjacent
shrubland late in nesting
season
Not expected to occur. No
suitable riparian habitat
present.

Fishes
Eucyclogobius
newberryi
tidewater goby FE/None Brackish water habitats along
the California coast from
Agua Hedionda Lagoon, San
Diego County, to the mouth of
the Smith River
Not expected to occur. No
suitable aquatic habitat
present.

Oncorhynchus
mykiss irideus
pop. 10
southern
steelhead -
southern
California DPS
FE/None Clean, clear, cool, welloxygenated streams; needs relatively deep pools in
migration and gravelly
substrate to spawn
Not expected to occur. No
suitable aquatic habitat
present.

Mammals
Antrozous
pallidus
pallid bat None/SSC Grasslands, shrublands,
woodlands, forests; most
common in open, dry habitats
with rocky outcrops for
roosting, but also roosts in
man-made structures and
trees
Not expected to occur.

While marginally suitable
habitat is present, this
species is known from
only one occurrence in the
region2 which was
recorded in 1906 (CDFW
2020).

Chaetodipus
californicus
femoralis
Dulzura
pocket mouse
None/SSC Open habitat, coastal scrub,
chaparral, oak woodland,
chamise chaparral, mixedconifer habitats; disturbance
specialist; 0 to 3,000 feet
above mean sea level
Not expected to occur. The
site is outside this species
known geographic range,
and is only known to occur
as west as Ojai and/or
Weldon (CDFW 2020).

Choeronycteris
mexicana
Mexican longtongued bat None/SSC Desert and montane riparian, desert succulent scrub,
desert scrub, and pinyon–
juniper woodland; roosts in
caves, mines, and buildings
Not expected to occur. No
suitable desert habitat
present.

APPENDIX C2

PLANT AND WILDLIFE SPECIES NOT EXPECTED TO OCCUR WITHIN THE BIOLOGICAL SURVEY AREA 11032
C2-9 March 2021
Special-Status Wildlife Species Not Expected to Occur within the Biological Survey Area Scientific Name
Common
Name
Regulatory
Status1 Habitat Requirements
Potential to Occur within
the BSA
Lasiurus
cinereus
hoary bat None/None Forest, woodland riparian,
and wetland habitats; also
juniper scrub, riparian forest,
and desert scrub in arid
areas; roosts in tree foliage
and sometimes cavities, such
as woodpecker holes
Not expected to occur. No
suitable trees for roosting
habitat or wetland,
woodland, riparian, or
desert habitat for foraging
present.

Taxidea taxus American
badger
None/SSC Dry, open, treeless areas;
grasslands, coastal scrub,
agriculture, and pastures,
especially with friable soils
Not expected to occur.

While marginally suitable
coastal scrub is present,
the species is known from
only one occurrence in the
region2 which is located
inland near Foster Park
and not along the coast
(CDFW 2020).

Invertebrates
Branchinecta
lynchi
vernal pool
fairy shrimp
FT/None Vernal pools, seasonally
ponded areas within vernal
swales, and ephemeral
freshwater habitats
Not expected to occur. No
suitable vernal pool,
vernal swale, or
ephemeral freshwater
habitat present.

Cicindela
hirticollis
gravida
sandy beach
tiger beetle
None/None Inhabits areas adjacent to
non-brackish water along the
coast of California from San
Francisco Bay to northern
Mexico
Not expected to occur. No
suitable non-brackish
aquatic habitat present or
nearby.

Coelus globosus globose dune
beetle
None/None Inhabitant of coastal sand
dune habitat; erratically
distributed from Ten Mile
Creek in Mendocino County
south to Ensenada, Mexico
Not expected to occur. No
suitable dune habitat
present.

Panoquina
errans
wandering
skipper
None/None Saltmarsh Not expected to occur. No
suitable saltmarsh habitat
present.

APPENDIX C2

PLANT AND WILDLIFE SPECIES NOT EXPECTED TO OCCUR WITHIN THE BIOLOGICAL SURVEY AREA 11032
C2-10 March 2021
Special-Status Wildlife Species Not Expected to Occur within the Biological Survey Area Scientific Name
Common
Name
Regulatory
Status1 Habitat Requirements
Potential to Occur within
the BSA
Streptocephalus
woottoni
Riverside fairy
shrimp
FE/None Vernal pools, non-vegetated
ephemeral pools
Not expected to occur. No
suitable vernal or
ephemeral pool habitat
present.
1Federal Designations:

FC Candidate for federal listing as threatened or endangered (FD) Federally delisted; monitored for five years
FE Federally listed Endangered
FT Federally listed as Threatened
FDL Federally delisted
BCC Bird of Conservation Concern
State Designations:

SC Candidate for state listing as endangered
SSC Species of Special Concern
FP California Department of Fish and Game Protected and Fully Protected Species SE State listed as Endangered
ST State listed as Threatened
SDL State delisted
WL Watch List 2 Region: “Region” refers to species recorded in the USGS 7.5-minute White Ledge Peak quadrangle, as well as the surrounding coastal quadrangles including Carpinteria, Pitas Point, Ventura, and Matilija (CDFW 2020; USFWS 2020).

CDFW (California Department of Fish and Wildlife). 2020. Rarefind 5: Commercial version. Online database.

California Natural Diversity Database. CDFW, Biogeographic Data Branch. Accessed December 2020. http://www.dfg.ca.gov/biogeodata/cnddb/mapsanddata.asp.

USFWS (United States Fish and Wildlife Service). 2020. Information for Planning and Consulting (IPaC). Accessed December 2020: https://ecos.fws.gov/ipac/
Appendix D
Cultural Appendix – CONFIDENTIAL

Appendix E
Geotechnical Report

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Appendix F
EnviroStor and GeoTracker Database Maps

GeoTracker Web-Site https://geotracker.waterboards.ca.gov/map/?CMD=runreport&myaddress=Rincon+Beach+County+Park# Accessed: January 14, 2021
GeoTracker Web-Site https://geotracker.waterboards.ca.gov/map/?CMD=runreport&myaddress=Rincon+Beach+County+Park# Accessed: January 14, 2021

GeoTracker Web-Site https://geotracker.waterboards.ca.gov/map/?CMD=runreport&myaddress=Rincon+Beach+County+Park# Accessed: January 14, 2021

EnviroStor Web-Site https://www.envirostor.dtsc.ca.gov/public/map/?myaddress=Rincon+Beach+County+Park Accessed: January 14, 2021

Appendix G
Drainage System Feaibility Discsusion

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Appendix H
Noise

NOISE APPENDIX
Published Noise Contour Maps

Fig
ure
N
-
2: F
uture
N
ois
e
C
o
nto
urs
Santa Barbara County Comprehensive Plan Noise Element - Carpinteria Area Noise Contours (2009)

NOISE APPENDIX
Construction Noise Modeling Data
Rincon Trail - Acoustical Analysis Report
Nearest Residential Receiver at Rincon Point
Construction Noise Modeling Worksheets
To User: bordered cells are inputs, unbordered cells have formulae noise level limit for construction phase, per County = 70 allowable hours over which Leq is to be averaged (example: 8 for County of San Diego, FTA guidance) = 8 Construction Phase Equipment Total Equipment Qty AUF % (from FHWA RCNM) Reference
Lmax @ 50 ft.
from FHWA
RCNM
Client Equipment Description,
Data Source and/or Notes
Source to NSR
Distance (ft.)
DistanceAdjusted Lmax Allowable Operation Time (hours) Allowable Operation Time (minutes) Predicted 8- hour Leq Site Preparation Grader 1 40 85 775 61.2 8 480 57
Dozer 1 40 82 775 58.2 7 420 54Front End Loader 1 40 79 775 55.2 8 480 51 Total for Site Preparation Phase: 59.5
Grading Grader 1 40 85 775 61.2 7 420 57
Tractor 1 40 84 Crawler Tractor 775 60.2 6 360 55
Front End Loader 1 40 79 775 55.2 7 420 51
Total for Grading Phase: 59.5
Trail Construction Tractor 1 40 84 Crawler Tractor 775 60.2 7 420 56 Backhoe 1 40 78 775 54.2 6 360 49
Total for Trail Construction Phase: 56.5
Bridge Construction Crane 1 16 81 775 57.2 8 480 49
Backhoe 1 40 78 775 54.2 6 360 49Welder / Torch 3 40 73 775 49.2 8 480 50 Total for Bridge Construction Phase: 54.2
Paving Tractor 1 40 84 775 60.2 8 480 56
Dump Truck 2 40 76 775 52.2 8 480 51
Total for Paving Phase: 57.4
Rincon Trail RCNM prepared by Dudek Nearest Residence S Rincon Trail - Acoustical Analysis Report
Nearest Residential Receiver North of US Hwy 101
Construction Noise Modeling Worksheets
To User: bordered cells are inputs, unbordered cells have formulae noise level limit for construction phase, per County = 70 allowable hours over which Leq is to be averaged (example: 8 for County of San Diego, FTA guidance) = 8 Construction Phase Equipment Total Equipment Qty AUF % (from FHWA RCNM) Reference
Lmax @ 50 ft.
from FHWA
RCNM
Client Equipment Description,
Data Source and/or Notes
Source to NSR
Distance (ft.)
DistanceAdjusted Lmax Allowable Operation Time (hours) Allowable Operation Time (minutes) Predicted 8- hour Leq Site Preparation Grader 1 40 85 600 63.4 8 480 59
Dozer 1 40 82 600 60.4 7 420 56Front End Loader 1 40 79 600 57.4 8 480 53 Total for Site Preparation Phase: 61.7
Grading Grader 1 40 85 600 63.4 7 420 59
Tractor 1 40 84 Crawler Tractor 600 62.4 6 360 57
Front End Loader 1 40 79 600 57.4 7 420 53
Total for Grading Phase: 61.7
Trail Construction Tractor 1 40 84 Crawler Tractor 600 62.4 7 420 58 Backhoe 1 40 78 600 56.4 6 360 51
Total for Trail Construction Phase: 58.7
Bridge Construction Crane 1 16 81 600 59.4 8 480 51
Backhoe 1 40 78 600 56.4 6 360 51Welder / Torch 3 40 73 600 51.4 8 480 52 Total for Bridge Construction Phase: 56.4
Paving Tractor 1 40 84 600 62.4 8 480 58
Dump Truck 2 40 76 600 54.4 8 480 53
Total for Paving Phase: 59.6
Rincon Trail RCNM prepared by Dudek Nearest Residence N Rincon Trail - Acoustical Analysis Report
Nearest Commercial Receiver North of US Hwy 101
Construction Noise Modeling Worksheets
To User: bordered cells are inputs, unbordered cells have formulae noise level limit for construction phase, per County = 75 allowable hours over which Leq is to be averaged (example: 8 for County of San Diego, FTA guidance) = 8 Construction Phase Equipment Total Equipment Qty AUF % (from FHWA RCNM) Reference
Lmax @ 50 ft.
from FHWA
RCNM
Client Equipment Description,
Data Source and/or Notes
Source to NSR
Distance (ft.)
DistanceAdjusted Lmax Allowable Operation Time (hours) Allowable Operation Time (minutes) Predicted 8- hour Leq Site Preparation Grader 1 40 85 655 62.7 8 480 59
Dozer 1 40 82 655 59.7 7 420 55Front End Loader 1 40 79 655 56.7 8 480 53 Total for Site Preparation Phase: 61.0
Grading Grader 1 40 85 655 62.7 7 420 58
Tractor 1 40 84 Crawler Tractor 655 61.7 6 360 56
Front End Loader 1 40 79 655 56.7 7 420 52
Total for Grading Phase: 61.0
Trail Construction Tractor 1 40 84 Crawler Tractor 655 61.7 7 420 57 Backhoe 1 40 78 655 55.7 6 360 50
Total for Trail Construction Phase: 57.9
Bridge Construction Crane 1 16 81 655 58.7 8 480 51
Backhoe 1 40 78 655 55.7 6 360 50Welder / Torch 3 40 73 655 50.7 8 480 51 Total for Bridge Construction Phase: 55.6
Paving Tractor 1 40 84 655 61.7 8 480 58
Dump Truck 2 40 76 655 53.7 8 480 53
Total for Paving Phase: 58.9
Rincon Trail RCNM prepared by Dudek Nearest Commercial N RCNM Equipment With Sound Generation Levels - Typical Construction Noise Modeling Worksheets Equipment Description Impact Device? Acoustical Use Factor (%) Lesser of or available Lmax Spec. 721 Lmax Measured Lmax @50ft (dBA, slow) All Other Equipment > 5 HP No 50 85 85 -- N/A --Auger Drill Rig No 20 84 85 84Backhoe No 40 78 80 78Bar Bender No 20 80 80 -- N/A --Blasting Yes -- N/A -- 94 94 -- N/A --Boring Jack Power Unit No 50 80 80 83Chain Saw No 20 84 85 84Clam Shovel (dropping) Yes 20 87 93 87Compactor (ground) No 20 80 80 83Compressor (air) No 40 78 80 78Concrete Batch Plant No 15 83 83 -- N/A --Concrete Mixer Truck No 40 79 85 79Concrete Pump Truck No 20 81 82 81Concrete Saw No 20 90 90 90Crane No 16 81 85 81Dozer No 40 82 85 82Drill Rig Truck No 20 79 84 79Drum Mixer No 50 80 80 80Dump Truck No 40 76 84 76Excavator No 40 81 85 81Flat Bed Truck No 40 74 84 74Front End Loader No 40 79 80 79Generator No 50 72 72 81Generator (<25KVA, VMS signs) No 50 70 70 73Gradall No 40 83 85 83Grader No 40 85 85 -- N/A --Grapple (on backhoe) No 40 85 85 87Horizontal Boring Hydr. Jack No 25 80 80 82Hydra Break Ram Yes 10 90 90 -- N/A --Impact Pile Driver Yes 20 95 95 101Jackhammer Yes 20 85 85 89Man Lift No 20 75 85 75Mounted Impact Hammer (hoe ram) Yes 20 90 90 90Pavement Scarafier No 20 85 85 90Paver No 50 77 85 77Pickup Truck No 40 55 55 75Pneumatic Tools No 50 85 85 85Pumps No 50 77 77 81Refrigerator Unit No 100 73 82 73Rivit Buster/chipping gun Yes 20 79 85 79Rock Drill No 20 81 85 81Roller No 20 80 85 80Sand Blasting (Single Nozzle) No 20 85 85 96Scraper No 40 84 85 84Shears (on backhoe) No 40 85 85 96Slurry Plant No 100 78 78 78Slurry Trenching Machine No 50 80 82 80Soil Mix Drill Rig No 50 80 80 -- N/A --Tractor No 40 84 84 -- N/A --Vacuum Excavator (Vac-truck) No 40 85 85 85Vacuum Street Sweeper No 10 80 80 82Ventilation Fan No 100 79 85 79Vibrating Hopper No 50 85 85 87Vibratory Concrete Mixer No 20 80 80 80Vibratory Pile Driver No 20 95 95 101Warning Horn No 5 83 85 83Welder / Torch No 40 73 73 74 prepared by Dudek
Appendix I
Airflow Analysis

Airflow analysis for the proposed regrading
of the Rincon bluffs
Paolo Luzzatto-Fegiz, PhD
January 22, 2021
Summary
This report provides an estimate of the change in vertical air velocity over the Rincon bluffs, as a consequence of the regrading associated with the proposed Rincon trail project. The analysis uses methodologies informed by a review of published scientific studies, civil engineering codes, as well well as practices from the paragliding and soaring communities. The analysis focuses on the specific case where wind is approaching perpendicular to the bluff, which is the case of greatest practical relevance.

As a consequence of the proposed regrading, the vertical wind velocity above the front of the bluff is expected to decrease by an amount between 10% and 30%. The addition of horizontal sections (that is, benches) in the bluff profile is likely to introduce some additional turbulence, which however is expected to remain close to the surface of the bluff, without significantly affecting altitudes greater than approximately 75ft above the bluff. A regrading involving one fewer bench near the bluff top is estimated to provide a reduction in vertical wind velocity between 10% and 20%.

Contents
1 Relevant prior work on topographic amplification and ridge lift . . . ............ 1

1.1 Wind amplification over topography .......................... 2

1.2 Vertical wind velocity over topography ......................... 3

1.3 Effect of introducing horizontal sections (benches) in the topographic profile .... 4

1.4 Connection to literature on soaring ........................... 4 2 Analysis ............................................. 4

2.1 Approximate representations of the topography .................... 5

2.2 Wind amplification .................................... 6

2.3 Vertical wind velocity .................................. 6

2.4 Effect of introducing horizontal sections (benches) in the topographic profile . . . . 11 3 Conclusions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 11 References . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12 List of Figures . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13 1 Relevant prior work on topographic amplification and ridge lift Although numerous studies have examined the effect of topography on local wind velocity, the focus in the literature has been predominantly on developing predictions for wind loads on buildings.

Studies have therefore typically focused on horizontal wind speeds and on gust velocities near the surface. By contrast, the vertical wind velocities induced by topography have received little attention. A review of relevant studies follows below.

Figure 1: Sketch of the key aerodynamic features of flow over topography, based on academic literature (e.g.

Jackson and Hunt, 1975), engineering codes (e.g. American Society of Civil Engineers, 2017) as well as soaring literature (e.g. Crawley and Schmanske, 1994; Pagen, 1992, 2001). The left-hand panel shows the definition of the reference velocity VH, which is the velocity of the undisturbed flow at the elevation of the top of the topography.

1.1 Wind amplification over topography
The study of wind acceleration over topography received its formal foundation in the theoretical modeling work of Jackson and Hunt (1975); this and subsequent efforts are summarized in the review of Belcher and Hunt (1998). Although their quantitative predictions are limited to gentle hills (and are therefore inapplicable here), their qualitative analysis of the aerodynamics of complex terrain remains relevant even for steep topography, and is illustrated in figure 1. The airflow accelerates over the terrain, as the flow is essentially forced to move through a smaller area; this is associated with a contraction of the streamlines in figure 1 (here, streamlines are used to illustrate the time-averaged path of the airflow). The region of fastest airflow occurs at the top of the topography, where the distance between the streamlines is smallest; this region is shown by the purple shaded region in the figure. The region of fastest vertical velocity (which is of relevance to soaring activities) occurs at the front of the topography, and is highlighted by the orange region in the figure.

Over the front of the topography, the interaction between airflow and surface roughness (such as vegetation, structures, or uneven terrain) and with more significant irregularities (such as benches) produces turbulence. This turbulence is transported by the mean airflow, and therefore moves essentially along the streamlines. As a result, at the front of the topography, the turbulence remains confined to a relatively thin layer near the surface. At the top of the topography, this layer grows in thickness, forming a region of stronger turbulence that can separate from the topography and is transported downstream; this is represented by the yellow region in figure 1. This qualitative overview of the flow is consistent with experiments, field measurements, recent engineering standards, as well as with the literature on soaring, as described below.

Bowen and Lindley (1977) performed wind tunnel experiments that systematically investigated the effect of steep topography on airflow. They measured horizontal velocities around topographies with front slopes varying from 4:1 to a vertical cliff; some of their results are shown later in figure 3. Bowen and Lindley (1977) found that, for small slope angles, an increase in slope yields a 2 corresponding increase in the maximum velocity above the topography. However, once the slope angle is increased past approximately 2:1, the maximum flow velocity no longer increases significantly, and instead remains around 1.8 times the wind velocity upstream of the topography. Bowen (1980) later showed that, for the front and top regions of the topography, field measurements at full scale agreed closely with the wind tunnel experiments of Bowen and Lindley (1977). For the region behind the topography, differences between wind tunnel and field measurements were found for front slopes steeper than 1:1. Bowen and Lindley (1977) and Bowen (1980) found that surface-generated turbulence remained confined to the near-surface region over the front of the topography, as it was essentially transported by the mean flow. Several other laboratory and field measurements have also supported these findings (including Hauf and Neumann-Hauf, 1982; Lange et al., 2016; Liu et al., 2016).

Theoretical predictions of the airflow over steep topography are challenging. Bowen (1983) summarized available theories for the “outer” flow (which is unaffected by the turbulence), noting that theories perform poorly once the slope exceeds 2:1. This was also confirmed by Jensen (1983) and Glanville and Kwok (1997), who compared theory to field data and reduced-scale experiments.

In addition, Bowen (1983) and Jensen (1983) discussed the difficult question of choosing approximate representations for complex topographies; these works inform our choices of approximate bluff profiles later in section 2. Overall, this review of past efforts suggests that, for topographies steeper than 2:1, it is best to rely on empirical or semi-empirical modeling approaches, rather than on theoretical analyses attempting to model the overall flow.

The results from wind tunnel experiments and field measurements reviewed above have been effectively implemented in engineering codes, such as ASCE 7-16, which provides semi-empirical relations for the maximum horizontal wind and gust velocities (American Society of Civil Engineers, 2017, p. 266; other engineering codes for flow over steep topography have been reviewed by Safaei Pirooz and Flay, 2018).

1.2 Vertical wind velocity over topography
To the best of our knowledge, current engineering codes do not provide relations for predicting vertical wind velocity at the front of steep topography; vertical wind velocities are rarely reported in experiments or field measurements.

In the soaring literature, a common approach for estimating vertical velocity over topography is to assume that the airflow is locally parallel to the surface (Crawley and Schmanske, 1994; Pagen, 1992). The vertical wind velocity is therefore obtained by multiplying a reference wind velocity Vwind by the sine of the slope angle α,
Vz = Vwind sin α. (1)
This approach, involving equation 1, is used for example in the book by Pagen (1992) to prepare their figure 139 on p. 158, although this does not appear to be made explicit in their presentation.

If the reference wind velocity Vwind is based on the flow upstream of the topography, equation 1 underestimates the actual vertical velocity Vz, as it neglects flow amplification, which is significant near the top of the topography. To address this issue, Crawley and Schmanske (1994) proposed a semi-empirical expression accounting for amplification, based on wind tunnel experiments. They tuned their expression to estimate vertical velocity at an altitude H/8 above the topography (which has maximum elevation H; in their specific experiments, this corresponded to a soaring altitude of 150 ft above the surface). Their expression is
Vz = Vwind
cH
cH − ztopo(x)
sin α(x), (2)
3 where H is the maximum elevation of the topography (see figure 1), ztopo(x) is the local elevation of the topography at a horizontal coordinate x, α(x) is the local slope angle, and c is an empirical constant, which they estimate between 3.5 and 4.0. The predictions of equation 2 are compared to our analysis in section 2 below. A significant limitation of equation 2 is that it is intended to only provide predictions at a fixed altitude of H/8 above the slope, and cannot be used at other altitudes.

1.3 Effect of introducing horizontal sections (benches) in the topographic profile Introducing a horizontal segment (a “bench”) on the topography has two main effects. First, if the highest elevation of the topography is shifted downstream, the average slope angle will be effectively reduced. This will reduce the vertical velocity. Second, the bench may introduce turbulence, which is associated with flow separation and unsteadiness that occurs at the front of the bench, where the topography rapidly curves away from the incoming flow (figure 1). For small benches, a local region of recirculating flow may form, with the outer airflow effectively ‘skipping’ over the bench, and continuing to follow the topography at a higher elevation.

The only formal study of the effect of a significant bench appears to be the wind tunnel experiment of Zheng et al. (2018), who examined the effect of a large bench (of horizontal extent H/2) on a 1:1 slope. They measured flow velocities and turbulence at an altitude of 0.2H from the surface and above. Zheng et al. (2018) found that the bench had a negligible effect on flow amplification near the top of the topography. The turbulence generated over the bench followed the surface of the topography; for an altitude of more than 0.5H above the surface, there was no measurable increase in turbulence intensity. At 0.2H above the surface, a small increase in turbulence intensity was found, corresponding to an increase of approximately 4% in gust velocity. An increase in turbulence intensity was found close to the top surface of the topography (consistently with the sketch shown earlier in figure 1).

Although Zheng et al. (2018) appear to provide the only targeted investigation of the effect of benches, several studies have examined complex, realistic topographies featuring irregularities (e.g.

Cuerva-Tejero et al., 2018; Glanville and Kwok, 1997); a common finding is that the turbulence generated over the surface does not significantly affect the outer flow on the front of the topography.

1.4 Connection to literature on soaring
As already noted above, the findings from the scientific and engineering literature are consistent with the qualitative discussions found in the soaring literature. Two key references are Pagen’s books “The Art of Paragliding” and “Understanding the Sky” (Pagen, 1992, 2001). The regions highlighted in figure 1 match those discussed for example in figures 13-3, 13-6, 13-11, 13-12 and 13-13 of Pagen (2001). The region of strongest vertical velocity in figure 1 corresponds to the “soarable envelope”, whereas the region of maximum velocity corresponds to Pagen’s “Venturi area”.

In addition, figures 105, 106 and 115 of Pagen (1992) indicate that airflow above the slope can be largely unaffected by turbulence produced on the slope surface, consistently with the measurements summarized in the previous section.
2 Analysis
As noted earlier, theoretical models that attempt to describe the complete flow can be inaccurate for steep topographies. Civil engineering codes provide semi-empirical formulas for horizontal wind velocity, but do not appear to consider vertical wind velocities. For this reason, the analysis 4 Figure 2: (a): comparison of original bluff profile and proposed regrading. (b): proposed regrading without top bench. (c) Approximations to the original profile, based on mean slope (blue) and near-top slope (red). (d): approximations for proposed regrading, and (e) approximations for proposed regrading without top bench.
presented here employs several semi-empirical approaches, relying also on the well-established data set of Bowen and Lindley (1977), who measured flow over topographies with different slope angles.

2.1 Approximate representations of the topography
The analysis is based on a representative two-dimensional section of the Rincon bluffs, shown in figure 2(a). To approximate the topography, two approaches are used and compared. The first approximation defines a mean slope, which joins the foot of the bluffs (where the topography rapidly departs from horizontal) to the top of the topography; this approach is consistent with 5 approximations used in the academic literature (e.g. Jensen, 1983), and is expected to approximate the airflow at an altitude larger than the lengthscale of the benches. This mean slope is shown by the blue lines in figure 2(c,d). The second approximation uses a slope based on the bluff shape near the top, where the maximum air velocity is expected. This approximation may be more representative of local flow conditions experienced very close to the ridge, and is shown by the red lines in figure 2(c,d). Quantities referring to the original bluffs and to the proposed regrading are represented using dashed and continuous lines, respectively. The slope angles associated with each approximation are shown in the figure.

An alternative proposed regrading was also considered, which essentially removed the bench closest to the top of the topography. This is sketched in figure 2(b,e), and only implies a change in the mean slope.

The analysis does not consider other effects, such as changes in vegetation patterns, and addition or removal of other structures. As noted earlier, the incoming wind direction is assumed perpendicular to the bluffs. A neutrally stratified atmosphere is assumed.

2.2 Wind amplification
To estimate wind amplification, the data of Bowen and Lindley (1977) for the wind amplification factor Az are digitized. The quantity Az is defined as the ratio between the wind speed measured at a point over the topography and the wind speed found upstream of the topography, at the same altitude (for example, a point 30 ft above the bluff is compared to an upstream point that is 30 ft above the ocean surface). Figure 3 shows maps of Az for topographies ranging from a 2:1 slope to a vertical cliff. Lengths are normalized by the maximum elevation H of the topography. These maps of wind amplification are used to calculate vertical wind velocity in the next section.

2.3 Vertical wind velocity
To obtain a first estimate of the change in vertical velocity due to the regrading, we note that the wind amplification at a given elevation is not expected to change significantly after the regrading, since the mean slope remains significantly steeper than 2:1. Noting that the vertical velocity near the surface will be equal to the wind magnitude times sin(α), the ratio of the vertical velocities before and after the regrading may be approximated as
Vw|
regrading
Vw|
original
= sin(αregrading)
sin(αoriginal) . (3)
This expression can also be obtained from equation 2 (due to Crawley and Schmanske, 1994), as long as one compares slope locations with the same elevation. Using the slopes in figure 2, equation 3 implies a reduction in Vz between 12% and 20% for the proposed regrading, and a reduction between 12% and 15% for the regrading without the top bench. This simple prediction is expected to be reasonable at an altitude that is small compared to H (say, around 0.1 H, corresponding to approximately 15 ft).

To obtain an estimate of the change in Vz at greater altitudes, we return to the data set of Bowen and Lindley (1977). As noted in section 1, Bowen and Lindley (1977) did not measure vertical velocities; for this reason, we deduce the vertical velocity Vz from the horizontal velocity Vx over the topography, which is calculated from Az. Since the time-averaged flow is exclusively in the x − z plane, mass conservation implies ∂Vx
∂x + ∂Vz∂z = 0 (e.g. Batchelor, 2000). We calculate ∂Vx∂x and integrate the equation for mass conservation to find Vz(z)= Vz(z1) − z z1
∂Vx
∂x dz, where z1 is an
6 Figure 3: Acceleration of flow over slopes of varying steepness, for a given altitude, expressed by the amplification factor Az, such that Az > 1 represents accelerated flow relative to the undisturbed conditions upstream. Contours are shown at intervals of 0.1. The Az =1.0 contours are shown by dotted lines. Each panel shows: (a) 2:1 slope, (b) 1:1 slope, and (c) a vertical bluff. Data adapted from the wind tunnel experiments of Bowen and Lindley (1977). 7 Figure 4: Vertical wind velocities over slopes of varying steepness, deduced from the wind tunnel experiments of Bowen and Lindley (1977). The theory of Crawley and Schmanske (1994) (corresponding to equation 2, valid only for z/H =1.125) is shown for comparison. elevation at which Vz(z1) is known; we take z1 =5.5H, where the vertical flow is small compared to the vertical velocities induced near the topography, such that Vz(z1) 0.

The calculated vertical velocities Vz for each of the experiments of Bowen and Lindley (1977) are shown in figure 4. The left-hand panels show fields of vertical velocity over each topography, normalized by VH, which is the wind velocity of the upstream flow at an elevation z = H (se 8 Figure 5: Change in vertical velocity associated with the proposed regrading. (a) and (c) show estimated vertical velocities, whereas (b) and (d) show percentage changes. The top two panels (a) and (b) use the mean slope, whereas the bottom two panels (c) and (d) use the maximum slope near the bluff top. The circles in (b) and (d) show the prediction of the simple approximation in equation 3, which is valid close to the slope surface.
figure 1). The contour corresponding to the arbitrary value Vz = VH/4 is drawn to convey the extent of the region where uplift is experienced (uplift is experienced also outside of this region, although with lower intensity). Within this contour, the line showing the x-location of highest vertical velocity at each z is shown by by a dashed line. The vertical velocity along this line is plotted in the right-hand panels. As a check on our calculation, we compared our calculated Vz for the 2:1 slope with the wind tunnel data of Liu et al. (2016), who measured Vz at selected locations over a similar topography, finding consistent predictions. We also compare our results with the theory of Crawley and Schmanske (1994), which predicts Vz only at an altitude of H/8 above the slope, finding good agreement for this altitude, as shown in the right-hand panels of figure 4.

To predict Vz for the slopes relevant to the Rincon bluffs, we interpolate the horizontal velocities of Bowen and Lindley (1977) with respect to slope angle, thereby obtaining approximate horizontal velocities for the slopes shown earlier in figure 2. We then use the same approach described above to 9 Figure 6: Change in vertical velocity associated with the proposed regrading, for the case involving one fewer bench near the bluff top. (a) and (c) show estimated vertical velocities, whereas (b) and (d) show percentage changes. The top two panels (a) and (b) use the mean slope, whereas the bottom two panels (c) and (d) use the maximum slope near the bluff top. The circles in (b) and (d) show the prediction of the simple approximation in equation 3, which is valid close to the slope surface. deduce vertical velocities Vz. The maximum vertical velocities at each z are shown in the left-hand panels of figure 5, for both the original bluff and the proposed regrading. The right-hand panels show the percentage change at each z. The analysis based on the mean slope predicts that the vertical velocity will be reduced by approximately 30%, whereas the analysis based on the near-top slope predicts a reduction of around 10%. Panels (b) and (d) also show the simple prediction from equation 3; since this result is valid only close to the slope surface, we display it using circles placed at the bluff top.

For the regrading that involves one fewer bench, the mean slope increases relative to the initially proposed regrading, which brings the predicted reduction in Vz to around 20%, as shown in panel (d) of figure 6. For completeness, predictions for the near-top slope analysis are also reported, although they are the same as in figure 5.
10 2.4 Effect of introducing horizontal sections (benches) in the topographic profile As discussed earlier in section 1.3, the introduction of a bench through regrading implies a reduction in the mean slope, and therefore a reduction in vertical velocity; this effect is already accounted for in the mean-slope analysis in section 2.3. To estimate the additional turbulence introduced by the bench, we refer to the wind-tunnel study of Zheng et al. (2018); accoordingly, one may expect that introducing a bench would result in increase in turbulence of the order of 5% at an altitude of around 0.2 H above the topography, corresponding to an altitude of approximately 30 ft above the Rincon bluffs. Based on the data of Zheng et al. (2018), this additional turbulence is expected to become negligible by an altitude of 0.5 H above the topography, corresponding to approximately 75 ft above the Rincon bluffs. Turbulence on the top surface of the bluffs (in the high-turbulence region highlighted in figure 1) is likely to be increased more significantly. 3 Conclusions
Based on a review of the scientific, engineering and soaring literature, the change in vertical airflow associated with a proposed regrading of the Rincon bluffs has been estimated. The approach used simplified slope profiles, together with a re-analysis of published experimental data for slopes of various angles. It is estimated that the proposed regrading would reduce the vertical airflow velocity by 10% to 30% relative to current conditions; for altitudes relevant to soaring activities, the reduction is expected to be closer to 30%. An alternative proposed regrading, involving one fewer bench near the bluff top, would reduce the airflow velocity by 10% to 20%. Based on available experimental results, the introduction of a bench is expected to provide a small increase in turbulence (of the order of 5%) at an altitude of 30 ft above the front of the bluffs, becoming negligible by an altitude of approximately 75 ft.

Disclaimer
The aerodynamics of wind over complex topography are the subject of ongoing research, and no standard engineering approach exists for the calculations reported here. While every effort has been made to ensure accuracy of the predictions, within the constraints associated with the assumptions and methodologies used, no warranties are made or implied with regards to the predictions obtained from this study.
11 References
American Society of Civil Engineers. (2017): ASCE/SEI 7-2016: Minimum design loads and associated criteria for buildings and other structures. American Society of Civil Engineers.

Batchelor, G. K. (2000): An introduction to fluid dynamics. Cambridge University Press.

Belcher, S. E., & Hunt, J. C. R. (1998): Turbulent flow over hills and waves. Annu. Rev. Fluid Mech., 30 (1), 507–538.

Bowen, A. J. (1980): Full scale measurements of the atmospheric turbulence over two escarpments.

In J. E. Cermak (Ed.), Wind engineering (pp. 161–172). Pergamon.

Bowen, A. J. (1983): The prediction of mean wind speed above simple 2D hill shapes. J. Wind Eng.

Ind. Aerodyn., 15 (1), 259–270.

Bowen, A. J., & Lindley, D. (1977): A wind-tunnel investigation of the wind speed and turbulence characteristics close to the ground over various escarpment shapes. Bound.-Layer Meteorol., 12 (3), 259–271.

Crawley, E. F., & Schmanske, M. (1994): Optimum ridge lift: A scaled experimental investigation.

Technical Soaring, 18 (4), 120–128.

Cuerva-Tejero, A., Avila-Sanchez, S., Gallego-Castillo, C., Lopez-Garcia, Ó., Pérez-Alvarez, J., & Yeow, T. S. (2018): Measurement of spectra over the bolund hill in wind tunnel. Wind Energy, 21 (2), 87–99.

Glanville, M. J., & Kwok, K. C. S. (1997): Measurements of topographic multipliers and flow separation from a steep escarpment. part II. model-scale measurements. J. Wind Eng. Ind.

Aerodyn., 69-71, 893–902.

Hauf, T., & Neumann-Hauf, G. (1982): The turbulent wind flow over an embankment. Bound.-Layer Meteorol., 24 (3), 357–369.

Jackson, P. S., & Hunt, J. C. R. (1975): Turbulent wind flow over a low hill. Quart. J. Roy. Meteor.

Soc., 101 (430), 929–955.

Jensen, N. O. (1983): Escarpment induced flow perturbations, a comparison of measurements and theory. J. Wind Eng. Ind. Aerodyn., 15 (1), 243–251.

Lange, J., Mann, J., Angelou, N., Berg, J., Sjöholm, M., & Mikkelsen, T. (2016): Variations of the wake height over the bolund escarpment measured by a scanning lidar. Bound.-Layer Meteorol., 159 (1), 147–159.

Liu, Z., Ishihara, T., Tanaka, T., & He, X. (2016): LES study of turbulent flow fields over a smooth 3-D hill and a smooth 2-D ridge. J. Wind Eng. Ind. Aerodyn., 153, 1–12.

Pagen, D. (1992): Understanding the sky (First Edition). Sport Aviation Publications.

Pagen, D. (2001): The art of paragliding (1st ed.). Sport Aviation Publications.

Safaei Pirooz, A. A., & Flay, R. G. J. (2018): Comparison of speed-up over hills derived from wind-tunnel experiments, wind-loading standards, and numerical modelling. Boundary Layer Meteorol., 168 (2), 213–246.

Zheng, K., Tian, W., Qin, J., & Hu, H. (2018): An experimental study on the turbulent flow over two-dimensional plateaus [2018–0754]. 2018 Wind Energy Symposium. American Institute of Aeronautics and Astronautics.
12 List of Figures
1 Sketch of the key aerodynamic features of flow over topography, based on academic literature (e.g. Jackson and Hunt, 1975), engineering codes (e.g. American Society of Civil Engineers, 2017) as well as soaring literature (e.g. Crawley and Schmanske, 1994; Pagen, 1992, 2001). The left-hand panel shows the definition of the reference velocity VH, which is the velocity of the undisturbed flow at the elevation of the top of the topography. ..................................... 2 2 (a): comparison of original bluff profile and proposed regrading. (b): proposed regrading without top bench. (c) Approximations to the original profile, based on mean slope (blue) and near-top slope (red). (d): approximations for proposed regrading, and (e) approximations for proposed regrading without top bench. .... 5 3 Acceleration of flow over slopes of varying steepness, for a given altitude, expressed by the amplification factor Az, such that Az > 1 represents accelerated flow relative to the undisturbed conditions upstream. Contours are shown at intervals of 0.1. The Az =1.0 contours are shown by dotted lines. Each panel shows: (a) 2:1 slope, (b) 1:1 slope, and (c) a vertical bluff. Data adapted from the wind tunnel experiments of Bowen and Lindley (1977). ................................ 7 4 Vertical wind velocities over slopes of varying steepness, deduced from the wind tunnel experiments of Bowen and Lindley (1977). The theory of Crawley and Schmanske (1994) (corresponding to equation 2, valid only for z/H =1.125) is shown for comparison. ......................................... 8 5 Change in vertical velocity associated with the proposed regrading. (a) and (c) show estimated vertical velocities, whereas (b) and (d) show percentage changes. The top two panels (a) and (b) use the mean slope, whereas the bottom two panels (c) and (d) use the maximum slope near the bluff top. The circles in (b) and (d) show the prediction of the simple approximation in equation 3, which is valid close to the slope surface. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 9 6 Change in vertical velocity associated with the proposed regrading, for the case involving one fewer bench near the bluff top. (a) and (c) show estimated vertical velocities, whereas (b) and (d) show percentage changes. The top two panels (a) and (b) use the mean slope, whereas the bottom two panels (c) and (d) use the maximum slope near the bluff top. The circles in (b) and (d) show the prediction of the simple approximation in equation 3, which is valid close to the slope surface. . . . . . . . . 10 13 Appendix J
Transportation Memorandum

February 18, 2021
John Ilasin, Public Works Director/City Engineer
City of Carpinteria
Public Works Department
5775 Carpinteria Avenue
Carpinteria, CA 93013
Re: Evaluation of Rincon Multi-Use Trail Preliminary Design Dear Mr. Ilasin,
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Traffic Engineering
Municipal Services
Interwest Consulting Group, Inc.

Appendix K
County Connector Trail Proposal – Rincon Park Project
Components Study

County Connector Trail
Rincon Park Project

Page 1 ends

Carpinteria City CouncilMarch 28, 2022

Carpinteria City Council
March 28, 2022