Cities Index.
Agenda packet

South El Monte City Council
January 25, 2022

Document
Agenda packet
Meeting
January 25, 2022
Body
South El Monte City Council
Pages
816
Original file
78.9 MB
Text extracted from the city's file for reading and search. Open the original on southelmonteca.api.civicclerk.com. That file is the official record.

Section 4.0
Environmental Analysis
102 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration
SGVWC is able to rely on the Central Basin for adequate supply over the next 20 years under single year and multiple year droughts.

In 2015, SGVWC pumped 31,211 AF of groundwater. Projected groundwater supplies are expected to reach 45,452 AF by 2040. In 2015, actual water consumption was 120 gallons per capita per day (gpcd).

Future water use projections are based on SGVWC’s calculated SB X7-7 water use target of 142 gpcd. The project is expected to have 332 new residents, which would generate approximately 47,144 gallons per day (gpd), or 52.8 AF per year. The project’s water demand, if solely relied from groundwater resources, would represent 0.17 percent of the total groundwater supply in 2015. Further, the City would continue to comply with SB X7-7 Requirements. Compliance SB X7-7 reduction targets would reduce any projectrelated impacts on sustainable groundwater management plans. Impacts are less than significant and no mitigation is required.

Cumulative Impacts
Buildout of the proposed project, in combination with present and reasonably foreseeable future development that would occur within the watershed, would involve construction activities, new development from which runoff would discharge into waterways, potential increased in storm water runoff from new impervious surfaces, and a potential reduction in groundwater recharge areas.

Construction of new development within the watershed could result in the erosion of soil, thereby cumulatively impacting water quality within the watershed. In addition, the increase in impermeable surfaces and more intensive land uses within the watershed resulting from future development may also adversely affect water quality by increasing the amount of storm water runoff and common urban contaminants entering the storm drain system. However, new development would be required to comply with existing regulations regarding construction and operational practices that minimize risks of erosion and runoff. Compliance with requirements would minimize degradation of water quality at individual construction sites. As such, no significant cumulative impacts are anticipated.

Mitigation Program
Standard Conditions and Mitigation Measures
No standard conditions or mitigation measures are applicable to the project.

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Section 4.0
Environmental Analysis
103 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration

4.11 Land Use and Planning
Threshold (a) Would the project physically divide an established community? No Impact. Examples of projects that could physically divide an established community include a new freeway or highway that traverse an established neighborhood. The project site is within an urbanized and established area of the City of South El Monte. The project site is at the southwest corner of the Rosemead Boulevard at Mabel Avenue intersection and is bordered by light industrial and commercial uses to the north and west, two single-family residences to the west, and mobile home park to the south.

The proposed project would allow for the development of a mixed-use building with retail and residential uses. The project does not propose any new streets or other physical barriers that could physically divide an established community. Given the location and nature of the proposed project, the project would not physically divide established communities. No impact would occur and no mitigation is required.

Threshold (b) Would the project cause a significant environmental impact due to a conflict with any land use plan, policy, or regulation adopted for the purpose of avoiding or mitigating an environmental effect?
Less Than Significant Impact. The proposed project requires a General Plan Amendment to change the land use designation from Commercial-Manufacturing to Mixed-Use and a zone change from CommercialManufacturing (C-M) to Commercial Residential (C-R). Once entitled, the proposed project would be consistent with the goals and policies of the City of South El Monte General Plan. Table 4.11-1: General Plan Consistency Analysis demonstrates the proposed project’s consistency with General Plan policies.

Table 4.11-1: General Plan Consistency Analysis
Land Use Element
Goal 1: Maintain a balanced mix and distribution
of land uses throughout South El Monte
Consistent. The proposed project would introduce a mixeduse development on a large vehicle storage and junkyard, near existing single-family residential and mobile home park uses to the south and west and commercial uses to the north and east.

Policy 1.1 Provide opportunities for housing
developments at a range of densities and
housing types that accommodate the carried
interests and needs of present and future
residents.

Consistent. The project would include a mix of one to threebedroom leasable apartment units ranging in size from 770 sf to 1,469 sf. The proposed project would have 73 apartment units on a 1.73-acre site at a density of 42.4 du/ac. This mix of uses and increase in density on the site would be consistent with implementation of Policy 1.1 and Policy 1.2. Policy 1.2 Allow for the transition of mixeddensity neighborhoods to higher density development with underlying General Plan land
use and zoning designations.

Policy 1.4 Create opportunities for two types of
commercial development: (1) commercial uses
that meet the retail and service needs of the
local resident and employee populations, and (2)
regional-serving retail commercial businesses
that capture revenues from a broader
population base.

Consistent. The project proposes 13,630 sf of commercial retail and 3,170 sf of food retail uses on the ground level of the building fronting on to Rosemead Boulevard. Commercial retail space would be available for lease for offices and retails/services, while food retail would be available for restaurant and coffee shop uses. The mix of proposed uses would serve local retail and service needs and would be consistent with implementation of Policy 1.4.

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Section 4.0
Environmental Analysis
104 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration
Table 4.11-1: General Plan Consistency Analysis
Land Use Element
Goal 2: Focus new revenue-generating
development in those areas of the City with high
visibility.

Consistent. The project would be located at the intersection of Rosemead Boulevard at Mabel Avenue with retail frontage on Rosemead Boulevard, which is a key roadway through the City.

Policy 2.2 Expand development opportunities
along Rosemead Boulevard by allowing for a
broader range of commercial, as well as office
uses. Rezone the east side of Rosemead
Boulevard Commercial-Manufacturing.

Consistent. The proposed project would introduce a mix of commercial retail and food retail uses as well as residential units to the project site, located on Rosemead Boulevard. The mix of commercial uses would introduce additional
development to the area and would be consistent with
implementation of Policy 2.2.

Goal 3.0: Accommodate new development that
is compatible with and complements existing
land uses.

Consistent. The project area includes a mix of residential, commercial, and light-industrial uses. The proposed project would include residential and commercial uses, consistent with established uses in the area.

Policy 3.1 Require that multi-family
development provide adequate buffers (such as
decorative walls and landscaped setbacks) at the
designated boundaries with adjacent singlefamily residential uses to prevent impacts on residences due to noise, traffic, parking, light
and glare, and differences in scale; to ensure
privacy; and to provide visual compatibility.

Policy 3.2 Require that commercial development
provide adequate buffers (such as decorative
walls and landscaped setbacks) at the
designated boundaries with adjacent singlefamily residential uses to prevent impacts on residences due to noise, traffic, parking, light
and glare, and differences in scale; to ensure
privacy; and to provide visual compatibility.

Consistent. The project would include six-foot-high concrete block walls along the southern and western site boundaries and this area would be landscaped. The proposed walls would separate the development from existing off-site residential uses and preclude significant off-site impacts related to noise and lighting. Project lighting would include outdoor lighting for security, wayfinding. Additionally, exterior lighting fixtures along the building frontage would provide illumination for retail storefronts and signage. All lighting would be directed on to the site and oriented away from off-site residential uses to reduce the potential for impacts from light and glare.

Accordingly, the project would be consistent with
implementation of Policy 3.1 and Policy 3.2.

Circulation Element
Goal 4.0: Accommodate alternative modes of
transit in land use and circulation system
planning.

The proposed project is approximately 0.2 mile east of the Rio Hondo bikeway. Future proposed bikeways in the project
vicinity include a Class II bikeway along Rosemead Boulevard and a Class III bikeway along Loma Avenue and Mabel
Avenue. The proposed project would not result in impacts to existing or planned bikeways and would support the use of alternative modes of transit. The project would include bike storage on the ground floor of the parking garage.

Accordingly, the project would be consistent with
implementation of Goal 4.0.

Public Safety Element
Goal 3.0: Minimize the adverse effects of
excessive or unusual noise on the City’s
residential and business populations.

As discussed in Section 4.13, the proposed project would result in a less than significant impact concerning construction and operational noise and would comply with Municipal Code Section 8.20.020, Exterior Noise Limits. Section 8.20.020 codifies Table General Plan Table PS-1, Noise/Land Use

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Section 4.0
Environmental Analysis
105 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration
Table 4.11-1: General Plan Consistency Analysis
Land Use Element
Policy 3.1 Use the noise/land use compatibility
standards presented in Table PS-1 as a guide for
future planning and development decisions.

Compatibility Chart. Accordingly, the project would be
consistent with implementation of Goal 3.0 and Policy 3.1.

As discussed in Table 4.11-1, the proposed project would be consistent with or otherwise would not conflict with the identified Land Use Element, Circulation Element, or Public Safety Element goals and policies of the General Plan. Further, the City is currently updating its Housing Element as part of the 6th Cycle Update, which covers the 2021-2029 planning period. SCAG has issued the regional housing needs assessment (RHNA) for the City of South El Monte for the 6th cycle update. The 6th Cycle Update RHNA allocation for the City identifies a need for 577 housing units during the 2021-2029 planning period.

The project would provide for 73 dwelling units; accordingly, the project would be consistent with the General Plan Housing Element by assisting the City in meeting its housing needs. Therefore, the proposed project would not conflict with any land use plan, policy, or regulation adopted to mitigate an environmental effect. Impacts would be less than significant and no mitigation is required.

Cumulative Impacts
While project implementation would require a General Plan Amendment and zone change, proposed uses would be consistent with applicable goals and policies identified in the General Plan. Further, this Initial Study finds that all potential environmental impacts of the project would either be less than significant or can be mitigated to a less than significant level. City growth would be subject to review for consistency with adopted land use plans and policies by the City, in accordance with the requirements of CEQA, the State Zoning and Planning Law, and the State Subdivision Map Act, all of which require findings of plan and policy consistency prior to approval of entitlements for development. Therefore, no significant cumulative impacts associated with plans and policies would occur.

Mitigation Program
Standard Conditions and Mitigation Measures
No standard conditions or mitigation measures are required.

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Section 4.0
Environmental Analysis
106 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration

4.12 Mineral Resources
Threshold (a) Would the project result in the loss of availability of a known mineral resource that would be of value to the region and the residents of the state? and Threshold (b) Would the project result in the loss of availability of a locally-important mineral resource recovery site delineated on a local general plan, specific plan or other land use plan?
No Impact. The project site has not historically and is not currently a site for mineral recovery. There are no land within the City of South El Monte designated by the California Department of Conservation as known significant mineral resource areas, defined by the State as Mineral Resources Zone 2 (MRZ-2) areas.

The City’s General Plan does not designate any mineral resource zones within the City. Further, the proposed project does not involve any use that would result in any impacts to mineral resources.

Therefore, there would be no loss of a known mineral resource and no impact would occur.

Cumulative Impacts
The analysis of potential impacts indicated that no impacts would result from the proposed project. As a result, no cumulative impacts related to mineral resources would occur.

Mitigation Program
Standard Conditions and Mitigation Measures
No standard conditions or mitigation measures are required.

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Section 4.0
Environmental Analysis
107 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration

4.13 Noise
A noise analysis was prepared by Kimley-Horn and Associates, Inc. (Kimley-Horn, 2021) for the proposed project. The noise analysis results are summarized in this Initial Study.

Background
Sound is technically described in terms of amplitude (loudness) and frequency (pitch). The standard unit of sound amplitude measurement is the decibel (dB). The decibel scale is a logarithmic scale that describes the physical intensity of the pressure vibrations that make up any sound. The pitch of the sound is related to the frequency of the pressure vibration. Since the human ear is not equally sensitive to a given sound level at all frequencies, a special frequency-dependent rating scale has been devised to relate noise to human sensitivity. The A-weighted decibel scale (dBA) provides this compensation by discriminating against frequencies in a manner approximating the sensitivity of the human ear.

Noise, on the other hand, is typically defined as unwanted sound. A typical noise environment consists of a base of steady ambient noise that is the sum of many distant and indistinguishable noise sources.

Superimposed on this background noise is the sound from individual local sources. These can vary from an occasional aircraft or train passing by to virtually continuous noise from traffic on a major highway.

Several rating scales have been developed to analyze the adverse effect of community noise on people.

Since environmental noise fluctuates over time, these scales consider that the effect of noise on people is largely dependent on the total acoustical energy content of the noise as well as the time of day when the noise occurs. For example, the equivalent continuous sound level (Leq) is the average acoustic energy content of noise for a stated period of time; therefore, the Leq of a time-varying noise and that of a steady noise are the same if they deliver the same acoustic energy to the ear during exposure. The Day-Night Sound level (Ldn) is a 24-hour average Leq with a 10 dBA “weighting” added to noise during the hours of 10:00 PM to 7:00 AM to account for noise sensitivity in the nighttime. The Community Noise Equivalent Level (CNEL) is a 24-hour average Leq with a 10 dBA weighting added to noise during the hours of 10:00 PM to 7:00 AM and an additional 5 dBA weighting during the hours of 7:00 PM to 10:00 PM to account for noise sensitivity in the evening and nighttime.

Existing Setting
The project site would involve site clearing of the existing storage uses and construction of a four-story mixed-use development with 73 apartment units with ground floor retail uses, and ground level parking with an above ground parking deck. The area surrounding the project site is urbanized. The site is bordered by Mabel Avenue to the north, Rosemead Boulevard to the east, a mobile home park to the south, and two single-family residences and light industrial uses to the west. Mobile sources of noise, especially cars and trucks, are the most common and significant sources of noise in the area. Most of the existing mobile noise in the project area is generated from vehicles along surrounding roadways, primarily Rosemead Boulevard as well as by Mabel Avenue. The primary sources of stationary noise are urban activities (i.e., mechanical equipment, parking areas, and pedestrians). The noise associated with these sources may represent a single-event noise occurrence, short-term or long-term/continuous noise.

Noise-Sensitive Receptors. Noise-sensitive land uses are generally considered to include those uses where noise exposure could result in health-related risks to individuals, as well as places where quiet is an essential element of their intended purpose. Residential dwellings are of primary concern because of the potential for increased and prolonged exposure of individuals to both interior and exterior noise

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Section 4.0
Environmental Analysis
108 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration
levels. Additional land uses such as parks, historic sites, cemeteries, and recreation areas are considered sensitive to increases in exterior noise levels. Schools, churches, hotels, libraries, and other places where low interior noise levels are essential are also considered noise-sensitive land uses.

Noise-sensitive uses south of the project site include the mobile home park at 2663 Rosemead Boulevard, a single-family residence at 2653 Rosemead Boulevard (south of the mobile home park), and a singlefamily residence at 2660 Troy Avenue. Additionally, noise-sensitive uses include a single-family residence and associated structures at 9336 Mabel Avenue, west of the project site.

Regulatory Setting
California Code of Regulations, Title 24. The State’s noise insulation standards are codified in the California Code of Regulations, Title 24: Part 1, Building Standards Administrative Code, and Part 2, California Building Code. These noise standards are applied to new construction in California for the purpose of interior noise compatibility from exterior noise sources. The regulations specify that acoustical studies must be prepared when noise-sensitive structures, such as residential buildings, schools, or hospitals, are located near major transportation noise sources, and where such noise sources create an exterior noise level of 65 dBA CNEL or higher. Acoustical studies that accompany building plans must demonstrate that the structure has been designed to limit interior noise in habitable rooms to acceptable noise levels. For new residential buildings, schools, and hospitals, the acceptable interior noise limit for new construction is 45 dBA CNEL.

City of South El Monte Code of Ordinances. The Noise Ordinance codified under Municipal Code 8.20 – Noise Regulations, contains noise standards that are correlated with land use zoning classifications, meant to maintain identified ambient noise levels and to limit, mitigate, or eliminate intrusive noise that exceeds the ambient noise levels within a specified zone.

The City has also set restrictions to control noise impacts from construction activities. Municipal Code Section 8.20.030 (D) states:

No person shall operate or cause or authorize the operation of any tools or equipment used in construction, drilling, repair, alteration or demolition work between the hours of ten PM and seven AM, or at any time on weekends or holidays, such that the sound therefrom creates a noise disturbance across the real property line of an adjacent or nearby property developed entirely or partially for residential use.

Although the Municipal Code limits the hours of construction, it does not provide specific noise level performance standards for construction. Municipal Code Section 8.20.020 identifies the maximum permissible sound levels for different land uses. The noise/land use compatibility guidelines for land uses in the City are presented in Table 4.13-1: Exterior Noise Limits.

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Section 4.0
Environmental Analysis
109 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration
Table 4.13-1: Exterior Noise Limits
By Zone
Receiving Land Zoning Category Time Period
Noise Level
Standard (dBA)
One- or Two-Family Residential Zone
10 PM – 7 AM 45
7 AM – 10 PM 55
Multiple Dwelling Residential Zone, Public Zone
10 PM – 7 AM 50
7 AM – 10 PM 60
Commercial Zone or Commercial-Manufacturing Zone
10 PM – 7 AM 55
7 AM – 10 PM 60
Manufacturing Zone Any time 70
By Use
Receiving Land Zoning Category Time Period
Noise Level
Standard (dBA)
Property Partially or Entirely developed for One- or TwoFamily Residential Uses 10 PM – 7 AM 45 Property Partially or Entirely developed for Multi-Family Residential Uses 10 PM – 7 AM 50
Source: South El Monte Municipal Code Section 8.20.020.

Threshold (a) Would the project result in the generation of a substantial temporary or permanent increase in ambient noise levels in the vicinity of the project in excess of standards established in the local general plan or noise ordinances, or applicable standards of other agencies?
Less Than Significant Impact.

Construction. Construction noise represents a short-term impact on ambient noise levels. Noise generated by equipment for demolition and construction equipment, including trucks, graders, bulldozers, concrete mixers and portable generators can reach high levels. Construction activities on the project site would expose existing noise-sensitive uses would be exposed to increased noise levels. In typical construction projects, such as the proposed project, the loudest noise generally occurs during grading activity because it involves the largest equipment. Maximum noise levels generated by construction equipment are identified in Table 4.13-2: Maximum Noise Levels Generated by Construction Equipment. It should be noted that the noise levels identified in the table are maximum sound levels (Lmax), which are the highest individual sound occurring at an individual time period.

Operating cycles for these types of construction equipment may involve one or two minutes of full power operation followed by three to four minutes at lower power settings. Other primary sources of acoustical disturbance would be due to random incidents, which would last less than one minute (such as dropping large pieces of equipment or the hydraulic movement of machinery lifts).

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Environmental Analysis
110 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration
Table 4.13-2: Maximum Noise Levels Generated by Construction Equipment Equipment
Typical Noise Level (dBA) at 50 Feet from Source
Acoustical Use Factor Lmax at 50 Feet (dBA) Lmax at 100 Feet (dBA) Concrete Saw 20 90 84
Crane 16 81 75
Concrete Mixer Truck 40 79 73
Backhoe 40 78 72
Dozer 40 82 76
Excavator 40 81 75
Forklift 40 78 72
Paver 50 77 71
Roller 20 80 74
Tractor 40 84 78
Water Truck 40 80 74
Grader 40 85 79
General Industrial Equipment 50 85 79
dBA: A-weighted decibels; Lmax: maximum noise level
Note: Acoustical Use Factor (percent): Estimates the fraction of time each piece of construction equipment is operating at full power (i.e., its loudest condition) during a construction operation.

Source: Federal Highway Administration, Roadway Construction Noise Model User’s Guide, January 2006.

Noise-sensitive receptors may be exposed to elevated noise levels during project construction. However, construction noise would be acoustically dispersed throughout the project site and not concentrated in one area near surrounding sensitive uses. The City’s Noise Ordinance does not establish quantitative construction noise standards. Instead, the Noise Ordinance has established allowable hours of construction. Construction activities cannot occur between 10:00 PM and 7:00 AM on weekdays, or at any time on weekends or holidays, such that the sound therefrom creates a noise disturbance across the real property line of an adjacent or nearby property developed entirely or partially for residential use. The project would be required to comply with SC N-1, which requires the construction contractor to comply with noise regulations prescribing the hours allowed for construction activity identified in Municipal Code Section 8.20.030(D). SC N-2 would further minimize impacts from construction noise as it requires construction equipment to be equipped with properly operating and maintained mufflers and other State required noise attenuation devices. Implementation of SC N-1 and SC N-2 would preclude significant construction-related noise impacts.

Operation. After project completion, typical noise associated with residential land uses include children playing, pet noise, amplified music, and delivery drop offs. Noise from residential stationary sources would be consistent with the surrounding uses and would primarily occur during the “daytime” activity hours of 7:00 AM to 10:00 PM The residences would be required to comply with the noise standards set forth in the Municipal Code Section 8.20.020, Exterior Noise Limits. Further, the outdoor amenities and open-air courtyard would be surrounded by the proposed building, which would attenuate noise from the on-site recreational areas to nearby off-site sensitive receptors. In addition, a perimeter wall proposed along the project site’s southern and western boundary would also attenuate operational noise, further reducing noise levels in the surrounding area. The commercial retail uses on the ground floor would be located

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Section 4.0
Environmental Analysis
111 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration
along the Rosemead Boulevard frontage. According to the Caltrans Traffic Census, Rosemead Boulevard currently has 77,000 average daily vehicles.
34 Existing mobile source noise along Rosemead Boulevard and Mabel Avenue would mask operational noise impacts on adjacent land uses.

Traffic associated with parking lots is typically not of sufficient volume to exceed community noise standards, which are based on a time-averaged scale such as the CNEL scale. However, the instantaneous maximum sound levels generated by a car door slamming, engine starting up, and car pass-bys may be an annoyance to adjacent noise-sensitive receptors. Impacts associated with parking would be considered minimal since the majority of parking spaces would be enclosed by walls within the ground level garage and above-ground parking deck. Parking lot noise would also be partially masked by background noise from traffic along Rosemead Boulevard and Mabel Avenue. Noise associated with parking lot activities is not anticipated to exceed the City’s noise standards. Impacts would be less than significant.

Trash collection would be conducted by a scout service, which would bring trash bins to Mabel Avenue, and ultimately collected by Athens Services. Trash collection would occur on a weekly basis. Existing mobile noise from Rosemead Boulevard and Mabel Avenue would mask noise associated with trash collection. Furthermore, trash collection does not span long durations and are short noise events. Impacts are considered less than significant.

Implementation of the project would generate increased traffic volumes along nearby roadway segments.

In general, a traffic noise increase of less than 3 dBA is barely perceptible to people, while a 5-dBA increase is readily noticeable.35 Generally, traffic volumes on project area roadways would have to approximately double for the resulting traffic noise levels to increase by 3 dBA.36 Therefore, permanent increases in ambient noise levels of less than 3 dBA would be less than significant. As discussed above, Rosemead Boulevard currently has 77,000 average daily vehicles. The proposed project would generate approximately 1,034 daily vehicle trips, which would not double the existing traffic volumes and would not result in a perceivable noise increase. Overall, operational noise impacts would be less than significant due to project design features, existing environmental factors, and with compliance with the Municipal Code Section 8.20.020.

Threshold (b) Would the project result in the generation of excessive groundborne vibration or groundborne noise levels?
Less Than Significant Impact. Project construction can generate varying degrees of groundborne vibration, depending on the construction procedure and the construction equipment used. Operation of construction equipment generates vibrations that spread through the ground and diminish in amplitude with distance from the source. The effect on buildings located near the construction site often varies depending on soil type, ground strata, and construction characteristics of the receiver building(s). The results from vibration can range from no perceptible effects at the lowest vibration levels, to low rumbling sounds and perceptible vibration at moderate levels, to slight damage at the highest levels. Ground-borne vibrations from construction activities rarely reach levels that damage structures. 34 California Department of Transportation, Traffic Census Program, https://dot.ca.gov/programs/traffic-operations/census.

Accessed March 23, 2021. 35 Federal Highway Administration, Highway Traffic Noise Analysis and Abatement Policy and Guidance, Noise Fundamentals, https://www.fhwa.dot.gov/environMent/noise/regulations_and_guidance/polguide/polguide02.cfm. Accessed March 11, 2021. 36 California Department of Transportation, Technical Noise Supplement to the Traffic Noise Analysis Protocol, 2013.

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Environmental Analysis
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Initial Study and Mitigated Negative Declaration
The Federal Transit Administration (FTA) has published standard vibration velocities for construction equipment operations. In general, the FTA architectural damage criterion for continuous vibrations (i.e.,

0.20 inch/second) appears to be conservative. The types of construction vibration impact include human annoyance and building damage. Human annoyance occurs when construction vibration rises significantly above the threshold of human perception for extended periods of time. Building damage can be cosmetic or structural. Typical vibration levels produced by construction equipment is identified in Table 4.13-3:

Typical Vibration Levels for Construction Equipment.

Table 4.13-3: Typical Vibration Levels for Construction Equipment Equipment
Approximate Peak
Particle Velocity at 25
Feet (inches/second)
Approximate Peak
Particle Velocity at 50
Feet (inches/second)
Large bulldozer 0.089 0.0315
Loaded trucks 0.076 0.0269
Small bulldozer 0.003 0.0011
Jackhammer 0.035 0.0124
Ground-borne vibration decreases rapidly with distance. The project would not require pile driving. As indicated in the table, based on the FTA data, vibration velocities from typical heavy construction equipment operations that would be used during project construction range from 0.003 to 0.089 inchper-second peak particle velocity (PPV) (which is noticeably below the FTA’s 0.20 PPV threshold) at 25 feet from the source of activity. The nearest structure and sensitive receptors are adjacent to the west and south of the potential active construction zone and it is acknowledged that construction activities would occur throughout the project site and would not be concentrated at the point closest to the nearest structure. Therefore, vibration effects would be less than significant and no mitigation is required.

Threshold (c) For a project located within the vicinity of a private airstrip or an airport land use plan or, where such a plan has not been adopted, within two miles of a public airport or public use airport, would the project expose people residing or working in the project area to excessive noise levels?
No Impact. The closest airport to the project site is El Monte Airport, located approximately 2.4 miles northeast of the project site. Implementation of the proposed project would not result in exposure of people residing or working in the project area to excessive or high noise impact levels. Therefore, no impacts would occur and no mitigation is required.

Cumulative Impacts
As discussed above, all construction and operational noise impacts can be mitigated to a less than significant level. Construction noise impacts are by nature localized. The distance of separation among the project site and other cumulative project sites would be such that the temporary noise and vibration effects of the proposed project would not compound or increase similar noise or vibration effects from other cumulative projects. As discussed above, operational noise caused by the proposed project would be less than significant. Due to site distance and these intervening land uses, cumulative stationary noise impacts would not occur. No known past, present, or reasonably foreseeable projects would compound or increase the operational noise levels generated by the project. Therefore, cumulative impacts relative

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Environmental Analysis
113 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration
to temporary and permanent noise generation associated with the proposed project would be less than significant.

Mitigation Program
Standard Conditions and Requirements
SC N-1 All construction activities should be limited to the hours between the hours of 7:00 AM and 10:00 PM on weekdays, or any time on weekends or holidays.

SC N-2 The Applicant shall ensure through contract specifications that construction best management practices (BMPs) be implemented by contractors to reduce construction noise levels. Contract specifications shall be included in construction documents, which shall be reviewed by the City prior to issuance of a grading or building permit (whichever is issued first). The construction BMPs shall include the following:
 Ensure that construction equipment is properly muffled according to industry standards and be in good working condition.
 Place noise-generating construction equipment and locate construction staging areas away from sensitive uses, where feasible.
 Use electric air compressors and similar power tools rather than diesel equipment, where feasible.
 Turn off construction-related equipment, including heavy-duty equipment, motor vehicles, and portable equipment when not in use for more than 5 minutes.  Clearly post construction hours, allowable workdays, and the phone number of the job superintendent at all construction entrances to allow for surrounding owners and residents to contact the job superintendent. If the City or the job superintendent receives a complaint, the superintendent shall investigate, take appropriate corrective action, and report the action taken to the reporting party.

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Initial Study and Mitigated Negative Declaration

4.14 Population and Housing
Threshold (a) Would the project induce substantial unplanned population growth in an area, either directly (for example, by proposing new homes and businesses) or indirectly (for example, through extension of roads or other infrastructure)? Less Than Significant Impact. The California Department of Finance (CDOF) reports the City’s estimated population was 21,296 with an estimated 4.37 person per household as of January 1, 2021. 37 The
proposed project would allow for the construction of 73 apartment units within a mixed-use building.

Assuming 4.37 persons per household, the project would have 319 residents, which represents less than

1.5 percent of the existing population of the City. The City’s Regional Housing Needs Assessment (RHNA) allocation for the 6th Cycle 2021-2029 planning period identifies the City’s future housing need is 577 units.

Table 4.14-1: RHNA Requirements by Income Level lists a breakdown of the City’s RHNA targets by income level. The project includes six affordable housing units, specifically four low-income and two very low-income housing units. According to the City’s 6th Cycle Housing Element, which is set to be adopted in October 2021, very low-income households earn between $23,963 and $38,650 and low-income households earn between $38,650 and $61,840.38 The project would contribute to the future housing need for the 2021‐2029 planning period.

Table 4.14-1: RHNA Requirement by Income Level
Income Level Required Units
Very-Low Income 131
Low Income 64
Moderate Income 70
Above Moderate Income 312
Source: City of South El Monte 6th Cycle Housing Element Update (2021-2029) SCAG has developed growth forecasts for individual cities and counties, which is included in its Connect SoCal: 2020-2045 Regional Transportation Plan/Sustainable Communities Strategy. The City of South El Monte’s population is expected to increase to 22,600 residents and 5,300 households by 2045. 39 An
increase of 73 dwelling units with a potential population increase of 319 residents would be consistent with the SCAG growth forecasts for the City. Additionally, the project does not include the extension of roads or other infrastructure to unserved areas, which could induce indirect growth. Therefore, no significant impact would occur and no mitigation is required. 37 State of California Department of Finance. January 2021. E-5 Population and Housing Estimates for Cities, Counties, and the State, 2011-2021 with 2010 Census Benchmark. Available at http://dof.ca.gov/Forecasting/Demographics/Estimates/E-5/.

Accessed September 13, 2021. 38 Calculations based on an Area Median Income (AMI) of $77,300. Low-income: 51-80% of the AMI, Very Low-Income: 31-50% of the AMI. 39 SCAG. Adopted Final Connect SoCal 2020–2045 Regional Transportation Plan/Sustainable Communities Strategy. https://scag.ca.gov/read-plan-adopted-final-plan. Accessed December 23, 2020.

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Threshold (b) Would the project displace substantial numbers of existing people or housing, necessitating the construction of replacement housing elsewhere? No Impact. The project site does not include any existing housing and no housing would be removed to accommodate the proposed project. Therefore, no impact would occur and no mitigation is required.

Cumulative Impacts
The proposed project is consistent with the City’s growth projections. Additional development in the City would be subject to review for consistency with the adopted General Plan, in accordance with the requirements of CEQA. Therefore, no significant cumulative impacts associated with population and housing would occur.

Mitigation Program
Standard Conditions and Mitigation Measures
No standard conditions or mitigation measures are required.

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4.15 Public Services
Threshold (a.i) Would the project result in substantial adverse physical impacts associated with the provision of new or physically altered governmental facilities, need for new or physically altered governmental facilities, the construction of which could cause significant environmental impacts, in order to maintain acceptable service ratios, response times or other performance objectives for fire protection? Less Than Significant Impact. The City contracts with Los Angeles County Fire Department for fire services.

The nearest fire station is Station 90, located at 10115 Rush Street, approximately one mile southeast of the project site. The population growth that the analysis forecasts for the project would incrementally increase the demand for fire protection and emergency medical services in the area. However, the forecast population growth and increased demand for services would not exceed population projections and anticipated public service needs. Additionally, the incremental increase would not require the construction of new or alteration of existing fire protection facilities to maintain an adequate level of service to the project area. The proposed project would be subject to Municipal Code Chapter 15.14, which adopts the County of Los Angeles Fire Code. Therefore, no physical impacts associated with fire protection services and facilities would occur. Additionally, the project would be subject to the County Fire Department review process and be subject to pay any applicable fees. Compliance with Fire Code and building standards would minimize the project’s operational impacts to fire protection services to the greatest extent practicable. Therefore, impacts are less than significant and no mitigation is required.

Threshold (a.ii) Would the project result in substantial adverse physical impacts associated with the provision of new or physically altered governmental facilities, need for new or physically altered governmental facilities, the construction of which could cause significant environmental impacts, in order to maintain acceptable service ratios, response times or other performance objectives for police protection? Less Than Significant Impact. The City contracts with the Los Angeles County Sheriff’s Department for law enforcement services. South El Monte is served by designated deputies of the Sheriff’s Temple Station, located at 8838 Las Tunas Drive in City of Temple City. The project site is approximately 2.9 miles south of the Temple Station. The Sheriff’s Department provides emergency response to all life-threatening incidents and prevents crime by community policing.

The population growth that the analysis forecasted for the project would incrementally increase the demand for police protection services to the project area. However, the forecast population growth and increased demand for services would not exceed population projections and anticipated public service needs. The proposed project’s development standards would adhere to all California Building Code regulations. The City has incorporated the County of Los Angeles Building Code standards under Municipal Code Section 15.02.010. Emergency access requirements would minimize site safety hazards and potential construction-related impacts to police services. Compliance with California Building Code requirements related to site security and building, and site safety design recommendations would ensure adequate police protection services can be provided to the project site. As a result, the proposed project would not adversely impact service ratios or response times or require new or altered facilities. Therefore, the project’s impact on police protection services would be less than significant and no mitigation is required.

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Threshold (a.iii) Would the project result in substantial adverse physical impacts associated with the provision of new or physically altered governmental facilities, need for new or physically altered governmental facilities, the construction of which could cause significant environmental impacts, in order to maintain acceptable service ratios, response times or other performance objectives schools? Less Than Significant Impact. The project site is served by the Valle Lindo School District and the El Monte Union High School District. The Valle Lindo School District has one elementary school and one middle school that would serve the proposed project. New Temple Elementary School currently has an enrollment of 502 students and Dean L. Shively Middle School has an enrollment of 501 students.40 According to Superintendent Lynn Bulgin, both schools have capacity for more students.41 The El Monte Union High School District has nine facilities, including five high schools, one continuation high school, one community day school, and one adult school, and one adult transition center. South El Monte High School would serve high school students from the proposed project. South El Monte High School currently has 1,261 students enrolled.42 According to Superintendent Edward Zuniga, South El Monte High School has capacity for 2,295 students. Therefore, the high school has capacity to serve the proposed project.43 Further, project construction would not disrupt school services in the project vicinity and would not generate additional students that would significantly impact school services or facilities.

School funding comes predominantly from federal, State, and local contributions, such as business and personal income taxes, sales tax, property tax, etc. Although the project would result in an incremental increased demand for school services, the project would be required to comply with SB 50 requirements, which allow school districts to collect impact fees from developers of new projects. The El Monte Union High School District collects developer fees on behalf of both school districts. The current development fee for residential uses is $3.36/sf and for retail uses is $0.347/sf.44 As stated in Government Code Section 65995(h), “The payment or satisfaction of a fee, charge, or other requirement levied or imposed …are hereby deemed to be full and complete mitigation of the impacts of any legislative or adjudicative act, or both, involving, but not limited to, the planning, use, or development of real property, or any change in governmental organization or reorganization …on the provision of adequate school facilities.” Payment of these fees would offset impacts from increased demand for school services associated with development of the proposed project by providing an adequate financial base to construct and equip new and existing schools. Overall, both school districts would be able to provide adequate school facilities for the projected student residents of the project, and payment of impact fees would ensure that impacts are offset and remain less than significant. 40 California Department of Education, Data Quest, available at:
https://dq.cde.ca.gov/Dataquest/dqcensus/EnrGrdLevels.aspx?cds=19645191995661&agglevel=school&year=2020-21, Accessed June 16, 2021. 41 Personal Communication with Lynn Bulgin, VLSD – Superintendent. June 16, 2021. 42 Ibid. 43 Personal Email connection with Edward Zuniga, EMHSUD Superintendent. June 22, 2021. 44 Phone conservation with Esmeralda Vargas, EMUHSD Business Services - Administrative Secretary. June 2, 2021.

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Threshold (a.iv) Would the project result in substantial adverse physical impacts associated with the provision of new or physically altered governmental facilities, need for new or physically altered governmental facilities, the construction of which could cause significant environmental impacts, in order to maintain acceptable service ratios, response times or other performance objectives for parks? Less Than Significant Impact. Please refer to Section 4.16, Recreation.

Threshold (a.v) Would the project result in substantial adverse physical impacts associated with the provision of new or physically altered governmental facilities, need for new or physically altered governmental facilities, the construction of which could cause significant environmental impacts, in order to maintain acceptable service ratios, response times or other performance objectives for other public facilities? Less Than Significant Impact. The Los Angeles County Library provides library services to over 3.4 million residents living in unincorporated areas and to residents of 49 of the 88 incorporated cities of Los Angeles County, inclusive of the City of South El Monte. Table 4.15-1: Nearby County Library Facilities identifies the two libraries near the project site. The Rosemead Library has 29,860 sf of space45 and the South El Monte Library has 6,416 sf of space for the community and patrons.46 Table 4.15-1: Nearby County Library Facilities
Library Address Driving Distance to Project Site
Rosemead Library 8800 Valley Boulevard, Rosemead 1.0 mile South El Monte Library 1430 North Central Avenue, South El Monte 1.6 miles The proposed project is expected to have 319 new residents, thereby incrementally increasing the demand for library services. The proposed project would increase the City’s population by 1.5 percent, which is within the anticipated growth projections from SCAG. Therefore, given the nominal increase in population growth, the demand of library services is not anticipated to increase substantially, necessitating the need for additional library facilities. The proposed mixed-use development would have a nominal impact on library services.

The threshold for determining impacts pursuant to CEQA is based upon whether a project would result in substantial adverse physical impacts associated with the provision of new or physically altered governmental facilities, need for new or physically altered governmental facilities, the construction of which could cause significant environmental impacts, to maintain acceptable service ratios or other performance objectives. The impacts to the overall per capita availability of books, media, computers, and library public service space would not create significant physical or environmental impacts. Therefore, project-related impacts to library facilities would be less than significant and no mitigation is required.

Cumulative Impacts
The provision of public services and facilities takes into consideration a larger service area than is associated with a project site. Therefore, the study area is the service area for the respective agencies and 45 Los Angeles County Library, About Rosemead Library, Available at: https://lacountylibrary.org/rosemead-library/. Accessed May 25, 2021. 46 Los Angeles County Library, About South El Monte Library, Available at: https://lacountylibrary.org/south-el-montelibrary/. Accessed May 25, 2021.

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districts. Through coordination with the public services and facilities providers, the cumulative needs of the area are considered. The proposed project does not cause the need to construct any new or expand any existing facilities. Therefore, the project would not result in incremental effects to public services or facilities that could be compounded or increased when considered together with similar effects from other past, present, and reasonably foreseeable probable future projects. The project would not result in cumulatively considerable impacts to public services or facilities.

Mitigation Program
Standard Conditions and Mitigation Measures
No standard conditions or mitigation measures are required.

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4.16 Recreation
Quimby Act
The Quimby Act of 1975, (California Government Code §66477), commonly called the “Quimby Act,” allows a city or county to pass an ordinance that requires, as a condition of approval of a subdivision, either the dedication of land, the payment of a fee in lieu of dedication, or a combination of both for park and recreational purposes. It allows a city or county to require a maximum parkland dedication standard of 3 acres of parkland per 1,000 residents for new subdivision development unless the jurisdiction can demonstrate that the amount of existing neighborhood and community parkland exceeds that limit. In accordance with Section 66477, a jurisdiction may establish a parkland dedication standard based on its existing parkland ratio, provided required dedications do not exceed 5 acres per 1,000 persons.

Would the project:

Threshold (a) Would the project increase the use of existing neighborhood and regional parks or other recreational facilities such that substantial physical deterioration of the facility would occur or be accelerated? and
Threshold (b) Does the project include recreational facilities or require the construction or expansion of recreational facilities which might have an adverse physical effect on the environment?
Less Than Significant Impact. The City operates three parks, three community centers, and an aquatic center. The nearest City park facility is Mary Van Dyke Park located at 1819 Central Avenue, approximately

1.3 miles east of the project site. The proposed project includes 73 multi-family dwelling units with an expected residential population of 319 residents. According to General Plan Resources Element Goal 1, the City’s park standard is 2 acres for every 1,000 residents. The proposed project would provide 9,625 sf of open space and 11,213 sf of private open space in the form of private balconies and decks. The project includes an open-air courtyard, recreation room, and gym facilities on the second floor. Future residents would likely use the on-site amenities for some of their recreational needs. Further, the proposed project would not require construction or expansion of existing recreational facilities as on-site amenities including a recreation room, gym, and open-air courtyard would be provided to residents.

The proposed project would be subject to South El Monte Municipal Code 16.36.015 – Park land dedications and fees. Construction of residential dwelling units or subdivisions for residential purposes are subject to dedicating a portion of such land, pay a fee, or both, for the purpose of developing new or rehabilitating existing park or recreational facilities to serve future residents of the subdivision or development. Payment of these fees would ensure that the City has the required funds to upkeep facilities and prevent substantial deterioration of recreational facilities from occurring. Because the proposed project does not include parkland dedication, the project would be subject to in-lieu fees. In-lieu fees are calculated based on the fair market value of the amount of parkland which would otherwise be required to be dedicated. Per Municipal Code 16.36.015, the proposed project’s parkland dedication would be

0.161 acre. Payment of in-lieu fees would satisfy the City’s requirement for parkland dedication and would provide funds to upkeep facilities to prevent substantial deterioration. Therefore, the proposed project would not result in substantial physical deterioration of existing parks and recreational facilities and a less than significant impact would occur and no new recreational facilities would be required.

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Cumulative Impacts
The proposed project would not result in a significant increased use of recreational facilities or require construction or expansion of existing recreational facilities. Therefore, no cumulative impacts on recreational facilities would result from project implementation.

Mitigation Program
Standard Conditions and Mitigation Measures
No standard conditions or mitigation measures are required.

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4.17 Transportation
A transportation analysis was prepared by Kimley-Horn and Associates, Inc. (Kimley-Horn, 2021) for the proposed project. The modeling outputs and study are included in Appendix G of this Initial Study and the results are summarized herein.

Site Access
Regional access is provided by Interstate 10 (I-10), which is located approximately 0.75 mile north of the project site, and SR-60, which is located approximately 1.4 miles south of the project site. Local access into the project site is currently restricted by locked gates, although there are driveways on Mabel Avenue and Rosemead Boulevard for private access.

Rosemead Boulevard (SR-164) is a six-lane, north-south arterial highway within the project area. The roadway begins at Sierra Madre Villa Avenue and continues south until it becomes SR-19 south of the City of Pico Rivera. Rosemead Boulevard provides access to I-210, I-10, and SR-60. Near the project site, the roadway provides local cross-town circulation between residential and retail land uses. The speed limit within the study area is 45 miles per hour (mph).

Mabel Avenue is a two-lane, east-west local roadway within the project area. To the east, it connects to Rosemead Boulevard and turns into Loma Avenue to the west as it becomes a north-south roadway.

Mabel Avenue intersects with Lee Avenue and provides driveway access to retail land uses. The posted speed limit is 25 mph.

Lee Avenue is a two-lane, north-south local roadway. It connects to Garvey Avenue to the north and Rush Street to the south. Lee Avenue provides access of retail and industrial land uses. The speed limit within the study area is 25 mph.

Garvey Avenue is a four-lane, east-west arterial highway. It connects to Durfee Avenue to the east and becomes West Ramona Boulevard to the west. The roadway serves residential and retail land uses and provides access to I-10, I-605, and I-710. The speed limit within the study area is 35 mph.

Transit Service
Public transit service is provided by Foothill Transit, Metro, and Norwalk Transit.

Foothill Transit provides fixed-route bus public transit service to the San Gabriel Valley in the greater Los Angeles area. Foothill Transit Line 269 is a north-south fixed-route bus service that operates from the El Monte Station to the Montebello Town Center. On weekdays, Line 269 operates between 5:55 AM and 10:19 PM on 30-60-minute headways. On weekends, Line 269 operates between 6:30 AM and 8:30 PM on 60-minute headways. The nearest bus stop is at the intersection of Garvey Avenue and Santa Anita Avenue, which is approximately 1.3 miles east of from the project site.

Los Angeles County Metropolitan Transportation Authority (Metro) provides bus rapid transit service throughout Los Angeles County.
 Line 287 is an north-south fixed-route bus service that operates from The Shops at Montebello to Arcadia Station. On weekdays, Line 287 runs between 5:34 AM and 10:36 PM on approximately 40-minute headways. On Saturdays, Sundays, and Holidays, Line 287 runs from only El Monte Station to Arcadia Station between 6:00 AM and 10:22 PM. The nearest bus stop is at the

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intersection of Rosemead Boulevard at Garvey Avenue, which is approximately 500 feet north of the project site.
 Line 266 is a north-south fixed-route bus service that operates from Sierra Madre Villa in Pasadena to Lakewood Center Mall in Lakewood. On weekdays, Line 266 runs between 5:09 AM and 11:34 PM on approximately 20-minute headways. On Saturdays, Sundays and Holidays the route runs between 5:33 AM and 11:49 PM on approximately 40-minute headways. The nearest bus stop is at the intersection of Rosemead Boulevard and Garvey Avenue, which is approximately 430 feet north of the project site.
 Line 70 is an east-west fixed-route bus service that operates from the El Monte Station to 17th Street and Hill Street in Los Angeles. Monday through Friday, Line 70 operates between 4:50 AM and 5:09 PM 24-hours on approximately 10-minute headways. The nearest bus stop is at the intersection of Rosemead Boulevard and Garvey Avenue, which is approximately 430 feet north of the project site.

Norwalk Transit provides rapid bus and paratransit services within the City of Norwalk, along with several adjacent cities, including the City of South El Monte. Norwalk Transit Route 7 is a north-south fixed-route bus service that operates from the El Monte Station to the Norwalk Green Line Station. On weekdays, Route 7 operates between 4:07 AM and 9:11 PM on 15-60-minute headways. On weekends, the route runs from 5:49 AM to 7:57 PM on approximately 60-minute headways. The nearest bus stop is at the intersection of Garvey Avenue and Santa Anita Avenue, which is approximately 1.3 miles east from the project site.

Bikeways
There are currently no bikeways adjacent to the project site. The nearest bikeway is the Rio Hondo bikeway, approximately 0.2 mile west of the project site. Future proposed bikeways include a Class II bikeway along Rosemead Boulevard and a Class III bikeway along Loma Avenue and Mabel Avenue.47 Threshold (a) Would the project conflict with a program, plan, ordinance, or policy addressing the circulation system, including transit, roadway, bicycle and pedestrian facilities? Less Than Significant Impact.

Construction Traffic. Automobile and truck traffic volumes associated with project-related construction activities would vary throughout the construction phases, as different activities occur. However, projectrelated construction traffic would be temporary and cease upon project completion.

Project Trip Generation. Daily and peak hour trips were estimated for the proposed project based on the Institute of Transportation Engineers (ITE) Trip Generation Manual (10th Edition) trip rates for the following uses:
 Multifamily Housing (Mid-Rise) (ITE Code 221)
 Shopping Center (ITE Code 820)
47 Alta Planning + Design. 2014. San Gabriel Valley Regional Bicycle Master Plan, available at:
https://www.baldwinpark.com/index.php/docssidemenu/public-notices/175-sgv-bike-master-plan/file, accessed June 18, 2021.

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Table 4.17-1: Project Trip Generation provides the trip generation rates and the estimated project trip generation for the proposed project. The project is estimated to generate 899 average daily trips, with 42 trips in the morning peak hour and 72 trips in the evening peak hour. For purposes of determining the worst-case impacts of traffic on the surrounding street network, the trips generated by a proposed project are estimated for the morning peak hour (between the hours of 7:00 AM and 9:00 AM), and for the evening peak hour (between 4:00 PM and 6:00 PM) on a typical weekday. As noted, trips generated by the mixed-use development were based on the average rates for ITE Land Use 221 (Multifamily Housing Mid-Rise) for the residential component and ITE Land Use 820 (Shopping Center) for the retail space.

Internal capture for Land Use Code 820 (Shopping Center) from the National Cooperative Highway Research Program (NCHRP) 684 Methodology was used, which assumes no internal capture during the morning peak hour and an internal capture of 25 percent during the evening peak hour. It should be noted that NCHRP 684 does not provide for daily internal capture; therefore, this analysis assumes an average of the peak hour percentages.

Table 4.17-1: Project Trip Generation
Land Use Quantity Unit
Trip Generation Estimates
Daily
AM Peak Hour PM Peak Hour
In Out Total In Out Total
Multifamily Housing
(Mid-Rise) 73 DU 398 7 19 26 20 12 32
Shopping Center 16.8 KSF 636 10 6 16 31 33 64
Total Project Trips 1,034 17 25 42 51 45 96
Internal Capture (Daily 13%, AM 0%,
PM 25%)1 -135 0 0 0 -12 -12 -24
Total External Project Trips 899 17 25 42 39 33 72
Notes: Institute of Transportation Engineers (ITE) Trip Generation Manual, 10th Edition 1 Calculated using NCHRP 684 Methodology. NCHRP 684 does not provide daily internal capture, therefore an average of the AM and PM peak hour percentages were used.

Source: Kimley-Horn, 2021.

According to the Caltrans Traffic Census, Rosemead Boulevard currently has 77,000 average daily vehicles.

The net increase of 899 daily trips generated on Rosemead Boulevard associated with the proposed project represents a nominal increase in daily traffic and can be accommodated by the existing roadway infrastructure. The project would not conflict with any programs or policies related to roadway facilities given the negligible increase in daily peak traffic trips to and from the project site onto Rosemead Boulevard.

Public Transit. As discussed above, public transit service is provided by Foothill Transit, Metro, and Norwalk Transit. Specifically, Metro is provides the nearest public transit bus service to the project site, with bus routes along Rosemead Boulevard and Garvey Avenue, approximately 430 feet north of the project site. The proximity of these bus stops would provide more transit opportunities and access to future residents for the proposed project. Pedestrian facilities (i.e., sidewalks) on Mabel Avenue and Rosemead Boulevard would be maintained as part of the project. Further, the project would include bicycle parking on the ground level parking garage. Future bikeways are proposed on Rosemead Boulevard and Mabel Avenue.

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SCAG’s Connect SoCal: 2020-2045 RTP/SCS addresses regional challenges in several ways. A key, formative step is to develop a Regional Growth Forecast in collaboration with local jurisdictions, which helps SCAG identify opportunities and barriers to development. The plan forecasts the number of people, households and jobs (at the jurisdictional level) expected throughout SCAG’s 191 cities and in unincorporated areas by 2045. This information is typically a component of the City’s General Plan, and if available, the City’s traffic analysis model. Growth assumed in the City’s General Plan and its corresponding traffic assumptions would be the information supplied to SCAG. Although the proposed project requires a General Plan Amendment and a rezone, it is consistent with the growth assumptions for the City.

Additionally, SCAG’s Connect SoCal identifies the need to create sustainable, mixed-use communities conducive to public transit, walking, and biking by promoting development along major existing transit and transportation corridors. As noted in this Initial Study, the project would be consistent with the RTP/SCS and the applicable goals and policies of the General Plan. Therefore, project construction and operations would not conflict with an applicable plan, ordinance, or policy concerning the circulation system and no mitigation is required.

Threshold (b) Conflict or be inconsistent with CEQA Guidelines section 15064.3, subdivision (b)? Less Than Significant Impact. SB 743, approved in 2013, required the Governor’s Office of Planning and Research (OPR) to establish recommendations for identifying and mitigating transportation impacts within the CEQA framework. Generally, SB 743 moves away from using delay-based level of service (LOS) as the primary metric for identifying a project’s significant impact to instead using vehicle miles traveled (VMT). On January 20, 2016, OPR released revisions to its proposed CEQA Guidelines for the implementation of SB 743, and final review and rulemaking for the new guidelines were completed in December 2018. OPR allowed lead agencies an opt-in period to adopt VMT guidelines before the mandatory adoption date of July 1, 2020. These revisions to the CEQA Guidelines criteria for determining the significance of transportation impacts are primarily focused on projects within transit priority areas, and shifts the focus from driver delay to reduction of GHG emissions, creation of multimodal networks, and promotion of a mix of land uses. VMT, is a measure of the total number of miles driven to or from a development and is sometimes expressed as an average per trip or per person.

State CEQA Guidelines Section 15064.3(b)(1) provides that “VMT traveled exceeding an applicable threshold of significance may indicate a significant impact. Generally, projects within 0.5 mile of either an existing major transit stop or a stop along an existing high-quality transit corridor should be presumed to cause a less than significant transportation impact. Projects that decrease vehicle miles traveled in the project area compared to existing conditions should be presumed to have a less than significant transportation impact”.

In anticipation of the change to VMT, the San Gabriel Valley Council of Governments (SGVCOG) prepared the SGVCOG SB 743 Implementation Study to assist its member agencies in answering important implementation questions about the methodology, thresholds, and mitigation approaches for VMT. The City of South El Monte used the information produced through the Implementation Study to adopt a methodology and significance thresholds for use in CEQA compliance. Consistent with SGVCOG SB 743 Implementation Study, the City recommends using the SCAG Travel Demand Model as its methodology to measure VMT.

The City’s draft SB 743 Implementation Guidelines (City’s Implementation Guidelines) provides details on appropriate screening thresholds that can be used to identify when a proposed land use project is

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anticipated to result in a less than significant impact without conducting a detailed analysis. Screening thresholds are broken into the following three steps. A land use project needs only meet one of the above screening thresholds to be presumed to result in no significant impact under CEQA pursuant to SB 743.

1. Transit Priority Areas (TPA) Screening: Projects located within one-half mile from an existing major transit stop or within one-half mile from an existing stop along a high-quality transit corridor can be screened out. Transit service in the project area is provided by Foothill Transit, Metro, and Norwalk Transit. The nearest transit provider to the project site is Metro, which provides four bus routes: Metro Line 266, Metro Line 70, Metro Line 770, and Metro Line 176.

These bus routes operate with headways varying from 15 to 60 minutes during the peak commute periods. The Metro bus stops for these routes are located within one-half mile (430 feet north) of the project site.

The proposed project meets the TPA screening criteria.

2. Low VMT-Generation Area Screening: Projects generating VMT below 15 percent of the regional average can be screened out. South El Monte has selected SGVCOG’s regional average VMT screening. For a mixed-used project, all components of the project should be analyzed against the low VMT maps for either the dominant project land use (if applicable) or for each individual land use (if there is no dominant project land use). Reductions in VMT may be applied to account for internal trips that would occur within the project site. Based on the SGVCOG VMT tool, the proposed project’s residential component is below 15 percent of the regional VMT per Capita.

However, the retail component is not below 15 percent of the regional VMT per service population.

Therefore, the project is not screened out based on the low VMT-Generation Area screening.

3. Project Type Screening: Some project types have been identified in the City’s Implementation Guidelines as having the presumption of a less than significant impact. The following uses can be presumed to have a less than significant impact absent substantial evidence to the contrary as their uses are local serving in nature:
a. Local-serving retail uses less than 50,000 sf
b. Other local-serving uses as approved by the City staff c. Projects generating less than 110 daily vehicle trips The proposed project’s retail component can be screened out based on the Project Type screening criteria. However, the project is a mixed-use development and therefore project impacts need to be evaluated as a whole, and not by project components.

Although the proposed project can be screened out from VMT analysis per the TPA screening criteria, a quantitative VMT analysis was prepared at the request of the City. The City adopted the following VMT significance criteria:
 The baseline project generated Home-Based VMT per Capita exceeds the 15 percent below the SGVCOG baseline Home-Based VMT per Capita for residential projects.

Home-Based trip are the primary automobile trips associated with residential uses (i.e., the proposed project). The residential use is expected to generate several trips related to work, shopping, and schools in the region. The efficiency of VMT associated with home-based trips has

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been assessed based on the SCAG Travel Demand Model consistent with the City’s Implementation Guidelines.
 Project shows a net increase in Total VMT in the region for retail projects Total trips include all vehicle trips and trip purposes including truck trips. The retail component of the project is evaluated using total VMT per service population. The efficiency of VMT associated with total trips has been assessed based on the SCAG Travel Demand Model consistent with the City’s Implementation Guidelines.

The City’s Implementation Guidelines recommend the use of Total VMT per service population as an efficiency metric to evaluate retail projects. However, for mixed-use projects, OPR recommends analyzing each land use separately and comparing each result to the appropriate threshold. Combining land uses in a VMT analysis is not recommended by OPR because different land uses generate different amounts of VMT; the outcome of such an analysis could depend more on the mix of uses than on their travel efficiency. Therefore, for the purpose of this analysis, the two thresholds ─ Home-Based VMT per Capita and Total VMT─ were used to evaluate the project’s potential VMT impacts.

If a project is consistent with SCAG’s RTP/SCS, then the cumulative impacts shall be considered less than significant subject to consideration of other substantial evidence. Although the project would require a General Plan Amendment and a Zone Change, the population projections are consistent with SCAG RTP/SCS projections. Therefore, the project’s cumulative impacts are considered less than significant.

Project VMT was derived using the most current version of the SCAG Travel Demand Model. The SCAG model is a trip-based model and considers interaction between different land uses based on socioeconomic data such as population, households and employment. Adjustments in socioeconomic data (households, population and employment) were made to the appropriate traffic analysis zone (TAZ) within the SCAG model to reflect the project’s proposed land uses.

The Home-Based VMT per Capita is the Home-Based production VMT divided by population derived from the SCAG Travel Demand Model. Home-Based VMT per Capita is used to measure efficiency of VMT generated by residential uses. Table 4.17-2: Project VMT Impact Evaluation compares the project area Home-Based VMT per Capita for the existing and existing plus project conditions. As shown in the table for the residential component of the project, the project area Home-Based VMT per Capita would remain 15 percent below SGVCOG average VMT per Capita. Net VMT in the SGVCOG region is reduced with the project compared to existing conditions. The numerical threshold value (16.27) shown in the table is based on the City’s Implementation Guidelines methodology. The threshold of significance is based on the percentage of the with and without project VMT.

Table 4.17-2: Project VMT Impact Evaluation
Land Use
Existing SGVCOG
Average VMT VMT Threshold
(Existing + Project)
Project Area VMT
Potentially
Significant?
Residential: Home-Based
VMT per Capita 16.27 13.83 (85%) 12.99 No
Retail: SGVCOG Total VMT 74,437,225 Less than Existing 74,424,935 No Source: Kimley-Horn, 2021.

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For retail land uses, OPR recommends “net increase” as the threshold for significance. This means that if a proposed retail use results in a net increase in VMT in the region, a significant impact would occur. Net change in regional VMT is also used to measure the project’s VMT impact. Total SGVCOG regional VMT was derived for the “with” and “without project” conditions, and net change in the VMT was using the SCAG model. The retail component of the project was also analyzed qualitatively.

Local serving retail primarily serves pre-existing needs (i.e., they do not generate new trips because they meet existing demand). Therefore, local-serving retail uses can be presumed to reduce trip lengths when a new store is proposed as people drive shorter distances to commercial uses. Mixed-use projects place commercial retail uses close to residential uses. As shown Table 4.17-2, the net regional VMT is reduced with the project.

In summary, the proposed project would be consistent with CEQA Guidelines Section 15064.3(b). The proposed project would be below the 15 percent SGVCOG baseline Home-Based VMT per capita for residential projects and would not result in a net increase in Total VMT in the region for retail projects.

Impacts would be less than significant and no mitigation is required.

Threshold (c) Would the project substantially increase hazards due to a geometric design feature (e.g., sharp curves or dangerous intersections) or incompatible uses (e.g., farm equipment)?
Less Than Significant Impact. Vehicular access to the project site would be provided from two driveways, one on Mabel Avenue and the other on Rosemead Boulevard. The driveway on Rosemead Boulevard would be restricted to a right-in, right-out turning movements. Parking for the retail uses would be provided from this driveway access. The full access driveway on Mabel Avenue would provide vehicular access to retail uses as well. Access to the above-ground residential parking deck would be gated.

The construction of the project driveways and internal circulation improvements would be pursuant to City Building and Fire Department standards. The proposed project is a mixed-use development bordered by existing residential and commercial land uses. The proposed project does not include the use of any incompatible vehicles or equipment, such as farm equipment. There are no components of the project that would increase hazards to the public due to incompatible use, as the residential and commercial uses proposed by the project would be fully compatible with surrounding land uses. Therefore, such impacts are considered less than significant and no mitigation is required.

Threshold (d) Would the project result in inadequate emergency access? No Impact. As noted above, the proposed project would provide access from Mabel Avenue and Rosemead Boulevard. The Rosemead Boulevard driveway would serve as primary emergency access to the site. The Rosemead Boulevard drive aisle would extend to a fire access hammerhead located on the southeast site corner. Additionally, the proposed project would be required to incorporate all applicable design and safety requirements as set forth in current fire codes, building codes, and safety standards. No changes to the existing roadway network would occur. The County of Los Angeles Department of Public Works designates Rosemead Boulevard as a Disaster Route.48 The project would not require the complete closure of any public or private streets or roadways during construction. Temporary construction activities would not impede use of the road for emergencies or access for emergency response vehicles. Therefore, 48 County of Los Angeles Department of Public Works, Disaster Route Maps By City, Available at: Disaster Route Maps - By City (lacounty.gov), Accessed March 2, 2021.

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the project would not result in inadequate emergency access. No impact would occur and no mitigation is required.

Cumulative Impacts
The Transportation Study addresses the project-specific VMT impacts. No impacts have been identified.

Therefore, the project’s contribution to cumulatively significant impacts would be less than significant.

Mitigation Program
Standard Conditions and Mitigation Measures
No standard conditions or mitigation measures are required.

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4.18 Tribal Cultural Resources
Threshold (a) Would the project cause a substantial adverse change in the significance of a tribal cultural resource, defined in Public Resources Code Section 21074 as either a site, feature, place, cultural landscape that is geographically defined in terms of the size and scope of the landscape, sacred place, or object with cultural value to a California Native American tribe, and that is:
i) Listed or eligible for listing in the California Register of Historical Resources, or in a local register of historical resources as defined in Public Resources Code section 5020.1(k), or
ii) A resource determined by the lead agency, in its discretion and supported by substantial evidence, to be significant pursuant to criteria set forth in subdivision (c) of Public Resources Code Section 5024.1. In applying the criteria set forth in subdivision (c) of Public Resources Code Section 5024.1, the lead agency shall consider the significance of the resource to a California Native American tribe.

Less Than Significant with Mitigation. Chapter 532 Statutes of 2014 (i.e., AB 52) requires that lead agencies evaluate a project’s potential impact on “tribal cultural resources.” Such resources include “sites, features, places, cultural landscapes, sacred places, and objects with cultural value to a California Native American tribe that are eligible for inclusion in the California Register of Historical Resources or included in a local register of historical resources.” A records search was performed on the California Historical Resources Information System and did not identify any historical resources on the project site or within a

0.25-mile radius of the project site. AB 52 also gives lead agencies the discretion to determine, based on substantial evidence, whether a resource qualifies as a “tribal cultural resource.” There are no known Native American cultural resources on or within the immediate project area. In compliance with PRC Section 21080.3.1(b), the City has provided formal notification to California Native American tribal representatives identified by the California Native American Heritage Commission. Native American groups may have knowledge about cultural resources in the area and may have concerns about adverse effects from development on tribal cultural resources as defined in PRC Section 21074. The City has contacted the tribal representatives noted below. Correspondence to and from tribal representatives is included as Appendix H to this Initial Study. As of the release date of the Initial Study, the City has received one request for consultation from Gabrieleño Band of Mission Indians – Kizh Nation, Andrew Salas; consultation occurred on March 31, 2021.
 Gabrieleño Band of Mission Indians – Kizh Nation, Andrew Salas  Gabrieleño/Tongva San Gabriel Band of Mission Indians, Anthony Morales  Gabrieleño/Tongva Nation, Sandonne Goad
 Gabrieleño/Tongva Indians of California Tribal Council, Robert Dorame  Gabrieleño/Tongva Tribe, Charles Alvarez
 Soboba Band of Luiseno Indians, Scott Cozart
 Santa Rosa Band of Cahuilla Indians, Lovina Redner
 Gabrieleño Tongva Tribe, Sam Dunlap

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The project site has been used as a large vehicle storage and junkyard. Since the site has not experience substantial development and native underlying soils are intact, there is the potential for the project to affect previously unidentified Native American tribal cultural resources. Construction activities would include excavation and grading. MM TCR-1, TCR-2, and TCR-3 have been identified to mitigate potential impacts to tribal cultural resources.

Mitigation Program
Standard Conditions and Mitigation Measures
MM TCR-1 Retain a Native American Monitor Prior to Commencement of Ground-Disturbing Activities.

A. The Applicant shall retain a Native American monitor from (or approved by) the Gabrieleño Band of Mission Indians – Kizh Nation (the “Kizh” or the “Tribe”) - the direct lineal descendants of the project location. The monitor shall be retained prior to the commencement of any “ground-disturbing activity” for the subject project, at all project locations (i.e., both on-site and any off-site locations that are included in the project description/definition and/or required in connection with the project, such as public improvement work). “Ground-disturbing activity” includes, but is not limited to, pavement removal, potholing, auguring, grubbing, tree removal, boring, grading, excavation, drilling, and trenching.

B. A copy of the executed monitoring agreement shall be provided to the City of South El Monte prior to the earlier of the commencement of any ground-disturbing activity for the project, or the issuance of any permit necessary to commence a grounddisturbing activity.

C. The Applicant shall provide the Tribe with a minimum of 30 days advance written notice of the commencement of any project ground-disturbing activity so that the Tribe has sufficient time to secure and schedule a monitor for the project.

D. The Applicantshall hold at least one pre-construction sensitivity/educational meeting prior to the commencement of any ground-disturbing activities, where at a senior member of the Tribe will inform and educate the project’s construction and managerial crew and staff members (including any project subcontractors and consultants) about the tribal cultural resources (“TCR”) mitigation measures and compliance obligations, as well as places of significance located on the project site (if any), the appearance of potential TCRs, and other informational and operational guidance to aid in the project’s compliance with the TCR mitigation measures.

E. The monitor will complete daily monitoring logs that will provide descriptions of the relevant ground disturbing activities, the type of construction activities performed, locations of ground-disturbing activities, soil types, cultural-related materials, and any other facts, conditions, materials, or discoveries of significance to the Tribe.

Monitor logs will identify and describe any discovered TCRs, including but not limited to, Native American cultural and historical artifacts, remains, places of significance, etc. (collectively, tribal cultural resources, or “TCR”), as well as any discovered Native American (ancestral) human remains and burial goods. Copies of monitor logs will be provided to the City upon written request.

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F. Native American monitoring for the project shall conclude upon the latter of the following: (1) written confirmation from a designated project point of contact to the Tribe that all ground-disturbing activities and all phases that may involve grounddisturbing activities on the project site and at any off-site project location are complete; or (2) written notice by the Tribe to the Applicant and City that no future, planned construction activity and/or development/construction phase (known by the Tribe at that time) at the project site and at any off-site project location possesses the potential to impact TCRs.

MM TCR-2 Discovery of TCRs, Human Remains, and/or Grave Goods A. Upon the discovery of a TCR, all construction activities in the immediate vicinity of the discovery (i.e., not less than the surrounding 50 feet) shall cease. The Tribe shall be immediately informed of the discovery, and a Kizh monitor and/or Kizh archaeologist will promptly report to the location of the discovery to evaluate the TCR and advise the project manager regarding the matter, protocol, and any mitigating requirements. No project construction activities shall resume in the surrounding 50 feet of the discovered TCR unless and until the Tribe has completed its assessment/evaluation/recovery of the discovered TCR and surveyed the surrounding area.

B. The Tribe will recover and retain all discovered TCRs in the form and/or manner the Tribe deems appropriate in its sole discretion, and for any purpose the Tribe deems appropriate, including but not limited to, educational, cultural and/or historic purposes.

C. If Native American human remains and/or grave goods are discovered or recognized on the project site or at any off-site project location, then all construction activities shall immediately cease. Native American “human remains” are defined to include “an inhumation or cremation, and in any state of decomposition or skeletal completeness.” (Public Resources Code [PRC] §5097.98 (d)(1).) Funerary objects, referred to as “associated grave goods,” shall be treated in the same manner and with the same dignity and respect as human remains. (PRC §5097.98 (a), d)(1) and (2).

D. Any discoveries of human skeletal material or human remains shall be immediately reported to the County Coroner (Health & Safety Code §7050.5(c); 14 Cal. Code Regs. §15064.5(e)(1)(B)), and all ground-disturbing project ground-disturbing activities on site and in any other area where the presence of human remains and/or grave goods are suspected to be present, shall immediately halt and remain halted until the coroner has determined the nature of the remains. (14 Cal. Code Regs. §15064.5(e).) If the coroner recognizes the human remains to be those of a Native American or has reason to believe they are Native American, he or she shall contact, within 24 hours, the Native American Heritage Commission, and Public Resources Code Section 5097.98 shall be followed.

E. Thereafter, construction activities may resume in other parts of the project site at a minimum of 200 feet away from discovered human remains and/or grave goods, if the Tribe determines in its sole discretion that resuming construction activities at that distance is acceptable and provides the project manager express consent of that

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determination (along with any other mitigation measures the Tribal monitor and/or archaeologist deems necessary). (14 Cal. Code Regs. §15064.5(f).) F. Preservation in place (i.e., avoidance) is the preferred manner of treatment for discovered human remains and/or grave goods.

G. Any historic archaeological material that is not Native American in origin (non-TCRs) shall be curated at a public, non-profit institution with a research interest in the materials, such as the Natural History Museum of Los Angeles County or the Fowler Museum, if such an institution agrees to accept the material. If no institution accepts the archaeological material, it shall be offered to a local school or historical society in the area for educational purposes.

H. Any discovery of human remains and/or grave goods discovered and/or recovered shall be kept confidential to prevent further disturbance.

MM TCR-3 Procedures for Burials, Funerary Remains, and Grave Goods A. As the Most Likely Descendant (“MLD”), the Koo-nas-gna Burial Policy shall be implemented for all discovered Native American human remains and/or grave goods.

Tribal Traditions include, but are not limited to, the preparation of the soil for burial, the burial of funerary objects and/or the deceased, and the ceremonial burning of human remains.

B. If the discovery of human remains includes four (4) or more burials, the discovery location shall be treated as a cemetery and a separate treatment plan shall be created.

C. The prepared soil and cremation soils are to be treated in the same manner as bone fragments that remain intact. Associated “grave goods” (aka, burial goods or funerary objects) are objects that, as part of the death rite or ceremony of a culture, are reasonably believed to have been placed with individual human remains either at the time of death or later, as well as other items made exclusively for burial purposes or to contain human remains. Cremations will either be removed in bulk or by means necessary to ensure complete recovery of all sacred materials.

D. In the case where discovered human remains cannot be fully recovered (and documented) on the same day, the remains will be covered with muslin cloth and a steel plate that can be moved by heavy equipment placed over the excavation opening to protect the remains. If this type of steel plate is not available, a 24-hour guard should be posted outside of working hours. The Tribe will make every effort to divert the project while keeping the remains in situ and protected. If the project cannot be diverted, it may be determined that burials will be removed.

E. In the event preservation in place is not possible despite good faith efforts by the Applicant and/or landowner, before ground-disturbing activities may resume on the project site, the landowner shall arrange a designated site location within the footprint of the project for the respectful reburial of the human remains and/or ceremonial objects. The site ofreburial/repatriation shall be agreed upon by the Tribe and the landowner, and shall be protected in perpetuity.

F. Each occurrence of human remains and associated grave goods will be stored using opaque cloth bags. All human remains, grave goods, funerary objects, sacred objects

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and objects of cultural patrimony will be removed to a secure container on site if possible. These items will be retained and shall be reburied within six months of recovery.

G. The Tribe will work closely with the project’s qualified archaeologist to ensure that the excavation is treated carefully, ethically and respectfully. If data recovery is approved by the Tribe, documentation shall be prepared and shall include (at a minimum) detailed descriptive notes and sketches. All data recovery data recoveryrelated forms of documentation shall be approved in advance by the Tribe. If any data recovery is performed, once complete, a final report shall be submitted to the Tribe and the NAHC. The Tribe does NOT authorize any scientific study or the utilization of any invasive and/or destructive diagnostics on human remains.

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4.19 Utilities and Service Systems
Threshold (a) Require or result in the relocation or construction of new or expanded water, wastewater treatment or storm water drainage, electric power, natural gas, or telecommunications facilities, the construction or relocation of which could cause significant environmental effects?
Less Than Significant Impact. The City of South El Monte Public Works Department is responsible for management and operation of approximately 38 miles of pipeline that connect to the Los Angeles County Sanitation Districts (LACSD) trunk system to convey wastewater to LACSD’streatment plants. Additionally, a portion of the City’s sewer facilities are operated and maintained by the Los Angeles Public Works Consolidated Sewer Maintenance District (LACSD).

LACSD’s service area is 850 square miles and encompasses 78 cities and unincorporated areas throughout the County. Through the operation of 11 wastewater treatment facilities, approximately 510 million gallons per day (mgd) of wastewater are treated at these facilities and 165 mgd are available for reuse.

All of the water reclamation plants (WRPs) are strategically located throughout the County to maximize water reuse and to easily return the cleaned water to local waterways, storage reservoirs, or the Pacific Ocean. Wastewater originating from the project site would ultimately be treated by facilities owned and operated by the LACSD. Project wastewater flows would be directed to the Whittier Narrows WRP.49 The Whittier Narrows WRP currently provides primary, secondary, and tertiary treatment with a design capacity of 15 mgd and serves a population of approximately 150,000 people.

The proposed project would increase wastewater generation on the project site. Projected wastewater demand for the project is shown in Table 4.19-1: Future Wastewater Generation. The projected peak wastewater generation is anticipated to be 16,868 gpd. The estimated project wastewater generation represents less than one percent of the total treatment capacity at the Whittier Narrows WRP. Therefore, existing wastewater treatment facilities are able to accommodate the project-generated wastewater and continue maintaining a substantial amount of remaining capacity for future wastewater treatment.

Impacts would be less than significant.

Table 4.19-1: Future Wastewater Generation
Land Use Unit of Measure Proposed Project
Demand Factor
(gpd)
Generated
Wastewater (gpd)
Residential DU 73 DU 156 11,388
Shopping Center1 1000 sf 16,800 sf 325 5,460
Total 16,868
gpd = gallons per day; DU = dwelling unit

1. Per phone call with LACSD, mixed-use commercial retail uses are classified as “shopping center” Source: LACSD. Will Serve Program, Table 1: Loadings for Each Class of Land Use.

Further, the project does not require and would not result in the construction of new storm drainage facilities or expansion of existing facilities. While modifications to the existing on‐site storm drain system 49 Los Angeles County Sanitation District. (2021). Wastewater Treatment Facilities. Retrieved from:
https://www.lacsd.org/facilities/?tab=2&number=4. Accessed on March 30, 2021.

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would be required for project implementation, the existing facilities are adequate to accommodate the development.

The projectsite is somewhatimpervious and does not promote substantial stormwater infiltration. Runoff from the project site flows from the northeast to the southwest. The proposed drainage pattern is similar to the existing condition, except the proposed site would incorporate source control measures to reduce potential off-site impacts. Site runoff would be directed to an on-site infiltration system before overflowing to existing storm drains in Troy Avenue. Additionally, the project would implement source control measures including storm drain messaging and signage, efficient landscape irrigation, and alternative building materials to reduce pollutant sources in stormwater runoff. Under the postdevelopment condition, through the addition of permeable landscape areas, the site would be 94 percent impervious and 6 percent pervious. The proposed drainage system would connect to existing storm drainage facilities and project implementation would not require construction of new storm drainage facilities. Impacts would be less than significant and no mitigation is required.

Threshold (b) Would the project have sufficient water supplies available to serve the project and reasonably foreseeable future development during normal, dry, and multiple dry years? Less Than Significant Impact. The San Gabriel Valley Water Company (SGVWC) provides water service to the City, inclusive of the project site. The SGVWC 2015 Final Draft Urban Water Management Plan (UWMP) was prepared in compliance with the requirements of Water Code Sections 10610 through 10656 of the Urban Water Management Planning Act. The UWMP requires every urban water supplier providing water for municipal purposes to more than 3,000 customers or supplying more than 3,000 AF of water annually to prepare, adopt, and file an UWMP with the California Department of Water Resources every five years in the years ending in zero and five. The 2015 UWMP provides water supply planning for a 25- year planning period in 5-year increments and identifies water supplies needed to meet existing and future demands. The demand analysis must identify supply reliability under three hydrologic conditions:
a normal year, a single-year, and multiple-dry years.

As discussed under Section 4.10 Threshold (b), SGVWC uses local groundwater from 31 wells located in the Main San Gabriel Groundwater Basin (Main Basin) and from 4 wells in the Central Groundwater Basin (Central Basin). SGVWC can purchase imported water supplies from Metropolitan Water District of Southern California. SGVWC has not purchased treated imported water supplies since 2007. SGVWC plans to use treated imported water only as an emergency water supply source. SGVWC does not use selfsupplied surface water to meet its water demands.

Table 4.19-2: Future Water Demand summarizes water demand estimates for the proposed project. The project’s water demand would be approximately 49,700 gpd, or 55.7 acre-feet per year. Indoor water conservation measures include low flow rate plumbing fixtures, while outdoor water use would use subsurface dripline irrigation, low water use plant materials, weather-based irrigation controllers, and mulch. Additionally, the project would be required to comply with Municipal Code Chapter Section 17.25, Water Efficient Landscaping.

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Table 4.19-2: Project Water Demand
Land Use
Total Residents/
Employees
Demand Factor
(gpd/unit)2,3 Water Demand (gpd)
Residential 319 142 45,298
Shopping Center 311 142 4,402
Total 49,700

1. Total employees based on 550 sf per employee for retail/service use

2. gpd = gallons per day

3. Water demand estimates are based on the SGVWC UWMP calculated water use target of 142 gpcd (2015 UWMP, Table 4-2)
Sources: SGVWC, 2015 UWMP. Accessed March 30, 2021 and USGBC, Appendix 2. Default occupancy counts. Accessed March 31, 2021.

The SGVWC anticipates an increase in water use for multi‐family and commercial uses through 2040.

Water demand for multi‐family uses is anticipated to increase from 5,948 AF to 7,697 AF by 2040. Water demand for commercial uses is anticipated to increase from 9,539 AF to 12,344 SF by 2040. According to the SGVWC 2015 UWMP, the available water supply would meet projected demand during normal, dry, and multiple dry years through 2040. The increase in water demand associated with the proposed project would represent a nominal portion of SGVWC’s projected water demand increase. Therefore, the increase in water demand generated by project implementation can be accommodated by the SGVWC. No significant impact would occur, and no mitigation is required.

Threshold (c) Would the project result in a determination by the wastewater treatment provider which serves or may serve the project that it has adequate capacity to serve the project’s projected demand in addition to the provider’s existing commitments? Less Than Significant Impact. The proposed project would result in an incremental increase in the demand for wastewater conveyance and treatment facilities. The project’s wastewater would connect to the existing sewer system lines surrounding the project site. The project site is served by LACSD District 15.

As shown in Table 4.19-1: Future Wastewater Generation, the projected peak wastewater generation is anticipated to be 16,868 gpd. The estimated project wastewater generation represents less than one percent of the total treatment capacity at the Whittier Narrows WRP. Therefore, the LACSD has adequate remaining capacity to serve the proposed project. The increase would not require the construction of new water or wastewater treatment facilities or expansion of existing facilities. Therefore, impacts would be less than significant and no mitigation is required.

Threshold (d) Would the project generate solid waste in excess of State or local standards, or in excess of the capacity of local infrastructure, or otherwise impair the attainment of solid waste reduction goals?
Less Than Significant Impact. The City’s Environmental Services Division addresses all matters related to solid waste collection, hazardous waste and recycling programs provided to the residents and businesses of the City. The City contracts with Athens Services for residential trash collection. Athens Services is responsible for collection, materials recovery facility (MRF) processing, recycling and disposal of non‐ recyclable solid waste. The Athens MRF is in the City of Industry. Solid waste not diverted for recycling at

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the MRF are disposed of at landfills within the greater Southern California region, specifically in San Bernardino County.50
The County of San Bernardino Waste Management Division has five regional landfills and nine transfer stations. Table 4.19-3: County of San Bernardino Landfill Capacities, provides capacity details for each of the County landfills.

Table 4.19-3: County of San Bernardino Landfill Capacities Landfill
Maximum Daily Permitted
Tonnage (tons per day)
Maximum Permitted
Capacity (Cubic Yards)
Remaining Capacity (Cubic
Yards)
Barstow 1,500 80,354,500 71,481,660
Landers 1,200 13,983,500 11,148,100
Mid-Valley 7,500 101,300,000 67,520,000
San Timoteo 2,000 20,400,000 11,402,000
Victorville 3,000 83,200,000 81,510,000
Source: CalRecycle. Solid Waste Information System (SWIS). 2019.

Table 4.19-4: Estimated Project Solid Waste Generation shows the proposed project’s approximate solid waste generation, using CalRecycle’ s estimated solid waste generation per land use.51 As shown in Table 4.19-4, the proposed project would generate 463,780 pounds of solid waste per year, or 231.89 tons per year.

Table 4.19-4: Estimated Project Solid Waste Generation
Land Use Generation Rate Project Information
Solid Waste
Generation (lbs/yr)
Multi-Family Residential 8.6 lbs/du/day 73 du 229,147
Commercial Retail 0.046 lbs/sf/day 13,630 sf 228,848
Restaurant 0.005 lbs/sf/day 3,170 sf 5,785
Total 463,780
Source: CalRecycle. 2019.

The solid waste volume would be less than one ton per day (0.63 ton per day), and therefore considered a nominal amount of the daily capacity of any of the landfills serving the project site. Further, the project would not require demolition of the existing structures (other than a small guard shack), which would generate additional debris to be removed from the site. All paving removed from the site would be disposed of in compliance with the State of California Waste Management Act (AB 939), and Municipal Code Section 13.12.730, Recycling Plan, which requires applicants to develop and submit a plan to recycle 50 City of South El Monte, Proposed Third Amendment to Solid Waste Collection Agreement with Athens Waste, Available at:
https://south-el-monte.granicus.com/MetaViewer.php?view_id=2&clip_id=1049&meta_id=54882, Accessed March 23, 2021. 51 CalRecycle, Estimated Solid Waste Generation Rates, Available at:
https://www2.calrecycle.ca.gov/wastecharacterization/general/rates, Accessed March 23, 2021.

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and salvage the projected construction and demolition debris to the greatest extent feasible. Existing landfills have sufficient capacity to serve the project, therefore impacts are less than significant.

Threshold (e) Would the project comply with federal, State, and local management and reduction statutes and regulations related to solid waste?
No Impact. State, County, and local agencies with regulatory authority related to solid waste include the California Department of Resources Recycling and Recovery, the City’s Environmental Services Division, and Athens Services. Regulations specifically applicable to the proposed project include the California Integrated Waste Management Act of 1989 (AB 939), Section 4.408 of the CalGreen Code, and AB 341, which requires multi‐family residential development and commercial uses to implement recycling programs.

The Integrated Waste Management Act, which requires every City and County in the State to prepare a Source Reduction and Recycling Element (SRRE) to its Solid Waste Management Plan, identifies how each jurisdiction will meet the State’s mandatory waste diversion goal of 50 percent by and after the year 2000.

AB 341 increased the diversion goal to 75 percent by 2020. Municipal Code Chapter 13.12, the City’s solid waste handling and recycling services ordinance, stipulates standards and regulations for the collection and management of solid waste in the City, in accordance with the Integrated Waste Management Act.

Further, the 2019 CalGreen Code Section 4.408 requires preparation of a Construction Waste Management Plan that outlines ways in which the contractor would recycle and/or salvage for reuse a minimum of 65 percent of the nonhazardous construction and demolition debris. During the construction phase, the proposed project would comply with the CalGreen Code through the recycling and reuse of at least 65 percent of the nonhazardous construction and demolition debris from the project site. No conflict with statutes and regulations related to solid waste would occur. No mitigation is required.

Cumulative Impacts
The proposed project would have a less than significant impact with respect to utilities and service systems. The project would require water and wastewater infrastructure, as well as solid waste disposal for building operation. Development of public utility infrastructure is part of an extensive planning process involving utility providers and jurisdictions with discretionary review authority. The coordination process associated with the preparation of development and infrastructure plans is intended to ensure that adequate resources are available to serve both individual projects and cumulative demand for resources and infrastructure as a result of cumulative growth and development in the area. Each individual project is subject to review for utility capacity to avoid unanticipated interruptions in service or inadequate supplies. Coordination with the utility companies would allow for the provision of utility service to the proposed project and other developments. The project and other planned projects are subject to connection and service fees to assist in facility expansion and service improvements triggered by an increase in demand. Because of the utility planning and coordination activities described above, no significant cumulative utility impacts are anticipated.

Mitigation Program
Standard Conditions and Mitigation Measures
No standard conditions or mitigation measures are required.

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4.20 Wildfire
Threshold (a) If located in or near State responsibility areas or lands classified as very high fire hazard severity zones, would the Project substantially impair an adopted emergency response plan or emergency evacuation plan?
No Impact. According to CalFire Fire Hazard Severity Zone Map for Los Angeles County, the project site is not within a State Responsibility Area.
52 The project site is in a Non-Very High Fire Hazard Severity Zone (Non-VHFHSZ) zone within a local responsible area. Project design and site access would adhere to Los Angeles County Fire regulations and designs. Further, project construction would not require the complete closure of any public or private streets or roadways during construction. Temporary construction activities would not impede use of the road for emergencies or access for emergency response vehicles. Therefore, the project would not result in inadequate emergency access, and no impact would occur.

Threshold (b) If located in or near State responsibility areas or lands classified as very high fire hazard severity zones, due to slope, prevailing winds, and other factors, would the Project exacerbate wildfire risks and thereby expose Project occupants to pollutant concentrations from a wildfire or the uncontrolled spread of a wildfire? No Impact. As discussed above, the project is not within an area classified as very high fire hazard severity zone. Therefore, no impacts would occur and no mitigation is required.

Threshold (c) If located in or near State responsibility areas or lands classified as very high fire hazard severity zones, would the Project require the installation or maintenance of associated infrastructure (such as roads, fuel breaks, emergency water sources, power lines or other utilities) that may exacerbate fire risk or that may result in temporary or ongoing impacts to the environment?
No Impact. The project is not within an area classified as very high fire hazard severity zone. The proposed project is surrounded by existing development within an urbanized area of the City. The proposed project would tie into existing infrastructure that currently serves the project area. Project implementation would not result in the new construction, installation, or maintenance of new infrastructure. No impact would occur and no mitigation is required.

Threshold (d) If located in or near State responsibility areas or lands classified as very high fire hazard severity zones, would the Project expose people or structures to significant risks, including downslope or downstream flooding or landslides, as a result of runoff, postfire slope instability, or drainage changes? No Impact. The project is not within an area classified as very high fire hazard severity zone. The project site does not include any downslopes. According to the California Geological Survey, the project site is not within an area identified as having a potential for landslides.53 The project site and surrounding vicinity are relatively flat. There are no known landslides near the site nor is the site in the path of any known or potential landslides. Therefore, no impacts would occur and no mitigation is required. 52 California Department of Forestry and Fire Protection, Los Angeles County Fire Severity Map, Available at:
https://osfm.fire.ca.gov/media/7280/losangelescounty.pdf. Accessed March 13, 2021. 53 California Geological Survey, Geologic Hazards Data and Maps Data Viewer, Available at:
https://maps.conservation.ca.gov/geologichazards/. Accessed December 28, 2020 and September 13, 2021.

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Section 4.0
Environmental Analysis
141 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration
Mitigation Program
Standard Conditions and Mitigation Measures
No standard conditions or mitigation measures are required.

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Section 4.0
Environmental Analysis
142 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration

4.21 Mandatory Findings of Significance
Threshold (a) Does the project have the potential to substantially degrade the quality of the environment, substantially reduce the habitat of a fish or wildlife species, cause a fish or wildlife population to drop below self-sustaining levels, threaten to eliminate a plant or animal community, substantially reduce the number or restrict the range of a rare or endangered plant or animal or eliminate important examples of the major periods of California history or prehistory?
Less Than Significant Impact. On the basis of the foregoing analysis, the proposed project does not have the potential to significantly degrade the quality of the environment, substantially reduce the habitat of a fish or wildlife species, cause a fish or wildlife population to drop below self-sustaining levels, threaten or eliminate a plant or animal community, substantially reduce the number or restrict the range of a rare or endangered plant or animal or eliminate important examples of the major periods of California history or prehistory. The project site is surrounded by existing development in an urbanized area of the City of South El Monte. The proposed project is consistent with the General Plan and the Municipal Code subject to approval of a General Plan amendment and zone change. Therefore, the project would not have a significant impact on any sensitive, rare, or endangered plant/wildlife community.

Threshold (b) Does the project have possible environmental effects which are individually limited, but cumulatively considerable?
Less Than Significant Impact. The proposed project does not have impacts that are individually limited, but cumulatively considerable. Incremental impacts resulting from development and operation of the proposed project and other cumulative projects that would be under construction include air quality, cultural resources, geology and soils, hazards and hazardous materials, and tribal resources. The analysis concluded that these incremental impacts are each less than significant or can be mitigated to a less than significant level. When viewed in connection with the effects of past projects, the effects of other current projects, and the effects of probable future projects, these impacts are not cumulatively considerable. No cumulative impacts are anticipated in connection with this or other projects. The proposed project complies with long-term regional air quality plans, regional population forecasts, and is within the service capabilities of utility purveyors. No significant adverse environmental impacts have been identified. The analysis contained in this Initial Study evaluated existing conditions, potential impacts associated with the development of the project, and possible environmental cumulative impacts. The project does not have any impact on projected growth or planned projects for the City of South El Monte or neighboring jurisdictions known as of the date of this analysis.

Threshold (c) Does the project have environmental effects which will cause substantial adverse effects on human beings, either directly or indirectly? Less Than Significant Impact. There are no known substantial adverse effects on human beings that would be directly or indirectly caused by the proposed project. The environmental evaluation has concluded that no significant environmental impacts will result from the project.

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Section 5.0
References
143 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration

5.0 REFERENCES
California, State of, Department of Conservation. California Important Farmland Finder. Available at https://maps.conservation.ca.gov/dlrp/ciff/. Accessed March 9, 2021.

California, State of, Department of Conservation, Earthquake Zones of Required Investigation EQ Zapp Application, Available at https://maps.conservation.ca.gov/cgs/EQZApp/app/. Accessed February 5, 2021.

California Gas and Electric Utilities. 2018 California Gas Report - Southern California Gas Company Annual Gas Supply 2018-2035 Table 1-SCG. Accessed January 20, 2021.

California, State of, Energy Commission. 2019 Building Energy and Efficiency Standards Frequently Asked Questions Fact Sheet. Available at:
https://www.energy.ca.gov/title24/2019standards/documents/2018_Title_24_2019_Building_Sta ndards_FAQ.pdf. Accessed January 20, 2021.

California, State of, Energy Commission. California Energy Demand 2018-2030 Revised Forecast - Figure 49 Historical and Projected Baseline Consumption SCE Planning Area. Accessed January 20, 2021.

California, State of, Department of Forestry and Fire Protection, Los Angeles County Fire Severity Map, Available at: https://osfm.fire.ca.gov/media/7280/losangelescounty.pdf. Accessed March 13, 2021.

California, State of, Department of Finance. E-5 Population and Housing Estimates for Cities, Counties and the State — January 1, 2011-2018. Accessed March 15, 2021.

California, State of, Department of Toxic Substances Control. Hazardous Waste and Substances Site List - Site Cleanup (Cortese List). Available at: http://www.dtsc.ca.gov/SiteCleanup/Cortese_List.cfm.

Accessed: November 20, 2020.

California, State of, Department of Toxic Substances Control. Envirostor Tool. Available at http://www.envirostor.dtsc.ca.gov/public/. Accessed November 20, 2020.

California, State of, Department of Transportation. California Scenic Highway Mapping System, Available at: https://dot.ca.gov/programs/design/lap-landscape-architecture-and-community-livability/lap-livi-scenic-highways. Accessed December 22, 2020.

California, State of, Water Resources Control Board. Available at http://geotracker.waterboards.ca.gov/.

Accessed November 20, 2020.

California, State of, Water Resources Control Board. Sustainable Groundwater Management Act (SGMA).

Available at https://www.waterboards.ca.gov/water_issues/programs/gmp/sgma.html. Accessed March 30, 2021.

Calland Engineering, Inc. Topographic Map. February 11, 2020.

CalRecycle. Solid Waste Information System (SWIS). Available at https://www2.calrecycle.ca.gov/SWFacilities/Directory. Accessed March 30, 2021.

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Section 5.0
References
144 Mye Plaza Mixed-Use Development Project
Initial Study and Mitigated Negative Declaration
City of South El Monte. General Plan. Available at https://www.cityofsouthelmonte.org/186/GeneralPlan. Accessed on March 30, 2021.

County of Los Angeles Department of Regional Planning, Los Angeles County Airport Land Use Commission, San Gabriel Valley Airport Layout Plan. Available at https://planning.lacounty.gov/assets/upl/project/aluc_elmonte-plan.pdf. Accessed March 9, 2021.

County of Los Angeles Department of Public Works. Disaster Route Maps, City of South El Monte.

Available at: https://pw.lacounty.gov/dsg/DisasterRoutes/map/South%20El%20Monte.pdf.

Accessed March 9, 2021.

Los Angeles County Sanitation District. (2021). Wastewater Treatment Facilities. Retrieved from:
https://www.lacsd.org/facilities/?tab=2&number=4. Accessed March 30, 2021.

San Gabriel Valley Water Company, Los Angeles County Division. 2015 Urban Water Management Plan.

Available at https://www.sgvwater.com/wp-content/uploads/2018/09/Volume-I-FINALAMENDED_2015-UWMP_SGVWC_LACD.pdf. Accessed March 30, 2021.

Southern California Area of Governments. Adopted Final Connect SoCal 2020–2045 Regional Transportation Plan/Sustainable Communities Strategy. Available at https://scag.ca.gov/read-plan-adopted-final-plan. Accessed December 23, 2020.

State of California Department of Finance. December 2020. E-5 Population and Housing Estimates for Cities, Counties, and the State, 2011-2020 with 2010 Census Benchmark. Available at http://dof.ca.gov/Forecasting/Demographics/Estimates/E-5/. Accessed December 19, 2020.

United States, Federal Emergency Management Agency. FEMA. Flood Insurance Rate Map 06037C1665F. https://msc.fema.gov/portal#. Accessed March 4, 2021.

United States Department of Agriculture, Web Soil Survey, https://websoilsurvey.sc.egov.usda.gov/App/WebSoilSurvey.aspx. Accessed March 31, 2021.

United States Green Building Council, Default Occupancy Counts, Available at: Appendix 2. Default occupancy counts | U.S. Green Building Council (usgbc.org). Accessed March 31, 2021.

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APPENDIX A

AIR QUALITY AND GREENHOUSE GAS DATA

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1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Enclosed Parking with Elevator 1.95 Acre 1.95 85,081.00 0 City Park 0.22 Acre 0.22 9,625.00 0
Apartments Mid Rise 73.00 Dwelling Unit 2.05 89,337.00 209 Strip Mall 16.80 1000sqft 0.39 16,800.00 0

1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
9 Wind Speed (m/s) 2.2 Precipitation Freq (Days) 33

1.3 User Entered Comments & Non-Default Data

1.0 Project Characteristics
Utility Company Southern California Edison
Operational Year 2024
CO2 Intensity
(lb/MWhr)
531.44 CH4 Intensity 0.029
(lb/MWhr)
N2O Intensity 0.006
(lb/MWhr)
Mye Plaza project
Los Angeles-South Coast County, Summer
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Project Characteristics - Adjusted per the SCE 2019 Corporate Responsibility and Sustainability Report. The report provides intensity factor of CO2e, the CO2 intensity factor is calculated as 534-25*0.029-298*0.00617=531.4363 to avoid double counting.

Land Use - per site plan
Construction Phase - anticipated schedule
Off-road Equipment -
Off-road Equipment -
Off-road Equipment - no demolition
Off-road Equipment -
Off-road Equipment -
Off-road Equipment -
Grading -
Vehicle Trips - per traffic study
Woodstoves - no wood burning fireplaces per rule 445 SCAQMD Energy Use - 2019 Title 24
Construction Off-road Equipment Mitigation - SCAQMD rule compliance Water Mitigation -
Waste Mitigation -
Area Mitigation -
Table Name Column Name Default Value New Value
tblConstDustMitigation CleanPavedRoadPercentReduction 0 6 tblConstDustMitigation WaterUnpavedRoadMoistureContent 0 12 tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstructionPhase NumDays 20.00 0.00
tblConstructionPhase NumDays 5.00 7.00
tblConstructionPhase NumDays 8.00 30.00
tblConstructionPhase NumDays 230.00 370.00
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tblConstructionPhase NumDays 18.00 20.00
tblConstructionPhase NumDays 18.00 30.00
tblEnergyUse LightingElect 741.44 519.01
tblEnergyUse LightingElect 1.75 1.23
tblEnergyUse LightingElect 6.26 4.38
tblEnergyUse T24E 252.63 176.84
tblEnergyUse T24E 3.92 2.74
tblEnergyUse T24E 4.01 2.81
tblFireplaces NumberGas 62.05 65.70
tblFireplaces NumberWood 3.65 0.00
tblGrading MaterialImported 0.00 100.00
tblLandUse LandUseSquareFeet 84,942.00 85,081.00
tblLandUse LandUseSquareFeet 9,583.20 9,625.00
tblLandUse LandUseSquareFeet 73,000.00 89,337.00
tblLandUse LotAcreage 1.92 2.05
tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00 tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 0.00 tblOffRoadEquipment OffRoadEquipmentUnitAmount 2.00 0.00 tblProjectCharacteristics CO2IntensityFactor 702.44 531.44 tblTripsAndVMT HaulingTripNumber 13.00 12.00
tblTripsAndVMT WorkerTripNumber 0.00 15.00
tblVehicleTrips HO_TTP 40.60 40.40
tblVehicleTrips HS_TTP 19.20 19.00
tblVehicleTrips HW_TTP 40.20 40.60
tblVehicleTrips ST_TR 6.39 5.45
tblVehicleTrips ST_TR 22.75 0.00
tblVehicleTrips ST_TR 42.04 37.86
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2.0 Emissions Summary
tblVehicleTrips SU_TR 5.86 5.45
tblVehicleTrips SU_TR 16.74 0.00
tblVehicleTrips SU_TR 20.43 37.86
tblVehicleTrips WD_TR 6.65 5.45
tblVehicleTrips WD_TR 1.89 0.00
tblVehicleTrips WD_TR 44.32 37.86
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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 3.2424 33.1314 20.6295 0.0444 18.2675 1.6142 19.8816 9.9840 1.4850 11.4691 0.0000 4,339.535 0 4,339.535
0 1.1976 0.0000 4,356.593
0 2023 1.9973 16.4423 20.1616 0.0438 1.2619 0.7102 1.9720 0.3384 0.6681 1.0065 0.0000 4,278.681 6 4,278.681
6 0.6707 0.0000 4,295.448
3 2024 24.8654 8.3170 12.8590 0.0210 0.2236 0.4003 0.6239 0.0593 0.3700 0.4293 0.0000 2,010.756 2 2,010.756
2 0.5724 0.0000 2,025.064
9 Maximum 24.8654 33.1314 20.6295 0.0444 18.2675 1.6142 19.8816 9.9840 1.4850 11.4691 0.0000 4,339.535 0 4,339.535
0 1.1976 0.0000 4,356.593
0 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 3.2424 33.1314 20.6295 0.0444 7.9140 1.6142 9.5282 4.2962 1.4850 5.7812 0.0000 4,339.535 0 4,339.535
0 1.1976 0.0000 4,356.593
0 2023 1.9973 16.4423 20.1616 0.0438 1.1976 0.7102 1.9078 0.3227 0.6681 0.9908 0.0000 4,278.681 6 4,278.681
6 0.6707 0.0000 4,295.448
3 2024 24.8654 8.3170 12.8590 0.0210 0.2119 0.4003 0.6122 0.0564 0.3700 0.4265 0.0000 2,010.756 2 2,010.756
2 0.5724 0.0000 2,025.064
9 Maximum 24.8654 33.1314 20.6295 0.0444 7.9140 1.6142 9.5282 4.2962 1.4850 5.7812 0.0000 4,339.535 0 4,339.535
0 1.1976 0.0000 4,356.593
0 Mitigated Construction
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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 52.80 0.00 46.40 54.97 0.00 44.22 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2016.3.2 Page 6 of 33 Date: 3/2/2021 3:42 PM Mye Plaza project - Los Angeles-South Coast County, Summer

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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 4.6134 1.4511 24.3782 0.0657 3.0403 3.0403 3.0403 3.0403 430.8196 1,402.142 6 1,832.962
2 2.0511 0.0255 1,891.840
2 Energy 0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105 Mobile 1.4174 5.8932 16.9272 0.0647 5.4718 0.0481 5.5200 1.4642 0.0447 1.5089 6,602.792 1 6,602.792
1 0.3134 6,610.626
1 Total 6.0605 7.5986 41.4167 0.1320 5.4718 3.1090 8.5808 1.4642 3.1056 4.5698 430.8196 8,329.019 3 8,759.838
9 2.3707 0.0315 8,828.476
8 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 2.6432 1.1592 6.4858 7.2700e0030.1215 0.1215 0.1215 0.1215 0.0000 1,402.142 6 1,402.142
6 0.0371 0.0255 1,410.670
8 Energy 0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105 Mobile 1.4174 5.8932 16.9272 0.0647 5.4718 0.0481 5.5200 1.4642 0.0447 1.5089 6,602.792 1 6,602.792
1 0.3134 6,610.626
1 Total 4.0903 7.3067 23.5243 0.0736 5.4718 0.1902 5.6620 1.4642 0.1868 1.6510 0.0000 8,329.019 3 8,329.019
3 0.3567 0.0315 8,347.307
3 Mitigated Operational
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3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Demolition Demolition 6/1/2022 5/31/2022 5 0
2 Site Preparation Site Preparation 6/1/2022 6/9/2022 5 7 3 Grading Grading 6/10/2022 7/21/2022 5 30
4 Building Construction Building Construction 7/22/2022 12/21/2023 5 370 5 Paving Paving 12/22/2023 1/18/2024 5 20
6 Architectural Coating Architectural Coating 1/19/2024 2/29/2024 5 30 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

32.51 3.84 43.20 44.22 0.00 93.88 34.02 0.00 93.99 63.87 100.00 0.00 4.92 84.96 0.00 5.45 Residential Indoor: 180,907; Residential Outdoor: 60,302; Non-Residential Indoor: 25,200; Non-Residential Outdoor: 8,400; Striped Parking Area: 5,105 (Architectural Coating ±sqft)
Acres of Grading (Site Preparation Phase): 0
Acres of Grading (Grading Phase): 15
Acres of Paving: 1.95
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Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor Demolition Concrete/Industrial Saws 0 8.00 81 0.73
Demolition Excavators 0 8.00 158 0.38
Demolition Rubber Tired Dozers 0 8.00 247 0.40
Site Preparation Rubber Tired Dozers 3 8.00 247 0.40
Site Preparation Tractors/Loaders/Backhoes 4 8.00 97 0.37 Grading Excavators 1 8.00 158 0.38
Grading Graders 1 8.00 187 0.41
Grading Rubber Tired Dozers 1 8.00 247 0.40
Grading Tractors/Loaders/Backhoes 3 8.00 97 0.37
Building Construction Cranes 1 7.00 231 0.29
Building Construction Forklifts 3 8.00 89 0.20
Building Construction Generator Sets 1 8.00 84 0.74
Building Construction Tractors/Loaders/Backhoes 3 7.00 97 0.37 Building Construction Welders 1 8.00 46 0.45
Paving Cement and Mortar Mixers 2 6.00 9 0.56
Paving Pavers 1 8.00 130 0.42
Paving Paving Equipment 2 6.00 132 0.36
Paving Rollers 2 6.00 80 0.38
Paving Tractors/Loaders/Backhoes 1 8.00 97 0.37
Architectural Coating Air Compressors 1 6.00 78 0.48
Trips and VMT
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3.2 Demolition - 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
Off-Road 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 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 0.0000 0.0000 Unmitigated Construction On-Site

3.1 Mitigation Measures Construction
Replace Ground Cover
Water Exposed Area
Water Unpaved Roads
Reduce Vehicle Speed on Unpaved Roads
Clean Paved 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
Demolition 0 15.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Site Preparation 7 18.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Grading 6 15.00 0.00 12.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Building Construction 9 98.00 26.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Paving 8 20.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 20.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2016.3.2 Page 10 of 33 Date: 3/2/2021 3:42 PM Mye Plaza project - Los Angeles-South Coast County, Summer

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3.2 Demolition - 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 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 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 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 0.0000 0.0000 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 0.0000 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 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 0.0000 0.0000 Mitigated Construction On-Site
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3.2 Demolition - 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 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 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 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 0.0000 0.0000 Mitigated Construction Off-Site

3.3 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 18.0663 0.0000 18.0663 9.9307 0.0000 9.9307 0.0000 0.0000 Off-Road 3.1701 33.0835 19.6978 0.0380 1.6126 1.6126 1.4836 1.4836 3,686.061 9 3,686.061
9 1.1922 3,715.865
5 Total 3.1701 33.0835 19.6978 0.0380 18.0663 1.6126 19.6788 9.9307 1.4836 11.4143 3,686.061 9 3,686.061
9 1.1922 3,715.865
5 Unmitigated Construction On-Site
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3.3 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 0.0723 0.0479 0.6689 1.9800e0030.2012 1.5700e0030.2028 0.0534 1.4500e0030.0548 197.7682 197.7682 5.4600e003197.9047 Total 0.0723 0.0479 0.6689 1.9800e0030.2012 1.5700e0030.2028 0.0534 1.4500e0030.0548 197.7682 197.7682 5.4600e003197.9047 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 7.7233 0.0000 7.7233 4.2454 0.0000 4.2454 0.0000 0.0000 Off-Road 3.1701 33.0835 19.6978 0.0380 1.6126 1.6126 1.4836 1.4836 0.0000 3,686.061 9 3,686.061
9 1.1922 3,715.865
5 Total 3.1701 33.0835 19.6978 0.0380 7.7233 1.6126 9.3359 4.2454 1.4836 5.7289 0.0000 3,686.061 9 3,686.061
9 1.1922 3,715.865
5 Mitigated Construction On-Site
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3.3 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 0.0723 0.0479 0.6689 1.9800e0030.1907 1.5700e0030.1923 0.0508 1.4500e0030.0522 197.7682 197.7682 5.4600e003197.9047 Total 0.0723 0.0479 0.6689 1.9800e0030.1907 1.5700e0030.1923 0.0508 1.4500e0030.0522 197.7682 197.7682 5.4600e003197.9047 Mitigated Construction Off-Site

3.4 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 6.5527 0.0000 6.5527 3.3675 0.0000 3.3675 0.0000 0.0000 Off-Road 1.9486 20.8551 15.2727 0.0297 0.9409 0.9409 0.8656 0.8656 2,872.046 4 2,872.046
4 0.9289 2,895.268
4 Total 1.9486 20.8551 15.2727 0.0297 6.5527 0.9409 7.4936 3.3675 0.8656 4.2331 2,872.046 4 2,872.046
4 0.9289 2,895.268
4 Unmitigated Construction On-Site
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3.4 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 3.1700e0030.0997 0.0249 3.1000e0046.9900e0032.9000e0047.2800e0031.9200e0032.7000e0042.1900e00333.4574 33.4574 2.2600e00333.5140 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 0.0602 0.0399 0.5574 1.6500e0030.1677 1.3100e0030.1690 0.0445 1.2100e0030.0457 164.8069 164.8069 4.5500e003164.9206 Total 0.0634 0.1396 0.5823 1.9600e0030.1747 1.6000e0030.1763 0.0464 1.4800e0030.0479 198.2643 198.2643 6.8100e003198.4346 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 lb/day lb/day
Fugitive Dust 2.8013 0.0000 2.8013 1.4396 0.0000 1.4396 0.0000 0.0000 Off-Road 1.9486 20.8551 15.2727 0.0297 0.9409 0.9409 0.8656 0.8656 0.0000 2,872.046 4 2,872.046
4 0.9289 2,895.268
4 Total 1.9486 20.8551 15.2727 0.0297 2.8013 0.9409 3.7421 1.4396 0.8656 2.3052 0.0000 2,872.046 4 2,872.046
4 0.9289 2,895.268
4 Mitigated Construction On-Site
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3.4 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 3.1700e0030.0997 0.0249 3.1000e0046.6800e0032.9000e0046.9600e0031.8400e0032.7000e0042.1100e00333.4574 33.4574 2.2600e00333.5140 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 0.0602 0.0399 0.5574 1.6500e0030.1589 1.3100e0030.1602 0.0423 1.2100e0030.0435 164.8069 164.8069 4.5500e003164.9206 Total 0.0634 0.1396 0.5823 1.9600e0030.1656 1.6000e0030.1672 0.0442 1.4800e0030.0456 198.2643 198.2643 6.8100e003198.4346 Mitigated Construction Off-Site

3.5 Building Construction - 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
Off-Road 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Total 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Unmitigated Construction On-Site
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3.5 Building Construction - 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 0.0742 2.4006 0.6244 6.6200e0030.1665 4.5100e0030.1710 0.0479 4.3200e0030.0522 708.4633 708.4633 0.0407 709.4797 Worker 0.3935 0.2608 3.6417 0.0108 1.0954 8.5700e0031.1040 0.2905 7.9000e0030.2984 1,076.738 1 1,076.738
1 0.0297 1,077.481
0 Total 0.4677 2.6614 4.2661 0.0174 1.2619 0.0131 1.2750 0.3384 0.0122 0.3507 1,785.201 4 1,785.201
4 0.0704 1,786.960
7 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 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 0.0000 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Total 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 0.0000 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Mitigated Construction On-Site
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3.5 Building Construction - 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 0.0742 2.4006 0.6244 6.6200e0030.1593 4.5100e0030.1639 0.0462 4.3200e0030.0505 708.4633 708.4633 0.0407 709.4797 Worker 0.3935 0.2608 3.6417 0.0108 1.0383 8.5700e0031.0468 0.2765 7.9000e0030.2844 1,076.738 1 1,076.738
1 0.0297 1,077.481
0 Total 0.4677 2.6614 4.2661 0.0174 1.1976 0.0131 1.2107 0.3227 0.0122 0.3349 1,785.201 4 1,785.201
4 0.0704 1,786.960
7 Mitigated Construction Off-Site

3.5 Building 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 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Total 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Unmitigated Construction On-Site
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3.5 Building 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 0.0550 1.8215 0.5639 6.4000e0030.1665 2.1000e0030.1686 0.0479 2.0100e0030.0499 686.1593 686.1593 0.0360 687.0600 Worker 0.3695 0.2360 3.3537 0.0104 1.0954 8.3300e0031.1037 0.2905 7.6700e0030.2982 1,037.312 4 1,037.312
4 0.0268 1,037.982
2 Total 0.4246 2.0574 3.9176 0.0168 1.2619 0.0104 1.2723 0.3384 9.6800e0030.3481 1,723.471 7 1,723.471
7 0.0628 1,725.042
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
Off-Road 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 0.0000 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Total 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 0.0000 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Mitigated Construction On-Site
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3.5 Building 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 0.0550 1.8215 0.5639 6.4000e0030.1594 2.1000e0030.1615 0.0462 2.0100e0030.0482 686.1593 686.1593 0.0360 687.0600 Worker 0.3695 0.2360 3.3537 0.0104 1.0383 8.3300e0031.0466 0.2765 7.6700e0030.2842 1,037.312 4 1,037.312
4 0.0268 1,037.982
2 Total 0.4246 2.0574 3.9176 0.0168 1.1976 0.0104 1.2081 0.3227 9.6800e0030.3323 1,723.471 7 1,723.471
7 0.0628 1,725.042
2 Mitigated Construction Off-Site

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
Off-Road 0.9181 8.7903 12.1905 0.0189 0.4357 0.4357 0.4025 0.4025 1,805.430 4 1,805.430
4 0.5673 1,819.612
2 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.9181 8.7903 12.1905 0.0189 0.4357 0.4357 0.4025 0.4025 1,805.430 4 1,805.430
4 0.5673 1,819.612
2 Unmitigated Construction On-Site
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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 0.0754 0.0482 0.6844 2.1200e0030.2236 1.7000e0030.2253 0.0593 1.5700e0030.0609 211.6964 211.6964 5.4700e003211.8331 Total 0.0754 0.0482 0.6844 2.1200e0030.2236 1.7000e0030.2253 0.0593 1.5700e0030.0609 211.6964 211.6964 5.4700e003211.8331 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 0.9181 8.7903 12.1905 0.0189 0.4357 0.4357 0.4025 0.4025 0.0000 1,805.430 4 1,805.430
4 0.5673 1,819.612
2 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.9181 8.7903 12.1905 0.0189 0.4357 0.4357 0.4025 0.4025 0.0000 1,805.430 4 1,805.430
4 0.5673 1,819.612
2 Mitigated Construction On-Site
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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 0.0754 0.0482 0.6844 2.1200e0030.2119 1.7000e0030.2136 0.0564 1.5700e0030.0580 211.6964 211.6964 5.4700e003211.8331 Total 0.0754 0.0482 0.6844 2.1200e0030.2119 1.7000e0030.2136 0.0564 1.5700e0030.0580 211.6964 211.6964 5.4700e003211.8331 Mitigated Construction Off-Site

3.6 Paving - 2024
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 0.8814 8.2730 12.2210 0.0189 0.3987 0.3987 0.3685 0.3685 1,805.620 5 1,805.620
5 0.5673 1,819.803
9 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.8814 8.2730 12.2210 0.0189 0.3987 0.3987 0.3685 0.3685 1,805.620 5 1,805.620
5 0.5673 1,819.803
9 Unmitigated Construction On-Site
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3.6 Paving - 2024
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 0.0713 0.0439 0.6380 2.0600e0030.2236 1.6800e0030.2252 0.0593 1.5400e0030.0608 205.1357 205.1357 5.0200e003205.2611 Total 0.0713 0.0439 0.6380 2.0600e0030.2236 1.6800e0030.2252 0.0593 1.5400e0030.0608 205.1357 205.1357 5.0200e003205.2611 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 0.8814 8.2730 12.2210 0.0189 0.3987 0.3987 0.3685 0.3685 0.0000 1,805.620 5 1,805.620
5 0.5673 1,819.803
9 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.8814 8.2730 12.2210 0.0189 0.3987 0.3987 0.3685 0.3685 0.0000 1,805.620 5 1,805.620
5 0.5673 1,819.803
9 Mitigated Construction On-Site
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3.6 Paving - 2024
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 0.0713 0.0439 0.6380 2.0600e0030.2119 1.6800e0030.2136 0.0564 1.5400e0030.0580 205.1357 205.1357 5.0200e003205.2611 Total 0.0713 0.0439 0.6380 2.0600e0030.2119 1.6800e0030.2136 0.0564 1.5400e0030.0580 205.1357 205.1357 5.0200e003205.2611 Mitigated Construction Off-Site

3.7 Architectural Coating - 2024
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 24.6133 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.1808 1.2188 1.8101 2.9700e0030.0609 0.0609 0.0609 0.0609 281.4481 281.4481 0.0159 281.8443 Total 24.7941 1.2188 1.8101 2.9700e0030.0609 0.0609 0.0609 0.0609 281.4481 281.4481 0.0159 281.8443 Unmitigated Construction On-Site
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3.7 Architectural Coating - 2024
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 0.0713 0.0439 0.6380 2.0600e0030.2236 1.6800e0030.2252 0.0593 1.5400e0030.0608 205.1357 205.1357 5.0200e003205.2611 Total 0.0713 0.0439 0.6380 2.0600e0030.2236 1.6800e0030.2252 0.0593 1.5400e0030.0608 205.1357 205.1357 5.0200e003205.2611 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 24.6133 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.1808 1.2188 1.8101 2.9700e0030.0609 0.0609 0.0609 0.0609 0.0000 281.4481 281.4481 0.0159 281.8443 Total 24.7941 1.2188 1.8101 2.9700e0030.0609 0.0609 0.0609 0.0609 0.0000 281.4481 281.4481 0.0159 281.8443 Mitigated Construction On-Site
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4.0 Operational Detail - Mobile

4.1 Mitigation Measures Mobile

3.7 Architectural Coating - 2024
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 0.0713 0.0439 0.6380 2.0600e0030.2119 1.6800e0030.2136 0.0564 1.5400e0030.0580 205.1357 205.1357 5.0200e003205.2611 Total 0.0713 0.0439 0.6380 2.0600e0030.2119 1.6800e0030.2136 0.0564 1.5400e0030.0580 205.1357 205.1357 5.0200e003205.2611 Mitigated Construction Off-Site
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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 1.4174 5.8932 16.9272 0.0647 5.4718 0.0481 5.5200 1.4642 0.0447 1.5089 6,602.792 1 6,602.792
1 0.3134 6,610.626
1 Unmitigated 1.4174 5.8932 16.9272 0.0647 5.4718 0.0481 5.5200 1.4642 0.0447 1.5089 6,602.792 1 6,602.792
1 0.3134 6,610.626
1 4.2 Trip Summary Information

4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Apartments Mid Rise 397.85 397.85 397.85 1,363,318 1,363,318 City Park 0.00 0.00 0.00
Enclosed Parking with Elevator 0.00 0.00 0.00
Strip Mall 636.05 636.05 636.05 1,210,142 1,210,142
Total 1,033.90 1,033.90 1,033.90 2,573,460 2,573,460
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 Apartments Mid Rise 14.70 5.90 8.70 40.60 19.00 40.40 86 11 3 City Park 16.60 8.40 6.90 33.00 48.00 19.00 66 28 6
Enclosed Parking with Elevator 16.60 8.40 6.90 0.00 0.00 0.00 0 0 0 Strip Mall 16.60 8.40 6.90 16.60 64.40 19.00 45 40 15

4.4 Fleet Mix
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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

0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105 NaturalGas
Unmitigated

0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105

5.1 Mitigation Measures Energy
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH Apartments Mid Rise 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 City Park 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 Enclosed Parking with Elevator 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 Strip Mall 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 Historical Energy Use: N
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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 lb/day lb/day
Apartments Mid
Rise
2679.23 0.0289 0.2469 0.1051 1.5800e0030.0200 0.0200 0.0200 0.0200 315.2040 315.2040 6.0400e0035.7800e003317.0771 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 Enclosed Parking
with Elevator
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 Strip Mall 75.4849 8.1000e0047.4000e0036.2200e0034.0000e0055.6000e0045.6000e0045.6000e0045.6000e0048.8806 8.8806 1.7000e0041.6000e0048.9334 Total 0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105 Unmitigated
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Use only Natural Gas Hearths

6.1 Mitigation Measures Area

6.0 Area Detail

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 lb/day lb/day
Apartments Mid
Rise

2.67923 0.0289 0.2469 0.1051 1.5800e0030.0200 0.0200 0.0200 0.0200 315.2040 315.2040 6.0400e0035.7800e003317.0771 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 Enclosed Parking
with Elevator
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 Strip Mall 0.0754849 8.1000e0047.4000e0036.2200e0034.0000e0055.6000e0045.6000e0045.6000e0045.6000e0048.8806 8.8806 1.7000e0041.6000e0048.9334 Total 0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105 Mitigated
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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 2.6432 1.1592 6.4858 7.2700e0030.1215 0.1215 0.1215 0.1215 0.0000 1,402.142 6 1,402.142
6 0.0371 0.0255 1,410.670
8 Unmitigated 4.6134 1.4511 24.3782 0.0657 3.0403 3.0403 3.0403 3.0403 430.8196 1,402.142 6 1,832.962
2 2.0511 0.0255 1,891.840
2 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

0.2023 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products

2.1321 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 2.0978 1.3817 18.3562 0.0653 3.0070 3.0070 3.0070 3.0070 430.8196 1,391.294 1 1,822.113
7 2.0407 0.0255 1,880.731
3 Landscaping 0.1812 0.0694 6.0220 3.2000e0040.0334 0.0334 0.0334 0.0334 10.8485 10.8485 0.0104 11.1089 Total 4.6134 1.4511 24.3782 0.0657 3.0403 3.0403 3.0403 3.0403 430.8196 1,402.142 6 1,832.962
2 2.0511 0.0255 1,891.840
2 Unmitigated
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8.1 Mitigation Measures Waste
Install Low Flow Bathroom Faucet
Install Low Flow Kitchen Faucet
Install Low Flow Toilet
Install Low Flow Shower
Use Water Efficient Irrigation System

7.1 Mitigation Measures Water

7.0 Water Detail

8.0 Waste Detail

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

0.2023 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products

2.1321 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.1275 1.0899 0.4638 6.9600e0030.0881 0.0881 0.0881 0.0881 0.0000 1,391.294 1 1,391.294
1 0.0267 0.0255 1,399.561
9 Landscaping 0.1812 0.0694 6.0220 3.2000e0040.0334 0.0334 0.0334 0.0334 10.8485 10.8485 0.0104 11.1089 Total 2.6432 1.1592 6.4858 7.2800e0030.1215 0.1215 0.1215 0.1215 0.0000 1,402.142 6 1,402.142
6 0.0371 0.0255 1,410.670
8 Mitigated
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Institute Recycling and Composting Services

11.0 Vegetation

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
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
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1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Enclosed Parking with Elevator 1.95 Acre 1.95 85,081.00 0 City Park 0.22 Acre 0.22 9,625.00 0
Apartments Mid Rise 73.00 Dwelling Unit 2.05 89,337.00 209 Strip Mall 16.80 1000sqft 0.39 16,800.00 0

1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
9 Wind Speed (m/s) 2.2 Precipitation Freq (Days) 33

1.3 User Entered Comments & Non-Default Data

1.0 Project Characteristics
Utility Company Southern California Edison
Operational Year 2024
CO2 Intensity
(lb/MWhr)
531.44 CH4 Intensity 0.029
(lb/MWhr)
N2O Intensity 0.006
(lb/MWhr)
Mye Plaza project
Los Angeles-South Coast County, Winter
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Project Characteristics - Adjusted per the SCE 2019 Corporate Responsibility and Sustainability Report. The report provides intensity factor of CO2e, the CO2 intensity factor is calculated as 534-25*0.029-298*0.00617=531.4363 to avoid double counting.

Land Use - per site plan
Construction Phase - anticipated schedule
Off-road Equipment -
Off-road Equipment -
Off-road Equipment - no demolition
Off-road Equipment -
Off-road Equipment -
Off-road Equipment -
Grading -
Vehicle Trips - per traffic study
Woodstoves - no wood burning fireplaces per rule 445 SCAQMD Energy Use - 2019 Title 24
Construction Off-road Equipment Mitigation - SCAQMD rule compliance Water Mitigation -
Waste Mitigation -
Area Mitigation -
Table Name Column Name Default Value New Value
tblConstDustMitigation CleanPavedRoadPercentReduction 0 6 tblConstDustMitigation WaterUnpavedRoadMoistureContent 0 12 tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstructionPhase NumDays 20.00 0.00
tblConstructionPhase NumDays 5.00 7.00
tblConstructionPhase NumDays 8.00 30.00
tblConstructionPhase NumDays 230.00 370.00
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tblConstructionPhase NumDays 18.00 20.00
tblConstructionPhase NumDays 18.00 30.00
tblEnergyUse LightingElect 741.44 519.01
tblEnergyUse LightingElect 1.75 1.23
tblEnergyUse LightingElect 6.26 4.38
tblEnergyUse T24E 252.63 176.84
tblEnergyUse T24E 3.92 2.74
tblEnergyUse T24E 4.01 2.81
tblFireplaces NumberGas 62.05 65.70
tblFireplaces NumberWood 3.65 0.00
tblGrading MaterialImported 0.00 100.00
tblLandUse LandUseSquareFeet 84,942.00 85,081.00
tblLandUse LandUseSquareFeet 9,583.20 9,625.00
tblLandUse LandUseSquareFeet 73,000.00 89,337.00
tblLandUse LotAcreage 1.92 2.05
tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00 tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 0.00 tblOffRoadEquipment OffRoadEquipmentUnitAmount 2.00 0.00 tblProjectCharacteristics CO2IntensityFactor 702.44 531.44 tblTripsAndVMT HaulingTripNumber 13.00 12.00
tblTripsAndVMT WorkerTripNumber 0.00 15.00
tblVehicleTrips HO_TTP 40.60 40.40
tblVehicleTrips HS_TTP 19.20 19.00
tblVehicleTrips HW_TTP 40.20 40.60
tblVehicleTrips ST_TR 6.39 5.45
tblVehicleTrips ST_TR 22.75 0.00
tblVehicleTrips ST_TR 42.04 37.86
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2.0 Emissions Summary
tblVehicleTrips SU_TR 5.86 5.45
tblVehicleTrips SU_TR 16.74 0.00
tblVehicleTrips SU_TR 20.43 37.86
tblVehicleTrips WD_TR 6.65 5.45
tblVehicleTrips WD_TR 1.89 0.00
tblVehicleTrips WD_TR 44.32 37.86
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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 3.2508 33.1365 20.3783 0.0435 18.2675 1.6142 19.8816 9.9840 1.4850 11.4691 0.0000 4,257.134 4 4,257.134
4 1.1973 0.0000 4,274.213
4 2023 2.0441 16.4592 19.9133 0.0430 1.2619 0.7103 1.9722 0.3384 0.6682 1.0066 0.0000 4,199.523 5 4,199.523
5 0.6711 0.0000 4,216.301
0 2024 24.8742 8.3216 12.8015 0.0209 0.2236 0.4003 0.6239 0.0593 0.3700 0.4293 0.0000 1,998.781 3 1,998.781
3 0.5720 0.0000 2,013.082
1 Maximum 24.8742 33.1365 20.3783 0.0435 18.2675 1.6142 19.8816 9.9840 1.4850 11.4691 0.0000 4,257.134 4 4,257.134
4 1.1973 0.0000 4,274.213
4 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 3.2508 33.1365 20.3783 0.0435 7.9140 1.6142 9.5282 4.2962 1.4850 5.7812 0.0000 4,257.134 4 4,257.134
4 1.1973 0.0000 4,274.213
4 2023 2.0441 16.4592 19.9133 0.0430 1.1976 0.7103 1.9079 0.3227 0.6682 0.9909 0.0000 4,199.523 5 4,199.523
5 0.6711 0.0000 4,216.301
0 2024 24.8742 8.3216 12.8015 0.0209 0.2119 0.4003 0.6122 0.0564 0.3700 0.4265 0.0000 1,998.781 3 1,998.781
3 0.5720 0.0000 2,013.082
1 Maximum 24.8742 33.1365 20.3783 0.0435 7.9140 1.6142 9.5282 4.2962 1.4850 5.7812 0.0000 4,257.134 4 4,257.134
4 1.1973 0.0000 4,274.213
4 Mitigated Construction
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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 52.80 0.00 46.40 54.97 0.00 44.22 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2016.3.2 Page 6 of 33 Date: 3/2/2021 3:41 PM Mye Plaza project - Los Angeles-South Coast County, Winter

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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 4.6134 1.4511 24.3782 0.0657 3.0403 3.0403 3.0403 3.0403 430.8196 1,402.142 6 1,832.962
2 2.0511 0.0255 1,891.840
2 Energy 0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105 Mobile 1.3713 5.9984 16.2037 0.0616 5.4718 0.0484 5.5202 1.4642 0.0450 1.5092 6,282.341 7 6,282.341
7 0.3141 6,290.193
1 Total 6.0144 7.7038 40.6932 0.1288 5.4718 3.1092 8.5811 1.4642 3.1058 4.5700 430.8196 8,008.568 9 8,439.388
5 2.3714 0.0315 8,508.043
7 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 2.6432 1.1592 6.4858 7.2700e0030.1215 0.1215 0.1215 0.1215 0.0000 1,402.142 6 1,402.142
6 0.0371 0.0255 1,410.670
8 Energy 0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105 Mobile 1.3713 5.9984 16.2037 0.0616 5.4718 0.0484 5.5202 1.4642 0.0450 1.5092 6,282.341 7 6,282.341
7 0.3141 6,290.193
1 Total 4.0442 7.4119 22.8008 0.0705 5.4718 0.1904 5.6623 1.4642 0.1870 1.6512 0.0000 8,008.568 9 8,008.568
9 0.3574 0.0315 8,026.874
3 Mitigated Operational
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3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Demolition Demolition 6/1/2022 5/31/2022 5 0
2 Site Preparation Site Preparation 6/1/2022 6/9/2022 5 7 3 Grading Grading 6/10/2022 7/21/2022 5 30
4 Building Construction Building Construction 7/22/2022 12/21/2023 5 370 5 Paving Paving 12/22/2023 1/18/2024 5 20
6 Architectural Coating Architectural Coating 1/19/2024 2/29/2024 5 30 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

32.76 3.79 43.97 45.31 0.00 93.88 34.01 0.00 93.98 63.87 100.00 0.00 5.10 84.93 0.00 5.66 Residential Indoor: 180,907; Residential Outdoor: 60,302; Non-Residential Indoor: 25,200; Non-Residential Outdoor: 8,400; Striped Parking Area: 5,105 (Architectural Coating ±sqft)
Acres of Grading (Site Preparation Phase): 0
Acres of Grading (Grading Phase): 15
Acres of Paving: 1.95
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Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor Demolition Concrete/Industrial Saws 0 8.00 81 0.73
Demolition Excavators 0 8.00 158 0.38
Demolition Rubber Tired Dozers 0 8.00 247 0.40
Site Preparation Rubber Tired Dozers 3 8.00 247 0.40
Site Preparation Tractors/Loaders/Backhoes 4 8.00 97 0.37 Grading Excavators 1 8.00 158 0.38
Grading Graders 1 8.00 187 0.41
Grading Rubber Tired Dozers 1 8.00 247 0.40
Grading Tractors/Loaders/Backhoes 3 8.00 97 0.37
Building Construction Cranes 1 7.00 231 0.29
Building Construction Forklifts 3 8.00 89 0.20
Building Construction Generator Sets 1 8.00 84 0.74
Building Construction Tractors/Loaders/Backhoes 3 7.00 97 0.37 Building Construction Welders 1 8.00 46 0.45
Paving Cement and Mortar Mixers 2 6.00 9 0.56
Paving Pavers 1 8.00 130 0.42
Paving Paving Equipment 2 6.00 132 0.36
Paving Rollers 2 6.00 80 0.38
Paving Tractors/Loaders/Backhoes 1 8.00 97 0.37
Architectural Coating Air Compressors 1 6.00 78 0.48
Trips and VMT
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3.2 Demolition - 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
Off-Road 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 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 0.0000 0.0000 Unmitigated Construction On-Site

3.1 Mitigation Measures Construction
Replace Ground Cover
Water Exposed Area
Water Unpaved Roads
Reduce Vehicle Speed on Unpaved Roads
Clean Paved 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
Demolition 0 15.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Site Preparation 7 18.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Grading 6 15.00 0.00 12.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Building Construction 9 98.00 26.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Paving 8 20.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 20.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2016.3.2 Page 10 of 33 Date: 3/2/2021 3:41 PM Mye Plaza project - Los Angeles-South Coast County, Winter

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3.2 Demolition - 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 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 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 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 0.0000 0.0000 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 0.0000 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 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 0.0000 0.0000 Mitigated Construction On-Site
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3.2 Demolition - 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 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 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 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 0.0000 0.0000 Mitigated Construction Off-Site

3.3 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 18.0663 0.0000 18.0663 9.9307 0.0000 9.9307 0.0000 0.0000 Off-Road 3.1701 33.0835 19.6978 0.0380 1.6126 1.6126 1.4836 1.4836 3,686.061 9 3,686.061
9 1.1922 3,715.865
5 Total 3.1701 33.0835 19.6978 0.0380 18.0663 1.6126 19.6788 9.9307 1.4836 11.4143 3,686.061 9 3,686.061
9 1.1922 3,715.865
5 Unmitigated Construction On-Site
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3.3 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 0.0806 0.0530 0.6105 1.8700e0030.2012 1.5700e0030.2028 0.0534 1.4500e0030.0548 186.2225 186.2225 5.1300e003186.3507 Total 0.0806 0.0530 0.6105 1.8700e0030.2012 1.5700e0030.2028 0.0534 1.4500e0030.0548 186.2225 186.2225 5.1300e003186.3507 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 7.7233 0.0000 7.7233 4.2454 0.0000 4.2454 0.0000 0.0000 Off-Road 3.1701 33.0835 19.6978 0.0380 1.6126 1.6126 1.4836 1.4836 0.0000 3,686.061 9 3,686.061
9 1.1922 3,715.865
5 Total 3.1701 33.0835 19.6978 0.0380 7.7233 1.6126 9.3359 4.2454 1.4836 5.7289 0.0000 3,686.061 9 3,686.061
9 1.1922 3,715.865
5 Mitigated Construction On-Site
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3.3 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 0.0806 0.0530 0.6105 1.8700e0030.1907 1.5700e0030.1923 0.0508 1.4500e0030.0522 186.2225 186.2225 5.1300e003186.3507 Total 0.0806 0.0530 0.6105 1.8700e0030.1907 1.5700e0030.1923 0.0508 1.4500e0030.0522 186.2225 186.2225 5.1300e003186.3507 Mitigated Construction Off-Site

3.4 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 6.5527 0.0000 6.5527 3.3675 0.0000 3.3675 0.0000 0.0000 Off-Road 1.9486 20.8551 15.2727 0.0297 0.9409 0.9409 0.8656 0.8656 2,872.046 4 2,872.046
4 0.9289 2,895.268
4 Total 1.9486 20.8551 15.2727 0.0297 6.5527 0.9409 7.4936 3.3675 0.8656 4.2331 2,872.046 4 2,872.046
4 0.9289 2,895.268
4 Unmitigated Construction On-Site
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3.4 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 3.2500e0030.1008 0.0264 3.0000e0046.9900e0032.9000e0047.2900e0031.9200e0032.8000e0042.2000e00332.8727 32.8727 2.3400e00332.9312 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 0.0672 0.0442 0.5088 1.5600e0030.1677 1.3100e0030.1690 0.0445 1.2100e0030.0457 155.1854 155.1854 4.2700e003155.2922 Total 0.0704 0.1450 0.5351 1.8600e0030.1747 1.6000e0030.1763 0.0464 1.4900e0030.0479 188.0581 188.0581 6.6100e003188.2234 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 2.8013 0.0000 2.8013 1.4396 0.0000 1.4396 0.0000 0.0000 Off-Road 1.9486 20.8551 15.2727 0.0297 0.9409 0.9409 0.8656 0.8656 0.0000 2,872.046 4 2,872.046
4 0.9289 2,895.268
4 Total 1.9486 20.8551 15.2727 0.0297 2.8013 0.9409 3.7421 1.4396 0.8656 2.3052 0.0000 2,872.046 4 2,872.046
4 0.9289 2,895.268
4 Mitigated Construction On-Site
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3.4 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 3.2500e0030.1008 0.0264 3.0000e0046.6800e0032.9000e0046.9700e0031.8400e0032.8000e0042.1200e00332.8727 32.8727 2.3400e00332.9312 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 0.0672 0.0442 0.5088 1.5600e0030.1589 1.3100e0030.1602 0.0423 1.2100e0030.0435 155.1854 155.1854 4.2700e003155.2922 Total 0.0704 0.1450 0.5351 1.8600e0030.1656 1.6000e0030.1672 0.0442 1.4900e0030.0457 188.0581 188.0581 6.6100e003188.2234 Mitigated Construction Off-Site

3.5 Building Construction - 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
Off-Road 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Total 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Unmitigated Construction On-Site
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3.5 Building Construction - 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 0.0779 2.3941 0.6910 6.4400e0030.1665 4.6600e0030.1711 0.0479 4.4600e0030.0524 688.9227 688.9227 0.0433 690.0052 Worker 0.4389 0.2887 3.3239 0.0102 1.0954 8.5700e0031.1040 0.2905 7.9000e0030.2984 1,013.878 1 1,013.878
1 0.0279 1,014.576
0 Total 0.5168 2.6827 4.0149 0.0166 1.2619 0.0132 1.2751 0.3384 0.0124 0.3508 1,702.800 8 1,702.800
8 0.0712 1,704.581
1 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 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 0.0000 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Total 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 0.0000 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Mitigated Construction On-Site
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3.5 Building Construction - 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 0.0779 2.3941 0.6910 6.4400e0030.1593 4.6600e0030.1640 0.0462 4.4600e0030.0506 688.9227 688.9227 0.0433 690.0052 Worker 0.4389 0.2887 3.3239 0.0102 1.0383 8.5700e0031.0468 0.2765 7.9000e0030.2844 1,013.878 1 1,013.878
1 0.0279 1,014.576
0 Total 0.5168 2.6827 4.0149 0.0166 1.1976 0.0132 1.2108 0.3227 0.0124 0.3350 1,702.800 8 1,702.800
8 0.0712 1,704.581
1 Mitigated Construction Off-Site

3.5 Building 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 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Total 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Unmitigated Construction On-Site
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3.5 Building 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 0.0579 1.8132 0.6140 6.2300e0030.1665 2.2100e0030.1687 0.0479 2.1100e0030.0500 667.5274 667.5274 0.0381 668.4803 Worker 0.4135 0.2611 3.0553 9.8000e0031.0954 8.3300e0031.1037 0.2905 7.6700e0030.2982 976.7862 976.7862 0.0251 977.4146 Total 0.4713 2.0743 3.6693 0.0160 1.2619 0.0105 1.2724 0.3384 9.7800e0030.3482 1,644.313 6 1,644.313
6 0.0633 1,645.894
9 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 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 0.0000 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Total 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 0.0000 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Mitigated Construction On-Site
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3.5 Building 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 0.0579 1.8132 0.6140 6.2300e0030.1594 2.2100e0030.1616 0.0462 2.1100e0030.0483 667.5274 667.5274 0.0381 668.4803 Worker 0.4135 0.2611 3.0553 9.8000e0031.0383 8.3300e0031.0466 0.2765 7.6700e0030.2842 976.7862 976.7862 0.0251 977.4146 Total 0.4713 2.0743 3.6693 0.0160 1.1976 0.0105 1.2082 0.3227 9.7800e0030.3325 1,644.313 6 1,644.313
6 0.0633 1,645.894
9 Mitigated Construction Off-Site

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
Off-Road 0.9181 8.7903 12.1905 0.0189 0.4357 0.4357 0.4025 0.4025 1,805.430 4 1,805.430
4 0.5673 1,819.612
2 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.9181 8.7903 12.1905 0.0189 0.4357 0.4357 0.4025 0.4025 1,805.430 4 1,805.430
4 0.5673 1,819.612
2 Unmitigated Construction On-Site
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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 0.0844 0.0533 0.6235 2.0000e0030.2236 1.7000e0030.2253 0.0593 1.5700e0030.0609 199.3441 199.3441 5.1300e003199.4724 Total 0.0844 0.0533 0.6235 2.0000e0030.2236 1.7000e0030.2253 0.0593 1.5700e0030.0609 199.3441 199.3441 5.1300e003199.4724 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 0.9181 8.7903 12.1905 0.0189 0.4357 0.4357 0.4025 0.4025 0.0000 1,805.430 4 1,805.430
4 0.5673 1,819.612
2 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.9181 8.7903 12.1905 0.0189 0.4357 0.4357 0.4025 0.4025 0.0000 1,805.430 4 1,805.430
4 0.5673 1,819.612
2 Mitigated Construction On-Site
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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 0.0844 0.0533 0.6235 2.0000e0030.2119 1.7000e0030.2136 0.0564 1.5700e0030.0580 199.3441 199.3441 5.1300e003199.4724 Total 0.0844 0.0533 0.6235 2.0000e0030.2119 1.7000e0030.2136 0.0564 1.5700e0030.0580 199.3441 199.3441 5.1300e003199.4724 Mitigated Construction Off-Site

3.6 Paving - 2024
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 0.8814 8.2730 12.2210 0.0189 0.3987 0.3987 0.3685 0.3685 1,805.620 5 1,805.620
5 0.5673 1,819.803
9 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.8814 8.2730 12.2210 0.0189 0.3987 0.3987 0.3685 0.3685 1,805.620 5 1,805.620
5 0.5673 1,819.803
9 Unmitigated Construction On-Site
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3.6 Paving - 2024
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 0.0801 0.0486 0.5805 1.9400e0030.2236 1.6800e0030.2252 0.0593 1.5400e0030.0608 193.1608 193.1608 4.7000e003193.2783 Total 0.0801 0.0486 0.5805 1.9400e0030.2236 1.6800e0030.2252 0.0593 1.5400e0030.0608 193.1608 193.1608 4.7000e003193.2783 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 0.8814 8.2730 12.2210 0.0189 0.3987 0.3987 0.3685 0.3685 0.0000 1,805.620 5 1,805.620
5 0.5673 1,819.803
9 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.8814 8.2730 12.2210 0.0189 0.3987 0.3987 0.3685 0.3685 0.0000 1,805.620 5 1,805.620
5 0.5673 1,819.803
9 Mitigated Construction On-Site
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3.6 Paving - 2024
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 0.0801 0.0486 0.5805 1.9400e0030.2119 1.6800e0030.2136 0.0564 1.5400e0030.0580 193.1608 193.1608 4.7000e003193.2783 Total 0.0801 0.0486 0.5805 1.9400e0030.2119 1.6800e0030.2136 0.0564 1.5400e0030.0580 193.1608 193.1608 4.7000e003193.2783 Mitigated Construction Off-Site

3.7 Architectural Coating - 2024
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 24.6133 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.1808 1.2188 1.8101 2.9700e0030.0609 0.0609 0.0609 0.0609 281.4481 281.4481 0.0159 281.8443 Total 24.7941 1.2188 1.8101 2.9700e0030.0609 0.0609 0.0609 0.0609 281.4481 281.4481 0.0159 281.8443 Unmitigated Construction On-Site
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3.7 Architectural Coating - 2024
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 0.0801 0.0486 0.5805 1.9400e0030.2236 1.6800e0030.2252 0.0593 1.5400e0030.0608 193.1608 193.1608 4.7000e003193.2783 Total 0.0801 0.0486 0.5805 1.9400e0030.2236 1.6800e0030.2252 0.0593 1.5400e0030.0608 193.1608 193.1608 4.7000e003193.2783 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 24.6133 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.1808 1.2188 1.8101 2.9700e0030.0609 0.0609 0.0609 0.0609 0.0000 281.4481 281.4481 0.0159 281.8443 Total 24.7941 1.2188 1.8101 2.9700e0030.0609 0.0609 0.0609 0.0609 0.0000 281.4481 281.4481 0.0159 281.8443 Mitigated Construction On-Site
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4.0 Operational Detail - Mobile

4.1 Mitigation Measures Mobile

3.7 Architectural Coating - 2024
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 0.0801 0.0486 0.5805 1.9400e0030.2119 1.6800e0030.2136 0.0564 1.5400e0030.0580 193.1608 193.1608 4.7000e003193.2783 Total 0.0801 0.0486 0.5805 1.9400e0030.2119 1.6800e0030.2136 0.0564 1.5400e0030.0580 193.1608 193.1608 4.7000e003193.2783 Mitigated Construction Off-Site
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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 1.3713 5.9984 16.2037 0.0616 5.4718 0.0484 5.5202 1.4642 0.0450 1.5092 6,282.341 7 6,282.341
7 0.3141 6,290.193
1 Unmitigated 1.3713 5.9984 16.2037 0.0616 5.4718 0.0484 5.5202 1.4642 0.0450 1.5092 6,282.341 7 6,282.341
7 0.3141 6,290.193
1 4.2 Trip Summary Information

4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Apartments Mid Rise 397.85 397.85 397.85 1,363,318 1,363,318 City Park 0.00 0.00 0.00
Enclosed Parking with Elevator 0.00 0.00 0.00
Strip Mall 636.05 636.05 636.05 1,210,142 1,210,142
Total 1,033.90 1,033.90 1,033.90 2,573,460 2,573,460
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 Apartments Mid Rise 14.70 5.90 8.70 40.60 19.00 40.40 86 11 3 City Park 16.60 8.40 6.90 33.00 48.00 19.00 66 28 6
Enclosed Parking with Elevator 16.60 8.40 6.90 0.00 0.00 0.00 0 0 0 Strip Mall 16.60 8.40 6.90 16.60 64.40 19.00 45 40 15

4.4 Fleet Mix
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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

0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105 NaturalGas
Unmitigated

0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105

5.1 Mitigation Measures Energy
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH Apartments Mid Rise 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 City Park 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 Enclosed Parking with Elevator 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 Strip Mall 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 Historical Energy Use: N
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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 lb/day lb/day
Apartments Mid
Rise
2679.23 0.0289 0.2469 0.1051 1.5800e0030.0200 0.0200 0.0200 0.0200 315.2040 315.2040 6.0400e0035.7800e003317.0771 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 Enclosed Parking
with Elevator
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 Strip Mall 75.4849 8.1000e0047.4000e0036.2200e0034.0000e0055.6000e0045.6000e0045.6000e0045.6000e0048.8806 8.8806 1.7000e0041.6000e0048.9334 Total 0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105 Unmitigated
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Use only Natural Gas Hearths

6.1 Mitigation Measures Area

6.0 Area Detail

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 lb/day lb/day
Apartments Mid
Rise

2.67923 0.0289 0.2469 0.1051 1.5800e0030.0200 0.0200 0.0200 0.0200 315.2040 315.2040 6.0400e0035.7800e003317.0771 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 Enclosed Parking
with Elevator
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 Strip Mall 0.0754849 8.1000e0047.4000e0036.2200e0034.0000e0055.6000e0045.6000e0045.6000e0045.6000e0048.8806 8.8806 1.7000e0041.6000e0048.9334 Total 0.0297 0.2543 0.1113 1.6200e0030.0205 0.0205 0.0205 0.0205 324.0846 324.0846 6.2100e0035.9400e003326.0105 Mitigated
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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 2.6432 1.1592 6.4858 7.2700e0030.1215 0.1215 0.1215 0.1215 0.0000 1,402.142 6 1,402.142
6 0.0371 0.0255 1,410.670
8 Unmitigated 4.6134 1.4511 24.3782 0.0657 3.0403 3.0403 3.0403 3.0403 430.8196 1,402.142 6 1,832.962
2 2.0511 0.0255 1,891.840
2 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

0.2023 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products

2.1321 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 2.0978 1.3817 18.3562 0.0653 3.0070 3.0070 3.0070 3.0070 430.8196 1,391.294 1 1,822.113
7 2.0407 0.0255 1,880.731
3 Landscaping 0.1812 0.0694 6.0220 3.2000e0040.0334 0.0334 0.0334 0.0334 10.8485 10.8485 0.0104 11.1089 Total 4.6134 1.4511 24.3782 0.0657 3.0403 3.0403 3.0403 3.0403 430.8196 1,402.142 6 1,832.962
2 2.0511 0.0255 1,891.840
2 Unmitigated
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8.1 Mitigation Measures Waste
Install Low Flow Bathroom Faucet
Install Low Flow Kitchen Faucet
Install Low Flow Toilet
Install Low Flow Shower
Use Water Efficient Irrigation System

7.1 Mitigation Measures Water

7.0 Water Detail

8.0 Waste Detail

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

0.2023 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products

2.1321 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.1275 1.0899 0.4638 6.9600e0030.0881 0.0881 0.0881 0.0881 0.0000 1,391.294 1 1,391.294
1 0.0267 0.0255 1,399.561
9 Landscaping 0.1812 0.0694 6.0220 3.2000e0040.0334 0.0334 0.0334 0.0334 10.8485 10.8485 0.0104 11.1089 Total 2.6432 1.1592 6.4858 7.2800e0030.1215 0.1215 0.1215 0.1215 0.0000 1,402.142 6 1,402.142
6 0.0371 0.0255 1,410.670
8 Mitigated
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Institute Recycling and Composting Services

11.0 Vegetation

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
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
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1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Enclosed Parking with Elevator 1.95 Acre 1.95 85,081.00 0 City Park 0.22 Acre 0.22 9,625.00 0
Apartments Mid Rise 73.00 Dwelling Unit 2.05 89,337.00 209 Strip Mall 16.80 1000sqft 0.39 16,800.00 0

1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
9 Wind Speed (m/s) 2.2 Precipitation Freq (Days) 33

1.3 User Entered Comments & Non-Default Data

1.0 Project Characteristics
Utility Company Southern California Edison
Operational Year 2024
CO2 Intensity
(lb/MWhr)
531.44 CH4 Intensity 0.029
(lb/MWhr)
N2O Intensity 0.006
(lb/MWhr)
Mye Plaza project
Los Angeles-South Coast County, Annual
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Project Characteristics - Adjusted per the SCE 2019 Corporate Responsibility and Sustainability Report. The report provides intensity factor of CO2e, the CO2 intensity factor is calculated as 534-25*0.029-298*0.00617=531.4363 to avoid double counting.

Land Use - per site plan
Construction Phase - anticipated schedule
Off-road Equipment -
Off-road Equipment -
Off-road Equipment - no demolition
Off-road Equipment -
Off-road Equipment -
Off-road Equipment -
Grading -
Vehicle Trips - per traffic study
Woodstoves - no wood burning fireplaces per rule 445 SCAQMD Energy Use - 2019 Title 24
Construction Off-road Equipment Mitigation - SCAQMD rule compliance Water Mitigation -
Waste Mitigation -
Area Mitigation -
Table Name Column Name Default Value New Value
tblConstDustMitigation CleanPavedRoadPercentReduction 0 6 tblConstDustMitigation WaterUnpavedRoadMoistureContent 0 12 tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstructionPhase NumDays 20.00 0.00
tblConstructionPhase NumDays 5.00 7.00
tblConstructionPhase NumDays 8.00 30.00
tblConstructionPhase NumDays 230.00 370.00
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tblConstructionPhase NumDays 18.00 20.00
tblConstructionPhase NumDays 18.00 30.00
tblEnergyUse LightingElect 741.44 519.01
tblEnergyUse LightingElect 1.75 1.23
tblEnergyUse LightingElect 6.26 4.38
tblEnergyUse T24E 252.63 176.84
tblEnergyUse T24E 3.92 2.74
tblEnergyUse T24E 4.01 2.81
tblFireplaces NumberGas 62.05 65.70
tblFireplaces NumberWood 3.65 0.00
tblGrading MaterialImported 0.00 100.00
tblLandUse LandUseSquareFeet 84,942.00 85,081.00
tblLandUse LandUseSquareFeet 9,583.20 9,625.00
tblLandUse LandUseSquareFeet 73,000.00 89,337.00
tblLandUse LotAcreage 1.92 2.05
tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 0.00 tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 0.00 tblOffRoadEquipment OffRoadEquipmentUnitAmount 2.00 0.00 tblProjectCharacteristics CO2IntensityFactor 702.44 531.44 tblTripsAndVMT HaulingTripNumber 13.00 12.00
tblTripsAndVMT WorkerTripNumber 0.00 15.00
tblVehicleTrips HO_TTP 40.60 40.40
tblVehicleTrips HS_TTP 19.20 19.00
tblVehicleTrips HW_TTP 40.20 40.60
tblVehicleTrips ST_TR 6.39 5.45
tblVehicleTrips ST_TR 22.75 0.00
tblVehicleTrips ST_TR 42.04 37.86
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2.0 Emissions Summary
tblVehicleTrips SU_TR 5.86 5.45
tblVehicleTrips SU_TR 16.74 0.00
tblVehicleTrips SU_TR 20.43 37.86
tblVehicleTrips WD_TR 6.65 5.45
tblVehicleTrips WD_TR 1.89 0.00
tblVehicleTrips WD_TR 44.32 37.86
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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 0.1678 1.4953 1.4938 3.1500e0030.2366 0.0675 0.3040 0.1054 0.0631 0.1685 0.0000 279.4658 279.4658 0.0524 0.0000 280.7765 2023 0.2571 2.1214 2.5753 5.5500e0030.1578 0.0915 0.2494 0.0424 0.0861 0.1285 0.0000 492.4182 492.4182 0.0788 0.0000 494.3881 2024 0.3797 0.0773 0.1258 2.2000e0044.8200e0033.7400e0038.5600e0031.2800e0033.5300e0034.8100e0030.0000 19.2154 19.2154 3.9100e0030.0000 19.3132 Maximum 0.3797 2.1214 2.5753 5.5500e0030.2366 0.0915 0.3040 0.1054 0.0861 0.1685 0.0000 492.4182 492.4182 0.0788 0.0000 494.3881 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 0.1678 1.4953 1.4938 3.1500e0030.1403 0.0675 0.2078 0.0557 0.0631 0.1187 0.0000 279.4656 279.4656 0.0524 0.0000 280.7762 2023 0.2571 2.1214 2.5753 5.5500e0030.1498 0.0915 0.2413 0.0404 0.0861 0.1265 0.0000 492.4179 492.4179 0.0788 0.0000 494.3877 2024 0.3797 0.0773 0.1258 2.2000e0044.5700e0033.7400e0038.3100e0031.2200e0033.5300e0034.7500e0030.0000 19.2153 19.2153 3.9100e0030.0000 19.3132 Maximum 0.3797 2.1214 2.5753 5.5500e0030.1498 0.0915 0.2413 0.0557 0.0861 0.1265 0.0000 492.4179 492.4179 0.0788 0.0000 494.3877 Mitigated Construction
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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 26.19 0.00 18.60 34.72 0.00 17.16 0.00 0.00 0.00 0.00 0.00 0.00 Quarter Start Date End Date Maximum Unmitigated ROG + NOX (tons/quarter) Maximum Mitigated ROG + NOX (tons/quarter) 1 6-1-2022 8-31-2022 0.7615 0.7615
2 9-1-2022 11-30-2022 0.6662 0.6662
3 12-1-2022 2-28-2023 0.6171 0.6171
4 3-1-2023 5-31-2023 0.6066 0.6066
5 6-1-2023 8-31-2023 0.6059 0.6059
6 9-1-2023 11-30-2023 0.6007 0.6007
7 12-1-2023 2-29-2024 0.6257 0.6257
Highest 0.7615 0.7615
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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 0.4749 0.0259 0.9822 8.6000e0040.0418 0.0418 0.0418 0.0418 4.8854 17.0072 21.8926 0.0243 2.9000e00422.5869 Energy 5.4200e0030.0464 0.0203 3.0000e0043.7500e0033.7500e0033.7500e0033.7500e0030.0000 247.1619 247.1619 0.0116 3.1700e003248.3957 Mobile 0.2429 1.1097 2.9852 0.0114 0.9767 8.7700e0030.9854 0.2618 8.1500e0030.2699 0.0000 1,052.587 8 1,052.587
8 0.0515 0.0000 1,053.876
4 Waste 0.0000 0.0000 0.0000 0.0000 10.4013 0.0000 10.4013 0.6147 0.0000 25.7687 Water 0.0000 0.0000 0.0000 0.0000 1.9037 29.6100 31.5137 0.1972 4.9500e00337.9179 Total 0.7233 1.1820 3.9877 0.0125 0.9767 0.0543 1.0309 0.2618 0.0537 0.3154 17.1904 1,346.366 9 1,363.557
3 0.8993 8.4100e0031,388.545
6 Unmitigated Operational
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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 0.4503 0.0223 0.7586 1.3000e0045.2700e0035.2700e0035.2700e0035.2700e0030.0000 17.0072 17.0072 1.4800e0032.9000e00417.1305 Energy 5.4200e0030.0464 0.0203 3.0000e0043.7500e0033.7500e0033.7500e0033.7500e0030.0000 247.1619 247.1619 0.0116 3.1700e003248.3957 Mobile 0.2429 1.1097 2.9852 0.0114 0.9767 8.7700e0030.9854 0.2618 8.1500e0030.2699 0.0000 1,052.587 8 1,052.587
8 0.0515 0.0000 1,053.876
4 Waste 0.0000 0.0000 0.0000 0.0000 5.2006 0.0000 5.2006 0.3074 0.0000 12.8843 Water 0.0000 0.0000 0.0000 0.0000 1.5230 25.1857 26.7087 0.1578 3.9800e00331.8391 Total 0.6986 1.1784 3.7640 0.0118 0.9767 0.0178 0.9944 0.2618 0.0172 0.2789 6.7236 1,341.942 6 1,348.666
3 0.5298 7.4400e0031,364.126
1 Mitigated Operational

3.0 Construction Detail
Construction 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

3.41 0.31 5.61 5.83 0.00 67.23 3.54 0.00 68.00 11.57 60.89 0.33 1.09 41.09 11.53 1.76 CalEEMod Version: CalEEMod.2016.3.2 Page 8 of 40 Date: 3/2/2021 3:43 PM Mye Plaza project - Los Angeles-South Coast County, Annual

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Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Demolition Demolition 6/1/2022 5/31/2022 5 0
2 Site Preparation Site Preparation 6/1/2022 6/9/2022 5 7 3 Grading Grading 6/10/2022 7/21/2022 5 30
4 Building Construction Building Construction 7/22/2022 12/21/2023 5 370 5 Paving Paving 12/22/2023 1/18/2024 5 20
6 Architectural Coating Architectural Coating 1/19/2024 2/29/2024 5 30 OffRoad Equipment
Residential Indoor: 180,907; Residential Outdoor: 60,302; Non-Residential Indoor: 25,200; Non-Residential Outdoor: 8,400; Striped Parking Area: 5,105 (Architectural Coating ±sqft)
Acres of Grading (Site Preparation Phase): 0
Acres of Grading (Grading Phase): 15
Acres of Paving: 1.95
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Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor Demolition Concrete/Industrial Saws 0 8.00 81 0.73
Demolition Excavators 0 8.00 158 0.38
Demolition Rubber Tired Dozers 0 8.00 247 0.40
Site Preparation Rubber Tired Dozers 3 8.00 247 0.40
Site Preparation Tractors/Loaders/Backhoes 4 8.00 97 0.37 Grading Excavators 1 8.00 158 0.38
Grading Graders 1 8.00 187 0.41
Grading Rubber Tired Dozers 1 8.00 247 0.40
Grading Tractors/Loaders/Backhoes 3 8.00 97 0.37
Building Construction Cranes 1 7.00 231 0.29
Building Construction Forklifts 3 8.00 89 0.20
Building Construction Generator Sets 1 8.00 84 0.74
Building Construction Tractors/Loaders/Backhoes 3 7.00 97 0.37 Building Construction Welders 1 8.00 46 0.45
Paving Cement and Mortar Mixers 2 6.00 9 0.56
Paving Pavers 1 8.00 130 0.42
Paving Paving Equipment 2 6.00 132 0.36
Paving Rollers 2 6.00 80 0.38
Paving Tractors/Loaders/Backhoes 1 8.00 97 0.37
Architectural Coating Air Compressors 1 6.00 78 0.48
Trips and VMT
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3.2 Demolition - 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
Off-Road 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 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 0.0000 0.0000 Unmitigated Construction On-Site

3.1 Mitigation Measures Construction
Replace Ground Cover
Water Exposed Area
Water Unpaved Roads
Reduce Vehicle Speed on Unpaved Roads
Clean Paved 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
Demolition 0 15.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Site Preparation 7 18.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Grading 6 15.00 0.00 12.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Building Construction 9 98.00 26.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Paving 8 20.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 20.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2016.3.2 Page 11 of 40 Date: 3/2/2021 3:43 PM Mye Plaza project - Los Angeles-South Coast County, Annual

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3.2 Demolition - 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 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 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 0.0000 0.0000 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 0.0000 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 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 0.0000 0.0000 Mitigated Construction On-Site
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3.2 Demolition - 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 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 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 0.0000 0.0000 Mitigated Construction Off-Site

3.3 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 0.0632 0.0000 0.0632 0.0348 0.0000 0.0348 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0111 0.1158 0.0689 1.3000e0045.6400e0035.6400e0035.1900e0035.1900e0030.0000 11.7038 11.7038 3.7900e0030.0000 11.7984 Total 0.0111 0.1158 0.0689 1.3000e0040.0632 5.6400e0030.0689 0.0348 5.1900e0030.0400 0.0000 11.7038 11.7038 3.7900e0030.0000 11.7984 Unmitigated Construction On-Site
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3.3 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 2.5000e0041.9000e0042.2000e0031.0000e0056.9000e0041.0000e0057.0000e0041.8000e0041.0000e0051.9000e0040.0000 0.6011 0.6011 2.0000e0050.0000 0.6015 Total 2.5000e0041.9000e0042.2000e0031.0000e0056.9000e0041.0000e0057.0000e0041.8000e0041.0000e0051.9000e0040.0000 0.6011 0.6011 2.0000e0050.0000 0.6015 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 0.0270 0.0000 0.0270 0.0149 0.0000 0.0149 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0111 0.1158 0.0689 1.3000e0045.6400e0035.6400e0035.1900e0035.1900e0030.0000 11.7038 11.7038 3.7900e0030.0000 11.7984 Total 0.0111 0.1158 0.0689 1.3000e0040.0270 5.6400e0030.0327 0.0149 5.1900e0030.0201 0.0000 11.7038 11.7038 3.7900e0030.0000 11.7984 Mitigated Construction On-Site
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3.3 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 2.5000e0041.9000e0042.2000e0031.0000e0056.5000e0041.0000e0056.6000e0041.7000e0041.0000e0051.8000e0040.0000 0.6011 0.6011 2.0000e0050.0000 0.6015 Total 2.5000e0041.9000e0042.2000e0031.0000e0056.5000e0041.0000e0056.6000e0041.7000e0041.0000e0051.8000e0040.0000 0.6011 0.6011 2.0000e0050.0000 0.6015 Mitigated Construction Off-Site

3.4 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 0.0983 0.0000 0.0983 0.0505 0.0000 0.0505 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0292 0.3128 0.2291 4.4000e0040.0141 0.0141 0.0130 0.0130 0.0000 39.0822 39.0822 0.0126 0.0000 39.3982 Total 0.0292 0.3128 0.2291 4.4000e0040.0983 0.0141 0.1124 0.0505 0.0130 0.0635 0.0000 39.0822 39.0822 0.0126 0.0000 39.3982 Unmitigated Construction On-Site
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3.4 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 5.0000e0051.5400e0033.8000e0040.0000 1.0000e0040.0000 1.1000e0043.0000e0050.0000 3.0000e0050.0000 0.4519 0.4519 3.0000e0050.0000 0.4527 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 9.1000e0046.8000e0047.8400e0032.0000e0052.4700e0032.0000e0052.4900e0036.5000e0042.0000e0056.7000e0040.0000 2.1469 2.1469 6.0000e0050.0000 2.1483 Total 9.6000e0042.2200e0038.2200e0032.0000e0052.5700e0032.0000e0052.6000e0036.8000e0042.0000e0057.0000e0040.0000 2.5988 2.5988 9.0000e0050.0000 2.6011 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 0.0420 0.0000 0.0420 0.0216 0.0000 0.0216 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0292 0.3128 0.2291 4.4000e0040.0141 0.0141 0.0130 0.0130 0.0000 39.0821 39.0821 0.0126 0.0000 39.3981 Total 0.0292 0.3128 0.2291 4.4000e0040.0420 0.0141 0.0561 0.0216 0.0130 0.0346 0.0000 39.0821 39.0821 0.0126 0.0000 39.3981 Mitigated Construction On-Site
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3.4 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 5.0000e0051.5400e0033.8000e0040.0000 1.0000e0040.0000 1.0000e0043.0000e0050.0000 3.0000e0050.0000 0.4519 0.4519 3.0000e0050.0000 0.4527 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 9.1000e0046.8000e0047.8400e0032.0000e0052.3400e0032.0000e0052.3600e0036.2000e0042.0000e0056.4000e0040.0000 2.1469 2.1469 6.0000e0050.0000 2.1483 Total 9.6000e0042.2200e0038.2200e0032.0000e0052.4400e0032.0000e0052.4600e0036.5000e0042.0000e0056.7000e0040.0000 2.5988 2.5988 9.0000e0050.0000 2.6011 Mitigated Construction Off-Site

3.5 Building Construction - 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
Off-Road 0.0990 0.9057 0.9491 1.5600e0030.0469 0.0469 0.0442 0.0442 0.0000 134.4006 134.4006 0.0322 0.0000 135.2056 Total 0.0990 0.9057 0.9491 1.5600e0030.0469 0.0469 0.0442 0.0442 0.0000 134.4006 134.4006 0.0322 0.0000 135.2056 Unmitigated Construction On-Site
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3.5 Building Construction - 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 4.4000e0030.1414 0.0382 3.8000e0049.5000e0032.7000e0049.7600e0032.7400e0032.5000e0043.0000e0030.0000 36.8452 36.8452 2.2000e0030.0000 36.9002 Worker 0.0229 0.0172 0.1981 6.0000e0040.0623 5.0000e0040.0628 0.0165 4.6000e0040.0170 0.0000 54.2342 54.2342 1.4900e0030.0000 54.2715 Total 0.0273 0.1586 0.2362 9.8000e0040.0718 7.7000e0040.0725 0.0193 7.1000e0040.0200 0.0000 91.0794 91.0794 3.6900e0030.0000 91.1717 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 0.0990 0.9057 0.9491 1.5600e0030.0469 0.0469 0.0442 0.0442 0.0000 134.4005 134.4005 0.0322 0.0000 135.2054 Total 0.0990 0.9057 0.9491 1.5600e0030.0469 0.0469 0.0442 0.0442 0.0000 134.4005 134.4005 0.0322 0.0000 135.2054 Mitigated Construction On-Site
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3.5 Building Construction - 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 4.4000e0030.1414 0.0382 3.8000e0049.1000e0032.7000e0049.3600e0032.6400e0032.5000e0042.9000e0030.0000 36.8452 36.8452 2.2000e0030.0000 36.9002 Worker 0.0229 0.0172 0.1981 6.0000e0040.0591 5.0000e0040.0595 0.0158 4.6000e0040.0162 0.0000 54.2342 54.2342 1.4900e0030.0000 54.2715 Total 0.0273 0.1586 0.2362 9.8000e0040.0682 7.7000e0040.0689 0.0184 7.1000e0040.0191 0.0000 91.0794 91.0794 3.6900e0030.0000 91.1717 Mitigated Construction Off-Site

3.5 Building 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 0.1997 1.8269 2.0630 3.4200e0030.0889 0.0889 0.0836 0.0836 0.0000 294.3920 294.3920 0.0700 0.0000 296.1428 Total 0.1997 1.8269 2.0630 3.4200e0030.0889 0.0889 0.0836 0.0836 0.0000 294.3920 294.3920 0.0700 0.0000 296.1428 Unmitigated Construction On-Site
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3.5 Building 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 7.1500e0030.2339 0.0750 8.0000e0040.0208 2.7000e0040.0211 6.0000e0032.6000e0046.2600e0030.0000 78.1525 78.1525 4.2600e0030.0000 78.2590 Worker 0.0472 0.0341 0.3988 1.2700e0030.1364 1.0600e0030.1374 0.0362 9.7000e0040.0372 0.0000 114.4086 114.4086 2.9500e0030.0000 114.4822 Total 0.0544 0.2680 0.4738 2.0700e0030.1572 1.3300e0030.1585 0.0422 1.2300e0030.0435 0.0000 192.5611 192.5611 7.2100e0030.0000 192.7412 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 0.1997 1.8269 2.0630 3.4200e0030.0889 0.0889 0.0836 0.0836 0.0000 294.3917 294.3917 0.0700 0.0000 296.1425 Total 0.1997 1.8269 2.0630 3.4200e0030.0889 0.0889 0.0836 0.0836 0.0000 294.3917 294.3917 0.0700 0.0000 296.1425 Mitigated Construction On-Site
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3.5 Building 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 7.1500e0030.2339 0.0750 8.0000e0040.0199 2.7000e0040.0202 5.7900e0032.6000e0046.0500e0030.0000 78.1525 78.1525 4.2600e0030.0000 78.2590 Worker 0.0472 0.0341 0.3988 1.2700e0030.1293 1.0600e0030.1304 0.0345 9.7000e0040.0355 0.0000 114.4086 114.4086 2.9500e0030.0000 114.4822 Total 0.0544 0.2680 0.4738 2.0700e0030.1492 1.3300e0030.1505 0.0403 1.2300e0030.0415 0.0000 192.5611 192.5611 7.2100e0030.0000 192.7412 Mitigated Construction Off-Site

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
Off-Road 2.7500e0030.0264 0.0366 6.0000e0051.3100e0031.3100e0031.2100e0031.2100e0030.0000 4.9136 4.9136 1.5400e0030.0000 4.9522 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 2.7500e0030.0264 0.0366 6.0000e0051.3100e0031.3100e0031.2100e0031.2100e0030.0000 4.9136 4.9136 1.5400e0030.0000 4.9522 Unmitigated Construction On-Site
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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 2.3000e0041.6000e0041.9200e0031.0000e0056.6000e0041.0000e0056.6000e0041.7000e0040.0000 1.8000e0040.0000 0.5515 0.5515 1.0000e0050.0000 0.5519 Total 2.3000e0041.6000e0041.9200e0031.0000e0056.6000e0041.0000e0056.6000e0041.7000e0040.0000 1.8000e0040.0000 0.5515 0.5515 1.0000e0050.0000 0.5519 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 2.7500e0030.0264 0.0366 6.0000e0051.3100e0031.3100e0031.2100e0031.2100e0030.0000 4.9136 4.9136 1.5400e0030.0000 4.9522 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 2.7500e0030.0264 0.0366 6.0000e0051.3100e0031.3100e0031.2100e0031.2100e0030.0000 4.9136 4.9136 1.5400e0030.0000 4.9522 Mitigated Construction On-Site
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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 2.3000e0041.6000e0041.9200e0031.0000e0056.2000e0041.0000e0056.3000e0041.7000e0040.0000 1.7000e0040.0000 0.5515 0.5515 1.0000e0050.0000 0.5519 Total 2.3000e0041.6000e0041.9200e0031.0000e0056.2000e0041.0000e0056.3000e0041.7000e0040.0000 1.7000e0040.0000 0.5515 0.5515 1.0000e0050.0000 0.5519 Mitigated Construction Off-Site

3.6 Paving - 2024
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 6.1700e0030.0579 0.0856 1.3000e0042.7900e0032.7900e0032.5800e0032.5800e0030.0000 11.4662 11.4662 3.6000e0030.0000 11.5563 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 6.1700e0030.0579 0.0856 1.3000e0042.7900e0032.7900e0032.5800e0032.5800e0030.0000 11.4662 11.4662 3.6000e0030.0000 11.5563 Unmitigated Construction On-Site
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3.6 Paving - 2024
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 5.0000e0043.5000e0044.1800e0031.0000e0051.5300e0031.0000e0051.5500e0034.1000e0041.0000e0054.2000e0040.0000 1.2470 1.2470 3.0000e0050.0000 1.2478 Total 5.0000e0043.5000e0044.1800e0031.0000e0051.5300e0031.0000e0051.5500e0034.1000e0041.0000e0054.2000e0040.0000 1.2470 1.2470 3.0000e0050.0000 1.2478 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 6.1700e0030.0579 0.0856 1.3000e0042.7900e0032.7900e0032.5800e0032.5800e0030.0000 11.4662 11.4662 3.6000e0030.0000 11.5563 Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 6.1700e0030.0579 0.0856 1.3000e0042.7900e0032.7900e0032.5800e0032.5800e0030.0000 11.4662 11.4662 3.6000e0030.0000 11.5563 Mitigated Construction On-Site
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3.6 Paving - 2024
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 5.0000e0043.5000e0044.1800e0031.0000e0051.4500e0031.0000e0051.4700e0033.9000e0041.0000e0054.0000e0040.0000 1.2470 1.2470 3.0000e0050.0000 1.2478 Total 5.0000e0043.5000e0044.1800e0031.0000e0051.4500e0031.0000e0051.4700e0033.9000e0041.0000e0054.0000e0040.0000 1.2470 1.2470 3.0000e0050.0000 1.2478 Mitigated Construction Off-Site

3.7 Architectural Coating - 2024
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 0.3692 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 2.7100e0030.0183 0.0272 4.0000e0059.1000e0049.1000e0049.1000e0049.1000e0040.0000 3.8299 3.8299 2.2000e0040.0000 3.8353 Total 0.3719 0.0183 0.0272 4.0000e0059.1000e0049.1000e0049.1000e0049.1000e0040.0000 3.8299 3.8299 2.2000e0040.0000 3.8353 Unmitigated Construction On-Site
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3.7 Architectural Coating - 2024
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 1.0800e0037.5000e0048.9500e0033.0000e0053.2900e0033.0000e0053.3100e0038.7000e0042.0000e0059.0000e0040.0000 2.6722 2.6722 7.0000e0050.0000 2.6738 Total 1.0800e0037.5000e0048.9500e0033.0000e0053.2900e0033.0000e0053.3100e0038.7000e0042.0000e0059.0000e0040.0000 2.6722 2.6722 7.0000e0050.0000 2.6738 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 0.3692 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 2.7100e0030.0183 0.0272 4.0000e0059.1000e0049.1000e0049.1000e0049.1000e0040.0000 3.8299 3.8299 2.2000e0040.0000 3.8353 Total 0.3719 0.0183 0.0272 4.0000e0059.1000e0049.1000e0049.1000e0049.1000e0040.0000 3.8299 3.8299 2.2000e0040.0000 3.8353 Mitigated Construction On-Site
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4.0 Operational Detail - Mobile

4.1 Mitigation Measures Mobile

3.7 Architectural Coating - 2024
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 1.0800e0037.5000e0048.9500e0033.0000e0053.1200e0033.0000e0053.1400e0038.3000e0042.0000e0058.5000e0040.0000 2.6722 2.6722 7.0000e0050.0000 2.6738 Total 1.0800e0037.5000e0048.9500e0033.0000e0053.1200e0033.0000e0053.1400e0038.3000e0042.0000e0058.5000e0040.0000 2.6722 2.6722 7.0000e0050.0000 2.6738 Mitigated Construction Off-Site
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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 0.2429 1.1097 2.9852 0.0114 0.9767 8.7700e0030.9854 0.2618 8.1500e0030.2699 0.0000 1,052.587 8 1,052.587
8 0.0515 0.0000 1,053.876
4 Unmitigated 0.2429 1.1097 2.9852 0.0114 0.9767 8.7700e0030.9854 0.2618 8.1500e0030.2699 0.0000 1,052.587 8 1,052.587
8 0.0515 0.0000 1,053.876
4 4.2 Trip Summary Information

4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Apartments Mid Rise 397.85 397.85 397.85 1,363,318 1,363,318 City Park 0.00 0.00 0.00
Enclosed Parking with Elevator 0.00 0.00 0.00
Strip Mall 636.05 636.05 636.05 1,210,142 1,210,142
Total 1,033.90 1,033.90 1,033.90 2,573,460 2,573,460
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 Apartments Mid Rise 14.70 5.90 8.70 40.60 19.00 40.40 86 11 3 City Park 16.60 8.40 6.90 33.00 48.00 19.00 66 28 6
Enclosed Parking with Elevator 16.60 8.40 6.90 0.00 0.00 0.00 0 0 0 Strip Mall 16.60 8.40 6.90 16.60 64.40 19.00 45 40 15

4.4 Fleet Mix
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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 193.5060 193.5060 0.0106 2.1800e003194.4211 Electricity
Unmitigated

0.0000 0.0000 0.0000 0.0000 0.0000 193.5060 193.5060 0.0106 2.1800e003194.4211 NaturalGas
Mitigated

5.4200e0030.0464 0.0203 3.0000e0043.7500e0033.7500e0033.7500e0033.7500e0030.0000 53.6558 53.6558 1.0300e0039.8000e00453.9747 NaturalGas
Unmitigated

5.4200e0030.0464 0.0203 3.0000e0043.7500e0033.7500e0033.7500e0033.7500e0030.0000 53.6558 53.6558 1.0300e0039.8000e00453.9747

5.1 Mitigation Measures Energy
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH Apartments Mid Rise 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 City Park 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 Enclosed Parking with Elevator 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 Strip Mall 0.545348 0.044620 0.206559 0.118451 0.015002 0.006253 0.020617 0.031756 0.002560 0.002071 0.005217 0.000696 0.000850 Historical Energy Use: N
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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
Apartments Mid
Rise
977920 5.2700e0030.0451 0.0192 2.9000e0043.6400e0033.6400e0033.6400e0033.6400e0030.0000 52.1856 52.1856 1.0000e0039.6000e00452.4957 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 Enclosed Parking
with Elevator
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 Strip Mall 27552 1.5000e0041.3500e0031.1300e0031.0000e0051.0000e0041.0000e0041.0000e0041.0000e0040.0000 1.4703 1.4703 3.0000e0053.0000e0051.4790 Total 5.4200e0030.0464 0.0203 3.0000e0043.7400e0033.7400e0033.7400e0033.7400e0030.0000 53.6558 53.6558 1.0300e0039.9000e00453.9747 Unmitigated
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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
Apartments Mid
Rise
977920 5.2700e0030.0451 0.0192 2.9000e0043.6400e0033.6400e0033.6400e0033.6400e0030.0000 52.1856 52.1856 1.0000e0039.6000e00452.4957 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 Enclosed Parking
with Elevator
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 Strip Mall 27552 1.5000e0041.3500e0031.1300e0031.0000e0051.0000e0041.0000e0041.0000e0041.0000e0040.0000 1.4703 1.4703 3.0000e0053.0000e0051.4790 Total 5.4200e0030.0464 0.0203 3.0000e0043.7400e0033.7400e0033.7400e0033.7400e0030.0000 53.6558 53.6558 1.0300e0039.9000e00453.9747 Mitigated
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5.3 Energy by Land Use - Electricity
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
Apartments Mid
Rise
273746 65.9885 3.6000e0037.5000e00466.3006
City Park 0 0.0000 0.0000 0.0000 0.0000
Enclosed Parking
with Elevator
353937 85.3190 4.6600e0039.6000e00485.7225
Strip Mall 175056 42.1985 2.3000e0034.8000e00442.3980 Total 193.5060 0.0106 2.1900e003194.4211
Unmitigated
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Use only Natural Gas Hearths

6.1 Mitigation Measures Area

6.0 Area Detail

5.3 Energy by Land Use - Electricity
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
Apartments Mid
Rise
273746 65.9885 3.6000e0037.5000e00466.3006
City Park 0 0.0000 0.0000 0.0000 0.0000
Enclosed Parking
with Elevator
353937 85.3190 4.6600e0039.6000e00485.7225
Strip Mall 175056 42.1985 2.3000e0034.8000e00442.3980 Total 193.5060 0.0106 2.1900e003194.4211
Mitigated
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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 0.4503 0.0223 0.7586 1.3000e0045.2700e0035.2700e0035.2700e0035.2700e0030.0000 17.0072 17.0072 1.4800e0032.9000e00417.1305 Unmitigated 0.4749 0.0259 0.9822 8.6000e0040.0418 0.0418 0.0418 0.0418 4.8854 17.0072 21.8926 0.0243 2.9000e00422.5869

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

0.0369 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Consumer
Products

0.3891 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Hearth 0.0262 0.0173 0.2295 8.2000e0040.0376 0.0376 0.0376 0.0376 4.8854 15.7770 20.6624 0.0231 2.9000e00421.3271 Landscaping 0.0227 8.6700e0030.7528 4.0000e0054.1700e0034.1700e0034.1700e0034.1700e0030.0000 1.2302 1.2302 1.1800e0030.0000 1.2597 Total 0.4749 0.0259 0.9822 8.6000e0040.0418 0.0418 0.0418 0.0418 4.8854 17.0072 21.8926 0.0243 2.9000e00422.5869 Unmitigated
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Install Low Flow Bathroom Faucet
Install Low Flow Kitchen Faucet
Install Low Flow Toilet
Install Low Flow Shower
Use Water Efficient Irrigation System

7.1 Mitigation Measures Water

7.0 Water Detail

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

0.0369 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Consumer
Products

0.3891 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Hearth 1.5900e0030.0136 5.8000e0039.0000e0051.1000e0031.1000e0031.1000e0031.1000e0030.0000 15.7770 15.7770 3.0000e0042.9000e00415.8708 Landscaping 0.0227 8.6700e0030.7528 4.0000e0054.1700e0034.1700e0034.1700e0034.1700e0030.0000 1.2302 1.2302 1.1800e0030.0000 1.2597 Total 0.4503 0.0223 0.7586 1.3000e0045.2700e0035.2700e0035.2700e0035.2700e0030.0000 17.0072 17.0072 1.4800e0032.9000e00417.1305 Mitigated
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Total CO2 CH4 N2O CO2e
Category MT/yr
Mitigated 26.7087 0.1578 3.9800e00331.8391
Unmitigated 31.5137 0.1972 4.9500e00337.9179

7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
Apartments Mid
Rise

4.75624 /

2.9985

24.4683 0.1562 3.9200e00329.5419
City Park 0 /

0.262126

0.7020 4.0000e0051.0000e0050.7053
Enclosed Parking
with Elevator
0 / 0 0.0000 0.0000 0.0000 0.0000
Strip Mall 1.24442 /

0.762708

6.3434 0.0409 1.0200e0037.6706
Total 31.5137 0.1972 4.9500e00337.9179
Unmitigated
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8.1 Mitigation Measures Waste
Institute Recycling and Composting Services

7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
Apartments Mid
Rise

3.805 /

2.81559

20.6909 0.1251 3.1500e00324.7551
City Park 0 /

0.246136

0.6592 4.0000e0051.0000e0050.6623
Enclosed Parking
with Elevator
0 / 0 0.0000 0.0000 0.0000 0.0000
Strip Mall 0.995535 /

0.716183

5.3587 0.0327 8.2000e0046.4218
Total 26.7087 0.1578 3.9800e00331.8391
Mitigated

8.0 Waste Detail
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Total CO2 CH4 N2O CO2e
MT/yr
Mitigated 5.2006 0.3074 0.0000 12.8843
Unmitigated 10.4013 0.6147 0.0000 25.7687
Category/Year

8.2 Waste by Land Use
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
Apartments Mid
Rise

33.58 6.8164 0.4028 0.0000 16.8874
City Park 0.02 4.0600e0032.4000e0040.0000 0.0101
Enclosed Parking
with Elevator
0 0.0000 0.0000 0.0000 0.0000
Strip Mall 17.64 3.5808 0.2116 0.0000 8.8712
Total 10.4013 0.6147 0.0000 25.7687
Unmitigated
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8.2 Waste by Land Use
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
Apartments Mid
Rise

16.79 3.4082 0.2014 0.0000 8.4437
City Park 0.01 2.0300e0031.2000e0040.0000 5.0300e003 Enclosed Parking
with Elevator
0 0.0000 0.0000 0.0000 0.0000
Strip Mall 8.82 1.7904 0.1058 0.0000 4.4356
Total 5.2006 0.3074 0.0000 12.8843
Mitigated

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
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
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11.0 Vegetation
Equipment Type Number
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Health Risk Assessment
Mye Plaza Project
City of South El Monte
Prepared by:

Kimley-Horn and Associates, Inc.
1100 W. Town and Country Road, Suite 700
Orange, California 92868
Contact: Mr. Ace Malisos
714.939.1030
March 2021

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TABLE OF CONTENTS
1 INTRODUCTION

1.1 Project Location.................................................................................................................... 1

1.2 Project Description ............................................................................................................... 1 2 ENVIRONMENTAL SETTING

2.1 Climate................................................................................................................................. 4

2.2 Meteorology......................................................................................................................... 4

2.3 Toxic Air Contaminants......................................................................................................... 5

2.4 Sensitive Receptors............................................................................................................... 6 3 REGULATORY SETTING

3.1 Federal ................................................................................................................................. 7

3.2 State of California................................................................................................................. 8

3.3 Regional ............................................................................................................................... 9 4 SIGNIFICANCE CRITERIA AND METHODOLOGY

4.1 Health Risk Analysis Thresholds.......................................................................................... 11

4.2 Methodology...................................................................................................................... 11 5 POTENTIAL HEALTH RISK IMPACTS

5.1 Carcinogenic Risk................................................................................................................ 16

5.2 Non-Carcinogenic Hazards.................................................................................................. 18

5.3 Off-Site Sensitive Receptors................................................................................................ 19 6 REFERENCES
References.......................................................................................................................... 21 TABLES
Table 1 Project Summary .................................................................................................................. 1 Table 2 Age Sensitivity Factors, Fraction of Time at Home, and Daily Breathing Rates..................... 14 Table 3 Unmitigated Risk Assessment Results................................................................................. 17 Table 4 Mitigated Risk Assessment Results ..................................................................................... 18 Table 5 Chronic and Acute Hazards Assessment Results.................................................................. 18

EXHIBITS
Exhibit 1 Regional and Local Vicinity Map............................................................................................ 2 Exhibit 2 Site Plan ............................................................................................................................... 3

APPENDIX
Appendix A: Modeling Data

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LIST OF ABBREVIATED TERMS
A absorption factor from inhalation
ACES Advanced Collaborative Emissions Study
ASF age sensitivity factor
AB Assembly Bill
APN Assessor’s Parcel Number
APS auxiliary power system
AT averaging time
AQMP Air Quality Management Plan
ATCM Air Toxic Control Measure
CARB California Air Resources Board
CCAA California Clean Air Act
CEQA California Environmental Quality Act
CSMA California Subdivision Map Act
CPF cancer potency factor
CGP Carson General Plan
Cair air concentration from model
Ci air concentration of substance
DBR daily breathing rate
DOORS Diesel Off-Road Reporting System
DPM Diesel Particulate Matter
DRRP Diesel Risk Reduction Plan
Dose-air does through inhalation
du/ac dwelling units per acre
EMFAC Emissions Factor Model
ED exposure duration
EF exposure frequency
°F Fahrenheit
FCAA Federal Clean Air Act
FAH fraction of time spent at home
GSP gross state product
GVWR gross vehicle weight rating
HAP hazardous air pollutant
HOA homeowner's association
HQ health quotient
HRA health risk assessment
kg kilograms
L liter
MATES Multiple Air Toxics Exposure Study
MICR Maximum Individual Cancer Risk
mg milligrams
µg/m3 micrograms per cubic meter
MSAT Mobile Source Air Toxic
NAAQS National Ambient Air Quality Standards
NED National Elevation Dataset
NESHAP National Emissions Standards for Hazardous Air Pollutants

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LIST OF ABBREVIATED TERMS (CONTINUED)
NO2 nitrogen dioxide
NOX nitrogen oxides
O3 ozone
OEHHA Office Environmental Health Hazard Assessment
PM particulate matter
PM10 particulate matter less than 10 microns in diameter PM2.5 particulate matter less than 2.5 microns in diameter PERP Portable Equipment Registration Program
REL Reference Exposure Level
RELi Reference Exposure Level of substance
Riskinh-res residential inhalation cancer risk
SB Senate Bill
SCAB South Coast Air Basin
SCAQMD South Coast Air Quality Management District
T-BACT toxics best available control technology
TAC Toxic Air Contaminant
U.S. EPA United States Environmental Protection Agency
VMT vehicle miles traveled
VOC volatile organic compound

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1 INTRODUCTION
The purpose of this Health Risk Assessment (HRA) is to evaluate potential health risks associated with Toxic Air Contaminants (TAC) including Diesel Particulate Matter (DPM) and Total Organic Gases (TOG) resulting from the implementation of the proposed Mye Plaza Project in the City of South El Monte. This HRA was prepared in accordance with the requirements of the South Coast Air Quality Management District (SCAQMD) and guidance from the Office of Environmental Health Hazard Assessment (OEHHA) to determine if health risks are likely to occur from the Project. Technical data is included as see Appendix A: Modeling Data.

1.1 Project Location
The project site is located at 2727 North Rosemead Boulevard in the western portion of the City of South El Monte, Los Angeles County, California. The approximate 1.73-acre project site includes six different parcels legally described as Assessor Parcel Number (APN) 5281-002-005, -006, -009, -010, -011, -018. The property is generally bordered by Mabel Avenue to the north, Rosemead Boulevard (State Route [SR] 164) to the east, a mobile home park and Troy Avenue to the south, and light industrial uses to the west.

Regional access is provided by Interstate 10 (I-10), which is located approximately 0.75 miles north of the project site, and SR- 60, which is located approximately 1.4 miles south of the project site. Local access to the project site is currently restricted by locked gates, though site driveways exist on Mabel and Rosemead Boulevard for private access. The project site is shown in a regional and local context on Exhibit 1, Regional and Local Vicinity Map and Exhibit 2, Site Plan, respectively.

1.2 Project Description
The project would develop a 4-story, 106,137-square foot mixed-use building. Table 1: Project Summary identifies proposed uses and associated square footage.

Table 1: Project Summary
Use Type Net Square Feet
Residential 89,337
Food Retail 3,170
Commercial Retail 13,630
Total 106,137
Source: SLA Architects, 2020.

The project would provide 223 vehicle parking spaces throughout a ground floor parking garage and parking deck. The maximum proposed building height would be 60’-0” (to top of roof, excluding parapet).

The project would include a mix of one to three-bedroom leasable apartment units ranging in size from 770 square feet (sf) to 1,469 sf.

The project site currently has a General Plan designation of Commercial-Manufacturing (CM). According to the General Plan, the CM designation allows for general commercial and limited manufacturing uses.

The project would require a General Plan Amendment to change the designation from CM to Mixed-Use (C/R). The C/R designation allows for a mixture of commercial, office, and residential uses.

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EXHIBIT 1: Regional and Local Vicinity Map
Mye Plaza Mixed-Use Project
Garvey Avenue
Mabel Avenue
Lee Avenue
Project Site
Garvey Avenue
Rosemead Boulevard
City of South El Monte
Pacific Ocean
Los Angeles
Troy Avenue
Rio Hondo

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NOT TO SCALE
EXHIBIT 2: Site Plan
Mye Plaza Mixed Use Project

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2 ENVIRONMENTAL SETTING

2.1 Climate
The general region lies in the semi‐permanent high‐pressure zone of the eastern Pacific. The climate is mild and tempered by cool sea breezes. The usually mild climatological pattern is interrupted infrequently by periods of extremely hot weather, winter storms, or Santa Ana winds. The extent and severity of the air pollution problem in the South Coast Air Basin (SCAB) is a function of the area’s natural physical characteristics (weather and topography), as well as man‐made influences (development patterns and lifestyle). Factors such as wind, sunlight, temperature, humidity, rainfall, and topography all affect the accumulation and/or dispersion of pollutants throughout the SCAB. These factors along with applicable regulations are discussed below.

The average annual temperature varies little throughout the SCAB, averaging 75 degrees Fahrenheit (°F).

However, with a less‐pronounced oceanic influence, the eastern inland portions of the SCAB show greater variability in annual minimum and maximum temperatures. All portions of the SCAB have had recorded temperatures over 100°F in recent years.

2.2 Meteorology
Although the SCAB has a semi‐arid climate, the air near the surface is moist due to the presence of a shallow marine layer. Except for infrequent periods when dry, continental air is brought into the SCAB by offshore winds, the ocean effect is dominant. Periods with heavy fog are frequent, and low stratus clouds, occasionally referred to as “high fog,” are a characteristic climate feature. Annual average relative humidity is 70 percent at the coast and 57 percent in the eastern part of the SCAB. Precipitation in the SCAB is typically nine to 14 inches annually and is rarely in the form of snow or hail due to typically warm weather. The frequency and amount of rainfall is greater in the coastal areas of the SCAB.

A temperature inversion is defined as an increase in temperature with height, or to the layer within which such an increase occurs. The height of the inversion is important in determining pollutant concentration.

When the inversion is approximately 2,500 feet above sea level, the sea breezes carry the pollutants inland to escape over the mountain slopes or through the passes. At a height of 1,200 feet, the terrain prevents the pollutants from entering the upper atmosphere, resulting in a settlement in the foothill communities.

Below 1,200 feet, the inversion puts a tight lid on pollutants, concentrating them in a shallow layer over the entire SCAB. Usually, inversions are lower before sunrise than during the day. Mixing heights for inversions are lower in the summer and more persistent, being partly responsible for the high levels of ozone (O3) observed during summer months in the SCAB. Smog in Southern California is generally the result of these temperature inversions combining with coastal day winds and local mountains to contain the pollutants for long periods of time, allowing them to form secondary pollutants by reacting with sunlight. The SCAB has a limited ability to disperse these pollutants due to typically low wind speeds.

The area in which the Project is located offers clear skies and sunshine, yet it is still susceptible to air inversions. These inversions trap a layer of stagnant air near the ground, where it is then further loaded with pollutants. These inversions cause haziness, which is caused by moisture, suspended dust, and a variety of chemical aerosols emitted by trucks, automobiles, furnaces, and other sources.

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2.3 Toxic Air Contaminants
Toxic Air Contaminants (TACs) are airborne substances capable of causing short‐term (acute) and long‐ term (chronic or carcinogenic, i.e., cancer causing) adverse human health effects (i.e., injury or illness).

TACs include both organic and inorganic chemical substances. They may be emitted from a variety of common sources including gasoline stations, automobiles, dry cleaners, industrial operations, and painting operations. The current California list of TACs includes approximately 200 compounds, including particulate emissions from diesel‐fueled engines.

Hazardous Air Pollutants (HAP) is a term used by the Federal Clean Air Act (FCAA) that includes a variety of pollutants generated or emitted by industrial production activities. Identified as TACs under the California Clean Air Act (CCAA), ten have been singled out through ambient air quality data as being the most substantial health risk in California. Direct exposure to these pollutants has been shown to cause cancer, birth defects, damage to the brain and nervous system, and respiratory disorders. The California Air Resources Board (CARB) provides emission inventories for only the larger air basins.

TACs do not have ambient air quality standards because no safe levels of TACs can be determined. Instead, TAC impacts are evaluated by calculating the health risks associated with a given exposure. The requirements of the Air Toxic “Hot Spots” Information and Assessment Act (Assembly Bill [AB] 2588) apply to facilities that use, produce, or emit toxic chemicals. Facilities subject to the toxic emission inventory requirements of the act must prepare and submit toxic emission inventory plans and reports, and periodically update those reports.

Mobile sources and industrial facilities are significant sources of TACs. Various common urban facilities also produce TAC emissions, such as gasoline stations (benzene), hospitals (ethylene oxide), and dry cleaners (perchloroethylene). Automobile exhaust also contains TACs such as benzene and 1,3-butadiene.

Diesel particulate matter (DPM) was identified as a TAC by CARB in 1998. DPM differs from other TACs in that it is not a single substance but rather a complex mixture of hundreds of substances. SCAQMD research indicates that mobile-source emissions of DPM, benzene, and 1,3-butadiene represent a substantial portion of the ambient background risk from TACs.

In California, on‐road diesel‐fueled engines contribute approximately 24 percent of the statewide total, with an additional 71 percent attributed to other mobile sources such as construction and mining equipment, agricultural equipment, and transport refrigeration units. Stationary sources contribute about 5 percent of total DPM. It should be noted that CARB has developed several plans and programs to reduce diesel emissions such as the Diesel Risk Reduction Plan (DRRP), the Statewide Portable Equipment Registration Program (PERP), and the Diesel Off‐Road Reporting System (DOORS). The PERP and DOORS programs allow owners or operators of portable engines and certain other types of equipment can register their units in order to operate their equipment throughout California without having to obtain individual permits from local air districts.

Diesel exhaust and many individual substances contained in it (including arsenic, benzene, formaldehyde, and nickel) have the potential to contribute to mutations in cells that can lead to cancer. Long‐term exposure to diesel exhaust particles poses the highest cancer risk of any TAC evaluated by OEHHA. CARB estimates that about 70 percent of the cancer risk that the average Californian faces from breathing toxic air pollutants stems from diesel exhaust particles.

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Exposure to diesel exhaust can have immediate health effects. Diesel exhaust can irritate the eyes, nose, throat, and lungs, and it can cause coughs, headaches, lightheadedness, and nausea. In studies with human volunteers, diesel exhaust particles made people with allergies more susceptible to the materials to which they are allergic, such as dust and pollen. Exposure to diesel exhaust also causes inflammation in the lungs, which may aggravate chronic respiratory symptoms and increase the frequency or intensity of asthma attacks.

Diesel engines are a major source of fine particulate pollution. The elderly and people with emphysema, asthma, and chronic heart and lung disease are especially sensitive to fine‐particle pollution. Numerous studies have linked elevated particle levels in the air to increased hospital admissions, emergency room visits, asthma attacks, and premature deaths among those suffering from respiratory problems. Because children’s lungs and respiratory systems are still developing, they are also more susceptible than healthy adults to fine particles. Exposure to fine particles is associated with increased frequency of childhood illnesses and can also reduce lung function in children. In California, diesel exhaust particles have been identified as a carcinogen.

2.4 Sensitive Receptors
Sensitive populations are more susceptible to the effects of air pollution than is the general population.

Sensitive receptors that are in proximity to localized sources of toxics are of particular concern. Land uses considered sensitive receptors include residences, schools, playgrounds, childcare centers, long‐term health care facilities, rehabilitation centers, convalescent centers, and retirement homes. For the purposes of this study, sensitive receptors are the on-site residents that would be located within the project site.

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3 REGULATORY SETTING

3.1 Federal
Federal Clean Air Act
The FCAA was amended in 1990 to address the numerous air pollutants that are known to cause or may reasonably be anticipated to cause adverse effects to human health or adverse environmental effects. 188 specific pollutants and chemical groups were initially identified as HAPs, and the list has been modified over time. The FCAA Amendments included new regulatory programs to control acid deposition and for the issuance of stationary source operating permits.

In 2001, the United States Environmental Protection Agency (U.S. EPA) issued its first Mobile Source Air Toxics Rule, which identified 21 mobile source air toxic (MSAT) compounds as being HAPs that required regulation. A subset of six of these MSAT compounds were identified as having the greatest influence on health: benzene, 1,3‐butadiene, formaldehyde, acrolein, acetaldehyde, and DPM. More recently, the U.S.

EPA issued a second MSAT Rule in February 2007, which generally supported the findings in the first rule and provided additional recommendations of compounds having the greatest impact on health. The rule also identified several engine emission certification standards that must be implemented. Unlike the criteria pollutants, toxics do not have National Ambient Air Quality Standards (NAAQS) making evaluation of their impacts more subjective.

National Emissions Standards for Hazardous Air Pollutants (NESHAPs) were incorporated into a greatly expanded program for controlling toxic air pollutants. The provisions for attainment and maintenance of the NAAQS were substantially modified and expanded. Other revisions included provisions regarding stratospheric ozone protection, increased enforcement authority, and expanded research programs.

Section 112 of the FCAA Amendments governs the federal control program for HAPs. NESHAPs are issued to limit the release of specified HAPs from specific industrial sectors. These standards are technology‐ based, meaning that they represent the best available control technology an industrial sector could afford.

The level of emissions controls required by NESHAPs are not based on health risk considerations because allowable releases and resulting concentrations have not been determined to be safe for the public. The FCAA does not establish air quality standards for HAPs that define legally acceptable concentrations of these pollutants in ambient air.

Federal Emissions Standards for On-Road Trucks
To reduce emissions from on-road, heavy-duty diesel trucks, the U.S. EPA established a series of increasingly strict emission standards for new engines, starting in 1988. The U.S. EPA promulgated the final and cleanest standards with the 2007 Heavy-Duty Highway Rule.1 The PM emission standard of 0.01 gram per horsepower-hour (g/hp-hr) is required for new vehicles beginning with model year 2007. Also, the NOX and nonmethane hydrocarbon (NMHC) standards of 0.20 g/hp-hr and 0.14 g/hp-hr, respectively, were phased in together between 2007 and 2010 on a percent of sales basis: 50 percent from 2007 to 2009 and 100 percent in 2010.
1 United States Environmental Protection Agency (U.S. EPA), Control of Air Pollution from New Motor Vehicles: Heavy-Duty Engine and Vehicle Standards and Highway Diesel Fuel Sulfur Control Requirements, Final Rule. 40 Code of Federal Regulations, Parts 69, 80, and 86. January 18, 2001.

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3.2 State of California
California Air Resources Board
CARB’s statewide comprehensive air toxics program was established in 1983 with AB 1807 the Toxic Air Contaminant Identification and Control Act (Tanner Air Toxics Act of 1983). AB 1807 created California's program to reduce exposure to air toxics and sets forth a formal procedure for CARB to designate substances as TACs. Once a TAC is identified, CARB adopts an airborne toxics control measure (ATCM) for sources that emit designated TACs. If there is a safe threshold for a substance at which there is no toxic effect, the control measure must reduce exposure to below that threshold. If there is no safe threshold, the measure must incorporate toxics best available control technology (T‐BACT) to minimize emissions.

CARB also administers the State’s mobile source emissions control program and oversees air quality programs established by State statute, such as AB 2588. Under AB 2588, TAC emissions from individual facilities are quantified and prioritized by the air quality management district or air pollution control district. High priority facilities are required to perform a health risk assessment and, if specific thresholds are exceeded, required to communicate the results to the public in the form of notices and public meetings. In September 1992, the AB 2588 was amended by Senate Bill (SB) 1731 which required facilities that pose a significant health risk to the community to reduce their risk through a risk management plan.

Diesel Risk Reduction Plan
The identification of DPM as a TAC in 1998 led CARB to adopt the Risk Reduction Plan to Reduce Particulate Matter Emissions from Diesel‐Fueled Engines and Vehicles (DRRP) in October 2000. The DRRP's goals include an 85 percent reduction in DPM by 2020 from the 2000 baseline2. The DRRP includes regulations to establish cleaner new diesel engines, cleaner in‐use diesel engines (retrofits), and cleaner diesel fuel.

Truck and Bus Regulation Reducing Emissions from Existing Diesel Vehicles On December 12, 2008, CARB approved the Truck and Bus Regulation to significantly reduce particulate matter (PM) and oxides of nitrogen (NOX) emissions from existing diesel vehicles operating in California.

The regulation requires diesel trucks and buses that operate in California to be upgraded to reduce emissions. Heavier trucks must be retrofitted with PM filters beginning January 1, 2012, and older trucks must be replaced starting January 1, 2015. By January 1, 2023, nearly all trucks and buses would need to have 2010 model year engines or equivalent.

The regulation applies to most privately-owned and federally‐owned diesel fueled trucks and buses and to privately and publicly owned school buses with a gross vehicle weight rating (GVWR) greater than 14,000 pounds. Small fleets with three or fewer diesel trucks can delay compliance for heavier trucks and there are several extensions for low‐mileage construction trucks, early PM filter retrofits, adding cleaner vehicles, and other situations. Privately and publicly owned school buses have different requirements.

Heavy‐Duty Vehicle Idling Emission Reduction Program
The purpose of the CARB ATCM to Limit Diesel‐Fueled Commercial Motor Vehicle Idling is to reduce public exposure to diesel particulate matter and criteria pollutants by limiting the idling of diesel‐fueled commercial vehicles. The driver of any vehicle subject to this ATCM is prohibited from idling the vehicle’s 2 California Air Resources Board, Risk Reduction Plan to Reduce Particulate Matter Emissions from Diesel‐Fueled Engines and Vehicles, October 2000.

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primary diesel engine for greater than five minutes at any location and is prohibited from idling a diesel‐ fueled auxiliary power system (APS) for more than five minutes to power a heater, air conditioner, or any ancillary equipment on the vehicle if it has a sleeper berth and the truck is located within 100 feet of a restricted area (homes and schools).

CARB Final Regulation Order, Requirements to Reduce Idling Emissions from New and In‐Use Trucks, beginning in 2008, would require that new 2008 and subsequent model‐year heavy‐duty diesel engines be equipped with an engine shutdown system that automatically shuts down the engine after 300 seconds of continuous idling operation once the vehicle is stopped, the transmission is set to “neutral” or “park”, and the parking brake is engaged.

CARB 2017 Technical Advisory (Strategies to Reduce Air Pollution Exposure Near High-Volume Roadways)
CARB published a Technical Advisory in 2017 to provide planners and other stakeholders involved in land use planning and decision-making with information on scientifically based strategies to reduce exposure to traffic emissions near high-volume roadways. Near-roadway development is a result of a variety of factors, including economic growth, demand for built environment uses, and the scarcity of developable land in some areas. The Technical Advisory notes that research has demonstrated the public health, climate, financial, and other benefits of compact, infill development along transportation corridors, and demonstrates that planners, developers, and local governments can pursue infill development while simultaneously reducing exposure to traffic-related pollution. On-site strategies to remove air pollution identified in the Technical Advisory include the use of particle filtration systems (i.e., high efficiency filtration in mechanical ventilation systems), solid barriers, and vegetation.

California Energy Commission - Title 24 Building Energy Efficiency Standards The Energy Efficiency Standards for Residential and Nonresidential Buildings, as specified in California Code of Regulations (CCR) Title 24 Part 6, were established in 1978 in response to a legislative mandate to reduce California’s energy consumption. The standards are updated periodically to allow consideration and possible incorporation of new energy efficiency technologies and methods. The 2019 Energy Standards include requirements for mandatory mechanical ventilation intended to improve indoor air quality in homes, and requirements for Minimum Efficiency Reporting Value (MERV) 13 air filtration on space conditioning systems, and ventilation systems that provide outside air to a dwelling’s occupiable space. The Residential Compliance Manual for the 2019 Building Energy Efficiency Standards notes that air filter efficiencies of at least MERV 13 protect occupants from exposure to the smaller airborne particles (i.e., PM2.5) that are known to adversely affect respiratory health. CCR Title 24 Part 6 requires a particle size efficiency rating equal to or greater than 85 percent in the 1.0 to 0.3 µg range.

3.3 Regional
South Coast Air Quality Management District
The CCAA provides the SCAQMD with the authority to manage transportation activities at indirect sources and regulate stationary source emissions. Indirect sources of pollution are generated when minor sources collectively emit a substantial amount of pollution. An example of this would be the motor vehicles at an intersection, a mall, and on highways. As a State agency, CARB regulates motor vehicles and fuels for their emissions.

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City of South El Monte Mye Plaza Project
Health Risk Assessment
March 2021
Page | 10
Air Toxics Control Plan
The Air Toxics Control Plan (March 2000, revised March 26, 2004) is a planning document designed to examine the overall direction of the SCAQMD’s air toxics control program. It includes development and implementation of strategic initiatives to monitor and control air toxics emissions. Control strategies that are deemed viable and are within the SCAQMD’s jurisdiction will each be brought to the SCAQMD Board for further consideration through the normal public review process. Strategies that are to be implemented by other agencies will be developed in a cooperative effort, and the progress will be reported back to the Board periodically.

Multiple Air Toxics Exposure Study
The SCAQMD conducted an in‐depth analysis of the toxic air contaminants and their resulting health risks for all of Southern California. The Multiple Air Toxics Exposure Study (MATES) in the SCAB (MATES IV) shows that cancer risk has decreased more than 50 percent between MATES III (2008) and MATES IV (2015).

MATES IV is the most comprehensive dataset documenting the ambient air toxic levels and health risks associated with the SCAB emissions. Therefore, MATES IV study represents the baseline health risk for a cumulative analysis. MATES IV estimates the average excess cancer risk level from exposure to TACs is less than 400 in one million basin‐wide. These model estimates were based on monitoring data collected at ten fixed sites within the SCAB. None of the fixed monitoring sites are near the project site. However, MATES IV has extrapolated the excess cancer risk levels throughout the SCAB by modeling the specific grids. MATES IV modeling predicted an excess cancer risk of 1,144 in one million for the Project area3.

DPM is included in this cancer risk along with all other TAC sources. DPM accounts for 68 percent of the total risk shown in MATES IV. The SCAQMD is currently preparing MATES V, which will be the latest comprehensive study of levels of toxic air pollutants the region, MATES V will include an advanced monitoring component with a focus on refinery emissions. 3 South Coast Air Quality Management District, MATES IV Estimated Risk, https://scaqmdonline.maps.arcgis.com/apps/webappviewer/index.html?id=470c30bc6daf4ef6a43f0082973ff45f

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