Bellflower City Council
April 27, 2026

City of Bellflower
Bellflower Convenience Center
Exhibit 1: Regional Vicinity
Air Quality Assessment
Source: Google Maps, 2022
November 2025
Kim
ey>»Horn

City of Bellflower
Bellflower Convenience Center
Exhibit 3: Conceptual Site Plan
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Air Quality Assessment
November 2025
Kim
ey>» Horn

City of Bellflower Bellflower Convenience Center
Air Quality Assessment
2 ENVIRONMENTAL SETTING

2.1 Climate and Meteorology
The California Air Resources Board (CARB) divides the State into 15 air basins that share similar meteorological and topographical features.' The Project is located within the South Coast Air Basin (SCAB), which includes the non -desert portions of Los Angeles, Riverside, and San Bernardino counties, as well as all of Orange County. The SCAB is on a coastal plain with connecting broad valleys and low hills, bounded by the Pacific Ocean on the southwest and high mountains forming the remainder of the perimeter2. Air quality in this area is determined by such natural factors as topography, meteorology, and climate, in addition to the presence of existing air pollution sources and ambient conditions. These factors along with applicable regulations are discussed below.

The SCAB is part of a semi -permanent high-pressure zone in the eastern Pacific. As a result, the climate is mild and tempered by cool sea breezes. This usually mild weather pattern is occasionally interrupted by periods of extreme heat, winter storms, and Santa Ana winds. The annual average temperature throughout the 6,645 -square -mile SCAB ranges from low 60 to high 80 degrees Fahrenheit with little variance. With more oceanic influence, coastal areas show less variability in annual minimum and maximum temperatures than inland areas.

Contrasting the steady pattern of temperature, rainfall is seasonally and annually highly variable. Almost all annual rainfall occurs between the months of November and April. Summer rainfall is reduced to widely scattered thundershowers near the coast, with slightly heavier activity in the east and over the mountains.

Although the SCAB has a semiarid climate, the air closer to the Earth's surface is typically moist because of the presence of a shallow marine layer. Except for occasional periods when dry, continental air is brought into the SCAB by offshore winds, the "ocean effect" is dominant. Periods of heavy fog are frequent and low clouds known as high fog are characteristic climatic features, especially along the coast.

Annual average humidity is 70 percent at the coast and 57 percent in the eastern portions of the SCAB.

Wind patterns across the SCAB are characterized by westerly or southwesterly on -shore winds during the day and easterly or northeasterly breezes at night. Wind speed is typically higher during the dry summer months than during the rainy winter. Between periods of wind, air stagnation may occur in both the morning and evening hours. Air stagnation is one of the critical determinants of air quality conditions on any given day. During winter and fall, surface high-pressure systems over the SCAB, combined with other meteorological conditions, result in very strong, downslope Santa Ana winds. These winds normally continue for a few days before predominant meteorological conditions are reestablished.' The mountain ranges to the east affect the diffusion of pollutants by inhibiting the eastward transport of pollutants. Air quality in the SCAB generally ranges from fair to poor and is similar to air quality in most of coastal Southern California. The entire region experiences heavy concentrations of air pollutants during prolonged periods of stable atmospheric conditions.

South Coast Air Quality Management District, 2022 Air Quality Management Plan, December 2022, https://www.aq md.gov/dots/defa uIt-sou rce/clean-ai r-plans/ai r-qual ity-management-plans/2022-a ir-quality-management- plan/final-2022-aqmp/final-2022-aqmp.pdf?sfvrsn=16, accessed November 6, 2025. 2 South Coast Air Quality Management District, CEQA Air Quality Handbook, 1993. 3 California Air Resources Board, Almanac Resources, 2024, https://ww2.arb.ca.gov/resources/documents/almanac-resources , accessed November 6, 2025.

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Kimley>»Horn

City of Bellflower Bellflower Convenience Center
Air Quality Assessment
In addition to the characteristic wind patterns that affect the rate and orientation of horizontal pollutant transport, two distinct types of temperature inversions control the vertical depth through which air pollutants are mixed. These inversions are the marine inversion and the radiation inversion. The height of the base of the inversion at any given time is called the "mixing height."4 The combination of winds and inversions is a critical determinant leading to highly degraded air quality for the SCAB in the summer and generally good air quality in the winter.

12.2 Air Pollutants of Concern
The air pollutants emitted into the ambient air by stationary and mobile sources are regulated by state and federal laws. These regulated air pollutants are known as "criteria air pollutants" and are categorized into primary and secondary pollutants.

Primary air pollutants are emitted directly from sources. Carbon monoxide (CO), reactive organic gases (ROG), nitrogen oxide (NOx), sulfur dioxide (S02), coarse particulate matter (PN/110), fine particulate matter (PM2.5), and lead are primary air pollutants. Of these, CO, NOx, S02, PM1o, and PM2.5 are criteria pollutants.' ROG and NOx are criteria pollutant precursors and form secondary criteria pollutants through chemical and photochemical reactions in the atmosphere.' For example, the criteria pollutant ozone (03) is formed by a chemical reaction between ROG and NOx in the presence of sunlight. 03 and nitrogen dioxide (NO2) are the principal secondary pollutants. Sources and health effects commonly associated with criteria pollutants are summarized in Table 1: Air Contaminants and Associated Public Health Concerns.

Table 1: Air Contaminants and Associated Public Health Concerns Pollutant
Major Man -Made Sources
Human Health Effects
Particulate Matter
(PM10 and PM2.5)
Power plants, steel mills, chemical plants,
unpaved roads and parking lots, wood-
burning stoves and fireplaces, automobiles
and others.

Increased respiratory symptoms, such as
irritation of the airways, coughing, or difficulty
breathing; asthma; chronic bronchitis; irregular
heartbeat; nonfatal heart attacks; and
premature death in people with heart or lung
disease. Impairs visibility.

Ozone (O3)
Formed by a chemical reaction between
reactive organic gases/volatile organic
compounds (ROG or VOC)1 and nitrogen
oxides (NOx) in the presence of sunlight.

Motor vehicle exhaust industrial emissions,
gasoline storage and transport, solvents,
paints and landfills.

Irritates and causes inflammation of the
mucous membranes and lung airways; causes
wheezing, coughing, and pain when inhaling
deeply; decreases lung capacity; aggravates
lung and heart problems. Damages plants;
reduces crop yield.

Sulfur Dioxide (SO2)
A colorless gas formed when fuel containing
sulfur is burned and when gasoline is
extracted from oil. Examples are petroleum
refineries, cement manufacturing, metal
processing facilities, locomotives, and ships.

Respiratory irritant. Aggravates lung and heart
problems. In the presence of moisture and
oxygen, sulfur dioxide converts to sulfuric acid
which can damage marble, iron and steel.

Damages crops and natural vegetation. Impairs
visibility. Precursor to acid rain.

Carbon Monoxide (CO)
An odorless, colorless gas formed when
carbon in fuel is not burned completely; a
component of motor vehicle exhaust.

Reduces the ability of blood to deliver oxygen
to vital tissues, affecting the cardiovascular and
nervous system. Impairs vision, causes
4 South Coast Air Quality Management District, Final 2016 Air Quality Management Plan, March 2017 5 U.S. Environmental Protection Agency, Criteria Air Pollutants, https://www.epa.gov/criteria-air-pollutants , accessed November 6, 2025.
6 Ibid.

November 2025
Kimley>»Horn

City of Bellflower
Bellflower Convenience Center
Air Quality Assessment
Table 1: Air Contaminants and Associated Public Health Concerns Pollutant
Major Man -Made Sources
Human Health Effects
dizziness, and can lead to unconsciousness or
death.

Nitrogen Dioxide (NO2)
A reddish -brown gas formed during fuel
combustion for motor vehicles and
industrial sources. Sources include motor
vehicles, electric utilities, and other sources
that burn fuel.

Respiratory irritant; aggravates lung and heart
problems. Precursor to O3. Contributes to
global warming and nutrient overloading which
deteriorates water quality. Causes brown
discoloration of the atmosphere.

Lead (Pb)
Lead is a metal found naturally in the
environment as well as in manufactured
products. The major sources of lead
emissions have historically been motor
vehicles (such as cars and trucks) and
industrial sources. Due to the phase out of
leaded gasoline, metals processing is the
major source of lead emissions to the air
today. The highest levels of lead in air are
generally found near lead smelters. Other
stationary sources are waste incinerators,
utilities, and lead -acid battery
manufacturers.

Exposure to lead occurs mainly through
inhalation of air and ingestion of lead in food,
water, soil, or dust. It accumulates in the blood,
bones, and soft tissues and can adversely affect
the kidneys, liver, nervous system, and other
organs. Excessive exposure to lead may cause
neurological impairments such as seizures,
mental retardation, and behavioral disorders.

Even at low doses, lead exposure is associated
with damage to the nervous systems of fetuses
and young children, resulting in learning
deficits and lowered IQ.

Notes:

1. Volatile Organic Compounds (VOCs or Reactive Organic Gases [ROG]) are hydrocarbons/organic gases that are formed solely of hydrogen and carbon. There are several subsets of organic gases including ROGs and VOCs. Both ROGs and VOCs are emitted from the incomplete combustion of hydrocarbons or other carbon -based fuels. The major sources of hydrocarbons are combustion engine exhaust, oil refineries, and oil -fueled power plants; other common sources are petroleum fuels, solvents, dry cleaning solutions, and paint (via evaporation).

Source: U.S. Environmental Protection Agency, Criteria Air Pollutants, https://www.epa.gov/criteria-air-pollutants , accessed November 6, 2025.

Toxic Air Contaminants
Toxic air contaminants (TACs) are airborne substances that can cause short-term (acute) or long-term (i.e., chronic, carcinogenic or 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 more than 200 compounds, including particulate emissions from diesel -fueled engines.'
CARB identified diesel particulate matter (DPM) as a toxic air contaminant. DPM differs from other TACs in that it is not a single substance but rather a complex mixture of hundreds of substances. Diesel exhaust is a complex mixture of particles and gases produced when an engine burns diesel fuel. DPM is a concern because it causes lung cancer; many compounds found in diesel exhaust are carcinogenic. DPM includes the particle -phase constituents in diesel exhaust. The chemical composition and particle sizes of DPM vary between different engine types (heavy-duty, light -duty), engine operating conditions (idle, accelerate, decelerate), fuel formulations (high/low sulfur fuel), and the year of the engine. Some short-term (acute) effects of diesel exhaust include eye, nose, throat, and lung irritation, and diesel exhaust can cause coughs, headaches, light-headedness, and nausea. DPM poses the greatest health risk among the TACs. ' California Air Resources Board, Common Air Pollutants, 2024, https://ww2.arb.ca.gov/resources/common-air-pollutants , accessed November 6, 2025.

November 2025
Kimley>»Horn

City of Bellflower Bellflower Convenience Center
Air Quality Assessment
Almost all diesel exhaust particle mass is 10 microns or less in diameter. Due to their extremely small size, these particles can be inhaled and eventually trapped in the bronchial and alveolar regions of the lung.8 Ambient Air Quality
CARB monitors ambient air quality at approximately 250 air monitoring stations across the State. These stations usually measure pollutant concentrations ten feet above ground level; therefore, air quality is often referred to in terms of ground -level concentrations. Existing levels of ambient air quality, historical trends, and projections near the Project are documented by measurements made by the South Coast Air Quality Management District (SCAQMD), the air pollution regulatory agency in the SCAB that maintains air quality monitoring stations which process ambient air quality measurements.

Pollutants of concern in the SCAB include O3, Milo, and PM2.5. The closest air monitoring station to the Project that monitors ambient concentrations of these pollutants is the Compton Monitoring Station (located approximately 5 miles to the northwest). Local air quality data from 2022 to 2024 are provided in Table 2: Ambient Air Quality Data, which lists the monitored maximum concentrations and number of exceedances of state or federal air quality standards for each year.

Table 2: Ambient Air Quality Data
Criteria Pollutant
2022
2023
2024
Ozone (O3)1
1 -hour Maximum Concentration (ppm)

0.111

0.084

0.087
8 -hour Maximum Concentration (ppm)

0.085

0.071

0.064
Number of Days Standard Exceeded
CAAQS 1 -hour (>0.09 ppm)
1 2
0 NAAQS 8 -hour (>0.070 ppm)
1 1
0 Carbon Monoxide (CO)'
1 -hour Maximum Concentration (ppm)

3.44 3.16

3.51 Number of Days Standard Exceeded
NAAQS 1 -hour (>35 ppm)
0 0
0 CAAQS 1 -hour (>20 ppm)
0 0
0 Nitrogen Dioxide (NO2)1
1 -hour Maximum Concentration (ppm)

0.065

0.053

0.061
Number of Days Standard Exceeded
NAAQS 1 -hour (>.100 ppm)
0 0
0 CAAQS 1 -hour (>0.18 ppm)
0 0
0 Particulate Matter Less Than 10 Microns (PM1o)1
National 24 -hour Maximum Concentration
—
—
—
State 24 -hour Maximum Concentration
—
—
—
State Annual Average Concentration (CAAQS=20 µg/m3)
—
—
—
Number of Days Standard Exceeded
NAAQS 24 -hour (>150 µg/m3)
—
—
—
CAAQS 24 -hour (>50 µg/m3)
—
—
—
Particulate Matter Less Than 2.5 Microns (PMz.5)1
National 24 -hour Maximum Concentration

52.8 54.6

57.4 State 24 -hour Maximum Concentration

54.6 54.6

57.4 Number of Days Standard Exceeded
NAAQS 24 -hour (>35 µg/m3)
—
—
—
NAAQS = National Ambient Air Quality Standards; CAAQS = California Ambient Air Quality Standards; ppm = parts per million; 8 California Air Resources Board, Overview: Diesel Exhaust & Health, https://ww2.arb.ca.gov/resources/overview-diesel- exhaust-and-health, accessed November 6, 2025.

November 2025
Kimley>>Horn

City of Bellflower
Bellflower Convenience Center
Air Quality Assessment
µg/m3 = micrograms per cubic meter; — = not measured
Notes:

1. Measurements taken at the Compton Monitoring Station (ARB# 70112) at 700 N. Bullis Road, Compton, CA 90221 Source: All pollutant measurements are from the CARB Aerometric Data Analysis and Management system database ( https://www.arb.ca.gov/adam) except for CO, which were retrieved from the CARB Air Quality and Meteorological Information System ( https://www.arb.ca.gov/qaweb/siteinfo . ph p).

2.3 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. Sensitive land uses surrounding the Project consist mostly of residential communities. Table 3: Sensitive Receptors lists the distances and locations of nearby sensitive receptors.

Table 3: Sensitive Receptors
Receptor Description
Distance and Direction from the Project Site
Multi -family residential
Adjacent to the west
Multi -family residential
35 feet south
Single-family residential
90 feet northwest
Ramona Senior Center
480 feet northeast
Grace Filipino Christian Church
700 feet west
BellOne Christian Reformed Church
850 feet east
Bellflower Senior Center
885 feet east
Kingdom Hall of Jehovah's Witnesses
950 feet east
Thomas Jefferson Elementary School
1300 feet southeast

1. Distance measured from the Project site property line to the nearest sensitive receptor property line.

Source: Google Earth, 2025.

November 2025
Kimley>»Horn

City of Bellflower Bellflower Convenience Center
Air Quality Assessment
3 REGULATORY SETTING

3.1 Federal
Federal Clean Air Act
Air quality is federally protected by the Federal Clean Air Act (FCAA) and its amendments. Under the FCAA, the United States Environmental Protection Agency (EPA) developed the primary and secondary National Ambient Air Quality Standards (NAAQS) for the criteria air pollutants including O3, NO2, CO, SO2, PN/110, PM25, and lead. Proposed projects in or near nonattainment areas could be subject to more stringent air - permitting requirements. The FCAA requires each state to prepare a State Implementation Plan to demonstrate how it will attain the NAAQS within the federally imposed deadlines.

The EPA can withhold certain transportation funds from states that fail to comply with the planning requirements of the FCAA. If a state fails to correct these planning deficiencies within two years of Federal notification, the EPA is required to develop a Federal implementation plan for the identified nonattainment area or areas. The provisions of 40 Code of Federal Regulations Parts 51 and 93 apply in all nonattainment and maintenance areas for transportation -related criteria pollutants for which the area is designated nonattainment or has a maintenance plan. The EPA has designated enforcement of air pollution control regulations to the individual states. Applicable federal standards are summarized in Table 4: State and Federal Ambient Air Quality Standards.

Table 4: State and Federal Ambient Air Quality Standards Pollutant
Averaging Time
State Standards1'2
Federal Standards3.4,5
Ozone (O3) 6
8 Hour

0.070 ppm (137 µg/m3)

0.070 ppm
1 Hour

0.09 ppm (180 µg/m3)
NA
Particulate Matter (PM1°)'
24 -Hour
50 µg/m3
150 µg/m3
Annual Arithmetic Mean
20 µg/m3
NA
Fine Particulate Matter (PMz.$)'
24 -Hour
NA
35 µg/m3
Annual Arithmetic Mean
12 µg/m3
9µg/m3
Carbon Monoxide (CO)
8 Hour

9.0 ppm (10 mg/m3)
9 ppm (10 mg/m3)
1 Hour
20 ppm (23 mg/m3)
35 ppm (40 mg/m3)
Nitrogen Dioxide (NO2)$
1 Hour

0.18 ppm (339 µg/m3)

0.10 ppm"
Annual Arithmetic Mean

0.030 ppm (57 µg/m3)

0.053 ppm (100 µg/m3)
Sulfur Dioxide (SO2) 9
24 Hour

0.04 ppm (105 µg/m3)

0.14 ppm (365 µg/m3)
1 Hour

0.25 ppm (655 µg/m3)

0.075 ppm (196 µg/m3)
Annual Arithmetic Mean
NA

0.03 ppm (80 µg/m3)
Sulfates (SO4-2)
24 Hour
25 µg/m3
NA
Lead (Pb)1°, 11
30 -Day Average
L5 µg/m3
NA
Calendar Quarter
NA

1.5 µg/m3
Rolling 3 -Month Average
NA

0.15 µg/m3
Hydrogen Sulfide (H2S)
1 Hour

0.03 ppm (0.42 µg/m3)
NA
Vinyl Chloride (C2H3CI) 1°
24 Hour

0.01 ppm (26 µg/m3)
NA
ppm = parts per million; µg/m3= micrograms per cubic meter; mg/m3= milligrams per cubic meter; — = no information available.

Notes:

1. California standards for O3, carbon monoxide (except Lake Tahoe), sulfur dioxide (1 -hour and 24 -hour), nitrogen dioxide, suspended particulate matter (PMio, PM2.s, and visibility reducing particles), are values that are not to be exceeded. All others are not to be equaled or exceeded. California ambient air quality standards are listed in the Table of Standards in Section 70200 of Title 17 of the California Code of Regulations.

2. Concentration expressed first in units in which it was promulgated. Equivalent units given in parentheses are based upon a reference temperature of 25°C and a reference pressure of 760 torr. Most measurements of air quality are to be corrected to a reference temperature of 25°C and a reference pressure of 760 torr; ppm in this table refers to ppm by volume, or micromoles of pollutant per mole of gas.

November 2025
Kimley>»Horn

City of Bellflower
Bellflower Convenience Center
Air Quality Assessment
Table 4: State and Federal Ambient Air Quality Standards Pollutant
Averaging Time
State Standards1'2
Federal Standards3,4,s

3. National standards (other than ozone, particulate matter, and those based on annual arithmetic mean) are not to be exceeded more than once a year. The ozone standard is attained when the fourth highest 8 -hour concentration measured at each site in a year, averaged over three years, is equal to or less than the standard. For PM10, the 24 hour standard is attained when the expected number of days per calendar year with a 24 -hour average concentration above 150 µg/m3 is equal to or less than one. For PM2.5, the 24 hour standard is attained when 98 percent of the daily concentrations, averaged over three years, are equal to or less than the standard. Contact the U.S. EPA for further clarification and current national policies. 4. National Primary Standards: The levels of air quality necessary, with an adequate margin of safety to protect the public health.

5. On October 1, 2015, the national 8 -hour ozone primary and secondary standards were lowered from 0.075 to 0.070 ppm.

6. On February 7, 2024, the national annual PM2.5 primary standard was lowered from 12.0 µg/m3 to 9.0 µg/m3. The existing national 24 -hour PM2.5 standards (primary and secondary) were retained at 35 µg/m3, as was the annual secondary standard of 15.0 µg/m3. The existing 24 -hour PM10 standards (primary and secondary) of 150 µg/m3 also were retained. The form of the annual primary and secondary standards is the annual mean, averaged over 3 years.

7. To attain the 1 -hour national standard, the 3 -year average of the annual 98th percentile of the 1 -hour daily maximum concentrations at each site must not exceed 100 ppb. Note that the national 1 -hour standard is in units of parts per billion (ppb). California standards are in units of parts per million (ppm). To directly compare the national 1 -hour standard to the California standards the units can be converted from ppb to ppm. In this case, the national standard of 100 ppb is identical to 0.100 ppm.

8. On June 2, 2010, a new 1 -hour SO2 standard was established and the existing 24 -hour and annual primary standards were revoked. To attain the 1 -hour national standard, the 3 -year average of the annual 99th percentile of the 1 -hour daily maximum concentrations at each site must not exceed 75 ppb. The 1971 SO2 national standards (24 -hour and annual) remain in effect until one year after an area is designated for the 2010 standard, except that in areas designated nonattainment for the 1971 standards, the 1971 standards remain in effect until implementation plans to attain or maintain the 2010 standards are approved. Note that the 1 -hour standard is in units of parts per billion (ppb). California standards are in units of parts per million (ppm). To directly compare the 1 -hour standard to the California standard the units can be converted to ppm. In this case, the national standard of 75 ppb is identical to 0.075 ppm.

9. The ARB has identified lead and vinyl chloride as "toxic air contaminants" with no threshold level of exposure for adverse health effects determined.

These actions allow for the implementation of control measures at levels below the ambient concentrations specified for these pollutants.

10. The national standard for lead was revised on October 15, 2008 to a rolling 3 -month average. The 1978 lead standard (1.5 µg/m3 as a quarterly average) remains in effect until one year after an area is designated for the 2008 standard, except that in areas designated nonattainment for the 1978 standard, the 1978 standard remains in effect until implementation plans to attain or maintain the 2008 standard are approved. 11. In 1989, the ARB converted both the general statewide 10 -mile visibility standard and the Lake Tahoe 30 -mile visibility standard to instrumental equivalents, which are "extinction of 0.23 per kilometer" and "extinction of 0.07 per kilometer" for the statewide and Lake Tahoe Air Basin standards, respectively.

Source: South Coast Air Quality Management District, Table of Air Quality Standards, July 2024, https://ww2.arb.ca.gov/sites/default/files/2024- 08/AAQS%20Table_ADA_FINAL_07222024.pdf, accessed November 6, 2025.

3.2 State of California
California Air Resources Board
CARB administers the air quality policy in California. The California Ambient Air Quality Standards (CAAQS) were established in 1969 pursuant to the Mulford -Carrell Act. These standards, included with the NAAQS in Table 4, are generally more stringent and apply to more pollutants than the NAAQS. In addition to the criteria pollutants, CAAQS have been established for visibility reducing particulates, hydrogen sulfide, and sulfates.9
The California Clean Air Act (CCAA), which was approved in 1988, requires that each local air district prepare and maintain an Air Quality Management Plan (AQMP) to achieve compliance with CAAQS.

These AQMPs also serve as the basis for the preparation of the State Implementation Plan for meeting federal clean air standards for the State of California.10 Like the EPA, CARB also designates areas within California as either attainment or nonattainment for each criteria pollutant based on whether the CAAQS have been achieved. Under the CCAA, areas are designated as nonattainment for a pollutant if air quality data shows that a state standard for the pollutant was violated at least once during the 9 California Air Resources Board, California Ambient Air Quality Standards, https://ww2.arb.ca.gov/resources/california- ambient-air-quality-standards, accessed November 6, 2025. 1° South Coast Air Quality Management District, Final 2016 Air Quality Management Plan, March 2017, https://www.aq md.gov/dots/defa uIt-sou rce/clean-ai r-plans/ai r-qual ity-management-plans/2016-a ir-quality-management- plan/final-2016-aqmp/final2016agmp.pdf?sfvrsn=15, accessed November 6, 2025.

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City of Bellflower Bellflower Convenience Center
Air Quality Assessment
previous three calendar years. Exceedances that are affected by highly irregular or infrequent events such as wildfires, volcanoes, etc. are not considered violations of a state standard, and are not used as a basis for designating areas as nonattainment. The applicable State standards are summarized in Table 4.

3.3 Regional
South Coast Air Quality Management District
The SCAQMD is the air pollution control agency for Orange County and the urban portions of Los Angeles, Riverside, and San Bernardino Counties. The agency's primary responsibility is ensuring that state and federal ambient air quality standards are attained and maintained in the SCAB. The SCAQMD is also responsible for adopting and enforcing rules and regulations concerning air pollutant sources, issuing permits for stationary sources of air pollutants, inspecting stationary sources of air pollutants, responding to citizen complaints, monitoring ambient air quality and meteorological conditions, awarding grants to reduce motor vehicle emissions, conducting public education campaigns, and many other activities. All projects are subject to SCAQMD rules and regulations in effect at the time of construction.

The SCAQMD is also the lead agency in charge of developing the AQMP, with input from the Southern California Association of Governments (SCAG) and CARB. The AQMP is a comprehensive plan that includes control strategies for stationary and area sources, as well as for on -road and off -road mobile sources.

SCAG has the primary responsibility for providing future growth projections and the development and implementation of transportation control measures. CARB, in coordination with federal agencies, provides the control element for mobile sources.

The 2016 AQMP was adopted by the SCAQMD Governing Board on March 3, 2017.11 The purpose of the 2016 AQMP is to set forth a comprehensive and integrated program that would lead the SCAB into compliance with those NAAQS for which the basin is in nonattainment (i.e., the federal 24 -hour PM2.5 air quality standard), and to provide an update to the SCAQMD's commitments towards meeting the federal 8 -hour O3 standards. The 2016 AQMP incorporated the latest scientific and technological information and planning assumptions, including the 2016-2040 Regional Transportation Plan/Sustainable Communities Strategy (RTP/SCS) and updated emission inventory methodologies for various source categories.12 On October 1, 2015, the U.S. EPA strengthened the NAAQS for ground -level O3. The 2022 AQMP, adopted by the SCAQMD Governing Board on December 2, 2022, was developed to address the strengthened requirements for meeting the 2015 ground -level 8 -hour O3 standard.13 The 2022 AQMP builds upon measures already in place from previous AQMPs. It also includes a variety of additional strategies such as regulation, accelerated deployment of available cleaner technologies (e.g., zero emissions technologies, when cost-effective and feasible, and low NOx technologies in other applications), best management practices, co -benefits from existing programs (e.g., climate and energy efficiency), incentives, and other FCAA measures to achieve the 2015 8 -hour ozone standard. Like earlier AQMPs, the 2022 AQMP 11 Ibid.
12 Southern California Association of Governments, Connect SoCal (2020-2045 RTP/SCS), Demographics and Growth Forecast adopted September 2020, https://scag.ca.gov/sites/main/files/file-attachments/0903fconnectsocal_demographics-and- growth-forecast.pdf? 1606001579, accessed November 6, 2025. 13 South Coast Air Quality Management District, 2022 Air Quality Management Plan, December 2022, https://www.aq md.gov/dots/defa uIt-sou rce/clean-ai r-plans/ai r-qual ity-management-plans/2022-a ir-quality-management- plan/final-2022-aqmp/final-2022-aqmp.pdf?sfvrsn=16, accessed November 6, 2025.

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City of Bellflower Bellflower Convenience Center
Air Quality Assessment
incorporates the latest scientific and technological information and planning assumptions, including the 2020-2045 RTP/SCS and updated emission inventory methodologies for various source categories.l4 The SCAQMD has published the CEQA Air Quality Handbook (approved by the SCAQMD Governing Board in 1993 and augmented with guidance for Local Significance Thresholds [LST] in 2008).15 The SCAQMD guidance helps local government agencies and consultants to develop environmental documents required by California Environmental Quality Act (CEQA) and provides identification of suggested thresholds of significance for criteria pollutants for both construction and operation (see discussion of thresholds below). With the help of the CEQA Air Quality Handbook and associated guidance, local land use planners and consultants are able to analyze and document how proposed and existing projects affect air quality in order to meet the requirements of the CEQA review process. The SCAQMD periodically provides supplemental guidance and updates to the handbook on their website.

The SCAG is the regional planning agency for Los Angeles, Orange, Ventura, Riverside, San Bernardino, and Imperial Counties and serves as a forum for regional issues relating to transportation, the economy, community development, and the environment. Under federal law, SCAG is designated as a Metropolitan Planning Organization and under State law as a Regional Transportation Planning Agency and a Council of Governments.

The state and federal attainment status designations for the SCAB are summarized in Table 5: South Coast Air Basin Attainment Status. The SCAB is currently designated as a nonattainment area with respect to the State O3, PM10, and PM2.5 standards, as well as the national 8 -hour O3 and PM2.5 standards. The SCAB is designated as attainment or unclassified for the remaining state and federal standards.

Table 5: South Coast Air Basin Attainment Status
Pollutant
State
Federal
Ozone (O3)
(1 Hour Standard)
Non -Attainment
Non -Attainment (Extreme)
Ozone (O3)
(8 Hour Standard)
Non -Attainment
Non -Attainment (Extreme)
Particulate Matter (PM2.5)
(24 Hour Standard)
_
Non -Attainment (Serious)
Particulate Matter (PM2.5)
(Annual Standard)
Non -Attainment
Non -Attainment (Moderate)
Particulate Matter (PM1o)
(24 Hour Standard)
Non -Attainment
Attainment (Maintenance)
Particulate Matter (PM1o)
(Annual Standard)
Non -Attainment
—
Carbon Monoxide (CO)
(1 Hour Standard)
Attainment
Attainment (Maintenance)
Carbon Monoxide (CO)
(8 Hour Standard)
Attainment
Attainment (Maintenance)
Nitrogen Dioxide (NO2)
(1 Hour Standard)
Attainment
Unclassifiable/Attainment
14 Southern California Association of Governments, Connect SoCal (2020-2045 RTP/SCS), Demographics and Growth Forecast adopted September 2020, https://scag.ca.gov/sites/main/files/file-attachments/0903fconnectsocal_demographics-and- growth-forecast.pdf? 1606001579, accessed November 6, 2025. 15 South Coast Air Quality Management District, Final Localized Significance Threshold Methodology, July 2008, https://www.ag md.gov/home/ru les-comp) fiance/cega/ai r-qual ity-analysis-handbook/local ized-significance-thresholds, accessed November 6, 2025.

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Air Quality Assessment
Table 5: South Coast Air Basin Attainment Status
Pollutant
State
Federal
Nitrogen Dioxide (NO2)
(Annual Standard)
Attainment
Attainment (Maintenance)
Sulfur Dioxide (SO2)
(1 Hour Standard)
Attainment
Unclassifiable/Attainment
Sulfur Dioxide (SO2)
(24 Hour Standard)
Attainment
—
Lead (Pb)
(30 Day standard)
—
Unclassifiable/Attainment
Lead (Pb)
(3 Month Standard)
Attainment
Nonattainment (Partial)
Sulfates (SO4-z)
(24 Hour Standard)
Attainment
—
Hydrogen Sulfide (H2S)
(1 Hour Standard)
Unclassified
—
Source: South Coast Air Quality Management District, Air Quality Management Plan, 2016; United States Environmental Protection Agency, Nonattainment Areas for Criteria Pollutants (Green Book), 2018.

The following is a list of SCAQMD rules that are required of construction activities associated with the Project:
• Rule 402 (Nuisance) — This rule prohibits the discharge from any source whatsoever such quantities of air contaminants or other material which cause injury, detriment, nuisance, or annoyance to any considerable number of persons or to the public, or which endanger the comfort, repose, health, or safety of any such persons or the public, or which cause, or have a natural tendency to cause, injury or damage to business or property. This rule does not apply to odors emanating from agricultural operations necessary for the growing of crops or the raising of fowl or animals.
• Rule 403 (Fugitive Dust) — This rule requires fugitive dust sources to implement best available control measures for all sources, and all forms of visible particulate matter are prohibited from crossing any property line. This rule is intended to reduce PM10 emissions from any transportation, handling, construction, or storage activity that has the potential to generate fugitive dust. PM10 suppression techniques are summarized below.
a) Portions of a construction site to remain inactive longer than a period of three months will be seeded and watered until grass cover is grown or otherwise stabilized. b) All on -site roads will be paved as soon as feasible or watered periodically or chemically stabilized.
c) All material transported off -site will be either sufficiently watered or securely covered to prevent excessive amounts of dust.
d) The area disturbed by clearing, grading, earthmoving, or excavation operations will be minimized at all times.
e) Where vehicles leave a construction site and enter adjacent public streets, the streets will be swept daily or washed down at the end of the work day to remove soil tracked onto the paved surface.

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• Rule 1113 (Architectural Coatings) — This rule requires manufacturers, distributors, and end users of architectural and industrial maintenance coatings to reduce ROG emissions from the use of these coatings, primarily by placing limits on the ROG content of various coating categories.

3.4 Local
City of Bellflower General Plan
The Conservation Element of the City's General Plan identifies goals that will result in a healthier city.

Goals and policies that relate to air quality impacts include the following:

Goal 2: Improve air quality.

Policy 2.2: Encourage increased vehicle occupancy and carpooling. Provide attractive walkways and bike paths. Improve traffic monitoring and metering systems.

Policy 2.3: Actively participate in regional and local governmental efforts to improve air quality.

Policy 2.5: Encourage the creation of alternate fuel and energy regeneration stations and repair facilities within the city.

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4 SIGNIFICANCE CRITERIA AND METHODOLOGY

4.1 Air Quality Thresholds
Based upon the criteria derived from Appendix G of the CEQA Guidelines, a Project normally would have a significant effect on the environment if it would:
• Conflict with or obstruct implementation of the applicable air quality plan. • Result in a cumulatively considerable net increase of any criteria pollutant for which the project region is in nonattainment under an applicable state or federal ambient air quality standard. • Expose sensitive receptors to substantial pollutant concentrations. • Result in other emissions (such as those leading to odors) adversely affecting a substantial number of people.

SCAQMD Thresholds
According to the CEQA Appendix G, an air quality impact is considered significant if the Project would violate any ambient air quality standard, contribute substantially to an existing or projected air quality violation, or expose sensitive receptors to substantial pollutant concentrations. The SCAQMD has established thresholds of significance for criteria pollutant and precursor pollutants (i.e., ROG and NOx) emissions during construction and operational activities of land use development projects, as shown in Table 6: South Coast Air Quality Management District Emissions Thresholds.

Table 6: South Coast Air Quality Management District Emissions Thresholds Criteria Air Pollutants and Precursors
Maximum Pounds Per Day
Construction -Related
Operational -Related
Reactive Organic Gases (ROG)
75 55
Carbon Monoxide (CO)
550
550
Nitrogen Oxides (NOX)
100
55 Sulfur Oxides (SOX)
150
150
Coarse Particulates (PM1o)
150
150
Fine Particulates (PM2.5)
55 55
Source: South Coast Air Quality Management District, South Coast AQMD Air Quality Significance Thresholds, March 2023.

Localized Carbon Monoxide
In addition to the daily thresholds listed above, development associated with the Project would also be subject to the ambient air quality standards. These are addressed though an analysis of localized CO impacts known as the CO "hot spots" analysis. An analysis of CO "hot spots" determines whether the change in the level of service (LOS) of an intersection as a result of Project activities would have the potential to result in exceedances of the CAAQS or NAAQS. It has long been recognized that one of the greatest contributors of CO to outdoor air is cars.16 Vehicle emissions standards have become increasingly stringent in the last 20 years. Currently, the CO standard in California is a maximum of 3.4 grams per mile 16 U.S. Environmental Protection Agency, Basic Information about Carbon Monoxide (CO) Outdoor Air Pollution, 2023, https://www.epa.gov/co-pollution/basic-information-about-carbon-monoxide-co-outdoor-air-pollution , accessed November 6, 2025.

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for passenger cars (requirements for certain vehicles are more stringent).17 With the turnover of older vehicles, introduction of cleaner fuels, and implementation of control technology on industrial facilities, CO concentrations have steadily declined.'8''
Accordingly, with steadily decreasing CO emissions from vehicles, even very busy intersections do not result in exceedances of the CO standard. An analysis prepared for CO attainment in the SCAB by the SCAQMD is useful for current evaluations of the potential for CO exceedances. CO attainment was thoroughly analyzed as part of the SCAQMD's 2003 Air Quality Management Plan.20 Considering the region's unique meteorological conditions and the increasingly stringent CO emissions standards, CO modeling was performed as part of air quality management plans. The SCAB was re -designated as attainment (as reported in Error! Reference source not found. above) in 2007 and CO is no longer a ddressed in the SCAQMD's Air Quality Management Plan (AQMP).

The 2003 Air Quality Management Plan is the most recent AQMP that addressed CO concentrations. As part of the 2003 AQMP CO Modeling Attainment Demonstration, an analysis was performed utilizing dispersion modeling.21 As an initial screening step, if a project roadway segment does not exceed and ADT of 100,000 per day, then the project does not need to prepare a detailed CO hot spot analysis.

Localized Significance Thresholds
In addition to the CO hotspot analysis, the SCAQMD developed LSTs for emissions of NO2, CO, PM10, and PM2.sgenerated at new development sites (off -site mobile source emissions are not included in the LST analysis). LSTs represent the maximum emissions that can be generated at a project without expecting to cause or substantially contribute to an exceedance of the most stringent state or federal ambient air quality standards. LSTs are based on the ambient concentrations of that pollutant within the Project source receptor area (SRA), as demarcated by the SCAQMD, and the distance to the nearest sensitive receptor. LST analysis for construction is applicable for all projects that disturb 5 acres or less on a single day. The City of Bellflower is located within SCAQMD SRA 5 (Southeast LA County). Table 7: Local Significance Thresholds for Construction/Operations, shows the LSTs for a 1 -acre, 2 -acre, and 5 -acre project in SRA 5 with sensitive receptors located within 25 meters of the Project site. LSTs associated with all acreage categories are provided in Table 7 for informational purposes. Table 7 shows that the LSTs increase as acreages increase. It should be noted that LSTs are screening thresholds and are therefore conservative. The construction LST acreage is determined based daily acreage disturbed. The operational LST acreage is based on the total area of the Project site. Although the Project site is greater than 3.5 acres, the 3 -acre operational LSTs are conservatively used to evaluate the Project. 17 California Code of Regulations Section 1961, Exhaust Emission Standards and Test Procedures — 2004 through 2019 Model Passenger Cars, Light -Duty Trucks, and Medium -Duty Vehicles, 2022, https://ww2.arb.ca.gov/sites/default/files/2023- 02/cleancomplete_lev ghg_regs_11_2022.pdf, accessed November 6, 2025. 18 South Coast Air Quality Management District, Carbon Monoxide Redesignation Request and Maintenance Plan, February 2005, https://ww2.arb.ca.gov/sites/default/files/classic/planning/sip/sccosip05/sccosip_redesig_mplan.pdf , accessed November 6, 2025.
19 U.S. Environmental Protection Agency, Carbon Monoxide Trends, 2023, https://www.epa.gov/air-trends/carbon-monoxide- trends, accessed November 6, 2025.
20 South Coast Air Quality Management District, Air Quality Management Plan, Appendix V, Modeling and Attainment Demonstrations, August 2003, https://www.agmd.gov/home/air-quality/air-quality-management-plans/air-quality-mgt- plan/2003-aqmp, accessed November 6, 2025.
21 Ibid.

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Table 7: Local Significance Thresholds for Construction/Operations Project Size
Maximum Pounds Per Day
Nitrogen Oxide
(NO.)
Carbon Monoxide
(CO)
Coarse Particulates
(PMio)
Fine Particulates
(PM2.5)
1 Acre
80/80
571/571
4/1
3/1
2 Acres
114/114
861/861
7/2
4/1
5 Acres
172/172
1,480/1,480
14/4
7/2
Source: South Coast Air Quality Management District, Localized Significance Threshold Methodology, July 2008.

4.2 Methodology
This air quality impact analysis considers construction and operational impacts associated with the Project. Where criteria air pollutant quantification was required, emissions were modeled using the California Emissions Estimator Model (CaIEEMod). CaIEEMod is a Statewide land use emissions computer model designed to quantify potential criteria pollutant emissions associated with both construction and operations from a variety of land use projects. Air quality impacts were assessed according to methodologies recommended by CARB and the SCAQMD.

Construction equipment, trucks, worker vehicles, and ground -disturbing activities associated with Project construction would generate emissions of criteria air pollutants and precursors. Daily regional construction emissions are estimated by assuming construction occurs at the earliest feasible date (i.e., a conservative estimate of construction activities) and applying off -road, fugitive dust, and on -road emissions factors in CaIEEMod.

Project operations would result in emissions of area sources (consumer products), energy sources (natural gas usage), and mobile sources (motor vehicles from Project generated vehicle trips). Project -generated increases in operational emissions would be predominantly associated with motor vehicle use. Since the site is currently vacant, the proposed Project would cause an increase of traffic over existing conditions.

Other operational emissions from area, energy, and stationary sources were quantified in CaIEEMod based on land use activity data.

As discussed above, the SCAQMD provides significance thresholds for emissions associated with proposed Project construction and operations. The proposed Project's construction and operational emissions are compared to the daily criteria pollutant emissions significance thresholds in order to determine the significance of a Project's impact on regional air quality.

The localized effects from the Project's on -site emissions were evaluated in accordance with the SCAQMD's LST methodology, which uses on -site mass emissions rate look -up tables and Project -specific modeling. LSTs represent the maximum emissions from a project that are not expected to cause or contribute to an exceedance of the most stringent applicable federal or state ambient air quality standards and are developed based on the ambient concentrations of that pollutant for each source receptor area and distance to the nearest sensitive receptor.

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Air Quality Assessment
5 POTENTIAL IMPACTS AND MITIGATION

5.1 Air Quality Analysis
Threshold 5.1 Would the project conflict with or obstruct implementation of the applicable air quality plan?
As part of its enforcement responsibilities, the EPA requires each state with nonattainment areas to prepare and submit a State Implementation Plan that demonstrates the means to attain the federal standards. The State Implementation Plan must integrate federal, state, and local plan components and regulations to identify specific measures to reduce pollution in nonattainment areas, using a combination of performance standards and market -based programs. Similarly, under State law, the CCAA requires an air quality attainment plan to be prepared for areas designated as nonattainment regarding the state and federal ambient air quality standards. Air quality attainment plans outline emissions limits and control measures to achieve and maintain these standards by the earliest practical date.

The Project is located within the SCAB, which is under the jurisdiction of the SCAQMD. The SCAQMD is required, pursuant to the FCAA, to reduce emissions of criteria pollutants for which the SCAB is in nonattainment. To reduce such emissions, the SCAQMD drafted the 2016 AQMP and 2022 AQMP. The 2016 AQMP establishes a program of rules and regulations directed at reducing air pollutant emissions and achieving State (California) and national air quality standards. The 2022 AQMP builds upon measures already in place from previous AQMPs.22 The primary purpose of the 2022 AQMP is to identify, develop, and implement strategies and control measures to meet the 2015 8 -hour O3 NAAQS. Air quality management planning is a regional and multi -agency effort including the SCAQMD, CARB, SCAG, and U.S.

EPA. The AQMPs' pollutant control strategies are based on the latest scientific and technical information and planning assumptions, including SCAG's growth projections and the RTP/SCS, updated emission inventory methodologies for various source categories, and SCAG's latest growth forecasts. SCAG's latest growth forecasts were defined in consultation with local governments and with reference to local general plans. The Project is subject to the SCAQMD's 2016 and 2022 AQMPs.

Criteria for determining consistency with the AQMP are defined by the following indicators:
• Consistency Criterion No. 1: The project will not result in an increase in the frequency or severity of existing air quality violations, or cause or contribute to new violations, or delay the timely attainment of air quality standards or the interim emissions reductions specified in the AQMP. • Consistency Criterion No. 2: The project will not exceed the assumptions in the AQMP or increments based on the years of the project build -out phase.

According to the SCAQMD's CEQA Air Quality Handbook, the purpose of the consistency finding is to determine if a project is inconsistent with the assumptions and objectives of the regional air quality plans, and thus if it would interfere with the region's ability to comply with CAAQS and NAAQS. 22 South Coast Air Quality Management District, 2022 Air Quality Management Plan, page ES -2, December 2022. http://www.agmd.gov/home/air-quality/clean-air-plans/air-quality-mgt-plan , accessed November 6, 2025.

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Air Quality Assessment
The violations to which Consistency Criterion No. 1 refers are CAAQS and NAAQS. As shown in Table 8 and Table 9 below, the Project would not exceed the construction and operational emission standards. Thus, the Project would be consistent with the first criterion.

Concerning Consistency Criterion No. 2, the AQMP contains air pollutant reduction strategies based on SCAG's latest growth forecasts, and SCAG's growth forecasts were defined in consultation with local governments and with reference to local general plans. The Project site has a General Plan land use designation of Commercial (C) and is within the Design for Development (DFD) Zoning District. The Project is consistent with the City's General Plan Land Use Designations and the Zoning Designations and would not require a General Plan Amendment (GPA) or a Zone Change. As such, the Project is consistent with SCAG's latest growth forecasts. Thus, the Project is consistent with the second criterion. Therefore, impacts would be less than significant.

Mitigation Measures: No mitigation is required.

Level of Significance: Less than significant impact.

Threshold 5.2 Would the project result in a cumulatively considerable net increase of any criteria pollutant for which the project region is non -attainment under an applicable state or federal ambient air quality standard?
The nature of air emissions is largely a cumulative impact. As a result, no single project is sufficient in size to, by itself, result in nonattainment of ambient air quality standards. Instead, individual project emissions contribute to existing cumulatively significant adverse air quality impacts. Appendix D of the SCAQMD White Paper on Potential Control Strategies to Address Cumulative Impacts from Air Pollution (2003) notes that projects that result in emissions that do not exceed the project -specific SCAQMD regional thresholds of significance are considered to result in a less than significant impact on a cumulative basis unless there is other pertinent information to the contrary.23 Therefore, a project with projected emissions that would exceed SCAQMD thresholds would also make a cumulatively considerable contribution to a significant cumulative impact and, conversely, a project with projected emissions that would be below SCAQMD thresholds would not make a cumulatively considerable contribution to a significant cumulative impact.

Construction Emissions
Construction associated with the Project would generate short-term emissions of criteria air pollutants.

The criteria pollutants of primary concern within the Project area include O3 -precursor pollutants (i.e., ROG and NOx) and PM10 and PM25. Construction -generated emissions are short term and of temporary duration, lasting only as long as construction activities occur, but would be considered a significant air quality impact if the volume of pollutants generated exceeds the SCAQMD's thresholds of significance.

Construction results in the temporary generation of emissions resulting from site grading, road paving, motor vehicle exhaust associated with construction equipment and worker trips, and the movement of construction equipment, especially on unpaved surfaces. Emissions of airborne particulate matter are 23 South Coast Air Quality Management District, White Paper on Potential Control Strategies to Address Cumulative Impacts from Air Pollution, August 2003, https://www.agmd.gov/docs/default-source/Agendas/Environmental-Justice/cumulative-impacts- working-group/cumulative-impacts-white-paper-appendix.pdf, accessed November 6, 2025.

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largely dependent on the amount of ground disturbance associated with site preparation activities as well as weather conditions and the appropriate application of water.

The duration of construction activities associated with the Project is estimated to last approximately 11 months. Construction -generated emissions associated the Project were calculated using the CARB- approved CaIEEMod computer program, which is designed to model emissions for land use development projects, based on typical construction requirements. See A33endix A: Air Quality Modeling Data for more information regarding the construction assumptions used in this analysis. Predicted maximum daily construction -generated emissions for the Project are summarized in Table 8: Construction -Related Emissions.

Fugitive dust emissions may have a substantial, temporary impact on local air quality. In addition, fugitive dust may be a nuisance to those living and working in the Project vicinity. Uncontrolled dust from construction can become a nuisance and potential health hazard to those living and working nearby.

SCAQMD Rules 402 and 403 (prohibition of nuisances, watering of inactive and perimeter areas, track out requirements, etc.), are applicable to the Project and were applied in CaIEEMod to minimize fugitive dust emissions. Standard Condition (SC) AQ-1 requires the implementation of Rule 402 and 403 dust control techniques to minimize PM10 and PM2.5 concentrations. While impacts would be considered less than significant, Project would be subject to SCAQMD Rules for reducing fugitive dust, described in the Regulatory Framework subsection above and identified in Standard Conditions SC AQ-1.

Table 8: Construction -Related Emissions
Construction Year
Maximum Pounds Per Dayl
ROG
NOx

CO
SO2
PM10
PM2.5
2026

3.11 27.82

30.87 0.05

4.44 2.55
2027

5.30 9.48

13.6 0.03

4.58 1.02
Maximum Emissions

5.30 27.82

30.87 0.05

4.58 2.55
SCAQMD Threshold
75 100
550
150
150
55 Exceed SCAQMD
Threshold?
No
No
No
No
No
No

1. SCAQMD Rule 403 Fugitive Dust applied. Rule 403 reduction/credits include the following: properly maintain mobile and other construction equipment; water exposed surfaces three times daily; and limit speeds on unpaved roads to 15 miles per hour. Reductions percentages from the SCAQMD CEQA Handbook (Tables XI -A through XI -E) were applied. No mitigation was applied to construction equipment.

ROG = Reactive Organic Gases; NOx = Nitrogen Oxides; CO = Carbon Monoxide; SO2 = Sulfur Dioxide; PMio = Particulate Matter 10 microns in diameter or less; PM2.5= Particulate Matter 2.5 microns in diameter or less.

Source: CaIEEMod version 2022.1.. Refer to Appendix A for model outputs.

As shown in Table 8, all criteria pollutant emissions would remain below their respective thresholds. While impacts would be considered less than significant, the Project would be subject to SCAQMD Rules 402, 403, and 1113, described in the Regulatory Framework subsection above and required by SC AQ-1.

Operational Emissions
The Project's operational emissions would be associated with area sources (e.g., landscape maintenance equipment, architectural coatings, consumer products, etc.), energy sources, mobile sources (i.e., motor vehicle use), and off -road equipment. Primary sources of operational criteria pollutants are from motor vehicle use. Long-term operational emissions attributable to the Project are summarized in Table 9:

Operational Emissions. The operational emissions sources are described below.

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• Area Source Emissions. Area source emissions would be generated due to consumer products (e.g., fertilizers/pesticides, detergents; cleaning compounds; polishes; floor finishes; cosmetics; personal care products; home, lawn, and garden products; disinfectants; sanitizers; aerosol paints, etc.), architectural coating, and gasoline -powered landscaping equipment that were previously not present on the site. • Energy Source Emissions. Energy source emissions would be generated due to electricity and natural gas usage associated with the Project. Primary uses of electricity and natural gas by the Project would be for space heating and cooling, water heating, ventilation, lighting, appliances, and electronics.
• Mobile Source. Mobile sources are emissions from motor vehicles, including tailpipe and evaporative emissions. Depending upon the pollutant being discussed, the potential air quality impact may be of either regional or local concern. For example, ROG, NOx, PM10, and PM2.5 are all pollutants of regional concern. NOx and ROG react with sunlight to form O3, known as photochemical smog. Additionally, wind currents readily transport PM10 and PM2.5.

However, CO tends to be a localized pollutant, dispersing rapidly at the source. • Gas Dispensing Facility. The proposed project includes eight vehicle fueling positions. The eight vehicle fueling positions would dispense gasoline and therefore would be considered a gasoline dispensing facility (GDF). GDFs are regulated by the SCAQMD, and GDFs require permits from the SCAQMD. Thus, emissions attributed to the GDF were estimated separately from the area source operational emissions above. The emissions calculations are based on annual daily throughput of 8,448 gallons of gasoline (approximately 3.08 million gallons per year). In addition to traffic -related emissions, the GDF is also a source of ROG emissions associated with loading, storage, refueling of vehicles and spillage that results in evaporative emissions. Table 9 also presents the evaporative ROG emissions associated with the proposed GDF.
• Emergency Backup Generators. The proposed Project would use backup generators only in the event of a power failure and would not be part of the Project's normal daily operations.

Nonetheless, emissions associated with this equipment were included to be conservative.

Emissions from an emergency backup generator for the proposed warehouse building were calculated separately from CaIEEMod; refer to Appendix A. However, CaIEEMod default emissions rates were used. If backup generators are required, the end user would be required to obtain a permit from the SCAQMD prior to installation. Emergency backup generators must meet SCAQMD's Best Available Control Technology (BACT) requirements and comply with SCAQMD Rule 1470 (Requirements for Stationary Diesel -Fueled Internal Combustion and Other Compression Ignition Engines), which would minimize emissions.

Project -generated vehicle emissions are based on the trip generation within the Project Trip Generation Forecast (Linscott, Law & Greenspan, Engineers, 2025) and incorporated into CaIEEMod as recommended by the SCAQMD. Per the Project Trip Generation Forecast, the Project would generate 3,080 daily vehicle trips.

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Table 9: Long -Term Operational Emissions
Source
Maximum Pounds Per Day
ROG
NO

CO
5O2
PM10
PM2.5
Area Source Emissions

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The SCAQMD has not established separate significance thresholds for cumulative operational emissions.

The nature of air emissions is largely a cumulative impact. As a result, no single project is sufficient in size to, by itself, result in nonattainment of ambient air quality standards. Instead, individual project emissions contribute to existing cumulatively significant adverse air quality impacts. The SCAQMD developed the operational thresholds of significance based on the level above which individual project emissions would result in a cumulatively considerable contribution to the SCAB's existing air quality conditions. Therefore, a project that exceeds the SCAQMD operational thresholds would also be a cumulatively considerable contribution to a significant cumulative impact.

As shown in Table 9, the Project operational emissions do not exceed the SCAQMD thresholds. Therefore, the proposed Project would not generate a cumulatively considerable contribution to air pollutant emissions during construction.

Standard Conditions and Requirements:

SC AQ-1
Prior to the issuance of grading permits, the City Engineer shall confirm that the Grading Plan, Building Plans and Specifications require all construction contractors to comply with South Coast Air Quality Management District's (SCAQMD's) Rules 402 and 403 to minimize construction emissions of dust and particulates. The measures include, but are not limited to, the following:
• Portions of a construction site to remain inactive longer than a period of three months will be seeded and watered until grass cover is grown or otherwise stabilized. • All on -site roads will be paved as soon as feasible or watered periodically or chemically stabilized.
• All material transported off site will be either sufficiently watered or securely covered to prevent excessive amounts of dust.
• The area disturbed by clearing, grading, earthmoving, or excavation operations will be minimized at all times.
• Where vehicles leave a construction site and enter adjacent public streets, the streets will be swept daily or washed down at the end of the work day to remove soil tracked onto the paved surface.

Mitigation Measures: No mitigation is required.

Level of Significance: Less than significant impact.

Threshold 5.3 Would the Project expose sensitive receptors to substantial pollutant concentrations? Localized Construction Significance Analysis
The nearest sensitive receptors are the multi -family residences adjoining the Project site to the west. To identify impacts to sensitive receptors, the SCAQMD recommends addressing LSTs for construction. LSTs were developed in response to SCAQMD Governing Boards' Environmental Justice Enhancement Initiative (I-4). The SCAQMD provided the Final Localized Significance Threshold Methodology (dated June 2003 November 2025
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[revised 2008]) for guidance. The LST methodology assists lead agencies in analyzing localized impacts associated with Project -specific emissions.

Since CaIEEMod calculates construction emissions based on the number of equipment hours and the maximum daily soil disturbance activity possible for each piece of equipment, Table 10: Equipment- Saecific Disturbance Rates, is used to determine the maximum daily disturbed acreage for comparison to LSTs. The appropriate SRA for the localized significance thresholds is the Southeast LA County (SRA 5) since this area includes the Project. LSTs apply to CO, NO2, PM10, and PM2.5. The SCAQMD produced look- up tables for projects that disturb areas less than or equal to 5 acres in size. Project construction is anticipated to disturb a maximum of 2 acres in a single day.

Table 10: Equipment -Specific Disturbance Rates
Construction Phase
Equipment
Type
Equipment
Quantity
Acres Disturbed
per 8 -Hour Day
Operating
Hours
per Day
Acres Graded
per Day
Grading
Crawler Tractors
0 0.5
8 0
Graders
1 0.5
8 0.5
Dozers
1 0.5
8 0.5
Scrapers
0 1.0
8 0
Total Acres Graded per Day

1.0 1. Total acres graded each day is based on the number of equipment hours and the maximum daily soil disturbance activity possible for each piece of equipment, not the total acreage of the project site Source: CaIEEMod version 2022,1. Refer to Appendix A for model outputs.

The SCAQMD's methodology states that "off -site mobile emissions from the Project should not be included in the emissions compared to LSTs." Therefore, only emissions included in the CaIEEMod "on - site" emissions outputs were considered. The nearest sensitive receptors are the multi -family residences adjoining the Project site to the west. LST thresholds are provided for distances to sensitive receptors of 25, 50, 100, 200, and 500 meters. Therefore, LSTs for receptors located at the closest distance of 25 meters are utilized in this analysis. Table 11: Localized Significance of Construction Emissions, presents the results of localized emissions during construction.

Table 11: Localized Significance of Construction Emissions Construction Activity
Maximum Pounds Per Day
NO„
CO
PMlo
PM2.5
Individual Phases
Grading (2026)

14.97 17.44

3.41 1.93
Building Construction (2027)

9.39 12.94

0.34 0.31
Paving (2027)

6.09 8.83

3.57 0.73
Architectural Coating (2027)

0.83 1.13

0.02 0.02
Infrastructure Improvement (2026)

11.98 11.53

0.53 0.49
Overlapping Phases
Paving (2027) + Architectural Coating
(2027)

6.92 9.95

3.59 0.74
Building Construction (2027) +
Infrastructure Improvement (2026)

21.37 24.47

0.87 0.80
Maximum Emissions

21.37 24.47

3.59 1.93
SCAQMD Localized Screening Threshold
(1 acres at 25 meters)
80 571
4 3
November 2025
Kimley>»Horn

City of Bellflower
Bellflower Convenience Center
Air Quality Assessment
Exceed SCAQMD Threshold?
No
No
No
No
NOx = Nitrogen Oxides; CO = Carbon Monoxide; PMio = Particulate Matter 10 microns in diameter or less; PM2s = Particulate Matter 2.5 microns in diameter or less

1. Totals may be slightly off due to rounding.

Source: CaIEEMod version 2022.1. Refer to Appendix A for model outputs.

Table 11 shows that the emissions of these pollutants on the peak day of Project construction would not result in significant concentrations of pollutants at nearby sensitive receptors. Therefore, the Project would result in a less than significant impact concerning LSTs during construction activities.

Localized Operational Significance Analysis
Since the Project site is approximately 3.63 acres, the 3 -acre threshold was used for evaluation of operational emissions. As noted above, the LSTs increase as site acreage increases. The on -site operational emissions are compared to the LSTthresholds in Table 12: Localized Significance ofOaerational Emissions.

Table 12 shows that the maximum daily emissions of these pollutants during Project operations would not result in significant concentrations of pollutants at nearby sensitive receptors. Therefore, the Project would result in a less than significant impact concerning LSTs during operational activities.

Table 12: Localized Significance of Operational Emissions Activity
(Maximum Pounds Per Day)
Nitrogen
Oxide
(NO.)
Carbon
Monoxide
(CO)
Coarse
Particulate
Matter
(PMio)
Fine
Particulate
Matter
(PM2.5)
On -Site Area and Energy Source Emissions

0.30 0.79

0.02 0.02
SCAQMD Localized Screening Threshold
(3 acres at 25 meters)
133
1,067
3 1
Exceed SCAQMD Threshold?
No
No
No
No
NOx = Nitrogen Oxides; CO = Carbon Monoxide; PM10 = Particulate Matter 10 microns in diameter or less; PM2.s = Particulate Matter 2.5 microns in diameter or less
1, Totals may be slightly off due to rounding.

Source: CaIEEMod version 2022.1. Refer to Appendix A for model outputs.

Criteria Pollutant Health Impacts
On December 24, 2018, the California Supreme Court issued an opinion identifying the need to provide sufficient information connecting a project's air emissions to health impacts or explain why such information could not be ascertained (Sierra Club v. County of Fresno [Friant Ranch, L.P.] [2018] Cal.5tn Case No. S219783). The SCAQMD has set its CEQA significance thresholds based on the FCAA, which defines a major stationary source (in extreme ozone nonattainment areas such as the South Coast Air Basin) as emitting 10 tons per year. The thresholds correlate with the trigger levels for the federal New Source Review (NSR) Program and SCAQMD Rule 1303 for new or modified sources. The NSR Program' was created by the FCAA to ensure that stationary sources of air pollution are constructed or modified in a manner that is consistent with attainment of health -based federal ambient air quality standards. The federal ambient air quality standards establish the levels of air quality necessary, with an adequate margin of safety, to protect the public health. Therefore, projects that do not exceed the SCAQMD's LSTs and mass emissions thresholds would not violate any air quality standards or contribute substantially to an existing or projected air quality violation and no criteria pollutant health impacts. 24 Code of Federal Regulation (CFR) [i.e., PSD (40 CFR 52.21, 40 CFR 51.166, 40 CFR 51.165 (b)), Non -attainment NSR (40 CFR

52.24, 40 CFR 51.165, 40 CFR part 51, Appendix S)
November 2025
Kimley>»Horn

City of Bellflower Bellflower Convenience Center
Air Quality Assessment
NOx and ROG are precursor emissions that form ozone in the atmosphere in the presence of sunlight where the pollutants undergo complex chemical reactions. It takes time and the influence of meteorological conditions for these reactions to occur, so ozone may be formed at a distance downwind from the sources. Breathing ground -level ozone can result health effects that include: reduced lung function, inflammation of airways, throat irritation, pain, burning, or discomfort in the chest when taking a deep breath, chest tightness, wheezing, or shortness of breath. In addition to these effects, evidence from observational studies strongly indicates that higher daily ozone concentrations are associated with increased asthma attacks, increased hospital admissions, increased daily mortality, and other markers of morbidity. The consistency and coherence of the evidence for effects upon asthmatics suggests that ozone can make asthma symptoms worse and can increase sensitivity to asthma triggers.

According the SCAQMD's 2016 AQMP, ozone, NOx, and ROG have been decreasing in the Basin since 1975 and are projected to continue to decrease in the future. Although vehicle miles traveled in the Basin continue to increase, NOx and ROG levels are decreasing because of the mandated controls on motor vehicles and the replacement of older polluting vehicles with lower -emitting vehicles. NOx emissions from electric utilities have also decreased due to the use of cleaner fuels and renewable energy. The 2016 AQMP demonstrates how the SCAQMD's control strategy to meet the 8 -hour ozone standard in 2023 would lead to sufficient NOx emission reductions to attain the 1 -hour ozone standard by 2022. In addition, since NOx emissions also lead to the formation of PM25, the NOx reductions needed to meet the ozone standards will likewise lead to improvement of PM2.5 levels and attainment of PM2.5 standards.

The SCAQMD's air quality modeling demonstrates that NOx reductions prove to be much more effective in reducing ozone levels and will also lead to significant improvement in PM2.5 concentrations. NOx- emitting stationary sources regulated by the SCAQMD include Regional Clean Air Incentives Market (RECLAIM) facilities (e.g., refineries, power plants, etc.), natural gas combustion equipment (e.g., boilers, heaters, engines, burners, flares) and other combustion sources that burn wood or propane. The 2016 AQMP identifies robust NOx reductions from new regulations on RECLAIM facilities, non -refinery flares, commercial cooking, and residential and commercial appliances. Such combustion sources are already heavily regulated with the lowest NOx emissions levels achievable but there are opportunities to require and accelerate replacement with cleaner zero -emission alternatives, such as residential and commercial furnaces, pool heaters, and backup power equipment. The SCAQMD plans to achieve such replacements through a combination of regulations and incentives. Technology -forcing regulations can drive development and commercialization of clean technologies, with future year requirements for new or existing equipment. Incentives can then accelerate deployment and enhance public acceptability of new technologies.

The 2016 AQMP also emphasizes that beginning in 2012, continued implementation of previously adopted regulations will lead to NOx emission reductions of 68 percent by 2023 and 80 percent by 2031. With the addition of 2016 AQMP proposed regulatory measures, a 30 percent reduction of NOx from stationary sources is expected in the 15 -year period between 2008 and 2023. This is in addition to significant NOx reductions from stationary sources achieved in the decades prior to 2008.

As previously discussed, localized effects of on -site Project emissions on nearby receptors were found to be less than significant (refer to Table 11 and Table 12). The LSTs represent the maximum emissions from a project that are not expected to cause or contribute to an exceedance of the most stringent applicable state or federal ambient air quality standard. The LSTs were developed by the SCAQMD based on the ambient concentrations of that pollutant for each SRA and distance to the nearest sensitive receptor. The November 2025
Kimley>»Horn

City of Bellflower Bellflower Convenience Center
Air Quality Assessment
ambient air quality standards establish the levels of air quality necessary, with an adequate margin of safety, to protect public health, including protecting the health of sensitive populations such as asthmatics, children, and the elderly. However, as discussed above, neither the SCAQMD nor any other air district currently have methodologies that would provide Lead Agencies and CEQA practitioners with a consistent, reliable, and meaningful analysis to correlate specific health impacts that may result from a proposed project's mass emissions. Information on health impacts related to exposure to ozone and particulate matter emissions published by the U.S. EPA and CARB have been summarized above and discussed in the Regulatory Framework section. Health studies are used by these agencies to set the NAAQS and CAAQS.

Ozone concentrations are dependent upon a variety of complex factors, including the presence of sunlight and precursor pollutants, natural topography, nearby structures that cause building downwash, atmospheric stability, and wind patterns. Because of the complexities of predicting ground -level ozone concentrations in relation to the NAAQS and CAAQS, none of the health -related information can be directly correlated to the pounds/day or tons/year of emissions estimated from a single, proposed project.

It should also be noted that this analysis identifies health concerns related to particulate matter, CO, O3, and NO2. Table 1 includes a list of criteria pollutants and summarizes common sources and effects. Thus, this analysis is reasonable and intended to foster informed decision making.

Carbon Monoxide Hotspots
An analysis of CO "hot spots" is needed to determine whether the change in the level of service of an intersection resulting from the Project would have the potential to result in exceedances of the CAAQS or NAAQS. It has long been recognized that CO exceedances are caused by vehicular emissions, primarily when vehicles are idling at intersections. Vehicle emissions standards have become increasingly stringent in the last 20 years. Currently, the CO standard in California is a maximum of 3.4 grams per mile for passenger cars (requirements for certain vehicles are more stringent). With the turnover of older vehicles, introduction of cleaner fuels, and implementation of control technology on industrial facilities, CO concentrations have steadily declined. Accordingly, with the steadily decreasing CO emissions from vehicles, even very busy intersections do not result in exceedances of the CO standard.

The South Coast Air Basin (SCAB) was re -designated as attainment in 2007 and is no longer addressed in the SCAQMD's AQMP. The 2003 AQMP is the most recent version that addresses CO concentrations. As part of the SCAQMD CO Hotspot Analysis, the Wilshire Boulevard/Veteran Avenue intersection, one of the most congested intersections in Southern California with an average daily traffic (ADT) volume of approximately 100,000 vehicles per day, was modeled for CO concentrations. This modeling effort identified a CO concentration high of 4.6 ppm, which is well below the 35-ppm Federal standard. Based on data within the Project's Traffic Impact Analysis, the surrounding roadways would have a maximum ADT volume of 24,552 during the Opening Year 2023 plus Project scenario. Therefore, the Project would not produce the volume of traffic required to generate a CO hot spot in the context of SCAQMD's CO Hotspot Analysis. As the CO hotspots were not experienced at the Wilshire Boulevard/Veteran Avenue intersection even as it accommodates 100,000 vehicles daily, it can be reasonably inferred that CO hotspots would not be experienced at any vicinity intersections resulting from 3,080 additional vehicle trips attributable to the Project. Therefore, the Project would not result in a CO hotspot and impacts would be less than significant.

Construction -Related Diesel Particulate Matter
November 2025
Kimley>»Horn

City of Bellflower Bellflower Convenience Center
Air Quality Assessment
Construction of the Project would result in the generation of DPM emissions from the use of required off - road diesel equipment. The amount to which the receptors are exposed (a function of concentration and duration of exposure) is the primary factor used to determine health risk (i.e., potential exposure to TAC emission levels that exceed applicable standards). Health -related risks associated with diesel -exhaust emissions are primarily linked to long-term exposure and the associated risk of contracting cancer. The use of diesel -powered construction equipment would be temporary and episodic. The duration of exposure would be short and exhaust from construction equipment dissipates rapidly. Current models and methodologies for conducting health risk assessments are associated with longer -term exposure periods of 9, 30, and 70 years, which do not correlate well with the temporary and highly variable nature of construction activities. The California Office of Environmental Health Hazard Assessment (OEHHA) has not identified short-term health effects from DPM. Construction is temporary and would be transient throughout the site (i.e., move from location to location) and would not generate emissions in a fixed location for extended periods of time which would limit the exposure of any proximate individual sensitive receptor to TACs.

Additionally, construction is subject to and would comply with California regulations (e.g., California Code of Regulations, Title 13, Sections 2485 and 2449), which reduce diesel PM and criteria pollutant emissions from in -use off -road diesel -fueled vehicles and limit the idling of heavy-duty construction equipment to no more than five minutes. These regulations would further reduce nearby sensitive receptors' exposure to temporary and variable DPM emissions. Given the temporary and intermittent nature of construction activities likely to occur within specific locations in the Project site (i.e., construction is not likely to occur in any one location for an extended time), the dose of DPM of any one receptor is exposed to would be limited. Therefore, considering the relatively short duration of DPM-emitting construction activity at any one location, and the highly dispersive properties of DPM, sensitive receptors would not be exposed to substantial concentrations of construction -related TAC emissions. Impacts would be less than significant.

Mitigation Measures: No mitigation is required.

Level of Significance: Less than significant impact.

Threshold 5.4 Would the project result in other emissions (such as those leading to odors) adversely affecting a substantial number of people?
Construction
Odors that could be generated by construction activities are required to follow SCAQMD Rule 402 to prevent odor nuisances on sensitive land uses. SCAQMD Rule 402, Nuisance, states:

A person shall not discharge from any source whatsoever such quantities of air contaminants or other material which cause injury, detriment, nuisance, or annoyance to any considerable number of persons or to the public, or which endanger the comfort, repose, health or safety of any such persons or the public, or which cause, or have a natural tendency to cause, injury or damage to business or property.

During construction, emissions from construction equipment, such as diesel exhaust, and volatile organic compounds from architectural coatings and paving activities may generate odors. However, these odors would be temporary, are not expected to affect a substantial number of people and would disperse November 2025
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City of Bellflower Bellflower Convenience Center
Air Quality Assessment
rapidly. Therefore, impacts related to odors associated with the Project's construction -related activities would be less than significant.

Operations
The SCAQMD CEQA Air Quality Handbook identifies certain land uses as sources of odors. These land uses include agriculture (farming and livestock), wastewater treatment plants, food processing plants, chemical plants, composting facilities, refineries, landfills, dairies, and fiberglass molding. The Project would not include any of the land uses that have been identified by the SCAQMD as odor sources.

Therefore, the Project would not create objectionable odors.

Mitigation Measures: No mitigation is required.

Level of Significance: Less than significant impact.

November 2025
Kimley>»Horn

City of Bellflower Bellflower Convenience Center
Air Quality Assessment
6 REFERENCES

1. California Air Resources Board, Almanac Resources, 2024. Available at:
https://ww2.arb.ca.gov/resources/documents/almanac-resources . Accessed November 6, 2025.

2. California Air Resources Board, California Ambient Air Quality Standards. Available at:
https://ww2.arb.ca.gov/resources/california-ambient-air-quality-standards . Accessed November 6, 2025.

3. California Air Resources Board, Common Air Pollutants, 2024. Available at:
https://ww2.arb.ca.gov/resources/common-air-pollutants . Accessed November 6, 2025.

4. California Air Resources Board, Overview: Diesel Exhaust & Health. Available at:
https://ww2.arb.ca.gov/resources/overview-diesel-exhaust-and-health . Accessed November, 2025.

5. California Code of Regulations Section 1961, Exhaust Emission Standards and Test Procedures — 2004 through 2019 Model Passenger Cars, Light -Duty Trucks, and Medium -Duty Vehicles, 2022. Available at: https://ww2.arb.ca.gov/sites/default/files/2023-02/cleancom plete_lev_ghg_regs_11_2022.pdf.

Accessed November 6, 2025.

6. California Energy Commission, 2022 Building Energy Efficiency Standards for Residential and Nonresidential Buildings. Available at: https://www.energy.ca.gov/publications/2022/2022-building- energy-efficiency-standards-residential-and-nonresidential. Accessed November 6, 2025.

7. City of Bellflower, General Plan, 1994.

8. Code of Federal Regulation (CFR) [i.e., PSD (40 CFR 52.21, 40 CFR 51.166, 40 CFR 51.165 (b)), Non - attainment NSR (40 CFR 52.24, 40 CFR 51.165, 40 CFR part 51, Appendix S)

9. Linscott, Law & Greenspan, Engineers, Project Trip Generation Forecast, 2025.

10. South Coast Air Quality Management District, 2022 Air Quality Management Plan, December 2022.

Available at: https://www.agmd.gov/docs/default-source/clean-air-plans/air-quality-management- plans/2022-air-quality-management-plan/final-2022-aqmp/final-2022-agmp.pdf?sfvrsn=16.

Accessed November 6, 2025.

11. South Coast Air Quality Management District, Air Quality Management Plan, Appendix V, Modeling and Attainment Demonstrations, August 2003. Available at: https://www.agmd.gov/home/air- quality/air-quality-management-plans/air-quality-mgt-plan/2003-aqmp. Accessed November 6, 2025.

12. South Coast Air Quality Management District, Carbon Monoxide Redesignation Request and Maintenance Plan, February 2005. Available at:
https://ww2.arb.ca.gov/sites/default/files/classic/planning/sip/sccosip05/sccosip_redesig_mpla n. pd f. Accessed November 6, 2025.

13. South Coast Air Quality Management District, CEQA Air Quality Handbook, 1993.

14. South Coast Air Quality Management District, Final 2016 Air Quality Management Plan, March 2017.

Available at: https://www.agmd.gov/docs/default-source/clean-air-plans/air-quality-management- plans/2016-air-quality-management-plan/final-2016-aqmp/final2016agmp.pdf?sfvrsn=15. Accessed November 6, 2025.

November 2025
Kimley>»Horn

City of Bellflower Bellflower Convenience Center
Air Quality Assessment

15. South Coast Air Quality Management District, Final Localized Significance Threshold Methodology, July 2008. Available at: https://www.agmd.gov/home/rules-compliance/ceqa/air-quality-analysis- handbook/localized-significance-thresholds. Accessed November 6, 2025.

16. South Coast Air Quality Management District, Localized Significance Thresholds. Available at:
https://www.agmd.gov/home/rules-compliance/ceqa/air-quality-analysis-handbook/localized- significance-thresholds. Accessed November 6, 2025.

17. South Coast Air Quality Management District, Sample Construction Scenarios for Projects Less than Five Acres in Size, February 2005. Available at: https://www.aqmd.gov/docs/default- source/ceqa/handbook/localized-significance-thresholds/final-sample-construction-scenario- report.pdf?sfvrsn=2. Accessed November 6, 2025.

18. South Coast Air Quality Management District, White Paper on Potential Control Strategies to Address Cumulative Impacts from Air Pollution, August 2003. Available at:
https://www.agmd.gov/docs/default-source/Agendas/Environmental-Justice/cumulative-impacts- working-group/cumulative-impacts-white-paper-appendix.pdf. Accessed November 6, 2025.

19. Southern California Association of Governments, Connect SoCal (2020-2045 RTP/SCS), Demographics and Growth Forecast, adopted September 2020. Available at:
https://scag.ca.gov/sites/main/files/file-attachments/0903fconnectsocal_demographics-and- growth-forecast.pdf? 1606001579. Accessed November 6, 2025.

20. Southern California Association of Governments, Connect SoCal (2024-2050 RTP/SCS), Demographics and Growth Forecast adopted April 4, 2024. Available at:
https://www.scag.ca.gov/sites/default/files/2024-05/23-2987-tr-demographics-growth-forecast- final-040424.pdf. Accessed November 6, 2025.

21. U.S. Environmental Protection Agency, Basic Information about Carbon Monoxide (CO) Outdoor Air Pollution, 2023. Available at: https://www.epa.gov/co-pollution/basic-information-about-carbon- monoxide-co-outdoor-airpollution#:':text=The%20greatest%20s ources%20 of%20CO,can%20affect%20a it%20quality%20indoors. Accessed November 6, 2025.

22. U.S. Environmental Protection Agency, Carbon Monoxide Trends, 2023. Available at:
https://www.epa.gov/air-trends/carbon-monoxide-trends . Accessed November 6, 2025.

23. U.S. Environmental Protection Agency, Criteria Air Pollutants. Available at:
https://www.epa.gov/criteria-air-pollutants . Accessed November 6, 2025.

November 2025
Kimley>»Horn

Appendix A
Air Quality Modeling Data

SCAQMD Localized Significance Thresholds
Acreage Estimate
SRA No.:
5 Receptor Dist. 1 (meters):
25 Receptor Dist. 2 (meters):
50 Interpolated Distance:
25 Acres:
1 Distance 1
25 meters
Southeast LA County
Construction LST
NOX
CO
Milo
PM2.s
1 Acre
80 571
4 3

1.5 Acres
97 716
6 4
2 Acres
114
861
7 4

2.5 Acres
124
964
8 5
3 Acres
133
1,067
9 5

3.5 Acres
143
1,171
11 6
4 Acres
153
1,274
12 6

4.5 Acres
162
1,377
13 7
5 Acres
172
1,480
14 7
Distance 2
50 meters
Construction LST
NOX
CO
Milo
PM2.s
1 Acres
81 735
13 4

1.5 Acres
96 909
17 5
2 Acres
111
1,082
21 6

2.5 Acres
120
1,211
25 7
3 Acres
129
1,340
28 7

3.5 Acres
138
1,469
32 8
4 Acres
147
1,597
35 9

4.5 Acres
156
1,726
39 9
5 Acres
165
1,855
42 10
Equipment
Acres/8hr Day
Equipment Modeled
Disturbed Acres
Crawler Tractors

0.5 0
0 Graders

0.5 1

0.5 Dozers

0.5 1

0.5 Scrapers
1 0
0 Total Acres
1 Operational LST
NOX
CO
PM.o
PM2.s
1 Acres
80 571
1 1

1.5 Acres
97 716
2 1
2 Acres
114
861
2 1

2.5 Acres
124
964
2 1
3 Acres
133
1,067
3 1

3.5 Acres
143
1,171
3 2
4 Acres
153
1,274
3 2

4.5 Acres
162
1,377
4 2
5 Acres
172
1,480
4 2
Operational LST
NOX
CO
PMio
PM2.s
1 Acres
81 735
3 1

1.5 Acres
96 909
4 2
2 Acres
111
1,082
5 2

2.5 Acres
120
1,211
6 2
3 Acres
129
1,340
7 2

3.5 Acres
138
1,469
8 3
4 Acres
147
1,597
8 3

4.5 Acres
156
1,726
9 3
5 Acres
165
1,855
10 3

Interpolated Dist. 25 meters _
Construction 1ST
NOX
CO
PM10
PM2.5
1 Acres
80 571
4 3

1.5 Acres
97 716
6 4
2 Acres
114
861
7 4

2.5 Acres
124
964
8 5
3 Acres
133
1,067
9 5

3.5 Acres
143
1,171
11 6
4 Acres
153
1,274
12 6

4.5 Acres
162
1,377
13 7
5 Acres
172
1,480
14 7
Operational LST
NOX
CO
PM10
PM2.5
1 Acres
80 571
1 1

1.5 Acres
97 716
2 1
2 Acres
114
861
2 1

2.5 Acres
124
964
2 1
3 Acres
133
1,067
3 1

3.5 Acres
143
1,171
3 2
4 Acres
153
1,274
3 2

4.5 Acres
162
1,377
4 2
5 Acres
172
1,480
4 2

Below LST
Construction
Operations
Above LST
Construction
Operations
NOX CO PM10
114 861 7
114 861 2
NOX CO PM10
165 735 42
165 735 10
NOX Const. and Op! 25 50 100
1 80 81 94
2 114 111 121
5 172 165 176
CO Const. and Ops. 25 50 100
1 571 735 1088
2 861 1082 1496
5 571 735 1088
PM10 Construction 25 50 100
1 4 13 30
2 7 21 39
5 14 42 60
PM2.5 Construction 25 50 100
1 3 4 8
2 4 6 10
5 7 10 15
PM10 Operation
PM2.5 Operation
25 50 100
1 1 3 8
2 2 5 10
5 4 10 15
25 50 100
1 1 1 2
2 1 2 3
5 2 3 4
PM2.5
4 1
PM2.5
10 3
200 500
123 192
145 145
194 194
200 500
2104 6854
2625 7500
2104 6854
200 500
66 173
74 182
95 203
200 500
19 86
22 92
30 103
200 500
16 42
18 44
23 49
200 500
5 21
6 22
8 25

Building Demolition Truck Trip Estimates Based on Square Footage Building Area (Square Feet):

Building Volume (Cubic Feet):

Waste Volume (Cubic Feet):

Waste Volume (Cubic Yards):

Building Waste (Tons):
ft2
0 ft3
0 ft3
0 yd3
0 tons
Total Demo
8,062 tons
1 ft2 floor space = 10 ft3 original building volume,
1 ft3 building volume = 0.25 ft3 waste volume,
1 yd3 building waste = 0.5 ton weight,
Mean truck capacity = 20 yd3 haulage volume, and therefore 1 ft2 represents 0.046 ton of waste material.

From CaIEEMod User's Guide: If the total building waste weight is not known, the program will estimate the tonnage using the building waste tonnage —structural floor space relationship determined from a 1976 analysis by Murphy and Chatterjee of the demolition of 12 commercial brick, concrete, and steel buildings.

Pavement Demolition Estimates Based on Square Foota
Pavement Area:

Pavement Thickness:

Pavement Volume:

Pavement Density:
139,000 ft2

0.8 feet
111,200 ft3
145 I bs/ft3
16,124,000 pounds
8,062 tons
Source: California Air Pollution Control Officers Association, CaIEEMod User's Guide, Appendix A: Calculation Details, Page 13, October 2017.

Midwest Research Institute. 1988. Gap Filling PM10 Emission Factors for Selected Open Area Dust Sources.

Inputs - 11/18/2025
Potential To Emit Calculator for Gasoline Dispensing Facilities - Inputs 3/23/2015
This workbook is designed to calculate the potential to emit of your gasoline dispensing facility.

The gasoline dispensing facility (GDF) owner/operator shall provide two pieces of information. These include whether or not the GDF is in a designated ozone nonattainment area and the number of vehicle refueling positions at the GDF for both gasoline and diesel vehicles. Ozone attainment/nonattainment designation status can be found at Directions - Enter the facility's information in the yellow -highlighted boxes below.

The facility wide emissions will be displayed on the "Output" sheet.

Facility Profile - User Inputs
What is the number of gasoline only refueling positions at your dispensing facility? 8 A vehicle refueling position is a single gasoline dispensing machine and its associated nozzle(s). The total number of vehicle refueling positions at your GDF is the number of gasoline -fueled vehicles that can be refueled simultaneously.

What is the number of automotive/ nonroad diesel only refueling positions at your facility? 0 A vehicle refueling position is a single diesel fuel dispenser and its associated nozzle(s). The total number of automotive/nonroad only diesel refueling positions at your facility is the number of automotive -type vehicles (passenger car, light truck)or nonroad equipment that can be refueled simultaneously. This count would include free standing aboveground tanks used to refuel nonroad equipment.

What is the number of dispensers capable of refueling with either gasoline or diesel? These are normally multi -grade dispensers with separate gasoline and diesel fuel nozzles on the same dispenser. These are used primarily to refuel automotive and light truck type vehicles.

What is the number of heavy-duty (HD) truck diesel refueling positions at your facility? 0 0
A HD truck (e.g., over the road) refueling position is a single diesel fuel dispenser and its associated nozzle(s). The total number of HD truck refueling positions at your facility is the number of HD trucks that can be refueled simultaneously.

Ozone designation status can be found at http://www.epa.gov/oar/oaqps/greenbk/hindex.html or co Enter either attainment or nonattainment.

What is the current year?
Enter the current year (a number between 2013 and 2030). nonattainment
2025

Output - Criteria - 11/18/2025
Potential To Emit Calculator for Gasoline Dispensing Facilities - Outputs 3/23/2015
Potential to Emit (tons VOC/year)

1.341
This facility is located in an ozone nonattainment area.

Drum - Prod.Crit - 11/18/2025
Potential To Emit Calculator for Gasoline Dispensing Facilities 3/23/2015
This sheet calculates the maximum fuel throughput, based on the number of vehicle refueling positions at your GDF. The calculations use fixed values for hours of operation, the time required for each refueling event, and the average amount of fuel dispensed per refueling event.

The sheet than calculates the emissions of VOC from your GDF, based on emissions factors and the attainment status of your location. Note that while this calculator is designed primarily to address emissions of gasoline vapor, it includes algorithms to account for diesel fuel vapor as well and could even be used if the sole fuel dispensed was diesel.

HD truck diesel refueling positions
0 Automotive dispensers with gasoline
or diesel
0 Automotive/Nonroad Diesel Refueling
Positions
0 Gasoline Vehicle Refueling Positions
Location - Ozone Attainment Status
8 Nonattainment Area
Max. Gasoline Throughput If No
Automotive/nonroad Diesel
3,083,520
gallons/year
Max. Automotive/Nonroad Diesel
Throughput
Max. HD Truck Diesel
0 gallons/year
Max. Combined Automotive plus HD
Truck Diesel Throughput
0 gallons/year
0 gallons/year
Internally fixed values in calculation -- gasoline and automotive/nonroad diesel Average time between start of refueling events

0.25 hours
Number of hours of GDF operation per day
24 hours/day
Number of days per year open for business
365
days/year
Number of gallons per refueling event
11 gal/refueling event
Percent of refueling events which use automotive diesel dispensers
5 %/year
Gasoline VOC Emissions -- apply these values to GDFs using USTs or ASTs7 Description 4
VOC Emission
factor
(Ib/1,000 cal)
Potential to Emit
VOC (tons/yr)
Add'I Emissions for Small Volume GDFs6

12.0 0.000
Storage Tank Filling '

0.30 0.463
Storage Tank Breathing Losses 2

0.25 0.385
Dispensing 3

0.32 0.493
Totals

0.870

1.341

18.424
Internally fixed values -- HD truck diesel
8,448
Average time between start of refueling events

0.33 hours
Number of hours of GDF operation per day
24 hours/day
Number of days per year open for business
365
days/year
Number of gallons per refueling event
110
gal/refueling event
Diesel VOC Emissions -- apply these values to GDFs using USTs or ASTs Description 4
VOC Emission
factors
Potential to Emit VOC
(Ib/1,000 gal)
(ton/yr)
Storage Tank Filling

0.040

0.000
Storage Tank Breathing Losses

0.028

0.000
Dispensing

0.040

0.000
Totals

0.108

0.000
Methodology
Maximum Throughput (gal/yr) = vehicle refueling positions / refueling event time (hrs) x hours of operation (hr/yr) x fuel dispensed (gal/refueling event) Potential to Emit of VOC (tons/yr) = Maximum Throughput (gal/yr) x VOC Emission Factor (Ib/1,000 gal) x 1 ton/2,000 Ibs Notes:

Emission factors are from AP 42, Chapter 5.2, Transportation and Marketing of Petroleum Liquids, Table 5.2-7, (June 2008), except where noted.

Assume Stage 1 controls are in place. 40 CFR 63, Subpart CCCCCC requires that new or modified gasoline dispensing facilities with a monthly throughput greater than 100,000 gallons per month install Stage 1 vapor balance system that achieves a 90% emissions reduction. 2 40 CFR 63, Subpart CCCCCC requires that new or modified gasoline dispensing facilities with a monthly throughput greater than 100,000 gallons per month install pressure/vacuum (PV) vent valves on the storage tank vent pipes. This model uses a 75 percent efficiency for PV valves in reducing breathing losses. 3 The displacement VOC emission rate in Ibs/1000 gallons depends on the gasoline Reid Vapor Pressure, the dispensed fuel temperature, and the difference between the temperature of the fuel in the tank and the dispensed fuel. For these purposes EPA calculated the uncontrolled displacement VOC emission rate in Ibs/1000 gallons. EPA has used 10 psi RVP and national average summer -time temperatures for ozone attainment areas. This yields a value of about 10.8 Ibs/1000 gallons. EPA has used 7 psi RVP and temperatures representative of the summer -time western US for ozone non -attainment areas. This yields a value of about 7.5 Ibs/1000 gallons. In 76 FR 41723, EPA determined that 80% of the vehicle fleet will have ORVR installed as of 2014, and widespread use will be achieved on a national basis on June 30, 2013. Therefore, this value has been reduced by 80% for 2014 and increases each year subsequent to 2014 as fleet turnover occurs.

See memorandum to Public Docket EPA -HQ -OAR -2010-1076, Updated Data for ORVR Widespread Use Assessment, Glenn Passavant, OTAQ, 2012 and U.S.EPA, Guidance on Removing Stage II Gasoline Vapor Control Programs from State Implementation Plans and Assessing Comparable Measures, EPA -457/B-12-001, August 7, 2012.
4 Even though spillage is a specific category of emissions related to fuel dispensing in AP -42, it is considered a fugitive emission for purposes of NSR permits and thus is not included here.
s Diesel emission factors were derived using the no.2 diesel true vapor pressure and vapor molecular weight from AP -42 Table 7.1-2 at 70F and equation 1 of section 5.2.2 with an S factor value of 1.45 for storage tank and vehicle tank filling and an S factor of 1.0 for breathing losses. 6 GDFs with a gasoline throughput of < 10,000 gallons per month have higher storage tank filling and breathing loss emissions because they are not required to install Stage I vapor recovery controls under 40 CFR 63 CCCCCC.

Using these values for an AST assumes a 45% average ullage in a 2000 gal AST

Drive -Through On Site Emissions
Total Trips/Day
Drive -Through Trips
Minutes/Trip
Distance (miles/trip)
3,080
2,156
5 0.15
EMFAC Emissions Rate (g/mi)
Pounds/Day
EMFAC Emissions Rate (g/mi)
MT/year
ROG NOX CO SO2 PM10 PM25

0.042904 0.04581 0.757827 0.003388 0.004099 0.003773

0.00 0.00 0.05 0.00 0.00 0.00
CO2 CH4 N2O CO2e
342.8382 0.00994 0.004631

3.37 0.00 0.00 3.388434
Source: EMFAC2021 (v1.0.2) Emission Rates, Los Angeles (SC) Sub -Area, Year 2027, Annual.

Notes

1. Drive-thru percent is assumed with 70%.

2. Drive -thru distances measured as a total of 0.15 mile from GoogleEarth.

Source: EMFAC2021 (v1.0.2) Emission Rates
Region Type: Sub -Area
Region: Los Angeles (SC)
Calendar Year: 2027
Season: Annual
Vehicle Classification: EMFAC2007 Categories
Units: miles/year for Combustion VMT and Electric VMT, g/mile for RUNEX, PMBW and PMTW, mph for Speed, gallon/mile for Fuel Consumption, kWh/mile for Energy Consumption.

Region Calendar Yi Vehicle Cat Model Yea' Speed Fuel Total VMT CVMT EVMT NOx_RUNE PM2.5_RUI PM10_RUI` CO2_RUNE CH4_RUNE N2O_RUNE ROG_RUNE TOG_RUNE CO_RUNEX SOx_RUNE NH3_RUNE PM10_PMI PM2.5_PM Fuel Consu Energy Con Los Angele: 2027 HHDT Aggregate 5 Gasoline 0.244457 0.244457 0 7.197845 0.007553 0.008214 4706.9 0.69922 0.266278 3.459899 5.048677 66.31138 0.046532 0.044956 0.150856 0.0528 0.547117 0 Los Angele: 2027 HHDT Aggregate 5 Diesel 457.8292 457.8292 0 10.99993 0.013838 0.014463 3045.225 0.00589 0.479776 0.126802 0.144354 1.073316 0.028836 0.215524 0.140506 0.049177 0.29986 0 Los Angele: 2027 HHDT Aggregate 5 Electricity 7.395425 0 7.395425 0 0 0 0 0 0 0 0 0 0 0 0.07534 0.026369 0 5.908862 Los Angela 2027 HHDT Aggregate 5 Natural Ga: 36.47972 36.47972 0 3.942275 0.005856 0.006369 4656.894 9.620471 0.949338 0.297337 10.00055 61.07476 0 0.750048 0.184967 0.064738 0.593336 0 Los Angele: 2027 HHDT Aggregate 10 Gasoline 4.062336 4.062336 0 6.440602 0.004829 0.005252 3825.265 0.443804 0.234901 2.202602 3.214031 58.1867 0.037817 0.044956 0.150856 0.0528 0.444639 0 Los Angele: 2027 HHDT Aggregate 10 Diesel 7335.993 7335.993 0 7.94046 0.011666 0.012194 2620.826 0.003454 0.412912 0.074359 0.084653 0.671482 0.024818 0.215479 0.14049 0.049172 0.25807 0 Los Angele: 2027 HHDT Aggregate 10 Electricity 118.2366 0 118.2366 0 0 0 0 0 0 0 0 0 0 0 0.075357 0.026375 0 2.798892 Los Angela 2027 HHDT Aggregate 10 Natural Ga: 589.9764 589.9764 0 2.778525 0.005309 0.005774 3569.07 6.534078 0.727578 0.213414 6.805287 41.95828 0 0.750449 0.184904 0.064716 0.454736 0 Los Angele: 2027 HHDT Aggregate 15 Gasoline 16.12106 16.12106 0 5.845225 0.003257 0.003542 3133.745 0.297763 0.210036 1.482238 2.162879 51.91879 0.03098 0.044956 0.148853 0.052099 0.364258 0 Los Angele: 2027 HHDT Aggregate 15 Diesel 29125.65 29125.65 0 5.20992 0.008953 0.009358 2153.216 0.001703 0.33924 0.036671 0.041747 0.371703 0.02039 0.215706 0.138573 0.0485 0.212025 0 Los Angele: 2027 HHDT Aggregate 15 Electricity 463.4035 0 463.4035 0 0 0 0 0 0 0 0 0 0 0 0.074329 0.026015 0 2.333098 Los Angela 2027 HHDT Aggregate 15 Natural Ga: 2218.169 2218.169 0 1.744735 0.004354 0.004735 2550.506 3.88391 0.519937 0.115275 4.031926 26.29771 0 0.756544 0.183321 0.064163 0.324961 0 Los Angele: 2027 HHDT Aggregate 20 Gasoline 47.86897 47.86897 0 5.404146 0.002317 0.00252 2609.858 0.210603 0.191265 1.051416 1.534224 46.81397 0.025801 0.044956 0.145622 0.050968 0.303363 0 Los Angele: 2027 HHDT Aggregate 20 Diesel 211687.7 211687.7 0 3.383386 0.005772 0.006033 1925.469 0.000966 0.303358 0.020805 0.023685 0.238675 0.018233 0.218047 0.066113 0.02314 0.189599 0 Los Angele: 2027 HHDT Aggregate 20 Electricity 5361.818 0 5361.818 0 0 0 0 0 0 0 0 0 0 0 0.021842 0.007645 0 2.071519 Los Angela 2027 HHDT Aggregate 20 Natural Ga: 7064.603 7064.603 0 1.256129 0.003556 0.003868 2043.12 2.698089 0.416503 0.065738 2.784573 19.21429 0 0.767739 0.180463 0.063162 0.260315 0 Los Angele: 2027 HHDT Aggregate 25 Gasoline 88.19587 88.19587 0 5.068495 0.001738 0.00189 2234.376 0.15721 0.176724 0.787057 1.148472 42.61068 0.022089 0.044956 0.142391 0.049837 0.259718 0 Los Angele: 2027 HHDT Aggregate 25 Diesel 184949.4 184949.4 0 3.090407 0.006536 0.006831 1721.03 0.000777 0.271149 0.016727 0.019042 0.195756 0.016297 0.21601 0.132585 0.046405 0.169468 0 Los Angele: 2027 HHDT Aggregate 25 Electricity 2900.759 0 2900.759 0 0 0 0 0 0 0 0 0 0 0 0.071178 0.024912 0 1.899864 Los Angela 2027 HHDT Aggregate 25 Natural Ga: 12908.75 12908.75 0 1.027499 0.002884 0.003137 1737.62 2.116008 0.354225 0.051301 2.183544 15.13701 0 0.765232 0.179706 0.062897 0.221391 0 Los Angele: 2027 HHDT Aggregate 30 Gasoline 152.82 152.82 0 4.834112 0.001374 0.001494 1984.24 0.123643 0.16616 0.620634 0.905627 39.04468 0.019616 0.044956 0.140388 0.049136 0.230643 0 Los Angele: 2027 HHDT Aggregate 30 Diesel 343330.4 343330.4 0 2.372445 0.00665 0.00695 1599.923 0.000635 0.252068 0.013672 0.015565 0.154522 0.01515 0.216082 0.130734 0.045757 0.157543 0 Los Angele: 2027 HHDT Aggregate 30 Electricity 5366.048 0 5366.048 0 0 0 0 0 0 0 0 0 0 0 0.070203 0.024571 0 1.523504 Los Angela 2027 HHDT Aggregate 30 Natural Ga: 23396.49 23396.49 0 0.87548 0.002376 0.002584 1527.8 1.746189 0.311452 0.042857 1.802516 12.29239 0 0.767718 0.178577 0.062502 0.194658 0 Los Angele: 2027 HHDT Aggregate 35 Gasoline 181.4199 181.4199 0 4.673406 0.001145 0.001245 1838.846 0.102554 0.158534 0.516023 0.752979 36.0322 0.018179 0.044956 0.11881 0.041584 0.213743 0 Los Angele: 2027 HHDT Aggregate 35 Diesel 446563.5 446563.5 0 1.797369 0.007664 0.008011 1504.363 0.000528 0.237013 0.011359 0.012931 0.119585 0.014245 0.21633 0.11087 0.038805 0.148133 0 Los Angele: 2027 HHDT Aggregate 35 Electricity 6882.503 0 6882.503 0 0 0 0 0 0 0 0 0 0 0 0.060031 0.021011 0 1.549735 Los Angela 2027 HHDT Aggregate 35 Natural Ga: 28147.2 28147.2 0 0.755963 0.002004 0.002179 1373.768 1.481489 0.280052 0.036075 1.528952 10.14851 0 0.777062 0.168835 0.059092 0.175032 0 Los Angele: 2027 HHDT Aggregate 40 Gasoline 195.3206 195.3206 0 4.581229 0.001005 0.001093 1777.608 0.089606 0.153608 0.451845 0.659332 33.45815 0.017573 0.044956 0.103174 0.036111 0.206624 0 Los Angele: 2027 HHDT Aggregate 40 Diesel 426388.1 426388.1 0 1.406753 0.009647 0.010083 1446.671 0.000459 0.227924 0.009883 0.011252 0.091272 0.013699 0.216093 0.096635 0.033822 0.142452 0 Los Angele: 2027 HHDT Aggregate 40 Electricity 6645.305 0 6645.305 0 0 0 0 0 0 0 0 0 0 0 0.053008 0.018553 0 1.641432 Los Angela 2027 HHDT Aggregate 40 Natural Ga: 28959.85 28959.85 0 0.689983 0.001748 0.001901 1253.514 1.295732 0.255537 0.031829 1.33756 8.581296 0 0.768814 0.16488 0.057708 0.159711 0 Los Angele: 2027 HHDT Aggregate 45 Gasoline 216.7851 216.7851 0 4.547067 0.000929 0.001011 1780.13 0.082534 0.150982 0.416969 0.60844 31.30197 0.017598 0.044956 0.087537 0.030638 0.206918 0 Los Angele: 2027 HHDT Aggregate 45 Diesel 458530.2 458530.2 0 1.1741 0.012518 0.013084 1414.127 0.000424 0.222796 0.009125 0.010388 0.068891 0.013391 0.215817 0.082468 0.028864 0.139248 0 Los Angele: 2027 HHDT Aggregate 45 Electricity 7257.416 0 7257.416 0 0 0 0 0 0 0 0 0 0 0 0.046072 0.016125 0 1.742847 Los Angela 2027 HHDT Aggregate 45 Natural Ga: 33557.2 33557.2 0 0.642296 0.001639 0.001782 1156.28 1.15356 0.235715 0.028608 1.191107 7.376347 0 0.759829 0.161624 0.056568 0.147322 0 Los Angele: 2027 HHDT Aggregate 50 Gasoline 196.3866 196.3866 0 4.545667 0.000905 0.000984 1828.176 0.080315 0.149797 0.406437 0.593071 29.60497 0.018073 0.044956 0.076279 0.026698 0.212502 0 Los Angele: 2027 HHDT Aggregate 50 Diesel 388441.8 388441.8 0 1.092312 0.016258 0.016993 1409.681 0.000421 0.222096 0.009068 0.010323 0.052629 0.013349 0.215568 0.072337 0.025318 0.13881 0 Los Angele: 2027 HHDT Aggregate 50 Electricity 6266.475 0 6266.475 0 0 0 0 0 0 0 0 0 0 0 0.041208 0.014423 0 1.744645 Los Angela 2027 HHDT Aggregate 50 Natural Ga: 30562.08 30562.08 0 0.607139 0.001672 0.001819 1075.865 1.041801 0.219322 0.026218 1.076146 6.452777 0 0.751097 0.160271 0.056095 0.137076 0 Los Angele: 2027 HHDT Aggregate 55 Gasoline 215.5132 215.5132 0 4.610239 0.000928 0.00101 1899.203 0.082204 0.151136 0.416524 0.607791 28.25332 0.018776 0.044956 0.076279 0.026698 0.220758 0 Los Angele: 2027 HHDT Aggregate 55 Diesel 441861.6 441861.6 0 1.150771 0.020923 0.021869 1428.883 0.000452 0.225121 0.009738 0.011086 0.042488 0.013531 0.215559 0.07235 0.025323 0.140701 0 Los Angele: 2027 HHDT Aggregate 55 Electricity 7144.219 0 7144.219 0 0 0 0 0 0 0 0 0 0 0 0.041214 0.014425 0 1.793761 Los Angela 2027 HHDT Aggregate 55 Natural Ga: 34823.26 34823.26 0 0.575183 0.001834 0.001994 1009.755 0.949277 0.205845 0.024273 0.981009 5.711625 0 0.750469 0.160455 0.056159 0.128653 0 Los Angele: 2027 HHDT Aggregate 60 Gasoline 312.4496 312.4496 0 4.717896 0.001002 0.00109 1973.12 0.08875 0.154253 0.450125 0.656822 27.37917 0.019506 0.044956 0.076279 0.026698 0.22935 0 Los Angele: 2027 HHDT Aggregate 60 Diesel 823147.9 823147.9 0 1.309893 0.026623 0.027826 1463.16 0.000514 0.230521 0.011068 0.0126 0.038037 0.013855 0.21628 0.071942 0.02518 0.144076 0 Los Angele: 2027 HHDT Aggregate 60 Electricity 12805.57 0 12805.57 0 0 0 0 0 0 0 0 0 0 0 0.040365 0.014128 0 1.790573 Los Angela 2027 HHDT Aggregate 60 Natural Ga: 52685.29 52685.29 0 0.550632 0.001875 0.002039 1014.185 0.93871 0.206748 0.023239 0.969218 5.580524 0 0.772392 0.154081 0.053928 0.129218 0 Los Angele: 2027 HHDT Aggregate 65 Gasoline 364.1469 364.1469 0 4.882062 0.00114 0.00124 2031.757 0.100853 0.159609 0.511804 0.746823 27.0399 0.020086 0.044956 0.076279 0.026698 0.236166 0 Los Angele: 2027 HHDT Aggregate 65 Diesel 789053.7 789053.7 0 1.68528 0.032895 0.034383 1545.131 0.000608 0.243436 0.01308 0.01489 0.040552 0.014631 0.215983 0.072113 0.02524 0.152148 0 Los Angele: 2027 HHDT Aggregate 65 Electricity 12511.01 0 12511.01 0 0 0 0 0 0 0 0 0 0 0 0.040766 0.014268 0 1.887754 Los Angela 2027 HHDT Aggregate 65 Natural Ga: 56136.5 56136.5 0 0.562259 0.001893 0.002059 1012.083 0.943457 0.20632 0.023671 0.974477 5.643557 0 0.761733 0.157177 0.055012 0.12895 0 Los Angele: 2027 HHDT Aggregate 70 Gasoline 401.5379 401.5379 0 5.107487 0.001239 0.001347 2049.856 0.108292 0.167118 0.549414 0.801704 26.82242 0.020265 0.044956 0.076279 0.026698 0.23827 0 Los Angele: 2027 HHDT Aggregate 70 Diesel 2367122 2367122 0 1.597705 0.03353 0.035046 1514.682 0.000611 0.238639 0.013145 0.014965 0.039643 0.014343 0.217574 0.071135 0.024897 0.149149 0 Los Angele: 2027 HHDT Aggregate 70 Electricity 33731.43 0 33731.43 0 0 0 0 0 0 0 0 0 0 0 0.038562 0.013497 0 1.805204 Los Angela 2027 HHDT Aggregate 70 Natural Ga: 86762.76 86762.76 0 0.444124 0.001715 0.001865 1033.958 0.895914 0.210779 0.019338 0.921795 5.004815 0 0.868661 0.126083 0.044129 0.131737 0 Los Angele 2027 LDA Aggregate 5 Gasoline 159436.1 159436.1 0 0.059305 0.007688 0.008361 635.1271 0.013503 0.007272 0.049184 0.071769 1.293801 0.006279 0.037156 0.005951 0.002083 0.073825 0 Los Angela 2027 LDA Aggregate 5 Diesel 246.675 246.675 0 0.218859 0.061156 0.063921 582.388 0.012695 0.091755 0.273317 0.311153 4.550629 0.005518 0.0031 0.00609 0.002131 0.057347 0 Los Angele 2027 LDA Aggregate 5 Electricity 269547.5 0 269547.5 0 0 0 0 0 0 0 0 0 0 0 0.001328 0.000465 0 0.694461 Los Angela 2027 LDA Aggregate 5 Plug-in HyL 37636.65 2867.896 34768.76 0.001859 0.000582 0.000633 63.83611 0.000642 0.000331 0.002044 0.002982 0.161475 0.000631 0.003059 0.001329 0.000465 0.00742 0.481429 Los Angele 2027 LDA Aggregate 10 Gasoline 938973.8 938973.8 0 0.051864 0.004844 0.005269 513.5241 0.008505 0.006376 0.031034 0.045285 1.157195 0.005077 0.037156 0.007359 0.002576 0.059691 0 Los Angele: 2027 LDA Aggregate 10 Diesel 1452.754 1452.754 0 0.202658 0.04457 0.046585 485.1841 0.009323 0.076441 0.200729 0.228516 3.391043 0.004597 0.0031 0.007531 0.002636 0.047776 0 Los Angele: 2027 LDA Aggregate 10 Electricity 431226.1 0 431226.1 0 0 0 0 0 0 0 0 0 0 0 0.002349 0.000822 0 0.468686 Los Angela 2027 LDA Aggregate 10 Plug-in HyL 155909.3 16890.02 139019.2 0.001709 0.00052 0.000566 63.48253 0.000435 0.000305 0.001386 0.002023 0.136282 0.000628 0.004349 0.002351 0.000823 0.007379 0.329548 Los Angele 2027 LDA Aggregate 15 Gasoline 2174546 2174546 0 0.045665 0.00322 0.003502 420.0445 0.005668 0.005625 0.020718 0.030232 1.054359 0.004153 0.037156 0.00876 0.003066 0.048825 0 Los Angela 2027 LDA Aggregate 15 Diesel 3364.397 3364.397 0 0.173157 0.033574 0.035092 399.0626 0.005126 0.062872 0.110363 0.125641 1.73048 0.003781 0.0031 0.008965 0.003138 0.039295 0 Los Angele 2027 LDA Aggregate 15 Electricity 960377.5 0 960377.5 0 0 0 0 0 0 0 0 0 0 0 0.00337 0.00118 0 0.39428 Los Angela 2027 LDA Aggregate 15 Plug-in HyL 379362.6 39115.18 340247.5 0.001253 0.000329 0.000358 49.15077 0.000269 0.000223 0.000857 0.001251 0.096469 0.000486 0.004139 0.003374 0.001181 0.005713 0.286883 Los Angele 2027 LDA Aggregate 20 Gasoline 6576761 6576761 0 0.040872 0.002258 0.002456 349.39 0.003985 0.005041 0.014587 0.021285 0.965394 0.003454 0.037156 0.010169 0.003559 0.040612 0 Los Angela 2027 LDA Aggregate 20 Diesel 10175.38 10175.38 0 0.154368 0.026206 0.027391 327.3609 0.002643 0.051576 0.056899 0.064775 0.758603 0.003102 0.0031 0.010406 0.003642 0.032235 0 Los Angele 2027 LDA Aggregate 20 Electricity 1410379 0 1410379 0 0 0 0 0 0 0 0 0 0 0 0.004395 0.001538 0 0.369213 Los Angela 2027 LDA Aggregate 20 Plug-in HyL 613269.4 118301.1 494968.3 0.001947 0.000431 0.000468 79.46407 0.000371 0.000347 0.001181 0.001724 0.146532 0.000786 0.007744 0.0044 0.00154 0.009237 0.241931 Los Angele 2027 LDA Aggregate 25 Gasoline 13839714 13839714 0 0.037194 0.00167 0.001816 298.7713 0.002953 0.004592 0.010824 0.015795 0.886019 0.002954 0.037156 0.011327 0.003964 0.034728 0 Los Angele: 2027 LDA Aggregate 25 Diesel 21412.42 21412.42 0 0.148495 0.021246 0.022207 274.4075 0.001848 0.043233 0.039792 0.045301 0.494214 0.0026 0.0031 0.011591 0.004057 0.027021 0 Los Angele 2027 LDA Aggregate 25 Electricity 1540421 0 1540421 0 0 0 0 0 0 0 0 0 0 0 0.005001 0.00175 0 0.365378 Los Angela 2027 LDA Aggregate 25 Plug-in HyL 744448.3 248945.3 495503 0.002923 0.000552 0.0006 122.9932 0.000507 0.000521 0.001616 0.002358 0.216017 0.001216 0.013424 0.005008 0.001753 0.014296 0.191541 Los Angele 2027 LDA Aggregate 30 Gasoline 21653382 21653382 0 0.034494 0.001302 0.001416 264.9745 0.002306 0.00426 0.008459 0.012344 0.813224 0.00262 0.037156 0.012249 0.004287 0.0308 0 Los Angela 2027 LDA Aggregate 30 Diesel 33501.51 33501.51 0 0.147946 0.017988 0.018801 237.6873 0.00148 0.037448 0.031866 0.036278 0.389933 0.002252 0.0031 0.012536 0.004388 0.023405 0 Los Angele 2027 LDA Aggregate 30 Electricity 1544359 0 1544359 0 0 0 0 0 0 0 0 0 0 0 0.00519 0.001817 0 0.365798 Los Angela 2027 LDA Aggregate 30 Plug-in HyL 785374.7 389495.6 395879.1 0.003862 0.000637 0.000693 166.1334 0.00062 0.000688 0.001973 0.002879 0.27982 0.001642 0.019908 0.005199 0.001819 0.019311 0.142655 Los Angele 2027 LDA Aggregate 35 Gasoline 19608287 19608287 0 0.032584 0.001071 0.001165 245.3409 0.001897 0.004025 0.006963 0.01016 0.747387 0.002425 0.037156 0.013164 0.004608 0.028518 0 Los Angela 2027 LDA Aggregate 35 Diesel 30337.4 30337.4 0 0.149437 0.015847 0.016563 214.8645 0.001246 0.033852 0.026829 0.030543 0.325383 0.002036 0.0031 0.013472 0.004715 0.021157 0 Los Angele 2027 LDA Aggregate 35 Electricity 1451455 0 1451455 0 0 0 0 0 0 0 0 0 0 0 0.005383 0.001884 0 0.367514 Los Angela 2027 LDA Aggregate 35 Plug-in HyL 636821.9 352709 284113 0.003919 0.000585 0.000637 171.3375 0.000587 0.000698 0.001869 0.002727 0.278134 0.001694 0.022234 0.005392 0.001887 0.019916 0.124866 Los Angele 2027 LDA Aggregate 40 Gasoline 9922670 9922670 0 0.031256 0.000929 0.001011 237.2286 0.001645 0.003859 0.006039 0.008812 0.689382 0.002345 0.037156 0.012031 0.004211 0.027575 0 Los Angela 2027 LDA Aggregate 40 Diesel 15352.08 15352.08 0 0.152081 0.014498 0.015154 201.0651 0.001097 0.031678 0.023607 0.026875 0.284551 0.001905 0.0031 0.012312 0.004309 0.019799 0 Los Angele 2027 LDA Aggregate 40 Electricity 1263922 0 1263922 0 0 0 0 0 0 0 0 0 0 0 0.004971 0.00174 0 0.372577 Los Angela 2027 LDA Aggregate 40 Plug-in HyL 370270.8 178486.5 191784.3 0.003136 0.000442 0.000481 139.1933 0.000443 0.000559 0.00141 0.002058 0.218858 0.001376 0.019351 0.004978 0.001742 0.016179 0.151694 Los Angele: 2027 LDA Aggregate 45 Gasoline 7882908 7882908 0 0.030455 0.00085 0.000925 237.8578 0.001504 0.003758 0.005519 0.008054 0.638666 0.002351 0.037156 0.008849 0.003097 0.027648 0 Los Angela 2027 LDA Aggregate 45 Diesel 12196.22 12196.22 0 0.155466 0.013763 0.014385 194.2134 0.001006 0.030598 0.021655 0.024653 0.259914 0.00184 0.0031 0.009056 0.00317 0.019124 0 Los Angele 2027 LDA Aggregate 45 Electricity 934301.7 0 934301.7 0 0 0 0 0 0 0 0 0 0 0 0.003949 0.001382 0 0.380162 Los Angela 2027 LDA Aggregate 45 Plug-in HyL 256593.5 141795.8 114797.7 0.003337 0.000463 0.000504 150.2066 0.000448 0.000595 0.001426 0.00208 0.229786 0.001485 0.022184 0.003956 0.001385 0.01746 0.133664 Los Angele 2027 LDA Aggregate 50 Gasoline 6009343 6009343 0 0.029962 0.00082 0.000892 245.2441 0.001452 0.003693 0.005325 0.007771 0.599084 0.002424 0.037156 0.005659 0.001981 0.028507 0 Los Angele: 2027 LDA Aggregate 50 Diesel 9297.488 9297.488 0 0.159281 0.013556 0.014169 194.7078 0.000961 0.030676 0.0207 0.023566 0.248089 0.001845 0.0031 0.005791 0.002027 0.019173 0 Los Angele 2027 LDA Aggregate 50 Electricity 533514.7 0 533514.7 0 0 0 0 0 0 0 0 0 0 0 0.002931 0.001026 0 0.391342 Los Angela 2027 LDA Aggregate 50 Plug-in HyL 163272.4 108094.6 55177.89 0.003713 0.000536 0.000583 170.9418 0.00048 0.000662 0.00153 0.002232 0.256896 0.00169 0.026577 0.002936 0.001028 0.01987 0.10361 Los Angele 2027 LDA Aggregate 55 Gasoline 5258663 5258663 0 0.030152 0.000835 0.000908 255.2055 0.001475 0.00371 0.005405 0.007887 0.559354 0.002523 0.037156 0.003643 0.001275 0.029664 0 Los Angela 2027 LDA Aggregate 55 Diesel 8136.058 8136.058 0 0.163519 0.013868 0.014495 203.7464 0.000959 0.0321 0.02064 0.023497 0.248275 0.001931 0.0031 0.003728 0.001305 0.020063 0 Los Angele 2027 LDA Aggregate 55 Electricity 211109.4 0 211109.4 0 0 0 0 0 0 0 0 0 0 0 0.002163 0.000757 0 0.406738 Los Angela 2027 LDA Aggregate 55 Plug-in HyL 113306.9 94591.52 18715.37 0.004403 0.000688 0.000749 205.3414 0.000547 0.000785 0.001743 0.002543 0.302133 0.00203 0.033513 0.002167 0.000758 0.023868 0.055209 Los Angele 2027 LDA Aggregate 60 Gasoline 6770750 6770750 0 0.030975 0.000896 0.000974 265.4212 0.001579 0.003803 0.005778 0.008432 0.523784 0.002624 0.037156 0.002793 0.000978 0.030852 0 Los Angela 2027 LDA Aggregate 60 Diesel 10475.52 10475.52 0 0.168624 0.014836 0.015507 220.8856 0.001012 0.034801 0.02179 0.024806 0.26777 0.002093 0.0031 0.002858 0.001 0.02175 0 Los Angele 2027 LDA Aggregate 60 Electricity 54057.99 0 54057.99 0 0 0 0 0 0 0 0 0 0 0 0.001644 0.000575 0 0.426187 Los Angela 2027 LDA Aggregate 60 Plug-in HyL 125409.4 121790.6 3618.813 0.004859 0.00086 0.000936 228.4889 0.00058 0.000866 0.001848 0.002696 0.329746 0.002259 0.038985 0.001647 0.000577 0.026559 0.010149 Los Angele: 2027 LDA Aggregate 65 Gasoline 6150067 6150067 0 0.031822 0.001014 0.001103 274.5788 0.001789 0.003897 0.006538 0.00954 0.499497 0.002714 0.037156 0.001943 0.00068 0.031916 0 Los Angela 2027 LDA Aggregate 65 Diesel 9515.213 9515.213 0 0.173996 0.016597 0.017347 248.3201 0.001126 0.039123 0.024245 0.027601 0.309036 0.002353 0.0031 0.001988 0.000696 0.024452 0 Los Angele 2027 LDA Aggregate 65 Electricity 7890.789 0 7890.789 0 0 0 0 0 0 0 0 0 0 0 0.001128 0.000395 0 0.446191 Los Angela 2027 LDA Aggregate 65 Plug-in HyL 111013.7 110625.9 387.7888 0.004671 0.001 0.001088 226.1018 0.000549 0.000832 0.001747 0.00255 0.324034 0.002235 0.040003 0.00113 0.000396 0.026281 0.001349 Los Angele 2027 LDA Aggregate 70 Gasoline 16559765 16559765 0 0.034121 0.0011 0.001197 273.2183 0.001917 0.004171 0.007 0.010215 0.460528 0.002701 0.037156 0.001943 0.00068 0.031758 0 Los Angele: 2027 LDA Aggregate 70 Diesel 25620.81 25620.81 0 0.177437 0.017824 0.01863 268.1464 0.001206 0.042247 0.025956 0.02955 0.33792 0.002541 0.0031 0.001988 0.000696 0.026404 0 Los Angele 2027 LDA Aggregate 70 Electricity 1279.818 0 1279.818 0 0 0 0 0 0 0 0 0 0 0 0.001128 0.000395 0 0.495717 Los Angela 2027 LDA Aggregate 70 Plug-in HyL 297896.2 297872.9 23.31653 0.004664 0.00109 0.001186 215.1951 0.000503 0.000831 0.001602 0.002338 0.292253 0.002127 0.04014 0.00113 0.000396 0.025014 3.02E-05 Los Angele: 2027 LDT1 Aggregate 5 Gasoline 13987.14 13987.14 0 0.244796 0.011424 0.012425 761.8716 0.041683 0.017552 0.182045 0.265639 2.987045 0.007532 0.038704 0.008476 0.002966 0.088558 0 Los Angela 2027 LDT1 Aggregate 5 Diesel 1.15187 1.15187 0 0.901154 0.83407 0.871783 999.6286 0.051866 0.157492 1.116634 1.271214 5.470057 0.009472 0.0031 0.009638 0.003373 0.098432 0 Los Angele 2027 LDT1 Aggregate 5 Electricity 1778.935 0 1778.935 0 0 0 0 0 0 0 0 0 0 0 0.001327 0.000464 0 0.694461 Los Angela 2027 LDT1 Aggregate 5 Plug-in HyL 464.9625 30.13586 434.8266 0.001581 0.000338 0.000368 54.35756 0.000546 0.000282 0.001738 0.002537 0.137827 0.000537 0.002722 0.001324 0.000463 0.006318 0.487363 Los Angele 2027 LDT1 Aggregate 10 Gasoline 82375.06 82375.06 0 0.208467 0.007309 0.007949 616.3222 0.026862 0.015078 0.117644 0.171666 2.621262 0.006093 0.038704 0.010545 0.003691 0.07164 0 Los Angela 2027 LDT1 Aggregate 10 Diesel 6.78376 6.78376 0 0.946752 0.580748 0.607007 841.4539 0.036145 0.132571 0.778182 0.885909 3.890427 0.007973 0.0031 0.011991 0.004197 0.082857 0 Los Angele 2027 LDT1 Aggregate 10 Electricity 2845.967 0 2845.967 0 0 0 0 0 0 0 0 0 0 0 0.002348 0.000822 0 0.468686 Los Angela 2027 LDT1 Aggregate 10 Plug-in HyL 1916.089 177.4804 1738.609 0.001461 0.000304 0.000331 54.3288 0.000372 0.00026 0.001185 0.001729 0.116867 0.000537 0.00389 0.002343 0.00082 0.006315 0.335353

Los Angela 2027 LDT1 Aggregate
Los Angele 2027 LDT1 Aggregate
Los Angela 2027 LDT1 Aggregate
Los Angele 2027 LDT1 Aggregate
Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
Los Angele 2027 LDT1 Aggregate
Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
Los Angele 2027 LDT1 Aggregate
Los Angela 2027 LDT1 Aggregate
Los Angele 2027 LDT1 Aggregate
Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT1 Aggregate
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Los Angela 2027 LDT2 Aggregate
Los Angele 2027 LDT2 Aggregate
Los Angela 2027 LDT2 Aggregate
Los Angele 2027 LDT2 Aggregate
Los Angela 2027 LDT2 Aggregate
Los Angele 2027 LDT2 Aggregate
Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
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Los Angela 2027 LDT2 Aggregate
Los Angele 2027 LDT2 Aggregate
Los Angela 2027 LDT2 Aggregate
Los Angele 2027 LDT2 Aggregate
Los Angela 2027 LDT2 Aggregate
Los Angele 2027 LDT2 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
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45 Gasoline
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Plug-in Hyt
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Plug-in Hyt
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Plug-in Hyt
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Gasoline
190770.3

15.71034
6338.212
4666.241
576971.5

47.51482
9308.09
7433.304
1214142

99.98713
10166.33
8812.8
1899626
156.4382
10192.32
9043.782
1720212
141.6631
9579.178
7259.453
870504.2

71.68785
8341.517
4274.038
691558.2

56.95128
6166.12
2925.679
527192.6

43.41542
3521.042
1825.926
461336.4

37.99202
1393.261
1228.027
593990

48.91632
356.767
1325.033
539538.2

44.43211

52.07691
1167.307
1452769
119.6386

8.446427
3130.341
87628.77
306.551
18480.49
8102.316
516075.9
1805.384
29565.36
33459.09
1195167
4181.043
65844.59
81454.96
3614700
12645.27
96697.19
130528.2
7606542
26609.9
105613
156248.3
11901067
41633.4
105883
162188.5
10777048
37701.25
99513.39
130740.4
5453668
19078.52
86655.93
76572.43
4332580
15156.63
64056.8
52685.68
3302837
11554.29
36578.38
33151.12
2890251
10110.94
14473.9
22597.16
3721319
13018.26
3706.278
24653.76
3380182
11824.86
541.0016
21764.95
9101528
31839.8

87.7458
58383.26
1162.975
422.3919

59.23935
15698.87
5453.73
789.3216
54141.26
19324.17
2743.663
163457.4
71476.37
8831.004
308637.2
132805.3
16584.68
490529.9
228002.9
27064.6
512109.2
269901.2
29583.9
421734.1
196054.5
23270.03
422239.9
190770.3

15.71034
0 411.0224
576971.5

47.51482
0 1243.108
1214142

99.98713
0 2615.918
1899626
156.4382
0 4092.821
1720212
141.6631
0 3706.266
870504.2

71.68785
0 1875.536
691558.2

56.95128
0 1489.99
527192.6

43.41542
0 1135.858
461336.4

37.99202
0 993.9678
593990

48.91632
0 1279.775
539538.2

44.43211
0 1162.457
1452769
119.6386
0 3130.049
87628.77
306.551
0 562.0605
516075.9
1805.384
0 3310.168
1195167
4181.043
0 7665.934
3614700
12645.27
0 23185.08
7606542
26609.9
0 48789.19
11901067
41633.4
0 76334.75
10777048
37701.25
0 69125.16
5453668
19078.52
0 34980.42
4332580
15156.63
0 27789.64
3302837
11554.29
0 21184.76
2890251
10110.94
0 18538.38
3721319
13018.26
0 23868.95
3380182
11824.86
0 21680.85
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0 Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
Los Angele 2027 LHDT1 Aggregate
Los Angela 2027 LHDT1 Aggregate
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45 45
50 50
50 55
55 55
60 60
60 65
65 65
70 70
70 5
5 5
10 10
10 15
15 15
20 20
20 25
25 25
30 30
30 35
35 35
40 40
40 45
45 45
50 50
50 55
55 55
60 60
60 65
65 65
70 70
70 5
10 15
20 25
30 35
40 45
50 55
60 65
70 5
5 5
5 10
10 10
10 15
15 15
15 20
20 20
20 25
25 25
25 30
30 30
30 35
35 35
35 40
40 40
40 45
45 45
45 50
50 50
50 55
55 55
55 60
60 60
60 65
65 65
65 70
70 70
70 Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Diesel
Electricity
Gasoline
Gasoline
Gasoline
Gasoline
Gasoline
Gasoline
Gasoline
Gasoline
Gasoline
Gasoline
Gasoline
Gasoline
Gasoline
Gasoline
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
Gasoline
Diesel
Electricity
Plug-in HyL
178721.5
22565.47
341282.3
134342.3
17817.3
351556.5
143535.8
18568.37
501040.7
275035.4
29401.77
507736.8
229289.3
27734.15
852747.9
903321
68186.32
163.5466
189.8018

12.76 2207.697
2450.634
167.7021
7613.762
8683.318
587.8051
22986.64
32117.92
2015.201
43402.94
59676.06
3765.596
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102453.1
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121280.1
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71401.86
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119920
405907.4
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54303.42
114272.6
178789
161902.9
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65088.09
49618.32
43420.06
55905.16
50780.27
136731.7
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555.9769
19580.64
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281564.9
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652069.1
7582.959
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1972137
22934.13
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4150039
48261.11
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6493081
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1576887
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23610.6
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1844187
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4965686
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92.96932
33248.57
178721.5
0 341282.3
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0 351556.5
143535.8
0 501040.7
275035.4
0 507736.8
229289.3
0 852747.9
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0 1316.442
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54303.42
114272.6
178789
161902.9
81930.13
65088.09
49618.32
43420.06
55905.16
50780.27
136731.7
47809.22
555.9769
0 320.087
281564.9
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0 1885.102
652069.1
7582.959
0 4365.661
1972137
22934.13
0 13203.63
4150039
48261.11
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6493081
75508.52
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5879830
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2363804
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1801989
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3.31E-05

Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MH Aggregate
Los Angele 2027 MH Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 MHDT Aggregate
Los Angele 2027 MHDT Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
Los Angele 2027 OBUS Aggregate
Los Angela 2027 OBUS Aggregate
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Gasoline
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Diesel
Gasoline
Diesel
Gasoline
Diesel
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Diesel
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Diesel
Gasoline
Diesel
Gasoline
Diesel
Gasoline
Diesel
Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline
Diesel
Electricity
Natural Ga:

Gasoline

94.52034

32.22739
575.9587
188.7081
1832.601
611.1971
5399.611
1993.333
10292.58
3829.995
15294.68
5947.896
15259.2
6251.285
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4839.737
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4729.259
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482.5025
1742.761

62.83571

28.28481
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52541.04
187064
6782.55
3170.146
78075.48
276745.2
10056.46
4791.462
77894.4
271982.8
9933.043
4854.645
63682.14
227325.3
8244.277
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233572.6
8429.755
3938.042
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198059.7
7201.044
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273921.7
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255328.2
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8.41369

49.30749
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24.58936
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65.13267
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2009.537
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14046.74
344.4888
2018.838
11716.04
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342.7871
2008.866
13116.31
18418.05
383.756
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19100.17

94.52034

32.22739
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6251.285
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10021.9
482.5025
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0 28.28481
2940.124
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98316.97
0 1658.35
52541.04
187064
0 3170.146
78075.48
276745.2
0 4791.462
77894.4
271982.8
0 4854.645
63682.14
227325.3
0 3917.623
64339.41
233572.6
0 3938.042
55957.53
198059.7
0 3418.305
60219.78
209239.7
0 3719.102
83350.93
273921.7
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263476.9
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255328.2
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11719.96
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Los Angela 2027 OBUS Aggregate 60 Diesel 31153.35 31153.35 0 1.311437 0.033893 0.035426 1384.571 0.001531 0.21814 0.03296 0.037522 0.107796 0.013111 0.213081 0.058773 0.020571 0.136337 0 Los Angele 2027 OBUS Aggregate 60 Electricity 558.8313 0 558.8313 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.065251 Los Angela 2027 OBUS Aggregate 60 Natural Ga: 3274.968 3274.968 0 0.080186 0.000569 0.000618 685.5978 0.364429 0.139764 0.005207 0.371927 1.445158 0 1.06 0.041585 0.014555 0.087352 0 Los Angele: 2027 OBUS Aggregate 65 Gasoline 9309.122 9309.122 0 0.390061 0.000773 0.00084 1667.421 0.008054 0.018864 0.039327 0.057386 0.902052 0.016484 0.04499 0.041585 0.014555 0.193816 0 Los Angela 2027 OBUS Aggregate 65 Diesel 17556.25 17556.25 0 1.609286 0.037754 0.039461 1499.409 0.001497 0.236233 0.03222 0.03668 0.103296 0.014199 0.214016 0.060351 0.021123 0.147645 0 Los Angele 2027 OBUS Aggregate 65 Electricity 272.3656 0 272.3656 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.123067 Los Angela 2027 OBUS Aggregate 65 Natural Ga: 1596.168 1596.168 0 0.08041 0.000569 0.000618 685.5978 0.364429 0.139764 0.005207 0.371927 1.445158 0 1.06 0.041585 0.014555 0.087352 0 Los Angele: 2027 OBUS Aggregate 70 Gasoline 9.486073 9.486073 0 0.394727 0.000839 0.000913 1682.784 0.0088 0.019094 0.042971 0.062704 0.913489 0.016636 0.04499 0.041585 0.014555 0.195602 0 Los Angela 2027 OBUS Aggregate 70 Diesel 16.52692 16.52692 0 1.611131 0.038196 0.039923 1481.207 0.001568 0.233365 0.033762 0.038436 0.10823 0.014026 0.213523 0.059518 0.020831 0.145853 0 Los Angele 2027 OBUS Aggregate 70 Electricity 0.277543 0 0.277543 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.073955 Los Angela 2027 OBUS Aggregate 70 Natural Ga: 1.626509 1.626509 0 0.080251 0.000569 0.000618 685.5978 0.364429 0.139764 0.005207 0.371927 1.445158 0 1.06 0.041585 0.014555 0.087352 0 Los Angele 2027 SBUS Aggregate 5 Gasoline 1908.186 1908.186 0 0.687611 0.004679 0.005089 1868.397 0.047791 0.039608 0.235739 0.343989 1.730854 0.018471 0.045 0.061496 0.021524 0.217177 0 Los Angela 2027 SBUS Aggregate 5 Diesel 834.5888 834.5888 0 18.27244 0.137289 0.143497 2394.688 0.041606 0.377284 0.895765 1.01976 1.2409 0.022676 0.096897 0.061496 0.021524 0.235803 0 Los Angele 2027 SBUS Aggregate 5 Electricity 67.21372 0 67.21372 0 0 0 0 0 0 0 0 0 0 0 0.030748 0.010762 0 3.515312 Los Angela 2027 SBUS Aggregate 5 Natural Ga: 1195.589 1195.589 0 6.434457 0.011267 0.012254 8856.763 26.46876 1.805509 0.378186 27.01331 97.75756 0 1.06 0.061496 0.021524 1.128443 0 Los Angele 2027 SBUS Aggregate 10 Gasoline 2734.49 2734.49 0 0.60176 0.002944 0.003202 1516.803 0.029963 0.034663 0.147797 0.215665 1.570853 0.014995 0.045 0.061496 0.021524 0.176309 0 Los Angela 2027 SBUS Aggregate 10 Diesel 1195.992 1195.992 0 15.01659 0.113569 0.118705 2101.626 0.031239 0.331112 0.672564 0.765663 1.011103 0.019901 0.096897 0.061496 0.021524 0.206945 0 Los Angele 2027 SBUS Aggregate 10 Electricity 96.31934 0 96.31934 0 0 0 0 0 0 0 0 0 0 0 0.030748 0.010762 0 1.665122 Los Angela 2027 SBUS Aggregate 10 Natural Ga: 1713.316 1713.316 0 3.466889 0.01022 0.011115 5649.466 16.26411 1.151681 0.232382 16.59872 58.24338 0 1.06 0.061496 0.021524 0.7198 0 Los Angele 2027 SBUS Aggregate 15 Gasoline 3917.545 3917.545 0 0.534205 0.001954 0.002125 1240.551 0.019835 0.030772 0.097838 0.142764 1.430681 0.012264 0.045 0.061496 0.021524 0.144198 0 Los Angela 2027 SBUS Aggregate 15 Diesel 1713.427 1713.427 0 10.40929 0.075523 0.078938 1703.324 0.01621 0.268359 0.349007 0.397318 0.683387 0.016129 0.096897 0.061496 0.021524 0.167725 0 Los Angele 2027 SBUS Aggregate 15 Electricity 137.9911 0 137.9911 0 0 0 0 0 0 0 0 0 0 0 0.030748 0.010762 0 1.388011 Los Angela 2027 SBUS Aggregate 15 Natural Ga: 2454.568 2454.568 0 1.589914 0.008312 0.00904 3206.264 8.805781 0.653618 0.125817 8.986945 30.33202 0 1.06 0.061496 0.021524 0.408511 0 Los Angele: 2027 SBUS Aggregate 20 Gasoline 4743.824 4743.824 0 0.480189 0.001368 0.001488 1031.306 0.013876 0.02766 0.068445 0.099875 1.308759 0.010196 0.045 0.06063 0.021221 0.119876 0 Los Angela 2027 SBUS Aggregate 20 Diesel 2074.819 2074.819 0 8.014307 0.049459 0.051696 1421.362 0.00775 0.223936 0.166865 0.189963 0.470836 0.013459 0.096897 0.06063 0.021221 0.13996 0 Los Angele 2027 SBUS Aggregate 20 Electricity 167.0959 0 167.0959 0 0 0 0 0 0 0 0 0 0 0 0.030315 0.01061 0 1.232392 Los Angela 2027 SBUS Aggregate 20 Natural Ga: 2972.279 2972.279 0 0.951178 0.006651 0.007234 2207.791 5.878324 0.450073 0.08399 5.99926 19.73634 0 1.06 0.06063 0.021221 0.281295 0 Los Angele 2027 SBUS Aggregate 25 Gasoline 6640.38 6640.38 0 0.439257 0.001011 0.001099 881.5874 0.010233 0.025302 0.050477 0.073656 1.199603 0.008715 0.045 0.049809 0.017433 0.102473 0 Los Angela 2027 SBUS Aggregate 25 Diesel 2904.321 2904.321 0 7.399176 0.039102 0.04087 1279.774 0.005598 0.201629 0.120513 0.137195 0.377401 0.012119 0.096897 0.049809 0.017433 0.126018 0 Los Angele 2027 SBUS Aggregate 25 Electricity 233.8999 0 233.8999 0 0 0 0 0 0 0 0 0 0 0 0.024905 0.008717 0 1.130271 Los Angela 2027 SBUS Aggregate 25 Natural Ga: 4160.581 4160.581 0 0.648255 0.005237 0.005696 1670.812 4.346704 0.340606 0.062106 4.43613 14.3175 0 1.06 0.049809 0.017433 0.212879 0 Los Angele: 2027 SBUS Aggregate 30 Gasoline 7710.632 7710.632 0 0.407512 0.000788 0.000857 782.292 0.007969 0.023474 0.039309 0.05736 1.103554 0.007734 0.045 0.044399 0.01554 0.090932 0 Los Angela 2027 SBUS Aggregate 30 Diesel 3372.421 3372.421 0 7.053801 0.033459 0.034972 1194.99 0.004466 0.188271 0.09616 0.109471 0.319673 0.011316 0.096897 0.044399 0.01554 0.117669 0 Los Angele 2027 SBUS Aggregate 30 Electricity 271.5983 0 271.5983 0 0 0 0 0 0 0 0 0 0 0 0.022199 0.00777 0 0.906366 Los Angela 2027 SBUS Aggregate 30 Natural Ga: 4831.155 4831.155 0 0.477212 0.004071 0.004428 1337.479 3.415734 0.272654 0.048804 3.486007 11.08049 0 1.06 0.044399 0.01554 0.170409 0 Los Angele 2027 SBUS Aggregate 35 Gasoline 8216.873 8216.873 0 0.384794 0.000648 0.000704 725.1451 0.006542 0.022165 0.03227 0.047089 1.017188 0.007169 0.045 0.041585 0.014555 0.084289 0 Los Angela 2027 SBUS Aggregate 35 Diesel 3593.837 3593.837 0 6.790987 0.029891 0.031243 1128.116 0.003599 0.177735 0.077476 0.088201 0.273543 0.010683 0.096897 0.041585 0.014555 0.111084 0 Los Angele 2027 SBUS Aggregate 35 Electricity 289.4301 0 289.4301 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 0.921971 Los Angela 2027 SBUS Aggregate 35 Natural Ga: 5148.345 5148.345 0 0.369918 0.003152 0.003428 1111.31 2.794753 0.226548 0.039932 2.85225 8.951533 0 1.06 0.041585 0.014555 0.141592 0 Los Angele 2027 SBUS Aggregate 40 Gasoline 6207.515 6207.515 0 0.367826 0.000562 0.000611 701.885 0.005676 0.021188 0.027999 0.040857 0.94181 0.006939 0.045 0.041585 0.014555 0.081585 0 Los Angela 2027 SBUS Aggregate 40 Diesel 2714.998 2714.998 0 6.60351 0.028395 0.029679 1078.695 0.002981 0.169949 0.064172 0.073055 0.238311 0.010215 0.096897 0.041585 0.014555 0.106218 0 Los Angele 2027 SBUS Aggregate 40 Electricity 218.6527 0 218.6527 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 0.976524 Los Angela 2027 SBUS Aggregate 40 Natural Ga: 3889.366 3889.366 0 0.297267 0.002481 0.002698 948.2428 2.35341 0.193306 0.033626 2.401827 7.456278 0 1.06 0.041585 0.014555 0.120816 0 Los Angele 2027 SBUS Aggregate 45 Gasoline 3823.062 3823.062 0 0.355615 0.000514 0.000559 704.2485 0.005208 0.020484 0.025689 0.037485 0.876338 0.006962 0.045 0.041585 0.014555 0.08186 0 Los Angela 2027 SBUS Aggregate 45 Diesel 1672.103 1672.103 0 6.489951 0.028972 0.030282 1046.457 0.002602 0.16487 0.056022 0.063777 0.213474 0.009909 0.096897 0.041585 0.014555 0.103044 0 Los Angele 2027 SBUS Aggregate 45 Electricity 134.663 0 134.663 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.036858 Los Angela 2027 SBUS Aggregate 45 Natural Ga: 2395.368 2395.368 0 0.245347 0.002056 0.002236 825.358 2.024923 0.168255 0.028932 2.066583 6.354721 0 1.06 0.041585 0.014555 0.105159 0 Los Angele: 2027 SBUS Aggregate 50 Gasoline 2621.688 2621.688 0 0.348139 0.000496 0.00054 724.7987 0.005049 0.020054 0.024905 0.036341 0.818926 0.007165 0.045 0.041585 0.014555 0.084249 0 Los Angela 2027 SBUS Aggregate 50 Diesel 1146.655 1146.655 0 6.450882 0.03163 0.033061 1031.235 0.002454 0.162472 0.052844 0.060159 0.198683 0.009765 0.096897 0.041585 0.014555 0.101545 0 Los Angele 2027 SBUS Aggregate 50 Electricity 92.34601 0 92.34601 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.037928 Los Angela 2027 SBUS Aggregate 50 Natural Ga: 1642.639 1642.639 0 0.20674 0.001879 0.002044 729.5873 1.771698 0.148731 0.025314 1.808148 5.513175 0 1.06 0.041585 0.014555 0.092957 0 Los Angele: 2027 SBUS Aggregate 55 Gasoline 3615.801 3615.801 0 0.354254 0.000505 0.00055 754.4336 0.005107 0.020406 0.025191 0.036759 0.759174 0.007458 0.045 0.041585 0.014555 0.087693 0 Los Angela 2027 SBUS Aggregate 55 Diesel 1581.453 1581.453 0 6.51204 0.036383 0.038028 1032.925 0.002531 0.162738 0.054484 0.062026 0.193704 0.009781 0.096897 0.041585 0.014555 0.101711 0 Los Angele 2027 SBUS Aggregate 55 Electricity 127.3625 0 127.3625 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.067148 Los Angela 2027 SBUS Aggregate 55 Natural Ga: 2265.508 2265.508 0 0.177817 0.00195 0.002121 652.9474 1.571025 0.133108 0.022447 1.603346 4.851626 0 1.06 0.041585 0.014555 0.083192 0 Los Angele 2027 SBUS Aggregate 60 Gasoline 2640.032 2640.032 0 0.358023 0.000543 0.00059 784.9237 0.005511 0.020623 0.027183 0.039665 0.713336 0.00776 0.045 0.041585 0.014555 0.091237 0 Los Angela 2027 SBUS Aggregate 60 Diesel 1154.678 1154.678 0 6.565217 0.039791 0.04159 1050.572 0.002665 0.165518 0.057374 0.065316 0.19482 0.009948 0.096897 0.041585 0.014555 0.103449 0 Los Angele 2027 SBUS Aggregate 60 Electricity 92.99216 0 92.99216 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.065251 Los Angela 2027 SBUS Aggregate 60 Natural Ga: 1654.132 1654.132 0 0.177576 0.00195 0.002121 652.9474 1.571025 0.133108 0.022447 1.603346 4.851626 0 1.06 0.041585 0.014555 0.083192 0 Los Angele: 2027 SBUS Aggregate 65 Gasoline 1551.436 1551.436 0 0.363804 0.000615 0.000669 808.8283 0.006305 0.020956 0.031102 0.045384 0.675392 0.007996 0.045 0.041585 0.014555 0.094016 0 Los Angela 2027 SBUS Aggregate 65 Diesel 678.5557 678.5557 0 6.580378 0.040402 0.042229 1078.185 0.002692 0.169869 0.057951 0.065972 0.195599 0.01021 0.096897 0.041585 0.014555 0.106168 0 Los Angele 2027 SBUS Aggregate 65 Electricity 54.64758 0 54.64758 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.123067 Los Angela 2027 SBUS Aggregate 65 Natural Ga: 972.0638 972.0638 0 0.177066 0.00195 0.002121 652.9474 1.571025 0.133108 0.022447 1.603346 4.851626 0 1.06 0.041585 0.014555 0.083192 0 Los Angele: 2027 SBUS Aggregate 70 Gasoline 1551.436 1551.436 0 0.372549 0.000668 0.000727 816.2394 0.006849 0.02146 0.033782 0.049295 0.654838 0.008069 0.045 0.041585 0.014555 0.094877 0 Los Angela 2027 SBUS Aggregate 70 Diesel 678.5557 678.5557 0 6.580378 0.040402 0.042229 1078.185 0.002692 0.169869 0.057954 0.065976 0.195622 0.01021 0.096897 0.041585 0.014555 0.106168 0 Los Angele 2027 SBUS Aggregate 70 Electricity 54.64758 0 54.64758 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.073955 Los Angela 2027 SBUS Aggregate 70 Natural Ga: 972.0638 972.0638 0 0.177066 0.00195 0.002121 652.9474 1.571025 0.133108 0.022447 1.603346 4.851626 0 1.06 0.041585 0.014555 0.083192 0 Los Angele: 2027 SBUS Aggregate 75 Gasoline 1551.436 1551.436 0 0.372549 0.000668 0.000727 816.2394 0.006849 0.02146 0.033782 0.049295 0.654838 0.008069 0.045 0.041585 0.014555 0.094877 0 Los Angela 2027 SBUS Aggregate 75 Diesel 678.5557 678.5557 0 6.580378 0.040402 0.042229 1078.185 0.002692 0.169869 0.057957 0.06598 0.195654 0.01021 0.096897 0.041585 0.014555 0.106168 0 Los Angele 2027 SBUS Aggregate 75 Electricity 54.64758 0 54.64758 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.073955 Los Angela 2027 SBUS Aggregate 75 Natural Ga: 972.0638 972.0638 0 0.177066 0.00195 0.002121 652.9474 1.571025 0.133108 0.022447 1.603346 4.851626 0 1.06 0.041585 0.014555 0.083192 0 Los Angele: 2027 SBUS Aggregate 80 Gasoline 1551.436 1551.436 0 0.372549 0.000668 0.000727 816.2394 0.006849 0.02146 0.033782 0.049295 0.654838 0.008069 0.045 0.041585 0.014555 0.094877 0 Los Angela 2027 SBUS Aggregate 80 Diesel 678.5557 678.5557 0 6.580378 0.040402 0.042229 1078.185 0.002692 0.169869 0.057961 0.065984 0.195695 0.01021 0.096897 0.041585 0.014555 0.106168 0 Los Angele 2027 SBUS Aggregate 80 Electricity 54.64758 0 54.64758 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.073955 Los Angela 2027 SBUS Aggregate 80 Natural Ga: 972.0638 972.0638 0 0.177066 0.00195 0.002121 652.9474 1.571025 0.133108 0.022447 1.603346 4.851626 0 1.06 0.041585 0.014555 0.083192 0 Los Angele: 2027 SBUS Aggregate 85 Gasoline 1551.436 1551.436 0 0.372549 0.000668 0.000727 816.2394 0.006849 0.02146 0.033782 0.049295 0.654838 0.008069 0.045 0.041585 0.014555 0.094877 0 Los Angela 2027 SBUS Aggregate 85 Diesel 678.5557 678.5557 0 6.580378 0.040402 0.042229 1078.185 0.002692 0.169869 0.057966 0.06599 0.195744 0.01021 0.096897 0.041585 0.014555 0.106168 0 Los Angele 2027 SBUS Aggregate 85 Electricity 54.64758 0 54.64758 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.073955 Los Angela 2027 SBUS Aggregate 85 Natural Ga: 972.0638 972.0638 0 0.177066 0.00195 0.002121 652.9474 1.571025 0.133108 0.022447 1.603346 4.851626 0 1.06 0.041585 0.014555 0.083192 0 Los Angele: 2027 SBUS Aggregate 90 Gasoline 1551.436 1551.436 0 0.372549 0.000668 0.000727 816.2394 0.006849 0.02146 0.033782 0.049295 0.654838 0.008069 0.045 0.041585 0.014555 0.094877 0 Los Angela 2027 SBUS Aggregate 90 Diesel 678.5557 678.5557 0 6.580378 0.040402 0.042229 1078.185 0.002693 0.169869 0.057972 0.065996 0.195802 0.01021 0.096897 0.041585 0.014555 0.106168 0 Los Angele 2027 SBUS Aggregate 90 Electricity 54.64758 0 54.64758 0 0 0 0 0 0 0 0 0 0 0 0.020793 0.007277 0 1.073955 Los Angela 2027 SBUS Aggregate 90 Natural Ga: 972.0638 972.0638 0 0.177066 0.00195 0.002121 652.9474 1.571025 0.133108 0.022447 1.603346 4.851626 0 1.06 0.041585 0.014555 0.083192 0 Los Angele: 2027 UBUS Aggregate 5 Gasoline 295.8103 295.8103 0 0.373113 0.007127 0.007751 4191.595 0.022514 0.034881 0.073945 0.107901 0.476714 0.041438 0.045 0.109872 0.038455 0.48722 0 Los Angele: 2027 UBUS Aggregate 5 Diesel 12.28784 12.28784 0 2.445823 0.006761 0.007067 3076.002 0.010851 0.484625 0.233611 0.265948 0.399611 0.029147 0.22 0.11 0.0385 0.302891 0 Los Angele: 2027 UBUS Aggregate 5 Electricity 379.4042 0 379.4042 0 0 0 0 0 0 0 0 0 0 0 0.054999 0.01925 0 5.908862 Los Angela 2027 UBUS Aggregate 5 Natural Ga: 5176.441 5176.441 0 2.860558 0.000643 0.000672 11523.6 6.135789 2.349162 0.087689 6.262045 86.97544 0 0.97 0.109998 0.038499 1.468226 0 Los Angele: 2027 UBUS Aggregate 10 Gasoline 963.0255 963.0255 0 0.3176 0.004427 0.004815 3357.263 0.013917 0.029695 0.045703 0.06669 0.446968 0.03319 0.045 0.109459 0.038311 0.390239 0 Los Angele: 2027 UBUS Aggregate 10 Diesel 39.12827 39.12827 0 1.71027 0.006181 0.00646 2570.071 0.008316 0.404916 0.179044 0.203828 0.279017 0.024353 0.22 0.11 0.0385 0.253072 0 Los Angele: 2027 UBUS Aggregate 10 Electricity 1208.191 0 1208.191 0 0 0 0 0 0 0 0 0 0 0 0.054997 0.019249 0 2.798892 Los Angela 2027 UBUS Aggregate 10 Natural Ga: 16490.47 16490.47 0 1.620205 0.000595 0.000622 6932.158 4.759976 1.413166 0.068091 4.857992 66.98581 0 0.97 0.109989 0.038496 0.883229 0 Los Angele: 2027 UBUS Aggregate 15 Gasoline 1769.203 1769.203 0 0.273961 0.002911 0.003166 2706.818 0.009068 0.025619 0.029774 0.043447 0.41459 0.02676 0.045 0.109001 0.03815 0.314633 0 Los Angele: 2027 UBUS Aggregate 15 Diesel 70.0989 70.0989 0 1.089769 0.005336 0.005578 2049.39 0.005948 0.322882 0.128058 0.145784 0.177455 0.019419 0.22 0.11 0.0385 0.201801 0 Los Angele: 2027 UBUS Aggregate 15 Electricity 2164.597 0 2164.597 0 0 0 0 0 0 0 0 0 0 0 0.054994 0.019248 0 2.333098 Los Angela 2027 UBUS Aggregate 15 Natural Ga: 29557.71 29557.71 0 0.797078 0.000497 0.00052 3656.648 3.633649 0.745432 0.052055 3.708555 50.22511 0 0.97 0.10998 0.038493 0.465895 0 Los Angele: 2027 UBUS Aggregate 20 Gasoline 15220.26 15220.26 0 0.254127 0.002079 0.002261 2298.375 0.00653 0.023759 0.021445 0.031293 0.363425 0.022722 0.045 0.109654 0.038379 0.267157 0 Los Angele: 2027 UBUS Aggregate 20 Diesel 624.9523 624.9523 0 0.809864 0.004914 0.005136 1765.489 0.00477 0.278153 0.102691 0.116906 0.131712 0.016729 0.22 0.11 0.0385 0.173846 0 Los Angele: 2027 UBUS Aggregate 20 Electricity 19296.7 0 19296.7 0 0 0 0 0 0 0 0 0 0 0 0.054998 0.019249 0 2.071519 Los Angela 2027 UBUS Aggregate 20 Natural Ga: 263329.8 263329.8 0 0.501417 0.000385 0.000402 2401.954 3.135254 0.489654 0.044838 3.199801 42.67734 0 0.97 0.109993 0.038498 0.306034 0 Los Angele: 2027 UBUS Aggregate 25 Gasoline 1122.96 1122.96 0 0.133234 0.001325 0.001441 1441.568 0.003125 0.012523 0.010222 0.014916 0.396776 0.014251 0.045 0.101082 0.035379 0.167564 0 Los Angele: 2027 UBUS Aggregate 25 Diesel 24.9241 24.9241 0 0.616791 0.004915 0.005138 1587.149 0.004045 0.250056 0.087084 0.099138 0.105447 0.015039 0.22 0.109997 0.038499 0.156285 0 Los Angele: 2027 UBUS Aggregate 25 Electricity 770.8191 0 770.8191 0 0 0 0 0 0 0 0 0 0 0 0.054901 0.019215 0 1.899864 Los Angela 2027 UBUS Aggregate 25 Natural Ga: 10675.58 10675.58 0 0.355554 0.000596 0.000623 1738.889 2.799234 0.354484 0.041723 2.85871 37.64291 0 0.97 0.109681 0.038388 0.221552 0 Los Angele: 2027 UBUS Aggregate 30 Gasoline 1520.125 1520.125 0 0.108075 0.001057 0.00115 1184.477 0.002142 0.01018 0.007002 0.010217 0.331699 0.01171 0.045 0.099556 0.034845 0.13768 0 Los Angele: 2027 UBUS Aggregate 30 Diesel 28.63582 28.63582 0 0.452742 0.005337 0.005578 1447.078 0.003546 0.227988 0.076342 0.08691 0.088277 0.013712 0.22 0.109996 0.038498 0.142492 0 Los Angele: 2027 UBUS Aggregate 30 Electricity 886.1611 0 886.1611 0 0 0 0 0 0 0 0 0 0 0 0.054863 0.019202 0 1.523504 Los Angela 2027 UBUS Aggregate 30 Natural Ga: 12342.75 12342.75 0 0.270804 0.000584 0.000611 1350.451 2.594588 0.275298 0.039171 2.65026 34.54983 0 0.97 0.109563 0.038347 0.172061 0 Los Angele: 2027 UBUS Aggregate 35 Gasoline 1351.622 1351.622 0 0.087254 0.000895 0.000973 993.8287 0.001476 0.008245 0.004821 0.007035 0.278942 0.009825 0.045 0.09803 0.03431 0.11552 0 Los Angele: 2027 UBUS Aggregate 35 Diesel 20.92122 20.92122 0 0.322901 0.006179 0.006459 1337.106 0.003178 0.210662 0.068418 0.077889 0.076135 0.01267 0.22 0.109994 0.038498 0.131664 0 Los Angele: 2027 UBUS Aggregate 35 Electricity 648.0033 0 648.0033 0 0 0 0 0 0 0 0 0 0 0 0.054809 0.019183 0 1.549735 Los Angela 2027 UBUS Aggregate 35 Natural Ga: 9098.648 9098.648 0 0.216154 0.000601 0.000628 1093.059 2.438187 0.222827 0.037389 2.491135 32.20772 0 0.97 0.109396 0.038289 0.139267 0 Los Angele: 2027 UBUS Aggregate 40 Gasoline 1177.684 1177.684 0 0.088517 0.000812 0.000883 956.5806 0.001263 0.008361 0.004133 0.00603 0.249208 0.009457 0.045 0.098523 0.034483 0.11119 0 Los Angele: 2027 UBUS Aggregate 40 Diesel 19.50788 19.50788 0 0.227269 0.007443 0.007779 1257.351 0.002893 0.198096 0.062285 0.070907 0.067061 0.011914 0.22 0.109994 0.038498 0.12381 0 Los Angele: 2027 UBUS Aggregate 40 Electricity 604.0292 0 604.0292 0 0 0 0 0 0 0 0 0 0 0 0.054829 0.01919 0 1.641432 Los Angela 2027 UBUS Aggregate 40 Natural Ga: 8456.188 8456.188 0 0.177959 0.000471 0.000492 916.6768 2.344819 0.186871 0.0355 2.39524 30.76758 0 0.97 0.109457 0.03831 0.116794 0 Los Angele: 2027 UBUS Aggregate 45 Gasoline 1201.651 1201.651 0 0.08552 0.000772 0.00084 921.7541 0.001083 0.008085 0.003547 0.005175 0.244861 0.009112 0.045 0.098394 0.034438 0.107142 0 Los Angele: 2027 UBUS Aggregate 45 Diesel 19.56349 19.56349 0 0.165832 0.009128 0.009541 1207.678 0.002665 0.19027 0.057374 0.065315 0.060017 0.011443 0.22 0.109994 0.038498 0.118919 0 Los Angele: 2027 UBUS Aggregate 45 Electricity 605.8004 0 605.8004 0 0 0 0 0 0 0 0 0 0 0 0.054824 0.019188 0 1.742847 Los Angela 2027 UBUS Aggregate 45 Natural Ga: 8487.227 8487.227 0 0.150447 0.000416 0.000435 785.0141 2.262669 0.16003 0.034097 2.31115 29.52291 0 0.97 0.109442 0.038305 0.100019 0 Los Angele: 2027 UBUS Aggregate 50 Gasoline 1040.107 1040.107 0 0.089777 0.000775 0.000843 954.1761 0.00108 0.008485 0.003542 0.005169 0.264695 0.009433 0.045 0.098898 0.034614 0.110911 0 Los Angele: 2027 UBUS Aggregate 50 Diesel 18.08675 18.08675 0 0.138591 0.011235 0.011743 1188.15 0.002477 0.187193 0.053334 0.060717 0.05438 0.011258 0.22 0.109995 0.038498 0.116996 0 Los Angele: 2027 UBUS Aggregate 50 Electricity 559.9022 0 559.9022 0 0 0 0 0 0 0 0 0 0 0 0.054842 0.019195 0 1.744645 Los Angela 2027 UBUS Aggregate 50 Natural Ga: 7822.743 7822.743 0 0.150113 0.00036 0.000376 785.2679 2.269613 0.160082 0.033777 2.317779 29.61297 0 0.97 0.109499 0.038324 0.100051 0 Los Angele: 2027 UBUS Aggregate 55 Gasoline 1093.892 1093.892 0 0.091835 0.000817 0.000889 982.5031 0.001119 0.008684 0.003666 0.00535 0.308406 0.009713 0.045 0.09895 0.034633 0.114204 0 Los Angele: 2027 UBUS Aggregate 55 Diesel 19.14734 19.14734 0 0.145549 0.013764 0.014387 1198.716 0.00232 0.188858 0.049943 0.056857 0.049763 0.011358 0.22 0.109995 0.038498 0.118036 0 Los Angele: 2027 UBUS Aggregate 55 Electricity 592.7169 0 592.7169 0 0 0 0 0 0 0 0 0 0 0 0.054844 0.019195 0 1.793761 Los Angela 2027 UBUS Aggregate 55 Natural Ga: 8279.035 8279.035 0 0.150306 0.000342 0.000357 785.3241 2.270274 0.160093 0.033553 2.318198 29.62136 0 0.97 0.109504 0.038326 0.100058 0 Los Angele: 2027 UBUS Aggregate 60 Gasoline 1404.977 1404.977 0 0.093689 0.000903 0.000982 1008.996 0.001227 0.008869 0.004018 0.005863 0.380043 0.009975 0.045 0.098769 0.034569 0.117283 0 Los Angele: 2027 UBUS Aggregate 60 Diesel 24.03359 24.03359 0 0.186706 0.016715 0.017471 1239.388 0.002185 0.195266 0.047048 0.053561 0.045909 0.011744 0.22 0.109995 0.038498 0.122041 0

Los Angeles 2027 UBUS Aggregate 60 Electricity 744.0504 0 744.0504 0 0 0 0 0 0 0 0 0 0 0 0.054838 0.019193 0 1.790573 Los Angeles 2027 UBUS Aggregate 60 Natural Ga: 10402.53 10402.53 0 0.150978 0.000345 0.00036 785.5379 2.267897 0.160137 0.033352 2.315591 29.59034 0 0.97 0.109485 0.03832 0.100086 0 Los Angeles 2027 UBUS Aggregate 65 Gasoline 1194.487 1194.487 0 0.06941 0.001059 0.001152 834.6014 0.001042 0.006646 0.003395 0.004955 0.558068 0.008251 0.045 0.095564 0.033447 0.097012 0 Los Angeles 2027 UBUS Aggregate 65 Diesel 12.00562 12.00562 0 0.26206 0.020084 0.020992 1309.915 0.002069 0.206378 0.044537 0.050702 0.04264 0.012412 0.22 0.109988 0.038496 0.128986 0 Los Angeles 2027 UBUS Aggregate 65 Electricity 372.8594 0 372.8594 0 0 0 0 0 0 0 0 0 0 0 0.054646 0.019126 0 1.887754 Los Angeles 2027 UBUS Aggregate 65 Natural Ga: 5362.156 5362.156 0 0.155219 0.000611 0.000638 779.4662 2.19711 0.158899 0.032995 2.244061 28.66755 0 0.97 0.108908 0.038118 0.099312 0 Los Angeles 2027 UBUS Aggregate 70 Gasoline 1126.711 1126.711 0 0.030297 0.00128 0.001392 583.5238 0.000686 0.003069 0.0022 0.00321 0.876155 0.005769 0.045 0.091007 0.031852 0.067827 0 Los Angeles 2027 UBUS Aggregate 70 Diesel 0.025394 0.025394 0 0.283824 0.016526 0.017273 1040.265 0.001695 0.163894 0.036489 0.04154 0.045748 0.009857 0.22 0.10323 0.036131 0.102434 0 Los Angeles 2027 UBUS Aggregate 70 Electricity 3.481518 0 3.481518 0 0 0 0 0 0 0 0 0 0 0 0.007973 0.002791 0 1.805204 Los Angeles 2027 UBUS Aggregate 70 Natural Ga: 389.5214 389.5214 0 0.306889 0.009119 0.009532 620.2214 0.042182 0.126436 0.021654 0.066032 0.584228 0 0.97 0.091336 0.031968 0.079023 0 Los Angeles 2027 UBUS Aggregate 75 Gasoline 0 0 0
Los Angeles 2027 UBUS Aggregate 75 Diesel 0 0 0
Los Angeles 2027 UBUS Aggregate 75 Natural Ga: 0 0 0
Los Angeles 2027 UBUS Aggregate 80 Gasoline 0 0 0
Los Angeles 2027 UBUS Aggregate 80 Diesel 0 0 0
Los Angeles 2027 UBUS Aggregate 80 Natural Ga: 0 0 0
Los Angeles 2027 UBUS Aggregate 85 Gasoline 0 0 0
Los Angeles 2027 UBUS Aggregate 85 Diesel 0 0 0
Los Angeles 2027 UBUS Aggregate 85 Natural Ga: 0 0 0
Los Angeles 2027 UBUS Aggregate 90 Gasoline 0 0 0
Los Angeles 2027 UBUS Aggregate 90 Diesel 0 0 0
Los Angeles 2027 UBUS Aggregate 90 Natural Ga: 0 0 0

sumption

Emergency Backup Generator Emissions
Backup Generator
Backup Generator>750 hp

UNMITIGATED
Hours/Year Hours per HP -hr per Total hp -hr
Fuel Type Quantity HP LF per Unit Day day per year
Diesel 2 400 0.74 50 1 592 29,600
Diesel 0 3,600 0.74 50 1 0 0
ROG TOG CO NOx SO2 PM10 PM2.5 CO2
CH4
N2O CO2e
Emissions Rates (g/hp-hr) 1.020 1.120
Emissions Rates (>750) (g/hp-hr) 1.020 1.120
Emissions (pounds/day) 1.33 1.46
Emissions (tons/year) 0.03 0.04
GHG Emissions (metric tons) - -
Source: User Guide for CaIEEMod Version 2022.1, Appendix G, Table G-40.

2.600

2.600

3.39 0.08

2.850

4.560

3.72 0.09

0.005

0.005

0.01 0.00

0.150

0.150

0.20 0.00

0.150

0.150

0.20 0.00
521.640
521.640
680.81

17.02 15.44

0.021

0.021

0.03 0.00

0.00 0.004

0.004

0.01 0.00

0.00 15.49

Bellflower Convenience Center Update Detailed Report, 11/12/2025 Bellflower Convenience Center Update Detailed Report
Table of Contents

1. Basic Project Information

1.1. Basic Project Information

1.2. Land Use Types

1.3. User -Selected Emission Reduction Measures by Emissions Sector

2. Emissions Summary

2.1. Construction Emissions Compared Against Thresholds

2.2. Construction Emissions by Year, Unmitigated

2.4. Operations Emissions Compared Against Thresholds

2.5. Operations Emissions by Sector, Unmitigated

3. Construction Emissions Details

3.1. Grading (2026) - Unmitigated

3.3. Building Construction (2027) - Unmitigated

3.5. Paving (2027) - Unmitigated

3.7. Architectural Coating (2027) - Unmitigated

3.9. Infrastrucure Improvement (2026) - Unmitigated
1 / 52

Bellflower Convenience Center Update Detailed Report, 11/12/2025

4. Operations Emissions Details

4.1. Mobile Emissions by Land Use

4.1.1. Unmitigated

4.2. Energy

4.2.1. Electricity Emissions By Land Use - Unmitigated

4.2.3. Natural Gas Emissions By Land Use - Unmitigated

4.3. Area Emissions by Source

4.3.1. Unmitigated

4.4. Water Emissions by Land Use

4.4.1. Unmitigated

4.5. Waste Emissions by Land Use

4.5.1. Unmitigated

4.6. Refrigerant Emissions by Land Use

4.6.1. Unmitigated

4.7. Offroad Emissions By Equipment Type

4.7.1. Unmitigated

4.8. Stationary Emissions By Equipment Type