HomeMy WebLinkAboutAppendix B - Air Quality and Greenhouse Gas Emissions Study❖ APPENDICES ❖
7106/Summit Avenue Warehouse Project
Initial Study/Mitigated Negative Declaration May 2022
APPENDIX B
Air Quality and Greenhouse Gas Emissions
Study
AIR QUALITY AND GREENHOUSE GAS EMISSIONS REPORT
FOR THE
SUMMIT AVENUE WAREHOUSE PROJECT
FONTANA, CALIFORNIA
Prepared for:
City of Fontana
8353 Sierra Avenue
Fontana, CA 92335
Prepared by:
UltraSystems Environmental Inc.
16431 Scientific Way
Irvine, CA 92618
(949) 788-4900
April 2022
TABLE OF CONTENTS
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TABLE OF CONTENTS
INTRODUCTION .................................................................................................................................... 1‐1
PROJECT DESCRIPTION ..................................................................................................................... 2‐2
Project Overview .................................................................................................................................. 2-2
Construction ........................................................................................................................................... 2-2
Site Access, Circulation, and Parking ........................................................................... 2-2
Landscaping ............................................................................................................................ 2-2
Building Characteristics .................................................................................................... 2-5
Perimeter Fencing and Exterior Walls ........................................................................ 2-5
Infrastructure Improvements ......................................................................................... 2-5
Operations............................................................................................................................................... 2-6
EXISTING CONDITIONS ...................................................................................................................... 3‐1
Regional Climate ................................................................................................................................... 3-1
Regulatory Setting ............................................................................................................................... 3-2
Pollutants of Concern ......................................................................................................... 3-2
Applicable Air Quality Regulations ............................................................................... 3-6
Air Quality Management Plan (AQMP) ...................................................................... 3-11
SCAQMD Rule 403 .............................................................................................................. 3 - 1 1
SCAQMD Rule 2305 ........................................................................................................... 3-12
City of Fontana General Plan ......................................................................................... 3-12
Greenhouse Gas Emissions ............................................................................................ 3-14
Regional Air Quality .......................................................................................................................... 3-20
Local Air Quality ................................................................................................................................. 3-22
Sensitive Receptors ........................................................................................................................... 3-22
AIR QUALITY IMPACTS ANALYSIS ................................................................................................. 4‐1
Impact Review Criteria ...................................................................................................................... 4-1
Criteria Pollutants ................................................................................................................ 4-1
Greenhouse Gas Emissions .............................................................................................. 4-4
Methodology For Analyzing Criteria Pollutant Emissions .................................................. 4-5
Construction ........................................................................................................................... 4-5
Operations ............................................................................................................................... 4-6
Air Quality Impacts (Criteria Pollutants and Air Toxics)..................................................... 4-6
Construction Impacts ......................................................................................................... 4-6
Long-Term Impacts ............................................................................................................. 4-2
Consistency With Air Quality Management Plan .................................................... 4-3
Methodology for Analyzing Greenhouse Gas Emissions ...................................................... 4-4
Air Quality Impacts (Greenhouse Gas Emissions) .................................................................. 4-5
EMISSION REDUCTION MEASURES ................................................................................................ 5‐1
IMPACTS AFTER MITIGATION ........................................................................................................ 6‐1
LIST OF TABLES
Table 3.2‐1 - Ambient Air Quality Standards for Criteria Air Pollutants .................................................... 3-8
TABLE OF CONTENTS
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Table 3.3‐1 - Federal and State Attainment Status ............................................................................................ 3-21
Table 3.4‐1 - Ambient Air Quality Monitoring Data .......................................................................................... 3-22
Table 4.1‐1 - SCAQMD Emissions Thresholds for Significant Regional Impacts ..................................... 4-2
Table 4.2‐1 - Construction Equipment Assumptions .......................................................................................... 4-6
Table 4.3‐1 - Maximum Daily Unmitigated Regional Construction Emissions......................................... 4-1
Table 4.3‐2 - Results of Localized Significance Analysis.................................................................................... 4-2
Table 4.3‐3 - Maximum Daily Project Operational Emissions ......................................................................... 4-3
Table 4.5‐1 - Unmitigated Annual GHG Emissions, 2019 And Beyond ........................................................ 4-5
LIST OF FIGURES
Figure 2.1‐1 - Regional Location .................................................................................................................................. 2-3
Figure 2.1‐2 - Project Vicinity ....................................................................................................................................... 2-4
ATTACHMENTS
Attachment 1 CALEEMOD Output
INTRODUCTION
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INTRODUCTION
This air quality and greenhouse gas (GHG) emissions technical study was prepared by UltraSystems
Environmental Inc. (UltraSystems) to support an Initial Study (IS) and Mitigated Negative
Declaration (MND) for the Summit Avenue Warehouse in the city of Fontana, California. The project
applicant (SKG Enterprises, Inc. of Upland, CA) proposes to construct and operate an approximately
102,380-square-foot warehouse building and related uses on approximately 4.49 gross acres of land
at the northeast corner of Summit Avenue and Sierra Avenue in Fontana, California. The project
would consist of 92,380 square feet of warehousing space, 5,000 square feet of office space on first
floor, 5,000 square feet of office space on a mezzanine floor, 11 dock-high doors, 3 trailer stalls, and
53 automobile parking stalls. Construction is projected to start in July 2022, and operations are
anticipated to begin in February 2023.
The purpose of this report is to provide a detailed technical air quality and GHG analysis of the
proposed Summit Avenue warehouse project. The analysis was prepared in accordance with the
CEQA Air Quality Handbook prepared by the South Coast Air Quality Management District.1,2 Regional
climate and meteorology, air quality monitoring data, and the area’s attainment status with respect
to criteria air pollutants are discussed. The report includes a description of federal, state, and local
agencies that govern air quality and climate change, and their pertinent statutes and regulations. It
identifies potential impacts of air pollutants of concern for this project, including criteria pollutants
(i.e., pollutants for which National Ambient Air Quality Standards [NAAQS] have been established by
the U.S. Environmental Protection Agency, and their precursors) and air toxics. The report describes
the analytical methodologies and assumptions used for this study as well as the results of these
analyses.
1 CEQA Air Quality Handbook: South Coast Air Quality Management District, Diamond Bar, CA. 1993.
2 Updates to the CEQA Air Quality Handbook are at http://sfprod.aqmd.gov/home/regulations/ceqa/air-quality-
analysis-handbook.
PROJECT DESCRIPTION
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PROJECT DESCRIPTION
Project Overview
The project applicant proposes to construct and operate an approximately 102,380-square-foot
warehouse building and related uses on approximately 4.49 gross acres of land at the northeast
corner of Summit Avenue and Sierra Avenue in Fontana, California (APN 0239-161-28). The project
would consist of 92,380 square feet of warehousing space, 5,000 square feet of office space on first
floor, 5,000 square feet of office space on a mezzanine floor, 11 dock-high doors, 3 trailer stalls, and
53 automobile parking stalls.
The project site is currently vacant. On the southwest corner of the Summit Avenue/Sierra Avenue
intersection is residential development. West of the project site, across Sierra Avenue and
immediately abutting the project site to the north, south, and east are existing light industrial uses.
Figure 2.1‐1 shows the regional location of the project, and Figure 2.1‐2 shows the site area.
Construction
It is estimated that construction for the proposed project would begin in July 2022 and end in late
February 2023. Construction of the proposed project involves the following primary activities: 1) site
preparation and grading activities; 2) the installation of subsurface infrastructure; 3) building
foundation pouring, concrete panel creation, building construction, and painting; 5) utility
connection; 6) fine grading and the installation of surface elements including, but not limited to,
pavement and landscaping; 7) the construction of offsite improvements; and 8) installation of
interior furnishings, detail work, and completion of common areas. The foregoing activities are not
consecutive and often overlap. It is anticipated that the timeframe from site preparation to
occupancy-ready would be approximately seven months.
SITE ACCESS, CIRCULATION, AND PARKING
Primary site ingress and egress would be provided by a 30-foot-wide driveway along the
northwestern edge of the project site along Sierra Avenue. The proposed project would include 11
dock doors and three trailer stalls in compliance with the City’s requirements. There would be 53
automobile parking stalls that would consist of three American Disabilities Act (ADA) stalls and 50
regular parking stalls in the northern portion of the project site. Circulation within the site would be
along the 26-foot-wide fire lane inside the northern and southern perimeters of the project site, and
a 30-foot-wide fire lane inside the eastern perimeter of the project site.
LANDSCAPING
No trees are currently located within the boundary of the project site. New landscaping would include
drought-resistant species, including trees, tall shrubs, low shrubs, and groundcovers. Additionally,
water saving features, including smart irrigation with drip systems, would also be installed on site.
Most of the landscaping would occur along the perimeter of the project site, with a small number of
trees, low shrubs, and other types of groundcover located near the building entrance and around the
building perimeter.
PROJECT DESCRIPTION
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Figure 2.1‐1
REGIONAL LOCATION
PROJECT DESCRIPTION
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Figure 2.1‐2
PROJECT VICINITY
PROJECT DESCRIPTION
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BUILDING CHARACTERISTICS
The proposed warehouse would include a 5,000-square-foot office, a 5,000-square-foot office
mezzanine and 92,380 square feet of warehouse space. The warehouse would have 11 dock doors, 3
trailer stalls, and 53 automobile parking stalls that would be comprised of three ADA parking stalls
and 50 regular parking stalls. The building would be built to a maximum height of 75 feet. The
proposed building would have primarily tilt-up concrete walls with glass panes for the office areas.
Energy-efficient features, including insulated and glazed windows and low E coating on windows,
would be incorporated into building design to comply with the provisions of the California Green
Building Code, Title 24, Part 11 of the California Code of Regulations. Title 24, Part 11 requires new
structures to incorporate a variety of mandatory features to promote green buildings as means to
improve energy efficiency, reduce water demand, promote recycling, and other measures. The
project would be designed and constructed in compliance with applicable City codes, including, but
not limited to, the 2019 California Building Code, California Plumbing Code, California Mechanical
Code, California Electrical Code, California Building Energy Efficiency Standards, and California
Residential Codes.
PERIMETER FENCING AND EXTERIOR WALLS
The proposed project would construct a 14-foot-tall concrete tilt-up screen wall with decorative
pilasters and a 10-foot-tall wrought iron fence along the project perimeter. An eight-foot-tall tube
steel manually operated gate with a Knox padlock would be located at the northwestern driveway
entrance, and a swing gate would be installed in the northeastern portion of the project site to enter
the truck parking area and docks.
INFRASTRUCTURE IMPROVEMENTS
Utilities. To the maximum extent possible, utility connections would be provided from the closest
and/or most efficient locations for the proposed building.
Sanitary Sewer. The project proposes offsite sewer improvements to connect the sewer lines from
the project site to the existing sewer network in Sierra Avenue. All sewer line sizes and connections
are subject to review by the City. The project applicant will work with the City’s Public Works
Department for necessary approvals and ensure compliance with applicable requirements.
Domestic Water. New water meters would be installed as required to meet the demands calculated
by the plumber for the project and in compliance with the requirements of the City’s Public Works
Department. The project would extend the existing water mainline from Summit Avenue to the
southern edge of the site. Water would be provided by the West Valley Water District.
Dry Utilities. Natural gas service would be provided to the project site by the Southern California Gas
Company (SoCalGas), electricity would be provided by Southern California Edison Company (SCE),
and solid waste disposal would be provided by Burrtec 3
Stormwater. The natural terrain of this site drains in a southerly direction at a slope of 0.5%. An
existing master plan storm drain line is in Summit Avenue. The project proposes construction of two
3 City of Fontana, 2021. Utilities. https://www.fontana.org/3032/Utilities. Accessed on November 15, 2021.
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new catch basins and extension of the existing storm drain near the southwestern corner of the
project site. Onsite surface flows will discharge into this network of catch basins and storm drain
systems before entering the main storm drain line in Summit Avenue.
OPERATIONS
At the time this report was prepared, the future tenant(s) of the proposed building were unknown.
For environmental analysis, the future uses onsite are assumed to be any of those uses permitted by
the City of Fontana’s General Plan land use designation of Light Industrial (I-L), and the City’s zoning
designation of Light Industrial (M-1).
Since the future tenant(s) are not yet known, the number of jobs generated by the proposed project
is also unknown. Therefore, for the purpose of this study, employment was estimated by using
average employment density factors reported by the Southern California Association of Governments
(SCAG) in its publication “Employment Density Study Report.”4 This document states that for every
acre of light industrial land use in San Bernardino County, the median number of jobs supported is
6.92. Therefore, the proposed project site’s 4.49 acres are expected to result in approximately 32 jobs
for the operational phase of the project.
4 SCAG (Southern California Association of Governments), 2001. Employee Density Study. Accessed online at
https://docplayer.net/30300085-Employment-density-study-summary-report-october-31-prepared-for-southern-
california-association-of-governments.html , accessed on November 15, 2021.
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EXISTING CONDITIONS
Regional Climate
Air quality is affected by both the rate and location of pollutant emissions, and by meteorological
conditions that influence movement and dispersal of pollutants. Atmospheric conditions such as
wind speed, wind direction, and air temperature gradients, along with local topography, provide the
link between air pollutant emissions and air quality.
The project site is in the South Coast Air Basin (SCAB), which includes all of Orange County and the
non-desert portions of Los Angeles County, most of Riverside County, and the western portion of San
Bernardino County — including some portions of what was previously known as the Southeast
Desert Air Basin. The distinctive climate of the SCAB is determined by its terrain and geographic
location. The SCAB is a coastal plain with connecting broad valleys and low hills, bounded by the
Pacific Ocean to the southwest and high mountains around its remaining perimeter. The general
region lies in the semi-permanent high-pressure zone of the eastern Pacific, resulting in a mild
climate tempered by cool sea breezes with light average wind speeds. The usually mild climatological
pattern is interrupted occasionally by periods of extremely hot weather, winter storms, or Santa Ana
winds.
The vertical dispersion of air pollutants in the SCAB is hampered by the presence of persistent
temperature inversions. An upper layer of dry air that warms as it descends characterizes
high-pressure systems, such as the semi-permanent high-pressure zone in which the SCAB is located.
This upper layer restricts the mobility of cooler marine-influenced air near the ground surface and
results in the formation of subsidence inversions. Such inversions restrict the vertical dispersion of
air pollutants released into the marine layer and, together with strong sunlight, can produce
worst-case conditions for the formation of photochemical smog.
The atmospheric pollution potential of an area is largely dependent on winds, atmospheric stability,
solar radiation, and terrain. The combination of low wind speeds and low inversions produces the
greatest concentration of air pollutants. On days without inversions, or on days of winds averaging
over 15 mph, smog potential is greatly reduced.5
The annual average high and low temperatures, as recorded at the San Bernardino Fire Station #226
(latitude 34°08’04”, longitude -117°15’14”), which is approximately 13.5 miles northeast of the
project site (latitude 34°08’04”, longitude -117°15’14”),6 are 79.7- and 52.2-degrees Fahrenheit (°F),
respectively. Average winter (December, January, and February) high and low temperatures are
approximately 66.9°F and 42.6°F and average summer (June, July, and August) high and low
temperatures are approximately 93.1°F and 61.9°F.7 The annual average of total precipitation is
approximately 15.18 inches, which occurs mostly during the winter and relatively infrequently
during the summer. Monthly precipitation averages approximately 2.91 inches during the winter
(December, January, and February), approximately 1.38 inches during the spring (March, April, and
5 SCAQMD (South Coast Air Quality Management District), 1993. CEQA Air Quality Handbook. Diamond Bar, CA.
November.
6 Meteorological station location information from National Oceanographic and Atmospheric Administration, National
Climate Data Center, http://www.ncdc.noaa.gov/oa/climate/normals/norminv.txt. Accessed October 31, 2021.
7 Western Regional Climate Center. “Western U.S. Climate Historical Summaries.” Web site Available at:
http://www.wrcc.dri.edu/cgi-bin/cliMAIN.pl?ca5085. Accessed October 31, 2021.
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May), approximately 0.68 inch during the fall (September, October, and November), and
approximately 0.10 inch during the summer (June, July, and August).
Winds in the Basin are generally light, tempered by afternoon sea breezes. Severe weather is
uncommon in the Basin, but strong easterly winds known as the Santa Ana winds can reach 25 to
35 miles per hour below the passes and canyons. During the spring and summer months, air pollution
is carried out of the region through mountain passes in wind currents or is lifted by the warm vertical
currents produced by the heating of the mountain slopes. From the late summer through the winter
months, because of the average lower wind speeds and temperatures in the proposed project area
and its vicinity, air contaminants do not readily disperse, thus trapping air pollution in the area.
Regulatory Setting
POLLUTANTS OF CONCERN
3.2.1.1 Criteria Pollutants
Criteria pollutants are air pollutants for which acceptable levels of exposure can be determined and
an ambient air quality standard has been established by the U.S. Environmental Protection Agency
(USEPA) and/or the California Air Resources Board (ARB). The criteria air pollutants of concern are
nitrogen dioxide (NO2), carbon monoxide (CO), particulate matter (PM10 and PM2.5), sulfur dioxide
(SO2), lead (Pb), and ozone (O3), and their precursors. Since the proposed project would not generate
appreciable SO2 or Pb emissions,8 it is not necessary for the analysis to include those two pollutants.
Presented below is a description of the air pollutants of concern and their known health effects.
Nitrogen oxides (NOX) serve as integral participants in the process of photochemical smog production
and are precursors for certain particulate compounds that are formed in the atmosphere. The two
major forms of NOX are nitric oxide (NO) and NO2. NO is a colorless, odorless gas formed from
atmospheric nitrogen and oxygen when combustion takes place under high temperature and/or high
pressure. NO2 is a reddish-brown pungent gas formed by the combination of NO and oxygen. NO2 acts
as an acute respiratory irritant and eye irritant and increases susceptibility to respiratory pathogens.
A third form of NOX, nitrous oxide (N2O), is a GHG. (See Section 3.2.1.2.)
Carbon monoxide (CO) is a colorless, odorless non-reactive pollutant produced by incomplete
combustion of carbon substances (e.g., gasoline or diesel fuel). The primary adverse health effect
associated with CO is its binding with hemoglobin in red blood cells, which decreases the ability of
these cells to transport oxygen throughout the body. Prolonged exposure can cause headaches,
drowsiness, or loss of equilibrium; high concentrations are lethal.
Particulate matter (PM) consists of finely divided solids or liquids, such as soot, dust, aerosols, fumes,
and mists. Two forms of fine particulate matter are now regulated. Respirable particles, or PM10,
include that portion of the particulate matter with an aerodynamic diameter of 10 micrometers (i.e.,
10 one-millionths of a meter or 0.0004 inch) or less. Fine particles, or PM2.5, have an aerodynamic
diameter of 2.5 micrometers (i.e., 2.5 one-millionths of a meter or 0.0001 inch) or less. Particulate
discharge into the atmosphere results primarily from industrial, agricultural, construction, and
transportation activities. However, wind action on the arid landscape also contributes substantially
to the local particulate loading. Fossil fuel combustion accounts for a significant portion of PM2.5. In
8 Sulfur dioxide emissions will be about 0.03 pound per day during construction and about 0.01 pound per day during
operations.
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addition, particulate matter forms in the atmosphere through reactions of NOx and other compounds
(such as ammonia) to form inorganic nitrates and sulfates. Both PM10 and PM2.5 may adversely affect
the human respiratory system, especially in those people who are naturally sensitive or susceptible
to breathing problems.
Reactive organic gases (ROG) are compounds comprised primarily of atoms of hydrogen and carbon
that have high photochemical reactivity. The major source of ROG is the incomplete combustion of
fossil fuels in internal combustion engines. Other sources of ROG include the evaporative emissions
associated with the use of paints and solvents, the application of asphalt paving and the use of
household consumer products. Some ROG species are listed toxic air contaminants, which have been
shown to cause adverse health effects; however, most adverse effects on human health are not caused
directly by ROG, but rather by reactions of ROG to form other criteria pollutants such as ozone. ROG
are also transformed into organic aerosols in the atmosphere, contributing to higher levels of fine
particulate matter and lower visibility. The term “ROG” is used by the CARB for air quality analysis
and is defined essentially the same as the federal term “volatile organic compound” (VOC).
Ozone (O3) is a secondary pollutant produced through a series of photochemical reactions involving
ROG and NOX. O3 creation requires ROG and NOX to be available for approximately three hours in a
stable atmosphere with strong sunlight. Because of the long reaction time, peak ozone concentrations
frequently occur downwind of the sites where the precursor pollutants are emitted. Thus, O3 is
considered a regional, rather than a local, pollutant. The health effects of O3 include eye and
respiratory irritation, reduction of resistance to lung infection and possible aggravation of
pulmonary conditions in persons with lung disease. O3 is also damaging to vegetation and untreated
rubber.
3.2.1.2 Greenhouse Gases
GHGs are defined under the California Global Warming Solutions Act of 2006 (AB 32)9 as carbon
dioxide (CO2), methane (CH4), N2O, hydrofluorocarbons (HFCs), perfluorocarbons (PFCs) and sulfur
hexafluoride (SF6). Associated with each GHG species is a “global warming potential” (GWP), which
is a value used to compare the abilities of different GHGs to trap heat in the atmosphere. GWPs are
based on the heat-absorbing ability of each gas relative to that of CO2, as well as the decay rate of each
gas (the amount removed from the atmosphere over a given number of years). The GWPs of CH4 and
N2O are 25 and 298, respectively.10 “Carbon dioxide equivalent” (CO2e) emissions are calculated by
weighting each GHG compound’s emissions by its GWP and then summing the products. HFCs, PFCs,
and SF6 are not emitted in significant amounts by project sources, so they are not discussed further.
Carbon dioxide (CO2) is a clear, colorless, and odorless gas consisting of molecules made up of two
oxygen atoms and one carbon atom. Fossil fuel combustion is the main human-related source of CO2
emissions; electricity generation and transportation are first and second in the amount of CO2
emissions, respectively. Carbon dioxide is the basis of GWP, and thus has a GWP of 1.
Methane (CH4) is a clear, colorless gas, and is the main component of natural gas. Anthropogenic
sources of CH4 are fossil fuel production, biomass burning, waste management, and mobile and
stationary combustion of fossil fuel. Wetlands are responsible for most of the natural CH4 emissions.11
9 AB 32 is discussed in detail in Section 3.2.6.
10 GMI, 2019. What is a Global Warming Potential? And Which One Do I Use? GHG Management Institute.
https://ghginstitute.org/2010/06/28/what-is-a-global-warming-potential/. Accessed
11 USEPA, 2019. Overview of Greenhouse Gases. U.S. Environmental Protection Agency.
https://www.epa.gov/ghgemissions/overview-greenhouse-gases Accessed.
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As mentioned above, within a 100-year period CH4 is 25 times more effective in trapping heat than is
CO2.
Nitrous oxide (N2O) is a colorless, clear gas, with a slightly sweet odor. N2O has both natural and
human-related sources and is removed from the atmosphere mainly by photolysis (breakdown by
sunlight) in the stratosphere. The main human-related sources of N2O in the United States are
agricultural soil management (synthetic nitrogen fertilization), mobile and stationary combustion of
fossil fuel, adipic acid production, and nitric acid production. Nitrous oxide is also produced from a
wide range of biological sources in soil and water12. Within a 100-year span, N2O is 298 times more
effective in trapping heat than is CO2.13
3.2.1.3 Toxic Air Contaminants
A toxic air contaminant (TAC) is defined by California law as an air pollutant that “may cause or
contribute to an increase in mortality or in serious illness, or which may pose a present or potential
hazard to human health.”14 The USEPA uses the term hazardous air pollutant (HAP) in a similar sense.
The main mobile HAP source associated with this project will be combustion of diesel fuel by
construction equipment and by trucks serving the site. The following pollutants are components of
diesel fuel combustion in both stationary and mobile sources.
Acetaldehyde
Acetaldehyde is a colorless liquid with a high vapor pressure and, at dilute ambient concentrations,
a “fruity and pleasant odor.”15 It is present as a product of incomplete combustion in the exhausts of
stationary equipment (e.g., boilers and generators) and mobile sources. It is also a secondary
pollutant, formed through the photochemical reaction of VOC and NOX in the atmosphere. The
primary acute effect of inhalation exposure to acetaldehyde is irritation of the eyes, skin, and
respiratory tract in humans. At higher exposure levels, erythema, coughing, pulmonary edema, and
necrosis may also occur. Chronic exposure to acetaldehyde causes inflammation and injury to the
upper respiratory tract (e.g., lesions of the nasal passages).16 The chronic noncancer effects of
acetaldehyde in humans have not been well characterized. No information is available on the
reproductive or developmental effects of acetaldehyde in humans. The USEPA has classified
acetaldehyde as a probable human carcinogen.
Acrolein
Acrolein is a water-white or yellow liquid that burns easily, is readily volatilized, and has “a
disagreeable odor.”17 It is present as a product of incomplete combustion in the exhausts of stationary
equipment (e.g., boilers and heaters) and mobile sources. It is also a secondary pollutant, formed
through the photochemical reaction of VOC and NOX in the atmosphere. Acrolein is considered to
12 USEPA, 2019. Overview of Greenhouse Gases. U.S. Environmental Protection Agency.
https://www.epa.gov/ghgemissions/overview-greenhouse-gases Accessed
13 IPCC, 2007. Climate Change 2007: The Physical Science Basis. Contribution of Working Group I to the Fourth
Assessment Report of the Intergovernmental Panel on Climate Change. 2007
14 California Health and Safety Code §39655(a).
15 U.S. Environmental Protection Agency, “Acetaldehyde.” Technology Transfer Network, Air Toxics Web Site, Internet
URL: www.epa.gov/ttn/atw/hlthef/acetalde.html. Updated November 6, 2007.
16 California Office of Environmental Health Hazard Evaluation, “Acetaldehyde Reference Exposure Levels.” Draft
Technical Support Document for Noncancer RELs. Scientific Review Panel. December 2008.
17 U.S. Environmental Protection Agency, “Acrolein.” Technology Transfer Network, Air Toxics Web Site. Internet URL:
www.epa.gov/ttn/atw/hlthef/acrolein.html. Updated November 6, 2007.
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have high acute toxicity and causes upper respiratory tract irritation and congestion in humans. The
major effects from chronic (long-term) inhalation exposure to acrolein in humans consist of general
respiratory congestion and eye, nose, and throat irritation. No information is available on the
reproductive, developmental, or carcinogenic effects of acrolein in humans. The USEPA considers
acrolein data to be inadequate for an assessment of human carcinogenic potential.
Benzene
Benzene is a volatile, colorless, highly flammable liquid with a “sweet” odor.18 Most of the benzene in
ambient air is from incomplete combustion of fossil fuels and evaporation from gasoline service
stations. Acute inhalation exposure to benzene causes neurological symptoms, such as drowsiness,
dizziness, headaches, and unconsciousness in humans. Chronic inhalation of certain levels of benzene
causes disorders in the blood in humans. Benzene specifically affects bone marrow (the tissues that
produce blood cells). Aplastic anemia, excessive bleeding, and damage to the immune system (by
changes in blood levels of antibodies and loss of white blood cells) may develop. Human data on the
developmental effects of benzene are inconclusive due to concomitant exposure to other chemicals,
inadequate sample size, and lack of quantitative exposure data. The USEPA has classified benzene as
a known human carcinogen by inhalation.
1,3‐Butadiene
1,3-Butadiene is a colorless gas with a mild gasoline-like odor. Sources of 1,3-butadiene released into
the air include motor vehicle exhaust, manufacturing and processing facilities, forest fires or other
combustion, and cigarette smoke.19 Acute exposure to 1,3-butadiene by inhalation in humans results
in irritation of the eyes, nasal passages, throat, and lungs. Neurological effects, such as blurred vision,
fatigue, headache, and vertigo, have also been reported at very high exposure levels. One
epidemiological study reported that chronic exposure to 1,3-butadiene via inhalation resulted in an
increase in cardiovascular diseases, such as rheumatic and arteriosclerotic heart diseases, while
other human studies have reported effects on the blood. No information is available on reproductive
or developmental effects of 1,3-butadiene in humans. USEPA has classified 1,3-butadiene as a
“probable human carcinogen” by inhalation.20
Diesel Particulate Matter/Diesel Exhaust Organic Gases
Diesel particulate matter/diesel exhaust organic gases21 comprise a complex mixture of hundreds of
constituents in either a gaseous or particle form. Gaseous components of diesel exhaust (DE) include
CO2, oxygen, nitrogen, water vapor, CO, nitrogen compounds, sulfur compounds, and numerous
low-molecular-weight hydrocarbons. Among the gaseous hydrocarbon components of DE that are
individually known to be of toxicological relevance are several carbonyls (e.g., formaldehyde,
acetaldehyde, acrolein), benzene, 1,3-butadiene, and polycyclic aromatic hydrocarbons (PAHs) and
18 U.S. Environmental Protection Agency, “Benzene.” Technology Transfer Network, Air Toxics Web Site. Internet URL:
www.epa.gov/ttn/atw/hlthef/benzene.html. Updated February 4, 2008.
19 U.S. Environmental Protection Agency, “1,3-Butadiene.” Technology Transfer Network, Air Toxics Web Site. Internet
URL: www.epa.gov/ttn/atw/hlthef/butadiene.html. Updated March 31, 2009.
20 U.S. Environmental Protection Agency, “1,3-Butadiene (CASRN 106-99-0).” Integrated Risk Information System web
site, Internet URL: www.epa.gov/iris/subst/0139.htm. Updated July 9, 2009.
21 USEPA MSAT regulations consider both the particulate and gaseous components of diesel engine exhaust, while
California regulations focus on diesel particulate matter (DPM).
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nitro-PAHs.22 Diesel particulate matter (DPM) is composed of a center core of elemental carbon and
adsorbed organic compounds, as well as small amounts of sulfate, nitrate, metals, and other trace
elements. DPM consists primarily of PM2.5, including a subgroup with a large number of particles
having a diameter <0.1 micrometer. Collectively, these particles have a large surface area, which
makes them an excellent medium for adsorbing organics. Also, their small size makes them highly
respirable and able to reach the deep lung. A number of potentially toxicologically relevant organic
compounds, including PAHs, nitro-PAHs, and oxidized PAH derivatives, are on the particles. Diesel
exhaust is emitted from onroad mobile sources, such as automobiles and trucks, and from offroad
mobile sources (e.g., diesel locomotives, marine vessels, and construction equipment). DPM is
directly emitted from diesel-powered engines (primary particulate matter) and can be formed from
the gaseous compounds emitted by diesel engines (secondary particulate matter).
Acute or short-term (e.g., episodic) exposure to diesel exhaust (DE) can cause acute irritation (e.g.,
eye, throat, bronchial), neurophysiological symptoms (e.g., lightheadedness, nausea), and respiratory
symptoms (cough, phlegm). Evidence also exists for an exacerbation of allergenic responses to
known allergens and asthma-like symptoms.23 Information from the available human studies is
inadequate for a definitive evaluation of possible noncancer health effects from chronic exposure to
DE. However, on the basis of extensive animal evidence, DE is judged to pose a chronic respiratory
hazard to humans. USEPA has determined that DE is “likely to be carcinogenic to humans by
inhalation” and that this hazard applies to environmental exposures.24
Formaldehyde
Formaldehyde is a colorless gas with a pungent, suffocating odor at room temperature.25 The major
emission sources of formaldehyde appear to be power plants, manufacturing facilities, incinerators,
and automobile exhaust. However, most of the formaldehyde in ambient air is a result of secondary
formation through photochemical reaction of VOC and NOx.26 The major toxic effects caused by acute
formaldehyde exposure via inhalation are eye, nose, and throat irritation and effects on the nasal
cavity. Other effects seen from exposure to high levels of formaldehyde in humans are coughing,
wheezing, chest pains, and bronchitis. Chronic exposure to formaldehyde by inhalation in humans
has been associated with respiratory symptoms and eye, nose, and throat irritation. USEPA considers
formaldehyde to be a probable human carcinogen.
APPLICABLE AIR QUALITY REGULATIONS
3.2.2.1 Federal Regulations
The Federal Clean Air Act (CAA), passed in 1970, established the national air pollution control
program. The basic elements of the CAA are the NAAQS for criteria air pollutants, hazardous air
pollutants standards, state attainment plans, motor vehicle emissions standards, stationary source
22 U.S. Environmental Protection Agency, Health Assessment Document for Diesel Engine Exhaust. Washington, DC:
National Center for Environmental Assessment, Office of Research and Development, EPA/600/8-90/057F. May
2002.
23 U.S. Environmental Protection Agency, Health Assessment Document for Diesel Engine Exhaust. Washington, DC:
National Center for Environmental Assessment, Office of Research and Development, EPA/600/8-90/057F. May
2002.
24 Ibid.
25 U.S. Environmental Protection Agency, “Formaldehyde.” Technology Transfer Network, Air Toxics Web Site. Internet
URL: www.epa.gov/ttn/atw/hlthef/formalde.html. Updated November 6, 2007.
26 Rogozen, M. B. et al. Formaldehyde: A Survey of Airborne Concentrations and Sources. Hermosa Beach, California:
Science Applications, Inc. for the California Air Resources Board, Sacramento, California, SAI-84/1642. 1984.
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emissions standards and permits, acid rain control measures, stratospheric ozone protection, and
enforcement provisions.
The NAAQS are the maximum allowable concentrations of criteria pollutants, over specified
averaging periods, to protect human health. The CAA requires that the USEPA establish NAAQS and
reassess, at least every five years, whether they are adequate to protect public health, based on
current scientific evidence. The NAAQS are divided into primary and secondary standards; the
former are set to protect human health within an adequate margin of safety, and the latter to protect
environmental values, such as plant and animal life.
Data collected at permanent monitoring stations are used by the USEPA to classify regions as
“attainment” or “nonattainment,” depending on whether the regions have met the requirements
stated in the primary NAAQS. Nonattainment areas are subject to additional restrictions, as required
by the USEPA.
The CAA Amendments in 1990 substantially revised the planning provisions for those areas not
currently meeting NAAQS. The Amendments identify specific emission reduction goals that require
both a demonstration of reasonable further progress and attainment and incorporate more stringent
sanctions for failure to attain the NAAQS or to meet interim attainment milestones.
3.2.2.2 State Regulations
The State of California began to set California ambient air quality standards (CAAQS) in 1969 under
the mandate of the Mulford-Carrell Act. There were no attainment deadlines for the CAAQS originally.
However, the State Legislature passed the California Clean Air Act (CCAA) in 1988 to establish air
quality goals, planning mechanisms, regulatory strategies, and standards of progress to promote
their attainment. The ARB, which became part of the California Environmental Protection Agency
(CalEPA) in 1991, is responsible for ensuring implementation of the CCAA, responding to the federal
CAA, and for regulating emissions from motor vehicles and consumer products.
The California CAA requires attainment of CAAQS by the earliest practicable date. The state standards
are generally more stringent than the corresponding federal standards. Attainment plans are
required for air basins in violation of the State O3, PM10, CO, SO2, or NO2 standards. Responsibility for
achieving state standards is placed on the ARB and local air pollution control districts. District plans
for nonattainment areas must be designed to achieve a 5-percent annual reduction in emissions.
Preparation of and adherence to attainment plans are the responsibility of the local air pollution
districts or air quality management districts.
Table 3.2‐1 lists the NAAQS and CAAQS for criteria pollutants.
EXISTING CONDITIONS 7102/Summit Avenue Warehouse Project Page 3-8 Air Quality and Greenhouse Gas Emissions Report April 2022 Table 3.2‐1 AMBIENT AIR QUALITY STANDARDS FOR CRITERIA AIR POLLUTANTS Pollutant Averaging Time California Standards1 Federal Standards 2 Concentration3 Method4 Primary3,5 Secondary 3,6 Method7 Ozone (O3)8 1 Hour 0.09 ppm (180 µg/m3) Ultraviolet Photometry — Same as Primary Standard Ultraviolet Photometry 8 Hour 0.070 ppm(137 µg/m3) 0.070 ppm (137 µg/m3) Respirable Particulate Matter (PM10)9 24 Hour 50 µg/m3Gravimetric or Beta Attenuation 150 µg/m3Same as Primary Standard Inertial Separation and Gravimetric Analysis Annual Arithmetic Mean 20 µg/m3 — Fine Particulate Matter (PM2.5)9 24 Hour No Separate State Standard 35 µg/m3 Same as Primary Standard Inertial Separation and Gravimetric Analysis Annual Arithmetic Mean 12 µg/m3 Gravimetric or Beta Attenuation 12 µg/m3 15 µg/m3 Carbon Monoxide (CO) 1 Hour 20 ppm(23 mg/m3) Non-Dispersive Infrared Photometry (NDIR) 35 ppm(40 mg/m3) — Non-Dispersive Infrared Photometry(NDIR) 8 Hour 9.0 ppm(10 mg/m3) 9 ppm(10 mg/m3) 8 Hour (Lake Tahoe) 6 ppm (7 mg/m3) — — Nitrogen Dioxide (NO2)10 1 Hour 0.18 ppm(339 µg/m3) Gas Phase Chemiluminescence 100 ppm(188 µg/m3) — Gas Phase Chemiluminescence Annual Arithmetic Mean 0.030 ppm(57 µg/m3) 0.053 ppm(100 µg/m3) Same as Primary Standard Sulfur Dioxide (SO2)11 1 Hour 0.25 ppm(655 µg/m3) Ultraviolet Fluorescence 75 ppm(196 µg/m3) — Ultraviolet Fluorescence; Spectrophotometry (Pararosaniline Method) 3 Hour — — 0.5 ppm(1300 µg/m3) 24 Hour 0.04 ppm(105 µg/m3) 0.14 ppm(for certain areas)11— Annual Arithmetic Mean — 0.030 ppm(for certain areas)11—
EXISTING CONDITIONS 7102/Summit Avenue Warehouse Project Page 3-9 Air Quality and Greenhouse Gas Emissions Report April 2022 Pollutant Averaging Time California Standards1 Federal Standards 2 Concentration3 Method4 Primary3,5 Secondary 3,6 Method7 Lead12,13 30 Day Average 1.5 µg/m3Atomic Absorption —— High Volume Sampler and Atomic Absorption Calendar Quarter — 1.5 µg/m3 (for certain areas)12 Same as Primary Standard Rolling 3-Month Averagej — 0.15 µg/m3 Visibility Reducing Particles14 8 Hour See footnote 14 Beta Attenuation and Transmittance through Filter Tape No National Standards Sulfates 24 Hour 25 µg/m3Ion ChromatographyHydrogen Sulfide 1 Hour 0.03 ppm(42 µg/m3) Ultraviolet Fluorescence Vinyl Chloride12 24 Hour 0.01 ppm(26 µg/m3) Gas Chromatography 1. California standards for ozone, carbon monoxide (except 8-hour Lake Tahoe), sulfur dioxide (1 and 24 hour), nitrogen dioxide, suspended particulate matter–-PM10, PM2.5, and visibility reduction 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. National standards (other than ozone, particulate matter, and those based on annual averages or 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 in a year, averaged over 3 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 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% of the daily concentrations, averaged over 3 years, are equal to or less than the standard. 3. Concentration expressed first in units in which it was promulgated. Equivalent units given in parentheses are based upon a reference temperature of 25oC and a reference pressure of 760 torr. Most measurements of air quality are to be corrected to a reference temperature of 25oC and a reference pressure of 760 torr; ppm in this table refers to ppm by volume, or micromoles of pollutant per mole of gas. 4. Any equivalent procedure which can be shown to the satisfaction of the ARB to give equivalent results at or near the level of the air quality standard may be used. 5. National Primary Standards: The levels of air quality necessary, with an adequate margin of safety to protect the public health. 6. National Secondary Standards: The levels of air quality necessary to protect the public welfare from any known or anticipated adverse effects of a pollutant.7. Reference method as described by the EPA. An “equivalent method” of measurement may be used but must have a “consistent relationship to the reference method” and must be approved by EPA. 8. On October 1, 2015, the national 8-hour ozone primary and secondary standards were lowered from 0.075 to 0.070 ppm.
EXISTING CONDITIONS 7102/Summit Avenue Warehouse Project Page 3-10 Air Quality and Greenhouse Gas Emissions Report April 2022 Pollutant Averaging Time California Standards1 Federal Standards 2 Concentration3 Method4 Primary3,5 Secondary 3,6 Method7 9. As of December 14, 2012, the annual primary PM2.5 standard changed from 15 µg/m3 to 12 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 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. 10. 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. 11. 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 national 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 national 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. 12. 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. 13. 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. 14. 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.
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AIR QUALITY MANAGEMENT PLAN (AQMP)
The SCAQMD is required to produce plans to show how air quality will be improved in the region.
The CCAA requires that these plans be updated triennially to incorporate the most recent available
technical information. A multi-level partnership of governmental agencies at the federal, state,
regional, and local levels implements the programs contained in these plans. Agencies involved
include the USEPA, ARB, local governments, SCAG, and SCAQMD. The SCAQMD and the SCAG are
responsible for formulating and implementing the AQMP for the SCAB. The SCAQMD updates its
AQMP every three years.
The 2016 AQMP was adopted by the SCAQMD Board on March 3, 2017, and on March 10, 2017 was
submitted to the ARB as part of the California State Implementation Plan (SIP).27 It focuses largely on
reducing NOx emissions as a means of attaining the 1979 1-hour ozone standard by 2022, the 1997
8-hour ozone standard by 2023, and the 2008 8-hour standard by 2031.28 The AQMP prescribes a
variety of current and proposed new control measures, including a request to the USEPA for
increased regulation of mobile source emissions. The NOx control measures will also help the SCAB
attain the 24-hour standard for PM2.5.
SCAQMD RULE 403
3.2.4.1 Requirements for All Construction Projects
SCAQMD Rule 403 (Fugitive Dust) limits particulate matter emissions from construction projects.
The following requirements apply to all construction projects, regardless of the size of their disturbed
areas:29
No person shall cause or allow emissions of fugitive dust to remain visible in the atmosphere
beyond the property line of the emission source or to exceed 20 percent opacity if the dust
emission is a result of a moving motorized vehicle.
Apply applicable Best Available Control Measures (BACM) in Table 1 of Rule 403 to minimize
fugitive dust emissions during active operation.30
No person shall cause or allow PM10 levels to exceed 50 micrograms per cubic meter when
determined as the difference between upwind and downwind samples collected on
high-volume particulate matter samplers or other USEPA-approved equivalent method for
PM10 monitoring at the project limits for a five-hour period during the time of Active
Operations.31 Sampling will only occur if a complaint is reported to the SCAQMD, in which
case the decision to conduct sampling will be made by SCAQMD, and SCAQMD will conduct
sampling.
27 SCAQMD, 2017a. Letter from Wayne Nastri, Executive Officer, South Coast Air Quality Management District, Diamond
Bar, CA to Richard Corey, Executive Officer, California Air Resources Board, Sacramento, California re: Submittal of
2016 Air Quality Management Plan.
28 SCAQMD, 2017b. Final 2016 Air Quality Management Plan. South Coast Air Quality Management District. March 2017.
29 SCAQMD Rule 403(d), as Amended June 3, 2005.
30 SCAQMD Rule 403(d)(2), as Amended June 3, 2005.
31 SCAQMD Rule 403(d)(3), as Amended June 3, 2005.
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No person shall allow track-out to extend 25 feet or more in cumulative length from the point
of origin from an active operation, and all track-out from an active operation shall be removed
at the conclusion of each workday or evening shift.32
No person shall conduct an active operation with a disturbed surface area of five or more
acres, or with a daily import or export of 100 cubic yards or more of bulk material without at
least one of the measures listed under (D)(5) of Rule 403 at each vehicle egress.33
3.2.4.2 Requirements for Large Operations
If the disturbed surface area of a project site reaches 50 acres or if daily earth-moving or throughput
volume reaches 3,850 cubic meters (5,000 cubic yards), it is necessary to submit a Rule 403
Notification indicating that the project will be considered a “large operation” as defined in
Rule 403(c)(21). Large operations are required to install project signage, maintain a record of all dust
control actions taken, and revise the project Dust Control Plan34 annually. Also, SCAQMD prescribes
a separate list of additional best available dust control measures for large operations. These
measures are more numerous and more stringent than those for smaller operations. Because the
Summit Avenue warehouse site is less than 50 acres, these provisions do not apply to the project.
SCAQMD RULE 2305
If a new warehouse has at least 100,000 square feet of area dedicated to “warehousing activity” as
defined35 in the SCAQMD Warehousing Indirect Source Rule (Rule 2305), it will be subject to the Rule
and comply with the Warehouse Actions and Investments to Reduce Emissions (WAIRE) Program, a
menu-based points system. As stated in Section 2.2.3, the area of warehousing activities will be
92,380 square feet. Other building components, such as the office and mezzanine do not count as
warehousing. This analysis assumes, therefore, that Rule 2305 does not apply to the proposed
project.
CITY OF FONTANA GENERAL PLAN
The City of Fontana's General Plan36 outlines the concerns of the community and the means of
addressing those concerns. General Plan goals and policies that relate to air quality and greenhouse
gas impacts include the following:
Community Mobility and Circulation Element
Goal 1: The City of Fontana has a comprehensive and balanced transportation system with
safety and multimodal accessibility the top priority of citywide transportation planning, as
well as accommodating freight movement.
o Make land use decisions that support walking, bicycling, and public transit use, in
alignment with the 2014-2040 Regional Transportation Plan and Sustainable
Communities Strategy.
32 SCAQMD Rule 403(d)(4), as Amended June 3, 2005.
33 SCAQMD Rule 403(d)(5), as Amended June 3, 2005.
34 Only if the applicant has a dust control plan; Rule 403 does not require one.
35 SCAQMD Rule 2305(c)(33), as adopted May 7, 2021.
36 Fontana Forward: General Plan Update 2015-2035. City of Fontana. November 13, 2018. General Plan Update 2015 -
2035 | Fontana, CA - Official Website.
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Goal 4: Fontana’s neighborhood streets maintain a residential character and support a range
of transportation options.
o Balance neighborhood traffic circulation needs with the goal of creating walkable and
bike friendly neighborhoods.
Goal 5: Fontana’s commercial and mixed-use areas include a multifunctional street network
that ensures a safe, comfortable, and efficient movement of people, goods, and services to
support a high quality of life and economic vitality.
o Encourage mixed use and commercial developments that support walking, bicycling,
and public transit use while balancing the needs of motorized traffic to serve such
developments.
o Provide roadways that serve the needs of Fontana residents and commerce, and that
facilitate safe and convenient access to transit, bicycle facilities, and walkways
o Promote concentrated development patterns in coordination with transit planning to
maximize service efficiency and ridership.
o Coordinate with regional agencies and Caltrans to participate in regional efforts to
maintain transportation infrastructure in Fontana.
Goal 7: The city of Fontana participates in shaping regional transportation policies to reduce
traffic congestion and greenhouse gas emissions.
o Participate in the efforts of the SCAG to coordinate transportation planning and
services that support greenhouse gas reductions.
Infrastructure and Green Systems Element
Goal 2: Fontana promotes use of non-potable water for uses where drinking water is not
needed.
o Encourage use of processed water from the Inland Empire Utilities Agency (IEUA)
systems using recycled water for all non-drinking water purposes.
o Promote laundry-to-landscape greywater systems for single-family housing units.
Goal 3: The city continues to have an effective water-conservation program.
o Support landscaping in public and private spaces with drought-resistant plants.
o Continue successful city water conservation programs and partnerships.
Goal 7: Fontana is an energy-efficient community.
o Promote renewable energy and distributed energy systems in new development and
retrofits of existing development to work towards the highest levels of low-carbon
energy-efficiency.
Sustainability and Resilience Element
Goal 1: Fontana is a regional leader in sustainability and resilience with an effective
"Sustainable Fontana" program.
o Create a Sustainable Fontana program that promotes green practices in government
and in the community.
Goal 2: Government facilities and operations are models of resource efficiency.
o Incorporate goals into the City Code for resource efficiency in municipal facilities and
operations.
o Continue organizational and operational improvements to maximize energy and
resource efficiency and reduce waste.
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Goal 3: Renewable sources of energy, including solar and wind, and other energy-
conservation strategies are available to city households and businesses.
o Promote renewable energy and distributed energy systems in new development and
retrofits of existing development to work towards the highest levels of low-carbon
energy-efficiency.
Goal 4: Fontana meets the greenhouse gas reduction goals for 2030 and subsequent goals set
by the state.
o Continue to collaborate with SBCTA, infrastructure agencies and utilities on
greenhouse gas reduction studies and goals.
Goal 5: Green building techniques are used in new development and retrofits.
o Establish a residential "cool roofs" program to reduce air conditioning costs and the
urban heat island effect.
o Encourage retrofits of whole house fans for existing buildings.
o Establish an annual award for green development projects, including retrofits, in
Fontana.
Goal 6: Fontana is a leader energy-efficient development and retrofits.
o Promote energy-efficient development in Fontana.
o Meet or exceed state goals for energy-efficient new construction.
Goal 7: Conservation of water resources with best practices such as drought-tolerant plant
species, recycled water, greywater systems, has become a way of life in Fontana.
o Continue to promote and implement best practices to conserve water.
GREENHOUSE GAS EMISSIONS
3.2.7.1 Federal Climate Change Regulations
The federal government has been involved in climate change issues at least since 1978, when
Congress passed the National Climate Program Act (92 Stat. 601), under authority of which the
National Research Council prepared a report predicting that additional increases in atmospheric CO2
would lead to non-negligible changes in climate. At the “Earth Summit” in 1992 in Rio de Janeiro,
President George H. W. Bush signed the United Nations Framework Convention on Climate Change
(UNFCCC), a nonbinding agreement among 154 nations to reduce atmospheric concentrations of
carbon dioxide and other greenhouse gases. The treaty was ratified by the U.S. Senate. However,
when the UNFCCC signatories met in 1997 in Kyoto, Japan, and adopted a protocol that assigned
mandatory targets for industrialized nations to reduce greenhouse gas emissions, the U.S. Senate
expressed its opposition to the treaty. The Kyoto Protocol was not submitted to the Senate for
ratification.
In 2007, Massachusetts et al. v. Environmental Protection Agency et al. (549 U.S. 497), the U.S.
Supreme Court ruled that CO2 was an air pollutant under the Clean Air Act, and that consequently,
the USEPA had the authority to regulate its emissions. The Court also held that the Administrator
must determine whether emissions of greenhouse gases from new motor vehicles cause or
contribute to air pollution which may reasonably be anticipated to endanger public health or welfare,
or whether the science is too uncertain to make a reasoned decision. On April 24, 2009, the USEPA
published its intention to find that: (1) the current and projected concentrations of the mix of six key
greenhouse gases—CO2, CH4, N2O, HFCs, PFCs and SF6—in the atmosphere threaten the public health
and welfare of current and future generations, and that (2) the combined emissions of GHG from new
motor vehicles and motor vehicle engines contribute to the atmospheric concentrations of these key
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greenhouse gases and hence to the threat of climate change (74 Fed. Reg. 18886). These findings are
required for subsequent regulations that would control GHG emissions from motor vehicles.
The USEPA collects several types of GHG emissions data. These data help policy makers, businesses,
and the USEPA track GHG emissions trends and identify opportunities for reducing emissions and
increasing efficiency. The USEPA has been maintaining a national inventory of GHG emissions since
1990 and in 2009 established mandatory reporting of GHG emissions from large GHG emissions
sources.
USEPA is also getting GHG reductions through partnerships and initiatives; evaluating policy options,
costs, and benefits; advancing the science; partnering internationally and with states, localities, and
tribes; and helping communities adapt.
Heavy‐Duty National Program. In 2011, USEPA and the National Highway Traffic Safety
Administration (NHTSA) began taking coordinated steps to enable the production of a new
generation of clean heavy-duty vehicles, through reduced GHG emissions and improved fuel use from
onroad vehicles and engines. Phase 1 of the Greenhouse Gas Emissions Standards and Fuel Efficiency
Standards for Medium- and Heavy-Duty Engines and Vehicles addressed medium- and heavy-duty
trucks manufactured in model years 2014-2018. In August 2016, USEPA and NHTSA jointly finalized
Phase 2 standards for medium- and heavy-duty vehicles through model year 2027 and on August 5,
2021, USEPA announced plans for the next 3 years, addressing heavy-duty vehicles starting in model
year 2027.
3.2.7.2 California Climate Change Regulations
Executive Order S‐3‐05 (GHG Emissions Reductions). Executive Order #S-3-05, signed by Governor
Arnold Schwarzenegger on June 1, 2005, calls for a reduction in GHG emissions to 1990 levels by
2020 and for an 80% reduction in GHG emissions to below 1990 levels by 2050.
The California Global Warming Solutions Act of 2006 (AB 32). In September 2006, Governor
Arnold Schwarzenegger signed AB 32, the California Global Warming Solutions Act of 2006 (Health
and Safety Code § 38500 et seq.), into law. AB 32 was intended to effectively end the scientific debate
in California over the existence and consequences of global warming. In general, AB 32 directs the
ARB to do the following:
On or before June 30, 2007, publicly make available a list of discrete early action GHG
emission reduction measures that can be implemented prior to the adoption of the statewide
GHG limit and the measures required to achieve compliance with the statewide limit;
By January 1, 2008, determine the statewide levels of GHG emissions in 1990, and adopt a
statewide GHG emissions limit that is equivalent to the 1990 level (an approximately 28%
reduction in existing statewide GHG emissions);
On or before January 1, 2010, adopt regulations to implement the early action GHG emission
reduction measures;
On or before January 1, 2011, adopt quantifiable, verifiable, and enforceable emission
reduction measures by regulation that will achieve the statewide GHG emissions limit by
2020, to become operative on January 1, 2012, at the latest. The emission reduction measures
may include direct emission reduction measures, alternative compliance mechanisms, and
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potential monetary and non-monetary incentives that reduce GHG emissions from any
sources or categories of sources as the ARB finds necessary to achieve the statewide GHG
emissions limit; and
Monitor compliance with and enforce any emission reduction measure adopted pursuant to
AB 32.
On December 11, 2008, the ARB approved the Climate Change Scoping Plan37 pursuant to AB 32. The
Scoping Plan recommends a wide range of measures for reducing GHG emissions, including (but not
limited to):
Expanding and strengthening of existing energy efficiency programs;
Achieving a statewide renewables energy mix of 33 percent;
Developing a GHG emissions cap-and-trade program;
Establishing targets for transportation-related GHG emissions for regions throughout the
state, and pursuing policies and incentives to meet those targets;
Implementing existing state laws and policies, including California’s clean car standards,
goods movement measures and the Low Carbon Fuel Standard; and
Targeted fees to fund the state’s long-term commitment to administering AB 32.
2014 Update to Climate Change Scoping Plan: On May 22, 2014, the ARB approved the First Update
to the Climate Change Scoping Plan Pursuant to AB 32,38 which shows that California is on track to
meet the near-term 2020 greenhouse gas limit and is well positioned to maintain and continue
reductions beyond 2020 as required by AB 32. In accordance with the UNFCCC, the ARB is beginning
to transition to the use of the IPCC’s Fourth Assessment Report (AR4) 100-year GWPs in its climate
change programs. The ARB has recalculated the 1990 GHG emissions level with the AR4 GWPs to be
431 million metric ton of CO2e (MMTCO2e); therefore, the 2020 GHG emissions limit established in
response to AB 32 is now slightly higher than the 427 MMTCO2e in the initial Scoping Plan. The
updated scoping plan evaluates the effectiveness of policies from the original scoping plan and adds
recommendations for expanding and improving upon those programs including, but not limited to:
Leveraging public money to fund technologies including medium and heavy duty Zero
Emission Vehicles (ZEVs).
Expanding local, regional, and state transportation plan goals to improve transit efficiency.
Supporting the High-Speed Rail Authority and Sustainable Freight Strategy.
37 Climate Change Scoping Plan. A Framework for change. California Air Resources Board. December 2008. Final
Version (May 2009). URL:
https://ww2.arb.ca.gov/sites/default/files/classic/cc/scopingplan/document/adopted_scoping_plan.pdf.
38 First Update to the Climate Change Scoping Plan. Building on the Framework. California Air Resources Board. May
2014. URL:
https://ww2.arb.ca.gov/sites/default/files/classic/cc/scopingplan/2013_update/first_update_climate_change_scopi
ng_plan.pdf.
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Extending Low Carbon Fuel Standards beyond 2020 with more aggressive goals.
Developing accurate methods for estimating agricultural emissions so that greenhouse gas
reduction techniques can be assessed.
Eliminating disposal of organic matter and promote methane recovery at landfills.
Instituting the Forest Carbon Plan to model and understand the carbon cycle of forestry.
Implementing economic incentives for the destruction of short-lived climate pollutants.
Allowing limited future allowances for Cap-and-Trade to reduce cost spikes.
Setting interim goals to reach greenhouse gas emissions of 80% of 1990 levels by 2050.
2017 Update to Climate Change Scoping Plan: The 2017 Update to the Scoping Plan39 builds upon
the former Scoping Plans and Updates by outlining priorities and recommendations for the State to
achieve its long-term climate objectives. The 2017 Update establishes a proposed framework of
action for California to meet the climate target of a 40% reduction in GHGs by 2030, compared to
1990 levels. The major elements of the framework proposed are enhancement of the Renewables
Portfolio Standard and the Low Carbon Fuel Standard; a Mobile Source Strategy, Sustainable Freight
Action Plan, Short-Lived Climate Pollutant Reduction Strategy, Sustainable Communities Strategies,
and a Post-2020 Cap-and-Trade Program; a 20% reduction in GHG emissions from the refinery sector
and an Integrated Natural and Working Lands Action Plan.
Executive Order S‐01‐07 (Low Carbon Fuel Standard). Executive Order #S-01-07
(January 18, 2007) establishes a statewide goal to reduce the carbon intensity of California’s
transportation fuels by at least 10% by 2020 through establishment of a Low Carbon Fuel Standard.
Carbon intensity is the amount of CO2e per unit of fuel energy emitted from each stage of producing,
transporting, and using the fuel in a motor vehicle. On April 23, 2009, the ARB adopted a regulation
to implement the standard.
Senate Bill 97. Senate Bill 97 was signed by the governor on August 24, 2007. The bill required the
Office of Planning and Research (OPR), by July 1, 2009, to prepare, develop and transmit to the
Resources Agency guidelines for the feasible mitigation of GHG emissions or the effects of GHG
emissions, as required by CEQA, including, but not limited to, effects associated with transportation
or energy consumption. On April 13, 2009, OPR submitted to the Secretary for Natural Resources its
proposed amendments to the State CEQA Guidelines for greenhouse gas emissions. The Resources
Agency adopted those guidelines on December 30, 2009, and they became effective on
March 18, 2010. The amendments treat GHG emissions as a separate category of impacts; i.e., they
are not to be addressed as part of an analysis of air quality impacts.
Section 15064.4, which was added to the CEQA Guidelines, specifies how the significance of impacts
from GHGs is to be determined. First, the lead agency should “make a good faith effort” to describe,
calculate or estimate the amount of GHG emissions resulting from a project. After that, the lead
39 The 2017 Climate Change Scoping Plan Update: The Proposed Strategy for Achieving California’s 2030 Greenhouse
Gas Target. California Air Resources Board. January 20, 2017. URL:
https://www.arb.ca.gov/cc/scopingplan/2030sp_pp_final.pdf.
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agency should consider the following factors when assessing the impacts of the GHG emissions on
the environment:
The extent to which the project may increase or reduce GHG emissions, relative to the existing
environmental setting;
Whether the project emissions exceed a threshold of significance that the lead agency
determines applies to the project; and
The extent to which the project complies with regulations or requirements adopted to
implement a statewide, regional, or local plan for the reduction or mitigation of GHG
emissions.
The OPR asked the ARB to make recommendations for GHG-related thresholds of significance. On
October 24, 2008, the ARB issued a preliminary draft staff proposal for Recommended Approaches for
Setting Interim Significance Thresholds for Greenhouse Gases under the California Environmental
Quality Act.40 After holding two public workshops and receiving comments on the proposal, ARB staff
decided not to proceed with threshold development.41 Quantitative significance thresholds, if any,
are to be set by local agencies.
Senate Bill 375. Senate Bill (SB) 375 passed the Senate on August 30, 2008, and was signed by the
governor on September 30, 2008. According to SB 375, the transportation sector is the largest
contributor of GHG emissions and contributes over 40% of the GHG emissions in California, with
automobiles and light trucks alone contributing almost 30%. SB 375 indicates that GHGs from
automobiles and light trucks can be reduced by new vehicle technology. However, significant
reductions from changed land use patterns and improved transportation also are necessary. SB 375
states, “Without improved land use and transportation policy, California will not be able to achieve
the goals of AB 32.” SB 375 (1) requires metropolitan planning organizations to include sustainable
community strategies in their regional transportation plans for reducing GHG emissions, (2) aligns
planning for transportation and housing, and (3) creates specified incentives for the implementation
of the strategies.
Senate Bill 375 requires coordination of land use and transportation planning to reduce GHG
emissions from transportation sources. Regional transportation plans, which are developed by
metropolitan transportation organizations such as the SCAG, are to include “sustainable community
strategies” to reduce GHG emissions.
Title 24 Building Energy Efficiency Standards. The Energy Efficiency Standards for Residential and
Nonresidential Buildings (Title 24, Part 6, of the California Code of Regulations) were established in
1978 in response to a legislative mandate to reduce California's energy consumption. The standards
are updated periodically to allow consideration and possible incorporation of new energy efficiency
technologies and methods. Compliance with Title 24 will result in decreases in GHG emissions. The
California Energy Commission (CEC) adopted the 2019 changes to the Building Energy Efficiency
Standards on April 23, 2008, with an aim to promote the objectives listed below.42 They focus on
40 Preliminary Draft Staff Proposal. Recommended Approaches for Setting Interim Significance Thresholds for
Greenhouse Gases under the California Environmental Quality Act. California Air Resources Board. October 24, 2008,
URL: https://ww3.arb.ca.gov/cc/localgov/ceqa/meetings/102708/prelimdraftproposal102408.pdf.
41 Personal communication from Douglas Ito, California Air Resources Board, Sacramento, CA, to Michael Rogozen,
UltraSystems Environmental Inc., Irvine, CA. March 29, 2010.
42 The 2019 changes to Building Energy Efficiency Standards became effective January 1, 2020.
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improving “the energy efficiency of newly constructed buildings and additions and alterations to
existing buildings. The most significant efficiency improvements to the residential Standards include
the introduction of photovoltaic into the prescriptive package, improvements for attics, walls, water
heating, and lighting. The most significant efficiency improvements to the nonresidential Standards
include alignment with the ASHRAE 90.1 2017 national standards. The 2019 Standards also include
changes made throughout all of its sections to improve the clarity, consistency, and readability of the
regulatory language.”43
The provisions of Title 24, Part 6 apply to all buildings for which an application for a building permit
or renewal of an existing permit is required by law. They regulate design and construction of the
building envelope, space-conditioning and water-heating systems, indoor and outdoor lighting
systems of buildings, and signs located either indoors or outdoors. Title 24, Part 6 specifies
mandatory, prescriptive and performance measures, all designed to optimize energy use in buildings
and decrease overall consumption of energy to construct and operate residential and nonresidential
buildings. Mandatory measures establish requirements for manufacturing, construction, and
installation of certain systems; equipment and building components that are installed in buildings.
Title 24 California Green Building Standards Code. The California Green Building Standards Code
(Title 24, Part 11 code) commonly referred to as the CALGreen Code, is a statewide mandatory
construction code developed and adopted by the California Building Standards Commission and the
Department of Housing and Community Development. The CALGreen standards require new
residential and commercial buildings to comply with mandatory measures under the topics of
planning and design, energy efficiency, water efficiency/conservation, material conservation and
resource efficiency, and environmental quality. CALGreen also provides voluntary tiers and measures
that local governments may adopt that encourage or require additional measures in the five green
building topics.
The CEC updates Title 24 standards every three years and the most recent 2019 revisions to the
standards became effective July 1, 2020.
Executive Order B‐30‐15 (Interim GHG Emissions Reduction). On April 29, 2015, Governor Brown
signed Executive Order B-30-15, which sets a California GHG reduction target of 40% below 1990
levels by 2030.44 This target is an intermediate goal between the 2020 and 2050 targets set by
Executive Order S-3-05. The executive order also directs state agencies to update the Scoping Plan,
update an Adaptation Strategy every three years, and take climate change into account in their
planning and investment strategies. Additionally, it requires the State’s Five-Year Infrastructure Plan
to take current and future climate change impacts into account in all infrastructure projects.
Advanced Clean Truck Regulation. ARB adopted the Advanced Clean Truck Regulation in June 2020
requiring truck manufacturers to transition from diesel trucks and vans to electric zero emission
trucks beginning in 2024. By 2045, every new truck sold in California is required to be zero emission.
This rule directly addresses disproportionate risks and health and pollution burdens and puts
California on the path for an all zero-emission short haul drayage fleet in ports and railyards by 2035,
and zero emission "last mile" delivery trucks and vans by 2040. The Advanced Clean Truck
43 2019 Building Energy Efficiency Standards for Residential and Nonresidential Buildings for the 2019 Building
Efficiency Standards. California Energy Commission, Publication No. CEC-400-2018-020. URL:
https://www.energy.ca.gov/publications/2008/2019-building-energy-efficiency-standards-residential-and-
nonresidential. Accessed November 15, 2021.
44 New California Goal Aims to Reduce Emissions 40 Percent Below 1990 Levels by 2030. State of California. Office of
Governor. https://www.gov.ca.gov/news.php?id=18938.
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Regulation accelerates the transition of zero emission medium and heavy-duty vehicles from Class
2b to Class 8. The regulation has two components including a manufacturer sales requirement, and a
reporting requirement.
3.2.7.3 Local and Regional Climate Change Plans and Guidelines
The City, through its partnership in the San Bernardino County Regional Greenhouse Gas Reduction
Plan (Regional Plan),45 has identified measures that it could take to reduce GHG emissions from City
operations and from development in its jurisdiction. These measures could form the basis for a
climate action plan (CAP). However, the City has not formally adopted a CAP. In the interim, the City
has incorporated much of the measures from the Regional Plan into its General Plan Update,
primarily in its Sustainability and Resilience Element. Applicable goals and policies are presented in
Section 3.2.6.
The SCAQMD has issued guidelines for evaluating the significance under CEQA of a project’s GHG
emissions. These are discussed in Section 4.1.2.
On April 7, 2016, the SCAG Regional Council adopted the 2016 2040 Regional Transportation Plan/
Sustainable Communities Strategy (RTP/SCS). The RTP/SCS charts a course for closely integrating
land use and transportation so that the region can grow smartly and sustainably. The strategy was
prepared through a collaborative, continuous, and comprehensive process with input from local
governments, county transportation commissions, tribal governments, nonprofit organizations,
businesses, and local stakeholders within the counties of Imperial, Los Angeles, Orange, Riverside,
San Bernardino, and Ventura. The RTP/SCS is a long-range vision plan that balances future mobility
and housing needs with economic, environmental, and public health goals. The SCAG region strives
toward sustainability through integrated land use and transportation planning. The SCAG region
must achieve specific federal air quality standards and is required by state law to lower regional GHG
emissions.
Regional Air Quality
Table 3.3‐1 (Federal and State Attainment Status) shows the area designation status of the SCAB for
each criteria pollutant for both the NAAQS and CAAQS. Based on regional monitoring data, the SCAB
is currently designated as a state non-attainment area for O3, PM10, and PM2.5; a federal
non-attainment area for O3 and PM2.5; a federal maintenance area for CO, NO2, and PM10; and a state
and federal attainment area for SO2.46,47 Designation of the SCAB as a maintenance area means that,
although the Basin has achieved compliance with the NAAQS for CO and NO2, control strategies that
were used to achieve compliance must continue. The Federal ozone classification is “extreme.”48 An
45 San Bernardino County Regional Greenhouse Gas Reduction Plan. Prepared by ICF International and LSA for San
Bernardino Council of Governments. March 2021. URL: https://www.gosbcta.com/wp-
content/uploads/2019/09/San_Bernardino_Regional_GHG_Reduction_Plan_Main_Text_Mar_2021.pdf. Accessed
November 15, 2021.
46 According to the SCAQMD, the “Basin has met the PM10 standards at all stations and a request for re-designation to
attainment is pending with U.S. EPA.” (SCAQMD Board Meeting, December 7, 2012, Agenda Item 30, p. 6.)
47 On July 8, 2016, USEPA made a finding that the South Coast has attained the 1997 24-hour and annual PM2.5 standards
based on 2011-2013 data. https://www.regulations.gov/document?D=EPA-R09-OAR-2014-0708-0081. This
determination became effective August 24, 2016.
48 U.S. Environmental Protection Agency. 2011. “8-Hour Ozone Nonattainment State/Area/County Report.” Green Book.
http://www.epa.gov/air/oaqps/greenbook/gncs.html#CALIFORNIA. Updated December 14, 2012.
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extreme non-attainment area has an 8-hour ozone design value of 0.187 ppm,49 and has the
attainment deadline of June 15, 2024. On June 26, 2013, the USEPA approved, as a revision to the SIP,
the State's request to redesignate the South Coast Air Basin to attainment for the 24-hour PM10
NAAQS. The USEPA is also approving the PM10 maintenance plan and the associated PM10 motor
vehicle emissions budgets for use in transportation conformity determinations necessary for the
South Coast PM10 area. Finally, the USEPA approved the attainment year emissions inventory. The
USEPA took these actions because the SIP revision meets the requirements of the CAA and USEPA
guidance for such plans and motor vehicle emissions budgets.50
Table 3.3‐1
FEDERAL AND STATE ATTAINMENT STATUS
Pollutants Federal Classification State Classification51
Ozone (O3) Nonattainment (Extreme)52 Nonattainment
Particulate Matter (PM10) Maintenance (Serious)53 Nonattainment
Fine Particulate Matter (PM2.5) Nonattainment (Serious)54 Nonattainment
Carbon Monoxide (CO) Maintenance (Serious)55 Attainment
Nitrogen Dioxide (NO2) Maintenance56 Attainment
Sulfur Dioxide (SO2) Attainment57 Attainment
Sulfates
No Federal Standards
Attainment
Lead (Pb) Attainment
Hydrogen Sulfide (H2S) Attainment
Visibility Reducing Particles Unclassified
49 U.S. Environmental Protection Agency. 2011. “Designations.” Green Book.
www.epa.gov/air/oaqps/greenbook/define.html. Updated August 30, 2011.
50 “Approval and Promulgation of Implementation Plans; Designation of Areas for Air Quality Planning Purposes;
California; South Coast Air Basin; Approval of PM10 Maintenance Plan and Redesignation to Attainment for the PM10
Standard.” Federal Register 78 (123): 38223-38226. http://www.gpo.gov/fdsys/pkg/FR-2013-06-26/html/2013-
15145.htm.
51 State Area Designations. California Air Resources Board. https://ww2.arb.ca.gov/resources/documents/maps-state-
and-federal-area-designations. Accessed December 3, 2021.
52 Nonattainment Areas for the 2015 Ozone Standards. U.S. Environmental Protection Agency.
https://epa.maps.arcgis.com/apps/MapSeries/index.html?appid=d37c4a84a023422e8a24272dd8875f56. Accessed
December 3, 2021.
53 PM-10 (1987) Maintenance Area (Redesignated from Nonattainment) State/Area/County Report, November 30, 2021.
https://www3.epa.gov/airquality/greenbook/pmcs.html#CA, Accessed December 3, 2021.
54 PM-2.5 Nonattainment Areas (2012 Standard). U.S. Environmental Protection Agency.
https://www3.epa.gov/airquality/greenbook/map/mappm25_2012.pdf. Accessed December 3, 2021.
55 Carbon Monoxide (1971) Designated Area State/Area/County Report. U.S. Environmental Protection Agency.
November 30, 2021. https://www3.epa.gov/airquality/greenbook/cbcs.html#CA. Accessed December 3, 2021.
56 Nitrogen Dioxide (1971) Maintenance Area (Redesignated from Nonattainment) State/Area/County Report. U.S.
Environmental Protection Agency. U.S. Environmental Protection Agency. November 30, 2021.
https://www3.epa.gov/airquality/greenbook/nmcs.html. Accessed December 3, 2021.
57 Sulfur Dioxide. California Air Resources Board. https://ww2.arb.ca.gov/our-work/programs/state-and-federal-area-
designations/federal-area-designations/sulfur-dioxide. Accessed December 3, 2021.
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Local Air Quality
The SCAQMD has divided the SCAB into source receptor areas (SRAs), based on similar
meteorological and topographical features. The proposed project site is in SCAQMD’s Central
San Bernardino Valley (SRA 34), which is served by the Fontana-Arrow Monitoring Station, located
less than five miles southwest of the proposed project site, at 14360 Arrow Highway, in Fontana.
Criteria pollutants monitored at the Fontana-Arrow Monitoring Station include ozone, PM10, PM2.5,
and NO2. This station ceased monitoring CO in 2012 and CO has not been monitored anywhere in the
SCAB since 2012. The ambient air quality data in the proposed project vicinity as recorded at the
Fontana-Arrow Monitoring Station from 2018 to 2020 and the applicable state standards are shown
in Table 3.4‐1.
Table 3.4‐1
AMBIENT AIR QUALITY MONITORING DATA
Air
Pollutant Standard/Exceedance 2018 2019 2020
Ozone (O3)
Max. 1-hour Concentration (ppm)
Max. 8-hour Concentration (ppm)
# Days > Federal 8-hour Std. of 0.070 ppm
# Days > California 1-hour Std. of 0.070 ppm
# Days > California 8-hour Std. of 0.070 ppm
0.141
0.111
69
38
72
0.124
0.109
67
41
71
0.151
0.111
89
56
91
Nitrogen
Dioxide
(NO2)
Max. 1-hour Concentration (ppm)
Annual Average (ppm)
# Days > California 1-hour Std. of 0.070 ppm
0.063
0.018
0
0.0761
0.017
0
0.0664
0.019
0
Respirable
Particulate
Matter
(PM10)
Max. 24-hour Concentration microgram per cubic meter
(µg/m3)
Est. # Days > Fed. 24-hour Std. of 150 µg/m3
Annual Average (µg/m3)
61.5
0
34.6
85.1
0
35.3
73.6
0
37.2
Fine
Particulate
Matter
(PM2.5)
Max. 24-hour Concentration (µg/m3)
#Days > Fed. 24-hour Std. of 35 µg/m3 State Annual
Average (µg/m3)
29.2
0
11.1
81.3
3
11.3
57.6
4
12.3
Source: California Air Resources Board, “iADAM Air Quality Data Statistics.” Internet URL:
http://www.arb.ca.gov/adam/ (October 2021).
ND - There was insufficient (or no) data available to determine the value.
Sensitive Receptors
Some people, such as individuals with respiratory illnesses or impaired lung function because of
other illnesses, persons over 65 years of age, and children under 14, are particularly sensitive to
certain pollutants. Facilities and structures where these sensitive people live or spend considerable
amounts of time are known as sensitive receptors. Land uses identified to be sensitive receptors by
the SCAQMD CEQA Air Quality Handbook include residences, schools, playgrounds, childcare centers,
athletic facilities, long-term health care facilities, rehabilitation centers, convalescent centers, and
retirement homes. Sensitive receptors may be at risk of being affected by air emissions released from
the construction and operation of the proposed project.
The closest sensitive receptors to the proposed project are residences on the west side of Sierra
Avenue, which are about 162 feet from the project’s western boundary. The nearest school is
Fitzgerald Elementary School, which is about 1.1 miles to the northeast. At this writing, a new
residential development was under construction on Sierra Avenue, across the street from the
proposed project.
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AIR QUALITY IMPACTS ANALYSIS
Impact Review Criteria
Criteria Pollutants
4.1.1.1 CEQA Guidelines
In accordance with State CEQA Guidelines Appendix G, implementation of the project would result in
a potentially significant impact to air quality if it were to:
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 nonattainment under an applicable federal or state 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.
Where available, the significance criteria established by the applicable air quality management
district (AQMD) or air pollution control district (APCD) may be relied upon to make the significance
determinations. As will be discussed in the next section, the SCAQMD has developed a CEQA Air Quality
Handbook to provide a protocol for air quality analyses that are prepared under the requirements of
CEQA.
4.1.1.2 Emission Thresholds for Regional Air Quality Impacts
The SCAQMD has developed criteria for determining whether emissions from a project are regionally
significant. They are useful for estimating whether a project is likely to result in a violation of the
NAAQS and/or whether the project is in conformity with plans to achieve attainment. The SCAQMD
no longer has “indirect source” rules, e.g., rules that place restrictions on housing or commercial
development, or require reductions in trip generation and/or vehicle miles traveled to developed
commercial or industrial sites.58 Instead, the District has published guidance on conducting air
quality analyses under CEQA59 SCAQMD’s significance thresholds are summarized in Table 4.1‐1 for
criteria pollutant emissions during construction activities and project operation. A project is
considered to have a regional air quality impact if emissions from its construction and/or operational
activities exceed the corresponding SCAQMD significance thresholds.
58 Two indirect source rules (1501 - Work Trip Reduction Plans and 1501.1 - Alternatives to Work Trip Reduction
Plans) were repealed in 1995.
59 SCAQMD (South Coast Air Quality Management District), 1993. CEQA Air Quality Handbook. Diamond Bar, CA.
November.
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Table 4.1‐1
SCAQMD EMISSIONS THRESHOLDS FOR SIGNIFICANT REGIONAL IMPACTS
Pollutant
Mass Daily Thresholds (Pounds/Day)
Construction Operation
Nitrogen Oxides (NOX) 100 55
Volatile Organic Compounds (VOC) 75 55
Respirable Particulate Matter (PM10) 150 150
Fine Particulate Matter (PM2.5) 55 55
Sulfur Oxides (SOX) 150 150
Carbon Monoxide (CO) 550 550
Lead 3 3
Source: “SCAQMD Air Quality Significance Thresholds.” 2019. Diamond Bar, CA: South Coast Air Quality Management
District, http://www.aqmd.gov/docs/default-source/ceqa/handbook/scaqmd-air-quality-significance-
thresholds.pdf?sfvrsn=2. April 2019. Accessed December 3, 2019.
4.1.1.3 Emission Thresholds for Localized Air Quality Impacts
As part of its environmental justice program to address localized air quality impacts of development
projects, SCAQMD developed localized significance thresholds (LSTs) in 2003.60 LSTs represent the
maximum NOx, CO, PM10, and PM2.5 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
standard. NOx and CO LSTs are based on the ambient concentrations of that pollutant for each SRA61
and distance to the nearest offsite receptor. For PM10, LSTs were derived based on requirements in
SCAQMD Rule 403. Note that the LST analysis does not apply to ROG emissions, since there is no
ambient air quality standard for ROG.
For the purposes of a CEQA analysis, the SCAQMD considers a sensitive receptor to be a receptor such
as a residence, hospital, or convalescent facility where it is possible that an individual could remain
for 24 hours. Commercial and industrial facilities are not included in the definition of sensitive
receptor, because employees typically are present for shorter periods of time, such as eight hours.
Therefore, applying a 24-hour standard for PM10 is appropriate not only because the averaging
period for the state standard is 24 hours, but because the sensitive receptor would be present at the
location for the full 24 hours.
The SCAQMD has developed mass rate look-up tables that can be used to determine whether a project
may generate significant localized air quality impacts to offsite receptors (including sensitive
receptors). Note that the use of LSTs is voluntary, to be implemented at the discretion of the lead
agency pursuant to CEQA.
60 Chico, T. and J. Koizumi. Final Localized Significance Threshold Methodology: South Coast Air Quality Management
District, Diamond Bar, CA. July 2008. URL: http://www.aqmd.gov/docs/default-source/ceqa/handbook/localized-
significance-thresholds/final-lst-methodology-document.pdf?sfvrsn=2.
61 The SCAQMD has defined 38 source receptor areas (SRA) for various regulatory purposes. Each SRA is assumed to
have a unique set of geographic and meteorological characteristics.
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4.1.1.4 Impacts of Carbon Monoxide Hotspots
Increased local vehicle traffic may contribute to offsite air quality impacts. The traffic increases in
nearby intersections may contribute to traffic congestion, which may create “pockets” of CO called
hotspots. These pockets have the potential to exceed the state 1-hour standard of 20 parts per million
(ppm) and/or the 8-hour standard of 9.0 ppm, thus affecting sensitive receptors that are close to
these roadways or intersections. CO hotspots historically were found at busy intersections but could
also occur along congested major arterials and freeways. They occurred mostly in the early morning
hours when winds are stagnant and ambient CO concentrations are elevated.
It has long been recognized that CO exceedances are caused by vehicular emissions,62 primarily when
vehicles are idling at intersections.63,64 Accordingly, vehicle emissions standards have become
increasingly more stringent. Before the first vehicle emission regulations, cars in the 1950s were
typically emitting about 87 grams of CO per mile.65 Currently, the CO standard in California is a
maximum of 3.4 grams/mile for passenger cars (with provisions for certain cars to emit even less).66
With the turnover of older vehicles, introduction of cleaner fuels and implementation of control
technology on industrial facilities, CO concentrations in the Air Basin have steadily declined.
An analysis prepared for CO attainment in the SCAB by the SCAQMD can be used to assist in
evaluating the potential for CO exceedances due to development projects. CO attainment was
thoroughly analyzed as part of the SCAQMD’s 2003 Air Quality Management Plan (2003 AQMP) and
the 1992 Federal Attainment Plan for Carbon Monoxide (1992 CO Plan).67 In the 1992 CO Plan, a CO
hot spot analysis was conducted for the four worst-case scenario intersections in Los Angeles County
at the peak morning and afternoon time periods. The intersections evaluated included Long Beach
Boulevard and Imperial Highway (Lynwood); Wilshire Boulevard and Veteran Avenue (Westwood);
Sunset Boulevard and Highland Avenue (Hollywood); and La Cienega Boulevard and Century
Boulevard (Inglewood). These analyses did not predict a violation of CO standards. The peak modeled
CO concentrations due to vehicle emissions occurred at the intersection of Wilshire Boulevard and
Veteran Avenue, which had a daily traffic volume of approximately 100,000 vehicles. The 2003 AQMP
estimated that the 1-hour concentration for this intersection was 4.6 ppm, which indicates that the
most stringent 1-hour CO standard (20.0 ppm) would likely not be exceeded until the daily traffic at
the intersection exceeded more than 400,000 vehicles per day.68 The AQMP CO hotspots modeling
also took into account worst-case meteorological conditions and background CO concentrations. The
Los Angeles County Metropolitan Transportation Authority (Metro) evaluated the level of service
(LOS) in the vicinity of the Wilshire Boulevard and Veteran Avenue intersection and found it to be
Level E for peak morning traffic and Level F for peak afternoon traffic.69,70 If a project intersection
62 USEPA. 2000. Air Quality Criteria for Carbon Monoxide. EPA 600/P-099/001F.
63 SCAQMD. 1993. CEQA Air Quality Handbook. Section 4.5.
64 SCAQMD. 2003. Air Quality Management Plan.
65 USEPA, Timeline of Major Accomplishments in Transportation, Air Pollution, and Climate Change, www.epa.gov/air-
pollution-transportation/timeline-major-accomplishments-transportation-air-pollution-and-climate, accessed January 17,
2018.
66 California Air Resources Board. California 2015 and Subsequent Model Criteria Pollutant Exhaust Emission
Standards and Test Procedures and 2017 and Subsequent Model Greenhouse Gas Exhaust Emission Standards and
Test Procedures for Passenger Cars, Light-Duty Trucks, and Medium-Duty Vehicles. Adopted March 22, 2012.
67 SCAQMD, 1992. Federal Attainment Plan for Carbon Monoxide.
68 Based on the ratio of the CO standard (20.0 ppm) and the modeled value (4.6 ppm).
69 The Metropolitan Transportation Authority measured traffic volumes and calculated the LOS for the intersection of
Wilshire Blvd./ Sepulveda Ave. which is a block west along Wilshire Blvd., still east of Interstate 405.
70 Metropolitan Transportation Authority. 2004. Congestion Management Program for Los Angeles County. Exhibit 2-6
and Appendix A.
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does not exceed 400,000 vehicles per day, then the project does not need to prepare a detailed CO
hotspots analysis using California LINE Source Dispersion Model, version 4 (CALINE4), which is a
model used to assess air quality impacts near transportation facilities (i.e., roadways, intersections,
street canyons, and parking facilities).
4.1.1.5 Odor Impacts
The SCAQMD air quality significance thresholds discussed in Section 4.1.1 define a significant impact
for a situation in which a project creates an odor nuisance pursuant to SCAQMD Rule 402 [Nuisance].
Rule 402 broadly defines nuisance odors; in reality, it is imposed only in cases in which
(1) complaints are received by the District, and (2) an inspector personally observes the offensive
odor. Because the proposed facility is in a highly industrialized area, and unusually odorous materials
will not be handled, Rule 402 complaints are unlikely.
Greenhouse Gas Emissions
4.1.2.1 CEQA Impact Review Criteria
In accordance with State CEQA Guidelines Appendix G, implementation of the project would result in
a potentially significant impact to greenhouse gases if it were to:
Generate greenhouse gas emissions, either directly or indirectly, that may have a significant
impact on the environment;
Conflict with an applicable plan, policy or regulation adopted for the purpose of reducing the
emissions of greenhouse gases.
4.1.2.2 GHG Emissions Thresholds
Neither the City, the SCAQMD nor the State CEQA Guidelines Amendments has adopted specific
quantitative thresholds of significance for addressing a project’s GHG emissions. Nonetheless,
§ 15064.4 of the CEQA Guidelines serves to assist lead agencies in determining the significance of the
impacts of GHGs. As required in § 15064.4, this analysis includes an impact determination based on
(1) an estimate of the amount of GHG emissions resulting from the project; (2) a qualitative analysis
or performance based standards; (3) a quantification of the extent to which the project increases GHG
emissions as compared to the existing environmental setting; and (4) the extent to which the project
complies with regulations or requirements adopted to implement a statewide, regional, or local plan
for the reduction or mitigation of GHG emissions.
To provide guidance to local lead agencies on determining significance for GHG emissions in their
CEQA documents, the SCAQMD Board adopted an Interim CEQA GHG Significance Threshold for
Stationary Sources, Rules, and Plans,71 The Interim Guidance uses a tiered approach to determining
significance. Although this Interim Guidance was developed primarily to apply to stationary
source/industrial projects where the SCAQMD is the lead agency under CEQA, in absence of more
71 SCAQMD, 2008. Draft Guidance Document – Interim CEQA Greenhouse Gas (GHG) Significance Threshold. South Coast
Air Quality Management District. October 2008. http://www.aqmd.gov/docs/default-
source/ceqa/handbook/greenhouse-gases-(ghg)-ceqa-significance-thresholds/ghgattachmente.pdf.
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directly applicable policy, the SCAQMD’s Interim Guidance is often used as general guidance by local
agencies to address the long-term adverse impacts associated with global climate change.
The threshold selected for this analysis is Tier 3 – 90 Percent Capture Rate Emission Thresholds.
A 90% emission capture rate means that 90% of total emissions from all new or modified projects
would be subject to CEQA analysis. For Tier 3, the SCAQMD presents lead agencies with two options:
Option #1 – separate numerical thresholds for residential projects (3,500 metric tons [MT] CO2e per
year), commercial projects (1,400 MTCO2e per year), and mixed-use projects (3,000 MTCO2e per
year); and Option #2 – a single numerical threshold for all non-industrial projects of 3,000 MT CO2e
per year.72 The SCAQMD staff’s proposal was to recommend the use of option #2, but to allow lead
agencies to choose Option #1 if they prefer that approach.
The present analysis uses 3,000 MT of CO2e per year (option #2) as the significance threshold under
the first impact criterion above, as recommended by the City of Fontana for this project.73
Methodology For Analyzing Criteria Pollutant Emissions
Construction
Project construction activities will generate short-term air quality impacts. Construction emissions
can be distinguished as either onsite or offsite. Onsite air pollutant emissions would principally
consist of exhaust emissions from off-road heavy-duty construction equipment, as well as fugitive
particulate matter from earthworking, and material handling operations. Offsite emissions would
result from workers commuting to and from the job site, as well as from trucks hauling demolition
and construction debris for disposal.
Estimated criteria pollutant emissions from the project’s onsite and offsite project activities were
calculated using the California Emissions Estimator Model (CalEEMod), Version 2020.4.0.
CalEEMod74 is a planning tool for estimating emissions related to land use projects. Model-predicted
project emissions are compared with applicable thresholds to assess regional air quality impacts. As
some construction plans have not been finalized, CalEEMod defaults were used for construction
offroad equipment and onroad construction trips and vehicle miles traveled. The only modifications
to CalEEMod defaults are the construction schedule provided by client and operational fleet mix and
trip rates adjustments based on information from SCAQMD’s Analysis of Warehouse Trip Generation
Rates.75 It was also assumed that the construction contractor would comply with all pertinent
provisions of SCAQMD Rule 403.76
72 SCAQMD, 2010. Minutes for the GHG CEQA Significance Threshold Stakeholder Working Group #15. September 28,
2010. South Coast Air Quality Management Board. September 28, 2010. http://www.aqmd.gov/docs/default-
source/ceqa/handbook/greenhouse-gases-(ghg)-ceqa-significance-thresholds/year-2008-2009/ghg-meeting-
15/ghg-meeting-15-minutes.pdf)
73 Email from Cecily Session-Goins, Associate Planner, City of Fontana, to Hina Gupta, Project Manager, UltraSystems
Environmental Incorporated. April 5, 2022.
74 California Emissions Estimator Model® User’s Guide. Version 2020.4.0. Prepared by BREEZE Software for the California
Air Pollution Control Officers Association. November. URL: http://www.aqmd.gov/docs/default-
source/caleemod/user-guide-2021/01_user-39-s-guide2020-4-0.pdf?sfvrsn=6.
75 California Emissions Estimator Model® User’s Guide. Version 2013.2. Appendix E. California Air Pollution Control
Officers Association. July 2013. URL: http://www.aqmd.gov/docs/default-source/caleemod/caleemod-
appendixe.pdf?sfvrsn=6.
76 Rule 403 applies to fugitive dust emissions. All projects in the SCAQMD are required to implement dust control
measures such as regularly wetting disturbed soils.
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Air Quality and Greenhouse Gas Emissions Report April 2022
CalEEMod uses many default assumptions based upon surveys of various types of construction
projects. However, the user may override the default values where project-specific data are available.
Various construction and demolition quantity assumptions were presented in Section 2.2.
Table 4.2‐1 lists the construction equipment types and characteristics used in the modelling.
Table 4.2‐1
CONSTRUCTION EQUIPMENT ASSUMPTIONS
Construction
Phase Equipment Type No. of
Pieces HP Load Factor
Site Preparation Graders 1 187 0.41
Scrapers 1 367 0.48
Tractors/Loaders/Backhoes 1 97 0.37
Grading Graders 1 187 0.41
Rubber-Tired Dozers 1 247 0.40
Tractors/Loaders/Backhoes 2 97 0.37
Building Construction Cranes 1 231 0.29
Forklifts 2 89 0.20
Generator Sets 1 84 0.74
Tractors/Loaders/Backhoes 1 97 0.37
Welders 3 46 0.45
Paving Cement and Mortar Mixers 1 9 0.56
Pavers 1 130 0.42
Paving Equipment 1 132 0.36
Rollers 2 80 0.38
Tractors/Loaders/Backhoes 1 97 0.37
Architectural Coating Air Compressors 1 78 0.48
Operations
Operational emissions were calculated with CalEEMod. The model’s default values were used for
most parameters. However, trip generation rates and vehicle mix data were obtained from SCAQMD
Warehouse Truck Study as presented in Appendix E of the 2013.3.2 CalEEMod User’s Guide.77
Air Quality Impacts (Criteria Pollutants and Air Toxics)
Construction Impacts
4.3.1.1 Regional Impacts
Table 4.3‐1 (Maximum Daily Unmitigated Regional Construction Emissions) summarizes the results
of the CalEEMod analysis. CalEEMod inputs and results are provided in Attachment 1.
77 California Emissions Estimator Model® User’s Guide. Version 2013.2. Appendix E. California Air Pollution Control
Officers Association. July 2013. URL: http://www.aqmd.gov/docs/default-source/caleemod/caleemod-
appendixe.pdf?sfvrsn=6.
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Table 4.3‐1
MAXIMUM DAILY UNMITIGATED REGIONAL CONSTRUCTION EMISSIONS
Construction Activity
Maximum Emissions (lbs/day)
ROG NOx CO PM10 PM2.5
Maximum Emissions, 2020 47.7 17.0 16.4 8.0 4.2
SCAQMD Significance Thresholds 75 100 550 150 55
Significant? (Yes or No) No No No No No
Source: Calculated by OB-1 Air Analyses with CalEEMod (Version 2020.0.4).
For each criteria pollutant, construction emissions would be below the pollutant’s SCAQMD
significance threshold.
4.3.1.2 Impacts on Sensitive Receptors
Sensitive receptors are persons who are more susceptible to air pollution than the general
population, such as children, athletes, the elderly, and the chronically ill. Examples of land uses where
substantial numbers of sensitive receptors are often found are schools, daycare centers, parks,
recreational areas, medical facilities, nursing homes, and convalescent care facilities. Residential
areas are also considered to be sensitive to air pollution because residents (including children and
the elderly) tend to be at home for extended periods of time, resulting in sustained exposure to
pollutants.
Construction of the proposed project would generate short-term and intermittent emissions.
Following SCAQMD guidance,78 only onsite construction emissions were considered in the localized
significance analysis. Localized significance thresholds for projects in Source Receptor Area 34 were
obtained from tables in Appendix C of the SCAQMD’s Final Localized Significance Threshold
Methodology.79 Table 4.3‐2 shows the results of the localized significance analysis for the proposed
project.
78 Chico, T. and J. Koizumi. Final Localized Significance Threshold Methodology: South Coast Air Quality Management
District, Diamond Bar, CA. July 2008. URL: http://www.aqmd.gov/docs/default-source/ceqa/handbook/localized-
significance-thresholds/final-lst-methodology-document.pdf?sfvrsn=2.
79 Ibid.
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Table 4.3‐2
RESULTS OF LOCALIZED SIGNIFICANCE ANALYSIS
Nearest Sensitive Receptor
Maximum Onsite Emissions
(pounds/day)
NOx CO PM10 PM2.5
Maximum daily emissions 17.0 14.4 7.8 4.1
SCAQMD LST for 5 acres @ 50 meters 302 2,396 42 10
Significant (Yes or No) No No No No
During project construction, sensitive receptors would be exposed to diesel exhaust from
construction equipment, which has been associated with lung cancer.80 Therefore a screening health
risk assessment was performed for construction activities. A memorandum describing and
documenting the screening HRA was prepared for the Initial Study/Mitigated Negative Declaration
for this project.81 The resulting carcinogenic risk was estimated to be 0.39 in 1 million (3.9 x 10-7),
which is less than the SCAQMD’s significance threshold of 10 in 1 million. The chronic hazard index
was estimated to be 0.0003, which is less than the significance threshold of 1.0. Therefore, the long-
term cancer risk and chronic noncancer risk for the proposed project’s construction would be less
than significant.
Acute non-cancer risk assessments are based upon one-hour maximum exposures, but acute
reference exposure levels (RELs) for diesel exhaust and diesel particulate matter have not been
established by the Office of Environmental Health Hazard Assessment.82
Long‐Term Impacts
4.3.2.1 Regional Impacts
Operational emissions from the proposed project were estimated using the methods outlined in
Section 4.2.2. Results are presented in Table 4.3‐3 (Maximum Daily Project Operational Emissions).
As seen in Table 4.3‐3, for each criteria pollutant, operational emissions would be below the
pollutant’s SCAQMD significance threshold. Therefore, operational criteria pollutant emissions
would be less than significant.
80 Findings of the Scientific Review Panel on The Report on Diesel Exhaust as Adopted at the Panel’s April 22, 1998
Meeting. URL: URL: https://ww2.arb.ca.gov/sites/default/files/classic/toxics/dieseltac/de-fnds.pdf. Accessed on
November 15, 2021.
81 Screening Air Toxics Health Risk Assessment for the Summit Avenue Warehouse Project, Fontana, California.
Memorandum From Michael Rogozen, UltraSystems Environmental Incorporated, to Bobby Allard, Allard Engineering.
April 15, 2022.
82 http://www.oehha.ca.gov/air/allrels.html. Accessed June 28, 2014.
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Table 4.3‐3
MAXIMUM DAILY PROJECT OPERATIONAL EMISSIONS
Emission Source
Pollutant (lbs/day)
ROG NOX CO PM10 PM2.5
Area Source Emissions 2.29 0.00 0.01 0.00 0.00
Energy Source Emissions 0.01 0.06 0.05 0.00 0.00
Mobile Source Emissions 0.30 1.04 4.12 1.26 0.35
Total Operational Emissions 2.6 1.1 4.2 1.3 0.4
SCAQMD Significance Thresholds 55 55 550 150 55
Significant? (Yes or No) No No No No No
Source: Calculated by OB-1 Air Analyses with CalEEMod (Version 2020.4.0).
4.3.2.2 Carbon Monoxide Hotspots
Considering the discussion in Section 4.1.3, analysis, a CO hotspots analysis was not needed and was
not performed.
4.3.2.3 Odor Analysis
The aforementioned SCAQMD Air Quality Significance Thresholds define a significant impact for a
situation in which a project creates an odor nuisance pursuant to SCAQMD Rule 402 [Nuisance]. Rule
402 broadly defines nuisance odors; in reality, it is imposed only in cases in which (1) complaints are
received by the District and (2) an inspector personally observes the offensive odor. Because the
proposed facility is in a highly industrialized area, and unusually odorous materials will not be
handled, Rule 402 complaints are unlikely.
4.3.2.4 Screening Health Risk Assessment
The aforementioned health risk assessment memorandum prepared for the Initial Study/Mitigated
Negative Declaration for this project also covered long-term exposures during project operation. The
resulting carcinogenic risk was estimated to be 6.9 in 1 million (6.9 x 10-6), which is less than the
SCAQMD’s significance threshold of 10 in 1 million. The estimated hazard index for chronic
noncancer risk is estimated to be 0.0046, which is less than the significance threshold of 1.0. Given
that the screening approach assumed worst-case meteorological conditions, use of actual local
meteorological inputs would result in considerably lower risk estimates. Therefore, impacts from
exposure to diesel particulate matter would be less than significant.
Consistency With Air Quality Management Plan
As discussed in Section 3.2.3, The SCAQMD has established an AQMP that proposes policies and
measures to achieve federal and State standards for healthful air quality in the SCAB. The most
recently approved AQMP was adopted by the SCAQMD Board of Directors on March 3, 2017.
The AQMP incorporates land use assumptions from local general plans and regional growth
projections developed by the SCAG to estimate stationary and mobile air emissions associated with
projected population and planned land uses. If the proposed land use is consistent with the local
AIR QUALITY IMPACTS ANALYSIS
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Air Quality and Greenhouse Gas Emissions Report April 2022
general plan, then the impact of the project is presumed to have been accounted for in the AQMP.
This is because the land use and transportation control sections of the AQMP are based on the SCAG
regional growth forecasts, which incorporated projections from local general plans. As is concluded
in the IS/MND prepared for this project, the proposed project meets the main objectives of the land
use plans and ordinances governing the project site and appropriately balances the requirements of
the zoning code with and associated development limitations of the project site.
Another measurement tool in determining consistency with the AQMP is to determine whether a
project would generate population and employment growth and, if so, whether that growth would
exceed the growth rates forecasted in the AQMP and how the project would accommodate the
expected increase in population or employment. The project does not propose any residential or
commercial development and would not directly induce substantial growth in Fontana. The project
would not indirectly induce growth since no new public infrastructure is proposed or would be
required. Therefore, the project would not directly or indirectly induce growth in Fontana and would
not violate the assumptions of the AQMP.
Methodology for Analyzing Greenhouse Gas Emissions
GHG emissions come from both the construction and operation of the project. Construction of the
project would result in temporary emissions of GHGs from fuel combustion by onsite construction
equipment and by on-road vehicle traffic (i.e., worker commute and delivery truck trips). Operational
direct GHG emissions will come from on-road mobile sources and onsite area sources, such as
landscaping. Indirect GHG emissions will come from energy use, water supply, wastewater, and solid
waste.83 A detailed summary of the assumptions and model data used to estimate the project’s GHG
emissions are provided in Attachment 1.
One-time GHG emissions are those construction emissions that do not recur over the life of the
project. The major construction phases included in this analysis are grading, building construction,
paving, and architectural coating. Emissions are from offroad construction equipment and onroad
vehicles like worker and vendor commuting and trucks for soil and material hauling.
Other GHG emissions would occur annually after buildout. GHGs are emitted from buildings because
of activities for which electricity and natural gas are typically used as energy sources. Combustion of
carbon-based fuel emits CO2 and other GHGs directly into the atmosphere; these emissions are
considered direct emissions. The project’s primary direct source of annual GHG emissions will be
on-road mobile sources. GHGs are also emitted during the generation of electricity from fossil fuels;
when produced offsite, these emissions are indirectly associated with the project. Indirect GHG
emissions also result from the production of electricity used to convey, treat, and distribute water
and wastewater. A final indirect GHG emission source is decomposition of organic waste that is
generated by the project and transported to landfills.
Temporary construction and long-term operational GHG emissions from the project’s onsite and
offsite project activities were calculated using CalEEMod Version 2020.4.0 (CAPCOA, 2021).
CalEEMod is a planning tool for estimating emissions related to land use projects. Operational
emissions consider area emissions, such as space heating, from energy use associated with land uses,
and from the vehicle trips associated with the land uses. To assess the overall lifetime project GHG
83 Indirect emission sources are those for which the project is responsible, but which are not located at the project site.
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emissions, the SCAQMD developed an Interim Guidance84 that recommends that construction
emissions should be amortized over the life of the project, defined in the guidance as 30 years.
Annualized GHG emissions are then added to the operational emissions and the sum is compared to
the applicable interim GHG significance threshold.
Air Quality Impacts (Greenhouse Gas Emissions)
Each construction phase involves the use of a different mix of construction equipment and therefore
has its own distinct GHG emissions characteristics. A generalized construction schedule was supplied
by the applicant. CalEEMod defaults were used otherwise. Construction emissions occur both onsite
and offsite. Onsite air pollutant emissions consist principally of exhaust emissions from off-road
heavy-duty construction equipment. Offsite emissions result from workers commuting to and from
the job site, as well as from vendors and visitors to the site.
To be consistent with the guidance from the SCAQMD for calculating criteria pollutants from
construction activities, only GHG emissions from onsite construction activities and offsite hauling and
construction worker commuting are considered as project generated. As explained by California Air
Pollution Control Officers Association (CAPCOA) in its 2008 white paper,85 the information needed
to characterize GHG emissions from manufacture, transport, and end-of-life of construction materials
would be speculative at the CEQA analysis level. CEQA does not require an evaluation of speculative
impacts (CEQA Guidelines § 15145). Therefore, the construction analysis does not consider such GHG
emissions, but does consider non-speculative onsite construction activities, and offsite hauling and
construction worker trips. All GHG emissions are identified on an annual basis.
CalEEMod estimated construction GHG emissions to be 214.7 MT of CO2e. The 30-year amortized
value is 7.16 MT of CO2e per year. Table 4.5‐1 summarizes the results of the GHG emissions analysis
for both construction and operations.
Table 4.5‐1
UNMITIGATED ANNUAL GHG EMISSIONS, 2019 AND BEYOND
(Emissions in metric tons, or MT)
Category CO2e
(MT/year)
Direct – (Amortized Construction) 7.16
Direct – Mobile (Operational) 228.39
Direct – Purchased Natural Gas 11.05
Direct – Area Source <0.01
Indirect – Purchased Electricity (Power) 57.53
Indirect – Purchased Electricity (Water) 106.90
84 SCAQMD, 2008. Draft Guidance Document – Interim CEQA Greenhouse Gas (GHG) Significance Threshold. South Coast
Air Quality Management District. October 2008. http://www.aqmd.gov/docs/default-
source/ceqa/handbook/greenhouse-gases-(ghg)-ceqa-significance-thresholds/ghgattachmente.pdf.
85 CEQA & Climate Change. Evaluating and Addressing Greenhouse Gas Emissions from Projects Subject to the
California Environmental Quality Act. January. URL: http://www.capcoa.org/wp-
content/uploads/2012/03/CAPCOA-White-Paper.pdf.
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Air Quality and Greenhouse Gas Emissions Report April 2022
Category CO2e
(MT/year)
Direct – Fugitive – Solid Waste 48.40
TOTAL 459
Total unmitigated operational CO2e emissions from the project would be 452 MT of CO2e per year.
Mobile sources account for about 50.5% of these emissions.
With the addition of the amortized construction emissions, the total project GHG emissions would be
459 MT of CO2e per year, which is less than the significance threshold of 3,000 MT of CO2e per year.
Therefore, GHG emissions would be less than significant, and no mitigation is necessary.
EMISSION REDUCTION MEASURES
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Air Quality and Greenhouse Gas Emissions Report April 2022
EMISSION REDUCTION MEASURES
As discussed in Section 4.3 and Section 4.5, both the short-term and long-term criteria pollutant
and greenhouse gas emissions impacts of the project will be less than significant. Air quality- and
GHG-specific mitigation measures will not be necessary.
IMPACTS AFTER MITIGATION
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Air Quality and Greenhouse Gas Emissions Report April 2022
IMPACTS AFTER MITIGATION
As discussed in Section 4.3 and Section 4.5, both the short-term and long-term criteria pollutant
and greenhouse gas emissions impacts of the project will be less than significant. Air quality- and
GHG-specific mitigation measures will not be necessary.
ATTACHMENTS
7102/Summit Avenue Warehouse Project
Air Quality and Greenhouse Gas Emissions Report April 2022
ATTACHMENTS
ATTACHMENTS
7102/Summit Avenue Warehouse Project
Air Quality and Greenhouse Gas Emissions Report April 2022
ATTACHMENT 1
CALEEMOD OUTPUT
Summit Avenue Warehouse
San Bernardino-South Coast County, Summer
Project Characteristics - CalEEMod defaults
Land Use - Lot is 4.49 acres
Construction Phase - Construction schedule provided by the client
Architectural Coating - Per SCAQMD Rule 1113
Vehicle Trips - Recommended average trip rates as proposed in the SCAQMD Warehouse Truck Study for non-cold storage
Road Dust -
Consumer Products -
Area Coating - Per SCAQMD Rule 1113
Fleet Mix - Adjusted to reflect CalEEMod Ver 2013.2 Appendix E Analysis of Warehouse Trip Generation Rates by SCAQMD
Grading -
Off-road Equipment - Per client
Off-road Equipment - Per client
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population
Unrefrigerated Warehouse-No Rail 102.38 1000sqft 4.49 102,380.00 0
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
10
Wind Speed (m/s)Precipitation Freq (Days)2.2 32
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Southern California Edison
2024Operational Year
CO2 Intensity
(lb/MWhr)
531.98 0.033CH4 Intensity
(lb/MWhr)
0.004N2O Intensity
(lb/MWhr)
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 1 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
Off-road Equipment - Per client
Off-road Equipment - Per client
Off-road Equipment -
Table Name Column Name Default Value New Value
tblArchitecturalCoating EF_Nonresidential_Exterior 100.00 50.00
tblArchitecturalCoating EF_Nonresidential_Interior 100.00 50.00
tblConstructionPhase NumDays 5.00 3.00
tblConstructionPhase NumDays 8.00 6.00
tblConstructionPhase NumDays 230.00 140.00
tblConstructionPhase NumDays 18.00 10.00
tblConstructionPhase NumDays 18.00 10.00
tblFleetMix HHD 0.02 0.06
tblFleetMix LDA 0.54 0.55
tblFleetMix LDT1 0.06 0.04
tblFleetMix LDT2 0.17 0.18
tblFleetMix LHD1 0.03 0.02
tblFleetMix LHD2 7.1040e-003 5.1010e-003
tblFleetMix MCY 0.03 5.9030e-003
tblFleetMix MDV 0.14 0.12
tblFleetMix MH 4.8300e-003 9.4400e-004
tblFleetMix MHD 0.01 0.02
tblFleetMix OBUS 5.5400e-004 1.3570e-003
tblFleetMix SBUS 9.5400e-004 8.0800e-004
tblFleetMix UBUS 2.5100e-004 1.5650e-003
tblLandUse LotAcreage 2.35 4.49
tblOffRoadEquipment OffRoadEquipmentUnitAmount 2.00 1.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 2.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 2.00 1.00
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Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.0 Emissions Summary
tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 1.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 2.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 4.00 1.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 3.00
tblOffRoadEquipment UsageHours 6.00 8.00
tblOffRoadEquipment UsageHours 7.00 8.00
tblOffRoadEquipment UsageHours 8.00 7.00
tblOffRoadEquipment UsageHours 6.00 8.00
tblOffRoadEquipment UsageHours 6.00 8.00
tblOffRoadEquipment UsageHours 7.00 6.00
tblOffRoadEquipment UsageHours 8.00 7.00
tblOffRoadEquipment UsageHours 8.00 7.00
tblProjectCharacteristics CO2IntensityFactor 390.98 531.98
tblTripsAndVMT WorkerTripNumber 8.00 18.00
tblTripsAndVMT WorkerTripNumber 10.00 15.00
tblTripsAndVMT WorkerTripNumber 15.00 20.00
tblVehicleTrips ST_TR 1.74 1.34
tblVehicleTrips SU_TR 1.74 1.34
tblVehicleTrips WD_TR 1.74 1.34
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EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.1 Overall Construction (Maximum Daily Emission)
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2022 2.0672 17.0238 16.3954 0.0326 7.2503 0.7432 7.9934 3.4692 0.6839 4.1529 0.0000 3,077.810
0
3,077.810
0
0.7731 0.0616 3,107.720
6
2023 47.6800 14.3216 16.0819 0.0324 0.5896 0.6205 1.2100 0.1588 0.5945 0.7533 0.0000 3,049.659
1
3,049.659
1
0.5468 0.0585 3,078.395
2
Maximum 47.6800 17.0238 16.3954 0.0326 7.2503 0.7432 7.9934 3.4692 0.6839 4.1529 0.0000 3,077.810
0
3,077.810
0
0.7731 0.0616 3,107.720
6
Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2022 2.0672 17.0238 16.3954 0.0326 7.2503 0.7432 7.9934 3.4692 0.6839 4.1529 0.0000 3,077.810
0
3,077.810
0
0.7731 0.0616 3,107.720
6
2023 47.6800 14.3216 16.0819 0.0324 0.5896 0.6205 1.2100 0.1588 0.5945 0.7533 0.0000 3,049.659
1
3,049.659
1
0.5468 0.0585 3,078.395
2
Maximum 47.6800 17.0238 16.3954 0.0326 7.2503 0.7432 7.9934 3.4692 0.6839 4.1529 0.0000 3,077.810
0
3,077.810
0
0.7731 0.0616 3,107.720
6
Mitigated Construction
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 4 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 5 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Energy 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Mobile 0.2987 1.0407 4.1219 0.0138 1.2513 0.0124 1.2636 0.3344 0.0116 0.3461 1,427.695
0
1,427.695
0
0.0665 0.0887 1,455.791
9
Total 2.5929 1.0960 4.1788 0.0141 1.2513 0.0166 1.2679 0.3344 0.0159 0.3503 1,494.045
8
1,494.045
8
0.0678 0.0899 1,522.538
3
Unmitigated Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Energy 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Mobile 0.2987 1.0407 4.1219 0.0138 1.2513 0.0124 1.2636 0.3344 0.0116 0.3461 1,427.695
0
1,427.695
0
0.0665 0.0887 1,455.791
9
Total 2.5929 1.0960 4.1788 0.0141 1.2513 0.0166 1.2679 0.3344 0.0159 0.3503 1,494.045
8
1,494.045
8
0.0678 0.0899 1,522.538
3
Mitigated Operational
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 6 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Site Preparation Site Preparation 7/1/2022 7/5/2022 5 3
2 Grading Grading 7/6/2022 7/13/2022 5 6
3 Construction Building Construction 7/14/2022 1/25/2023 5 140
4 Paving Paving 1/26/2023 2/8/2023 5 10
5 Painting Architectural Coating 2/9/2023 2/22/2023 5 10
OffRoad Equipment
Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor
Site Preparation Graders 1 8.00 187 0.41
Site Preparation Scrapers 1 8.00 367 0.48
Site Preparation Tractors/Loaders/Backhoes 1 7.00 97 0.37
Grading Graders 1 8.00 187 0.41
Grading Rubber Tired Dozers 1 8.00 247 0.40
Grading Tractors/Loaders/Backhoes 2 7.00 97 0.37
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Residential Indoor: 0; Residential Outdoor: 0; Non-Residential Indoor: 153,570; Non-Residential Outdoor: 51,190; Striped Parking Area: 0
(Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 4.5
Acres of Grading (Grading Phase): 6
Acres of Paving: 0
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 7 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.1 Mitigation Measures Construction
Construction Cranes 1 8.00 231 0.29
Construction Forklifts 2 7.00 89 0.20
Construction Generator Sets 1 8.00 84 0.74
Construction Tractors/Loaders/Backhoes 1 6.00 97 0.37
Construction Welders 3 8.00 46 0.45
Paving Cement and Mortar Mixers 1 8.00 9 0.56
Paving Pavers 1 8.00 130 0.42
Paving Paving Equipment 1 8.00 132 0.36
Paving Rollers 2 8.00 80 0.38
Paving Tractors/Loaders/Backhoes 1 8.00 97 0.37
Painting Air Compressors 1 6.00 78 0.48
Trips and VMT
Phase Name Offroad Equipment
Count
Worker Trip
Number
Vendor Trip
Number
Hauling Trip
Number
Worker Trip
Length
Vendor Trip
Length
Hauling Trip
Length
Worker Vehicle
Class
Vendor
Vehicle Class
Hauling
Vehicle Class
Site Preparation 3 18.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Grading 4 15.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Construction 8 43.00 17.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Paving 6 20.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Painting 1 9.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 8 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 1.5908 0.0000 1.5908 0.1718 0.0000 0.1718 0.0000 0.0000
Off-Road 1.3784 15.6673 10.0558 0.0245 0.5952 0.5952 0.5476 0.5476 2,375.156
9
2,375.156
9
0.7682 2,394.361
3
Total 1.3784 15.6673 10.0558 0.0245 1.5908 0.5952 2.1859 0.1718 0.5476 0.7193 2,375.156
9
2,375.156
9
0.7682 2,394.361
3
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0762 0.0483 0.7405 1.8600e-
003
0.2012 1.0500e-
003
0.2023 0.0534 9.7000e-
004
0.0543 187.7072 187.7072 4.9100e-
003
4.7000e-
003
189.2310
Total 0.0762 0.0483 0.7405 1.8600e-
003
0.2012 1.0500e-
003
0.2023 0.0534 9.7000e-
004
0.0543 187.7072 187.7072 4.9100e-
003
4.7000e-
003
189.2310
Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 9 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 1.5908 0.0000 1.5908 0.1718 0.0000 0.1718 0.0000 0.0000
Off-Road 1.3784 15.6673 10.0558 0.0245 0.5952 0.5952 0.5476 0.5476 0.0000 2,375.156
9
2,375.156
9
0.7682 2,394.361
3
Total 1.3784 15.6673 10.0558 0.0245 1.5908 0.5952 2.1859 0.1718 0.5476 0.7193 0.0000 2,375.156
9
2,375.156
9
0.7682 2,394.361
3
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0762 0.0483 0.7405 1.8600e-
003
0.2012 1.0500e-
003
0.2023 0.0534 9.7000e-
004
0.0543 187.7072 187.7072 4.9100e-
003
4.7000e-
003
189.2310
Total 0.0762 0.0483 0.7405 1.8600e-
003
0.2012 1.0500e-
003
0.2023 0.0534 9.7000e-
004
0.0543 187.7072 187.7072 4.9100e-
003
4.7000e-
003
189.2310
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 10 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 7.0826 0.0000 7.0826 3.4247 0.0000 3.4247 0.0000 0.0000
Off-Road 1.5403 16.9836 9.2202 0.0206 0.7423 0.7423 0.6829 0.6829 1,995.482
5
1,995.482
5
0.6454 2,011.616
9
Total 1.5403 16.9836 9.2202 0.0206 7.0826 0.7423 7.8249 3.4247 0.6829 4.1076 1,995.482
5
1,995.482
5
0.6454 2,011.616
9
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0635 0.0402 0.6171 1.5500e-
003
0.1677 8.8000e-
004
0.1685 0.0445 8.1000e-
004
0.0453 156.4227 156.4227 4.0900e-
003
3.9200e-
003
157.6925
Total 0.0635 0.0402 0.6171 1.5500e-
003
0.1677 8.8000e-
004
0.1685 0.0445 8.1000e-
004
0.0453 156.4227 156.4227 4.0900e-
003
3.9200e-
003
157.6925
Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 11 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 7.0826 0.0000 7.0826 3.4247 0.0000 3.4247 0.0000 0.0000
Off-Road 1.5403 16.9836 9.2202 0.0206 0.7423 0.7423 0.6829 0.6829 0.0000 1,995.482
5
1,995.482
5
0.6454 2,011.616
9
Total 1.5403 16.9836 9.2202 0.0206 7.0826 0.7423 7.8249 3.4247 0.6829 4.1076 0.0000 1,995.482
5
1,995.482
5
0.6454 2,011.616
9
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0635 0.0402 0.6171 1.5500e-
003
0.1677 8.8000e-
004
0.1685 0.0445 8.1000e-
004
0.0453 156.4227 156.4227 4.0900e-
003
3.9200e-
003
157.6925
Total 0.0635 0.0402 0.6171 1.5500e-
003
0.1677 8.8000e-
004
0.1685 0.0445 8.1000e-
004
0.0453 156.4227 156.4227 4.0900e-
003
3.9200e-
003
157.6925
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 12 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.8555 14.6040 14.3533 0.0250 0.7022 0.7022 0.6731 0.6731 2,289.281
3
2,289.281
3
0.4417 2,300.323
0
Total 1.8555 14.6040 14.3533 0.0250 0.7022 0.7022 0.6731 0.6731 2,289.281
3
2,289.281
3
0.4417 2,300.323
0
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0296 0.7444 0.2732 3.1700e-
003
0.1089 8.8600e-
003
0.1178 0.0314 8.4700e-
003
0.0398 340.1170 340.1170 9.1900e-
003
0.0503 355.3457
Worker 0.1821 0.1153 1.7690 4.4400e-
003
0.4806 2.5200e-
003
0.4832 0.1275 2.3200e-
003
0.1298 448.4117 448.4117 0.0117 0.0112 452.0519
Total 0.2117 0.8597 2.0422 7.6100e-
003
0.5896 0.0114 0.6009 0.1588 0.0108 0.1696 788.5287 788.5287 0.0209 0.0616 807.3976
Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 13 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.8555 14.6040 14.3533 0.0250 0.7022 0.7022 0.6731 0.6731 0.0000 2,289.281
3
2,289.281
3
0.4417 2,300.323
0
Total 1.8555 14.6040 14.3533 0.0250 0.7022 0.7022 0.6731 0.6731 0.0000 2,289.281
3
2,289.281
3
0.4417 2,300.323
0
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0296 0.7444 0.2732 3.1700e-
003
0.1089 8.8600e-
003
0.1178 0.0314 8.4700e-
003
0.0398 340.1170 340.1170 9.1900e-
003
0.0503 355.3457
Worker 0.1821 0.1153 1.7690 4.4400e-
003
0.4806 2.5200e-
003
0.4832 0.1275 2.3200e-
003
0.1298 448.4117 448.4117 0.0117 0.0112 452.0519
Total 0.2117 0.8597 2.0422 7.6100e-
003
0.5896 0.0114 0.6009 0.1588 0.0108 0.1696 788.5287 788.5287 0.0209 0.0616 807.3976
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 14 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.7136 13.6239 14.2145 0.0250 0.6136 0.6136 0.5880 0.5880 2,289.523
3
2,289.523
3
0.4330 2,300.347
9
Total 1.7136 13.6239 14.2145 0.0250 0.6136 0.6136 0.5880 0.5880 2,289.523
3
2,289.523
3
0.4330 2,300.347
9
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0199 0.5963 0.2502 3.0400e-
003
0.1089 4.4800e-
003
0.1134 0.0314 4.2900e-
003
0.0357 326.2609 326.2609 8.5300e-
003
0.0482 340.8317
Worker 0.1680 0.1014 1.6172 4.2900e-
003
0.4806 2.3700e-
003
0.4830 0.1275 2.1800e-
003
0.1297 433.8748 433.8748 0.0105 0.0103 437.2157
Total 0.1879 0.6977 1.8674 7.3300e-
003
0.5896 6.8500e-
003
0.5964 0.1588 6.4700e-
003
0.1653 760.1358 760.1358 0.0190 0.0585 778.0473
Unmitigated Construction Off-Site
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Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.7136 13.6239 14.2145 0.0250 0.6136 0.6136 0.5880 0.5880 0.0000 2,289.523
3
2,289.523
3
0.4330 2,300.347
9
Total 1.7136 13.6239 14.2145 0.0250 0.6136 0.6136 0.5880 0.5880 0.0000 2,289.523
3
2,289.523
3
0.4330 2,300.347
9
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0199 0.5963 0.2502 3.0400e-
003
0.1089 4.4800e-
003
0.1134 0.0314 4.2900e-
003
0.0357 326.2609 326.2609 8.5300e-
003
0.0482 340.8317
Worker 0.1680 0.1014 1.6172 4.2900e-
003
0.4806 2.3700e-
003
0.4830 0.1275 2.1800e-
003
0.1297 433.8748 433.8748 0.0105 0.0103 437.2157
Total 0.1879 0.6977 1.8674 7.3300e-
003
0.5896 6.8500e-
003
0.5964 0.1588 6.4700e-
003
0.1653 760.1358 760.1358 0.0190 0.0585 778.0473
Mitigated Construction Off-Site
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Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.8802 8.6098 11.6840 0.0179 0.4338 0.4338 0.4003 0.4003 1,709.992
6
1,709.992
6
0.5420 1,723.541
4
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.8802 8.6098 11.6840 0.0179 0.4338 0.4338 0.4003 0.4003 1,709.992
6
1,709.992
6
0.5420 1,723.541
4
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0782 0.0472 0.7522 2.0000e-
003
0.2236 1.1000e-
003
0.2247 0.0593 1.0100e-
003
0.0603 201.8023 201.8023 4.8800e-
003
4.8000e-
003
203.3561
Total 0.0782 0.0472 0.7522 2.0000e-
003
0.2236 1.1000e-
003
0.2247 0.0593 1.0100e-
003
0.0603 201.8023 201.8023 4.8800e-
003
4.8000e-
003
203.3561
Unmitigated Construction Off-Site
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EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.8802 8.6098 11.6840 0.0179 0.4338 0.4338 0.4003 0.4003 0.0000 1,709.992
6
1,709.992
6
0.5420 1,723.541
4
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.8802 8.6098 11.6840 0.0179 0.4338 0.4338 0.4003 0.4003 0.0000 1,709.992
6
1,709.992
6
0.5420 1,723.541
4
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0782 0.0472 0.7522 2.0000e-
003
0.2236 1.1000e-
003
0.2247 0.0593 1.0100e-
003
0.0603 201.8023 201.8023 4.8800e-
003
4.8000e-
003
203.3561
Total 0.0782 0.0472 0.7522 2.0000e-
003
0.2236 1.1000e-
003
0.2247 0.0593 1.0100e-
003
0.0603 201.8023 201.8023 4.8800e-
003
4.8000e-
003
203.3561
Mitigated Construction Off-Site
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Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Painting - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 47.4531 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 0.1917 1.3030 1.8111 2.9700e-
003
0.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690
Total 47.6448 1.3030 1.8111 2.9700e-
003
0.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0352 0.0212 0.3385 9.0000e-
004
0.1006 5.0000e-
004
0.1011 0.0267 4.6000e-
004
0.0271 90.8110 90.8110 2.2000e-
003
2.1600e-
003
91.5103
Total 0.0352 0.0212 0.3385 9.0000e-
004
0.1006 5.0000e-
004
0.1011 0.0267 4.6000e-
004
0.0271 90.8110 90.8110 2.2000e-
003
2.1600e-
003
91.5103
Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 19 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Painting - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 47.4531 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 0.1917 1.3030 1.8111 2.9700e-
003
0.0708 0.0708 0.0708 0.0708 0.0000 281.4481 281.4481 0.0168 281.8690
Total 47.6448 1.3030 1.8111 2.9700e-
003
0.0708 0.0708 0.0708 0.0708 0.0000 281.4481 281.4481 0.0168 281.8690
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0352 0.0212 0.3385 9.0000e-
004
0.1006 5.0000e-
004
0.1011 0.0267 4.6000e-
004
0.0271 90.8110 90.8110 2.2000e-
003
2.1600e-
003
91.5103
Total 0.0352 0.0212 0.3385 9.0000e-
004
0.1006 5.0000e-
004
0.1011 0.0267 4.6000e-
004
0.0271 90.8110 90.8110 2.2000e-
003
2.1600e-
003
91.5103
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 20 of 26
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EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
4.0 Operational Detail - Mobile
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 0.2987 1.0407 4.1219 0.0138 1.2513 0.0124 1.2636 0.3344 0.0116 0.3461 1,427.695
0
1,427.695
0
0.0665 0.0887 1,455.791
9
Unmitigated 0.2987 1.0407 4.1219 0.0138 1.2513 0.0124 1.2636 0.3344 0.0116 0.3461 1,427.695
0
1,427.695
0
0.0665 0.0887 1,455.791
9
4.1 Mitigation Measures Mobile
4.2 Trip Summary Information
4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Unrefrigerated Warehouse-No Rail 137.19 137.19 137.19 587,954 587,954
Total 137.19 137.19 137.19 587,954 587,954
Miles Trip %Trip Purpose %
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C H-O or C-NW Primary Diverted Pass-by
Unrefrigerated Warehouse-No
Rail
16.60 8.40 6.90 59.00 0.00 41.00 92 5 3
4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH
Unrefrigerated Warehouse-No
Rail
0.553113 0.036408 0.180286 0.116335 0.016165 0.005101 0.018218 0.063797 0.001357 0.001565 0.005903 0.000808 0.000944
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Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
5.0 Energy Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
NaturalGas
Mitigated
6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
NaturalGas
Unmitigated
6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
Unrefrigerated
Warehouse-No
Rail
563.791 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Total 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Unmitigated
5.1 Mitigation Measures Energy
Historical Energy Use: N
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Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
6.1 Mitigation Measures Area
6.0 Area Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Unmitigated 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
Unrefrigerated
Warehouse-No
Rail
0.563791 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Total 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 23 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
0.2600 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
2.0271 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Landscaping 9.6000e-
004
9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Total 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 24 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
7.1 Mitigation Measures Water
7.0 Water Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
0.2600 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
2.0271 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Landscaping 9.6000e-
004
9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Total 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 25 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
11.0 Vegetation
8.1 Mitigation Measures Waste
8.0 Waste Detail
9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type
10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type
Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type
User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:17 PMPage 26 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
Summit Avenue Warehouse
San Bernardino-South Coast County, Winter
Project Characteristics - CalEEMod defaults
Land Use - Lot is 4.49 acres
Construction Phase - Construction schedule provided by the client
Architectural Coating - Per SCAQMD Rule 1113
Vehicle Trips - Recommended average trip rates as proposed in the SCAQMD Warehouse Truck Study for non-cold storage
Road Dust -
Consumer Products -
Area Coating - Per SCAQMD Rule 1113
Fleet Mix - Adjusted to reflect CalEEMod Ver 2013.2 Appendix E Analysis of Warehouse Trip Generation Rates by SCAQMD
Grading -
Off-road Equipment - Per client
Off-road Equipment - Per client
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population
Unrefrigerated Warehouse-No Rail 102.38 1000sqft 4.49 102,380.00 0
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
10
Wind Speed (m/s)Precipitation Freq (Days)2.2 32
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Southern California Edison
2024Operational Year
CO2 Intensity
(lb/MWhr)
531.98 0.033CH4 Intensity
(lb/MWhr)
0.004N2O Intensity
(lb/MWhr)
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 1 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
Off-road Equipment - Per client
Off-road Equipment - Per client
Off-road Equipment -
Table Name Column Name Default Value New Value
tblArchitecturalCoating EF_Nonresidential_Exterior 100.00 50.00
tblArchitecturalCoating EF_Nonresidential_Interior 100.00 50.00
tblConstructionPhase NumDays 5.00 3.00
tblConstructionPhase NumDays 8.00 6.00
tblConstructionPhase NumDays 230.00 140.00
tblConstructionPhase NumDays 18.00 10.00
tblConstructionPhase NumDays 18.00 10.00
tblFleetMix HHD 0.02 0.06
tblFleetMix LDA 0.54 0.55
tblFleetMix LDT1 0.06 0.04
tblFleetMix LDT2 0.17 0.18
tblFleetMix LHD1 0.03 0.02
tblFleetMix LHD2 7.1040e-003 5.1010e-003
tblFleetMix MCY 0.03 5.9030e-003
tblFleetMix MDV 0.14 0.12
tblFleetMix MH 4.8300e-003 9.4400e-004
tblFleetMix MHD 0.01 0.02
tblFleetMix OBUS 5.5400e-004 1.3570e-003
tblFleetMix SBUS 9.5400e-004 8.0800e-004
tblFleetMix UBUS 2.5100e-004 1.5650e-003
tblLandUse LotAcreage 2.35 4.49
tblOffRoadEquipment OffRoadEquipmentUnitAmount 2.00 1.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 2.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 2.00 1.00
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 2 of 26
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EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.0 Emissions Summary
tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 1.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 2.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 4.00 1.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 3.00
tblOffRoadEquipment UsageHours 6.00 8.00
tblOffRoadEquipment UsageHours 7.00 8.00
tblOffRoadEquipment UsageHours 8.00 7.00
tblOffRoadEquipment UsageHours 6.00 8.00
tblOffRoadEquipment UsageHours 6.00 8.00
tblOffRoadEquipment UsageHours 7.00 6.00
tblOffRoadEquipment UsageHours 8.00 7.00
tblOffRoadEquipment UsageHours 8.00 7.00
tblProjectCharacteristics CO2IntensityFactor 390.98 531.98
tblTripsAndVMT WorkerTripNumber 8.00 18.00
tblTripsAndVMT WorkerTripNumber 10.00 15.00
tblTripsAndVMT WorkerTripNumber 15.00 20.00
tblVehicleTrips ST_TR 1.74 1.34
tblVehicleTrips SU_TR 1.74 1.34
tblVehicleTrips WD_TR 1.74 1.34
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 3 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.1 Overall Construction (Maximum Daily Emission)
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2022 2.0589 17.0259 16.0892 0.0322 7.2503 0.7432 7.9934 3.4692 0.6839 4.1529 0.0000 3,035.899
1
3,035.899
1
0.7731 0.0620 3,065.942
2
2023 47.6787 14.3604 15.8034 0.0320 0.5896 0.6205 1.2101 0.1588 0.5945 0.7534 0.0000 3,009.657
3
3,009.657
3
0.5468 0.0590 3,038.535
6
Maximum 47.6787 17.0259 16.0892 0.0322 7.2503 0.7432 7.9934 3.4692 0.6839 4.1529 0.0000 3,035.899
1
3,035.899
1
0.7731 0.0620 3,065.942
2
Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2022 2.0589 17.0259 16.0892 0.0322 7.2503 0.7432 7.9934 3.4692 0.6839 4.1529 0.0000 3,035.899
1
3,035.899
1
0.7731 0.0620 3,065.942
2
2023 47.6787 14.3604 15.8034 0.0320 0.5896 0.6205 1.2101 0.1588 0.5945 0.7534 0.0000 3,009.657
3
3,009.657
3
0.5468 0.0590 3,038.535
6
Maximum 47.6787 17.0259 16.0892 0.0322 7.2503 0.7432 7.9934 3.4692 0.6839 4.1529 0.0000 3,035.899
1
3,035.899
1
0.7731 0.0620 3,065.942
2
Mitigated Construction
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 4 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 5 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Energy 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Mobile 0.2573 1.0986 3.5945 0.0129 1.2513 0.0124 1.2636 0.3344 0.0117 0.3461 1,339.781
7
1,339.781
7
0.0671 0.0897 1,368.188
9
Total 2.5514 1.1540 3.6514 0.0133 1.2513 0.0166 1.2679 0.3344 0.0159 0.3503 1,406.132
5
1,406.132
5
0.0685 0.0909 1,434.935
3
Unmitigated Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Energy 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Mobile 0.2573 1.0986 3.5945 0.0129 1.2513 0.0124 1.2636 0.3344 0.0117 0.3461 1,339.781
7
1,339.781
7
0.0671 0.0897 1,368.188
9
Total 2.5514 1.1540 3.6514 0.0133 1.2513 0.0166 1.2679 0.3344 0.0159 0.3503 1,406.132
5
1,406.132
5
0.0685 0.0909 1,434.935
3
Mitigated Operational
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 6 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Site Preparation Site Preparation 7/1/2022 7/5/2022 5 3
2 Grading Grading 7/6/2022 7/13/2022 5 6
3 Construction Building Construction 7/14/2022 1/25/2023 5 140
4 Paving Paving 1/26/2023 2/8/2023 5 10
5 Painting Architectural Coating 2/9/2023 2/22/2023 5 10
OffRoad Equipment
Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor
Site Preparation Graders 1 8.00 187 0.41
Site Preparation Scrapers 1 8.00 367 0.48
Site Preparation Tractors/Loaders/Backhoes 1 7.00 97 0.37
Grading Graders 1 8.00 187 0.41
Grading Rubber Tired Dozers 1 8.00 247 0.40
Grading Tractors/Loaders/Backhoes 2 7.00 97 0.37
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Residential Indoor: 0; Residential Outdoor: 0; Non-Residential Indoor: 153,570; Non-Residential Outdoor: 51,190; Striped Parking Area: 0
(Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 4.5
Acres of Grading (Grading Phase): 6
Acres of Paving: 0
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 7 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.1 Mitigation Measures Construction
Construction Cranes 1 8.00 231 0.29
Construction Forklifts 2 7.00 89 0.20
Construction Generator Sets 1 8.00 84 0.74
Construction Tractors/Loaders/Backhoes 1 6.00 97 0.37
Construction Welders 3 8.00 46 0.45
Paving Cement and Mortar Mixers 1 8.00 9 0.56
Paving Pavers 1 8.00 130 0.42
Paving Paving Equipment 1 8.00 132 0.36
Paving Rollers 2 8.00 80 0.38
Paving Tractors/Loaders/Backhoes 1 8.00 97 0.37
Painting Air Compressors 1 6.00 78 0.48
Trips and VMT
Phase Name Offroad Equipment
Count
Worker Trip
Number
Vendor Trip
Number
Hauling Trip
Number
Worker Trip
Length
Vendor Trip
Length
Hauling Trip
Length
Worker Vehicle
Class
Vendor
Vehicle Class
Hauling
Vehicle Class
Site Preparation 3 18.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Grading 4 15.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Construction 8 43.00 17.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Paving 6 20.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Painting 1 9.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 8 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 1.5908 0.0000 1.5908 0.1718 0.0000 0.1718 0.0000 0.0000
Off-Road 1.3784 15.6673 10.0558 0.0245 0.5952 0.5952 0.5476 0.5476 2,375.156
9
2,375.156
9
0.7682 2,394.361
3
Total 1.3784 15.6673 10.0558 0.0245 1.5908 0.5952 2.1859 0.1718 0.5476 0.7193 2,375.156
9
2,375.156
9
0.7682 2,394.361
3
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0732 0.0508 0.6083 1.6800e-
003
0.2012 1.0500e-
003
0.2023 0.0534 9.7000e-
004
0.0543 170.0061 170.0061 4.9000e-
003
4.8500e-
003
171.5751
Total 0.0732 0.0508 0.6083 1.6800e-
003
0.2012 1.0500e-
003
0.2023 0.0534 9.7000e-
004
0.0543 170.0061 170.0061 4.9000e-
003
4.8500e-
003
171.5751
Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 9 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 1.5908 0.0000 1.5908 0.1718 0.0000 0.1718 0.0000 0.0000
Off-Road 1.3784 15.6673 10.0558 0.0245 0.5952 0.5952 0.5476 0.5476 0.0000 2,375.156
9
2,375.156
9
0.7682 2,394.361
3
Total 1.3784 15.6673 10.0558 0.0245 1.5908 0.5952 2.1859 0.1718 0.5476 0.7193 0.0000 2,375.156
9
2,375.156
9
0.7682 2,394.361
3
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0732 0.0508 0.6083 1.6800e-
003
0.2012 1.0500e-
003
0.2023 0.0534 9.7000e-
004
0.0543 170.0061 170.0061 4.9000e-
003
4.8500e-
003
171.5751
Total 0.0732 0.0508 0.6083 1.6800e-
003
0.2012 1.0500e-
003
0.2023 0.0534 9.7000e-
004
0.0543 170.0061 170.0061 4.9000e-
003
4.8500e-
003
171.5751
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 10 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 7.0826 0.0000 7.0826 3.4247 0.0000 3.4247 0.0000 0.0000
Off-Road 1.5403 16.9836 9.2202 0.0206 0.7423 0.7423 0.6829 0.6829 1,995.482
5
1,995.482
5
0.6454 2,011.616
9
Total 1.5403 16.9836 9.2202 0.0206 7.0826 0.7423 7.8249 3.4247 0.6829 4.1076 1,995.482
5
1,995.482
5
0.6454 2,011.616
9
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0610 0.0423 0.5069 1.4000e-
003
0.1677 8.8000e-
004
0.1685 0.0445 8.1000e-
004
0.0453 141.6717 141.6717 4.0800e-
003
4.0400e-
003
142.9792
Total 0.0610 0.0423 0.5069 1.4000e-
003
0.1677 8.8000e-
004
0.1685 0.0445 8.1000e-
004
0.0453 141.6717 141.6717 4.0800e-
003
4.0400e-
003
142.9792
Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 11 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 7.0826 0.0000 7.0826 3.4247 0.0000 3.4247 0.0000 0.0000
Off-Road 1.5403 16.9836 9.2202 0.0206 0.7423 0.7423 0.6829 0.6829 0.0000 1,995.482
5
1,995.482
5
0.6454 2,011.616
9
Total 1.5403 16.9836 9.2202 0.0206 7.0826 0.7423 7.8249 3.4247 0.6829 4.1076 0.0000 1,995.482
5
1,995.482
5
0.6454 2,011.616
9
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0610 0.0423 0.5069 1.4000e-
003
0.1677 8.8000e-
004
0.1685 0.0445 8.1000e-
004
0.0453 141.6717 141.6717 4.0800e-
003
4.0400e-
003
142.9792
Total 0.0610 0.0423 0.5069 1.4000e-
003
0.1677 8.8000e-
004
0.1685 0.0445 8.1000e-
004
0.0453 141.6717 141.6717 4.0800e-
003
4.0400e-
003
142.9792
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 12 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.8555 14.6040 14.3533 0.0250 0.7022 0.7022 0.6731 0.6731 2,289.281
3
2,289.281
3
0.4417 2,300.323
0
Total 1.8555 14.6040 14.3533 0.0250 0.7022 0.7022 0.6731 0.6731 2,289.281
3
2,289.281
3
0.4417 2,300.323
0
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0285 0.7815 0.2828 3.1800e-
003
0.1089 8.8800e-
003
0.1178 0.0314 8.5000e-
003
0.0399 340.4922 340.4922 9.1300e-
003
0.0504 355.7454
Worker 0.1749 0.1213 1.4531 4.0200e-
003
0.4806 2.5200e-
003
0.4832 0.1275 2.3200e-
003
0.1298 406.1256 406.1256 0.0117 0.0116 409.8738
Total 0.2034 0.9028 1.7359 7.2000e-
003
0.5896 0.0114 0.6010 0.1588 0.0108 0.1697 746.6178 746.6178 0.0208 0.0620 765.6192
Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 13 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.8555 14.6040 14.3533 0.0250 0.7022 0.7022 0.6731 0.6731 0.0000 2,289.281
3
2,289.281
3
0.4417 2,300.323
0
Total 1.8555 14.6040 14.3533 0.0250 0.7022 0.7022 0.6731 0.6731 0.0000 2,289.281
3
2,289.281
3
0.4417 2,300.323
0
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0285 0.7815 0.2828 3.1800e-
003
0.1089 8.8800e-
003
0.1178 0.0314 8.5000e-
003
0.0399 340.4922 340.4922 9.1300e-
003
0.0504 355.7454
Worker 0.1749 0.1213 1.4531 4.0200e-
003
0.4806 2.5200e-
003
0.4832 0.1275 2.3200e-
003
0.1298 406.1256 406.1256 0.0117 0.0116 409.8738
Total 0.2034 0.9028 1.7359 7.2000e-
003
0.5896 0.0114 0.6010 0.1588 0.0108 0.1697 746.6178 746.6178 0.0208 0.0620 765.6192
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 14 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.7136 13.6239 14.2145 0.0250 0.6136 0.6136 0.5880 0.5880 2,289.523
3
2,289.523
3
0.4330 2,300.347
9
Total 1.7136 13.6239 14.2145 0.0250 0.6136 0.6136 0.5880 0.5880 2,289.523
3
2,289.523
3
0.4330 2,300.347
9
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0185 0.6298 0.2579 3.0500e-
003
0.1089 4.5000e-
003
0.1134 0.0314 4.3000e-
003
0.0357 327.0521 327.0521 8.4600e-
003
0.0483 341.6658
Worker 0.1619 0.1066 1.3311 3.8900e-
003
0.4806 2.3700e-
003
0.4830 0.1275 2.1800e-
003
0.1297 393.0818 393.0818 0.0105 0.0107 396.5220
Total 0.1804 0.7364 1.5890 6.9400e-
003
0.5896 6.8700e-
003
0.5964 0.1588 6.4800e-
003
0.1653 720.1340 720.1340 0.0190 0.0590 738.1877
Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 15 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.7136 13.6239 14.2145 0.0250 0.6136 0.6136 0.5880 0.5880 0.0000 2,289.523
3
2,289.523
3
0.4330 2,300.347
9
Total 1.7136 13.6239 14.2145 0.0250 0.6136 0.6136 0.5880 0.5880 0.0000 2,289.523
3
2,289.523
3
0.4330 2,300.347
9
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0185 0.6298 0.2579 3.0500e-
003
0.1089 4.5000e-
003
0.1134 0.0314 4.3000e-
003
0.0357 327.0521 327.0521 8.4600e-
003
0.0483 341.6658
Worker 0.1619 0.1066 1.3311 3.8900e-
003
0.4806 2.3700e-
003
0.4830 0.1275 2.1800e-
003
0.1297 393.0818 393.0818 0.0105 0.0107 396.5220
Total 0.1804 0.7364 1.5890 6.9400e-
003
0.5896 6.8700e-
003
0.5964 0.1588 6.4800e-
003
0.1653 720.1340 720.1340 0.0190 0.0590 738.1877
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 16 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.8802 8.6098 11.6840 0.0179 0.4338 0.4338 0.4003 0.4003 1,709.992
6
1,709.992
6
0.5420 1,723.541
4
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.8802 8.6098 11.6840 0.0179 0.4338 0.4338 0.4003 0.4003 1,709.992
6
1,709.992
6
0.5420 1,723.541
4
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0753 0.0496 0.6191 1.8100e-
003
0.2236 1.1000e-
003
0.2247 0.0593 1.0100e-
003
0.0603 182.8288 182.8288 4.8900e-
003
4.9600e-
003
184.4288
Total 0.0753 0.0496 0.6191 1.8100e-
003
0.2236 1.1000e-
003
0.2247 0.0593 1.0100e-
003
0.0603 182.8288 182.8288 4.8900e-
003
4.9600e-
003
184.4288
Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 17 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.8802 8.6098 11.6840 0.0179 0.4338 0.4338 0.4003 0.4003 0.0000 1,709.992
6
1,709.992
6
0.5420 1,723.541
4
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 0.8802 8.6098 11.6840 0.0179 0.4338 0.4338 0.4003 0.4003 0.0000 1,709.992
6
1,709.992
6
0.5420 1,723.541
4
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0753 0.0496 0.6191 1.8100e-
003
0.2236 1.1000e-
003
0.2247 0.0593 1.0100e-
003
0.0603 182.8288 182.8288 4.8900e-
003
4.9600e-
003
184.4288
Total 0.0753 0.0496 0.6191 1.8100e-
003
0.2236 1.1000e-
003
0.2247 0.0593 1.0100e-
003
0.0603 182.8288 182.8288 4.8900e-
003
4.9600e-
003
184.4288
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 18 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Painting - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 47.4531 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 0.1917 1.3030 1.8111 2.9700e-
003
0.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690
Total 47.6448 1.3030 1.8111 2.9700e-
003
0.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690
Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0339 0.0223 0.2786 8.1000e-
004
0.1006 5.0000e-
004
0.1011 0.0267 4.6000e-
004
0.0271 82.2729 82.2729 2.2000e-
003
2.2300e-
003
82.9930
Total 0.0339 0.0223 0.2786 8.1000e-
004
0.1006 5.0000e-
004
0.1011 0.0267 4.6000e-
004
0.0271 82.2729 82.2729 2.2000e-
003
2.2300e-
003
82.9930
Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 19 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Painting - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 47.4531 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 0.1917 1.3030 1.8111 2.9700e-
003
0.0708 0.0708 0.0708 0.0708 0.0000 281.4481 281.4481 0.0168 281.8690
Total 47.6448 1.3030 1.8111 2.9700e-
003
0.0708 0.0708 0.0708 0.0708 0.0000 281.4481 281.4481 0.0168 281.8690
Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 0.0339 0.0223 0.2786 8.1000e-
004
0.1006 5.0000e-
004
0.1011 0.0267 4.6000e-
004
0.0271 82.2729 82.2729 2.2000e-
003
2.2300e-
003
82.9930
Total 0.0339 0.0223 0.2786 8.1000e-
004
0.1006 5.0000e-
004
0.1011 0.0267 4.6000e-
004
0.0271 82.2729 82.2729 2.2000e-
003
2.2300e-
003
82.9930
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 20 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
4.0 Operational Detail - Mobile
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 0.2573 1.0986 3.5945 0.0129 1.2513 0.0124 1.2636 0.3344 0.0117 0.3461 1,339.781
7
1,339.781
7
0.0671 0.0897 1,368.188
9
Unmitigated 0.2573 1.0986 3.5945 0.0129 1.2513 0.0124 1.2636 0.3344 0.0117 0.3461 1,339.781
7
1,339.781
7
0.0671 0.0897 1,368.188
9
4.1 Mitigation Measures Mobile
4.2 Trip Summary Information
4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Unrefrigerated Warehouse-No Rail 137.19 137.19 137.19 587,954 587,954
Total 137.19 137.19 137.19 587,954 587,954
Miles Trip %Trip Purpose %
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C H-O or C-NW Primary Diverted Pass-by
Unrefrigerated Warehouse-No
Rail
16.60 8.40 6.90 59.00 0.00 41.00 92 5 3
4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH
Unrefrigerated Warehouse-No
Rail
0.553113 0.036408 0.180286 0.116335 0.016165 0.005101 0.018218 0.063797 0.001357 0.001565 0.005903 0.000808 0.000944
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 21 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
5.0 Energy Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
NaturalGas
Mitigated
6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
NaturalGas
Unmitigated
6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
Unrefrigerated
Warehouse-No
Rail
563.791 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Total 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Unmitigated
5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 22 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
6.1 Mitigation Measures Area
6.0 Area Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Unmitigated 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
Unrefrigerated
Warehouse-No
Rail
0.563791 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Total 6.0800e-
003
0.0553 0.0464 3.3000e-
004
4.2000e-
003
4.2000e-
003
4.2000e-
003
4.2000e-
003
66.3284 66.3284 1.2700e-
003
1.2200e-
003
66.7225
Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 23 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
0.2600 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
2.0271 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Landscaping 9.6000e-
004
9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Total 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 24 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
7.1 Mitigation Measures Water
7.0 Water Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
0.2600 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
2.0271 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Landscaping 9.6000e-
004
9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Total 2.2881 9.0000e-
005
0.0104 0.0000 4.0000e-
005
4.0000e-
005
4.0000e-
005
4.0000e-
005
0.0224 0.0224 6.0000e-
005
0.0239
Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 25 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
11.0 Vegetation
8.1 Mitigation Measures Waste
8.0 Waste Detail
9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type
10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type
Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type
User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:23 PMPage 26 of 26
Summit Avenue Warehouse - San Bernardino-South Coast County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
Summit Avenue Warehouse
San Bernardino-South Coast County, Annual
Project Characteristics - CalEEMod defaults
Land Use - Lot is 4.49 acres
Construction Phase - Construction schedule provided by the client
Architectural Coating - Per SCAQMD Rule 1113
Vehicle Trips - Recommended average trip rates as proposed in the SCAQMD Warehouse Truck Study for non-cold storage
Road Dust -
Consumer Products -
Area Coating - Per SCAQMD Rule 1113
Fleet Mix - Adjusted to reflect CalEEMod Ver 2013.2 Appendix E Analysis of Warehouse Trip Generation Rates by SCAQMD
Grading -
Off-road Equipment - Per client
Off-road Equipment - Per client
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population
Unrefrigerated Warehouse-No Rail 102.38 1000sqft 4.49 102,380.00 0
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
10
Wind Speed (m/s)Precipitation Freq (Days)2.2 32
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Southern California Edison
2024Operational Year
CO2 Intensity
(lb/MWhr)
531.98 0.033CH4 Intensity
(lb/MWhr)
0.004N2O Intensity
(lb/MWhr)
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 1 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
Off-road Equipment - Per client
Off-road Equipment - Per client
Off-road Equipment -
Table Name Column Name Default Value New Value
tblArchitecturalCoating EF_Nonresidential_Exterior 100.00 50.00
tblArchitecturalCoating EF_Nonresidential_Interior 100.00 50.00
tblConstructionPhase NumDays 5.00 3.00
tblConstructionPhase NumDays 8.00 6.00
tblConstructionPhase NumDays 230.00 140.00
tblConstructionPhase NumDays 18.00 10.00
tblConstructionPhase NumDays 18.00 10.00
tblFleetMix HHD 0.02 0.06
tblFleetMix LDA 0.54 0.55
tblFleetMix LDT1 0.06 0.04
tblFleetMix LDT2 0.17 0.18
tblFleetMix LHD1 0.03 0.02
tblFleetMix LHD2 7.1040e-003 5.1010e-003
tblFleetMix MCY 0.03 5.9030e-003
tblFleetMix MDV 0.14 0.12
tblFleetMix MH 4.8300e-003 9.4400e-004
tblFleetMix MHD 0.01 0.02
tblFleetMix OBUS 5.5400e-004 1.3570e-003
tblFleetMix SBUS 9.5400e-004 8.0800e-004
tblFleetMix UBUS 2.5100e-004 1.5650e-003
tblLandUse LotAcreage 2.35 4.49
tblOffRoadEquipment OffRoadEquipmentUnitAmount 2.00 1.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 2.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 2.00 1.00
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 2 of 30
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EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.0 Emissions Summary
tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 1.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 3.00 2.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 4.00 1.00
tblOffRoadEquipment OffRoadEquipmentUnitAmount 1.00 3.00
tblOffRoadEquipment UsageHours 6.00 8.00
tblOffRoadEquipment UsageHours 7.00 8.00
tblOffRoadEquipment UsageHours 8.00 7.00
tblOffRoadEquipment UsageHours 6.00 8.00
tblOffRoadEquipment UsageHours 6.00 8.00
tblOffRoadEquipment UsageHours 7.00 6.00
tblOffRoadEquipment UsageHours 8.00 7.00
tblOffRoadEquipment UsageHours 8.00 7.00
tblProjectCharacteristics CO2IntensityFactor 390.98 531.98
tblTripsAndVMT WorkerTripNumber 8.00 18.00
tblTripsAndVMT WorkerTripNumber 10.00 15.00
tblTripsAndVMT WorkerTripNumber 15.00 20.00
tblVehicleTrips ST_TR 1.74 1.34
tblVehicleTrips SU_TR 1.74 1.34
tblVehicleTrips WD_TR 1.74 1.34
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 3 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.1 Overall Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year tons/yr MT/yr
2022 0.1318 1.0210 1.0307 2.0800e-
003
0.0597 0.0467 0.1064 0.0203 0.0446 0.0649 0.0000 177.7289 177.7289 0.0284 3.4700e-
003
179.4736
2023 0.2601 0.1792 0.2150 4.1000e-
004
6.8000e-
003
8.1200e-
003
0.0149 1.8300e-
003
7.7100e-
003
9.5400e-
003
0.0000 34.8922 34.8922 6.2600e-
003
5.2000e-
004
35.2029
Maximum 0.2601 1.0210 1.0307 2.0800e-
003
0.0597 0.0467 0.1064 0.0203 0.0446 0.0649 0.0000 177.7289 177.7289 0.0284 3.4700e-
003
179.4736
Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year tons/yr MT/yr
2022 0.1318 1.0210 1.0307 2.0800e-
003
0.0597 0.0467 0.1064 0.0203 0.0446 0.0649 0.0000 177.7288 177.7288 0.0284 3.4700e-
003
179.4734
2023 0.2601 0.1792 0.2150 4.1000e-
004
6.8000e-
003
8.1200e-
003
0.0149 1.8300e-
003
7.7100e-
003
9.5400e-
003
0.0000 34.8921 34.8921 6.2600e-
003
5.2000e-
004
35.2029
Maximum 0.2601 1.0210 1.0307 2.0800e-
003
0.0597 0.0467 0.1064 0.0203 0.0446 0.0649 0.0000 177.7288 177.7288 0.0284 3.4700e-
003
179.4734
Mitigated Construction
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 4 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Quarter Start Date End Date Maximum Unmitigated ROG + NOX (tons/quarter)Maximum Mitigated ROG + NOX (tons/quarter)
1 7-1-2022 9-30-2022 0.5785 0.5785
2 10-1-2022 12-31-2022 0.5772 0.5772
3 1-1-2023 3-31-2023 0.4382 0.4382
Highest 0.5785 0.5785
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Area 0.4175 1.0000e-
005
1.3000e-
003
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 2.5400e-
003
2.5400e-
003
1.0000e-
005
0.0000 2.7100e-
003
Energy 1.1100e-
003
0.0101 8.4700e-
003
6.0000e-
005
7.7000e-
004
7.7000e-
004
7.7000e-
004
7.7000e-
004
0.0000 68.2959 68.2959 3.7700e-
003
6.3000e-
004
68.5784
Mobile 0.0467 0.2018 0.6789 2.3800e-
003
0.2235 2.2500e-
003
0.2257 0.0598 2.1200e-
003
0.0619 0.0000 223.6683 223.6683 0.0111 0.0149 228.3874
Waste 0.0000 0.0000 0.0000 0.0000 19.5359 0.0000 19.5359 1.1545 0.0000 48.3992
Water 0.0000 0.0000 0.0000 0.0000 7.5111 74.3879 81.8990 0.7761 0.0188 106.8959
Total 0.4653 0.2119 0.6887 2.4400e-
003
0.2235 3.0200e-
003
0.2265 0.0598 2.8900e-
003
0.0627 27.0470 366.3546 393.4015 1.9455 0.0343 452.2637
Unmitigated Operational
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 5 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Area 0.4175 1.0000e-
005
1.3000e-
003
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 2.5400e-
003
2.5400e-
003
1.0000e-
005
0.0000 2.7100e-
003
Energy 1.1100e-
003
0.0101 8.4700e-
003
6.0000e-
005
7.7000e-
004
7.7000e-
004
7.7000e-
004
7.7000e-
004
0.0000 68.2959 68.2959 3.7700e-
003
6.3000e-
004
68.5784
Mobile 0.0467 0.2018 0.6789 2.3800e-
003
0.2235 2.2500e-
003
0.2257 0.0598 2.1200e-
003
0.0619 0.0000 223.6683 223.6683 0.0111 0.0149 228.3874
Waste 0.0000 0.0000 0.0000 0.0000 19.5359 0.0000 19.5359 1.1545 0.0000 48.3992
Water 0.0000 0.0000 0.0000 0.0000 7.5111 74.3879 81.8990 0.7761 0.0188 106.8959
Total 0.4653 0.2119 0.6887 2.4400e-
003
0.2235 3.0200e-
003
0.2265 0.0598 2.8900e-
003
0.0627 27.0470 366.3546 393.4015 1.9455 0.0343 452.2637
Mitigated Operational
3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Site Preparation Site Preparation 7/1/2022 7/5/2022 5 3
2 Grading Grading 7/6/2022 7/13/2022 5 6
3 Construction Building Construction 7/14/2022 1/25/2023 5 140
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 6 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
4 Paving Paving 1/26/2023 2/8/2023 5 10
5 Painting Architectural Coating 2/9/2023 2/22/2023 5 10
OffRoad Equipment
Phase Name Offroad Equipment Type Amount Usage Hours Horse Power Load Factor
Site Preparation Graders 1 8.00 187 0.41
Site Preparation Scrapers 1 8.00 367 0.48
Site Preparation Tractors/Loaders/Backhoes 1 7.00 97 0.37
Grading Graders 1 8.00 187 0.41
Grading Rubber Tired Dozers 1 8.00 247 0.40
Grading Tractors/Loaders/Backhoes 2 7.00 97 0.37
Construction Cranes 1 8.00 231 0.29
Construction Forklifts 2 7.00 89 0.20
Construction Generator Sets 1 8.00 84 0.74
Construction Tractors/Loaders/Backhoes 1 6.00 97 0.37
Construction Welders 3 8.00 46 0.45
Paving Cement and Mortar Mixers 1 8.00 9 0.56
Paving Pavers 1 8.00 130 0.42
Paving Paving Equipment 1 8.00 132 0.36
Paving Rollers 2 8.00 80 0.38
Paving Tractors/Loaders/Backhoes 1 8.00 97 0.37
Painting Air Compressors 1 6.00 78 0.48
Residential Indoor: 0; Residential Outdoor: 0; Non-Residential Indoor: 153,570; Non-Residential Outdoor: 51,190; Striped Parking Area: 0
(Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 4.5
Acres of Grading (Grading Phase): 6
Acres of Paving: 0
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 7 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 2.3900e-
003
0.0000 2.3900e-
003
2.6000e-
004
0.0000 2.6000e-
004
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 2.0700e-
003
0.0235 0.0151 4.0000e-
005
8.9000e-
004
8.9000e-
004
8.2000e-
004
8.2000e-
004
0.0000 3.2321 3.2321 1.0500e-
003
0.0000 3.2582
Total 2.0700e-
003
0.0235 0.0151 4.0000e-
005
2.3900e-
003
8.9000e-
004
3.2800e-
003
2.6000e-
004
8.2000e-
004
1.0800e-
003
0.0000 3.2321 3.2321 1.0500e-
003
0.0000 3.2582
Unmitigated Construction On-Site
3.1 Mitigation Measures Construction
Trips and VMT
Phase Name Offroad Equipment
Count
Worker Trip
Number
Vendor Trip
Number
Hauling Trip
Number
Worker Trip
Length
Vendor Trip
Length
Hauling Trip
Length
Worker Vehicle
Class
Vendor
Vehicle Class
Hauling
Vehicle Class
Site Preparation 3 18.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Grading 4 15.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Construction 8 43.00 17.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Paving 6 20.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
Painting 1 9.00 0.00 0.00 14.70 6.90 20.00 LD_Mix HDT_Mix HHDT
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 8 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 1.0000e-
004
8.0000e-
005
9.6000e-
004
0.0000 3.0000e-
004
0.0000 3.0000e-
004
8.0000e-
005
0.0000 8.0000e-
005
0.0000 0.2360 0.2360 1.0000e-
005
1.0000e-
005
0.2382
Total 1.0000e-
004
8.0000e-
005
9.6000e-
004
0.0000 3.0000e-
004
0.0000 3.0000e-
004
8.0000e-
005
0.0000 8.0000e-
005
0.0000 0.2360 0.2360 1.0000e-
005
1.0000e-
005
0.2382
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 2.3900e-
003
0.0000 2.3900e-
003
2.6000e-
004
0.0000 2.6000e-
004
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 2.0700e-
003
0.0235 0.0151 4.0000e-
005
8.9000e-
004
8.9000e-
004
8.2000e-
004
8.2000e-
004
0.0000 3.2321 3.2321 1.0500e-
003
0.0000 3.2582
Total 2.0700e-
003
0.0235 0.0151 4.0000e-
005
2.3900e-
003
8.9000e-
004
3.2800e-
003
2.6000e-
004
8.2000e-
004
1.0800e-
003
0.0000 3.2321 3.2321 1.0500e-
003
0.0000 3.2582
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 9 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 1.0000e-
004
8.0000e-
005
9.6000e-
004
0.0000 3.0000e-
004
0.0000 3.0000e-
004
8.0000e-
005
0.0000 8.0000e-
005
0.0000 0.2360 0.2360 1.0000e-
005
1.0000e-
005
0.2382
Total 1.0000e-
004
8.0000e-
005
9.6000e-
004
0.0000 3.0000e-
004
0.0000 3.0000e-
004
8.0000e-
005
0.0000 8.0000e-
005
0.0000 0.2360 0.2360 1.0000e-
005
1.0000e-
005
0.2382
Mitigated Construction Off-Site
3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.0213 0.0000 0.0213 0.0103 0.0000 0.0103 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 4.6200e-
003
0.0510 0.0277 6.0000e-
005
2.2300e-
003
2.2300e-
003
2.0500e-
003
2.0500e-
003
0.0000 5.4308 5.4308 1.7600e-
003
0.0000 5.4747
Total 4.6200e-
003
0.0510 0.0277 6.0000e-
005
0.0213 2.2300e-
003
0.0235 0.0103 2.0500e-
003
0.0123 0.0000 5.4308 5.4308 1.7600e-
003
0.0000 5.4747
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 10 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 1.7000e-
004
1.3000e-
004
1.5900e-
003
0.0000 4.9000e-
004
0.0000 5.0000e-
004
1.3000e-
004
0.0000 1.3000e-
004
0.0000 0.3932 0.3932 1.0000e-
005
1.0000e-
005
0.3969
Total 1.7000e-
004
1.3000e-
004
1.5900e-
003
0.0000 4.9000e-
004
0.0000 5.0000e-
004
1.3000e-
004
0.0000 1.3000e-
004
0.0000 0.3932 0.3932 1.0000e-
005
1.0000e-
005
0.3969
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.0213 0.0000 0.0213 0.0103 0.0000 0.0103 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 4.6200e-
003
0.0510 0.0277 6.0000e-
005
2.2300e-
003
2.2300e-
003
2.0500e-
003
2.0500e-
003
0.0000 5.4308 5.4308 1.7600e-
003
0.0000 5.4747
Total 4.6200e-
003
0.0510 0.0277 6.0000e-
005
0.0213 2.2300e-
003
0.0235 0.0103 2.0500e-
003
0.0123 0.0000 5.4308 5.4308 1.7600e-
003
0.0000 5.4747
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 11 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 1.7000e-
004
1.3000e-
004
1.5900e-
003
0.0000 4.9000e-
004
0.0000 5.0000e-
004
1.3000e-
004
0.0000 1.3000e-
004
0.0000 0.3932 0.3932 1.0000e-
005
1.0000e-
005
0.3969
Total 1.7000e-
004
1.3000e-
004
1.5900e-
003
0.0000 4.9000e-
004
0.0000 5.0000e-
004
1.3000e-
004
0.0000 1.3000e-
004
0.0000 0.3932 0.3932 1.0000e-
005
1.0000e-
005
0.3969
Mitigated Construction Off-Site
3.4 Construction - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.1132 0.8909 0.8756 1.5300e-
003
0.0428 0.0428 0.0411 0.0411 0.0000 126.6849 126.6849 0.0244 0.0000 127.2959
Total 0.1132 0.8909 0.8756 1.5300e-
003
0.0428 0.0428 0.0411 0.0411 0.0000 126.6849 126.6849 0.0244 0.0000 127.2959
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 12 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 1.7700e-
003
0.0478 0.0169 1.9000e-
004
6.5400e-
003
5.4000e-
004
7.0800e-
003
1.8900e-
003
5.2000e-
004
2.4100e-
003
0.0000 18.8303 18.8303 5.1000e-
004
2.7900e-
003
19.6740
Worker 9.8800e-
003
7.7600e-
003
0.0930 2.5000e-
004
0.0288 1.5000e-
004
0.0289 7.6400e-
003
1.4000e-
004
7.7800e-
003
0.0000 22.9217 22.9217 6.6000e-
004
6.6000e-
004
23.1357
Total 0.0117 0.0555 0.1099 4.4000e-
004
0.0353 6.9000e-
004
0.0360 9.5300e-
003
6.6000e-
004
0.0102 0.0000 41.7520 41.7520 1.1700e-
003
3.4500e-
003
42.8097
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.1132 0.8908 0.8756 1.5300e-
003
0.0428 0.0428 0.0411 0.0411 0.0000 126.6847 126.6847 0.0244 0.0000 127.2957
Total 0.1132 0.8908 0.8756 1.5300e-
003
0.0428 0.0428 0.0411 0.0411 0.0000 126.6847 126.6847 0.0244 0.0000 127.2957
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 13 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 1.7700e-
003
0.0478 0.0169 1.9000e-
004
6.5400e-
003
5.4000e-
004
7.0800e-
003
1.8900e-
003
5.2000e-
004
2.4100e-
003
0.0000 18.8303 18.8303 5.1000e-
004
2.7900e-
003
19.6740
Worker 9.8800e-
003
7.7600e-
003
0.0930 2.5000e-
004
0.0288 1.5000e-
004
0.0289 7.6400e-
003
1.4000e-
004
7.7800e-
003
0.0000 22.9217 22.9217 6.6000e-
004
6.6000e-
004
23.1357
Total 0.0117 0.0555 0.1099 4.4000e-
004
0.0353 6.9000e-
004
0.0360 9.5300e-
003
6.6000e-
004
0.0102 0.0000 41.7520 41.7520 1.1700e-
003
3.4500e-
003
42.8097
Mitigated Construction Off-Site
3.4 Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.0154 0.1226 0.1279 2.3000e-
004
5.5200e-
003
5.5200e-
003
5.2900e-
003
5.2900e-
003
0.0000 18.6932 18.6932 3.5400e-
003
0.0000 18.7816
Total 0.0154 0.1226 0.1279 2.3000e-
004
5.5200e-
003
5.5200e-
003
5.2900e-
003
5.2900e-
003
0.0000 18.6932 18.6932 3.5400e-
003
0.0000 18.7816
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 14 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 1.7000e-
004
5.6400e-
003
2.2900e-
003
3.0000e-
005
9.6000e-
004
4.0000e-
005
1.0100e-
003
2.8000e-
004
4.0000e-
005
3.2000e-
004
0.0000 2.6665 2.6665 7.0000e-
005
3.9000e-
004
2.7857
Worker 1.3500e-
003
1.0100e-
003
0.0126 4.0000e-
005
4.2400e-
003
2.0000e-
005
4.2600e-
003
1.1300e-
003
2.0000e-
005
1.1500e-
003
0.0000 3.2731 3.2731 9.0000e-
005
9.0000e-
005
3.3020
Total 1.5200e-
003
6.6500e-
003
0.0149 7.0000e-
005
5.2000e-
003
6.0000e-
005
5.2700e-
003
1.4100e-
003
6.0000e-
005
1.4700e-
003
0.0000 5.9396 5.9396 1.6000e-
004
4.8000e-
004
6.0877
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.0154 0.1226 0.1279 2.3000e-
004
5.5200e-
003
5.5200e-
003
5.2900e-
003
5.2900e-
003
0.0000 18.6932 18.6932 3.5400e-
003
0.0000 18.7815
Total 0.0154 0.1226 0.1279 2.3000e-
004
5.5200e-
003
5.5200e-
003
5.2900e-
003
5.2900e-
003
0.0000 18.6932 18.6932 3.5400e-
003
0.0000 18.7815
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 15 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 1.7000e-
004
5.6400e-
003
2.2900e-
003
3.0000e-
005
9.6000e-
004
4.0000e-
005
1.0100e-
003
2.8000e-
004
4.0000e-
005
3.2000e-
004
0.0000 2.6665 2.6665 7.0000e-
005
3.9000e-
004
2.7857
Worker 1.3500e-
003
1.0100e-
003
0.0126 4.0000e-
005
4.2400e-
003
2.0000e-
005
4.2600e-
003
1.1300e-
003
2.0000e-
005
1.1500e-
003
0.0000 3.2731 3.2731 9.0000e-
005
9.0000e-
005
3.3020
Total 1.5200e-
003
6.6500e-
003
0.0149 7.0000e-
005
5.2000e-
003
6.0000e-
005
5.2700e-
003
1.4100e-
003
6.0000e-
005
1.4700e-
003
0.0000 5.9396 5.9396 1.6000e-
004
4.8000e-
004
6.0877
Mitigated Construction Off-Site
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 4.4000e-
003
0.0431 0.0584 9.0000e-
005
2.1700e-
003
2.1700e-
003
2.0000e-
003
2.0000e-
003
0.0000 7.7564 7.7564 2.4600e-
003
0.0000 7.8179
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 4.4000e-
003
0.0431 0.0584 9.0000e-
005
2.1700e-
003
2.1700e-
003
2.0000e-
003
2.0000e-
003
0.0000 7.7564 7.7564 2.4600e-
003
0.0000 7.8179
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 16 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 3.5000e-
004
2.6000e-
004
3.2500e-
003
1.0000e-
005
1.1000e-
003
1.0000e-
005
1.1000e-
003
2.9000e-
004
1.0000e-
005
3.0000e-
004
0.0000 0.8458 0.8458 2.0000e-
005
2.0000e-
005
0.8532
Total 3.5000e-
004
2.6000e-
004
3.2500e-
003
1.0000e-
005
1.1000e-
003
1.0000e-
005
1.1000e-
003
2.9000e-
004
1.0000e-
005
3.0000e-
004
0.0000 0.8458 0.8458 2.0000e-
005
2.0000e-
005
0.8532
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 4.4000e-
003
0.0431 0.0584 9.0000e-
005
2.1700e-
003
2.1700e-
003
2.0000e-
003
2.0000e-
003
0.0000 7.7564 7.7564 2.4600e-
003
0.0000 7.8178
Paving 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Total 4.4000e-
003
0.0431 0.0584 9.0000e-
005
2.1700e-
003
2.1700e-
003
2.0000e-
003
2.0000e-
003
0.0000 7.7564 7.7564 2.4600e-
003
0.0000 7.8178
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 17 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 3.5000e-
004
2.6000e-
004
3.2500e-
003
1.0000e-
005
1.1000e-
003
1.0000e-
005
1.1000e-
003
2.9000e-
004
1.0000e-
005
3.0000e-
004
0.0000 0.8458 0.8458 2.0000e-
005
2.0000e-
005
0.8532
Total 3.5000e-
004
2.6000e-
004
3.2500e-
003
1.0000e-
005
1.1000e-
003
1.0000e-
005
1.1000e-
003
2.9000e-
004
1.0000e-
005
3.0000e-
004
0.0000 0.8458 0.8458 2.0000e-
005
2.0000e-
005
0.8532
Mitigated Construction Off-Site
3.6 Painting - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Archit. Coating 0.2373 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 9.6000e-
004
6.5100e-
003
9.0600e-
003
1.0000e-
005
3.5000e-
004
3.5000e-
004
3.5000e-
004
3.5000e-
004
0.0000 1.2766 1.2766 8.0000e-
005
0.0000 1.2785
Total 0.2382 6.5100e-
003
9.0600e-
003
1.0000e-
005
3.5000e-
004
3.5000e-
004
3.5000e-
004
3.5000e-
004
0.0000 1.2766 1.2766 8.0000e-
005
0.0000 1.2785
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 18 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Painting - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 1.6000e-
004
1.2000e-
004
1.4600e-
003
0.0000 4.9000e-
004
0.0000 5.0000e-
004
1.3000e-
004
0.0000 1.3000e-
004
0.0000 0.3806 0.3806 1.0000e-
005
1.0000e-
005
0.3840
Total 1.6000e-
004
1.2000e-
004
1.4600e-
003
0.0000 4.9000e-
004
0.0000 5.0000e-
004
1.3000e-
004
0.0000 1.3000e-
004
0.0000 0.3806 0.3806 1.0000e-
005
1.0000e-
005
0.3840
Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Archit. Coating 0.2373 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Off-Road 9.6000e-
004
6.5100e-
003
9.0600e-
003
1.0000e-
005
3.5000e-
004
3.5000e-
004
3.5000e-
004
3.5000e-
004
0.0000 1.2766 1.2766 8.0000e-
005
0.0000 1.2785
Total 0.2382 6.5100e-
003
9.0600e-
003
1.0000e-
005
3.5000e-
004
3.5000e-
004
3.5000e-
004
3.5000e-
004
0.0000 1.2766 1.2766 8.0000e-
005
0.0000 1.2785
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 19 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Painting - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Worker 1.6000e-
004
1.2000e-
004
1.4600e-
003
0.0000 4.9000e-
004
0.0000 5.0000e-
004
1.3000e-
004
0.0000 1.3000e-
004
0.0000 0.3806 0.3806 1.0000e-
005
1.0000e-
005
0.3840
Total 1.6000e-
004
1.2000e-
004
1.4600e-
003
0.0000 4.9000e-
004
0.0000 5.0000e-
004
1.3000e-
004
0.0000 1.3000e-
004
0.0000 0.3806 0.3806 1.0000e-
005
1.0000e-
005
0.3840
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 20 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
4.0 Operational Detail - Mobile
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 0.0467 0.2018 0.6789 2.3800e-
003
0.2235 2.2500e-
003
0.2257 0.0598 2.1200e-
003
0.0619 0.0000 223.6683 223.6683 0.0111 0.0149 228.3874
Unmitigated 0.0467 0.2018 0.6789 2.3800e-
003
0.2235 2.2500e-
003
0.2257 0.0598 2.1200e-
003
0.0619 0.0000 223.6683 223.6683 0.0111 0.0149 228.3874
4.1 Mitigation Measures Mobile
4.2 Trip Summary Information
4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Unrefrigerated Warehouse-No Rail 137.19 137.19 137.19 587,954 587,954
Total 137.19 137.19 137.19 587,954 587,954
Miles Trip %Trip Purpose %
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C H-O or C-NW Primary Diverted Pass-by
Unrefrigerated Warehouse-No
Rail
16.60 8.40 6.90 59.00 0.00 41.00 92 5 3
4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH
Unrefrigerated Warehouse-No
Rail
0.553113 0.036408 0.180286 0.116335 0.016165 0.005101 0.018218 0.063797 0.001357 0.001565 0.005903 0.000808 0.000944
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 21 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
5.0 Energy Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Electricity
Mitigated
0.0000 0.0000 0.0000 0.0000 0.0000 57.3145 57.3145 3.5600e-
003
4.3000e-
004
57.5318
Electricity
Unmitigated
0.0000 0.0000 0.0000 0.0000 0.0000 57.3145 57.3145 3.5600e-
003
4.3000e-
004
57.5318
NaturalGas
Mitigated
1.1100e-
003
0.0101 8.4700e-
003
6.0000e-
005
7.7000e-
004
7.7000e-
004
7.7000e-
004
7.7000e-
004
0.0000 10.9814 10.9814 2.1000e-
004
2.0000e-
004
11.0467
NaturalGas
Unmitigated
1.1100e-
003
0.0101 8.4700e-
003
6.0000e-
005
7.7000e-
004
7.7000e-
004
7.7000e-
004
7.7000e-
004
0.0000 10.9814 10.9814 2.1000e-
004
2.0000e-
004
11.0467
5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 22 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr tons/yr MT/yr
Unrefrigerated
Warehouse-No
Rail
205784 1.1100e-
003
0.0101 8.4700e-
003
6.0000e-
005
7.7000e-
004
7.7000e-
004
7.7000e-
004
7.7000e-
004
0.0000 10.9814 10.9814 2.1000e-
004
2.0000e-
004
11.0467
Total 1.1100e-
003
0.0101 8.4700e-
003
6.0000e-
005
7.7000e-
004
7.7000e-
004
7.7000e-
004
7.7000e-
004
0.0000 10.9814 10.9814 2.1000e-
004
2.0000e-
004
11.0467
Unmitigated
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr tons/yr MT/yr
Unrefrigerated
Warehouse-No
Rail
205784 1.1100e-
003
0.0101 8.4700e-
003
6.0000e-
005
7.7000e-
004
7.7000e-
004
7.7000e-
004
7.7000e-
004
0.0000 10.9814 10.9814 2.1000e-
004
2.0000e-
004
11.0467
Total 1.1100e-
003
0.0101 8.4700e-
003
6.0000e-
005
7.7000e-
004
7.7000e-
004
7.7000e-
004
7.7000e-
004
0.0000 10.9814 10.9814 2.1000e-
004
2.0000e-
004
11.0467
Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 23 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
6.1 Mitigation Measures Area
6.0 Area Detail
5.3 Energy by Land Use - Electricity
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
Unrefrigerated
Warehouse-No
Rail
237522 57.3145 3.5600e-
003
4.3000e-
004
57.5318
Total 57.3145 3.5600e-
003
4.3000e-
004
57.5318
Unmitigated
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
Unrefrigerated
Warehouse-No
Rail
237522 57.3145 3.5600e-
003
4.3000e-
004
57.5318
Total 57.3145 3.5600e-
003
4.3000e-
004
57.5318
Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 24 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 0.4175 1.0000e-
005
1.3000e-
003
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 2.5400e-
003
2.5400e-
003
1.0000e-
005
0.0000 2.7100e-
003
Unmitigated 0.4175 1.0000e-
005
1.3000e-
003
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 2.5400e-
003
2.5400e-
003
1.0000e-
005
0.0000 2.7100e-
003
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory tons/yr MT/yr
Architectural
Coating
0.0475 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
0.3700 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Landscaping 1.2000e-
004
1.0000e-
005
1.3000e-
003
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 2.5400e-
003
2.5400e-
003
1.0000e-
005
0.0000 2.7100e-
003
Total 0.4175 1.0000e-
005
1.3000e-
003
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 2.5400e-
003
2.5400e-
003
1.0000e-
005
0.0000 2.7100e-
003
Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 25 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
7.1 Mitigation Measures Water
7.0 Water Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory tons/yr MT/yr
Architectural
Coating
0.0475 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
0.3700 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Landscaping 1.2000e-
004
1.0000e-
005
1.3000e-
003
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 2.5400e-
003
2.5400e-
003
1.0000e-
005
0.0000 2.7100e-
003
Total 0.4175 1.0000e-
005
1.3000e-
003
0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 2.5400e-
003
2.5400e-
003
1.0000e-
005
0.0000 2.7100e-
003
Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 26 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
Total CO2 CH4 N2O CO2e
Category MT/yr
Mitigated 81.8990 0.7761 0.0188 106.8959
Unmitigated 81.8990 0.7761 0.0188 106.8959
7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
Unrefrigerated
Warehouse-No
Rail
23.6754 /
0
81.8990 0.7761 0.0188 106.8959
Total 81.8990 0.7761 0.0188 106.8959
Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 27 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
Unrefrigerated
Warehouse-No
Rail
23.6754 /
0
81.8990 0.7761 0.0188 106.8959
Total 81.8990 0.7761 0.0188 106.8959
Mitigated
8.1 Mitigation Measures Waste
8.0 Waste Detail
Total CO2 CH4 N2O CO2e
MT/yr
Mitigated 19.5359 1.1545 0.0000 48.3992
Unmitigated 19.5359 1.1545 0.0000 48.3992
Category/Year
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 28 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
8.2 Waste by Land Use
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
Unrefrigerated
Warehouse-No
Rail
96.24 19.5359 1.1545 0.0000 48.3992
Total 19.5359 1.1545 0.0000 48.3992
Unmitigated
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
Unrefrigerated
Warehouse-No
Rail
96.24 19.5359 1.1545 0.0000 48.3992
Total 19.5359 1.1545 0.0000 48.3992
Mitigated
9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 29 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
11.0 Vegetation
10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type
Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type
User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2020.4.0 Date: 12/22/2021 2:24 PMPage 30 of 30
Summit Avenue Warehouse - San Bernardino-South Coast County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied