Riverside City Council
January 25, 2022

Sycamore Hills Distribution Center Project

Final Environmental Impact Report (FEIR)

Revised Appendix H – Greenhouse Gas Analysis

Greenhouse Gas Analysis for the
Sycamore Hills Distribution Project
Riverside, California

Prepared for
Ruth Villalobos & Associates, Inc.
3602 Inland Empire Boulevard, Suite C310
Ontario, CA 91764

Prepared by
RECON Environmental, Inc.
3111 Camino del Rio North, Suite 600
San Diego, CA 92108
P 619.308.9333

RECON Number 9309
October 6, 2020
Revised August 10, 2021

Jessica Fleming, Air Quality Analyst

Greenhouse Gas Analysis
Sycamore Hills Distribution Project
i

TABLE OF CONTENTS
Acronyms and Abbreviations .................................................................................. ii Executive Summary ................................................................................................... 1

1.0 Introduction ..................................................................................................... 2

1.1 Understanding Global Climate Change ............................................................. 2

1.2 Greenhouse Gases of Primary Concern ............................................................. 3

2.0 Project Description ......................................................................................... 4

3.0 Existing Conditions......................................................................................... 7

3.1 Environmental Setting ....................................................................................... 7

3.2 Regulatory Background ...................................................................................... 9

4.0 Significance Criteria and Analysis Methodologies ................................ 18

4.1 Determining Significance ................................................................................. 18

4.2 Calculation Methodology .................................................................................. 19

5.0 GHG Emission Calculations ........................................................................ 24

6.0 GHG Impact Analysis ................................................................................... 25

7.0 Conclusions ..................................................................................................... 39

8.0 References Cited ............................................................................................ 40

FIGURES
1: Regional Location .......................................................................................................... 5 2: Project Location on Aerial Photograph ......................................................................... 6 3: Site Plan ........................................................................................................................ 8 TABLES
1: Global Warming Potentials and Atmospheric Lifetimes (years) ................................ 4 2: California GHG Emissions By Sector in 1990, 2010, and 2017 ................................... 9 3: City of Riverside GHG Emissions in 2010.................................................................... 9 4: Construction Phases and Equipment ..........................................................................20 5: Project Trip Generation and Trip Length ................................................................... 21 6: Riverside Public Utilities Intensity Factors ................................................................23 7: Summary of Project GHG Emissions (metric tons per year) .....................................24 8: Project Consistency with RRG-CAP GHG Reduction Measures................................. 27

ATTACHMENT
1: CalEEMod Output
Greenhouse Gas Analysis
Sycamore Hills Distribution Project
ii
Acronyms and Abbreviations
AB Assembly Bill
BAU business as usual
CAFE Corporate Average Fuel Economy
CalEEMod California Emissions Estimator Model
CALGreen California Green Building Standards Code
CalRecycle California Department of Resources Recycling and Recovery CAP Climate Action Plan
CAPCOA California Air Pollution Control Officers Association CARB California Air Resources Board
CBC California Building Code
CEC California Energy Commission
CEQ Council on Environmental Quality
CEQA California Environmental Quality Act
CH4 methane
City City of Riverside
CO2 carbon dioxide
EO Executive Order
EPA Environmental Protection Agency
GHG greenhouse gas
GWP global warming potential
IPCC Intergovernmental Panel on Climate Change
MMT CO2E million metric tons carbon dioxide equivalent
MPF Marijuana Production Facility
mpg miles per gallon
MPO Metropolitan Planning Organizations
MT CO2E metric tons of carbon dioxide equivalent
MWh megawatt-hour
N2O nitrous oxide
Project Sycamore Hills Distribution Center
RPS Renewables Portfolio Standard
RRG Riverside Restorative Growthprint
RRG-CAP Riverside Restorative Growthprint-Climate Action Plan RRG-EPAP Riverside Restorative Growthprint-Economic Prosperity Action Plan SB Senate Bill
SCAG Southern California Association of Governments
SCAQMD South Coast Air Quality Management District
U.S. EPA U.S. Environmental Protection Agency
WRCOG Western Riverside Council of Governments

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Executive Summary
The Sycamore Hills Distribution Center project (project) is located north of Alessandro Boulevard and east of Barton Street in the city of Riverside, California (Assessor Parcel Numbers 263-060-022, 263-060-024, 263-060-026). The project proposes subdividing the site into two parcels (Parcels 1 and 2), and three lettered parcels (Parcels A, B, and C). Each parcel is proposed to be developed with a high cube transload short-term warehouse building (Buildings A and B). Building A, a 400,000-square-foot warehouse, would be constructed on Parcel 1. Building B, a 203,100 -square-foot warehouse, would be constructed on Parcel 2.

Associated improvements include parking, fire lanes, fencing and walls (including retaining walls), landscaping, and water quality treatment areas. Parcels A and Parcel B consist of existing Restricted Property of natural land. Parcel C would include a trailhead peaking lot for access to the Sycamore Canyon Wilderness Park.

The City of Riverside (City) has adopted the Riverside Restorative Growthprint (RRG), which combines two plans: the Economic Prosperity Action Plan (RRG -EPAP) and the Climate Action Plan (RRG-CAP) (City of Riverside 2016). However, the City has not adopted its own greenhouse gas (GHG) emissions thresholds of significance for the California Environmental Quality Act ( CEQA). This analysis evaluates the significance of the proposed project in accordance with CEQA and guidance from the South Coast Air Quality Management District (SCAQMD). This report evaluates the significance of the project in terms of (1) its contribution of GHGs to cumulative statewide emissions, and (2) whether the project would conflict with local and/or state regulations, plans, and policies adopted to reduce GHG emissions.

The significance of the project’s GHG emissions was assessed based on screening levels recommended by the SCAQMD’s Interim CEQA GHG Significance Thresholds (SCAQMD 2008). Consistent with the SCAQMD guidance, the recommended tiered approach for land use dev elopment projects in SCAQMD jurisdiction is assessment against the applicable screening levels. As the project is not exempt from CEQA and is not part of an approved local plan, project emissions are assessed against the industrial 10,000 metric tons of ca rbon dioxide equivalent (MT CO2E) screening level. This screening level is intended to exempt projects that are too small to have significant impacts from further analysis. This threshold is based on the concept of establishing a 90 percent GHG emission ca pture rate. Following rationale presented in the CAPCOA Guidance, the aggregate emissions from all projects with individual annual emissions that are equal to or less than the identified capture rate would not impede achievement of the state GHG emissions reduction targets codified by Assembly Bill 32 (2006) and Senate Bill 32 (2016), and impacts under CEQA would, therefore, be less than cumulatively considerable.

GHG emissions would result from construction and operation of the project. Construction activities emit GHGs primarily through the combustion of fuels in on- and off-road equipment and vehicles. Operational emissions include mobile, energy (electricity and natural gas), area (landscape maintenance equipment), water and wastewater, and solid waste sources. As shown calculated in this analysis, the project would result in a net increase of 7,4057,587 MT Greenhouse Gas Analysis
Sycamore Hills Distribution Project

CO2E per year. As project emissions would be less than the 10,000 MT CO2E screening level, GHG emissions impacts would be less than significant. Additionally, the project would be consistent with applicable RRG -CAP measure s, and is in line with the GHG reductions needed to achieve the 2050 GHG emission reduction targets identified by EO S -3-05.

Therefore, GHG impacts would be less than significant.

1.0 Introduction
This report ev aluates the greenhouse gas (GHG) emissions associated with the proposed Sycamore Hills Distribution Center project (project). The purpose of this report is to evaluate project-related construction and operational emissions and determine the level of GHG impacts as a result of constructing and operating the project.

1.1 Understanding Global Climate Change
To evaluate the incremental effect of the project on statewide GHG emissions and global climate change, it is important to have a basic understanding of th e nature of the global climate change problem. Global climate change is a change in the average weather of the earth, which can be measured by wind patterns, storms, precipitation, and temperature. The earth’s climate is in a state of constant flux with pe riodic warming and cooling cycles.

Extreme periods of cooling are termed “ice ages,” which may then be followed by extended periods of warmth. For most of the earth’s geologic history, these periods of warming and cooling have been the result of many complicated interacting natural factors that include volcanic eruptions that spew gases and particles (dust) into the atmosphere; the amount of water, vegetation, and ice covering the earth’s surface; subtle changes in the earth’s orbit; and the amount of energy released by the sun (sun cycles). However, since the beginning of the Industrial Revolution around 1750, the average temperature of the earth has been increasing at a rate that is faster than can be explained by natural climate cycles alone.

With the Ind ustrial Revolution came an increase in the combustion of carbon -based fuels such as wood, coal, oil, natural gas, and biomass. Industrial processes have also created emissions of substances not found in nature. This in turn has led to a marked increase in the emissions of gases shown to influence the world’s climate. These gases, termed “greenhouse” gases, influence the amount of heat trapped in the earth’s atmosphere. Recently observed increased concentrations of GHGs in the atmosphere appear to be related to increases in human activity. Therefore, the current cycle of “global warming” is believed to be largely due to human activity. Of late, the issue of global warming or global climate change has arguably become the most important and widely debated environmental issue in the United States and the world. Because it is believed that the increased GHG concentrations around the world are related to human activity and the collective of human actions taking place throughout the world, it is quintessentially a global or cumulative issue.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

1.2 Greenhouse Gases of Primary Concern
There are numerous GHGs, both naturally occurring and manmade. Each GHG has variable atmospheric lifetime and global warming potential (GWP). The atmospheric lifetime of the gas is the average time a molecule stays stable in the atmosphere. Most GHGs have long atmospheric lifetimes, staying in the atmosphere hundreds or thousands of years. GWP is a measure of the potential for a gas to trap heat and warm the atmosphere. Although GWP is related to its atmospheric lifetime, many other factors including chemical reactivity of the gas also influence GWP. GWP is reported as a unitless factor representing the potential for the gas to affect global climate relative to the potential of carbon dioxide (CO 2). Because CO2
is the reference gas for establishing GWP, by definition its GWP is 1. Although methane (CH4) has a shorter atmospheric lifetime than CO2, it has a 100-year GWP of 28; this means that CH4 has 28 times more effect on global warming than CO 2 on a molecule- by-molecule basis.

The GWP is officially defined as (U.S. Environmental Protection Agency [U.S. EPA] 2010):

The cumulative radiative forcing—both direct and indirect effects—integrated over a period of time from the emission of a unit mass of gas relative to some reference gas.

GHG emissions estimates are typically represented in terms of equivalent metric tons of CO2 (MT CO2E). CO2E emissions are the product of the amount of each gas by its GWP. The effects of several GHGs may be discussed in terms of MT CO2E and can be summed to represent the total potential of these gases to warm the global climate. Table 1 summarizes some of the most common GHGs.

It should be noted that the U.S. EPA and other organizations update the GWP values they use occasionally. This change can be due to updated scientific estimates of the energy absorption or lifetime of the gases or to changing atmospheric co ncentrations of GHGs that result in a change in the energy absorption of one additional ton of a gas relative to another.

The GWPs shown in Table 1 are the most current. However, it should be noted that in the California Emissions Estimator Model (CalEEMod), which is the model used in this analysis to calculate emission, CH4 has a GWP of 25 and nitrous oxide (N 2O) has a GWP of 298, consistent with the Scoping Plan.

All of the gases in Table 1 are produced by both biogenic (natural) and anthropogenic (human) sources. These are the GHGs of primary concern in this analysis. CO 2 would be emitted by the project due to the combustion of fossil fuels in vehicles (including construction), from electricity generation and natural gas consumption, water use, and from solid waste disposal.

Smaller amounts of CH4 and N2O would be emitted from the same project operations.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 1
Global Warming Potentials and Atmospheric Lifetimes
(years)
Gas
Atmospheric Lifetime
(years) 100-year GWP 20-year GWP
Carbon dioxide (CO2) 50–200 1 1
Methane (CH4) 12.4 25/28* 84
Nitrous oxide (N2O) 121 298/265* 264
HFC-23 222 12,400 10,800
HFC-32 5.2 677 2,430
HFC-125 28.2 3,170 6,090
HFC-134a 13.4 1,300 3,710
HFC-143a 47.1 4,800 6,940
HFC-152a 1.5 138 506
HFC-227ea 38.9 3,350 5,360
HFC-236fa 242 8,060 6,940
HFC-43-10mee 16.1 1,650 4,310
CF4 50,000 6,630 4,880
C2F6 10,000 11,100 8,210
C3F8 2,600 8,900 6,640
C4F10 2,600 9,200 6,870
c-C4F8 3,200 9,540 7,110
C5F12 4,100 8,550 6,350
C6F14 3,100 7,910 5,890
SF6 3,200 23,500 17,500
SOURCE: Intergovernmental Panel on Climate Change (IPCC) 2007, 2014.

GWP = growth warming potential
*The CH4 and N2O 100-year GWPs included in CalEEMod are 25 and 298, respectively, from the IPCC Fourth Assessment Report. All other values are from the current Fifth Assessment Report.

2.0 Project Description
The proposed project is to con struct an industrial warehouse development on three parcels (Assessor Parcel Numbers 263- 060-022, 263-060-024, 263-060-026], totaling 48.64 gross acres. The property is located at the northeast corner of Barton Street and Alessandro Boulevard in the city of Riverside, immediately south of the Sycamore Canyon Wilderness Park. The property is spread in an east to west direction with natural rolling land descending gradually from a west to east direction. There are two jurisdictional drainages on the site .

The undeveloped parcels are covered with a low to moderate growth of vegetation cover consisting of natural grasses and weeds with some granitic roc k outcrops. Figure 1 shows the regional location. Figure 2 shows an aerial photograph of the project site and vicinity.

FIGURE 1
Regional Location
kj
Box Springs
Mountain
Reserve
Norton
Younglove
Reserve
Ronald W Caspers
Wilderness PK
Santa Ana
River Reg Park
Lake
Perris State
Rec Area
San
Bernardino NF
Cleveland NF
Prado Flood
Control Basin
Perris
ReservoirLake
Mathews
Railroad
Canyon
Reservoir
Lake Elsinore
S
a
n
J
u
a
n
C
re
e
k
A r r o y o T r a b u c o
C o l o r a d o R i v e r A q u e d u c t
M
W
D
L
o
w
e
r
F
e
e
d
e
r
L y t l e
C r e e k
S a n J a c i n t o R i v e r
C
a
l i f or n i a
A
q
u
e
d
u
c
t
S a n t a A n a
R
i v e
r
M W D U p p
e
r
F e e d er
S a n t a A n a R
i v
e
r
El Cerrito
Glen Avon
Home Gardens
Mira Loma
Pedley
Sunnyslope
Bloomington
Highgrove
Lakeview
March
AFB
Mentone
Muscoy
Nuevo
Rubidoux
Running Springs
Woodcrest
Lakeland
Village
Homeland
Quail Valley
Romoland
Sedco
Hills
Sun City Winchester
UV66
UV259
UV74
UV18
UV79
UV330
UV30
UV60
UV91
§¨¦215
§¨¦10
§¨¦15

O R A N G E

C O U N T Y

R I V E R S I D E

C O U N T Y
S A N

B E R N A R D I N O

C O U N T Y
Beaumont
Calimesa
Canyon
Lake
Colton
Corona
Fontana
Grand
Terrace
Hemet
Highland
Lake Elsinore
Loma
Linda
Moreno Valley
Murrieta
Norco
Ontario
Perris
Rancho
Cucamonga
Rancho Santa
Margarita
Redlands
Rialto
Riverside
San
Bernardino
San
Jacinto
Yucaipa
kj
Box Springs
Mountain
Reserve
Norton
Younglove
Reserve
Ronald W Caspers
Wilderness PK
Santa Ana
River Reg Park
Lake
Perris State
Rec Area
San
Bernardino NF
Cleveland NF
Prado Flood
Control Basin
Perris
ReservoirLake
Mathews
Railroad
Canyon
Reservoir
Lake Elsinore
S
a
n
J
u
a
n
C
re
e
k
A r r o y o T r a b u c o
C o l o r a d o R i v e r A q u e d u c t
M
W
D
L
o
w
e
r
F
e
e
d
e
r
L y t l e
C r e e k
S a n J a c i n t o R i v e r
C
a
l i f or n i a
A
q
u
e
d
u
c
t
S a n t a A n a
R
i v e
r
M W D U p p
e
r
F e e d er
S a n t a A n a R
i v
e
r
El Cerrito
Glen Avon
Home Gardens
Mira Loma
Pedley
Sunnyslope
Bloomington
Highgrove
Lakeview
March
AFB
Mentone
Muscoy
Nuevo
Rubidoux
Running Springs
Woodcrest
Lakeland
Village
Homeland
Quail Valley
Romoland
Sedco
Hills
Sun City Winchester
UV66
UV259
UV74
UV18
UV79
UV330
UV30
UV60
UV91
§¨¦215
§¨¦10
§¨¦15

O R A N G E

C O U N T Y

R I V E R S I D E

C O U N T Y
S A N

B E R N A R D I N O

C O U N T Y
Beaumont
Calimesa
Canyon
Lake
Colton
Corona
Fontana
Grand
Terrace
Hemet
Highland
Lake Elsinore
Loma
Linda
Moreno Valley
Murrieta
Norco
Ontario
Perris
Rancho
Cucamonga
Rancho Santa
Margarita
Redlands
Rialto
Riverside
San
Bernardino
San
Jacinto
Yucaipa
0 5 Miles [
M:\JOBS5\9309\common_gis\fig1.mxd 12/17/2018 fmm

SAN DIEGO

RIVERSIDE

SAN BERNARDINO
ORANGE
MEXICO
Project Locationkj
FIGURE 2
Project Location on Aerial Photograph
BART
ON
ST

AVENIDA MUNOZ
VISTA
GRANDE
DR

PLANADA CT

AVENIDA HACIENDA

ALESSANDRO BLVD
CALLE
VISTA
DR
EL P
ASEO
RD

LOMA SOLA
RANCHO
VISTA
RD
BART
ON
ST

AVENIDA MUNOZ
VISTA
GRANDE
DR

PLANADA CT

AVENIDA HACIENDA

ALESSANDRO BLVD
CALLE
VISTA
DR
EL P
ASEO
RD

LOMA SOLA
RANCHO
VISTA
RD
Image Source: Nearmap (flown September 2018)
0 400 Feet [
Project Boundary
M:\JOBS5\9309\common_gis\fig2.mxd 12/17/2018 fmm
Greenhouse Gas Analysis
Sycamore Hills Distribution Project

The project proposes subdividing the site into two parcels (Parcels 1 and 2), and three lettered parcels (Parcels A, B, and C). Each parcel is proposed to be developed with a high cube transload short-term warehouse building (Buildings A and B). Building A, a 400,000-square- foot warehouse, would be constructed on Parcel 1. Building B, a 203,100 -square-foot warehouse, would be constructed on Parcel 2. Associated improvements include parking, fire lanes, fencing and walls (including retaining walls), landscap ing, and water quality treatment areas.

Parcels A and Parcel B consist of existing Restricted Property of natural land, with a supporting jurisdictional feature, totaling approximately 11.6 acres. A 0.67 -acre driveway would be constructed through the Res tricted Property to provide street access from Alessandro Boulevard to Parcel 1, which would reduce the Restricted Property to 10.93 acres.

However, 1.44 acres would be added to Parcel A to mitigate this loss, resulting in a total of

12.37 acres of Restric ted Property (net gain of 0.77 acre). A Conservation Easement is proposed to be placed over the amended 12.37 acres of Restricted Property.

A trailhead parking lot is proposed on Parcel C, totaling 1.18 acres, for access to the Sycamore Canyon Wilderness Park. Improvements include a parking lot, sidewalk, shade structure, bike rack, drinking fountain, fencing, and a Fire Department access gate. Parcel C will be dedicated to the City. Figure 3 shows the site plan.

3.0 Existing Conditions

3.1 Environmental Setting

3.1.1 State and Regional GHG Inventories
The California Air Resources Board (CARB) performs statewide GHG inventories. The inventory is divided into nine broad sectors of economic activity: agriculture, commercial, electricity generation, forestr y, high GWP emitters, industrial, recycling and waste, residential, and transportation. Emissions are quantified in million metric tons of CO 2 equivalent (MMT CO2E). Table 2 shows the estimated statewide GHG emissions for the years 1990, 2010, and 2017. Although annual GHG inventory data is available for years 2000 through 2017, the years 1990, 2010, and 2017 are highlighted in Table 2 because 1990 is the baseline year for established reduction targets, 2010 corresponds to the same years for which inventory data for the City is available, and 2017 is the most recent data available.

0 ?-2%6?

?QRV?JUDSKLFV?ILJDL 

 IPP
Map Source: HPA Architecture
FIGURE 3
Site Plan
Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 2
California GHG Emissions By Sector in 1990, 2010, and 2017 Sector
19901 Emissions
in MMT CO2E
(% total)2
20103 Emissions
in MMT CO2E
(% total)2
20173 Emissions in
MMT CO2E
(% total)2
Electricity Generation 110.5 (25.7%) 90.6 (20.2%) 62.6 (14.8%) Transportation 150.6 (35.0%) 170.2 (38.0%) 174.3 (41.1%) Industrial 105.3 (24.4%) 101.8 (22.7%) 101.1 (23.8%)
Commercial 14.4 (3.4%) 20.1 (4.5%) 23.3 (5.5%)
Residential 29.7 (6.9%) 32.1 (7.2%) 30.4 (7.2%)
Agriculture & Forestry 18.9 (4.4%) 33.7 (7.5%) 32.4 (7.6%) Not Specified 1.3 (0.3%) -- --
TOTAL4 430.7 448.5 424.1
SOURCE: CARB 2007 and 2019.
11990 data was obtained from the CARB 2007 source and are based on IPCC fourth assessment report GWPs.
2Percentages may not total 100 due to rounding.
32010 and 2017 data was retrieved from the CARB 2019 source and are based on IPCC fourth assessment report GWPs.
4Totals may vary due to independent rounding.

As shown in Table 2, statewide GHG source emissions totaled approximately 431 MMT CO2E in 1990, 449 MMT CO2E in 2010, and 424 MMT CO2E in 2017. Many factors affect year-to- year changes in GHG emissions, including economic activity, demographic influences, environmental conditions such as drought, and the impact of regulatory efforts to control GHG emissions. As shown, transportation-related emissions consistently contribute to the most GHG emissions.

A City of Riverside emissions inventory was prepared for baseline year 2010 as a part of the City’s CAP. The total community -wide GHG emissions in 2010 were 2,617,540 MT CO 2E.

Table 3 summarizes the sources and quantities of community emissions. The largest source of emissions is transportation.

Table 3
City of Riverside GHG Emissions in 2010
Sector
2010 GHG Emissions
(MT CO2E)
Residential Energy Use 481,903 (18.4%)
Commercial/Industrial
Energy Use
722.321 (27.6%)
Transportation 1,358,647 (51.9%)
Solid Waste 54,669 (2.1%)
TOTAL 2,617,540
SOURCE: City of Riverside 2016.

3.2 Regulatory Background
In response to rising concern associated with increasing GHG emissions and global climate change impacts, several plans and regulations have been adopted at the international, national, and state levels with the aim of reducing GHG emissions. The following is a discussion of the federal, state, and local plans and regulations most applicable to the project.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

3.2.1 Federal
The federal government, U.S. EPA, and other federal agencies have many federal level programs and projects to reduce GHG emissions. In June 2012, the Council on Environmental Quality (CEQ) revised the Federal Greenhouse Gas Accounting and Reporting Guidance originally issued in October 2010. The CE Q guidance identifies ways in which federal agencies can improve consideration of GHG emissions and climate change for federal actions.

The guidance states that National Environmental Policy Act documents should provide decision makers with relevant and ti mely information and should consider (1) GHG emissions of a Proposed Action and alternative actions and (2) the relationship of climate change effects to a Proposed Action or alternatives. Specifically, if a Proposed Action would be reasonably anticipated to cause direct emissions of 25,000 MT CO 2E GHG emissions on an annual basis, agencies should consider this as an indicator that a quantitative assessment may be meaningful to decision makers and the public (CEQ 2012).

3.2.1.1 U.S. Environmental Protection Agency
In 2009, the U.S. EPA issued its science -based finding that the buildup of heat -trapping GHGs in the atmosphere endangers public health and welfare. The “Endangerment Finding” reflects the overwhelming scientific evidence on the causes and impacts of climate change. It was made after a thorough rulemaking process considering thousands of public comments, and was upheld by the federal courts.

The U.S. EPA has many federal level programs and projects to reduce GHG emissions. The U.S. EPA provides technical expertise and encourages voluntary reductions from the private sector. One of the voluntary programs applicable to the project is the Energy Star program.

Energy Star products such as appliances, building products, heating and cooling equipment, and other energy-efficient equipment will be utilized by the project.

Energy Star is a joint program of U.S. EPA and the U.S. Department of Energy, which promotes energy-efficient products and practices. Tools and initiatives include the Energy Star Portfolio Manager, which helps track and assess energy and water consumption across an entire portfolio of buildings, and the Energy Star Most Efficient 2020, which provides information on exceptional products which represent the leading edge in energy -efficient products in the year 2020 (U.S. EPA 2020a).

The U.S. EPA also collaborates with the public sector, including states, tribes, localities and resource managers, to encourage smart growth, sustainability preparation, and renewable energy and climate change preparation. These initiatives include the Clean Energy – Environment State Partnership Program, the Climate Ready Water Utilities Initia tive, the Climate Ready Estuaries Program, and the Sustainable Communities Partnership (U.S. EPA 2020b).

Additionally, in 2004, the U.S. EPA introduced the SmartWay program, which is a partnership between the U.S. EPA and the freight industry to reduce fue l consumption and emissions. The program provides a system for tracking and documenting information about Greenhouse Gas Analysis
Sycamore Hills Distribution Project

fuel use and freight emissions across supply chains; helps companies identify more efficient carriers, transportation modes, equipment, and operations to improve sustainability and lower costs from goods movement, supports global energy security and offsets environmental risk; and reduces freight transportation -related emissions by accelerating the use of advanced fuel-saving technologies. SmartWay is supported by major transportation industry associations, environmental groups, state and local governments, international agencies, and the corporate community.

3.2.1.2 Corporate Average Fuel Economy Standards
The project would generate vehicle trips. These vehicles would consume fuel and would result in GHG emissions. The federal Corporate Average Fuel Economy (CAFE) standards determine the fuel efficiency of certain vehicle classes in the U.S. The first phase of the program applied to passenger cars, new light-duty trucks, and medium-duty passenger cars with model years 2012 through 2016, and required these vehicles to achieve a standard equivalent to 35.5 miles per gallon (mpg). The second phase of the program applies to model years 2017 through 2025 and increased the standards to 54.5 mpg. Separate standards were also established for medium- and heavy-duty vehicles. The first phase applied to model years 2014 through 2018 and the second phase applies to model years 2018 through 2027. With improved gas mileage, fewer gallons of transportation fuel would be combusted to travel the same distance, thereby reducing nationwide GHG emissions associated with vehicle travel.

3.2.2 State
The State of California has adopted a number of plans and regulations aimed at identifying statewide and regional GHG emissions caps, GHG emissions reduction targets, and actions and timelines to achieve the target GHG reductions.

3.2.2.1 Executive Orders and Statewide GHG Emission Targets Executive Order S-3-05
This Executive Order (EO) established the following GHG emission reduction targets for the State of California:
• by 2010, reduce GHG emissions to 2000 levels;
• by 2020, reduce GHG emissions to 1990 levels;
• by 2050, reduce GHG emissions to 80 percent below 1990 levels.

This EO also directs the secretary of the California Environmental Protection Agency to oversee the efforts made to reach these targets, and to prepare biannual reports on the progress made toward meeting the targets and on the impacts to California related to global warming, including impacts to water supply, public health, agriculture, the coastline, and forestry. With regard to impacts, the report shall also prepare and report on mitigation and Greenhouse Gas Analysis
Sycamore Hills Distribution Project

adaptation plans to combat the impacts. The first C limate Action Team Assessment Report was produced in March 2006, and has since been updated every two years.

Executive Order B-30-15
This EO, issued on April 29, 2015, establishes an interim GHG emission reduction goal for the state of California by 2030 of 40 percent below 1990 levels. This EO also directed all state agencies with jurisdiction over GHG emitting sources to implement measures designed to achieve the new interim 2030 goal, as well as the pre-existing, long-term 2050 goal identified in EO S -3-05. Additionally, this EO directed CARB to update its Climate Change Scoping Plan to address the 2030 goal.

3.2.2.2 California Global Warming Solutions Act
In response to EO S-3-05, the California Legislature passed AB 32, the California Global Warming Solutions Act of 2006, and thereby enacted Sections 38500–38599 of the California Health and Safety Code. The heart of AB 32 is its requirement that CARB establish an emissions cap and adopt rules and regulations that would reduce GHG emissions to 1990 levels by 2020. AB 32 also required CARB to adopt a plan by January 1, 2009 indicating how emission reductions would be achieved from significant GHG sources via regulations, market mechanisms, and other actions.

In 2008, CARB es timated that annual statewide G HG emissions were 427 MMT CO 2E in
1990 and would reach 596 MMT CO2E by 2020 under a business as usual ( BAU) condition (CARB 2008). To achieve the mandate of AB 32, CARB determined that a 169 MMTCO2E (or approximate 28.5 percent) reduction in BAU emissions was needed by 2020. In 2010, CARB prepared an updated 2020 forecast to account for the recession and slower forecasted growth.

CARB determined that the economic downturn reduced the 2020 BAU by 55 MMT CO2E; as a result, achieving the 1990 emissions level by 2020 would require a reduction in GHG emissions of 21.7 (not 28.5) percent from the 2020 BAU. California has been on track to achieve 1990 levels, and based on the GHG inventories shown in Table 2, achieved the goal by 2017.

Approved in September 2016, Senate Bill ( SB) 32 updates the California Global Warming Solutions Act of 2006 and enacts EO B-30-15. Under SB 32, the state would reduce its GHG emissions to 40 percent below 1990 levels by 2030. This is equivalent to an emissions level of approximately 260 MMT CO 2E for 2030. In implementing the 40 percent reduction goal, CARB is required to prioritize emissions reductions to consider the social costs of the emissions of GHGs; where “social costs” is defined as “an estimate of the economic damages, including, but not limited to, changes in net agricultural productivity; impacts to public health; climate adaptation impacts, such as property damages from increased flood risk; and changes in energy system costs, per metric ton of greenhouse gas emission per year.”

3.2.2.3 Climate Change Scoping Plan
As directed by the California Global Warming Solutions Act of 2006, in 2008, CARB adopted the Climate Change Scoping Plan: A Framework for Change (Scoping Plan), which identifies Greenhouse Gas Analysis
Sycamore Hills Distribution Project

the main strategies California will implement to achieve the GHG reductions necessary to reduce forecasted business as usual (BAU) emissions i n 2020 to the state’s historic 1990 emissions level (CARB 2008). In November 2017, CARB released the 2017 Climate Change Scoping Plan Update, the Strategy for Achieving California’s 2030 Greenhouse Gas Target (2017 Scoping Plan; CARB 2017). The 2017 Scoping Plan identifies state strategies for achieving the state’s 2030 interim GHG emissions reduction target codified by SB 32.

Measures under the 2017 Scoping Plan Scenario build on existing programs such as the Low Carbon Fuel Standard, Advanced Clean Cars P rogram, Renewables Portfolio Standard (RPS), Sustainable Communities Strategy, Short -Lived Climate Pollutant Reduction Strategy, and the Cap-and-Trade Program. Additionally, the 2017 Scoping Plan proposes new policies to address GHG emissions from natural and working lands.

3.2.2.4 Regional Emissions Targets – Senate Bill 375
SB 375, the 2008 Sustainable Communities and Climate Protection Act, was signed into law in September 2008 and requires CARB to set regional targets for reducing passenger vehicle GHG emissions in accordance with the Scoping Plan. The purpose of SB 375 is to align regional transportation planning efforts, regional GHG reduction targets, and fair -share housing allocations under state housing law. SB 375 requires Metropolitan Planning Organizations (MPOs) to adopt a Sustainable Communities Strategy or Alternative Planning Strategy to address GHG reduction targets from cars and light-duty trucks in the context of that MPO’s Regional Transportation Plan. Southern California Association of Governments (SCAG) is the region’s MPO. In 2018, CARB set targets for the SCAG region of an 8 percent reduction in GHG emissions per capita from automobiles and light-duty trucks compared to 2005 levels by 2020 and a 19 percent reduction by 2035. These targets are periodically reviewed and updated.

3.2.2.5 Renewables Portfolio Standard (RPS)
The RPS promotes diversification of the state’s electricity supply and decreased reliance on fossil fuel energy sources. Originally adopted in 2002 with a goal to achieve a 20 percent renewable energy mix by 2020 (referred to as the “Initial RPS”), the goal has been accelerated and increased by EOs S-14-08 and S-21-09 to a goal of 33 percent by 2020. In April 2011, SB 2 (1X) codified California’s 33 percent RPS goal. I n September 2015, the California Legislature passed SB 350 , which increases California’s renewable energy mix goal to 50 percent by year 2030. SB 100 (2018) further increased the standard set by SB 350 establishing the RPS goal of 44 percent by the end of 2024, 52 percent by the end of 2027, and 60 percent by 2030. Renewable energy includes (but is not limited to) wind, solar, geothermal, small hydroelectric, biomass, anaerobic digestion, and landfill gas.

3.2.2.6 Assembly Bill 341 – Solid Waste Diversion
The Commercial Recycling Requirements mandate that businesses (including public entities) that generate 4 cubic yards or more of commercial solid waste per week and multi -family residential with five units or more arrange for recycling services. Businesses can take one or any combination of the following in order to reuse, recycle, compost, or otherwise divert solid Greenhouse Gas Analysis
Sycamore Hills Distribution Project

waste from disposal. Additionally, Assembly Bill (AB) 341 mandates that 75 percent of the solid waste generated be reduced, recycled, or composted by 2020.

3.2.2.7 California Code of Regulations, Title 24 – California Building Code
The California Code of Regulations, Title 24, is referred to as the California Building Code, or CBC. It consists of a compilation of several distinct standards and codes related to building construction, including plumbing, electrical, interior acoustics, energy efficiency, handicap accessibility, and so on. Of particular relevance to GHG reductions are the CBC’s energy efficiency and green building standards as outlined below. a. Title 24, Part 6 – Energy Efficiency Standards
The California Code of Regulations , Title 24, Part 6 is the California Energy Efficiency Standards for Residential and Nonresidential Buildings (also known as the California Energy Code). This c ode, originally enacted in 1978, establishes energy -efficiency standards for residential and non-residential buildings in order to reduce California’s energy consumption.

The Energy Code is updated periodically to incorporate and consider new energy -efficient technologies and methodologies as they become available, and incentives in the form of rebates and tax breaks are provided on a sliding scale for buildings achieving energy efficiency above the minimum standards.

The current version of the Energy Code , known as 2019 Title 24, or the 2019 Energy Code, became effective January 1, 2020. The Energy Code provides mandatory energy -efficiency measures as well as voluntary tiers for increased energy efficiency. The California Energy Commission (CEC), in conjun ction with the California Public Utilities Commission , has adopted a goal that all new residential and commercial construction achieve zero net energy by 2020 and 2030, respectively. It is expected that achievement of the zero net energy goal will occur via revisions to the Title 24 standards.

New construction and major renovations must demonstrate their compliance with the current Energy Code through submission and approval of a Title 24 Compliance Report to the local building permit review authority and the CEC. The compliance reports must demonstrate a building’s energy performance through use of CEC approved energy performance software that shows iterative increases in energy efficiency given the selection of various heating, ventilation, and air condit ioning; sealing; glazing; insulation; and other components related to the building envelope.
b. Title 24, Part 11 – California Green Building Standards The California Green Building Standards Code, referred to as CALGreen, was added to Title 24 as Part 11 first in 2009 as a voluntary code, which then became mandatory effective January 1, 2011 (as part of the 2010 CBC). The most recent 2019 CALGreen instit utes mandatory minimum environmental performance standards for all ground -up new construction of non -residential and residential structures. L ocal jurisdictions must enforce Greenhouse Gas Analysis
Sycamore Hills Distribution Project

the minimum mandatory Green Building Standards and may adopt additional amendments for stricter requirements.

The mandatory standards require:
• Outdoor water use requirements as outlined in local water efficient landscaping ordinances or current Model Water Efficient Landscape Ordinance standards, whichever is more stringent;
• Requirements for water conserving plumbing fixtures and fittings; • 65 percent construction/demolition waste diverted from landfills; • Infrastructure requirements for electric vehicle charging stations; • Mandatory inspections of energy systems to ensure optimal working efficiency; and • Requirements for low-pollutant emitting exterior and interior finish materials such as paints, carpets, vinyl flooring, and particleboards.

Similar to the reporting procedure for demonstrating Energy Code compliance in new buildings and major renovations, compliance with the CALGreen mandatory requirements must be demonstrated through completion of compliance forms and worksheets.

3.2.2.8 Heavy-Duty Truck Regulations
a. Tractor-Trailer GHG Regulation
CARB approved the Tractor‐Trailer GHG Regulation to significantly reduce GHG emissions produced by certain heavy -duty tractor- trailers. The tractors and trailers subject to this regulation must either use EPA SmartWay certified tractors and trailers, or retrofit their existing fleet with SmartWay verified technologies. The regulation applies primarily to owners of 53 -foot or longer box -type trailers, including both dry -van and refrigerated -van trailers, and owners of the heavy-duty tractors that pull them on California highways. These owners are responsible for replacing or retrofitting their affected vehicles with compliant aerodynamic technologies and low rolling resistance tires. Sleeper cab tractors model year 2011 and later must be SmartWay certified. All other tractors must use SmartWay verified low-rolling resistance tires. There are also requirements for trailers to have low rolling resistance tires and aerodynamic devices.
b. Phase 1 and 2 Heavy-Duty Vehicle Standards
CARB has adopted heavy-duty vehicle standards for GHG emissions from heavy-duty trucks and engines sold in California. It establishes GHG emission limits on truck and engine manufacturers and harmonizes with the U.S. EPA rule for new trucks and engines nationally. Existing heavy -duty vehicle regulations in California include engine criteria emission standards, tractor -trailer GHG requirements to implement SmartWay strategies (i.e., the Heavy-Duty Tractor-Trailer Greenhouse Gas Regulation), and in -use fleet retrofit requirements such as the Truck and Bus Regulation. In September 2011, the U.S. EPA adopted their new rule for heavy-duty trucks and engines. The U.S. EPA rule has compliance Greenhouse Gas Analysis
Sycamore Hills Distribution Project

requirements for new compression and spark ignition engines, as well as trucks from Class 2b through Class 8. Compliance requirements begin with model year 2014 with stringency levels increasing through model year 2018. The rule organizes truck compliance into three groupings, which include (a) heavy-duty pickups and vans; (b) vocational vehicles; and (c) combination tractors. The U.S. EPA rule does not regulate trailers.

CARB staff has worked jointly with the U.S. EPA and the National Highway Traffic Safety Administration on the next phase of federal GHG emission standards for medium- and heavy- duty vehicles, called federal Phase 2. The federal Phase 2 standards were built on the improvements in engine and vehicle efficiency required by the Phase 1 emission standards and represent a significant opportunity to achieve further GHG reductions for 2018 and later model year heavy-duty vehicles, including trailers.

3.2.3 Local

3.2.3.1 South Coast Air Quality Management District
The South Coast Air Quality Management District (SCAQMD) is the agency responsible for air quality planning and regulation in the South Coast Air Basin. The SCAQMD addresses the impacts to climate change of projects subject to SCAQMD permit as a lead agency if they are the only agency having discretionary approval for the project and acts as a responsible agency when a land use agency must also approve discretionary permits for the project. The SCAQMD acts as an expert commen ting agency for impacts to air quality. This expertise carries over to GHG emissions, so the agency helps local land use agencies through the development of models and emission thresholds that can be used to address GHG emissions.

In 2008, SCAQMD formed a Working Group to identify GHG emissions thresholds for land use projects that could be used by local lead agencies in the South Coast Air Basin. The Working Group developed several different options that are contained in the SCAQMD Draft Guidance Document – Interim CEQA GHG Significance Thresholds for Stationary Sources, Rules, and Plans, that could be applied by lead agencies. The working group met again in 2010 to review the guidance. The SCAQMD Board has not approved the thresholds; however, the Guidance Document provides substantial evidence supporting the approaches to significance of GHG emissions that can be considered by the lead agency in adopting its own threshold. The current interim thresholds consist of the following tiered approach (SCAQMD 2008, 2010):
• Tier 1 – The project is exempt from the California Environmental Quality Act (CEQA).
• Tier 2 – The project is consistent with an applicable regional GHG emissions reduction plan. If a project is consistent with a qualifying local GHG reduction plan, it does not have significant GHG emissions. • Tier 3 – Project GHG emissions represent an incremental increase below or mitigated to less than Significance Screening Levels, where o Residential/Commercial Screening Level
Greenhouse Gas Analysis
Sycamore Hills Distribution Project

 Option 1: 3,000 MT CO2E screening level for all residential/commercial land uses
 Option 2: Screening level thresholds for land use type acceptable if used consistently by a lead agency:
• Residential: 3,500 MT CO2E
• Commercial: 1,400 MT CO2E
• Mixed-Use: 3,000 MT CO2E
o 10,000 MT CO2E is the Permitted Industrial Screening Level • Tier 4 – The project achieves performance standards, where performance standards may include:
o Option 1: Percent emission reduction target. SCAQMD has no recommendation regarding this approach at this time.
o Option 2: The project would implement substantial early implementation of measures identified in the CARB’s Scoping Plan. This option has been folded into Option 3.
o Option 3: SCAQMD Efficiency Targets.
 2020 Targets: 4.8 MT CO
2E per service population (SP) for project-level
analyses or 6.6 MT CO 2E per SP for plan level analyses where service population includes residential and employment populations provided by a project.
 2035 Targets: 3.0 MT CO
2E per SP for project- level analyses or

4.1 MT CO2E per SP for plan level analyses.
• Tier 5 – Offsets along or in combination with the above target Significance Screening Level. Offsets must be provided for a 30 -year project life, unless the project life is limited by permit, lease, or other legally binding condition.

If a project complies with any one of these tiers, its impacts related to GHG emissions would be considered less than significant.

The SCAQMD’s interim thresholds used the Executive Order S-3-05 year 2050 goal as the basis for the Tier 3 screening level. Achieving the EO ’s objective would contribute to worldwide efforts to cap CO
2 concentrations at 450 parts per million, thus stabilizing global climate.

SCAQMD only has authority over GHG emissions from development projects that include air quality permits. At this time, it is unknown if the project would include stationary sources of emissions subject to SCAQMD permits. Notwithstanding, if the project requires a stationary permit, it would be subject to the applicable SCAQMD regulations.

SCAQMD Regulation XXVII, adopted in 2009 includes the following rules:
• Rule 2700 defines terms and post global warming potentials. • Rule 2701, SoCal Climate Solutions Exchange, establishes a voluntary program to encourage, quantify, and certify voluntary, high quality certified GHG emission reductions in the SCAQMD.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

• Rule 2702, GHG Reduction Program created a program to produce GHG emission reductions within the SCAQMD. The SCAQMD will fund projects through contracts in response to requests for proposals or purchase reductions from other parties.

3.2.3.2 General Plan
The City ’s General Plan (City of Riverside 2007) includes an Air Quality Element that provides a number of provisions and programs to reduce current pollution emissions, to require new development to include measures to comply with air quality standards and to address new air quality requirements. These programs also serve to reduce GHG emissions.

The Air Quality Element contains objectives and policies related to land use strategies, transportation, stationary sources, energy conservation, public education, multi - jurisdictional cooperation, and sustainability.

3.2.3.3 Riverside Restorative Growthprint
The Riverside Restorative Growthprint (RRG), adopted in January 2016, combines two plans:
the Economic Prosperity Action Plan (RRG-EPAP) and the Climate Action Plan (RRG-CAP) (City of Riverside 2016 ). The RRG -CAP provides a roadmap for the City to achieve GHG emission reductions through 2035, and establishes policies and priorities enabling the City to implement strategies that fulfill the requirements of state initiatives AB 32 and SB 375.

The RRG-CAP includes a baseline GHG inventory (for year 2007 and updated in 2010) for local government operations and for the community as a whole, and establishes emission reduction targets consistent with state law. In 2007, the City’s total community -wide emissions were estimated at 3,024,066 MT CO2E, while emissions resulting from municipal operations were responsible for approximately 122,525 MT CO2E. In 2010, the community- wide and municipal operations emissions had decreased by approximately 13.4 percent, mainly due to City actions to reduce the carbon intensity of its electric portfolio. The RRG - CAP aims to reduce GHG emissions to 26.4 percent below year 2007 baseline emissions (15 percent below year 2010 baseline emissions) by 2020 for an emissions target of 2,224,908 MT CO
2E; and 49 percent below year 2007 baseline emissions by 2035 for an emissions target of 1,542,274 MT CO2E.

The RRG-EPAP identifies opportunities where the community can reduce GHG emissions in a way that also advances economic growth and pr ovide meaningful benefit to the residents, employees, investors, and visitors to the City. While the RRG-CAP identifies GHG reduction measures and strategies, the RRG-EPAP identifies those measures and strategies that have the most potential to spur economic development.

4.0 Significance Criteria and Analysis
Methodologies

4.1 Determining Significance
Based on the CEQA Guidelines Appendix G, impacts related to GHG emissions would be Greenhouse Gas Analysis
Sycamore Hills Distribution Project

significant if the project would:

1. Generate GHG emissions, either directly or indirectly, that may have a significant impact on the environment; or

2. Conflict with the City’s CAP or an applicable plan, policy, or regulation adopted for the purpose of reducing the emission of GHGs.

The CEQ A Guidelines allow lead agencies to establish significance thresholds for their respective jurisdictions. These significance thresholds may be adopted after consider ing thresholds of significance adopted or recommended by other public agencies or experts.

The City has not adopted its own GHG Thresholds of Significance for CEQA. The SCAQMD published its Interim CEQA GHG Significance Thresholds for Stationary Sources, Rules, and Plans in 2008 (SCAQMD 2008). The interim thresholds are a tiered approach; projects may be determined to be less than significant under each tier or require further analysis under subsequent tiers. The five tiers are discussed in Section 3.2.3.1.

Consistent with the SCAQMD guidance, the recommended tiered approach for land use development projects in SCAQMD jurisdiction is assessment against the applicable screening levels. As the project is not exempt from CEQA and is not part of an approved local p lan, project emissions are assessed against the industrial 10,000 MT CO 2E screening level. This
screening level is intended to exempt projects that are too small to have significant impacts from further analysis.

4.2 Calculation Methodology
The project’s G HG emissions were calculated using the CalEEMod Version 2016.3.2 (California Air Pollution Control Officers Association [ CAPCOA] 2017). The CalEEMod program is a tool used to estimate air emissions resulting from land development projects based on California-specific emission factors. CalEEMod can be used to calculate emissions from mobile (on-road vehicles), area (fireplaces, consumer products [cleansers, aerosols, and solvents], landscape maintenance equipment, architectural coatings), water and wastewater, and solid waste sources. GHG emissions are estimated in terms of total MT CO 2E.

The analysis methodology and input data are described in the following sections. Where project-specific data was not available, model inputs were based on information provided in the CalEEMod User’s Guide (CAPCOA 2017). Operational emissions were calculated for the projected soonest project operational year of 2023.

4.2.1 Construction Emissions
Construction activities emit GHGs primarily though combustion of fuels (mostly diesel) in the engines of off-road construction equipment and through combustion of diesel and gasoline in on -road construction vehicles and the commute vehicles of the construction workers.

Smaller amounts of GHGs are also emitted through the energy use embodied in water use for fugitive dust control.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Every phase of the construction process, including demolition, grading, paving, and building, emits GHGs in volumes directly related to the quantity and type of construction equipment used when building the project . GHG emissions associated with each phase of project construction are calculated by multiplying the total fuel consumed by the construction equipment and worker trips by applicable emission factors. The number and pieces of construction equipment are calculated based on the project-specific design. In the absence of project-specific construction information, equipment for all phases of construction is estimated based on the project size.

Construction emissions were modeled assuming site preparation/grading would last three months, and the remaining construction activities (building, paving, landscaping, architectural coatings) would last approximately one year for a total construction duration of 15 months.

During the grading phase, 40,000 cubic yards of soil quantities would be balanced on- site between the two building areas with no net import or export. Soil hauling between Parcel 1 and Parcel 2 could be done with the modeled grading equipment, which includes graders and scrapers capable of moving large quantities of soil. However, to be conservative and account for the usage of trucks to haul soil from one parcel to the other, 40,000 cubic yards of soil hauling has been added to the grading phase with a trip length of one mile.

Table 4 summarizes the anticipated construction phases, duration, and equipment.

Table 4
Construction Phases and Equipment
Equipment Quantity Daily Operation Time (Hours)
Site Preparation (18 days)
Rubber Tired Dozers 3 8
Tractors/Loaders/Backhoes 4 8
Grading (47 days)
Excavators 2 8
Graders 1 8
Rubber Tired Dozers 1 8
Scrapers 2 8
Tractors/Loaders/Backhoes 2 8
Building Construction (243 days)
Cranes 1 7
Forklifts 3 8
Generator Sets 1 8
Tractors/Loaders/Backhoes 3 7
Welders 1 8
Architectural Coatings (111 days)
Air Compressor 1 6
Paving (18 days)
Pavers 2 8
Paving Equipment 2 8
Rollers 2 8
NOTE: Each phase would also include vehicles associated with work commutes, dump trucks for hauling, and trucks for deliveries.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Based on guidance from the SCAQMD, total construction GHG emissions resulting from a project should be amortized over 30 years and added to operational GHG emissions to account for their contribution to GHG emissions over the lifetime of a project (SCAQMD 2009).

4.2.2 Mobile Emissions
GHG emissions from vehicles come from the combustion of fossil fuels in vehicle engines. The vehicle emissions are calculated based on the vehicle type and the trip rate for each land use.

The vehicle emission factors and fleet mix used in the current version of CalEEMod are derived from CARB’s 2014 Emission Factors model (EMFAC2014; CARB 2014). In August 2019, the U.S. EPA approved the use of CARB’s 2017 Emission Factor model (EMFAC2017).

However, this had not yet been incorporated into CalEEMod, and there is no standardized approach to modifying the emission factors included in CalEEMod. Generally, vehicles have become cleaner over time; therefore, the mobile emissions would not be higher if CalEEMod were adjusted using EMFAC2017 emission factors.

Mobile source operational emissions are based on the trip rate, trip length, and vehicle mix.

Total passenger vehicle and truck trip g eneration was obtained from the traffic report prepared for the project (Urban Crossroads 2019a). The trip lengths for passenger vehicles and trucks were obtained from the trip length analysis prepared for the project (Urban Crossroads 2019b). The project-specific trip generation and trip length data is summarized in Table 5.

Table 5
Project Trip Generation and Trip Length
Vehicle Type
Daily Trip
Generation (ADT)
Trip Length
(miles)
Passenger Cars 573 24.2
Trucks 274 38.7
2 axle 46 38.7
3 axle 57 38.7
4+-axle 171 38.7
TOTAL 847 --
SOURCE: Urban Crossroads 2019a and 2019b.

ADT = average daily traffic

Mobile source operational emissions are also based on the project’s vehicle mix. Based on the traffic report prepared for the project, the project would generate 573 passenger car trips and 274 truck trips, or which 46 would be 2-axle trucks, 57 would be 3-axle trucks, and 171 would be 4-axle+ trucks (Urban Crossroads 2019). The CalEEMod non-heavy truck vehicle fleet mix includes the following categories: passenger cars (LDA), light-duty trucks (LDT1 and LDT2), medium-duty trucks (MDV), and motorcycles (MCY). The 573 passenger car trips were modeled by proportionally altering these values based on the CalEEMod default values. Note that CalEEMod also includes other non- truck vehicles such as buses and motor homes, however, these vehicle classifications would not be associated with the project. For the truck mix, CalEEMod includes four truck categories: light- heavy-duty trucks (LHD1 and LHD2), medium-heavy-duty trucks (MHD), and heavy -heavy-duty trucks (HHD). The 2 -axle trucks Greenhouse Gas Analysis
Sycamore Hills Distribution Project

were modeled as LH D1, the 3 -axle trucks were modeled as LHD2, and the 4 -axle+ trucks were divided proportionally and modeled as MHD and HHD.

4.2.3 Energy Use Emissions
GHGs are emitted as a result of activities in buildings for which electricity and natural gas are used as energy sources. GHGs are emitted during the generation of electricity from fossil fuels off-site in power plants. These emissions are considered indirect but are calculated in association with a building’s overall operation. Electric power generation acco unts for the second largest sector contributing to both inventoried and projected statewide GHG emissions. Combustion of fossil fuel emits criteria pollutants and GHGs directly into the atmosphere. When this occurs in a building, it is considered a direct emissions source associated with the building. CalEEMod estimates emissions from the direct combustion of natural gas for space and water heating.

CalEEMod estimates GHG emissions from energy use by multiplying average rates of residential and non-residential energy consumption by the quantities of residential units and non-residential square footage entered in the land use module to obtain total projected energy use. This value is then multiplied by electricity and natural gas GHG emission factors applicable to the project location and utility provider.

Energy consumption values are based on the CEC sponsored California Commercial End Use Survey and Residential Appliance Saturation Survey studies, which identify energy use by building type and climate zon e. Because these studies are based on older buildings, adjustments have been made in CalEEMod to account for changes to Title 24 Building Codes.

CalEEMod 2016.3.2 is based on the 2016 Title 24 energy code (Part 6 of the Building Code).

The next version of the energy code, 2019 Title 24, went into effect on January 1, 2020. For non- residential buildings, it is estimated that the 2019 standards will decrease energy consumption by 30 percent (CEC 2018a ). The project would be subjec t to the 2019 Title 24 energy code standards. However, as a conservative analysis, GHG emissions were calculated assuming the default 2016 Title 24 energy code standards.

Electricity would be provided to the project by Riverside Public Utilities Therefore, Riverside Public Utilities’ specific energy-intensity factors (i.e., the amount of CO 2, CH4, and NOX per kilowatt-hour) are used in the calculations of GHG emissions. As discussed, the state mandate for renewable energy is 33 percent by 2020. However, the energy-intensity factors included in CalEEMod by default only represent an 18.4 percent procurement of renewable energy (Union of Concerned Scientists 2012). Current Riverside Public Utilities energy intensity factors were obtained from the newly released version of CalEEMod, Version 2020.4.0. To account for the continuing effects of RPS, the energy-intensity factors included in CalEEMod were adjusted to reflect the current procurement of 33 percent renewable energy. Riverside Public Utilities energy intensity factors are shown in Table 6.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 6
Riverside Public Utilities Intensity Factors
GHG
2009Default
CalEEMod 2016.3.2
Intensity Factors
(lbs/MWh)
2020Updated 2021
Intensity Factors
(lbs/MWh)
Carbon Dioxide (CO2) 1,325.65 789.9831,051.61
Methane (CH4) 0.029 0.0330.023
Nitrous Oxide (N2O) 0.006 0.0040.004
SOURCE: CPUC 2017CAPCOA 2017, 2021.
lbs = pound; MWh = megawatt hour

4.2.4 Area Source Emissions
Area sources include GHG emissions that would occur from the use of landscaping equipment. The use of landscape equipment emits GHGs associated with the equipment’s fuel combustion. The landscaping equipment emission values were derived from the 2011 In-Use Off-Road Equipment Inventory Model (CARB 2011).

4.2.5 Water and Wastewater Emissions
The Western Municipal Water District would provide water to the project site. The amount of water used and wastewater generated by a project has indirect GHG emissions associated with it. These emissions are a result of the energy used to supply, distribute, and treat the water and wastewater. In addition to the indirect GHG emissions associated with energy use, wastewater treatment can directly emit both CH
4 and N2O.

The indoor and outdoor water use consumption data for each land use subtype comes from the Pacific Institute’s Waste Not, Want Not: The Potential for Urban Water Conservation in California 2003 (as cited in CAPCOA 2017). Based on that report, a percentage of total water consumption was dedicated to landscape irrigation, which is used to determine outdoor water use. Wastewater generation was similarly based on a reported percentage of total indoor water use (CAPCOA 2017).

The project would be subject to C ALGreen, which requires a 20 percent increase in indoor water use efficiency compared to the CalEEMod default water consumption rates. However, as a conservative analysis, no reduction in indoor water use was modeled. Thus, in order to demonstrate compliance with C ALGreen, a 20 percent reduction in indoor water use was included in the water consumption calculations for the project.

In addition to water reductions under CALGreen, the GHG emissions from the energy used to transport the water are affected by RPS. As discussed previously, to account for the effects of RPS through 20202021, the Riverside Public Utilities energy-intensity factors included in CalEEMod were adjusted to reflect 33 percent renewable energy were updated to current 2021 values (see Table 6).

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

4.2.6 Solid Waste Emissions
The disposal of solid waste produces GHG emissions from anaerobic decomposition in landfills, incineration, and transportation of waste. To calculate the GHG emissions generated by disposing of solid waste for the project, the total volume of solid waste w as calculated using waste disposal rates identified by California Department of Resources Recycling and Recovery (CalRecycle). The methods for quantifying GHG emissions from solid waste are based on the Intergovernmental Panel on Climate Change method, usi ng the degradable organic content of waste. GHG emissions associated with the project’s waste disposal were calculated using these parameters. According to a CalRecyle report to the Legislature, as of 2013 California has achieved a statewide 50 percent diversion of solid waste from landfills through “reduce/recycle/compost” programs (CalRecycle 2015). However, AB 341 mandates that 75 percent of the solid waste generated be reduced, recycled, or composted by 2020. Therefore, to account for the continuing actions of recycling requirements under state law (i.e., AB 341), a 25 percent solid waste diversion rate was included in the model.However, as a conservative analysis, solid waste GHG emissions were modeled using CalEEMod default values with no increase in solid waste diversion.

5.0 GHG Emission Calculations
Based on the methodology summarized in Section 4.2, the primary sources of direct and indirect GHG emissions have been calculated. Table 7 summarizes the estimated emissions.

The complete model outputs are included in Attachment 1.

Table 7
Summary of Project GHG Emissions
(metric tons per year)
Source MT CO2 MT CH4 MT N2O MT CO2E
Mobile – Passenger Cars 1,2041,465 <1 0 1,2041,466
Mobile – Trucks 4,316 <1 0 4,320
Energy Source 781603 <1 <1 782604
Area Sources <1 <1 0 <1
Water/Wastewater Sources 728695 45 <1 846842
Solid Waste Sources 86115 57 10 214285
Construction (Amortized over 30 years) 3768 <1 0 3868
TOTAL 7,1527,262 912 <1 7,4057,587*
SCAQMD Significance Threshold for Industrial Sources 10,000 MT CO2E = metric tons of carbon dioxide equivalent
MT CH4 = metric tons of methane
MT N2O = metric tons of nitrous oxide
*As discussed in Section 1.2, the GWPs included in CalEEMod are from the IPCC Fourth Assessment Report. For informational purposes, total emissions calculated by CalEEMod were adjusted to account for the updated IPCC Fifth Assessment Report GWPs. Using the current GWPs, total annual project emissions would be 7,4287,618 MT CO2, and would also be less than the screening threshold. Note that the IPCC updates the GWPs periodically, and the next anticipated update will occur in 2022.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

As shown in Table 7, the project would result in a net increase of 7, 4057,587 MT CO2E per year. As discussed previously, the SCAQMD’s 10,000 MT CO2E screening level is appropriate for exempting industrial projects that are too small to have significant impacts from further analysis.

6.0 GHG Impact Analysis

1. Would the project generate GHG emissions, either directly or indirectly, that may have a significant impact on the environment?
As discussed previously, this analysis uses SCAQMD’s Interim CEQA GHG Significance Thresholds for Stationary Sources, Rules, and Plans . The interim thresholds are a tiered approach; project impacts may be determined to be less than significant under each t ier or require further analysis under subsequent tiers. Because the project is subject to CEQA and is not subject to a regional GHG emissions reduction plan, the project does not fall under Tiers 1 or 2. As shown in Table 7 , construction and operation of the project would result in the annual equivalent emission of 7,4057,587 MT CO
2E in 2023. Project GHG emissions
would be less than the applicable SCAQMD screening level of 10,000 MT CO2E for industrial uses. As project emissions would be less than the 10,000 MT CO 2E screening level, GHG emissions impacts would be less than significant without mitigation.

2. Would the project conflict with an applicable plan, policy , or regulation adopted for the purpose of reducing the emission of GHGs?
As discussed in Section 3.2.2, State Climate Change Regulations, EO S-3-05 established GHG emission reduction targets for the state, and AB 32 launched the CARB Climate Change Scoping Plan that outlined the reduction measures needed to reach the 2020 target. As discussed above, the project emissions would be below the screening level of 10,000 MT CO 2E
for industrial uses. This threshold is based on the concept of establishing a 90 percent GHG emission capture rate. A 90 percent emission capture rate means that 90 percent of total emissions from all new or modified stationary source projects would be subject to a CEQA analysis, which includes analyzing feasible alternatives and imposing feasible mitigation measures. The market capture rate is based on guidance from the California Air Pollution Control Officers Association (CAPCOA) report CEQA & Climate Change, dated January 2008, which identifies several potential approaches for assessing a project’s GHG emissions (CAPCOA 2008). Following the market capture rate approach, a lead agency defines an acceptable capture rate and identifies the corresponding emissions level. Following rationale presented in the CAPCOA Guidance, the aggregate emi ssions from all projects with individual annual emissions that are equal to or less than the identified market capture rate would not impede achievement of the state GHG emissions reduction targets codified by AB 32 (2006) and SB 32 (2016), and impacts und er CEQA would therefore be less than cumulatively considerable. A 90 percent emission capture rate sets the emission threshold low enough to capture a substantial fraction of future stationary source projects that will be constructed to accommodate future statewide population and economic growth, while setting the emission threshold high enough to exclude small projects that will in aggregate contribute a relatively small fraction of the cumulative statewide GHG emissions.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Project GHG emissions would be less than the applicable SCAQMD screening level of 10,000 MT CO2E for industrial uses. Further, project emissions would decline beyond the buildout year of the project, 2023, as a result of continued implementation of federal, state, and local reduction measures such as increased federal and state vehicle efficiency standards, and Riverside Public Utilities’ increased renewable sources of energy in accordance with RPS goals. Base d on currently available models and regulatory forecasting, project emissions would continue to decline through at least 2050. Given the reasonably anticipated decline in project emissions, once fully constructed and operational, the project is in line with the GHG reductions needed to achieve the 2050 GHG emission reduction targets identified by EO S-3-

05. As noted in Section 3.2.2.3, the 2017 Scoping Plan identifies state strategies for achieving the state’s 2030 interim GHG emissions reduction target codified by SB 32. Measures under the 2017 Scoping Plan scenario build on existing programs such as the Low Carbon Fuel Standard, Advanced Clean Cars Program, RPS, Sustainable Communities Strategy, Short- Lived Climate Pollutant Reduction Strategy, and the Ca p-and-Trade Program. The project would comply with all applicable provisions contained in the 2017 Scoping Plan since th e adopted regulations would apply to new development or the emission sectors associated with new development.
• Transportation – State regulations and 2017 Scoping Plan measures that would reduce the project’s mobile source emissions include the California Light-Duty Vehicle GHG Standards (AB 1493/Pavley I and II), the Low Carbon Fuel Standard, and the heavy-duty truck regulations discussed in Section 3.2.2.8. These measures are implemented at the state level and would result in project-related mobile source GHG emissions.
• Energy – State regulations and 2017 Scoping Plan measures that would reduce the project’s energy-related GHG emissions in clude RPS (see Section 3.2.2.5), Title 24 Energy Efficiency Standards (see Section 3.2.2.7a), and CALGreen (see Section

3.2.2.7b).

The project would be served by Riverside Public Utilities, which has achieved 36 percent renewables as of 2017 (CEC 2018b). The project’s energy related GHG emissions would decrease as Riverside Public Utilities increases its renewables procurement beyond 2020 towards the 2030 goal of 50 60 percent. Additionally, the project would be constructed in accordance with energy efficiency standards effective at the time building permits are issued. The current 2019 Energy Code is estimated to decrease energy consumption by 30 percent for non -residential buildings when compared to the 2016 Title 24 Energy Code.
• Water – State regulations and 2017 Scoping Plan measures that would reduce the project’s electricity consumption associated with water supply, treatment, and distribution, and wastewater treatment include RPS , C ALGreen, and the Model Water Efficient Landscape Ordinance. The project would be required to reduce indoor water consumption by 20 percent in accordance with C ALGreen. Additionally, the project would be subject to all City landscaping ordinance requirements.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

• Waste – State regulations and 2017 Scoping Plan measures that would reduce the project’s solid waste-related GHG emissions are related to landfill methane control, increases efficiency of landfill methane capture, and high recycling/zero waste. The project would be subject to CALGreen, which requires a diversion of construction and demolition waste from landfills. Additionally, the project would include recycling storage and would divert waste from landfills in accordance with AB 341.

In addition to meeting th e SCAQMD screening thresholds, the project was evaluated f or consistency with the strategies and actions contained in the RRG-CAP (see Section 3.2.3.3).

To achieve the City’s GHG emission reductions, the City’s RRG -CAP includes reduction measures for each category of GHG emissions: transportation, energy, water, and solid waste.

The RRG-CAP reduction measures further support the goals of SB 32 and the measures in the 2017 Scoping Plan. Table 8 summarizes the project’s consistency with RRG -CAP measures. As discussed in this table, the project would be consistent with applicable RRG - CAP measures. The project would be required to comply with the regulations discussed above that have been adopted to implement the Scoping Plan and to achieve the SB 32 2030 target.

As a res ult, the project would not conflict with applicable plans, policies, or regulations adopted for the purpose of reducing GHG emissions. Impacts would be less than significant without mitigation.

Table 8
Project Consistency with RRG-CAP GHG Reduction Measures Number Strategy/Goal Project Consistency
State and Regional Energy Measures
The following are state and regional measures that are expected to reduce GHG emissions associated with the energy sector.

SR-1 Renewables Portfolio
Standard (RPS)
Utilities must secure 33
percent of their power from
renewable sources by 2020.

The project would be served by
Riverside Public Utilities,
which has achieved 36 percent
renewables as of 2017. The
project’s energy related GHG
emissions would decrease as
Riverside Public Utilities
increases its renewables
procurement beyond 2020
towards the 2030 goal of 50 60
percent. The project would not
conflict or interfere with RPS.

SR-2 2013 California Building
Energy Efficiency
Standards (Title 24, Part 6)
Mandatory energy efficiency
standards for buildings.

The project would be
constructed in accordance with
energy efficiency standards
effective at the time building
permits are issued. The
current 2019 Energy Code is
estimated to decrease energy
consumption by 30 percent for
non-residential buildings when
compared to the 2016 Title 24
Energy Code.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 8
Project Consistency with RRG-CAP GHG Reduction Measures Number Strategy/Goal Project Consistency
SR-3 HERO Residential Program
Financing for homeowners to
make energy efficient,
renewable energy, and water
conservation improvements.

The project is not a residential
project and therefore this
measure does not apply to the
project.

SR-4 HERO Commercial
Program
Financing for business owners
to make energy efficient,
renewable energy, and water
conservation improvements.

The HERO Commercial
program is a public-private
partnership administered by
Western Riverside Council of
Governments (WRCOG), and
provides financing for energy
and water improvements to
business owners. As the
project is new warehouse
construction, this measure
does not apply to the project.

The project would not conflict
with WRCOG’s implementa-
tion of the HERO program.

State and Regional Transportation Measures
The following are state and regional measures that are expected to reduce GHG emissions associated with the transportation sector.

SR-6 Pavley and Low Carbon
Fuel Standard
Requirements for vehicles to
use cleaner fuels.

This measure is implemented
at the State level. Project
mobile-source GHG emissions
would be reduced through
implementation of these
measures. The project would
not conflict with
implementation.

SR-7 Metrolink Expansion
Additional Metrolink transit
service provided to Western
Riverside County.

Identified in SCAG’s 2012
RTP/SCS, the Metrolink Perris
Valley Line was extended from
Riverside to Perris in Western
Riverside County. The Perris
Valley Line opened for service
in 2016. Future employees
could use the expansion to
commute to the project site.

SR-8 Express Lanes
Additional express lanes added
along major freeways in
western Riverside County.

The project would not interfere
with construction of additional
freeway express lanes. Project
vehicle traffic would benefit
from decreased freeway
congestion.

SR-9 Congestion Pricing
Expansion of the toll lanes
along SR-91.

This measure does not apply
directly to the project. The
project would not interfere
with the expansion of SR-91
toll lanes.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 8
Project Consistency with RRG-CAP GHG Reduction Measures Number Strategy/Goal Project Consistency
SR-10 Telecommuting
Work arrangement in which
employees do not commute to a
central place to work.

The project is a high-cube
warehouse which would
require employees to
physically fulfill and transport
goods. This measure does not
apply to the project.

SR-11 Goods Movement
Efficiency movement of goods
through inland southern
California.

The project would support the
region’s role as a major hub for
importing and exporting goods.

To implement this measure, at
the state level more standards
are being implemented to
increase vehicle efficiencies
and the 20162020 RTP/SCS
and SCAQMD are supporting
greater penetration of low-
emission trucks in the region.

The estimated GHG reductions
associated with this measure
account for the region’s “share”
of SCAG and SCAQMD’s
anticipated investments. The
project would benefit from
reductions associated with
regional investments. Further,
by providing additional
warehouse space in the region,
the project could reduce truck
VMT by providing a hub closer
to the region than further
warehouses.

SR-12 Electric Vehicle Plan and
Infrastructure
Facilitate electric vehicle use
by providing necessary
infrastructure.

For the City of Riverside, this
measure would be
implemented by providing
both public and private
charging facilities, and by
updating development codes to
encourage or facilitate
charging stations. The project
would not interfere with
implementation of this
measure, and would be
constructed in accordance with
development codes in place at
the time building permits are
issued. The project would
install conduits for vehicle
charging stations.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 8
Project Consistency with RRG-CAP GHG Reduction Measures Number Strategy/Goal Project Consistency
State Solid Waste Measures
The following state measure is expected to reduce GHG emissions associated with the solid waste sector.

SR-13 Construction & Demolition
Waste Diversion
Meet mandatory requirement
to divert 50 percent of
construction & demolition
(C&D) waste from landfills by
2020 and exceed requirement
by diverting 90 percent of C&D
waste from landfills by 2035.

Project-related C&D waste
would be sorted, recycled, and
diverted from landfills in
accordance with mandatory
regulatory requirements.

Local Energy Measures
The following are local measures that can be implemented to reduce GHG emissions associated with the energy sector.

E-1 Traffic and Street Lights
Replace traffic and streetlights
with high-efficiency bulbs.

The project would not interfere
with implementation of this
measure.

E-2 Shade Trees
Strategically plant trees at
new residential developments
to reduce the urban heat
island effect.

This measure applies to
residential development and
does not apply to the project.

E-3 Local Utility Programs –
Electricity
Financing and incentives for
business and homeowners to
make energy efficient,
renewable energy, and water
conservation improvements.

To implement this measure,
Riverside Public Utilities
offers a selection of rebates
and other incentives to assist
property owners (residential
and commercial) with the
installation of energy- and
water-saving products. This
measure does not directly
apply to the project. However,
the project would be
constructed in accordance with
the Energy Code in place at
the time building permits are
issued, which would require
the project to be more energy
efficient than existing
development. The project
would also reduce water
consumption in accordance
with CALGreen.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 8
Project Consistency with RRG-CAP GHG Reduction Measures Number Strategy/Goal Project Consistency
E-4 Renewable Energy
Production on Public
Property
Large-scale renewable energy
installation on publicly owned
property and in public rights-
of-way.

This measure encourages the
City to seek opportunities to
install renewable energy
projects on public property,
public facilities and in public
rights of way. This measure
does not apply to the project.

E-5 UC Riverside Carbon
Neutral Program
Collaborate with UC Riverside
to achieve a carbon neutral
campus.

The project is not associated
with UC Riverside. This
measure does not apply to the
project.

E-6 Riverside Public Utilities
Technology Grants
Riverside Public Utilities
grant programs to foster
research, development and
demonstration of innovative
solutions to energy problems
Riverside Public Utilities
offers energy technology grant
programs to help foster the
development of innovative
solutions to energy problems.

This measure does not apply to
the project.

Local Transportation Measures
The following are local measures that can be implemented to reduce GHG emissions associated with the transportation sector.

T-1 Bicycle Infrastructure
Improvements
Expand on-street and off-
street bicycle infrastructure,
including bicycle lanes and
bicycle trails.

Adjacent to the project site,
Alessandro Boulevard is a
Class 2 bicycle facility. The
project driveway would
connect to Alessandro
Boulevard and the existing
bicycle lanes to provide access
to the project site.

Additionally, the project would
include the construction of a
new parking lot to provide
access to the Sycamore Canyon
Wilderness Park trails.

Additionally, the project would
include secure bicycle parking
at each building.

T-2 Bicycle Parking
Provide additional options for
bicycle parking.

The project would include
secure bicycle parking at each
building (at the northwest
corner and entrance of
Building B and at the
southeast corner and entrance
of Building A).

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 8
Project Consistency with RRG-CAP GHG Reduction Measures Number Strategy/Goal Project Consistency
T-3 End of Trip Facilities
Encourage use of non-
motorized transportation
modes by providing
appropriate facilities and
amenities for commuters.

The project would include
secure bicycle parking at each
building (at the northwest
corner and entrance of
Building B and at the
southeast corner and entrance
of Building A). Additionally,
Building A would have 8 clean
air/van pool parking spaces
and 24 electric vehicle parking
stalls, and Building B would
have 5 clean air/van pool
parking spaces and 15 electric
vehicle parking stalls. The
charging stations for the
electric vehicle parking stalls
would be provided by the
future tenant.

T-4 Promotional
Transportation Demand
Management
Encourage Transportation
Demand Management
strategies.

The project site is served by
two existing bus routes. Route
20 runs along Alessandro
Boulevard adjacent to the
project site, providing service
from Magnolia Center to
Moreno Valley. Route 208 is a
CommuterLink Express Route
providing service from
Temecula to the Riverside
Metrolink. Consistent with
Transportation Demand
Management strategies, future
employees would be
encouraged to use these routes
as an alternative form of
transportation. The project
would also provide secure
bicycle parking.

T-5 Traffic Signal Coordination
Incorporate technology to
synchronize and coordinate
traffic signals along local
arterials.

This measure is the
responsibility of the Public
Works Departments and is
currently in progress. This
measure does not apply to the
project. The project would not
interfere with implementation
of this measure.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 8
Project Consistency with RRG-CAP GHG Reduction Measures Number Strategy/Goal Project Consistency
T-6 Density
Improve jobs-housing balance
and reduce vehicle miles
traveled by increasing
household and employment
densities.

Single and multi-family
residential neighborhoods are
located south and west of the
project site. The project would
create new employment
opportunities for near-by
residents. In Riverside County,
the 2012 jobs-housing balance
was 0.89 jobs to household and
the 2040 projection is 1.10 jobs
to household, for an annual
growth of 0.8 percent.

T-7 Mixed-Use Development
Provide for a variety of
development types and uses.

The project site is surrounded
by single and multi-family
neighborhoods as well as
commercial and retail
development. The project
would create new employment
opportunities for near-by
residents, and future
employees could utilize near-
by commercial and retail
business, in support of this
measure.

T-8 Pedestrian Only Areas
Encourage walking by
providing pedestrian-only
community areas.

This measure refers to urban,
non-motorized pedestrian use
areas within central business
districts and major activity
centers. This measure does not
apply to the project.

T-9 Limited Parking
Requirements for New
Development
Reduce requirements for
vehicle parking in new
development projects.

Limiting parking
requirements would encourage
modes of transportation other
than single-occupancy
vehicles, thereby reducing
VMT and GHG emissions. The
City’s current Zoning Code
authorizes a reduction in the
number of required parking
spaces for mixed-use
development and/or stand-
alone uses in mixed-use zones
subject to the approval of a
shared parking arrangement.

The City’s future specific plan
and Zoning Code updates will
provide an opportunity for the
City to comprehensively
review its parking
requirements and further
Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 8
Project Consistency with RRG-CAP GHG Reduction Measures Number Strategy/Goal Project Consistency
incorporate state of the art
techniques such as shared
parking, parking cash out, and
other specific strategies.

The project is not a mixed-use
development; however, the
applicant is requesting a
variance to reduce the number
of parking spaces required.

T-10 Bus Rapid Transit Service
Implement bus rapid transit
service in the subregion to
provide alternative
transportation options.

The project site is served by
two existing bus routes. Route
20 runs along Alessandro
Boulevard adjacent to the
project site, providing service
from Magnolia Center to
Moreno Valley. Two Route 20
bus stops are located
immediately adjacent to the
project site along the southern
boundary on Alessandro
Boulevard. Route 208 is a
CommuterLink Express Route
providing service from
Temecula to the Riverside
Metrolink. Future employees
could use these routes as an
alternative form of
transportation. The project
would not interfere with the
City’s efforts to implement
additional bus rapid transit.

T-11 Voluntary Transportation
Demand Management
(TDM)
Encourage employers to create
TDM programs for their
employers.

Future employees would be
encouraged to use existing
public transit routes as an
alternative form of
transportation.

T-12 Accelerated Bike Plan
Implementation
Accelerate the implementation
of all or specified components
of a jurisdiction’s adopted bike
plan.

The City adopted a Bicycle
Master Plan in 2007.

Alessandro Boulevard is a
Class 2 bicycle facility. The
project driveway would
connect to Alessandro
Boulevard and the existing
bicycle lanes to provide access
to the project site. The project
would provide secure bicycle
parking, and would not
interfere with implementation
Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 8
Project Consistency with RRG-CAP GHG Reduction Measures Number Strategy/Goal Project Consistency
of the City’s Bicycle Master
Plan.

T-13 Fixed Guideway Transit
By 2020, complete feasibility
study and by 2025 Introduce a
fixed route transit service in
the jurisdiction.

This measure applies
specifically to the City’s efforts
on the “Riverside Reconnects”
Streetcar feasibility study.

This measure does not apply to
the project.

T-14 Neighborhood Electric
Vehicle Programs
Implement development
requirements to accommodate
Neighborhood Electric
Vehicles and supporting
infrastructure.

This measure does not apply to
the project. However, the
project would install conduits
for vehicle charging stations.

T-15 Subsidized Transit
Increase access to transit by
providing free or reduced
passes.

The tenants are unknown at
this stage of project design
and, therefore, a commitment
cannot be made that the future
tenants would provide free or
reduced transit passes to their
employees. However, the
project would not interfere
with the ability for future
tenants to provide transit
passes.

T-16 Bike Share Program
Create nodes offering bike
sharing at key locations
throughout the City.

This measure encourages bike
sharing, implemented by
third-party vendors, in
Downtown, transit center, and
mixed-use areas. This measure
does not directly apply to the
project. However, the project
would include secure bicycle
parking, and would not
interfere with bike sharing in
the region.

T-17 Car Share Program
Offer Riverside residents the
opportunity to use car sharing
to satisfy short-term mobility
needs.

Similar to bike sharing, car
sharing is offered by third-
party vendors. This measure
does not directly apply to the
project, and the project would
not interfere with car sharing
programs in the region.

T-18 SB 743 as Alternative to
LOS
Use SB 743 to incentivize
development in the downtown
and other areas served by
transit.

The project is not located
downtown. This measure does
not apply to the project.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Table 8
Project Consistency with RRG-CAP GHG Reduction Measures Number Strategy/Goal Project Consistency
T-19 Alternative Fuel and
Vehicle Technology
Infrastructure
Promote the use of alternative
fueled vehicles such as those
powered by electric, natural
gas, biodiesel, and fuel cells by
Riverside residents and
workers.

The project would install
conduits for vehicle charging
stations.

T-20 Eco-Corridor
Create a geographically
defined area(s) featuring best
practices in sustainable urban
design and green building
focused on supporting both
clean-tech and green
businesses.

A potential location for an Eco-
Corridor/Green Business Zone
is the Magnolia-University
Avenue corridor. The project is
not located in a potential Eco-
Corridor. This measure does
not apply to the project.

Local Water Measures
The following local measure is expected to reduce GHG emissions associated with the water sector.

W-1 Water Conservation and
Efficiency
Reduce per capita water use by
20 percent by 2020.

As discussed, the project would
be required to reduce indoor
water consumption by 20
percent in accordance with
CALGreen.

Local Solid Waste Measures
The following are local measures that can be implemented to reduce GHG emissions associated with the solid waste sector.

SW-1 Yard Waste Collection
Provide green waste collection
bins community-wide.

This measure applies to
residential uses. This measure
does not apply to the project.

SW-2 Food Scrap and Paper
Diversion
Divert food and paper waste
from landfills by implementing
commercial and residential
collection program.

This measure applies to
residential and commercial
uses. This measure does not
apply to the project. However,
the project would include
recycling storage and would
divert waste from landfills in
accordance with AB 341.

Local Agriculture Measures
The following are local measures that can be implemented to reduce GHG emissions associated with the urban forest and the local food and agricultural sectors.

A-1 Local Food and Agriculture
Promote local food and
agricultural programs.

The project is not associated
with food or agricultural uses.

This measure does not apply to
the project.

Additionally, the project was evaluated for consistency with the Western Riverside Council of Governments ’ Good Neighbor Guidelines for Site New and/or Modified Greenhouse Gas Analysis
Sycamore Hills Distribution Project

Warehouse/Distribution Facilities (Good Neighbor Guidelines; WRCOG 2005) as well as the City’s own Good Neighbor Guidelines for Siting New and/or Modified Warehouse Distribution Facilities (Good Neighbor Guidelines; City of Riverside 2008). Both of these Good Neighbor Guidelines were designed to help minimize the impacts of diesel particulate matter from on -road trucks associated with warehouses and distribution centers on existing communities and sensitive receptors located in the region. On October 14, 2008 the City adopted its own Good Neighbor Guidelines. The City’s Good Neighbor Guidelines are similar to the WRCOG with the City’s being tailored to the City’s unique characteristics and specific needs. Although the Good Neighbor Guidelines specifically address air quality issues, the recommended strategies also serve to reduce GHG emissions. These guidelines include the following goals that can be implemented at the regional level:
• Minimize exposur e to diesel emissions to neighbors that are situated in close proximity to the warehouse/distribution center;
o Recommended strategy: Design facilities to allow for the queuing of truck on -site and away from sensitive receptors. Conversely, prevent the queuing of trucks on streets or elsewhere outside of facility in compliance with Title 10 – Vehicles and Traffic – Chapter 10.44 – Stopping, Standing and Parking.

Project consistency: Based on the project location and design, no truck queuing would occ ur next to sensitive receptors, which are located south of Alessandro Boulevard. Truck queuing would not occur outside the facility.

o Recommended strategy: To the extent possible, locate driveways, loading docks and internal circulation route away from res idential uses or any other sensitive receptors.

Project consistency: Driveways, loading docks, and internal circulation routes are not adjacent to sensitive receptors. Further, as calculated in this analysis, emissions due to on -site operations would not expose sensitive receptors to substantial pollutant concentrations.

o Recommended strategy: Conduct SCAQMD URBEMIS and EMFAC computer models as appropriate, to initially evaluate warehouse and distribution projects on a case by case basis to determine the s ignificance of air quality impacts and whether air quality thresholds would be exceeded as a result of the project. Where thresholds are exceeded, a more detailed air quality specialist is required to be prepared and submitted by the project applicant.

Project consistency: As calculated and concluded in this analysis, the project would not result in significant air quality impacts.

o Recommended strategy: Enforce compliance with Riverside Municipal Code Section 19.880 – “Transportation Demand Management Regulations”. This section of the Code requires trip reduction plans to be submitted for all businesses, including warehouses, with ov er one hundred employees to reduce work -related Greenhouse Gas Analysis
Sycamore Hills Distribution Project

vehicles trips by six and one half percent from the number of trips related to the project.

Project consistency: The project would include transportation demand management measures that would reduce emissions associated with employee trips. These include access to public transit (Routes 20 and 208), bicycle parking, clean air/van pool parking spaces, and electric vehicle parking.

• Eliminate diesel trucks from unnecessarily traversing through residential neighborhoods;
o Recommended strategy: Require warehouse/distribution centers to establish a specific truck route between the warehouse/distribution center and the State Route 60 and Interstate 215 freeways for City approval as part of the Design Review process. I n addition, a haul route plan for construction activities should also be provided as part of the Design Review process.

Project consistency: The project site is located one mile west of Interstate 215, with direct access via Alessandro Boulevard which is an existing truck route.

o Recommended strategy: Require warehouse/distribution centers to clearly specify all entrance and exit points on the site plan submitted for City review and approval.

Project consistency: The project site plans indicate all entrance and exit points.

o Recommended strategy: Require warehouse/distribution centers to provide on-site signage for directional guidance to trucks entering and exiting the facility.

Project consistency: On-site signage for directional guidance will be provided.

o Recommended strategy: Require warehouse/distribution centers to provide signage or flyers that advise truck drivers of the closest restaurants, fueling stations, truck repair facilities, lodging and entertainment.

Project consistency: The future tenants are unknown at this time ; however, this information is readily available to truck drivers.

• Eliminate trucks from using residential areas and repairing vehicles on the streets; o Recommended strategy: Enforce compliance with Riverside Municipal Code Section 10.44.155 – “Parking of certain commercial vehicles, trailers and semi - trailers prohibited; exceptions”, Section 10.44.160 – “Parking of certain commercial vehicles prohibited in residential districts” and Section 10.44.040 “Parking for certain purposes prohibited”.

Project consistency: The project would comply with all Municipal Code requirements. No trucks would be parked off-site.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

• Reduce and/or eliminate diesel idling within the warehouse/distribution center; o Recommended strategy: Promote the installation of on -site electric hook -ups to eliminate the idling of main and auxiliary engines during loading and unloading of cargo and when trucks are not in use – especially where Tra nsportation Refrigeration Units are proposed to be used.

Project consistency: The project would not include Transportation Refrigeration Units. All trucks would be required to comply with the CARB idling limit of 5 minutes.

o Recommended strategy: Implement General Plan 2025 Program Final Program Environmental Impact Report, Mitigation Measure MM Air 12. This Mitigation Measure requires that all new truck terminals, warehouses and other shipping facilities requiring the use of refrigerated trucks and with more than 50 truck trips per day shall provide electrical hookups for the refrigerated units to reduce idling and its associated air quality pollutants. Additionally, future tenant improvements involving conversion of a warehouse for refrigeration storage shall include electrical hookups for refrigerated units.

Project consistency: The project would not include Transportation Refrigeration Units or refrigeration storage.

o Recommended strategy: Require signage (posted inside and outside of the warehouse facility) to inform truck drivers of CARB regulations, idling limits, authorized truck route, and designated truck parking locations. Post signs requesting truck drivers to turn off engines when not in use and restrict idling within facilities to less than 5 minutes.

Project consistency: The project would include signage regarding idling limits, truck routes, and parking.

Additionally, the City’s Guidelines recommend the enforcement of the Riverside Municipal Code.

The City is currently in the process of updating the Riverside Good Neighbor Guidelines. The updated guidelines include new limits of operations and require on -site electrical loading dock hook ups. The updated Good Neighbor Guidelines have not yet been adopted, but as proposed at the time of this report, the project would be in compliance with the proposed updates.

7.0 Conclusions
GHG emissions would result from construction and operation of the project. Construction activities emit GHGs primarily though the combustion of fuels in on- and off-road equipment and vehicles. Operational emissions include mobile, energy (electricity and natural gas), area (landscape maintenance equipment), water and wastewater, and solid waste sources. GHG emission associated with construction and operation of the project were calculated and Greenhouse Gas Analysis
Sycamore Hills Distribution Project

compared to the SCAQMD annual screening threshold of 10,000 MT CO2E for industrial uses.

This threshold is based on the concept of establishing a GHG emission market capture rate.

Following rationale presented in the CAPCOA Guidance, the aggregate emissions from all projects with individual annual emissions that are equal to or less than the identified market capture rate would not impede achievement of the state GHG emissions reduction targets codified by AB 32 (2006) and SB 32 (2016), and impacts under CEQA would , therefore, be less than cumulatively considerable. As shown in Table 7, the project would result in a net increase of 7,4057,587 MT CO2E per year. As project emissions would be less than the 10,000 MT CO 2E screening level, GHG emissions impacts would be less than significant.

Additionally, the project would be consistent with applicable 2017 Scoping Plan and RRG - CAP measures, and is in line with the GHG reductions needed to achieve the 2050 GHG emission reduction targets identified b y EO S -3-05. GHG impacts would be less than significant without mitigation.

8.0 References Cited
California Air Pollution Control Officers Association (CAPCOA) 2008 CEQA & Climate Change, Evaluating and Addressing Greenhouse Gas Emissions from Projects Subject to the California Environmental Quality Act, January.

2017 California Emissions Estimator model (CalEEMod). User’s Guide Version 2016.3.2. November.

2021 California Emissions Estimator model (CalEEMod). User’s Guide Version 2020.4.0. May.

California Air Resources Board (CARB)
2007 California Greenhouse Gas Inventory – Summary by Economic Sector. Last updated November 19, 2007.

2008 Climate Change Scoping Plan: A Framework for Change. http://www.arb.ca.gov/cc/scopingplan/document/adopted_scoping_plan.pdf.

December.

2011 In-Use Off-Road Equipment (Construction, Industrial, Ground Support, and Oil Drilling) 2011 Inventory Model.

2014 2014 EMission FACtors (EMFAC) model, version 1.07, update March 15, 2015.

2017 The 2017 Climate Change Scoping Plan Update: The Proposed Strategy for Achieving California’s 2030 Greenhouse Gas Target. January 20.

2019 Greenhouse Gas Inventory Data—2000 to 2017 (last updated August 12, 2019). https://ww2.arb.ca.gov/ghg-inventory-data.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

California Department of Resources Recycling and Recovery (CalRecycle) 2015 AB 341 Report to the Legislature. Publication #DRRR-2015-1538. https://www2.calrecycle.ca.gov/Publications/Download/1168.

California Energy Commission (CEC)
2018a An Overview of the 2019 Building Energy Efficiency Standards. Accessed at 2019 Building Energy Efficiency Standards. March 2018.

2018b City of Riverside Public Utilities 2017 Power Content Label. Version July 2018.

Council on Environmental Quality (CEQ)
2012 Federal Greenhouse Gas Accounting and Reporting Guidance, June 4. Accessed June 24, 2016. https://www.whitehouse.gov/sites/default/files/microsites/ceq/ ghg_guidance_document_0.pdf.

Intergovernmental Panel on Climate Change (IPCC)
2007 Fourth Assessment Report (AR4), Climate Change 2007: Synthesis Report.

2014 Fifth Assessment Report (AR5), Climate Change 2014: Synthesis Report.

Riverside, City of
2007 City of Riverside General Plan 2025. November.

2016 Economic Prosperity Action Plan and Climate Action Plan. January.

South Coast Air Quality Management District (SCAQMD)
2008 Draft Guidance Document – Interim CEQA GHG Significance Thresholds for Stationary Sources, Rules, and Plans. October.

2009 Greenhouse Gas CEQA Significance Threshold Stakeholder Working Group 14.

November 19, 2009.

2010 Greenhouse Gas CEQA Significance Thresholds Stakeholder Working Group 15.

September 28, 2010.

Union of Concerned Scientists
2012 Riverside Public Utilities – The Clean Energy Race: How Do California Public Utilities Measure Up. July.

U.S. Environmental Protection Agency (U.S. EPA)
2010 Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2008.

U.S. Greenhouse Gas Inventory Program, Office of Atmospheric Programs. 430-R- 10-006. April 15.

2020a Energy Star. Accessed June 17, 2020. Available at http://www.energystar.gov.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

2020b U.S. EPA State and Local Climate and Energy Program. Accessed June 17, 2020. http://www.epa.gov/statelocalclimate/index.html.

Urban Crossroads
2019 Sycamore Hills Distribution Center Traffic Impact Analysis.

2020 Sycamore Hills Distribution Center Vehicle Miles Traveled (VMT)/Trip Length Analysis. July 29, 2020.

Western Riverside Council of Governments
2005 Good Neighbor Guidelines for Site New and/or Modified Warehouse/Distribution Facilities. Regional Air Quality Task Force. September 12, 2005.

Greenhouse Gas Analysis
Sycamore Hills Distribution Project

ATTACHMENT 1
CalEEMod Output

1.1 Land Usage
Land Uses
Size
Metric
Lot Acreage
Floor Surface Area
Population
Unrefrigerated Warehouse-No Rail
603.10
1000sqft

16.00 603,100.00
0 Other Asphalt Surfaces

16.00 Acre

16.00 696,960.00
0 Parking Lot

5.00 Acre

5.00 217,800.00
0 1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
10 Wind Speed (m/s)
Precipitation Freq (Days)

2.2 31

1.3 User Entered Comments & Non-Default Data

1.0 Project Characteristics
Utility Company
Riverside Public Utilities
2023
Operational Year
CO2 Intensity
(lb/MWhr)
789.98

0.033
CH4 Intensity
(lb/MWhr)

0.004
N2O Intensity
(lb/MWhr)
9309 Sycamore Hills Distribution Center - Passenger Cars South Coast Air Basin, Annual
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

Project Characteristics - Current 2021 Riverside Public Utilities intensity factors Land Use -
37 acre site
603,100
sf
Construction Phase - Grading/Prliminary Road Construction - 3 months
Building Permit/Building Construction -
12 months
Off-road Equipment -
Off-road Equipment -
Off-road Equipment -
Trips and VMT - Soil would be balanced between Parcel 1 and 2 Grading -
Architectural Coating -
Vehicle Trips -
847
ADT
Passenger cars -
573
(

0.95 trips/ksf)

24.2 mile trip length
Area Coating -
Energy Use -
Water And Wastewater -
Construction Off-road Equipment Mitigation -
Waste Mitigation -
Fleet Mix - Employee cars (light and medium duty) only
Table Name
Column Name
Default Value
New Value
tblConstructionPhase
NumDays

30.00 18.00
tblConstructionPhase
NumDays

75.00 47.00
tblConstructionPhase
NumDays
740.00
243.00
tblConstructionPhase
NumDays

55.00 111.00
tblConstructionPhase
NumDays

55.00 18.00
tblFleetMix
HHD

0.03 0.00
tblFleetMix
LDA

0.55 0.60
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

2.0 Emissions Summary
tblFleetMix
LDT1

0.04 0.05
tblFleetMix
LDT2

0.20 0.22
tblFleetMix
LHD1

0.02 0.00
tblFleetMix
LHD2

5.8470e-003

0.00 tblFleetMix
MCY

4.8220e-003

5.1750e-003
tblFleetMix
MDV

0.12 0.13
tblFleetMix
MH

8.6900e-004

0.00 tblFleetMix
MHD

0.02 0.00
tblFleetMix
OBUS

2.1100e-003

0.00 tblFleetMix
SBUS

7.1000e-004

0.00 tblFleetMix
UBUS

1.7690e-003

0.00 tblGrading
MaterialExported

0.00 40,000.00
tblLandUse
LotAcreage

13.85 16.00
tblProjectCharacteristics
CH4IntensityFactor

0.029

0.033
tblProjectCharacteristics
CO2IntensityFactor
1325.65
789.98
tblProjectCharacteristics
N2OIntensityFactor

0.006

0.004
tblTripsAndVMT
HaulingTripLength

20.00 1.00
tblVehicleTrips
CC_TL

8.40 24.20
tblVehicleTrips
CNW_TL

6.90 24.20
tblVehicleTrips
CW_TL

16.60 24.20
tblVehicleTrips
ST_TR

1.68 0.95
tblVehicleTrips
SU_TR

1.68 0.95
tblVehicleTrips
WD_TR

1.68 0.95
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

2.1 Overall Construction
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Year
tons/yr
MT/yr
2021

0.4886

4.5855

3.9430

0.0125

0.9434

0.1353

1.0787

0.3293

0.1259

0.4552

0.0000
1,151.059
7 1,151.059
7 0.1293

0.0000
1,154.291
3 2022

3.2698

2.4393

2.8361

9.6400e-
003

0.5550

0.0604

0.6154

0.1494

0.0569

0.2063

0.0000
886.7648
886.7648

0.0684

0.0000
888.4738
Maximum

3.2698

4.5855

3.9430

0.0125

0.9434

0.1353

1.0787

0.3293

0.1259

0.4552

0.0000
1,151.059
7 1,151.059
7 0.1293

0.0000
1,154.291
3 Unmitigated Construction
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Year
tons/yr
MT/yr
2021

0.4886

4.5855

3.9430

0.0125

0.7406

0.1353

0.8759

0.2334

0.1259

0.3593

0.0000
1,151.059
4 1,151.059
4 0.1293

0.0000
1,154.290
9 2022

3.2698

2.4393

2.8361

9.6400e-
003

0.5550

0.0604

0.6154

0.1494

0.0569

0.2063

0.0000
886.7646
886.7646

0.0684

0.0000
888.4736
Maximum

3.2698

4.5855

3.9430

0.0125

0.7406

0.1353

0.8759

0.2334

0.1259

0.3593

0.0000
1,151.059
4 1,151.059
4 0.1293

0.0000
1,154.290
9 Mitigated Construction
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio-CO2
Total CO2
CH4
N20
CO2e
Percent
Reduction

0.00 0.00

0.00 0.00

13.53 0.00

11.97 20.02

0.00 14.49

0.00 0.00

0.00 0.00

0.00 0.00
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

2.2 Overall Operational
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Area

2.5314

7.0000e-
005

7.9600e-
003

0.0000

3.0000e-
005

3.0000e-
005

3.0000e-
005

3.0000e-
005

0.0000

0.0155

0.0155

4.0000e-
005

0.0000

0.0165
Energy

6.6000e-
003

0.0600

0.0504

3.6000e-
004

4.5600e-
003

4.5600e-
003

4.5600e-
003

4.5600e-
003

0.0000
602.6636
602.6636

0.0237

3.9200e-
003
604.4238
Mobile

0.2256

0.3844

4.5506

0.0162

1.7541

0.0111

1.7652

0.4655

0.0102

0.4758

0.0000
1,465.412
8 1,465.412
8 0.0416

0.0000
1,466.452
1 Waste

0.0000

0.0000

0.0000

0.0000
115.0776

0.0000
115.0776

6.8009

0.0000
285.0999
Water

0.0000

0.0000

0.0000

0.0000

44.2464
650.7246
694.9710

4.5717

0.1106
842.2230
Total

2.7636

0.4445

4.6089

0.0166

1.7541

0.0157

1.7698

0.4655

0.0148

0.4804
159.3240
2,718.816
5 2,878.140
6 11.4379

0.1145
3,198.215
3 Unmitigated Operational
Quarter
Start Date
End Date
Maximum Unmitigated ROG + NOX (tons/quarter)
Maximum Mitigated ROG + NOX (tons/quarter)
1 4-1-2021
6-30-2021

1.8445

1.8445
2 7-1-2021
9-30-2021

1.5867

1.5867
3 10-1-2021
12-31-2021

1.6006

1.6006
4 1-1-2022
3-31-2022

2.7104

2.7104
5 4-1-2022
6-30-2022

2.9920

2.9920
Highest

2.9920

2.9920
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

2.2 Overall Operational
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Area

2.5314

7.0000e-
005

7.9600e-
003

0.0000

3.0000e-
005

3.0000e-
005

3.0000e-
005

3.0000e-
005

0.0000

0.0155

0.0155

4.0000e-
005

0.0000

0.0165
Energy

6.6000e-
003

0.0600

0.0504

3.6000e-
004

4.5600e-
003

4.5600e-
003

4.5600e-
003

4.5600e-
003

0.0000
602.6636
602.6636

0.0237

3.9200e-
003
604.4238
Mobile

0.2256

0.3844

4.5506

0.0162

1.7541

0.0111

1.7652

0.4655

0.0102

0.4758

0.0000
1,465.412
8 1,465.412
8 0.0416

0.0000
1,466.452
1 Waste

0.0000

0.0000

0.0000

0.0000
115.0776

0.0000
115.0776

6.8009

0.0000
285.0999
Water

0.0000

0.0000

0.0000

0.0000

44.2464
650.7246
694.9710

4.5717

0.1106
842.2230
Total

2.7636

0.4445

4.6089

0.0166

1.7541

0.0157

1.7698

0.4655

0.0148

0.4804
159.3240
2,718.816
5 2,878.140
6 11.4379

0.1145
3,198.215
3 Mitigated Operational

3.0 Construction Detail
Construction Phase
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio-CO2
Total CO2
CH4
N20
CO2e
Percent
Reduction

0.00 0.00

0.00 0.00

0.00 0.00

0.00 0.00

0.00 0.00

0.00 0.00

0.00 0.00

0.00 0.00
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

Phase
Number
Phase Name
Phase Type
Start Date
End Date
Num Days
Week
Num Days
Phase Description
1 Site Preparation
Site Preparation
4/1/2021
4/26/2021
5 18
2 Grading
Grading
4/27/2021
6/30/2021
5 47
3 Building Construction
Building Construction
7/1/2021
6/6/2022
5 243
4 Architectural Coatings
Architectural Coating
1/27/2022
6/30/2022
5 111
5 Paving
Paving
6/7/2022
6/30/2022
5 18
OffRoad Equipment
Residential Indoor: 0; Residential Outdoor: 0; Non-Residential Indoor: 904,650; Non-Residential Outdoor: 301,550; Striped Parking Area:
54,886 (Architectural Coating
±
sqft)
Acres of Grading (Site Preparation Phase): 0
Acres of Grading (Grading Phase): 117.5
Acres of Paving: 21
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

Phase Name
Offroad Equipment Type
Amount
Usage Hours
Horse Power
Load Factor
Site Preparation
Rubber Tired Dozers
3 8.00
247

0.40 Site Preparation
Tractors/Loaders/Backhoes
4 8.00
97 0.37
Grading
Excavators
2 8.00
158

0.38 Grading
Graders
1 8.00
187

0.41 Grading
Rubber Tired Dozers
1 8.00
247

0.40 Grading
Scrapers
2 8.00
367

0.48 Grading
Tractors/Loaders/Backhoes
2 8.00
97 0.37
Building Construction
Cranes
1 7.00
231

0.29 Building Construction
Forklifts
3 8.00
89 0.20
Building Construction
Generator Sets
1 8.00
84 0.74
Building Construction
Tractors/Loaders/Backhoes
3 7.00
97 0.37
Building Construction
Welders
1 8.00
46 0.45
Paving
Pavers
2 8.00
130

0.42 Paving
Paving Equipment
2 8.00
132

0.36 Paving
Rollers
2 8.00
80 0.38
Architectural Coatings
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
7 18.00

0.00 0.00

14.70 6.90

20.00 LD_Mix
HDT_Mix
HHDT
Grading
8 20.00

0.00 5,000.00

14.70 6.90

1.00 LD_Mix
HDT_Mix
HHDT
Building Construction
9 638.00
249.00

0.00 14.70

6.90 20.00
LD_Mix
HDT_Mix
HHDT
Paving
6 15.00

0.00 0.00

14.70 6.90

20.00 LD_Mix
HDT_Mix
HHDT
Architectural Coatings
1 128.00

0.00 0.00

14.70 6.90

20.00 LD_Mix
HDT_Mix
HHDT
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.2 Site Preparation - 2021
ROG
NOx
CO
SO2
Fugitive
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

0.1626

0.0000

0.1626

0.0894

0.0000

0.0894

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Off-Road

0.0350

0.3645

0.1904

3.4000e-
004

0.0184

0.0184

0.0169

0.0169

0.0000

30.0922

30.0922

9.7300e-
003

0.0000

30.3355
Total

0.0350

0.3645

0.1904

3.4000e-
004

0.1626

0.0184

0.1810

0.0894

0.0169

0.1063

0.0000

30.0922

30.0922

9.7300e-
003

0.0000

30.3355
Unmitigated Construction On-Site

3.1 Mitigation Measures Construction
Water Exposed Area
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.2 Site Preparation - 2021
ROG
NOx
CO
SO2
Fugitive
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

6.7000e-
004

5.0000e-
004

5.6500e-
003

2.0000e-
005

1.7800e-
003

1.0000e-
005

1.7900e-
003

4.7000e-
004

1.0000e-
005

4.8000e-
004

0.0000

1.5498

1.5498

4.0000e-
005

0.0000

1.5508
Total

6.7000e-
004

5.0000e-
004

5.6500e-
003

2.0000e-
005

1.7800e-
003

1.0000e-
005

1.7900e-
003

4.7000e-
004

1.0000e-
005

4.8000e-
004

0.0000

1.5498

1.5498

4.0000e-
005

0.0000

1.5508
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

0.0732

0.0000

0.0732

0.0402

0.0000

0.0402

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Off-Road

0.0350

0.3645

0.1904

3.4000e-
004

0.0184

0.0184

0.0169

0.0169

0.0000

30.0921

30.0921

9.7300e-
003

0.0000

30.3354
Total

0.0350

0.3645

0.1904

3.4000e-
004

0.0732

0.0184

0.0916

0.0402

0.0169

0.0572

0.0000

30.0921

30.0921

9.7300e-
003

0.0000

30.3354
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.2 Site Preparation - 2021
ROG
NOx
CO
SO2
Fugitive
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

6.7000e-
004

5.0000e-
004

5.6500e-
003

2.0000e-
005

1.7800e-
003

1.0000e-
005

1.7900e-
003

4.7000e-
004

1.0000e-
005

4.8000e-
004

0.0000

1.5498

1.5498

4.0000e-
005

0.0000

1.5508
Total

6.7000e-
004

5.0000e-
004

5.6500e-
003

2.0000e-
005

1.7800e-
003

1.0000e-
005

1.7900e-
003

4.7000e-
004

1.0000e-
005

4.8000e-
004

0.0000

1.5498

1.5498

4.0000e-
005

0.0000

1.5508
Mitigated Construction Off-Site

3.3 Grading - 2021
ROG
NOx
CO
SO2
Fugitive
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

0.2061

0.0000

0.2061

0.0849

0.0000

0.0849

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Off-Road

0.0985

1.0904

0.7256

1.4600e-
003

0.0467

0.0467

0.0429

0.0429

0.0000
128.0632
128.0632

0.0414

0.0000
129.0987
Total

0.0985

1.0904

0.7256

1.4600e-
003

0.2061

0.0467

0.2528

0.0849

0.0429

0.1278

0.0000
128.0632
128.0632

0.0414

0.0000
129.0987
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.3 Grading - 2021
ROG
NOx
CO
SO2
Fugitive
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

4.8200e-
003

0.2497

0.0374

3.3000e-
004

2.2000e-
003

2.0000e-
004

2.3900e-
003

6.1000e-
004

1.9000e-
004

8.0000e-
004

0.0000

32.1224

32.1224

4.5000e-
003

0.0000

32.2350
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

1.9500e-
003

1.4500e-
003

0.0164

5.0000e-
005

5.1600e-
003

4.0000e-
005

5.2000e-
003

1.3700e-
003

4.0000e-
005

1.4100e-
003

0.0000

4.4963

4.4963

1.2000e-
004

0.0000

4.4993
Total

6.7700e-
003

0.2512

0.0538

3.8000e-
004

7.3600e-
003

2.4000e-
004

7.5900e-
003

1.9800e-
003

2.3000e-
004

2.2100e-
003

0.0000

36.6186

36.6186

4.6200e-
003

0.0000

36.7343
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

0.0927

0.0000

0.0927

0.0382

0.0000

0.0382

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Off-Road

0.0985

1.0904

0.7256

1.4600e-
003

0.0467

0.0467

0.0429

0.0429

0.0000
128.0631
128.0631

0.0414

0.0000
129.0985
Total

0.0985

1.0904

0.7256

1.4600e-
003

0.0927

0.0467

0.1394

0.0382

0.0429

0.0811

0.0000
128.0631
128.0631

0.0414

0.0000
129.0985
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.3 Grading - 2021
ROG
NOx
CO
SO2
Fugitive
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

4.8200e-
003

0.2497

0.0374

3.3000e-
004

2.2000e-
003

2.0000e-
004

2.3900e-
003

6.1000e-
004

1.9000e-
004

8.0000e-
004

0.0000

32.1224

32.1224

4.5000e-
003

0.0000

32.2350
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

1.9500e-
003

1.4500e-
003

0.0164

5.0000e-
005

5.1600e-
003

4.0000e-
005

5.2000e-
003

1.3700e-
003

4.0000e-
005

1.4100e-
003

0.0000

4.4963

4.4963

1.2000e-
004

0.0000

4.4993
Total

6.7700e-
003

0.2512

0.0538

3.8000e-
004

7.3600e-
003

2.4000e-
004

7.5900e-
003

1.9800e-
003

2.3000e-
004

2.2100e-
003

0.0000

36.6186

36.6186

4.6200e-
003

0.0000

36.7343
Mitigated Construction Off-Site

3.4 Building Construction - 2021
ROG
NOx
CO
SO2
Fugitive
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

0.1255

1.1505

1.0940

1.7800e-
003

0.0633

0.0633

0.0595

0.0595

0.0000
152.8806
152.8806

0.0369

0.0000
153.8027
Total

0.1255

1.1505

1.0940

1.7800e-
003

0.0633

0.0633

0.0595

0.0595

0.0000
152.8806
152.8806

0.0369

0.0000
153.8027
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.4 Building Construction - 2021
ROG
NOx
CO
SO2
Fugitive
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

0.0473

1.5985

0.4040

4.1100e-
003

0.1036

3.2600e-
003

0.1068

0.0299

3.1100e-
003

0.0330

0.0000
399.0283
399.0283

0.0257

0.0000
399.6714
Worker

0.1750

0.1299

1.4695

4.4600e-
003

0.4620

3.4800e-
003

0.4655

0.1227

3.2100e-
003

0.1259

0.0000
402.8270
402.8270

0.0108

0.0000
403.0980
Total

0.2223

1.7284

1.8735

8.5700e-
003

0.5656

6.7400e-
003

0.5723

0.1526

6.3200e-
003

0.1589

0.0000
801.8554
801.8554

0.0366

0.0000
802.7694
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

0.1255

1.1505

1.0940

1.7800e-
003

0.0633

0.0633

0.0595

0.0595

0.0000
152.8804
152.8804

0.0369

0.0000
153.8025
Total

0.1255

1.1505

1.0940

1.7800e-
003

0.0633

0.0633

0.0595

0.0595

0.0000
152.8804
152.8804

0.0369

0.0000
153.8025
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.4 Building Construction - 2021
ROG
NOx
CO
SO2
Fugitive
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

0.0473

1.5985

0.4040

4.1100e-
003

0.1036

3.2600e-
003

0.1068

0.0299

3.1100e-
003

0.0330

0.0000
399.0283
399.0283

0.0257

0.0000
399.6714
Worker

0.1750

0.1299

1.4695

4.4600e-
003

0.4620

3.4800e-
003

0.4655

0.1227

3.2100e-
003

0.1259

0.0000
402.8270
402.8270

0.0108

0.0000
403.0980
Total

0.2223

1.7284

1.8735

8.5700e-
003

0.5656

6.7400e-
003

0.5723

0.1526

6.3200e-
003

0.1589

0.0000
801.8554
801.8554

0.0366

0.0000
802.7694
Mitigated Construction Off-Site

3.4 Building Construction - 2022
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Off-Road

0.0947

0.8667

0.9082

1.4900e-
003

0.0449

0.0449

0.0422

0.0422

0.0000
128.6075
128.6075

0.0308

0.0000
129.3778
Total

0.0947

0.8667

0.9082

1.4900e-
003

0.0449

0.0449

0.0422

0.0422

0.0000
128.6075
128.6075

0.0308

0.0000
129.3778
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.4 Building Construction - 2022
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Hauling

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Vendor

0.0373

1.2755

0.3217

3.4200e-
003

0.0871

2.3800e-
003

0.0895

0.0251

2.2800e-
003

0.0274

0.0000
332.5824
332.5824

0.0209

0.0000
333.1044
Worker

0.1382

0.0987

1.1411

3.6100e-
003

0.3885

2.8500e-
003

0.3913

0.1032

2.6200e-
003

0.1058

0.0000
326.6079
326.6079

8.2300e-
003

0.0000
326.8138
Total

0.1755

1.3741

1.4628

7.0300e-
003

0.4756

5.2300e-
003

0.4808

0.1283

4.9000e-
003

0.1332

0.0000
659.1903
659.1903

0.0291

0.0000
659.9182
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

0.0947

0.8667

0.9082

1.4900e-
003

0.0449

0.0449

0.0422

0.0422

0.0000
128.6074
128.6074

0.0308

0.0000
129.3776
Total

0.0947

0.8667

0.9082

1.4900e-
003

0.0449

0.0449

0.0422

0.0422

0.0000
128.6074
128.6074

0.0308

0.0000
129.3776
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.4 Building Construction - 2022
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Hauling

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Vendor

0.0373

1.2755

0.3217

3.4200e-
003

0.0871

2.3800e-
003

0.0895

0.0251

2.2800e-
003

0.0274

0.0000
332.5824
332.5824

0.0209

0.0000
333.1044
Worker

0.1382

0.0987

1.1411

3.6100e-
003

0.3885

2.8500e-
003

0.3913

0.1032

2.6200e-
003

0.1058

0.0000
326.6079
326.6079

8.2300e-
003

0.0000
326.8138
Total

0.1755

1.3741

1.4628

7.0300e-
003

0.4756

5.2300e-
003

0.4808

0.1283

4.9000e-
003

0.1332

0.0000
659.1903
659.1903

0.0291

0.0000
659.9182
Mitigated Construction Off-Site

3.5 Architectural Coatings - 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
Archit. Coating

2.9226

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Off-Road

0.0114

0.0782

0.1007

1.6000e-
004

4.5400e-
003

4.5400e-
003

4.5400e-
003

4.5400e-
003

0.0000

14.1706

14.1706

9.2000e-
004

0.0000

14.1936
Total

2.9339

0.0782

0.1007

1.6000e-
004

4.5400e-
003

4.5400e-
003

4.5400e-
003

4.5400e-
003

0.0000

14.1706

14.1706

9.2000e-
004

0.0000

14.1936
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.5 Architectural Coatings - 2022
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Hauling

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Vendor

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Worker

0.0277

0.0198

0.2289

7.2000e-
004

0.0779

5.7000e-
004

0.0785

0.0207

5.3000e-
004

0.0212

0.0000

65.5264

65.5264

1.6500e-
003

0.0000

65.5677
Total

0.0277

0.0198

0.2289

7.2000e-
004

0.0779

5.7000e-
004

0.0785

0.0207

5.3000e-
004

0.0212

0.0000

65.5264

65.5264

1.6500e-
003

0.0000

65.5677
Unmitigated Construction Off-Site
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Archit. Coating

2.9226

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Off-Road

0.0114

0.0782

0.1007

1.6000e-
004

4.5400e-
003

4.5400e-
003

4.5400e-
003

4.5400e-
003

0.0000

14.1705

14.1705

9.2000e-
004

0.0000

14.1936
Total

2.9339

0.0782

0.1007

1.6000e-
004

4.5400e-
003

4.5400e-
003

4.5400e-
003

4.5400e-
003

0.0000

14.1705

14.1705

9.2000e-
004

0.0000

14.1936
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.5 Architectural Coatings - 2022
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Hauling

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Vendor

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Worker

0.0277

0.0198

0.2289

7.2000e-
004

0.0779

5.7000e-
004

0.0785

0.0207

5.3000e-
004

0.0212

0.0000

65.5264

65.5264

1.6500e-
003

0.0000

65.5677
Total

0.0277

0.0198

0.2289

7.2000e-
004

0.0779

5.7000e-
004

0.0785

0.0207

5.3000e-
004

0.0212

0.0000

65.5264

65.5264

1.6500e-
003

0.0000

65.5677
Mitigated Construction Off-Site

3.6 Paving - 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

9.9300e-
003

0.1001

0.1312

2.1000e-
004

5.1100e-
003

5.1100e-
003

4.7000e-
003

4.7000e-
003

0.0000

18.0248

18.0248

5.8300e-
003

0.0000

18.1705
Paving

0.0275

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Total

0.0374

0.1001

0.1312

2.1000e-
004

5.1100e-
003

5.1100e-
003

4.7000e-
003

4.7000e-
003

0.0000

18.0248

18.0248

5.8300e-
003

0.0000

18.1705
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

3.6 Paving - 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

5.3000e-
004

3.8000e-
004

4.3500e-
003

1.0000e-
005

1.4800e-
003

1.0000e-
005

1.4900e-
003

3.9000e-
004

1.0000e-
005

4.0000e-
004

0.0000

1.2452

1.2452

3.0000e-
005

0.0000

1.2460
Total

5.3000e-
004

3.8000e-
004

4.3500e-
003

1.0000e-
005

1.4800e-
003

1.0000e-
005

1.4900e-
003

3.9000e-
004

1.0000e-
005

4.0000e-
004

0.0000

1.2452

1.2452

3.0000e-
005

0.0000

1.2460
Unmitigated Construction Off-Site
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Off-Road

9.9300e-
003

0.1001

0.1312

2.1000e-
004

5.1100e-
003

5.1100e-
003

4.7000e-
003

4.7000e-
003

0.0000

18.0248

18.0248

5.8300e-
003

0.0000

18.1705
Paving

0.0275

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Total

0.0374

0.1001

0.1312

2.1000e-
004

5.1100e-
003

5.1100e-
003

4.7000e-
003

4.7000e-
003

0.0000

18.0248

18.0248

5.8300e-
003

0.0000

18.1705
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

4.0 Operational Detail - Mobile

4.1 Mitigation Measures Mobile

3.6 Paving - 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

5.3000e-
004

3.8000e-
004

4.3500e-
003

1.0000e-
005

1.4800e-
003

1.0000e-
005

1.4900e-
003

3.9000e-
004

1.0000e-
005

4.0000e-
004

0.0000

1.2452

1.2452

3.0000e-
005

0.0000

1.2460
Total

5.3000e-
004

3.8000e-
004

4.3500e-
003

1.0000e-
005

1.4800e-
003

1.0000e-
005

1.4900e-
003

3.9000e-
004

1.0000e-
005

4.0000e-
004

0.0000

1.2452

1.2452

3.0000e-
005

0.0000

1.2460
Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

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

0.2256

0.3844

4.5506

0.0162

1.7541

0.0111

1.7652

0.4655

0.0102

0.4758

0.0000
1,465.412
8 1,465.412
8 0.0416

0.0000
1,466.452
1 Unmitigated

0.2256

0.3844

4.5506

0.0162

1.7541

0.0111

1.7652

0.4655

0.0102

0.4758

0.0000
1,465.412
8 1,465.412
8 0.0416

0.0000
1,466.452
1 4.2 Trip Summary Information

4.3 Trip Type Information
Average Daily Trip Rate
Unmitigated
Mitigated
Land Use
Weekday
Saturday
Sunday
Annual VMT
Annual VMT
Other Asphalt Surfaces

0.00 0.00

0.00 Parking Lot

0.00 0.00

0.00 Unrefrigerated Warehouse-No Rail
572.95
572.95
572.95
4,706,914
4,706,914
Total
572.95
572.95
572.95
4,706,914
4,706,914
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
Other Asphalt Surfaces

16.60 8.40

6.90 0.00

0.00 0.00
0 0
0 Parking Lot

16.60 8.40

6.90 0.00

0.00 0.00
0 0
0 Unrefrigerated Warehouse-No
Rail

24.20 24.20

24.20 59.00

0.00 41.00
92 5
3 4.4 Fleet Mix
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

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

0.0000

0.0000

0.0000

0.0000

0.0000
537.3307
537.3307

0.0225

2.7200e-
003
538.7026
Electricity
Unmitigated

0.0000

0.0000

0.0000

0.0000

0.0000
537.3307
537.3307

0.0225

2.7200e-
003
538.7026
NaturalGas
Mitigated

6.6000e-
003

0.0600

0.0504

3.6000e-
004

4.5600e-
003

4.5600e-
003

4.5600e-
003

4.5600e-
003

0.0000

65.3329

65.3329

1.2500e-
003

1.2000e-
003

65.7212
NaturalGas
Unmitigated

6.6000e-
003

0.0600

0.0504

3.6000e-
004

4.5600e-
003

4.5600e-
003

4.5600e-
003

4.5600e-
003

0.0000

65.3329

65.3329

1.2500e-
003

1.2000e-
003

65.7212

5.1 Mitigation Measures Energy
Land Use
LDA
LDT1
LDT2
MDV
LHD1
LHD2
MHD
HHD
OBUS
UBUS
MCY
SBUS
MH
Other Asphalt Surfaces

0.552712

0.042774

0.202769

0.116939

0.015078

0.005847

0.021692

0.031910

0.002110

0.001769

0.004822

0.000710

0.000869
Parking Lot

0.552712

0.042774

0.202769

0.116939

0.015078

0.005847

0.021692

0.031910

0.002110

0.001769

0.004822

0.000710

0.000869
Unrefrigerated Warehouse-No
Rail

0.598766

0.047129

0.218324

0.130606

0.000000

0.000000

0.000000

0.000000

0.000000

0.000000

0.005175

0.000000

0.000000
Historical Energy Use: N
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Land Use
kBTU/yr
tons/yr
MT/yr
Other Asphalt
Surfaces
0 0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Parking Lot
0 0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Unrefrigerated
Warehouse-No
Rail

1.22429e
+006

6.6000e-
003

0.0600

0.0504

3.6000e-
004

4.5600e-
003

4.5600e-
003

4.5600e-
003

4.5600e-
003

0.0000

65.3329

65.3329

1.2500e-
003

1.2000e-
003

65.7212
Total

6.6000e-
003

0.0600

0.0504

3.6000e-
004

4.5600e-
003

4.5600e-
003

4.5600e-
003

4.5600e-
003

0.0000

65.3329

65.3329

1.2500e-
003

1.2000e-
003

65.7212
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
Other Asphalt
Surfaces
0 0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Parking Lot
0 0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Unrefrigerated
Warehouse-No
Rail

1.22429e
+006

6.6000e-
003

0.0600

0.0504

3.6000e-
004

4.5600e-
003

4.5600e-
003

4.5600e-
003

4.5600e-
003

0.0000

65.3329

65.3329

1.2500e-
003

1.2000e-
003

65.7212
Total

6.6000e-
003

0.0600

0.0504

3.6000e-
004

4.5600e-
003

4.5600e-
003

4.5600e-
003

4.5600e-
003

0.0000

65.3329

65.3329

1.2500e-
003

1.2000e-
003

65.7212
Mitigated
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

5.3 Energy by Land Use - Electricity
Electricity
Use
Total CO2
CH4
N2O
CO2e
Land Use
kWh/yr
MT/yr
Other Asphalt
Surfaces
0 0.0000

0.0000

0.0000

0.0000
Parking Lot
76230

27.3154

1.1400e-
003

1.4000e-
004

27.3852
Unrefrigerated
Warehouse-No
Rail

1.42332e
+006
510.0153

0.0213

2.5800e-
003
511.3174
Total
537.3307

0.0224

2.7200e-
003
538.7026
Unmitigated
Electricity
Use
Total CO2
CH4
N2O
CO2e
Land Use
kWh/yr
MT/yr
Other Asphalt
Surfaces
0 0.0000

0.0000

0.0000

0.0000
Parking Lot
76230

27.3154

1.1400e-
003

1.4000e-
004

27.3852
Unrefrigerated
Warehouse-No
Rail

1.42332e
+006
510.0153

0.0213

2.5800e-
003
511.3174
Total
537.3307

0.0224

2.7200e-
003
538.7026
Mitigated
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

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
tons/yr
MT/yr
Mitigated

2.5314

7.0000e-
005

7.9600e-
003

0.0000

3.0000e-
005

3.0000e-
005

3.0000e-
005

3.0000e-
005

0.0000

0.0155

0.0155

4.0000e-
005

0.0000

0.0165
Unmitigated

2.5314

7.0000e-
005

7.9600e-
003

0.0000

3.0000e-
005

3.0000e-
005

3.0000e-
005

3.0000e-
005

0.0000

0.0155

0.0155

4.0000e-
005

0.0000

0.0165
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

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

0.2923

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Consumer
Products

2.2384

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Landscaping

7.4000e-
004

7.0000e-
005

7.9600e-
003

0.0000

3.0000e-
005

3.0000e-
005

3.0000e-
005

3.0000e-
005

0.0000

0.0155

0.0155

4.0000e-
005

0.0000

0.0165
Total

2.5314

7.0000e-
005

7.9600e-
003

0.0000

3.0000e-
005

3.0000e-
005

3.0000e-
005

3.0000e-
005

0.0000

0.0155

0.0155

4.0000e-
005

0.0000

0.0165
Unmitigated
ROG
NOx
CO
SO2
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

0.2923

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Consumer
Products

2.2384

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Landscaping

7.4000e-
004

7.0000e-
005

7.9600e-
003

0.0000

3.0000e-
005

3.0000e-
005

3.0000e-
005

3.0000e-
005

0.0000

0.0155

0.0155

4.0000e-
005

0.0000

0.0165
Total

2.5314

7.0000e-
005

7.9600e-
003

0.0000

3.0000e-
005

3.0000e-
005

3.0000e-
005

3.0000e-
005

0.0000

0.0155

0.0155

4.0000e-
005

0.0000

0.0165
Mitigated
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

7.1 Mitigation Measures Water
Total CO2
CH4
N2O
CO2e
Category
MT/yr
Mitigated
694.9710

4.5717

0.1106
842.2230
Unmitigated
694.9710

4.5717

0.1106
842.2230

7.2 Water by Land Use
Indoor/Out
door Use
Total CO2
CH4
N2O
CO2e
Land Use
Mgal
MT/yr
Other Asphalt
Surfaces
0 / 0

0.0000

0.0000

0.0000

0.0000
Parking Lot
0 / 0

0.0000

0.0000

0.0000

0.0000
Unrefrigerated
Warehouse-No
Rail
139.467 /
0 694.9710

4.5717

0.1106
842.2230
Total
694.9710

4.5717

0.1106
842.2230
Unmitigated

7.0 Water Detail
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

8.1 Mitigation Measures Waste

7.2 Water by Land Use
Indoor/Out
door Use
Total CO2
CH4
N2O
CO2e
Land Use
Mgal
MT/yr
Other Asphalt
Surfaces
0 / 0

0.0000

0.0000

0.0000

0.0000
Parking Lot
0 / 0

0.0000

0.0000

0.0000

0.0000
Unrefrigerated
Warehouse-No
Rail
139.467 /
0 694.9710

4.5717

0.1106
842.2230
Total
694.9710

4.5717

0.1106
842.2230
Mitigated

8.0 Waste Detail
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

Total CO2
CH4
N2O
CO2e
MT/yr
Mitigated
115.0776

6.8009

0.0000
285.0999
Unmitigated
115.0776

6.8009

0.0000
285.0999
Category/Year

8.2 Waste by Land Use
Waste
Disposed
Total CO2
CH4
N2O
CO2e
Land Use
tons
MT/yr
Other Asphalt
Surfaces
0 0.0000

0.0000

0.0000

0.0000
Parking Lot
0 0.0000

0.0000

0.0000

0.0000
Unrefrigerated
Warehouse-No
Rail
566.91
115.0776

6.8009

0.0000
285.0999
Total
115.0776

6.8009

0.0000
285.0999
Unmitigated
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

8.2 Waste by Land Use
Waste
Disposed
Total CO2
CH4
N2O
CO2e
Land Use
tons
MT/yr
Other Asphalt
Surfaces
0 0.0000

0.0000

0.0000

0.0000
Parking Lot
0 0.0000

0.0000

0.0000

0.0000
Unrefrigerated
Warehouse-No
Rail
566.91
115.0776

6.8009

0.0000
285.0999
Total
115.0776

6.8009

0.0000
285.0999
Mitigated

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

10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type
Number
Hours/Day
Hours/Year
Horse Power
Load Factor
Fuel Type
Boilers
Equipment Type
Number
Heat Input/Day
Heat Input/Year
Boiler Rating
Fuel Type
User Defined Equipment
Equipment Type
Number
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

11.0 Vegetation
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:41 AM

9309 Sycamore Hills Distribution Center - Passenger Cars - South Coast Air Basin, Annual

1.1 Land Usage
Land Uses
Size
Metric
Lot Acreage
Floor Surface Area
Population
Unrefrigerated Warehouse-No Rail
603.10
1000sqft

16.00 603,100.00
0 Other Asphalt Surfaces

16.00 Acre

16.00 696,960.00
0 Parking Lot

5.00 Acre

5.00 217,800.00
0 1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
10 Wind Speed (m/s)
Precipitation Freq (Days)

2.2 31

1.3 User Entered Comments & Non-Default Data

1.0 Project Characteristics
Utility Company
Riverside Public Utilities
2023
Operational Year
CO2 Intensity
(lb/MWhr)
789.98

0.033
CH4 Intensity
(lb/MWhr)

0.004
N2O Intensity
(lb/MWhr)
9309 Sycamore Hills Distribution Center - Trucks
South Coast Air Basin, Annual
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

Project Characteristics - Current 2021 Riverside Public Utilities intensity factors Land Use -
37 acre site
603,100
sf
Construction Phase - Grading/Prliminary Road Construction - 3 months
Building Permit/Building Construction -
12 months
Off-road Equipment -
Off-road Equipment -
Off-road Equipment -
Trips and VMT - Soil would be balanced between Parcel 1 and 2 Grading -
Architectural Coating -
Vehicle Trips -
847
ADT
Trucks -
274
(

0.45 trips/ksf)

38.7 mile trip length
Area Coating -
Energy Use -
Water And Wastewater -
Construction Off-road Equipment Mitigation -
Waste Mitigation -
Fleet Mix - Trucks only, mix per TIA
Table Name
Column Name
Default Value
New Value
tblConstructionPhase
NumDays

30.00 18.00
tblConstructionPhase
NumDays

75.00 47.00
tblConstructionPhase
NumDays
740.00
243.00
tblConstructionPhase
NumDays

55.00 111.00
tblConstructionPhase
NumDays

55.00 18.00
tblFleetMix
HHD

0.03 0.37
tblFleetMix
LDA

0.55 0.00
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

tblFleetMix
LDT1

0.04 0.00
tblFleetMix
LDT2

0.20 0.00
tblFleetMix
LHD1

0.02 0.17
tblFleetMix
LHD2

5.8470e-003

0.21 tblFleetMix
MCY

4.8220e-003

0.00 tblFleetMix
MDV

0.12 0.00
tblFleetMix
MH

8.6900e-004

0.00 tblFleetMix
MHD

0.02 0.25
tblFleetMix
OBUS

2.1100e-003

0.00 tblFleetMix
SBUS

7.1000e-004

0.00 tblFleetMix
UBUS

1.7690e-003

0.00 tblGrading
MaterialExported

0.00 40,000.00
tblLandUse
LotAcreage

13.85 16.00
tblProjectCharacteristics
CH4IntensityFactor

0.029

0.033
tblProjectCharacteristics
CO2IntensityFactor
1325.65
789.98
tblProjectCharacteristics
N2OIntensityFactor

0.006

0.004
tblTripsAndVMT
HaulingTripLength

20.00 1.00
tblVehicleTrips
CC_TL

8.40 38.70
tblVehicleTrips
CNW_TL

6.90 38.70
tblVehicleTrips
CW_TL

16.60 38.70
tblVehicleTrips
DV_TP

5.00 0.00
tblVehicleTrips
PB_TP

3.00 0.00
tblVehicleTrips
PR_TP

92.00 100.00
tblVehicleTrips
ST_TR

1.68 0.45
tblVehicleTrips
SU_TR

1.68 0.45
tblVehicleTrips
WD_TR

1.68 0.45
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

2.0 Emissions Summary

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
2021

0.4886

4.5855

3.9430

0.0125

0.9434

0.1353

1.0787

0.3293

0.1259

0.4552

0.0000
1,151.059
7 1,151.059
7 0.1293

0.0000
1,154.291
3 2022

3.2698

2.4393

2.8361

9.6400e-
003

0.5550

0.0604

0.6154

0.1494

0.0569

0.2063

0.0000
886.7648
886.7648

0.0684

0.0000
888.4738
Maximum

3.2698

4.5855

3.9430

0.0125

0.9434

0.1353

1.0787

0.3293

0.1259

0.4552

0.0000
1,151.059
7 1,151.059
7 0.1293

0.0000
1,154.291
3 Unmitigated Construction
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Year
tons/yr
MT/yr
2021

0.4886

4.5855

3.9430

0.0125

0.7406

0.1353

0.8759

0.2334

0.1259

0.3593

0.0000
1,151.059
4 1,151.059
4 0.1293

0.0000
1,154.290
9 2022

3.2698

2.4393

2.8361

9.6400e-
003

0.5550

0.0604

0.6154

0.1494

0.0569

0.2063

0.0000
886.7646
886.7646

0.0684

0.0000
888.4736
Maximum

3.2698

4.5855

3.9430

0.0125

0.7406

0.1353

0.8759

0.2334

0.1259

0.3593

0.0000
1,151.059
4 1,151.059
4 0.1293

0.0000
1,154.290
9 Mitigated Construction
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

2.2 Overall Operational
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Area

2.5314

7.0000e-
005

7.9600e-
003

0.0000

3.0000e-
005

3.0000e-
005

3.0000e-
005

3.0000e-
005

0.0000

0.0155

0.0155

4.0000e-
005

0.0000

0.0165
Energy

6.6000e-
003

0.0600

0.0504

3.6000e-
004

4.5600e-
003

4.5600e-
003

4.5600e-
003

4.5600e-
003

0.0000
602.6636
602.6636

0.0237

3.9200e-
003
604.4238
Mobile

0.2951

6.7559

3.0128

0.0447

1.6875

0.0277

1.7152

0.4817

0.0265

0.5082

0.0000
4,316.199
7 4,316.199
7 0.1678

0.0000
4,320.394
6 Waste

0.0000

0.0000

0.0000

0.0000
115.0776

0.0000
115.0776

6.8009

0.0000
285.0999
Water

0.0000

0.0000

0.0000

0.0000

44.2464
650.7246
694.9710

4.5717

0.1106
842.2230
Total

2.8331

6.8160

3.0712

0.0451

1.6875

0.0323

1.7198

0.4817

0.0311

0.5128
159.3240
5,569.603
4 5,728.927
4 11.5641

0.1145
6,052.157
8 Unmitigated Operational
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio-CO2
Total CO2
CH4
N20
CO2e
Percent
Reduction

0.00 0.00

0.00 0.00

13.53 0.00

11.97 20.02

0.00 14.49

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 4-1-2021
6-30-2021

1.8445

1.8445
2 7-1-2021
9-30-2021

1.5867

1.5867
3 10-1-2021
12-31-2021

1.6006

1.6006
4 1-1-2022
3-31-2022

2.7104

2.7104
5 4-1-2022
6-30-2022

2.9920

2.9920
Highest

2.9920

2.9920
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

2.2 Overall Operational
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Area

2.5314

7.0000e-
005

7.9600e-
003

0.0000

3.0000e-
005

3.0000e-
005

3.0000e-
005

3.0000e-
005

0.0000

0.0155

0.0155

4.0000e-
005

0.0000

0.0165
Energy

6.6000e-
003

0.0600

0.0504

3.6000e-
004

4.5600e-
003

4.5600e-
003

4.5600e-
003

4.5600e-
003

0.0000
602.6636
602.6636

0.0237

3.9200e-
003
604.4238
Mobile

0.2951

6.7559

3.0128

0.0447

1.6875

0.0277

1.7152

0.4817

0.0265

0.5082

0.0000
4,316.199
7 4,316.199
7 0.1678

0.0000
4,320.394
6 Waste

0.0000

0.0000

0.0000

0.0000
115.0776

0.0000
115.0776

6.8009

0.0000
285.0999
Water

0.0000

0.0000

0.0000

0.0000

44.2464
650.7246
694.9710

4.5717

0.1106
842.2230
Total

2.8331

6.8160

3.0712

0.0451

1.6875

0.0323

1.7198

0.4817

0.0311

0.5128
159.3240
5,569.603
4 5,728.927
4 11.5641

0.1145
6,052.157
8 Mitigated Operational

3.0 Construction Detail
Construction Phase
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio-CO2
Total CO2
CH4
N20
CO2e
Percent
Reduction

0.00 0.00

0.00 0.00

0.00 0.00

0.00 0.00

0.00 0.00

0.00 0.00

0.00 0.00

0.00 0.00
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

Phase
Number
Phase Name
Phase Type
Start Date
End Date
Num Days
Week
Num Days
Phase Description
1 Site Preparation
Site Preparation
4/1/2021
4/26/2021
5 18
2 Grading
Grading
4/27/2021
6/30/2021
5 47
3 Building Construction
Building Construction
7/1/2021
6/6/2022
5 243
4 Architectural Coatings
Architectural Coating
1/27/2022
6/30/2022
5 111
5 Paving
Paving
6/7/2022
6/30/2022
5 18
OffRoad Equipment
Residential Indoor: 0; Residential Outdoor: 0; Non-Residential Indoor: 904,650; Non-Residential Outdoor: 301,550; Striped Parking Area:
54,886 (Architectural Coating
±
sqft)
Acres of Grading (Site Preparation Phase): 0
Acres of Grading (Grading Phase): 117.5
Acres of Paving: 21
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

Phase Name
Offroad Equipment Type
Amount
Usage Hours
Horse Power
Load Factor
Site Preparation
Rubber Tired Dozers
3 8.00
247

0.40 Site Preparation
Tractors/Loaders/Backhoes
4 8.00
97 0.37
Grading
Excavators
2 8.00
158

0.38 Grading
Graders
1 8.00
187

0.41 Grading
Rubber Tired Dozers
1 8.00
247

0.40 Grading
Scrapers
2 8.00
367

0.48 Grading
Tractors/Loaders/Backhoes
2 8.00
97 0.37
Building Construction
Cranes
1 7.00
231

0.29 Building Construction
Forklifts
3 8.00
89 0.20
Building Construction
Generator Sets
1 8.00
84 0.74
Building Construction
Tractors/Loaders/Backhoes
3 7.00
97 0.37
Building Construction
Welders
1 8.00
46 0.45
Paving
Pavers
2 8.00
130

0.42 Paving
Paving Equipment
2 8.00
132

0.36 Paving
Rollers
2 8.00
80 0.38
Architectural Coatings
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
7 18.00

0.00 0.00

14.70 6.90

20.00 LD_Mix
HDT_Mix
HHDT
Grading
8 20.00

0.00 5,000.00

14.70 6.90

1.00 LD_Mix
HDT_Mix
HHDT
Building Construction
9 638.00
249.00

0.00 14.70

6.90 20.00
LD_Mix
HDT_Mix
HHDT
Paving
6 15.00

0.00 0.00

14.70 6.90

20.00 LD_Mix
HDT_Mix
HHDT
Architectural Coatings
1 128.00

0.00 0.00

14.70 6.90

20.00 LD_Mix
HDT_Mix
HHDT
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

3.2 Site Preparation - 2021
ROG
NOx
CO
SO2
Fugitive
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

0.1626

0.0000

0.1626

0.0894

0.0000

0.0894

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Off-Road

0.0350

0.3645

0.1904

3.4000e-
004

0.0184

0.0184

0.0169

0.0169

0.0000

30.0922

30.0922

9.7300e-
003

0.0000

30.3355
Total

0.0350

0.3645

0.1904

3.4000e-
004

0.1626

0.0184

0.1810

0.0894

0.0169

0.1063

0.0000

30.0922

30.0922

9.7300e-
003

0.0000

30.3355
Unmitigated Construction On-Site

3.1 Mitigation Measures Construction
Water Exposed Area
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

3.2 Site Preparation - 2021
ROG
NOx
CO
SO2
Fugitive
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

6.7000e-
004

5.0000e-
004

5.6500e-
003

2.0000e-
005

1.7800e-
003

1.0000e-
005

1.7900e-
003

4.7000e-
004

1.0000e-
005

4.8000e-
004

0.0000

1.5498

1.5498

4.0000e-
005

0.0000

1.5508
Total

6.7000e-
004

5.0000e-
004

5.6500e-
003

2.0000e-
005

1.7800e-
003

1.0000e-
005

1.7900e-
003

4.7000e-
004

1.0000e-
005

4.8000e-
004

0.0000

1.5498

1.5498

4.0000e-
005

0.0000

1.5508
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

0.0732

0.0000

0.0732

0.0402

0.0000

0.0402

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Off-Road

0.0350

0.3645

0.1904

3.4000e-
004

0.0184

0.0184

0.0169

0.0169

0.0000

30.0921

30.0921

9.7300e-
003

0.0000

30.3354
Total

0.0350

0.3645

0.1904

3.4000e-
004

0.0732

0.0184

0.0916

0.0402

0.0169

0.0572

0.0000

30.0921

30.0921

9.7300e-
003

0.0000

30.3354
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

3.2 Site Preparation - 2021
ROG
NOx
CO
SO2
Fugitive
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

6.7000e-
004

5.0000e-
004

5.6500e-
003

2.0000e-
005

1.7800e-
003

1.0000e-
005

1.7900e-
003

4.7000e-
004

1.0000e-
005

4.8000e-
004

0.0000

1.5498

1.5498

4.0000e-
005

0.0000

1.5508
Total

6.7000e-
004

5.0000e-
004

5.6500e-
003

2.0000e-
005

1.7800e-
003

1.0000e-
005

1.7900e-
003

4.7000e-
004

1.0000e-
005

4.8000e-
004

0.0000

1.5498

1.5498

4.0000e-
005

0.0000

1.5508
Mitigated Construction Off-Site

3.3 Grading - 2021
ROG
NOx
CO
SO2
Fugitive
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

0.2061

0.0000

0.2061

0.0849

0.0000

0.0849

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Off-Road

0.0985

1.0904

0.7256

1.4600e-
003

0.0467

0.0467

0.0429

0.0429

0.0000
128.0632
128.0632

0.0414

0.0000
129.0987
Total

0.0985

1.0904

0.7256

1.4600e-
003

0.2061

0.0467

0.2528

0.0849

0.0429

0.1278

0.0000
128.0632
128.0632

0.0414

0.0000
129.0987
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

3.3 Grading - 2021
ROG
NOx
CO
SO2
Fugitive
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

4.8200e-
003

0.2497

0.0374

3.3000e-
004

2.2000e-
003

2.0000e-
004

2.3900e-
003

6.1000e-
004

1.9000e-
004

8.0000e-
004

0.0000

32.1224

32.1224

4.5000e-
003

0.0000

32.2350
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

1.9500e-
003

1.4500e-
003

0.0164

5.0000e-
005

5.1600e-
003

4.0000e-
005

5.2000e-
003

1.3700e-
003

4.0000e-
005

1.4100e-
003

0.0000

4.4963

4.4963

1.2000e-
004

0.0000

4.4993
Total

6.7700e-
003

0.2512

0.0538

3.8000e-
004

7.3600e-
003

2.4000e-
004

7.5900e-
003

1.9800e-
003

2.3000e-
004

2.2100e-
003

0.0000

36.6186

36.6186

4.6200e-
003

0.0000

36.7343
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

0.0927

0.0000

0.0927

0.0382

0.0000

0.0382

0.0000

0.0000

0.0000

0.0000

0.0000

0.0000
Off-Road

0.0985

1.0904

0.7256

1.4600e-
003

0.0467

0.0467

0.0429

0.0429

0.0000
128.0631
128.0631

0.0414

0.0000
129.0985
Total

0.0985

1.0904

0.7256

1.4600e-
003

0.0927

0.0467

0.1394

0.0382

0.0429

0.0811

0.0000
128.0631
128.0631

0.0414

0.0000
129.0985
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

3.3 Grading - 2021
ROG
NOx
CO
SO2
Fugitive
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

4.8200e-
003

0.2497

0.0374

3.3000e-
004

2.2000e-
003

2.0000e-
004

2.3900e-
003

6.1000e-
004

1.9000e-
004

8.0000e-
004

0.0000

32.1224

32.1224

4.5000e-
003

0.0000

32.2350
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

1.9500e-
003

1.4500e-
003

0.0164

5.0000e-
005

5.1600e-
003

4.0000e-
005

5.2000e-
003

1.3700e-
003

4.0000e-
005

1.4100e-
003

0.0000

4.4963

4.4963

1.2000e-
004

0.0000

4.4993
Total

6.7700e-
003

0.2512

0.0538

3.8000e-
004

7.3600e-
003

2.4000e-
004

7.5900e-
003

1.9800e-
003

2.3000e-
004

2.2100e-
003

0.0000

36.6186

36.6186

4.6200e-
003

0.0000

36.7343
Mitigated Construction Off-Site

3.4 Building Construction - 2021
ROG
NOx
CO
SO2
Fugitive
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

0.1255

1.1505

1.0940

1.7800e-
003

0.0633

0.0633

0.0595

0.0595

0.0000
152.8806
152.8806

0.0369

0.0000
153.8027
Total

0.1255

1.1505

1.0940

1.7800e-
003

0.0633

0.0633

0.0595

0.0595

0.0000
152.8806
152.8806

0.0369

0.0000
153.8027
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

3.4 Building Construction - 2021
ROG
NOx
CO
SO2
Fugitive
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

0.0473

1.5985

0.4040

4.1100e-
003

0.1036

3.2600e-
003

0.1068

0.0299

3.1100e-
003

0.0330

0.0000
399.0283
399.0283

0.0257

0.0000
399.6714
Worker

0.1750

0.1299

1.4695

4.4600e-
003

0.4620

3.4800e-
003

0.4655

0.1227

3.2100e-
003

0.1259

0.0000
402.8270
402.8270

0.0108

0.0000
403.0980
Total

0.2223

1.7284

1.8735

8.5700e-
003

0.5656

6.7400e-
003

0.5723

0.1526

6.3200e-
003

0.1589

0.0000
801.8554
801.8554

0.0366

0.0000
802.7694
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

0.1255

1.1505

1.0940

1.7800e-
003

0.0633

0.0633

0.0595

0.0595

0.0000
152.8804
152.8804

0.0369

0.0000
153.8025
Total

0.1255

1.1505

1.0940

1.7800e-
003

0.0633

0.0633

0.0595

0.0595

0.0000
152.8804
152.8804

0.0369

0.0000
153.8025
Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

3.4 Building Construction - 2021
ROG
NOx
CO
SO2
Fugitive
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

0.0473

1.5985

0.4040

4.1100e-
003

0.1036

3.2600e-
003

0.1068

0.0299

3.1100e-
003

0.0330

0.0000
399.0283
399.0283

0.0257

0.0000
399.6714
Worker

0.1750

0.1299

1.4695

4.4600e-
003

0.4620

3.4800e-
003

0.4655

0.1227

3.2100e-
003

0.1259

0.0000
402.8270
402.8270

0.0108

0.0000
403.0980
Total

0.2223

1.7284

1.8735

8.5700e-
003

0.5656

6.7400e-
003

0.5723

0.1526

6.3200e-
003

0.1589

0.0000
801.8554
801.8554

0.0366

0.0000
802.7694
Mitigated Construction Off-Site

3.4 Building Construction - 2022
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Off-Road

0.0947

0.8667

0.9082

1.4900e-
003

0.0449

0.0449

0.0422

0.0422

0.0000
128.6075
128.6075

0.0308

0.0000
129.3778
Total

0.0947

0.8667

0.9082

1.4900e-
003

0.0449

0.0449

0.0422

0.0422

0.0000
128.6075
128.6075

0.0308

0.0000
129.3778
Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2016.3.2
Date: 8/3/2021 10:59 AM

9309 Sycamore Hills Distribution Center - Trucks - South Coast Air Basin, Annual

3.4 Building Construction - 2022
ROG
NOx
CO
SO2
Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2
NBio- CO2
Total CO2
CH4
N2O
CO2e
Category
tons/yr
MT/yr
Hauling

0.0000

0.0000

0.0000

0.0000

0.0000