2. Refiners in the United States started adding lead compounds to gasoline in the 1920s in order to boost octane levels and improve engine performance. This practice did not officially end until 1992 when lead was banned as a fuel additive in California. Tailpipe emissions from automobiles using leaded gasoline contained lead and resulted in aerially deposited lead (ADL) being deposited in and along roadways throughout the state. ADL-contaminated soils still exist along roadsides and medians and can also be found underneath some existing road surfaces due to past construction activities. Due to the potential for ADL-contaminated soil DTSC, recommends collecting soil samples for lead analysis prior to performing any intrusive activities for the project described in the EIR.
3. If any sites within the project area or sites located within the vicinity of the project have been used or are suspected of having been used for mining activities, proper investigation for mine waste should be discussed in the EIR. DTSC recommends that any project sites with current and/or former mining operations onsite or in the project site area should be evaluated for mine waste according to DTSC’s 1998 Abandoned Mine Land Mines Preliminary Assessment Handbook
4. If buildings or other structures are to be demolished on any project sites included in the proposed project, surveys should be conducted for the presence of lead-based paints or products, mercury, asbestos containing materials, and polychlorinated biphenyl caulk. Removal, demolition and disposal of any of the above-mentioned chemicals should be conducted in compliance with California environmental regulations and policies. In addition, sampling near current and/or former buildings should be conducted in accordance with DTSC’s 2006 Interim Guidance Evaluation of School Sites with Potential Contamination from Lead Based Paint, Termiticides, and Electrical Transformers.
5. If any projects initiated as part of the proposed project require the importation of soil to backfill any excavated areas, proper sampling should be conducted to ensure that the imported soil is free of contamination. DTSC recommends the imported materials be characterized according to DTSC’s 2001 Information Advisory Clean Imported Fill Material.
6. If any sites included as part of the proposed project have been used for agricultural, weed abatement or related activities, proper investigation for organochlorinated pesticides should be discussed in the EIR. DTSC recommends the current and former agricultural lands be evaluated in accordance with DTSC’s 2008 Interim Guidance for Sampling Agricultural Properties (Third Revision).
Mr. Jason Ridenour
July 26, 2021
DTSC appreciates the opportunity to comment on the EIR. Should you need any assistance with an environmental investigation, please submit a request for Lead Agency Oversight Application. Additional information regarding voluntary agreements with DTSC can be found at DTSC’s Brownfield website.
If you have any questions, please contact me at (916) 255-3710 or via email at [email protected].
Sincerely,
Gavin McCreary
Project Manager
Site Evaluation and Remediation Unit
Site Mitigation and Restoration Program
Department of Toxic Substances Control
cc: (via email)
Governor’s Office of Planning and Research
State Clearinghouse
[email protected]
Mr. Dave Kereazis
Office of Planning & Environmental Analysis
Department of Toxic Substances Control
[email protected]
From: Jason Ridenour
To: Emily Bowen; Julia Lew; Jeff O"Neal
Cc: Troy Andres
Subject: Fw: Lombardi Street
Date: Tuesday, July 27, 2021 8:09:47 AM
Attachments: Outlook-i4lwsnr0.png
Good morning,
Please see the communication from Mr. Ennis that was received yesterday in respond to the NOP.
Thank you,
Jason Ridenour
Community Development Director
City of Porterville
559-782-7460
ChoosePorterville.com
From: [email protected] <[email protected]>
Sent: Monday, July 26, 2021 3:50 PM
To: Jason Ridenour <[email protected]>; Dennis Townsend <[email protected]>; [email protected] <[email protected]>; [email protected] <[email protected]>; Jim Robinson <[email protected]>; [email protected] <[email protected]> Cc: Patrice Hildreth <[email protected]>; Javier Sanchez <[email protected]>; Monte Reyes ([email protected]) <[email protected]> Subject: Lombardi Street
It was my understanding that we would have a meeting scheduled after our May Zoom call to address the traffic issues on Lombardi Street going to the Lombardi campus from Westfield prior to moving ahead so that all parties could give additional input. I have been waiting for that meeting so that we might further discuss ways to alleviate the traffic on Lombardi Street to the school. I am out of town and disappointed to find out that a Ceqa meeting is scheduled for tomorrow night for the subdivision prior to another meeting being scheduled by the City as promised. I might direct you to part of the Ceqa guidelines which states "2.1 Congestion and Accessibility 2.1.1 Defining Traffic Congestion Traffic congestion occurs when the demand for road space exceeds its supply in a given direction at a given time in the day. This imbalance between supply and demand creates a scarcity of road capacity; as more individuals use a relatively fixed supply of road capacity, less space is available for travel by others and queuing for the scarce capacity occurs." There should be no question about demand for road space exceeding it's supply due to some poor decision making on the City and Burton Schools part to locate a school on a one way in and one way out street. I am disappointed in the fact that it seems as if the City finds no merit in traffic mitigation for a street that is extremely impacted or on following through on the discussions to solve the issue. Due to the fact that I will not be available tomorrow evening, I would like to make certain that the portion of the Ceqa guidelines regarding traffic mitigation is added as an item that must be mitigated in the meeting.
Ben Ennis
This e-mail (and attachments, if any) may be subject to the California Public Records Act, and as such may therefore be subject to public disclosure unless otherwise exempt under the Act.
Lombardi Subdivision Project
[email protected] <[email protected]>
Tue 7/13/2021 6:37 AM
To: Planning <[email protected]>
Caution! This message was sent from outside your organization.
Jason, I am writing to you to provide some feedback on the Lombardi Project.
I live in Williams ranch and love this are of town. The only concern that I have to raise is concerning traffic flow.
The traffic bottleneck just north of the intersection of Henderson and Westwood will get worse with more traffic in this area of town.
Specifically the small bridge north of Henderson where cars get backed up during peak times is very dangerous and needs to be addressed.
Please reply with some basic response to traffic in the area and how the City will be addressing traffic increase in this area as a result of the additional Homes.
Sincerely,
Edward McKervey
2154 W. San Lucia CT
Porterville, Ca 93257
661-344-6260
Appendix B
Air Quality Impact Study
Air Quality, Greenhouse Gas, and
Energy Impact Assessment
Lombardi Development Project
July 23, 2021
Prepared for:
Crawford & Bowen Planning, Inc.
113 N. Church Street, #302
Visalia, CA 93291
Prepared by:
Stantec Consulting Services Inc.
6780 North West Avenue, Suite 103
Fresno, CA 93711
Contact: Elena Nuño, Principal Air
Quality Scientist/Planner
559.355.0580
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT i
Table of Contents
ABBREVIATIONS..........................................................................................................IV
1.0 EXECUTIVE SUMMARY................................................................................... 1.1
1.1 PROJECT UNDERSTANDING.......................................................................... 1.1
1.2 SUMMARY OF ANALYSIS................................................................................ 1.1
1.3 MITIGATION MEASURES APPLIED TO THE PROJECT................................. 1.2
2.0 INTRODUCTION............................................................................................... 2.1
2.1 PURPOSE OF ANALYSIS................................................................................. 2.1
2.2 PROJECT DESCRIPTION ................................................................................ 2.1
2.2.1 Surrounding Land Uses and Existing Conditions .............................. 2.2
3.0 AIR QUALITY.................................................................................................... 3.1
3.1 ENVIRONMENTAL SETTING ........................................................................... 3.1
3.1.1 Climate Topography .......................................................................... 3.1
3.1.2 Criteria Air Pollutants......................................................................... 3.2
3.1.3 Odors............................................................................................... 3.11
3.1.4 Toxic Air Contaminants ................................................................... 3.11
3.1.5 Valley Fever .................................................................................... 3.14
3.1.6 Attainment Status ............................................................................ 3.14
3.1.7 Ambient Air Quality.......................................................................... 3.15
3.1.8 Local Sources of Air Pollution.......................................................... 3.17
3.1.9 Sensitive Receptors......................................................................... 3.17
3.2 REGULATORY SETTING ............................................................................... 3.18
3.2.1 Federal ............................................................................................ 3.18
3.2.2 State................................................................................................ 3.19
3.2.3 Regional .......................................................................................... 3.21
3.2.4 Local................................................................................................ 3.24
4.0 GREENHOUSE GAS ........................................................................................ 4.1
4.1 ENVIRONMENTAL SETTING ........................................................................... 4.1
4.1.1 Local.................................................................................................. 4.1
4.1.2 Global Warming Potential.................................................................. 4.3
4.1.3 Sources of Greenhouse Gas Emissions............................................ 4.3
4.1.4 Effects of Global Climate Change ..................................................... 4.5
4.2 REGULATORY SETTING ................................................................................. 4.5
4.2.1 Federal .............................................................................................. 4.5
4.2.2 State.................................................................................................. 4.8
4.2.3 Regional .......................................................................................... 4.17
5.0 ENERGY ........................................................................................................... 5.1
5.1 ENVIRONMENTAL SETTING ........................................................................... 5.1
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT ii
5.2 REGULATORY SETTING ................................................................................. 5.1
5.2.1 Federal .............................................................................................. 5.1
5.2.2 State.................................................................................................. 5.3
5.2.3 Local.................................................................................................. 5.4
6.0 MODELING PARAMETERS AND ASSUMPTIONS ......................................... 6.1
6.1 CRITERIA AIR POLLUTANT AND GHG MODEL SELECTION ........................ 6.1
6.2 AIR POLLUTANTS AND GHGS ASSESSED.................................................... 6.1
6.2.1 Criteria Pollutants Assessed.............................................................. 6.1
6.2.2 GHGs Assessed................................................................................ 6.2
6.3 ASSUMPTIONS ................................................................................................ 6.2
6.4 HEALTH RISK ASSESSMENT MODEL SELECTION AND
PARAMETERS................................................................................................ 6.11
7.0 AIR QUALITY IMPACT ANALYSIS.................................................................. 7.1
7.1 CEQA GUIDELINES.......................................................................................... 7.1
7.2 AIR IMPACT ANALYSIS ................................................................................... 7.2
8.0 GREENHOUSE GAS IMPACT ANALYSIS....................................................... 8.1
8.1 CEQA GUIDELINES.......................................................................................... 8.1
8.2 GHG IMPACT ANALYSIS ................................................................................. 8.3
9.0 ENERGY ........................................................................................................... 9.1
9.1 CEQA GUIDELINES.......................................................................................... 9.1
9.2 ENERGY IMPACT ANALYSIS .......................................................................... 9.1
10.0 REFERENCES................................................................................................ 10.1
LIST OF TABLES
Table 1: California and National Ambient Air Quality Standards...............................................3.3 Table 2: San Joaquin Valley Air Basin Attainment Status.......................................................3.15 Table 3: Ambient Air Quality Summary ..................................................................................3.16 Table 4: CalEEMod Land Use Development Summary Table for the Proposed Project ...........6.3 Table 5: Project Construction Schedule ...................................................................................6.4 Table 6: Project Construction Equipment .................................................................................6.4 Table 7: Construction Vehicle Trips..........................................................................................6.6 Table 8: SJVAPCD Significance Thresholds ............................................................................7.2 Table 9: Construction Emissions – Unmitigated .......................................................................7.6 Table 10: Summary of Overlapping Phase One Operational and Phase Two Construction Criteria Air Pollutants - Unmitigated ......................................................7.8 Table 11: Summary of Operational Emissions of Criteria Air Pollutants – Unmitigated.............7.8 Table 12: Localized Concentrations of PM10, PM2.5, CO, and NOX for Construction ...........7.14 Table 13: Health Risks from Project Construction at the Maximally Exposed Sensitive Receptor (Unmitigated)............................................................................................7.19 Table 14: Health Risks from Project Construction at the Maximally Exposed Sensitive Receptor (Mitigated) ................................................................................................7.19
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT iii
Table 15: Construction Greenhouse Gas Emissions ................................................................8.4 Table 16: Operational Greenhouse Gas Emissions..................................................................8.4 Table 17: Project Consistency with Applicable 2017 Scoping Plan Greenhouse Gas Reduction Strategies .................................................................................................8.6 Table 18: Project Consistency with Applicable SJVAPCD CCAP GHG Reduction Measures...................................................................................................................8.8 Table 19: Project Consistency with Applicable Tulare COG Goals...........................................8.9 Table 20: Construction Off-Road Fuel Consumption ................................................................9.2 Table 21: Construction On-Road Fuel Consumption ................................................................9.2 Table 22: Construction Trailer..................................................................................................9.3
LIST OF FIGURES
Figure 1: Project Site.................................................................................................... 2.3 Figure 2: GHG Emissions by Economic Sector............................................................ 4.4 Figure 3: Project Site with Sensitive Receptors within 1,000 Feet ............................. 6.12 Figure 4: Project Site with a 1,000 Foot Buffer........................................................... 7.17
LIST OF APPENDICES
Appendix A: Criteria Air Pollutant and Greenhouse Gas Emissions Appendix B: Health Risk Assessment
Appendix C: Energy Estimate
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT iv
ABBREVIATIONS
μg/m3
AB
ACBMs
ATCMs
AQGGP
AQI
AQP
BACT
BAU
BPS
CAAQS
CalEEMod
CalEPA
CAPCOA
CARB
CCAA
CEQA
CF4
CH4
CO
CO2
C2F6
C3F8
C4F10
C4F8
C5F12
C6F14
DPM
DRRP
EO
EPA
FCAA
GAMAQI
GHG
GWP
HAP
HFC
H2S
LCFS
Micrograms Per Cubic Meter
Assembly Bill
Asbestos-Containing Building Materials
Airborne Toxic Control Measures
Air Quality Guidelines for General Plans
Air Quality Index
Air Quality Plan
Best Available Control Technology
Business-As-Usual
Best Performance Standards
California Ambient Air Quality Standards
California Emissions Estimator Model
California Environmental Protection Agency
California Air Pollution Control Officers Association
California Air Resources Board
California Clean Air Act
California Environmental Quality Act
Perfluoromethane
Methane
Carbon Monoxide
Carbon Dioxide
Perfluoroethane
Perfluoropropane
Perfluorobutane
Perfluorocyclobutane
Perfluoropentane
Perfluorohexane
Diesel Particulate Matter
Diesel Risk Reduction Plan
Executive Order
United States Environmental Protection Agency
Federal Clean Air Act
Guidance for Assessing and Mitigating Air Quality Impacts Greenhouse Gases
Global Warming Potential
Hazardous Air Pollutants
Hydrofluorocarbons
Hydrogen Sulfide
Low Carbon Fuel Standard
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT v
LOS
MMT
MMTCO2e
MTCO2e
NAAQS
NESHAP
NF3
N2O
NOA
NOX
NO2
O3
OAL
Pb
PEIR
PERP
PFCs
PG&E
PM
PM2.5
PM10¬
ppb
ppm
ROG
RPS
RTP
SB
SCS
SF6
SIL
SJVAB
SJVAPCD
SO2
SO4
SOX
TAC
VMT
VOC
Level of Service
Million Metric Tons
Million Metric Tons of Carbon Dioxide Equivalents
Metric Tons of Carbon Dioxide Equivalents
National Ambient Air Quality Standards
National Emissions Standards for Hazardous Air Pollutants Nitrogen Trifluoride
Nitrous Oxide
Naturally Occurring Asbestos
Oxides of Nitrogen
Nitrogen Dioxide
Ozone
Office of Administrative Law
Lead
Program Environmental Impact Report
Portable Equipment Registration Program
Perfluorocarbons
Pacific Gas and Electric Company
Particulate Matter
Fine particulate matter; particulate matter 2.5 microns or smaller Particulate matter; particulate matter 10 microns or smaller parts per billion
parts per million
Reactive Organic Gases
Renewable Portfolio Standard
Regional Transportation Plan
Senate Bill
Sustainable Communities Strategy
Sulfur Hexafluoride
Significant Impact Level
San Joaquin Valley Air Basin
San Joaquin Valley Air Pollution Control District
Sulfur Dioxide
Sulfates
Sulfur Oxides
Toxic Air Contaminants
Vehicle Miles Traveled
Volatile Organic Compounds
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Executive summary
1.1 1.0 EXECUTIVE SUMMARY
The following air quality, greenhouse gas, and energy impact analysis was prepared to evaluate whether construction and operation of the Lombardi Development in Porterville, California would cause significant impacts with respect to air quality, greenhouse gas, and energy in the Project area. This assessment was conducted within the context of the California Environmental Quality Act (CEQA) (California Public Resources Code Sections 21000, et seq.).
1.1 PROJECT UNDERSTANDING
The Lombardi Development Project (Project) proposes to construct and operate a new residential development with a community park. The project includes a zoning change from Very Low Density Residential Development (RS-1) to Low Density Residential (RS-2) on APN 245-010-087 and includes the annexation of Assessor Parcel Number (APN) 245-010-087, -041, -037, and -92. Construction will only occur on APN 245-010- 087 and the existing uses on the remaining parcels will remain.
1.2 SUMMARY OF ANALYSIS
Impact AIR-1: The Project would not conflict with or obstruct implementation of the applicable air quality plan. Less Than Significant Impact.
Impact AIR-2: The Project would not result in a cumulatively considerable net increase of any criteria pollutant for which the project region is nonattainment under an applicable federal or state ambient air quality standard. Less Than Significant Impact.
Impact AIR-3: The Project would not expose sensitive receptors to substantial pollutant concentrations. Less Than Significant Impact With Mitigation.
Impact AIR-4: The Project would not result in other emissions (such as those leading to odors) affecting a substantial number of people. Less Than Significant Impact.
Impact GHG-1: The Project would not generate direct and indirect greenhouse gas emissions that would result in a significant impact on the environment. Less Than Significant Impact.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Executive summary
1.2 Impact GHG-2: The Project would not conflict with any applicable plan, policy or regulation of an agency adopted to reduce the emissions of greenhouse gases. Less Than Significant Impact.
Impact ENERGY-1:The Project would not result in a potentially significant environmental impact due to wasteful, inefficient, or unnecessary consumption of energy resources during project construction or operation. Less Than Significant Impact.
Impact ENERGY-2:The Project would not conflict with or obstruct a state or local plan for renewable energy or energy efficiency. Less Than Significant Impact.
1.3 MITIGATION MEASURES APPLIED TO THE PROJECT
MM AIR-1: Clean Construction Fleet. The Project Applicant and/or their respective contractors shall submit documentation to the City of Porterville demonstrating that all off-road diesel-powered construction equipment greater than 50 horsepower meets EPA or ARB Tier 4 off-road emission standards.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Introduction
2.1 2.0 INTRODUCTION
2.1 PURPOSE OF ANALYSIS
The purpose of this Air Quality, Greenhouse Gas, and Energy Impact Assessment Technical Study (Study) is to analyze potential air quality, greenhouse gas (GHG), and energy impacts that could occur from the construction and operation of the Lombardi Development Project. This assessment was conducted within the context of the California Environmental Quality Act (CEQA).
2.2 PROJECT DESCRIPTION
The Project proposes to construct and operate a new residential development within the City of Porterville. The proposed Project consists of an Annexation, General Plan Amendment, Rezone and a Tentative Subdivision Map to allow for the construction of up to 233 single-family residential units. Parcels to be annexed include 245-010-087, - 092, -037 and -041 for a total of approximately 69.65 acres. The 56-acre subdivision would be developed on Assessor Parcel Number 245-010-087. The Project site is in northwest Porterville between N. Westwood Street and N. Lombardi Street, bounded to the south by W. Westfield Avenue. The proposed project includes the following components:
• Construction of 233 single family residential units.
• Development of a 152,217 square foot park in the center of the residential development.
• Construction of local roads with five points of ingress/egress; one on the southern boundary of the property off W. Westfield Avenue, one on the western boundary off N. Westwood Street, one on the northern boundary off an unnamed street adjacent to the Summit Charter Academy, Lombardi Campus, and two on the eastern boundary off N. Lombardi Street.
• Improvement of all streets in or adjacent to the subdivision, in accordance with the approved improvements plan, per Section 407.02(h) of the Porterville Development Ordinance.
• Development of a subdivision tree and landscaping design that will be approved by the City. At least one tree will be plants on each residential lot and street trees will be planted at 35 feet on center along all parkways within and/or bordering the subdivision.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Introduction
2.2 • Development of a Landscape plan, in accordance with Chapter 303 of the Porterville Development Ordinance.
• Change the zone on APN 245-010-087 from the prezoned RS-1 to RS-2 (Very Low Density Residential to Low Density Residential).
• Annexation of APN 245-010-087 (56.32-acres), APN 245-010-041 (1.00-acres), APN 245-010-037 (1.06-acres), and APN 245-010-092 (11.27-acres). Summit Charter Academy, Lombardi Campus, is on APN 245-010-087, and rural houses are on -037 and -041. The only physical changes proposed with this Project will occur on APN 245-010-087.
• Cancellation of Williamson Act contract Number 05126 and disestablishment of Ag Preserve 2034.
2.2.1 Surrounding Land Uses and Existing Conditions
The Project site is currently in use with primarily agricultural activities with two rural residences with one located along W. Westfield Avenue and one located along N.
Lombardi Street. Both residences are adjacent to vacant areas utilized for storage and staging heavy equipment.
The proposed site is surrounded by the following land uses:
• North: Summit Charter Academy, Lombardi Campus and a portion of the FriantKern Canal, identified as Public Land and Park Land. • South: Residential development and vacant land, identified as Low Density and Medium Density Residential.
• East: Residential development, vacant land and agriculture, identified as Very Low and Low Density Residential.
• West: Residential development, identified as Low Density Residential.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Introduction
2.3 Figure 1: Project Site
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality
3.1 3.0 AIR QUALITY
3.1 ENVIRONMENTAL SETTING
The proposed project is located within the San Joaquin Valley Air Basin (SJVAB). The San Joaquin Valley Air Pollution Control District (SJVAPCD) regulates air quality in eight counties including: Fresno, Kern, (western and central), Kings, Madera, Merced, San Joaquin, Stanislaus, and Tulare.
Air pollution in the SJVAB can be attributed to both human-related (anthropogenic) and natural (non-anthropogenic) activities that produce emissions. Air pollution from significant anthropogenic activities in the SJVAB includes a variety of industrial-based sources as well as on- and off-road mobile sources.
Activities that tend to increase mobile activity include increases in population, increases in general traffic activity (including automobiles, trucks, aircraft, and rail), urban sprawl (which will increase commuter driving distances), and general local land management practices as they pertain to modes of commuter transportation. These sources, coupled with geographical and meteorological conditions unique to the area, stimulate the formation of unhealthy air.
3.1.1 Climate Topography
The following information is excerpted from the most recent version of the SJVAPCD Guide for Assessing, and Mitigating Air Quality Impacts (GAMAQI) adopted in March 2015 (SJVAPCD 2015a).
The SJVAB has an “inland Mediterranean” climate and is characterized by long, hot, dry summers and short, foggy winters. Sunlight can be a catalyst in the formation of some air pollutants (such as ozone); the Basin averages over 260 sunny days per year. The SJVAB is generally shaped like a bowl. It is open in the north and is surrounded by mountain ranges on all other sides. The Sierra Nevada mountains are along the eastern boundary (8,000 to 14,000 feet in elevation), the Coast Ranges are along the western boundary (3,000 feet in elevation), and the Tehachapi Mountains are along the southern boundary (6,000 to 8,000 feet in elevation).
Dominant airflows provide the driving mechanism for transport and dispersion of air pollution. The mountains surrounding the SJVAB form natural horizontal barriers to the dispersion of air contaminants. The wind generally flows south-southeast through the valley, through the Tehachapi Pass and into the Southeast Desert Air Basin portion of Kern County. As the wind moves through the Basin, it mixes with the air pollution
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality
3.2 generated locally, generally transporting air pollutants from the north to the south in the summer and in a reverse flow in the winter.
Generally, the temperature of air decreases with height, creating a gradient from warmer air near the ground to cooler air at elevation. This gradient of cooler air over warm air is known as the environmental lapse rate. Inversions occur when warm air sits over cooler air, trapping the cooler air near the ground. These inversions trap pollutants from dispersing vertically and the mountains surrounding the San Joaquin Valley trap the pollutants from dispersing horizontally. Strong temperature inversions occur throughout the SJVAB in the summer, fall, and winter. Daytime temperature inversions occur at elevations of 2,000 to 2,500 feet above the San Joaquin Valley floor during the summer and at 500 to 1,000 feet during the winter. The result is a relatively high concentration of air pollution in the valley during inversion episodes. These inversions cause haziness, which in addition to moisture may include suspended dust, a variety of chemical aerosols emitted from vehicles, particulates from wood stoves, and other pollutants. In the winter, these conditions can lead to carbon monoxide “hotspots” along heavily traveled roads and at busy intersections. During summer’s longer daylight hours, stagnant air, high temperatures, and plentiful sunshine provide the conditions and energy for the photochemical reaction between reactive organic gases (ROG) and oxides of nitrogen (NOX), which results in the formation of ozone.
Because of the prevailing daytime winds and time-delayed nature of ozone, concentrations are highest in the southern portion of the Basin. Summers are often periods of hazy visibility and occasionally unhealthful air, while winter air quality impacts tend to be localized and can consist of (but are not exclusive to) odors from agricultural operations; soot or smoke around residential, agricultural, and hazard-reduction wood burning; or dust near mineral resource recovery operations.
3.1.2 Criteria Air Pollutants
For the protection of public health and welfare, the Federal Clean Air Act (FCAA) required that the United States Environmental Protection Agency (EPA) establish National Ambient Air Quality Standards (NAAQS) for various pollutants. These pollutants are referred to as "criteria" pollutants because the EPA publishes criteria documents to justify the choice of standards. These standards define the maximum amount of an air pollutant that can be present in ambient air. An ambient air quality standard is generally specified as a concentration averaged over a specific time, such as one hour, eight hours, 24 hours, or one year. The different averaging times and concentrations are meant to protect against different exposure effects. Standards established for the protection of human health are referred to as primary standards; whereas standards established for the prevention of environmental and property damage are called secondary standards. The FCAA allows states to adopt additional or more health-protective standards. The air quality regulatory framework and ambient air
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality
3.3 quality standards are discussed in greater detail later in this report. Table 1 provides a summary of the California and National Ambient Air Quality Standards.
Table 1: California and National Ambient Air Quality Standards Pollutant Averaging Time
California Standards National Standards
Concentration Primary Secondary
Ozone
1 Hour 0.09 ppm (180 μg/m3) — Same as Primary
Standard 8 Hour 0.070 ppm
(137 μg/m3)
0.070 ppm
(137 μg/m3)
Respirable
Particulate Matter
24 Hour 50 μg/m3 150 μg/m3 Same as Primary Annual Arithmetic Standard Mean 20 μg/m3 —
Fine Particulate
Matter
24 Hour — 35 μg/m3
Same as Primary Annual Arithmetic Standard
Mean 12 μg/m3 12 μg/m3
Carbon Monoxide
1 Hour 20 ppm (23 mg/m3) 35 ppm (40 mg/m3) —
8 Hour 9.0 ppm (10 mg/m3) 9 ppm (10 mg/m3) —
8 Hour (Lake
Tahoe) 6 ppm (7 mg/m3) — —
Nitrogen Dioxide
1 Hour 0.18 ppm (339 μg/m3) 100 ppb
(188 μg/m3) —
Annual Arithmetic
Mean 0.030 ppm (57 μg/m3) 0.053 ppm
(100 μg/m3)
Same as Primary
Standard
Sulfur Dioxide
1 Hour 0.25 ppm (655 μg/m3) 75 ppb (196 μg/m3) —
3 Hour — — 0.5 ppm (1,300
μg/m3)
24 Hour 0.04 ppm (105 μg/m3) 0.14 ppm
(for certain areas) —
Annual Arithmetic
Mean — 0.030 ppm
(for certain areas) —
Lead
30-Day Average 1.5 μg/m3 — —
Calendar Quarter — 1.5 μg/m3
Same as Primary Rolling 3-Month Standard
Average — 0.15 μg/m3
Visibility-Reducing
Particles 8 Hour See Footnote 1
No National Standards Sulfates 24 Hour 25 μg/m3
Hydrogen Sulfide 1 Hour 0.03 ppm (42 μg/m3)
Vinyl Chloride 24 Hour 0.01 ppm (26 μg/m3) —
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality
3.4 Pollutant Averaging Time
California Standards National Standards
Concentration Primary Secondary
Notes:
1 In 1989, the ARB converted both the general statewide 10-mile visibility standard and the Lake Tahoe 30-mile visibility standard to instrumental equivalents, which are "extinction of 0.23 per kilometer" and "extinction of 0.07 per kilometer" for the statewide and Lake Tahoe Air Basin standards, respectively. μg/m3 = micrograms per cubic meter
mg/m3 = milligrams per cubic meter
Source: CARB 2016c
The following provides a summary discussion of the primary and secondary criteria air pollutants of primary concern. In general, primary pollutants are directed emitted into the atmosphere, and secondary pollutants are formed by chemical reactions in the atmosphere.
Ozone
Ozone (O3) is a reactive gas consisting of three atoms of oxygen. Ozone occurs in two layers of the atmosphere. The layer surrounding the earth’s surface is the troposphere.
The troposphere extends to a level about 10 miles up where it meets the second layer, the stratosphere. While ozone in the upper atmosphere protects the earth from harmful ultraviolet radiation, high concentrations of ground-level ozone can adversely affect the human respiratory system.
Ozone, a colorless gas which is odorless at ambient levels, is the chief component of urban smog. Ozone is not directly emitted as a pollutant but is formed in the atmosphere when hydrocarbon and NOX precursor emissions react in the presence of sunlight. Meteorology and terrain play major roles in ozone formation. Generally, low wind speeds or stagnant air coupled with warm temperatures and cloudless skies provide the optimum conditions for ozone formation. As a result, summer is generally the peak ozone season. Because of the reaction time involved, peak ozone concentrations often occur far downwind of the precursor emissions. Therefore, ozone is a regional pollutant that often impacts a large area (California Air Resources Board [CARB] 2001).
Sources of precursor gases number in the thousands and include common sources such as consumer products, gasoline vapors, chemical solvents, and combustion byproducts of various fuels. Emissions of the ozone precursors ROG and NOX most commonly originate from motor vehicles, as well as commercial and industrial uses.
Many respiratory ailments, as well as cardiovascular disease, are aggravated by exposure to high ozone levels. High levels of ozone may negatively affect immune systems, making people more susceptible to respiratory illnesses, including bronchitis and pneumonia. Long-term exposure to ozone is linked to aggravation of asthma and is
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3.5 likely to be one of many causes of asthma development. Long-term exposures to higher concentrations of ozone may also be linked to permanent lung damage, such as abnormal lung development in children. People most at risk from breathing air containing ozone include people with asthma, children, older adults, and people who are active outdoors, especially outdoor workers. In addition, people with certain genetic characteristics, and people with reduced intake of certain nutrients, such as vitamins C and E, are at greater risk from ozone exposure (EPA 2021a).
Reactive Organic Gases and Volatile Organic Compounds
Hydrocarbons are organic gases that are formed solely of hydrogen and carbon. There are several subsets of organic gases, including Volatile Organic Compounds (VOCs) and ROGs. ROGs include all hydrocarbons except those exempted by CARB.
Therefore, ROGs are a set of organic gases based on state rules and regulations.
VOCs are like ROGs in that they include all organic gases except those exempted by federal law.
Both VOCs and ROGs are emitted from incomplete combustion of hydrocarbons or other carbon- based fuels. Combustion engine exhaust, oil refineries, and oil-fueled power plants are the primary sources of hydrocarbons. Another source of hydrocarbons is evaporation from petroleum fuels, solvents, dry cleaning solutions, and paint.
The primary health effects related to hydrocarbons stem from ozone (see discussion above). High levels of hydrocarbons in the atmosphere can interfere with oxygen intake by reducing the amount of available oxygen through displacement. There are no separate national or California ambient air quality standards for ROG. Carcinogenic forms of ROG, such as benzene, are also considered toxic air contaminants (TACs).
Nitrogen Dioxide and Nitrogen Oxides
Nitrogen dioxide (NO2) is one of a group of highly reactive gases known as “oxides of nitrogen (NOX).” NO2 is the component of greatest interest and the indicator for the larger group of NOX. It forms quickly from emissions from cars, trucks, and buses, powerplants, and off-road equipment. NOX is a strong oxidizing agent that reacts in the air to form corrosive nitric acid as well as toxic organic nitrates.
NOX is emitted from solvents and combustion processes in which fuel is burned at high temperatures. Mobile sources (including on-road and off-road vehicles) and stationary sources such as electric utilities and industrial boilers, constitute a majority of the statewide NOX emissions. To a lesser extent, area-wide sources, such as residential heaters, gas stoves, and managed burning and disposal, also contribute to total statewide NOX emissions (CARB 2010). NOX is also linked to the formation of ground-level ozone and fine particle pollution (see discussion above for ozone and particulate pollution for additional discussion of health-related impacts).
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3.6 Direct inhalation of NOX can cause a wide range of health effects. NOX can irritate the lungs, cause lung damage, and lower resistance to respiratory infections such as influenza. Short-term exposures (e.g., less than 3 hours) to low levels of NO2 may lead to changes in airway responsiveness and lung function in individuals with pre-existing respiratory illnesses. These exposures may also increase respiratory illnesses in children. Long-term exposures to NO2 may lead to increased susceptibility to respiratory infection and may cause irreversible lung damage. Other health effects are an increase in the incidence of chronic bronchitis and lung irritation. Chronic exposure may lead to eye and mucus membrane aggravation, along with pulmonary dysfunction. NOX can cause fading of textile dyes and additives, deterioration of cotton and nylon, and corrosion of metals due to the production of particulate nitrates. Airborne NOX can also impair visibility.
NOX also contributes to a wide range of environmental effects both directly and indirectly when combined with other precursors in acid rain and ozone. Increased nitrogen inputs to terrestrial and wetland systems can lead to changes in plant species composition and diversity. Similarly, direct nitrogen inputs to aquatic ecosystems such as those found in estuarine and coastal waters can lead to eutrophication (a condition that promotes excessive algae growth, which can lead to a severe depletion of dissolved oxygen and increased levels of toxins that are harmful to aquatic life).
Nitrogen, alone or in acid rain, also can acidify soils and surface waters. Acidification of soils causes the loss of essential plant nutrients and increased levels of soluble aluminum, which is toxic to plants. Acidification of surface waters creates low pH conditions and levels of aluminum that are toxic to fish and other aquatic organisms.
NOX also contributes to haze and visibility impairment (EPA 2019a, CARB 2016a).
Particulate Matter
Particulate matter (PM) is a mixture of substances that includes elements such as carbon and metals; compounds such as nitrates, sulfates, and organic compounds; and complex mixtures such as diesel exhaust and soil. PM2.5 includes fine particles with a diameter of 2.5 microns or smaller and is a subset of PM10. These particles come in many sizes and shapes and can be made up of hundreds of different chemicals. Some particles, known as primary particles, are emitted directly from a source, such as construction sites, unpaved roads, fields, smokestacks, or fires. Others form in complicated reactions in the atmosphere of chemicals such as sulfur dioxides and nitrogen oxides that are emitted from power plants, industries, and automobiles. These particles, known as secondary particles, make up most of the fine particle pollution in the country (EPA 2019a, CARB 2016a).
Area-wide sources account for about 65 and 83% of the statewide emissions of directly emitted PM2.5 and PM10, respectively. The major area-wide sources of PM2.5 and
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3.7 PM10 are fugitive dust, especially dust from unpaved and paved roads, agricultural operations, and construction and demolition. Sources of PM10 include crushing or grinding operations, and dust stirred up by vehicles traveling on roads. Sources of PM2.5 include all types of combustion, including motor vehicles, power plants, residential wood burning, forest fires, agricultural burning, and some industrial processes.
Exhaust emissions from mobile sources contribute only a very small portion of directly emitted PM2.5 and PM10 emissions but are a major source of the VOC and NOX that form secondary particles (CARB 2013).
PM2.5 and PM10 particles are small enough to be inhaled and lodged in the deepest parts of the lung where they evade the respiratory system’s natural defenses. Health problems begin as the body reacts to these foreign particles. Acute and chronic health effects associated with high particulate levels include the aggravation of chronic respiratory diseases; heart and lung disease; and coughing, bronchitis, and respiratory illnesses in children. Recent mortality studies have shown a statistically significant direct association between mortality and daily concentrations of particulate matter in the air.
PM2.5 and PM10 can aggravate respiratory disease and cause lung damage, cancer, and premature death.
Sensitive populations, including children, the elderly, exercising adults, and those suffering from chronic lung disease such as asthma or bronchitis are especially vulnerable to the effect of PM10. Non-health-related effects include reduced visibility and soiling of buildings.
Carbon Monoxide
Carbon Monoxide (CO) is an odorless, colorless gas that is highly toxic. CO is emitted by mobile and stationary sources because of incomplete combustion of hydrocarbons or other carbon-based fuels. CO is an odorless, colorless, poisonous gas that is highly reactive.
CO enters the bloodstream and binds more readily to hemoglobin, the oxygen-carrying protein in blood, than oxygen, thereby reducing the oxygen-carrying capacity of blood and reducing oxygen delivery to organs and tissues. The health threat from CO is most serious for those who suffer from cardiovascular disease. Healthy individuals are also affected but only at higher levels of exposure. Exposure to CO can cause chest pain in heart patients, headaches, and reduced mental alertness. At high concentrations, CO can cause heart difficulties in people with chronic diseases and can impair mental abilities. Exposure to elevated CO levels is associated with visual impairment, reduced work capacity, reduced manual dexterity, poor learning ability, difficulty performing complex tasks, and, with prolonged enclosed exposure, death.
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3.8 Very high levels of CO are not likely to occur outdoors. However, when CO levels are elevated outdoors, they can be of particular concern for people with some types of heart disease. These people already have a reduced ability for getting oxygenated blood to their hearts in situations where the heart needs more oxygen than usual. They are especially vulnerable to the effects of CO when exercising or under increased stress. In these situations, short-term exposure to elevated CO may result in reduced oxygen to the heart accompanied by chest pain also known as angina (EPA 2019a).
Sulfur Dioxide
Sulfur Dioxide (SO2) is one of a group of highly reactive gases known as “oxides of sulfur (SOX).” It is a colorless, irritating gas with a “rotten egg” smell that is formed primarily by the combustion of sulfur-containing fossil fuels. The largest source of SO2 in the atmosphere is the burning of fossil fuels by power plants and other industrial facilities. Smaller sources of SO2 emissions include industrial processes such as extracting metal from ore; natural sources such as volcanoes; and locomotives, ships and other vehicles and heavy equipment that burn fuel with a high sulfur content. State and national ambient air quality standards for SO2 are designed to protect against exposure to the entire group of sulfur oxides (SOX). SO2 is the component of greatest concern and is used as the indicator for the larger group of gaseous sulfur oxides.
High concentrations of SO2 can result in temporary breathing impairment for asthmatic children and adults who are active outdoors. Short-term exposures of asthmatic individuals to elevated SO2 levels during moderate activity may result in breathing difficulties that can be accompanied by symptoms such as wheezing, chest tightness, or shortness of breath. Other effects that have been associated with longer term exposures to high concentrations of SO2 in conjunction with high levels of particulate matter include aggravation of existing cardiovascular disease, respiratory illness, and alterations in the lungs’ defenses. The subgroups of the population that may be affected under these conditions include individuals with heart or lung disease, as well as the elderly and children.
Together, SO2 and NOX are the major precursors to acidic deposition (acid rain), which is associated with the acidification of soils, lakes, and streams and accelerated corrosion of buildings and monuments. SO2 also is a major precursor to PM2.5, which is a significant health concern, and a main contributor to poor visibility.
Lead
Lead (Pb) is a naturally occurring bluish-gray metal found in small amounts in the earth's crust. Lead can be found in all parts of our environment. Much of it comes from human activities including burning fossil fuels, mining, and manufacturing. Lead has many different uses. It is used in the production of batteries, ammunition, metal
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3.9 products (solder and pipes), and devices to shield X-rays. Because of health concerns, lead from paints and ceramic products, caulking, and pipe solder has been dramatically reduced in recent years. The use of lead as an additive to gasoline was banned in 1996 in the United States.
Exposure to lead occurs mainly through inhalation of air and ingestion of lead in food, water, soil, or dust. The effects of lead are the same regardless of the path of exposure.
Lead can affect almost every organ and system in your body. The main target for lead toxicity is the nervous system, both in adults and children. Long-term exposure of adults can result in decreased performance in some tests that measure functions of the nervous system. It may also cause weakness in fingers, wrists, or ankles.
Lead exposure also causes small increases in blood pressure, particularly in middleaged and older people and can cause anemia. Exposure to high lead levels can severely damage the brain and kidneys in adults or children and ultimately cause death.
In pregnant women, high levels of exposure to lead may cause miscarriage. High level exposure in men can damage the organs responsible for sperm production.
Exposure to lead is more dangerous for young and unborn children. Unborn children can be exposed to lead through their mothers. Harmful effects include premature births, smaller babies, decreased mental ability in the infant, learning difficulties, and reduced growth in young children. These effects are more common if the mother or baby was exposed to high levels of lead. Some of these effects may persist beyond childhood (Agency for Toxic Substances & Disease Registry [ATSDR] 2007).
Hydrogen Sulfide
Hydrogen Sulfide (H2S) is a colorless gas with the odor of rotten eggs. H2S occurs naturally and is also produced by human activities. H2S occurs naturally in crude petroleum, natural gas, volcanic gases, and hot springs. It can also result during bacterial decomposition of sulfur-containing organic substances. Emissions of H2S associated with human activities including various industrial activities, such as oil and gas production, refining, sewage treatment plants, food processing, and confined animal feeding operations.
Studies in humans suggest that the respiratory tract and nervous system are the most sensitive targets of H2S toxicity. Exposure to low concentrations of H2S may cause irritation to the eyes, nose, or throat. It may also cause difficulty in breathing for some asthmatics. Respiratory distress or arrest has been observed in people exposed to very high concentrations of H2S. Exposure to low concentrations of H2S may cause headaches, poor memory, tiredness, and balance problems. Brief exposures to high concentrations of H2S can cause loss of consciousness. In most cases, the person appears to regain consciousness without any other effects. However, in some
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3.10 individuals, there may be permanent or long-term effects such as headaches, poor attention span, poor memory, and poor motor function. H2S is extremely hazardous in high concentrations, especially in enclosed spaces. In some instances, exposure to high concentrations can cause death (ATSDR 2007b).
Other Pollutants
The State of California has established air quality standards for some pollutants not addressed by Federal standards. The CARB has established State standards for hydrogen sulfide, sulfates, vinyl chloride, and visibility reducing particles. Below is a summary of these pollutants and a description of the pollutants’ physical properties, health and other effects, sources, and the extent of the problems.
Sulfates
Sulfates (SO4) are the fully oxidized ionic form of sulfur. Sulfates occur in combination with metal and/or hydrogen ions. In California, emissions of sulfur compounds occur primarily from the combustion of petroleum-derived fuels (e.g., gasoline and diesel fuel) that contain sulfur. This sulfur is oxidized to SO2 during the combustion process and subsequently converted to sulfate compounds in the atmosphere. The conversion of SO2 to sulfates takes place comparatively rapidly and completely in urban areas of California due to regional meteorological features.
The CARB sulfates standard is designed to prevent aggravation of respiratory symptoms. Effects of sulfate exposure at levels above the standard include a decrease in ventilator function, aggravation of asthmatic symptoms, and an increased risk of cardio-pulmonary disease. Sulfates are particularly effective in degrading visibility, and, because they are usually acidic, can harm ecosystems and damage materials and property.
Visibility Reducing Particles
Visibility Reducing Particles are a mixture of suspended particulate matter consisting of dry solid fragments, solid cores with liquid coatings, and small droplets of liquid. The standard is intended to limit the frequency and severity of visibility impairment due to regional haze and is equivalent to a 10-mile nominal visual range.
Vinyl Chloride
Vinyl Chloride is a colorless gas that does not occur naturally. It is formed when other substances such as trichloroethane, trichloroethylene, and tetrachloro-ethylene are broken down. Vinyl chloride is used to make polyvinyl chloride which is used to make a variety of plastic products, including pipes, wire and cable coatings, and packaging materials.
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3.11 3.1.3 Odors
Typically, odors are generally regarded as an annoyance rather than a health hazard.
However, manifestations of a person’s reaction to foul odors can range from the psychological (i.e. irritation, anger, or anxiety) to the physiological, including circulatory and respiratory effects, nausea, vomiting, and headache.
The ability to detect odors varies considerably among the population and overall is quite subjective. Some individuals can smell very minute quantities of specific substances; others may not have the same sensitivity but may have sensitivities to odors of other substances. In addition, people may have different reactions to the same odor and in fact an odor that is offensive to one person may be perfectly acceptable to another (e.g., fast food restaurant). It is important to also note that an unfamiliar odor is more easily detected and is more likely to cause complaints than a familiar one. This is because of the phenomenon known as odor fatigue, in which a person can become desensitized to almost any odor and recognition only occurs with an alteration in the intensity.
Quality and intensity are two properties present in any odor. The quality of an odor indicates the nature of the smell experience. For instance, if a person describes an odor as flowery or sweet, then the person is describing the quality of the odor. Intensity refers to the strength of the odor. For example, a person may use the word strong to describe the intensity of an odor. Odor intensity depends on the odorant concentration in the air.
When an odorous sample is progressively diluted, the odorant concentration decreases.
As this occurs, the odor intensity weakens and eventually becomes so low that the detection or recognition of the odor is quite difficult. At some point during dilution, the concentration of the odorant reaches a detection threshold. An odorant concentration below the detection threshold means that the concentration in the air is not detectable by the average human.
Neither the state nor the federal governments have adopted rules or regulations for the control of odor sources. The SJVAPCD does not have an individual rule or regulation that specifically addresses odors; however, odors would be subject to SJVAPCD Rule 4102, Nuisance. Any actions related to odors would be based on citizen complaints to local governments and the SJVAPCD.
3.1.4 Toxic Air Contaminants
TACs are air pollutants that may cause or contribute to an increase in mortality or serious illness, or which may pose a hazard to human health. TACs are usually present in minute quantities in the ambient air, but due to their high toxicity, they may pose a threat to public health even at very low concentrations. Because there is no threshold level below which adverse health impacts are not expected to occur, TACs differ from criteria pollutants for which acceptable levels of exposure can be determined and for
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3.12 which state and federal governments have set ambient air quality standards. TACs, therefore, are not considered “criteria pollutants” under either the FCAA or the California Clean Air Act (CCAA) and are thus not subject to National or California ambient air quality standards (NAAQS and CAAQS, respectively). Instead, the EPA and the CARB regulate Hazardous Air Pollutants (HAPs) and TACs, respectively, through statutes and regulations that generally require the use of the maximum or best available control technology (BACT) to limit emissions. In conjunction with District rules, these federal and state statutes and regulations establish the regulatory framework for TACs. At the national levels, the EPA has established National Emission Standards for HAPs (NESHAPs), in accordance with the requirements of the FCAA and subsequent amendments. These are technology-based source-specific regulations that limit allowable emissions of HAPs.
Within California, TACs are regulated primarily through the Tanner Air Toxics Act (Assembly Bill [AB] 1807) and the Air Toxics Hot Spots Information and Assessment Act of 1987 (AB 2588). The Tanner Act sets forth a formal procedure for CARB to designate substances as TACs. The following provides a summary of the primary TACs of concern within the State of California and related health effects:
Diesel Particulate Matter
Diesel Particulate Matter (DPM) was identified as a TAC by the CARB in August 1998.
DPM is emitted from both mobile and stationary sources. In California, on-road dieselfueled vehicles contribute approximately 42% of the statewide total, with an additional 55% attributed to other mobile sources such as construction and mining equipment, agricultural equipment, and transport refrigeration units. Stationary sources, contributing about 3% of emissions, include shipyards, warehouses, heavy equipment repair yards, and oil and gas production operations. Emissions from these sources are from dieselfueled internal combustion engines. Stationary sources that report DPM emissions also include heavy construction, manufacturers of asphalt paving materials and blocks, and diesel-fueled electrical generation facilities (CARB 2013).
In October 2000, the CARB issued a report entitled: Risk Reduction Plan to Reduce Particulate Matter Emissions from Diesel-Fueled Engines and Vehicles, which is commonly referred to as the Diesel Risk Reduction Plan (DRRP). The DRRP provides a mechanism for combating the DPM problem. The goal of the DRRP is to reduce concentrations of DPM by 85% by the year 2020, in comparison to year 2000 baseline emissions. The key elements of the DRRP are to clean up existing engines through engine retrofit emission control devices, to adopt stringent standards for new diesel engines, and to lower the sulfur content of diesel fuel to protect new, and very effective, advanced technology emission control devices on diesel engines. When fully implemented, the DRPP will significantly reduce emissions from both old and new diesel fueled motor vehicles and from stationary sources that burn diesel fuel. In addition to
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3.13 these strategies, the CARB continues to promote the use of alternative fuels and electrification. As a result of these actions, DPM concentrations and associated health risks in future years are projected to decline (CARB 2013). In comparison to year 2010 inventory of statewide DPM emissions, CARB estimates that emissions of DPM in 2035 will be reduced by more than 50%.
DPM is typically composed of carbon particles (“soot”, also called black carbon) and numerous organic compounds, including over 40 known cancer-causing organic substances. Examples of these chemicals include polycyclic aromatic hydrocarbons, benzene, formaldehyde, acetaldehyde, acrolein, and 1,3-butadiene. Diesel exhaust also contains gaseous pollutants, including volatile organic compounds and NOx. NOx emissions from diesel engines are important because they can undergo chemical reactions in the atmosphere leading to formation of PM2.5 and ozone.
In California, diesel exhaust particles have been identified as a carcinogen accounting for an estimated 70% of the total known cancer risks in California. DPM is estimated to increase statewide cancer risk by 520 cancers per million residents exposed over an estimated 70-year lifetime. Non- cancer health effects associated with exposure to DPM include premature death, exacerbated chronic heart and lung disease, including asthma, and decreased lung function in children. Short-term exposure to diesel exhaust can also have immediate health effects. Diesel exhaust can irritate the eyes, nose, throat and lungs, and it can cause coughs, headaches, lightheadedness, and nausea. In studies with human volunteers, diesel exhaust particles made people with allergies more susceptible to the materials to which they are allergic, such as dust and pollen.
Exposure to diesel exhaust also causes inflammation in the lungs, which may aggravate chronic respiratory symptoms and increase the frequency or intensity of asthma attacks (CARB 2016b).
Individuals most vulnerable to non-cancer health effects of DPM are children whose lungs are still developing and the elderly who often have chronic health problems. The elderly and people with emphysema, asthma, and chronic heart and lung disease are especially sensitive to DPM (CARB 2016b). In addition to its health effects, DPM significantly contributes to haze and reduced visibility.
Asbestos
Asbestos is the name given to a number of naturally occurring fibrous silicate minerals that have been mined for their useful properties such as thermal insulation, chemical and thermal stability, and high tensile strength. The three most common types of asbestos are chrysotile, amosite, and crocidolite. Chrysotile, also known as white asbestos, is the most common type of asbestos found in buildings. Chrysotile makes up approximately 90 to 95 percent of all asbestos contained in buildings in the United States. Exposure to asbestos is a health threat; exposure to asbestos fibers may result
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3.14 in health issues such as lung cancer, mesothelioma (a rare cancer of the thin membranes lining the lungs, chest, and abdominal cavity), and asbestosis (a noncancerous lung disease that causes scarring of the lungs). Exposure to asbestos can occur during demolition or remodeling of buildings constructed prior to its ban for use in buildings in 1977. Exposure to naturally occurring asbestos can occur during soil disturbing activities in areas with deposits present.
3.1.5 Valley Fever
Valley Fever is an infection caused by a fungus that lives in the soil. About 10,000 U.S. cases are reported each year, mostly from Arizona and California. Valley fever can be misdiagnosed because its symptoms are like those of other illnesses.
The fungus that causes Valley fever, Coccidioides, is found in the southwestern United States, parts of Mexico and Central America, and parts of South America. The fungus grows naturally and is endemic in many areas along the southwestern region of Tulare County. People can get this infection by breathing in fungal spores from the air, especially when the wind blows the soil with the fungal spores into the air or the dirt is moved by human activity. About 40% of the people who come into contact with the fungal spores will develop symptoms that may require medical treatment and the symptoms will not go away on their own. Some people may develop a more severe infection, especially those with compromised immune systems (Centers for Disease Control and Prevention [CDC] 2020).
3.1.6 Attainment Status
The United States EPA and CARB designate air basins where ambient air quality standards are exceeded as “nonattainment” areas. If standards are met, the area is designated as an “attainment” area. If there is inadequate or inconclusive data to make a definitive attainment designation, they are considered “unclassified.” National nonattainment areas are further designated as marginal, moderate, serious, severe, or extreme as a function of deviation from standards.
Each standard has a different definition, or “form” of what constitutes attainment, based on specific air quality statistics. For example, the federal 8-hour CO standard is not to be exceeded more than once per year; therefore, an area is in attainment of the CO standard if no more than one 8-hour ambient air monitoring values exceeds the threshold per year. In contrast, the federal annual standard for PM2.5 is met if the 3- year average of the annual average PM2.5 concentration is less than or equal to the standard.
The current attainment designations for the SJVAB are shown in Table 2. The SJVAB is designated as nonattainment for ozone, PM10, and PM2.5.
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3.15 Table 2: San Joaquin Valley Air Basin Attainment Status Pollutant Designation/Classification
Federal Standardsa State Standardsb
Ozone – One hour No Federal Standardf Nonattainment/Severe Ozone – Eight Hour Nonattainment/Extremee Nonattainment PM10 Attainmentc Nonattainment
PM2.5 Nonattainmentd Nonattainment
Carbon Monoxide Attainment/Unclassified Attainment/Unclassified Nitrogen Dioxide Attainment/Unclassified Attainment
Sulfur Dioxide Attainment/Unclassified Attainment
Lead No Designation/Classification Attainment
Hydrogen Sulfide No Federal Standard Unclassified
Sulfates No Federal Standard Attainment
Visibility Reducing Particles No Federal Standard Unclassified Vinyl Chloride No Federal Standard Attainment
Notes:
a See 40 CFR Part 81
b See CCR Title 17 Sections 60200-60210
c On September 25, 2008, EPA redesignated the San Joaquin Valley to attainment for the PM10 National Ambient Air Quality Standard (NAAQS) and approved the PM10 Maintenance Plan. d The Valley is designated nonattainment for the 1997 PM2.5 NAAQS. EPA designated the Valley as nonattainment for the 2006 PM2.5 NAAQS on November 13, 2009 (effective December 14, 2009). e Though the Valley was initially classified as serious nonattainment for the 1997 8-hour ozone standard, EPA approved Valley reclassification to extreme nonattainment in the Federal Register on May 5, 2010 (effective June 4, 2010). f Effective June 15, 2005, the U.S. Environmental Protection Agency (EPA) revoked the federal 1-hour ozone standard, including associated designations and classifications. EPA had previously classified the SJVAB as extreme nonattainment for this standard. EPA approved the 2004 Extreme Ozone Attainment Demonstration Plan on March 8, 2010 (effective April 7, 2010).
Many applicable requirements for extreme 1-hour ozone nonattainment areas continue to apply to the SJVAB.
Source: SJVAPCD 2021
3.1.7 Ambient Air Quality
The local air quality can be evaluated by reviewing relevant air pollution concentrations near the Project. Table 3 summarizes published monitoring data for the most recent three-year period available from the nearest monitoring station at 1839 S. Newcomb Street Porterville, California, approximately 4.01 miles south of the project site. The data shows that during the past few years, the SJVAB has exceeded the ozone, PM10, and PM2.5 standards.
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3.16 Table 3: Ambient Air Quality Summary
Air Pollutant Averaging
Time
Item 2017 2018 2019
Ozone
1 Houra Max 1 Hour (ppm) 0.100 0.093 0.081
Days > State Standard (0.09 ppm) 4 0 0
8 Hour
Max 8 Hour (ppm) 0.090 0.085 0.073
Days > State Standard (0.070 ppm) 34 38 7
Days > National Standard (0.070
ppm) 97 97 94
Days > National Standard (0.075
ppm) 96 97 92
Carbon
Monoxide 8 Hour
Max 8 Hour (ppm) X X X
Days > State Standard (9.0 ppm) X X X
Days > National Standard (9.0 ppm) X X X
Nitrogen dioxide
Annual Annual Average (ppm) X X X
1 Hour Max 1 Hour (ppm) 58 63 64
Days > State Standard (0.18 ppm) 0 0 0
Sulfur dioxide
Annual Annual Average (ppm) X X X
24 Hour Max 24 Hour (ppm) X X X
Days > State Standard (0.04 ppm) X X X
Inhalable coarse
particles (PM10)
Annual
(National)
Annual Average (µg/m3) X X X
Annual
(State)
Annual Average (µg/m3) X X X
24 hour
24 Hour (µg/m3)
National
X X X
24 Hour (µg/m3)
State
X X X
Days > State Standard (50 µg/m3) X X X
Days > National Standard (150
µg/m3) X X X
Fine particulate
matter (PM2.5)
Annual
(National)
Annual Average (µg/m3) ID ID ID
Annual
(State)
Annual Average (µg/m3) ID 16.4 ID
24 Hour
24 Hour (µg/m3)
National
ID ID ID
24 Hour (µg/m3)
State
ID ID ID
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3.17 Days > National Standard (35 µg/m3) ID ID ID
Notes:
> = exceed
ppm = parts per million
g/m3 = micrograms per cubic meter
a = The Federal 1 hour Ozone Standard was revoked in June 2005; California retained a 1 hour Ozone Standard ID = insufficient data
X = No data available because concentrations are no longer monitored max = maximum
Bold = exceedance
State Standard = CAAQS
National Standard = NAAQS
Sulfur dioxide is reported on a statewide basis as it is no longer monitored locally Sources: CARB 2018a
The health impacts of the various air pollutants of concern can be presented in several ways. The clearest in comparison is to the state and federal ozone standards. If concentrations are below the standard, it is safe to say that no health impact would occur to anyone. When concentrations exceed the standard, impacts will vary based on the amount the standard is exceeded. Based on the air quality monitoring data, between 27 and 47 unhealthy ozone air days and up to 90 days with unhealthy PM10 levels and up to 27 days with unhealthy PM2.5 levels.
Unhealthy air quality levels can pose a risk to those most sensitive to air pollution such as the elderly, asthmatics, children, etc. The higher the air pollution levels rise the greater the population it affects.
3.1.8 Local Sources of Air Pollution
The Project’s site is located in a predominately urban setting with agricultural uses to the northwest., The main sources of air pollution are mobile sources traveling along the nearby roadways that surround the Project site. Nearby sources of air pollution include emissions from vehicles on North Westfield Avenue, North Lombardi Street, and North Westwood Street.
3.1.9 Sensitive Receptors
Those who are sensitive to air pollution include children, the elderly, and persons with pre-existing respiratory or cardiovascular illness. For purposes of CEQA, the SJVAPCD considers a sensitive receptor a location that houses or attracts children, the elderly, people with illnesses, or others who are especially sensitive to the effects of air pollutants. Examples of sensitive receptors include hospitals, residences, convalescent facilities, and schools.
The project site is located within 1,000 feet from existing sensitive receptors that could be exposed to diesel emission exhaust during the construction and operational periods.
The nearest sensitive receptors are residents occupying the single-family houses
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality
3.18 adjacent to the project site to the east, south, and west. In addition, the Summit Charter Academy Lombardi Campus lies immediately north of the project site and the lot on which is lies will be annexed into the project site. Additionally, William R. Buckley Elementary School lies approximately 750 feet southwest of the project site.
3.2 REGULATORY SETTING
Air quality within the project area is regulated by several jurisdictions including the U.S.
Environmental Protection Agency (EPA), the California Air Resources Board (CARB), and the San Joaquin Valley Air Pollution Control District (SJVAPCD). Each of these jurisdictions develops rules, regulations, and policies to attain the goals or directives imposed upon them through legislation. Although EPA regulations may not be superseded, both state and local regulations may be more stringent.
3.2.1 Federal
U.S. Environmental Protection Agency
At the federal level, the EPA has been charged with implementing national air quality programs. The EPA’s air quality mandates are drawn primarily from the FCAA, which was signed into law in 1970. Congress substantially amended the FCAA in 1977 and again in 1990.
Federal Clean Air Act
The FCAA required the EPA to establish NAAQS, and also set deadlines for their attainment. Two types of NAAQS have been established: primary standards, which protect public health, and secondary standards, which protect public welfare from nonhealth-related adverse effects, such as visibility restrictions. NAAQS are summarized in Table 4.
National Emission Standards for Hazardous Air Pollutants Pursuant to the FCAA of 1970, the EPA established the NESHAPs. These are technology-based source-specific regulations that limit allowable emissions of HAPs.
Among these sources include asbestos-containing building materials (ACBMs).
NESHAPs include requirements pertaining to the inspection, notification, handling, and disposal of ACBMs associated with the demolition and renovation of structures.
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3.19 3.2.2 State
California Air Resources Board
The CARB is the agency responsible for coordination and oversight of state and local air pollution control programs in California and for implementing the CCAA of 1988.
Other CARB duties include monitoring air quality (in conjunction with air monitoring networks maintained by air pollution control districts and air quality management districts), establishing California Ambient Air Quality Standards (CAAQS), which in many cases are more stringent than the NAAQS, and setting emissions standards for new motor vehicles. The emission standards established for motor vehicles differ depending on various factors including the model year, and the type of vehicle, fuel and engine used. The CAAQS are summarized in Table 1.
California Clean Air Act
The CCAA requires that all air districts in the state endeavor to achieve and maintain CAAQS for O3, CO, SO2, and NO2 by the earliest practical date. The CCAA specifies that districts focus attention on reducing the emissions from transportation and areawide emission sources, and the act provides districts with authority to regulate indirect sources. Each district plan is required to either (1) achieve a 5% annual reduction, averaged over consecutive 3-year periods, in district-wide emissions of each nonattainment pollutant or its precursors, or (2) to provide for implementation of all feasible measures to reduce emissions. Any planning effort for air quality attainment would thus need to consider both state and federal planning requirements.
Assembly Bills 1807 & 2588 - Toxic Air Contaminants
Within California, TACs are regulated primarily through AB 1807 (Tanner Air Toxics Act) and AB 2588 (Air Toxics Hot Spots Information and Assessment Act of 1987). The Tanner Air Toxics Act sets forth a formal procedure for CARB to designate substances as TACs. This includes research, public participation, and scientific peer review before CARB designates a substance as a TAC.
Existing sources of TACs that are subject to the Air Toxics Hot Spots Information and Assessment Act are required to: (1) prepare a toxic emissions inventory; (2) prepare a risk assessment if emissions are significant; (3) notify the public of significant risk levels; and (4) prepare and implement risk reduction measures.
Assembly Bill 617
In response to AB 617 (C. Garcia, Chapter 136, Statutes of 2017), the CARB established the Community Air Protection Program. The Community Air Protection Program includes community air monitoring and community emissions reduction
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality
3.20 program’s focus is to reduce exposure in communities most impacted by air pollution.
The Legislature has appropriated funding to support early actions to address localized air pollution through targeted incentive funding to deploy cleaner technologies in these communities, as well as grants to support community participation in the AB 617 process. AB 617 also includes new requirements for accelerated retrofit of pollution controls on industrial sources, increased penalty fees, and greater transparency and availability of air quality and emissions data, which will help advance air pollution control efforts throughout the State.
Portable Equipment Registration Program
Owners or operators of portable engines and certain other types of equipment can register their units under the CARB’s Statewide Portable Equipment Registration Program (PERP). PERP allows registered equipment to be operated throughout California without having to obtain individual permits from local air districts. To qualify, equipment must meet eligibility requirements, including applicable emissions standards.
Naturally-Occurring Asbestos Regulations
CARB has adopted two Airborne Toxic Control Measures (ATCMs) which regulates the control of Naturally Occurring Asbestos (NOA) associated with construction, surfacing, grading, mining, and quarrying activities. The NCUAQMD is responsible for enforcing Asbestos ATCMs. There are no known likely areas of NOA in the Project area (USGS 2011).
Regulatory Attainment Designations
Under the CCAA, CARB is required to designate areas of the state as attainment, nonattainment, or unclassified with respect to applicable standards. An “attainment” designation for an area signifies that pollutant concentrations did not violate the applicable standard in that area. A “nonattainment” designation indicates that a pollutant concentration violated the applicable standard at least once, excluding those occasions when a violation was caused by an exceptional event, as defined in the criteria.
Depending on the frequency and severity of pollutants exceeding applicable standards, the nonattainment designation can be further classified as serious nonattainment, severe nonattainment, or extreme nonattainment, with extreme nonattainment being the most severe of the classifications. An “unclassified” designation signifies that the data does not support either an attainment or nonattainment designation. The CCAA divides districts into moderate, serious, and severe air pollution categories, with increasingly stringent control requirements mandated for each category.
The EPA designates areas for O3, CO, and NO2 as “does not meet the primary standards,” “cannot be classified,” or “better than national standards.” For SO2, areas are designated as “does not meet the primary standards,” “does not meet the secondary
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality
3.21 standards,” “cannot be classified,” or “better than national standards.” However, CARB terminology of attainment, nonattainment, and unclassified is more frequently used. The EPA uses the same sub-categories for nonattainment status: serious, severe, and extreme. In 1991, EPA assigned new nonattainment designations to areas that had previously been classified as Group I, II, or III for PM10 based on the likelihood that they would violate national PM10 standards. All other areas are designated “unclassified.” As discussed previously, the SJVAB is designated as nonattainment for the federal ozone and PM2.5 standards. The SJVAB is nonattainment for State ozone, PM10, and PM2.5 standards.
3.2.3 Regional
San Joaquin Valley Air Pollution Control District
The SJVAPCD is the agency primarily responsible for ensuring that NAAQS and CAAQS are not exceeded and that air quality conditions are maintained in the SJVAB, within which the proposed project is located. Responsibilities of the SJVAPCD include, but are not limited to, preparing plans for the attainment of ambient air quality standards, adopting and enforcing rules and regulations concerning sources of air pollution, issuing permits for stationary sources of air pollution, inspecting stationary sources of air pollution and responding to citizen complaints, monitoring ambient air quality and meteorological conditions, and implementing programs and regulations required by the FCAA and the CCAA.
SJVAPCD Rules and Regulations
The SJVAPCD rules and regulations that may apply to projects that will occur during buildout of the project include but are not limited to the following:
Rule 2010 – Permits Required. The purpose of this rule is to require any person constructing, altering, replacing or operating any source operation which emits, may emit, or may reduce emissions to obtain an Authority to Construct or a Permit to Operate. This rule also explains the posting requirements for a Permit to Operate and the illegality of a person willfully altering, defacing, forging, counterfeiting or falsifying any Permit to Operate.
Rule 2201 – New and Modified Stationary Source Review Rule. The purpose of this rule is to provide for the following:
• The review of new and modified Stationary Sources of air pollution and to provide mechanisms including emission trade-offs by which Authorities to Construct such sources may be granted, without interfering with the attainment or maintenance of Ambient Air Quality Standards; and
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality
3.22 • No net increase in emissions above specified thresholds from new and modified Stationary Sources of all nonattainment pollutants and their precursors.
Rule 4002 – National Emission Standards for Hazardous Air Pollutants. This rule incorporates the National Emission Standards for Hazardous Air Pollutants from Part 61, Chapter I, Subchapter C, Title 40, Code of Federal Regulations (CFR) and the National Emission Standards for Hazardous Air Pollutants for Source Categories from Part 63, Chapter I, Subchapter C, Title 40, Code of Federal Regulations (CFR).
Rule 4102 – Nuisance. The purpose of this rule is to protect the health and safety of the public and applies to any source operation that emits or may emit air contaminants or other materials.
Rule 4601 – Architectural Coatings. The purpose of this rule is to limit Volatile Organic Compounds (VOC) emissions from architectural coatings. Emissions are reduced by limits on VOC content and providing requirements on coatings storage, cleanup, and labeling.
Rule 4623 – Storage of Organic Liquids. The purpose of this rule is to limit volatile organic compound (VOC) emissions from the storage of organic liquids.
Rule 4624 – Transfer of Organic Liquids. The purpose of this rule is to limit volatile organic compound (VOC) emissions from the transfer of organic liquids.
Rule 4641 – Cutback, Slow Cure, and Emulsified Asphalt, Paving and Maintenance Operations. The purpose of this rule is to limit VOC emissions from asphalt paving and maintenance operations. If asphalt paving will be used, then the paving operations will be subject to Rule 4641.
Regulation VIII – Fugitive PM10 Prohibitions. Rule 8011-8081 are designed to reduce PM10 emissions (predominantly dust/dirt) generated by human activity, including construction and demolition activities, road construction, bulk materials storage, paved and unpaved roads, carryout and trackout, etc. All development projects that involve soil disturbance are subject to at least one provision of the Regulation VIII series of rules.
Rule 9510 – Indirect Source Review. This rule reduces the impact of NOx and PM10 emissions from growth on the Air Basin. The rule places application and emission reduction requirements on development projects meeting applicability criteria to reduce emissions through onsite mitigation, offsite District -administered projects, or a combination of the two. This project must comply with Rule 9510 because it would develop more than 2,000 square feet of commercial space.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality
3.23 CEQA
The SJVAPCD has three roles under CEQA:
Lead Agency: responsible for preparing environmental analyses for its own projects (adoption of rules, regulations, or plans) or permit projects filed with the District where the District has primary approval authority over the project.
Responsible Agency: The discretionary authority of a Responsible Agency is more limited than a Lead Agency; having responsibility for mitigating or avoiding only the environmental effects of those parts of the project which it decides to approve, carry out, or finance. The District defers to the Lead Agency for preparation of environmental documents for land use projects that also have discretionary air quality permits unless no document is prepared by the Lead Agency and potentially significant impacts related to the permit are possible. The District comments on documents prepared by Lead Agencies to ensure that District concerns are addressed.
Commenting Agency: The District reviews and comments on air quality analyses prepared by other public agencies (such as the project).
The SJVAPCD also provides guidance and thresholds for CEQA air quality and GHG analyses. The result of this guidance as well as state regulations to control air pollution is an overall improvement in the Air Basin. In particular, the SJVAPCD’s 2015 GAMAQI states the following:
1. The District’s Air Quality Attainment Plans include measures to promote air quality elements in county and city general plans as one of the primary indirect source programs. The general plan is the primary long-range planning document used by cities and counties to direct development. Since air districts have no authority over land use decisions, it is up to cities and counties to ensure that their general plans help achieve air quality goals. Section 65302.1 of the California Government Code requires cities and counties in the San Joaquin Valley to amend appropriate elements of their general plans to include data, analysis, comprehensive goals, policies, and feasible implementation strategies to improve air quality in their next housing element revisions.
2. The Air Quality Guidelines for General Plans (AQGGP), adopted by the District in 1994 and amended in 2005, is a guidance document containing goals and policy examples that cities and counties may want to incorporate into their General Plans to satisfy Section 65302.1. When adopted in a general plan and implemented, the suggestions in the AQGGP can reduce vehicle trips and miles traveled and improve air quality. The specific suggestions in the AQGGP are
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3.24 voluntary. The District strongly encourages cities and counties to use their land use and transportation planning authority to help achieve air quality goals by adopting the suggested policies and programs.
3.2.4 Local
The City of Porterville General Plan’s Open Space and Conservation Element includes the following policies related to air quality that are applicable to the proposed project.
OSC-G-9: Improve and protect Porterville’s air quality by making air quality a priority in land use and transportation planning and in development review.
OSC-I-58: Continue to assess air quality impacts through environmental review and require developers to implement best management practices to reduce air pollutant emissions associated with the construction and operation of development projects.
The City will use the San Joaquin Valley Air Pollution Control District (SJVAPCD) Guidelines for Assessing and Mitigating Air Quality Impacts for determining and mitigating project air quality impacts and related thresholds of significance for use in environmental documents. The City shall cooperate with the SJVAPCD in the review of development proposals.
BMPs could include transportation demand management strategies for large development projects such as:
• Providing bicycle access and parking facilities;
• Providing preferential parking for high-occupancy vehicles, carpools, or alternative fuels vehicles;
• Establishing telecommuting programs or satellite work centers; • Allowing alternative work schedules;
• Subsidizing public transit costs for employee; and
• Scheduling deliveries at off-peak traffic periods.
OSC-I-59: Require preparation of a Health Risk Assessment for any development subject to the Air Toxics “Hot Spots” Act.
OSC-I-60: Require dust control measures as a condition of approval for subdivision maps, site plans, and all grading permits.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality
3.25 OSC-I-61: Coordinate air quality planning efforts with other local, regional and State agencies.
OSC-I-63: Notify local and regional jurisdictions of proposed projects that may affect regional air quality.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.1 4.0 GREENHOUSE GAS
4.1 ENVIRONMENTAL SETTING
To fully understand global climate change, it is important to recognize the naturally occurring “greenhouse effect” and to define the GHGs that contribute to this phenomenon. Various gases in the earth’s atmosphere, classified as atmospheric GHGs, play a critical role in determining the earth’s surface temperature. Solar radiation enters the earth’s atmosphere from space and a portion of the radiation is absorbed by the earth’s surface. The earth emits this radiation back toward space, but the properties of the radiation change from high-frequency solar radiation to lower-frequency infrared radiation. GHGs, which are transparent to solar radiation, are effective in absorbing infrared radiation. As a result, this radiation that otherwise would have escaped back into space is now retained, resulting in a warming of the atmosphere. This phenomenon is known as the greenhouse effect.
4.1.1 Local
Among the prominent GHGs contributing to the greenhouse effect are carbon dioxide, methane (CH4), nitrous oxide (N2O), hydrofluorocarbons (HFCs), perfluorocarbons (PFCs), and sulfur hexafluoride (SF6). Primary GHGs attributed to global climate change, are discussed in the following subsections.
Carbon Dioxide
Carbon dioxide (CO2) is a colorless, odorless gas. CO2 is emitted in a number of ways, both naturally and through human activities. The largest source of CO2 emissions globally is the combustion of fossil fuels such as coal, oil, and gas in power plants, automobiles, industrial facilities, and other sources. A number of specialized industrial production processes and product uses such as mineral production, metal production, and the use of petroleum-based products can also lead to CO2 emissions. The atmospheric lifetime of CO2 is variable because it is so readily exchanged in the atmosphere (EPA 2019b).
Methane
CH4 is a colorless, odorless gas that is not flammable under most circumstances. CH4 is the major component of natural gas, about 87% by volume. It is also formed and released to the atmosphere by biological processes occurring in anaerobic environments. CH4 is emitted from a variety of both human-related and natural sources.
Human-related sources include fossil fuel production, animal husbandry (enteric fermentation in livestock and manure management), rice cultivation, biomass burning,
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4.2 and waste management. These activities release significant quantities of methane to the atmosphere. Natural sources of methane include wetlands, gas hydrates, permafrost, termites, oceans, freshwater bodies, non-wetland soils, and other sources such as wildfires. The atmospheric lifetime of CH4 is about 12 years (EPA 2019b).
Nitrous Oxide
N2O is a clear, colorless gas with a slightly sweet odor. N2O is produced by both natural and human-related sources. Primary human-related sources of N2O are agricultural soil management, animal manure management, sewage treatment, mobile and stationary combustion of fossil fuels, adipic acid production, and nitric acid production. N2O is also produced naturally from a wide variety of biological sources in soil and water, particularly microbial action in wet tropical forests. The atmospheric lifetime of N2O is approximately 120 years (EPA 2017b).
Hydrofluorocarbons
HFCs are man-made chemicals, many of which have been developed as alternatives to ozone-depleting substances for industrial, commercial, and consumer products. The only significant emissions of HFCs before 1990 were of the chemical HFC-23, which is generated as a byproduct of the production of HCFC-22 (or Freon 22, used in air conditioning applications). The atmospheric lifetime for HFCs varies from just over a year for HFC-152a to 260 years for HFC-23. Most of the commercially used HFCs have atmospheric lifetimes of less than 15 years (e.g., HFC-134a, which is used in automobile air conditioning and refrigeration, has an atmospheric life of 14 years) (EPA 2017b).
Perfluorocarbons
PFCs are colorless, highly dense, chemically inert, and nontoxic. There are seven PFC gases: perfluoromethane (CF4), perfluoroethane (C2F6), perfluoropropane (C3F8), perfluorobutane (C4F10), perfluorocyclobutane (C4F8), perfluoropentane (C5F12), and perfluorohexane (C6F14). Natural geological emissions have been responsible for the PFCs that have accumulated in the atmosphere in the past; however, the largest current source is aluminum production, which releases CF4 and C2F6 as byproducts. The estimated atmospheric lifetimes for CF4 and C2F6 are 50,000 and 10,000 years, respectively (EPA 2017b).
Nitrogen Trifluoride
Nitrogen trifluoride (NF3) is an inorganic, colorless, odorless, toxic, nonflammable gas used as an etchant in microelectronics. NF3 is predominantly employed in the cleaning of the plasma-enhanced chemical vapor deposition chambers in the production of liquid crystal displays and silicon-based thin film solar cells. In 2009, NF3 was listed by
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.3 California as a potential GHG to be listed and regulated under AB 32 (Section 38505 Health and Safety Code).
Sulfur Hexafluoride
SF6 is an inorganic compound that is colorless, odorless, nontoxic, and generally nonflammable. SF6 is primarily used as an electrical insulator in high voltage equipment.
The electric power industry uses roughly 80% of all SF6 produced worldwide. Leaks of SF6 occur from aging equipment and during equipment maintenance and servicing. SF6 has an atmospheric life of 3,200 years (EPA 2017b).
Black Carbon
Black carbon is the most strongly light-absorbing component of PM emitted from burning fuels such as coal, diesel, and biomass. Black carbon contributes to climate change both directly by absorbing sunlight and indirectly by depositing on snow and by interacting with clouds and affecting cloud formation. Black carbon is considered a short-lived species, which can vary spatially and, consequently, it is very difficult to quantify associated global-warming potentials. The main sources of black carbon in California are wildfires, off-road vehicles (locomotives, marine vessels, tractors, excavators, dozers, etc.), on-road vehicles (cars, trucks, and buses), fireplaces, agricultural waste burning, and prescribed burning (planned burns of forest or wildlands). California has been an international leader in reducing emissions of black carbon, including programs that target reducing PM from diesel engines and burning activities (CARB 2013).
4.1.2 Global Warming Potential
Each GHG differs in its ability to absorb heat in the atmosphere based on the lifetime, or persistence, of the gas molecule in the atmosphere. Often, estimates of GHG emissions are presented in carbon dioxide equivalents (CO2e), which weight each gas by its global warming potential (GWP).
Expressing GHG emissions in carbon dioxide equivalents takes the contribution of all GHG emissions to the greenhouse effect and converts them to a single unit equivalent to the effect that would occur if only CO2 were being emitted. Based on a 100-year time horizon, Methane traps over 25 times more heat per molecule than CO2, and N2O absorbs roughly 298 times more heat per molecule than CO2. Additional GHGs with high GWP include NF3, SF6, PFCs, and black carbon.
4.1.3 Sources of Greenhouse Gas Emissions
On a global scale, GHG emissions are predominantly associated with activities related to energy production; changes in land use, such as deforestation and land clearing;
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.4 industrial sources; agricultural activities; transportation; waste and wastewater generation; and commercial and residential land uses. World-wide, energy production including the burning of coal, natural gas, and oil for electricity and heat is the largest single source of global GHG emissions.
California’s most recent GHG emissions inventory is depicted in Figure 2.
Figure 2: GHG Emissions by Economic Sector
Source: CARB 2018
In 2018, GHG emissions within California totaled 425.3 million metric tons (MMT) of CO2e. Within California, the transportation sector is the largest contributor, accounting for approximately 41% of the total statewide GHG emissions. Emissions associated with industrial uses are the second largest contributor, totaling roughly 24%. Electricity generation totaled roughly 15% (CARB 2018).
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.5 4.1.4 Effects of Global Climate Change
There are uncertainties as to exactly what the climate changes will be in various local areas of the earth. There are also uncertainties associated with the magnitude and timing of other consequences of a warmer planet: sea level rise, spread of certain diseases out of their usual geographic range, the effect on agricultural production, water supply, sustainability of ecosystems, increased strength and frequency of storms, extreme heat events, increased air pollution episodes, and the consequence of these effects on the economy.
Within California, climate changes would likely alter the ecological characteristics of many ecosystems throughout the state. Such alterations would likely include increases in surface temperatures and changes in the form, timing, and intensity of precipitation.
For instance, historical records are depicting an increasing trend toward earlier snowmelt in the Sierra Nevada. This snowpack is a principal supply of water for the state, providing roughly 50% of state’s annual runoff. If this trend continues, some areas of the state may experience an increased danger of floods during the winter months and possible exhaustion of the snowpack during spring and summer months. An earlier snowmelt would also impact the state’s energy resources. An early exhaustion of the Sierra snowpack may force electricity producers to switch to more costly or nonrenewable forms of electricity generation during spring and summer months. A changing climate may also impact agricultural crop yields, coastal structures, and biodiversity. As a result, resultant changes in climate will likely have detrimental effects on some of California’s largest industries, including agriculture, wine, tourism, skiing, recreational and commercial fishing, and forestry.
4.2 REGULATORY SETTING
4.2.1 Federal
U.S. Environmental Protection Agency “Endangerment” and “Cause or Contribute” Findings
On April 2, 2007, in Massachusetts v. USEPA, 549 US 497, the Supreme Court found that GHGs are air pollutants covered by the Clean Air Act (CAA). The Court held that the Unites States Environmental Protection Agency (USEPA) must determine whether emissions of GHGs from new motor vehicles cause or contribute to air pollution, which may reasonably be anticipated to endanger public health or welfare, or whether the science is too uncertain to make a reasoned decision. In making these decisions, the USEPA is required to follow the language of Section 202(a) of the CAA.
On April 17, 2009, the USEPA Administrator signed proposed “endangerment” and “cause or contribute” findings for GHGs under Section 202(a) of the CAA. The USEPA
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.6 held a 60-day public comment period, considered public comments, and issued final findings. The USEPA found that six GHGs taken in combination endanger both the public health and the public welfare of current and future generations. The USEPA also found that the combined emissions of these GHGs from new motor vehicles and new motor vehicle engines contribute to the greenhouse effect as air pollution that endangers public health and welfare under CAA Section 202(a).
Clean Vehicles
In collaboration with the National Highway Traffic Safety Administration, the USEPA adopted GHG emission standards for light-duty vehicles in May 2010 and for heavyduty vehicles in August of 2011. In 2012, the agencies jointly adopted more stringent Phase 2 standards for light duty cars and trucks, which would cover model years 2017 through 2025. In August of 2016, the agencies adopted more stringent Phase 2 standards for medium- and heavy-duty vehicles, which would cover model years 2018 through 2027 for certain trailers and model years 2021 through 2027 for semi-trucks, large pickup trucks, vans, and all types and sizes of buses and work trucks.
Mandatory Greenhouse Gas Reporting Rule
On September 22, 2009, the EPA released its final Greenhouse Gas Reporting Rule (Reporting Rule). The Reporting Rule is a response to the fiscal year 2008 Consolidated Appropriations Act (H.R. 2764; Public Law 110-161), that required the EPA to develop “…mandatory reporting of GHGs above appropriate thresholds in all sectors of the economy….” The Reporting Rule applies to most entities that emit 25,000 metric tons of CO2e (MTCO2e) or more per year. Since 2010, facility owners must submit an annual GHG emissions report with detailed calculations of facility GHG emissions. The Reporting Rule also mandates recordkeeping and administrative requirements in order for the EPA to verify annual GHG emissions reports.
New Source Review
The EPA issued a final rule on May 13, 2010 that establishes thresholds for GHGs, which will define when permits under the New Source Review Prevention of Significant Deterioration and Title V Operating Permit programs are required for new and existing industrial facilities. This final rule “tailors” the requirements of these Clean Air Act permitting programs to limit which facilities will be required to obtain Prevention of Significant Deterioration and Title V permits.
The EPA estimates that facilities responsible for nearly 70 percent of the national GHG emissions from stationary sources will be subject to permitting requirements under this rule. This includes the nation’s largest GHG emitters—power plants, refineries, and cement production facilities.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.7 Standards of Performance for Greenhouse Gas Emissions for New Stationary Sources:
Electric Utility Generating Units
As required by a settlement agreement, the EPA proposed new performance standards for emissions of carbon dioxide for new, affected, fossil fuel‐fired electric utility generating units on March 27, 2012. New sources greater than 25 megawatts would be required to meet an output based standard of 1,000 pounds of carbon dioxide per megawatt‐hour, based on the performance of widely used natural gas combined cycle technology.
President Obama and the EPA announced the Clean Power Plan in August of 2015. In 2030, the Clean Power Plan would cut carbon pollution from power plants by 32 percent below 2005 levels and increase renewable energy generation percent to nearly 20 percent of all power supplied. By comparison, in 2015, renewable energy accounted for about 13% of electricity generation. However, on February 9, 2016, the U.S. Supreme Court stayed implementation of the Clean Power Plan pending judicial review and on March 28, 2017, the Executive Order on Energy Independence (EO 13783) was signed and called for a review of the Clean Power Plan (USEPA 2018a). On October 16, 2017, the EPA issued the proposed rule Repeal of Carbon Pollution Emission Guidelines for Existing Stationary Sources: Electric Utility Generating Units an Energy Independence (EPA 2017).
Cap‐and‐Trade
Cap‐and‐Trade refers to a policy tool where emissions are limited to a certain amount and can be traded or provides flexibility on how the emitter can comply.
There is no federalGHG Cap‐and‐Trade program currently; however, some states have joined to create initiatives to provide a mechanism for Cap‐and‐Trade.
The Regional Greenhouse Gas Initiative is an effort to reduce GHGs among the states of Connecticut,Delaware, Maine, Maryland, Massachusetts, New Hampshire, New York, Rhode Island, and Vermont.Each state caps carbon dioxide emissions from power plants, auctions carbon dioxide emission allowances, and invests the proceeds in strategic energy programs that further reduce emissions, save consumers money, create jobs, and build a clean energy economy. The Initiative began in 2008.
The Western Climate Initiative partner jurisdictions have developed a comprehensive initiative to reduce regional GHG emissions to 15 percent below 2005 levels by 2020.
The partners are California,British Columbia, Manitoba, Ontario, and Quebec. Currently only California and Quebec are participating in the Cap‐and‐Trade program (C2ES 2015).
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.8 4.2.2 State
Assembly Bill 32
The California State Legislature enacted Assembly Bill (AB) 32, the California Global Warming Solutions Act of 2006. AB 32 requires that GHGs emitted in California be reduced to 1990 levels by the year 2020. “Greenhouse gases” as defined under AB 32 include CO2, methane (CH4), nitrogen oxides (NOX), hydrofluorocarbons, perfluorocarbons, and sulfur hexafluoride. Since AB 32 was enacted, a seventh chemical, nitrogen trifluoride, has also been added to the list of GHGs. The California Air Resources Board (CARB) is the state agency charged with monitoring and regulating sources of GHGs. AB 32 states the following:
Global warming poses a serious threat to the economic well‐being, public health, natural resources, and the environment of California. The potential adverse impacts of global warming include the exacerbation of air quality problems, a reduction in the quality and supply of water to the state from the Sierra snowpack, a rise in sea levels resulting in the displacement of thousands of coastal businesses and residences, damage to marine ecosystems and the natural environment, and an increase in the incidences of infectious diseases, asthma, and other human health-related problems.
CARB approved the 1990 GHG emissions level of 427 million metric tons of carbon dioxide equivalent (MMTCO2e) on December 6, 2007 (CARB 2007). Therefore, to meet the state’s target, emissions generated in California in 2020 are required to be equal to or less than 427 MMTCO2e. Emissions in 2020 in a business as usual (BAU) scenario were estimated to be 596 MMTCO2e, which do not account for reductions from AB 32 regulations (CARB 2008). At that rate, a 28 percent reduction was required to achieve the 427 MMTCO2e 1990 inventory. In October 2010, CARB prepared an updated 2020 forecast to account for the effects of the 2008 recession and slower forecasted growth.
The 2020 inventory without the benefits of adopted regulation is now estimated at 545 MMTCO2e. Therefore, under the updated forecast, a 21.7 percent reduction from BAU is required to achieve 1990 levels (CARB 2010).
Progress in Achieving Assembly Bill 32 Targets and Remaining Reductions Required The state has made steady progress in implementing AB 32 and achieving targets included in EO S‐3‐05. The progress is evident in updated emission inventories prepared by CARB, which showed that the state inventory dropped below 1990 levels for the first time in 2016 (CARB 2018). CARB’s Climate Change Scoping Plan (Scoping Plan) (subsequently amended by the 2017 update) includes projections indicating that the state would meet or exceed the 2020 target with adopted regulations (CARB 2017).
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.9 CARB 2008 Scoping Plan
The Scoping Plan contains measures designed to reduce the state’s emissions to 1990 levels by the year 2020 to comply with AB 32 (CARB 2008). The Scoping Plan identifies recommended measures for multiple GHG emission sectors and the associated emission reductions needed to achieve the year 2020 emissions target—each sector has a different emission reduction target. Most of the measures target the transportation and electricity sectors. As stated in the Scoping Plan, the key elements of the strategy for achieving the 2020 GHG target include the following:
• Expanding and strengthening existing energy efficiency programs as well as building and appliance standards;
• Achieving a statewide renewables energy mix of 33 percent; • Developing a California Cap‐and‐Trade Program that links with other Western Climate Initiative partner programs to create a regional market system; • Establishing targets for transportation‐related GHG emissions for regions throughout California and pursuing policies and incentives to achieve those targets; • Adopting and implementing measures pursuant to existing state laws and policies, including California’s clean car standards, goods movement measures, and the Low Carbon Fuel Standard; and
• Creating targeted fees, including a public goods charge on water use, fees on high global warming potential gases, and a fee to fund the administrative costs of the State’s long‐term commitment to AB 32 implementation.
In addition, the Scoping Plan differentiates between “capped” and “uncapped” strategies. Capped strategies are subject to the proposed Cap‐and‐Trade Program. The Scoping Plan states that the inclusion of these emissions within the Cap‐and‐Trade Program would help ensure that the year 2020 emission targets are met despite some degree of uncertainty in the emission reduction estimates for any individual measure.
Implementation of the capped strategies is calculated to achieve a sufficient amount of reductions by 2020 to achieve the emission target contained in AB 32. Uncapped strategies that will not be subject to the cap‐and‐trade emissions caps, and requirements are provided as a margin of safety by accounting for additional GHG emission reductions (CARB 2008).
Cap‐and‐Trade Program
The Cap‐and‐Trade Program is a key element of the Scoping Plan. It sets a statewide limit on sources responsible for 85 percent of California’s GHG emissions and establishes a price signal needed to drive long‐term investment in cleaner fuels and
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.10 more efficient use of energy. The program is designed to provide covered entities the flexibility to seek out and implement the lowest cost options to reduce emissions. The program conducted its first auction in November 2012. Compliance obligations began for power plants and large industrial sources in January 2013. Other significant milestones include linkage to Quebec’s Cap‐and‐Trade system in January 2014 and starting the compliance obligation for distributors of transportation fuels, natural gas, and other fuels in January 2015.
The Cap‐and‐Trade Program provides a firm cap, ensuring that the 2020 statewide emission limit would not be exceeded. An inherent feature of the Cap‐and‐Trade Program is that it does not guarantee GHG emissions reductions in any discrete location or by any particular source. Rather, GHG emissions reductions are guaranteed only on an accumulative basis.
The Cap‐and‐Trade Program works with other direct regulatory measures and provides an economic incentive to reduce emissions. If California’s direct regulatory measures reduce GHG emissions more than expected, then the Cap‐and‐Trade Program would be responsible for relatively fewer emissions reductions. If California’s direct regulatory measures reduce GHG emissions less than expected, then the Cap‐and‐Trade Program would be responsible for relatively more emissions reductions. Thus, the Cap‐and‐ Trade Program assures that California would meet its 2020 GHG emissions reduction mandate.
CARB approved the First Update to the Scoping Plan (Update) on May 22, 2014. The Update identified the next steps for California’s climate change strategy. The Update shows how California continues on its path to meet the near‐term 2020 GHG limit, but also sets a path toward long‐term, deep GHG emission reductions. The report established a broad framework for continued emission reductions beyond 2020, on the path to 80 percent below 1990 levels by 2050.
Assembly Bill 398
The Governor signed AB 398 on July 25, 2017, to extend the Cap‐and‐Trade Program to 2030.The legislation includes provisions to ensure that offsets used by sources are limited to 4 percent of their compliance obligation from 2021 to 2025 and 6 percent of their compliance obligation from 2026 through 2030. AB 398 also prevents air districts from adopting or implementing emission reduction rules from stationary sources that are also subject to the Cap‐and‐Trade Program (CARB 2017).
Senate Bill 32
Senate Bill (SB) 32 was signed into law on September 8, 2016. SB 32 gives CARB the statutory responsibility to include the 2030 target previously contained in EO B‐30‐15 in the 2017 Scoping Plan Update. SB 32 states that “In adopting rules and regulations to
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.11 achieve the maximum technologically feasible and cost‐effective greenhouse gas emissions reductions authorized by this division, the state [air resources] board shall ensure that statewide greenhouse gas emissions are reduced to at least 40 percent below the statewide greenhouse gas emissions limit no later than December 31, 2030.” 2017 Climate Change Scoping Plan Update
The 2017 Climate Change Scoping Plan Update was adopted on December 14, 2017 amending the 2008 Scoping Plan and addresses the SB 32 targets. The major elements of the framework proposed to achieve the 2030 target are as follows:
1. SB 350
a. Achieve 50 percent Renewables Portfolio Standard (RPS) by 2030. b. Doubling of energy efficiency savings by 2030.
2. Low Carbon Fuel Standard
a. Increased stringency (reducing carbon intensity 18 percent by 2030, up from 10 percent in 2020).
3. Mobile Source Strategy (Cleaner Technology and Fuels Scenario) a. Maintaining existing GHG standards for light‐ and heavy‐duty vehicles. b. Put 4.2 million zero‐emission vehicles on the roads. c. Increase zero‐emission vehicles buses and delivery and other trucks.
4. Sustainable Freight Action Plan
a. Improve freight system efficiency.
b. Maximize use of near‐zero emission vehicles and equipment powered by renewable energy.
c. Deploy over 100,000 zero‐emission trucks and equipment by 2030.
5. Short‐Lived Climate Pollutant Reduction Strategy
a. Reduce emissions of methane and hydrofluorocarbons 40 percent below 2013 levels by 2030.
b. Reduce emissions of black carbon 50 percent below 2013 levels by 2030.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.12 6. SB 375 Sustainable Communities Strategies
a. Increased stringency of 2035 targets.
7. Post‐2020 Cap‐and‐Trade Program
a. Declining caps, continued linkage with Québec, and linkage to Ontario, Canada. b. CARB will look for opportunities to strengthen the program to support more air quality co‐benefits, including specific program design elements. In Fall 2016, CARB staff described potential future amendments including reducing the offset usage limit, redesigning the allocation strategy to reduce free allocation to support increased technology and energy investment at covered entities and reducing allocation if the covered entity increases criteria or toxics emissions over some baseline.
8. 20 percent reduction in GHG emissions from the refinery sector.
9. Develop Integrated Natural and Working Lands Action Plan to secure California’s land base as a net carbon sink.
Many of the measures included in the 2017 Climate Change Scoping Plan Update are implemented on a statewide level and do not specifically apply to the Project. However, the short-lived climate pollutants would be applicable to the Program through the use of cleaner construction equipment.
Senate Bill 375: The Sustainable Communities and Climate Protection Act of 2008 SB 375 was signed into law on September 30, 2008. According to SB 375, the transportation sector is the largest contributor of GHG emissions, which emits more than 40 percent of the total GHG emissions in California. SB 375 states, “Without improved land use and transportation policy, California will not be able to achieve the goals of AB 32.” SB 375 does the following: (1) requires metropolitan planning organizations to include sustainable community strategies in their regional transportation plans for reducing GHG emissions, (2) aligns planning for transportation and housing, and (3) creates specified incentives for the implementation of the strategies.
CARB has prepared the Proposed Update to the SB 375 Greenhouse Gas Emission Reduction Targets.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.13 Assembly Bill 1493: Pavley Regulations and Fuel Efficiency Standards AB 1493, enacted on July 22, 2002, required CARB to develop and adopt regulations and fuel efficiency standards that reduce GHGs emitted by passenger vehicles and light duty trucks. Implementation of the regulation was delayed by lawsuits filed by automakers and by USEPA’s denial of an implementation waiver. USEPA subsequently granted the requested waiver in 2009, which was upheld by the by the U.S. District Court for the District of Columbia in 2011.
The standards were phased in during the 2009 through 2016 model years. When fully phased in, the near‐term (2009–2012) standards resulted in an approximately 22 percent reduction compared with the 2002 fleet, and the mid‐term (2013–2016) standards resulted in about a 30 percent reduction. Several technologies stand out as providing significant reductions in emissions at favorable costs. These include discrete variable valve lift or camless valve actuation to optimize valve operation, rather than relying on fixed valve timing and lift as has historically been done; turbocharging to boost power and allow for engine downsizing; improved multi‐speed transmissions; and improved air conditioning systems that operate optimally, leak less, and/or use an alternative refrigerant.
The second phase of the implementation for AB 1493 was incorporated into Amendments to the Low‐Emission Vehicle Program, referred to as LEV III or the Advanced Clean Cars program. The Advanced Clean Cars program combines the control of smog‐causing pollutants and GHG emissions into a single coordinated package of requirements for model years 2017 through 2025. The regulation would reduce GHGs from new cars by 34 percent from 2016 levels by 2025. The rules would reduce pollutants from gasoline and diesel‐powered cars and would deliver increasing numbers of zero‐emission technologies, such as full battery electric cars, newly emerging plug‐in hybrid electric vehicles, and hydrogen fuel cell cars. The regulations would also ensure that adequate fueling infrastructure is available for the increasing numbers of hydrogen fuel cell vehicles planned for deployment in California.
Senate Bill 1368: Emission Performance Standards
In 2006, the State Legislature adopted SB 1368, which was subsequently signed into law by the governor. SB 1368 directs the California Public Utilities Commission to adopt a performance standard for GHG emissions for the future power purchases of California utilities. SB 1368 seeks to limit carbon emissions associated with electrical energy consumed in California by forbidding procurement arrangements for energy longer than 5 years from resources that exceed the emissions of a relatively clean, combined cycle natural gas power plant.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.14 Because of the carbon content of its fuel source, a coal‐fired plant cannot meet this standard because such plants emit roughly twice as much carbon as natural gas, combined cycle plants. Accordingly, the new law effectively prevents California’s utilities from investing in, otherwise financially supporting, or purchasing power from new coal plants located in or out of the state. The California Public Utilities Commission adopted the regulations required by SB 1368 on August 29, 2007. The regulations implementing SB 1368 establish a standard for baseload generation owned by, or under long‐term contract to publicly owned utilities, of 1,100 pounds of CO2 per megawatt‐hour (MWh).
Senate Bill 1078: Renewable Electricity Standards
On September 12, 2002, Governor Gray Davis signed SB 1078, requiring California to generate 20 percent of its electricity from renewable energy by 2017. SB 107 changed the due date to 2010 instead of 2017. On November 17, 2008, Governor Arnold Schwarzenegger signed EO S‐14‐08, which established an RPS target for California requiring that all retail sellers of electricity serve 33 percent of their load with renewable energy by 2020. Governor Schwarzenegger signed EO S‐21‐09, which directed CARB to adopt a regulation by July 31, 2010, requiring the state’s load serving entities to meet a 33 percent renewable energy target by 2020. CARB approved the Renewable Electricity Standard on September 23, 2010, by Resolution 10‐23. In 2011, the State Legislature adopted this higher standard in SB X1‐2. Renewable sources of electricity include wind, small hydropower, solar, geothermal, biomass, and biogas.
Senate Bill 350: Clean Energy and Pollution Reduction Act of 2015 The legislature approved and the governor then signed SB 350 on October 7, 2015, which reaffirms California’s commitment to reducing its GHG emissions and addressing climate change. Key provisions include an increase in the RPS, higher energy efficiency requirements for buildings, initial strategies towards a regional electricity grid, and improved infrastructure for electric vehicle charging stations.
Senate Bill 100: California Renewables Portfolio Standard Program.
The Governor approved SB 100 on September 10, 2018. The legislation revised the RPS goals to achieve the 50 percent renewable resources target by December 31, 2026, and to achieve a 60 percent target by December 31, 2030. The bill would require that retail sellers and local publicly owned electric utilities procure a minimum quantity of electricity products from eligible renewable energy resources so that the total kilowatt hours of those products sold to their retail end‐use customers achieve 44 percent of retail sales by December 31, 2024; 52 percent by December 31, 2027; and 60 percent by December 31, 2030.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.15 Senate Bill X7‐7: The Water Conservation Act of 2009 SB X7-7 directs urban retail water suppliers to set individual 2020 per capita water use targets and to begin implementing conservation measures to achieve those goals.
Meeting this statewide goal of 20 percent decrease in demand will result in a reduction of almost 2 million acre‐feet of urban water use in 2020.
Executive Order S‐3‐05
On June 1, 2005, former California Governor Arnold Schwarzenegger announced EO S‐ 3‐05, which announced the following reduction targets for GHG emissions:
• 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.
The 2050 reduction goal represents what some scientists believe is necessary to reach levels that would stabilize the climate. The 2020 goal was established to be a mid‐term target. Because this is an EO, the goals are not legally enforceable for local governments or the private sector.
Executive Order B‐30‐15
On April 29, 2015, Governor Edmund G. Brown Jr. issued EO B-30-15 to establish a California GHG reduction target of 40 percent below 1990 levels by 2030. The Governor’s EO aligns California’s GHG reduction targets with those of leading international governments ahead of the United Nations Climate Change Conference in Paris in late 2015. The EO sets a new interim statewide GHG emission reduction target to reduce GHG emissions to 40 percent below 1990 levels by 2030 in order to ensure that California meets its target of reducing GHG emissions to 80 percent below 1990 levels by 2050, and directs CARB to update the Climate Change Scoping Plan to express the 2030 target in terms of MMTCO2e. The EO also requires the state’s climate adaptation plan to be updated every 3 years and for the state to continue its climate change research program, among other provisions. As with EO S‐3‐05, this EO is not legally enforceable against local governments and the private sector. Legislation that would update AB 32 to provide post‐2020 targets was signed by the Governor in 2016.
SB 32 includes a 2030 mandate matching the requirements of the EO.
Executive Order S‐01‐07: Low Carbon Fuel Standard
The governor signed EO S 01‐07 on January 18, 2007. The order mandates that a statewide goal shall be established to reduce the carbon intensity of California’s transportation fuels by at least 10 percent by 2020. In particular, the EO established a Low Carbon Fuel Standard (LCFS) and directed the Secretary for Environmental
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.16 Protection to coordinate the actions of the California Energy Commission, CARB, the University of California, and other agencies to develop and propose protocols for measuring the “life‐cycle carbon intensity” of transportation fuels. This analysis supporting development of the protocols was included in the State Implementation Plan for alternative fuels (State Alternative Fuels Plan adopted by California Energy Commission on December 24, 2007) and was submitted to CARB for consideration as an “early action” item under AB 32. CARB adopted the Low Carbon Fuel Standard on April 23, 2009.
The LCFS was subject to legal challenge in 2011. Ultimately, CARB was required to bring a new LCFS regulation for consideration in February 2015. The proposed LCFS regulation was required to contain revisions to the 2010 LCFS as well as new provisions designed to foster investments in the production of the low‐carbon fuels, offer additional flexibility to regulated parties, update critical technical information, simplify and streamline program operations, and enhance enforcement. The Office of Administrative Law approved the regulation on November 16, 2015. The regulation was last amended in 2018.
Executive Order S‐13‐08
EO S‐13‐08 states that “climate change in California during the next century is expected to shift precipitation patterns, accelerate sea level rise and increase temperatures, thereby posing a serious threat to California’s economy, to the health and welfare of its population and to its natural resources.” Pursuant to the requirements in the EO, the 2009 California Climate Adaptation Strategy was adopted, which is the “… first statewide, multi‐sector, region‐specific, and information‐based climate change adaptation strategy in the United States.” Objectives include analyzing risks of climate change in California, identifying and exploring strategies to adapt to climate change, and specifying a direction for future research.
Executive Order B‐55‐18
EO B‐55‐18 issued by Governor Brown on September 10, 2018, establishes a new statewide goal to achieve carbon neutrality as soon as possible, but no later than 2045, and to achieve and maintain net negative emissions thereafter. The EO directs CARB to work with relevant state agencies to develop a framework for implementation and accounting that tracks progress toward this goal.
California Energy Code
Compliance with the California Energy Code (Title 24, Part 6, of the California Code of Regulations [CCR], California’s Energy Efficiency Standards) and Title 20, Public Utilities and Energy, standards must occur for all new buildings constructed in
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas
4.17 California. These efficiency standards apply to new construction of both residential and nonresidential (i.e., maintenance buildings and pump station buildings associated with the Program) buildings, and they regulate energy consumed for heating, cooling, ventilation, water heating, and lighting. The building efficiency standards are enforced through the local building permit processes, and local government agencies may adopt and enforce energy standards for new buildings provided that these standards meet or exceed those provided in the Title 24 guidelines.
4.2.3 Regional
San Joaquin Valley Air Pollution Control District
On December 17, 2009, the San Joaquin Valley Air Pollution Control District (SJVAPCD) Governing Board adopted “Guidance for Valley Land‐use Agencies in Addressing GHG Emission Impacts for New Projects under CEQA,” and the policy “District Policy—Addressing GHG Emission Impacts for Stationary Source Projects Under CEQA When Serving as the Lead Agency.” SJVAPCD concluded that the existing science is inadequate to support quantification of the impacts that project‐ specific GHG emissions have on global climate change. SJVAPCD found the effects of project‐specific emissions to be cumulative, and without mitigation, their incremental contribution to global climate change could be considered cumulatively considerable.
SJVAPCD found that this cumulative impact is best addressed by requiring all projects to reduce their GHG emissions, whether through project design elements or mitigation.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Energy
5.1 5.0 ENERGY
5.1 ENVIRONMENTAL SETTING
Southern California Edison (SCE) provides electricity and The Southern California Gas Company (SoCal Gas) provides natural gas service to the City. Upon buildout of the project site, electricity to the project site would be provided by SCE. All electricity infrastructure would be located underground and would tie-in to existing infrastructure.
SCE serves approximately 15 million people in a 50,000 square-mile area of central, coastal, and Southern California. SCE’s service area includes portions of 15 counties and hundreds of cities and communities, including Porterville. SCE has set the goal of delivering 100% carbon-free power to customers in terms of retail sales. In 2020, approximately 43 percent of retail sales came from carbon-free resources.
SoCal Gas is the nation’s largest natural gas distribution utility serving more than 21 million consumers through nearly 5.9 million meters in more than 500 communities.
SoCal Gas has committed to achieving net zero greenhouse gas emissions in their operations and gas delivery by 2045. In order to achieve this goal, SoCal Gas has set a number of internal standards including the goal of delivering 5% renewable natural gas by 2022 and 20% by 2030 (SoCal Gas, 2021).
5.2 REGULATORY SETTING
5.2.1 Federal
Federal Energy Policy and Conservation Act
The Energy and Policy Conservation Act was enacted by Congress in 1975. This Act established the first fuel economy standards for on-road motor vehicles in the United States. Pursuant to the act, the National Highway Traffic Safety Administration (NHTSA) is responsible for establishing additional vehicle standards.
Energy Independence and Security Act of 2007
This Act set increased Corporate Average Fuel Economy (CAFÉ) standards for motor vehicles and includes the following provisions related to energy efficiency:
• Renewable fuel standards (RFS)
• Appliance and lighting efficiency standards
• Building energy efficiency
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Energy
5.2 This Act requires increasing levels of renewable fuels to replace petroleum. The U.S.
EPA is responsible for developing and implementing regulations to ensure transportation fuel sold into the US contains a minimum volume of renewable fuel.
The RFS programs regulations were developed in collaboration with refiners, renewable fuel products, and other stakeholders and were created under the Energy Policy Act of 2005. The RFS program established the first renewable fuel volume mandate in the US.
As required under the act, the original RFS program required 7.5 billion gallons of renewable fuel to be blended into gasoline by 2012. Under the Act, the RFS program was expanded in several ways that laid the foundation for achieving significant reductions of GHG emissions through the use of renewable fuels, for reducing imported petroleum, and for encouraging the development and expansion of the nation’s renewable fuels sector. The updated program is referred to as RFS2 and includes the following:
• EISA expanded the RFS program to include diesel, in addition to gasoline:
• EISA increase the volume of renewable fuel required to be blended into transportation fuel from 9 billion gallons in 2008 to 36 billion gallons by 2022; • EISA established new categories of renewable fuel and set separate volume requirements for each one; and
• EISA required by the U.S. EPA to apply lifecycle GHG performance threshold standards to ensure that each category of renewable fuel emits fewer GHGs than the petroleum fuel it replaces.
Additional provisions of the EISA address energy savings in government and public institutions, promoting research for alternate energy, additional research in carbon capture, international energy programs, and the creation of “green jobs.” Federal Vehicle Standards
The Energy Policy and Conservation Act of 1975 (EPCA) mandated that the National Highway Traffic Safety Administration (NHTSA) establish and implement a regulatory program for motor vehicle fuel economy, known as the corporate average fuel economy (CAFE) program, to reduce national energy consumption. As codified in Chapter 329 of Title 49 of the U.S. Code (U.S.C.) and, as amended by the Energy Independence and Security Act of 2007 (EISA), EPCA sets forth specific requirements concerning the establishment of average fuel economy standards for passenger cars and light trucks.
These are motor vehicles with a gross vehicle weight rating less than 8,500 pounds and medium-duty passenger vehicles with a gross vehicle weight rating less than 10,000 pounds. The Secretary of Transportation delegated responsibility for implementing the CAFE program to NHTSA.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Energy
5.3 EISA, enacted by Congress in December 2007, amended the EPCA CAFE program requirements by providing the Department of Transportation (DOT) additional rulemaking authority and responsibilities. Consistent with its statutory authority, in rulemaking to establish CAFE standards for model year 2017 and beyond passenger cars and light trucks, NHTSA developed two phases of standards. The first phase included final standards for model years 2017–2021. The second phase, covering model years 2022–2025, included standards that were not final, due to the statutory requirement that NHTSA set average fuel economy standards not more than five model years at a time. Rather, NHTSA wrote that those standards were augural, meaning that they represented its best estimate, based on the information available at that time, of what levels of stringency might be maximum feasible in those model years. In 2012, the agencies jointly adopted more stringent Phase 2 standards for light duty cars and trucks, which would cover model years 2017 through 2025. In August of 2016, the agencies adopted more stringent Phase 2 standards for medium- and heavy-duty vehicles, which would cover model years 2018 through 2027 for certain trailers and model years 2021 through 2027 for semi-trucks, large pickup trucks, vans, and all types and sizes of buses and work trucks.
On March 31, 2020, NHTSA and the USEPA released a new rule, the final Safer Affordable Fuel-Efficient (SAFE) Vehicles Rule, setting CAFE and carbon dioxide (CO2) emissions standards for model years 2021 through 2026 passenger cars and light trucks. The rule rolls back the 2012 standards for model years 2021 through 2026 for passenger cars and light trucks which required an average fleetwide fuel economy equivalent of 54.5 miles per gallon in model year 2025 with a 5 percent annual increase to an average fuel economy of about 40 miles per gallon in model year 2025 with annual increases of 1.5 percent starting in 2021. As a part of issuing the new SAFE rule, NHTSA issued a Final Environmental Impact Statement which found that the relaxed standards would result in increased petroleum consumption which in turn would result in increases to greenhouse gases and criteria pollutants known to contribute to adverse health impacts (NHTSA 2020). These estimated increases from the roll back of the 2012 standards are expected to result in more than a billion metric tons additional climate pollution through 2040 as determined by calculating the difference from the reduction of 2 billion metric tons the 2012 rule was expected to accomplish compared to the standards of the 2020 rule (NHTSA 2020).
5.2.2 State
In addition to the myriad of GHG legislation and Executive Orders that have the cross benefit of reducing energy usage, the State also has an aggressive Energy Code.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Energy
5.4 California Energy Code
Compliance with the California Energy Code (Title 24, Part 6, of the California Code of Regulations [CCR], California’s Energy Efficiency Standards) and Title 20, Public Utilities and Energy, standards must occur for all new buildings constructed in California. These efficiency standards apply to new construction of both residential and nonresidential (i.e., maintenance buildings and pump station buildings associated with the Program) buildings, and they regulate energy consumed for heating, cooling, ventilation, water heating, and lighting. The building efficiency standards are enforced through the local building permit processes, and local government agencies may adopt and enforce energy standards for new buildings provided that these standards meet or exceed those provided in the Title 24 guidelines.
5.2.3 Local
City of Porterville
The City of Porterville General Plan’s Open Space and Conservation Element includes the following polices related to energy conservation that are applicable to the proposed project.
OSC-G-10: Reduce and conserve energy use in existing and new commercial, industrial, and public structures.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.1 6.0 MODELING PARAMETERS AND ASSUMPTIONS
The following modeling parameters and assumptions were used to generate criteria air pollutant and greenhouse gas (GHG) emissions for the Lombardi Development Project.
6.1 CRITERIA AIR POLLUTANT AND GHG MODEL SELECTION
The California Emissions Estimator Model (CalEEMod) is a statewide land use emissions computer model designed to provide a uniform platform for government agencies, land use planners, and environmental professionals to quantify potential criteria pollutant and greenhouse gas (GHG) emissions associated with both construction and operations from a variety of land use projects. CalEEMod quantifies direct emissions from construction and operation activities (including vehicle use), as well as indirect emissions, such as GHG emissions from energy use, solid waste disposal, vegetation planting and/or removal, and water use. Further, CalEEMod identifies mitigation measures to reduce criteria pollutant and GHG emissions along with calculating the benefits achieved from measures chosen by the user.
CalEEMod was developed for the California Air Pollution Control Officers Association (CAPCOA) in collaboration with the California Air Districts. Default data (e.g., emission factors, trip lengths, meteorology, source inventory, etc.) have been provided by the various California Air Districts to account for local requirements and conditions.
CalEEMod is a comprehensive tool for quantifying air quality impacts from land use projects located throughout California. The model can be used for a variety of situations where an air quality analysis is necessary or desirable such as preparing CEQA or National Environmental Policy Act documents, conducting pre-project planning, and, verifying compliance with local air quality rules and regulations, etc.
CalEEMod version 2020.4.0 was used to estimate construction and operational impacts of the proposed project.
6.2 AIR POLLUTANTS AND GHGS ASSESSED
6.2.1 Criteria Pollutants Assessed
The following criteria air pollutants were assessed in this analysis: reactive organic gases (ROG), oxides of nitrogen (NOX), particulate matter less than 10 microns in diameter (PM10), and particulate matter less than 2.5 microns in diameter (PM2.5). Note that the proposed project would emit ozone precursors ROG and NOX. However, the
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.2 proposed project would not directly emit ozone since it is formed in the atmosphere during the photochemical reaction of ozone precursors.
6.2.2 GHGs Assessed
This analysis was restricted to GHGs identified by AB 32, which include carbon dioxide (CO2), methane (CH4), nitrous oxide (N2O), hydrofluorocarbons (HFCs), perfluorocarbons (PFCs), sulfur hexafluoride (SF6), and nitrogen trifluoride (NF3). The proposed project would generate a variety of GHGs, including several defined by AB 32 such as CO2, CH4, and N2O.
Certain GHGs defined by AB 32 would not be emitted by the project. HFCs, PFCs, SF6, and NF3 are typically used in industrial applications, none of which would be used for typical multifamily residential operations. Therefore, it is not anticipated that the proposed project would emit those GHGs.
GHG emissions associated with the proposed project construction, as well as future operations were estimated using CO2 equivalent (CO2e) emissions as a proxy for all GHG emissions. Construction GHG emissions were amortized over the lifetime of the proposed project. In order to obtain the CO2e, an individual GHG is multiplied by its Global Warming Potential (GWP). The GWP designates on a pound for pound basis the potency of the GHG compared to CO2.
6.3 ASSUMPTIONS
6.3.1 Construction Modeling Assumptions
Construction is anticipated to occur in two phases. The proposed construction phases will not overlap, therefore CalEEMod modeling was prepared for each phase of construction.
Land Use
Table 4 provides a summary of the land use inputs included in the CalEEMod modeling.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.3 Table 4: CalEEMod Land Use Development Summary Table for the Proposed Project
Project
Component
CalEEMod Land Use
Type
Land Use
Unit
Amount
(Size)
Land Use
Size Metric
Total Square
Footage
(Building
Square Footage
is Used for
Buildings)
Land Use
Acreage
Phase 1
Single Family
Homes Single Family Housing 128 DU 230,400 19.34 AC
Roadways Other Asphalt Surfaces 9.08 AC 395,525 9.08 AC Phase 2
Single Family
Homes Single Family Home 105 DU 189,000 18.88 AC
Roadways Other Asphalt Surfaces 8.43 AC 367,211 8.43 AC Park City Park 152,819 SF 01 3.51 AC
Notes:
DU = dwelling unit
SF = square feet
AC = acre
1 The City Park was assumed to not have any buildings constructed.
Construction Schedule
The proposed project would require various tasks including site preparation, grading, building construction, architectural coatings, and paving. Table 5 shows the anticipated construction schedule. The construction schedule utilized in the analysis will represent a “worst-case” analysis scenario since emission factors for construction equipment decrease as the analysis year increases, due to improvements in technology and more stringent regulatory requirements. Therefore, construction emissions would decrease if the construction schedule moved to later years or is phased over multiple years. The duration of construction activity and associated equipment represent a reasonable approximation of the expected construction fleet as required per CEQA guidelines. The site-specific construction fleet may vary due to specific project needs at the time of construction.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.4 Table 5: Project Construction Schedule
Construction Task Start Date End Date Workdays
Phase 1
Site Preparation 10/1/2021 10/14/2021 10
Grading 10/15/2021 11/18/2021 25
Building Construction 11/19/2021 8/25/2022 200
Paving 8/26/2022 9/12/2022 12
Architectural Coating 9/13/2022 9/30/2022 14
Phase 2
Site Preparation 1/1/2023 1/13/2023 10
Grading 1/14/2023 2/17/2023 25
Building Construction 2/18/2023 11/24/2023 300
Paving 11/25/2023 12/12/2023 12
Paving 12/13/2023 12/31/2023 13
Source: CalEEMod Output (Attachment A).
Construction Equipment
The off-road equipment fleet for construction were generated using default values from CalEEMod. CalEEMod generates construction fleets for construction activities based on the size of the construction areas. Construction equipment for each construction activity by phase is shown in Table 6.
Table 6: Project Construction Equipment
Construction Task Equipment Type
Pieces of
Equipment
Usage
(hours/day)Horsepower
Load
Factor
Fuel
Type
Phase 1
Site Preparation
Rubber Tired Dozers 3 8 247 0.40 Diesel
Tractors/Loaders/Backhoes 4 8 97 0.37 Diesel
Grading
Excavators 2 8 158 0.38 Diesel
Graders 1 8 187 0.41 Diesel
Rubber Tired Dozers 1 8 247 0.40 Diesel
Scrapers 2 8 367 0.48 Diesel
Tractors/Loaders/Backhoes 2 8 97 0.37 Diesel
Building
Construction
Cranes 1 7 231 0.29 Diesel
Forklifts 3 8 89 0.20 Diesel
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.5 Construction Task Equipment Type
Pieces of
Equipment
Usage
(hours/day)Horsepower
Load
Factor
Fuel
Type
Phase 1
Generator Sets 1 8 84 0.74 Diesel
Tractors/Loaders/Backhoes 3 7 97 0.37 Diesel
Welders 1 8 46 0.45 Diesel
Paving
Pavers 2 8 130 0.42 Diesel
Paving Equipment 2 8 132 0.36 Diesel
Rollers 2 8 80 0.38 Diesel
Architectural
Coating
Air Compressors 1 6 78 0.48 Diesel
Phase 2
Site Preparation
Rubber Tired Dozers 3 8 247 0.40 Diesel
Tractors/Loaders/Backhoes 4 8 97 0.37 Diesel
Grading
Excavators 2 8 158 0.38 Diesel
Graders 1 8 187 0.41 Diesel
Rubber Tired Dozers 1 8 247 0.40 Diesel
Scrapers 2 8 367 0.48 Diesel
Tractors/Loaders/Backhoes 2 8 97 0.37 Diesel
Building
Construction
Cranes 1 7 231 0.29 Diesel
Forklifts 3 8 89 0.20 Diesel
Generator Sets 1 8 84 0.74 Diesel
Tractors/Loaders/Backhoes 3 7 97 0.37 Diesel
Welders 1 8 46 0.45 Diesel
Paving
Pavers 2 8 130 0.42 Diesel
Paving Equipment 2 8 132 0.36 Diesel
Rollers 2 8 80 0.38 Diesel
Architectural
Coating
Air Compressors 1 6 78 0.48 Diesel
Source: CalEEMod Output (Attachment A)
Vehicle Trips
Off-site construction emissions are caused by motor vehicle exhaust from delivery vehicles, worker traffic, and road dust (PM10 and PM2.5). Table 7 provides a summary of
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.6 the construction-related vehicle trips. CalEEMod default values were used to estimate the number of construction-related vehicle trips.
CalEEMod quantifies the number of construction workers by multiplying 1.25 times the number of pieces of equipment for all phases (except Building Construction and Architectural Coating). CalEEMod default values were used to estimate the number of vendor vehicle trips. The number of vendor trips during the Building Construction phase is derived from a study conducted by the Sacramento Metropolitan Air Quality Management District (SMAQMD) as per the CalEEMod defaults. The SMAQMD trip survey during construction counted cement and water trucks as vendor trips (instead of counting them as off-road vehicle trips) and these trip rates were incorporated into the calculations for the Building Construction phase. The default values for hauling trips assume that a truck can haul 20 tons (or 16 cubic yards) of material per load. If one load of material is delivered, CalEEMod assumes that one haul truck importing material will also have a return trip with an empty truck (e.g., 2 one-way trips).
The fleet mix for worker trips is light-duty passenger vehicles to light-duty trucks. The vendor trips fleet mix is composed of a mixture of medium and heavy-duty diesel trucks.
The hauling trips were assumed to be 100 percent heavy-duty diesel truck trips.
CalEEMod default trip lengths for a project in Tulare County and an urban setting were used for the worker (10.8 miles), vendor (7.3 miles), and hauling trips (20 miles).
Table 7: Construction Vehicle Trips
Construction Task Worker Trips per Day Vendor Trips per Day Total Haul Truck
Trips
Phase 1
Site Preparation 18 0 0
Grading 20 0 0
Building Construction 212 79 0
Paving 15 0 0
Architectural Coating 42 0 0
Phase 2
Site Preparation 18 0 0
Grading 20 0 0
Building Construction 256 96 0
Paving 15 0 0
Architectural Coating 51 0 0
Notes:
No hauling trucks anticipated as there is no demolition and all grading will be balanced on the Project site.
Source: CalEEMod Output (Attachment A).
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.7 6.3.2 Construction Modeling Assumptions
Operational emissions are those emissions that occur during operation of the proposed project. The sources are summarized below.
Motor Vehicles
Motor vehicle emissions refer to exhaust and road dust emissions from the automobiles that would travel to and from the proposed project site. The trip generation rates within CalEEMod version 2020.4.0 rely on the Institute of Transportation Engineer’s (ITE) 10th Edition, which calculates trip rates for a variety of land uses based on land use sizes.
For single-family homes, ITE Code 210 was used as the default setting within the model and is consistent with trip generation tables prepared for the proposed project.
Trip Lengths
The CalEEMod default round trip lengths for an urban setting in Tulare County were used in this analysis. Trip lengths are for primary trips. Trip purpose are primary, diverted, and pass-by trips. Diverted trips take a slightly different path than a primary trip. The CalEEMod default rates for percentages of primary, diverted, and pass-by trips were used. The emissions estimate also considers the internal capture rates, consistent with the project-specific trip generation. Internal capture rates account for vehicle trips that visit the project site for the purpose of visiting more than land use within the project.
Vehicle Fleet Mix
The vehicle fleet mix is defined as the mix of motor vehicle classes active during the operation of the proposed project. Emission factors are assigned to the expected vehicle mix as a function of vehicle class, speed, and fuel use (gasoline- and dieselpowered vehicles). Project-specific fleet mixes were applied in the assessment.
Area Sources
Consumer Products
Consumer products are various solvents used in non-industrial applications that emit ROG during their product use. These typically include cleaning supplies, kitchen aerosols, cosmetics, and toiletries. The default CalEEMod values were used for this project.
Architectural Coatings (Painting)
Paints release VOC emissions. The buildings would be repainted on occasion.
CalEEMod defaults for the wall painting size and VOC paint concentration were used for this purpose.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.8 Landscaping Emissions
CalEEMod will estimate a total of 180 days for which landscaping equipment would be used to estimate potential emissions for the proposed project.
Indirect Emissions
For GHG emissions, CalEEMod contains calculations to estimate indirect GHG emissions. Indirect emissions are emissions where the location of consumption or activity is different from where actual emissions are generated. For example, electricity would be consumed at the proposed project site; however, emissions associated with producing that electricity are generated off-site at a power plant. Since the electricity can vary greatly based on locations, the user should override these values if they have more specific information regarding their specific water supply and treatment.
Energy Use
The Renewables Portfolio Standard (RPS) is not accounted for in CalEEMod 2016.3.2.
Reductions from RPS are addressed by revising the electricity emission intensity factor in CalEEMod to account for the utility RPS rate forecast for 2020. Pacific Gas and Electric (PG&E) would provide electricity and natural gas services to the project site.
PG&E provides emission factors for the electricity it provides to customers for its energy portfolio that is used to estimate project emissions. The utilities will be required to increase the use of renewable energy sources to 60 percent by 2030. The latest information available in PG&E’s 2020 Sustainability Report were used to adjust the project CO2 intensity factor for the project buildout year and 2030 scenarios.
The emissions associated with the building electricity and natural gas usage (nonhearth) were estimated based on the land use type and size. The electricity energy use is in units of kilowatt hours per size metric for each land use type. Natural gas use is in units of one thousand British Thermal Units per size metric for each land use type.
Sequestration
The Project will plant at least one tree at every subdivision lot. Trees sequester carbon from the atmosphere and act as a carbon sink. Within the modeling, it was assumed that a total of 233 trees would be planted (one for each lot). The amount of carbon absorbed from the atmosphere depends on the tree type. The Project will likely plant a variety of trees, as a result, the miscellaneous tree option was selected in order to account for an average amount of carbon sequestered per tree per year.
Other Indirect Emissions (Water Use, Wastewater Use, and Solid Waste) CalEEMod includes calculations for indirect GHG emissions for electricity consumptions, water consumption, and solid waste disposal. For water consumption,
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.9 CalEEMod calculates embedded energy (e.g., treatment, conveyance, distribution) associated with providing each gallon of potable water to the project. For solid waste disposal, GHG emissions are associated with the disposal of solid waste generated by the proposed project into landfills. CalEEMod default data were used for inputs associated with solid waste.
Fugitive Dust
Construction
Fugitive dust would be generated from site grading and other earth-moving activities.
Most of this fugitive dust would remain localized and would be deposited near the project site. However, the potential for impacts from fugitive dust exists unless control measures are implemented to reduce the emissions from the project site. Therefore, adherence to Regulation VIII would be required during construction of the proposed project. Regulation VIII would require fugitive dust control measures that are consistent with best management practices (BMPs) established by the SJVAPCD to reduce the proposed project’s construction-generated fugitive dust impacts to a less than significant level.
Visible Dust Emissions may not exceed 20% opacity during periods when soil is being disturbed by equipment or by wind at any time. Visible dust emissions opacity of 20% means dust that would obstruct an observer’s view of an object by 20%. District inspectors are state certified to evaluate visible emissions. Dust control may be achieved by applying water before/during earthwork and onto unpaved traffic areas, phasing work to limit dust, and setting up wind fences to limit wind blown dust.
Soil Stabilization is required at regulated construction sites after normal working hours and on weekends and holidays. This requirement also applies to inactive construction areas such as phased projects where disturbed land is left unattended. Applying water to form a visible crust on the soil and restricting vehicle access are often effective for short-term stabilization of disturbed surface areas. Long-term methods including applying dust suppressants and establishing vegetative cover.
Carryout and Trackout occur when materials from emptied or loaded vehicles falls onto a paved surface or shoulder of a public road or when materials adhere to vehicle tires and are deposited onto a paved surface or shoulder of a public road. Should either occur, the material must be cleaned up at least daily, and immediately if it extends more than 50 feet from the exit point onto a paved road. The appropriate clean-up methods require the complete removal and cleanup of mud and dirt from the paved surface and shoulder. Using a blower device or dry sweeping with any mechanical device other than a PM10-efficient street sweeper is a violation. Larger construction sites, or sites with a high amount of traffic on one or more days, must prevent carryout and trackout from
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.10 occurring by installing gravel pads, grizzlies, wheel washers, paved interior roads, or a combination thereof at each exit point from the site. In many cases, cleaning up trackout with water is also prohibited as it may lead to plugged storm drains. Prevention is the best method.
Unpaved Access and Haul Roads, as well as unpaved vehicle and equipment traffic areas at construction sites must have dust control. Speed limit signs limiting vehicle speed to 15 mph or less at construction sites must be posted every 500 feet on uncontrolled and unpaved roads.
Storage Piles and Bulk Materials have handling, storage, and transportation requirements that include applying water when handling materials, wetting or covering stored materials, and installing wind barriers to limit VDE. Also, limiting vehicle speeds, loading haul trucks with a freeboard of six inches or greater along with applying water to the top of the load, and covering the cargo compartments are effective measures for reducing VDE and carryout from vehicles transporting bulk materials.
Demolition: activities require the application of water to the exterior of the buildings and to unpaved surfaces where materials may fall. A Dust Control Plan will be required for large demolition projects. Consider all structures slated for demolition as possibly being regulated due to potential asbestos, per District Rule 4002 - National Emission Standards for Hazardous Air Pollutants. Contact the District well before starting because a 10 working-day notice will likely be required before a demolition can begin.
Dust Control Plans identify the dust sources and describe the dust control measures that will be implemented before, during, and after any dust generating activity for the duration of the project. Owners or operators are required to submit plans to the District at least 30 days prior to commencing the work for the following:
• Residential developments of ten or more acres of disturbed surface area. • Non-residential developments of five or more acres of disturbed surface area. • The relocation of more than 2,500 cubic yards per day of materials on at least three days.
Operations may not commence until the District has approved the Dust Control Plan. A copy of the plan must be on site and available to workers and District employees. All work on the site is subject to the requirements of the approved dust control plan. A failure to abide by the plan by anyone on site may be subject to enforcement action.
Owners or operators of construction projects that are at least one acre in size and where a Dust Control Plan is not required, must provide written notification to the District at least 48 hours in advance of any earthmoving activity.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.11 Record Keeping is required to document compliance with the rules and must be kept for each day any dust control measure is used. The District has developed record forms for water application, street sweeping, and “permanent” controls such as applying long term dust palliatives, vegetation, ground cover materials, paving, or other durable materials. Records must be kept for one year after the end of dust generating activities (Title V sources must keep records for five years).
Nuisances are prohibited at all times because District Rule 4102 – Nuisance applies to all construction sources of fugitive dust, whether or not they are exempt from Regulation VIII. It is important to monitor dust-generating activities and implement appropriate dust control measures to limit the public’s exposure to fugitive dust.
6.4 HEALTH RISK ASSESSMENT MODEL SELECTION AND PARAMETERS An air dispersion model is a mathematical formulation used to estimate the air quality impacts at specific locations (receptors) surrounding a source of emissions given the rate of emissions and prevailing meteorological conditions. The air dispersion model applied in this assessment was the United States Environmental Protection Agency (EPA) AERMOD (version 19191) air dispersion model. Specifically, the AERMOD model was used to estimate levels of air emissions at sensitive receptor locations from potential sources of project-generated TACs. The use of the AERMOD model provides a refined methodology for estimating construction impacts by utilizing long-term, measured representative meteorological data for the project site and a representative construction schedule.
The modeling analysis also considered the spatial distribution and elevation of each emitting source in relation to the sensitive receptors. Direction-dependent calculations were obtained by identifying the Universal Transverse Mercator (UTM) coordinates for each source location. Terrain elevations were obtained for the project site using the AERMAP model, the AERMOD terrain data pre-processor.
Specifically, National Elevation dataset (NED) data for the area were obtained and included in the model runs to account for complex terrain. The air dispersion model assessment used meteorological data from the Porterville 23149 Station. The meteorological data used was preprocessed for use with AERMOD by the SJVAPCD and included data for the years 2006 to 2009; all years were used in the assessment. To evaluate the proposed project’s localized impacts at the point of maximum impact, all receptors were placed within the breathing zone at zero meters above ground level.
6.4.1 Construction
For the construction period, construction emissions were assumed to be distributed over the project site assuming emissions would be evenly distributed over a 24-hour period.
Detailed parameters and complete calculations are contained in Appendix B.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Modeling Parameters and Assumptions
6.12 Figure 3 shows a representation of the modeling parameters, including a 1,000-foot buffer, the project area (construction area source) and locations of sensitive receptors.
Figure 3: Project Site with Sensitive Receptors within 1,000 Feet
6.4.2 Air Toxics Generated during Operations
The greatest potential during long-term operations for exposure to TACs is form the use of heavy-duty diesel trucks and stationary generators that use diesel fuel. The proposed Project will operate 233 residential homes and a park. Once operational, the majority of vehicle trips to and from the Project site would be from residents and, as a result, the Project would attract very few diesel truck trips. Additionally, the project does not propose any stationary generators on-site. As such, once operational, the proposed project would not be expected to expose nearby sensitive receptors to substantial amounts of air toxics and the project would have a less than significant impact.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.1 7.0 AIR QUALITY IMPACT ANALYSIS
This section calculates the expected emissions from construction and operation of the proposed project as necessary requisite for assessing the regulatory significance of proposed Project emissions on a regional and localized level.
7.1 CEQA GUIDELINES
According to the CEQA Guidelines’ Appendix G Environmental Checklist, the following questions are analyzed and evaluated to determine whether impacts to air quality are significant environmental effects.
Where available, the significance criteria established by the applicable air quality management or air pollution district may be relied upon to make the following determinations.
Where the Project:
a) Conflict with or obstruct implementation of the applicable air quality plan? b) Result in a cumulatively considerable net increase of any criteria pollutant for which the project region is non-attainment under an applicable federal or state ambient air quality standard?
c) Expose sensitive receptors to substantial pollutant concentrations? d) Result in other emissions (such as those leading to odors) affecting a substantial number of people?
7.1.1 Thresholds of Significance
While the final determination of whether a project is significant is within the purview of the Lead Agency pursuant to Section 15064(b) of the CEQA Guidelines, the SJVAPCD recommends that its quantitative air pollution thresholds (shown in Table 8) be used to determine the significance of project emissions. If the Lead Agency finds that the project has the potential to exceed these air pollution thresholds, the project should be considered to have significant air quality impacts.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.2 Table 8: SJVAPCD Significance Thresholds
Pollutant
Significance Threshold
Construction Emissions
(tons/year)
Operational Emission (tons/year)
CO 100 100
NOX 10 10
ROGs 10 10
SOX 27 27
PM10 15 15
PM2.5 15 15
Source: SJVAPCD 2015
The project does not contain sources that would produce substantial quantities of SO2 emissions during construction and operation. Modeling conducted for the project show that SO2 emissions are well below the SJVAPCD GAMAQI thresholds, as shown in the modeling results contained in Appendix A. No further analysis of SO2 is required.
7.2 AIR IMPACT ANALYSIS
Impact AIR-1 Conflict with or obstruct implementation of the applicable air quality plan?
Impact Analysis
The CEQA Guidelines indicate that a significant impact would occur if the Project would conflict with or obstruct implementation of the applicable air quality plan. The GAMAQI does not provide specific guidance on analyzing conformity with the Air Quality Plan (AQP). Therefore, this document proposes the following criteria for determining project consistency with the current AQP’s:
1. Will the project result in an increase in the frequency or severity of existing air quality violations or cause or contribute to new violations, or delay timely attainment of air quality standards or the interim emissions reductions specified in the AQPs? This measure is determined by comparison to the regional and localized thresholds identified by the District or Regional and Local Air Pollutants.
2. Will the project conform to the assumptions in the AQPs?
3. Will the project comply with applicable control measures in the AQPs?
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.3 The use of criteria listed above is a standard approach for CEQA analysis of projects in the SJVAPCD’s jurisdictions, as well as within other air districts, for the following reasons:
• Significant contribution to existing or new exceedances of the air quality standards would be inconsistent with the goal of attaining the air quality standards.
• Air Quality Plan (AQP) emissions inventories and attainment modeling are based on growth assumptions for the area within the SJVAPCD’s jurisdiction. • AQPs rely on a set or air district-initiated control measures as well as implementation of federal and state measures to reduce emissions within their jurisdictions, with the goal of attaining the air quality standards.
AQPs are plans for reaching attainment of air quality standards. The assumptions, inputs, and control measures are analyzed to determine if the SJVAB can reach attainment for the ambient air quality standards. To show attainment of the standards, the SJVAPCD analyzes the growth projections in the valley, contributing factors in air pollutant emissions and formations, and existing and adopted emissions controls. The SJVAPCD then formulates a control strategy to reach attainment that includes both State and SJVAPCD regulations and other local programs and measures. The applicable AQPs include the 2016 8-Hour Ozone Plan which contains measures to achieve reductions in emissions of ozone precursors and sets plans towards attainment of ambient ozone standards by 2031 and the 2018, 2016, 2015, 2012, and 2008 PM2.5 Plans to address multiple PM2.5 air quality standards and attainment deadlines.
Contribution to Air Quality Violations
A measure of determining if the Project is consistent with the air quality plans is if the Project would not result in an increase in the frequency or severity of existing air quality violations or cause or contribute to new violations or delay timely attainment of air quality standards or the interim emission reductions specified in the air quality plans.
Because of the region’s nonattainment status for ozone, PM2.5, and PM10, if Projectgenerated emissions of either of the ozone precursor pollutants (ROG and NOx), PM10, or PM2.5 would exceed the SJVAPCD’s significance thresholds, then the Project would be considered to conflict with the attainment plans.
As shown in Impact AIR-2, emissions of ROG, NOX, PM10, and PM2.5 from construction and operation of the Project would not exceed the SJVAPCD’s significance thresholds. As shown in Impact AIR-3, the Project would not expose sensitive receptors to a substantial pollutant concentration. Therefore, the Project would not contribute to air quality violations.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.4 Consistency with Assumptions in AQPs
The primary way of determining consistency with the AQP’s assumptions is determining consistency with the applicable General Plan to ensure that the project’s population density and land use are consistent with the growth assumptions used in the AQPs for the SJVAB.
As required by California law, city and county General Plan contain a Land Use Element that details the types and quantities of land uses that the city or county estimates will be needed for future growth and designates locations for land uses to regulate growth. The Tulare Council of Governments (Tulare COG) uses the growth projections and land use information in adopted general plans, among other sources to estimate future average daily trips and then vehicles miles traveled (VMT), which are then provided to the SJVAPCD to estimate future emissions in the AQPs. Existing and future pollutant emissions computed in the AQPs are based on land uses from area general plans.
AQPs detail the control measures and emission reductions required for reaching attainment of the air standards based on these growth and emission estimates.
The applicable General Plan for the project is the City of Porterville 2030 General Plan, which was adopted in 2008, prior to the SJVAPCD’s adoption of the applicable AQPs.
The Land Use General Plan designated the site as Low Density Residential. Therefore, the Project would be consistent with the modeling used to prepare the AQPs. The impact would be less than significant.
Control Measures
The AQP contains several control measures, which are enforceable requirements through the adoption of rules and regulations. A detailed description of rules and regulations that apply to this Project is provided in the Regulatory Setting. The Project would comply with all applicable SJVAPCD rules and regulations. Therefore, the project complies with this criterion and would not conflict with or obstruct implementation of the applicable air quality plan.
Conclusion
The Project would not conflict with or obstruct implementation of the applicable AQPs.
Level of Significance Before Mitigation
Less Than Significant Impact.
Mitigation Measures
None are required.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.5 Level of Significance After Mitigation
Less Than Significant Impact.
Impact AIR-2 Result in a cumulatively considerable net increase of any criteria pollutant for which the project region is non-attainment under an applicable federal or State ambient air quality standard?
Impact Analysis
To result in a less than significant impact, the following criteria must be true:
1. Regional analysis: emissions of nonattainment pollutants must be below the SJVAPCD’s regional significance thresholds. This is an approach recommended by the SJVAPCD in its GAMAQI.
2. Summary of projections: the project must be consistent with current air AQPs including control measures and regulations. This is an approach consistent with Section 15130(b) of the CEQA Guidelines.
3. Cumulative health impacts: the project must result in less than significant cumulative health effects from the nonattainment pollutants. This approach correlates the significance of the regional analysis with health effects, consistent with the court decision, Bakersfield Citizens for Local Control v. City of Bakersfield (2004) 124 Cal.App.4th 1184, 1219-20.
Step 1: Regional Analysis
Air pollutant emissions have regional effects and localized effects. This analysis assesses the regional effects of the Project’s criteria pollutant emissions in comparison to SJVAPCD thresholds of significance for short-term construction activities and longterm operation of the project. Localized emissions from Project construction and operation are also assessed using concentration-based thresholds that determine if the Project would result in a localized exceedance of any ambient air quality standards or would make a cumulatively considerable contribution to an existing exceedance.
The primary pollutants of concern during Project construction and operation are ROG, NOx, PM10, and PM2.5. The SJVAPCD GAMAQI adopted in 2015 contains thresholds for ROG and NOx; SOX, CO, PM10, and PM2.5.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.6 Ozone is a secondary pollutant that can be formed miles away from the source of emissions through reactions of ROG and NOx emissions in the presence of sunlight.
Therefore, ROG and NOx are termed ozone precursors. The SJVAB often exceeds the state and national ozone standards. Therefore, if the Project emits a substantial quantity of ozone precursors, the Project may contribute to an exceedance of the ozone standard. The SJVAB also exceeds air quality standards for PM10, and PM2.5; therefore, substantial Project emissions may contribute to an exceedance for these pollutants. The SJVAPCD’s annual emission significance thresholds used for the Project define substantial contribution both operational and construction emissions are provided in Table 14.
Construction Emissions
Construction emissions associated with the Project are shown in Table 9. For assumptions in estimating the emissions, please refer to Modeling Parameters and Assumptions. As shown in Table 12, the emissions are below the significance thresholds and, therefore, are less than significant on a Project basis.
Table 9: Construction Emissions – Unmitigated
Emissions
Source
Emissions (Tons/Year)
ROG NOX CO SOX PM10 PM2.5
Phase One
2021
Site
Preparation 0.02 0.20 0.11 <0.01 0.11 0.06
Grading 0.05 0.58 0.39 <0.01 0.14 0.07
Building
Construction
(2021)
0.05 0.36 0.39 <0.01 0.05 0.02
2021 Subtotal 0.12 1.15 0.89 <0.01 0.30 0.15
2022
Building
Construction
(2022)
0.23 1.74 2.03 <0.01 0.26 0.12
Paving 0.02 0.07 0.09 <0.01 0.00 0.00
Architectural
Coating 2.25 0.01 0.02 <0.01 0.00 0.00
2022 Subtotal 2.49 1.82 2.14 <0.01 0.27 0.12
Phase Two
2023
Site
Preparation 0.01 0.14 0.09 0.00 0.11 0.06
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.7 Emissions
Source
Emissions (Tons/Year)
ROG NOX CO SOX PM10 PM2.5
Grading 0.04 0.43 0.36 0.00 0.13 0.02
Building
Construction 0.26 1.93 2.45 0.01 0.34 0.14
Paving 0.02 0.06 0.09 <0.01 <0.01 <0.01
Architectural
Coating 1.85 0.01 0.02 <0.01 <0.01 <0.01
2023 Subtotal 2.18 2.57 3.01 <0.01 0.59 0.27
Total Construction Duration (Phase One and Phase Two)
Maximum in
Any Calendar
Year
2.49 2.57 3.01 <0.01 0.59 0.27
Significance
Thresholds 10 10 100 27 15 15
Any Year
Exceed
Significance
Thresholds?
No No No No No No
Notes:
Source of Emissions: CalEEMod Output (Attachment A).
Source of Thresholds: San Joaquin Valley Air Pollution Control District (Valley Air District). 2015. Guidance for Assessing and Mitigating Air Quality Impacts. February 19. Website: https://www.valleyair.org/transportation/GAMAQI-2015/FINAL-DRAFTGAMAQI.PDF. Accessed July 19, 2021.
Operations
Operational emissions occur over the lifetime of the project and from two main sources:
areas sources and motor vehicles. The SJVAPCS considers construction and operations emissions separately when making significance determination. However, Phase One will likely become operational when Phase Two is under construction. The overlap in emissions between Phase One operation and Phase Two construction are evaluated in Table 10 and demonstrate that emissions during this overlap would be less than the thresholds of significance for all criteria air pollutants.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.8 Table 10: Summary of Overlapping Phase One Operational and Phase Two Construction Criteria Air Pollutants - Unmitigated
Source Emissions (tons/year)
ROG NOX CO SOX PM10 PM2.5
Phase One Operation
Area 1.18 0.06 0.97 >0.01 0.01 0.01
Energy 0.02 0.14 0.06 >0.01 0.01 0.01
Mobile 0.69 1.23 6.45 0.01 1.27 0.35
Total Phase One
Operational
1.89 1.43 7.48 0.01 1.29 0.37
Phase Two Construction
Total Phase Two
Construction (2023) 2.18 2.57 3.01 <0.01 0.59 0.27
Total Overlapping Emissions (Phase One Operation and Phase Two Construction) Total 4.07 4.00 10.49 0.01 1.88 0.64
Significance
Thresholds 10 10 100 27 15 15
Exceed Significance
Thresholds? No No No No No No
Notes:
Emissions were quantified using CalEEMod, version 2020.4.0 based on project details and estimated operating year for the proposed project. Totals may not sum exactly due to rounding.
Source: CalEEMod Output (Attachment A).
The emissions output for project operation at full buildout for 2024 are summarized in Table 14. As shown in Table 11, the operational emissions would be less than the thresholds of significance for all criteria air pollutants. The impact is less than significant.
Table 11: Summary of Operational Emissions of Criteria Air Pollutants – Unmitigated
Source Emissions (tons/year)
ROG NOX CO SOX PM10 PM2.5
Phase One Operation
Area 1.18 0.06 0.97 >0.01 0.01 0.01
Energy 0.02 0.14 0.06 >0.01 0.01 0.01
Mobile 0.69 1.23 6.45 0.01 1.27 0.35
Subtotal Phase One
Operational
1.89 1.43 7.48 0.01 1.29 0.37
Phase Two Operation
Area 0.98 0.05 0.80 >0.01 0.01 0.01
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.9 Source Emissions (tons/year)
ROG NOX CO SOX PM10 PM2.5
Energy 0.01 0.12 0.05 >0.01 0.01 0.01
Mobile 0.50 0.83 4.64 0.01 1.04 0.29
Subtotal Phase Two
Operational
1.49 0.99 5.49 0.01 1.06 0.30
2024 Full Buildout
Total
3.38 2.42 12.97 0.02 2.35 0.67
Significance
Thresholds 10 10 100 27 15 15
Exceed Significance
Thresholds? No No No No No No
Notes:
Emissions were quantified using CalEEMod, version 2020.4.0 based on project details and estimated operating year for the proposed project. Totals may not sum exactly due to rounding.
Source: CalEEMod Output (Attachment A).
If an area is in nonattainment for a criteria pollutant, then the background concentration of that pollutant has historically exceeded the ambient air quality standard. It follows that if a project exceeds the regional threshold for that nonattainment pollutant, then it would result in a cumulatively considerable net increase of that pollutant and result in a significant cumulative impact.
The SJVAB is in nonattainment for PM10, PM2.5, and ozone. Therefore, if the Project exceeds the regional thresholds for PM10, or PM2.5, then it contributes to a cumulatively considerable impact for those pollutants. If the Project exceeds the regional threshold for NOX or ROG, then it follows that the Project would contribute to a cumulatively considerable impact for ozone.
The criteria pollutant emissions analysis, as shown in above, assessed whether the Project would exceed the SJVAPCD’s thresholds of significance. As shown in Table 11 and Table 12, criteria pollutant emissions would not exceed any threshold of significance during Project construction or operation. Therefore, the combination of unmitigated Project emissions with the criteria pollutants from other sources within the SJVAB would not cumulatively contribute to a significant impact according to this criterion.
Step 2: Plan Approach
Section 15130(b) of the CEQA Guidelines states the following:
The following elements are necessary to an adequate discussion of significant cumulative impacts: 1) Either: (A) A list of past, present, and probable future projects producing related or cumulative impacts, including, if necessary, those projects outside
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.10 the control of the agency, or (B) A summary of projections contained in an adopted general plan or related planning document, or in a prior environmental document which has been adopted or certified, which described or evaluated regional or area wide conditions contributing to the cumulative impact.
In accordance with CEQA Guidelines 15130(b), this analysis of cumulative impacts is based on a summary of projections analysis. The SJVAB is in nonattainment for ozone and particulate matter (PM10 and PM2.5), which means that concentrations of these pollutants currently exceed the applicable ambient air quality standards.
Cumulative impacts may be analyzed using other plans that evaluate relevant cumulative effects. The geographic scope for cumulative criteria pollution from air quality impacts is the SJVAB, because that is the area in which the air pollutants generated by the sources within the SJVAB circulate and are often trapped. The SJVAPCD is required to prepare and maintain air quality attainment plans and a State Implementation Plan to document the strategies and measures to be undertaken to reach attainment of ambient air quality standards. While the SJVAPCD does not have direct authority over land use decisions, it is recognized that changes in land use and circulation planning would help the SJVAB achieve clean air mandates. The SJVAPCD evaluated emissions from land uses and transportation in the entire SJVAB when it developed its attainment plans.
In accordance with CEQA Guidelines Section 15064, subdivision (h)(3), a lead agency may determine that a project’s incremental contribution to a cumulative effect is not cumulatively considerable if the Project complies with the requirements in a previously approved plan or mitigation program.
As discussed in Impact AIR-1, the project is consistent with all applicable control measures in the air quality attainment plans. The Project would be required to comply with any SJVAPCD rules and regulations that may pertain to implementation of the AQPs. Therefore, impacts would be less than significant with regard to compliance with control measures and regulations.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.11 Step 3: Cumulative Health Impacts
The SJVAB is in nonattainment for ozone, PM10, and PM2.5, which means that the background levels of those pollutants are at times higher than the ambient air quality standards. The air quality standards were set to protect public health, including the health of sensitive individuals (such as children, the elderly, and the infirm). Therefore, when the concentration of those pollutants exceeds the standard, it is likely that some sensitive individuals in the population would experience health effects.
Adverse health effects induced by ozone includes short-term effects such as coughing, difficulty breathing, and sore throat as well as long-term effects including inflamed or damaged airways, aggravated lung diseases like asthma or bronchitis, and increased frequency of asthma attacks. O3 is created through chemical reactions between NOx, VOCs, and oxygen (EPA, 2021c). Therefore, the health effects related to O3 are the product of emissions generated by numerous sources throughout the region.
Exposure to particulate matter (PM10 and PM2.5) can affect the lungs and heart and may cause irregular heartbeat, aggravated asthma, and decreased lung function (EPA, 2021b). Direct sources of particulate matter include construction sites, unpaved roads, fields, and fires. Particulate matter is also formed indirectly as a result of complex reactions of chemicals such as SOx and NOx (EPA, 2021b).
The SJVAPCD has acknowledged that while HRAs for localized air toxic impacts are commonly prepared, the currently available modeling tools are not equipped to provide a meaningful analysis of the correlation between an individual development project’s criteria air pollutant emissions and specific human health impacts (SJVAPCD, 2015b).
The South Coast Air Quality Management District (SCAQMD) states that based on their own modeling in the SCAQMD’s 2012 Air Quality Management Plan, a reduction of 432 tons (864,000 pounds) per day of NOx and a reduction of 187 tons (374,000 pounds) per day of VOC would reduce O3 levels at the highest monitored site by only nine parts per billion. As such, the SCAQMD concludes that it is not currently possible to accurately quantify O3-related health impacts caused by NOx or VOC emissions from relatively small projects (defined as projects with regional scope) due to photochemistry and regional model limitations (SCAQMD, 2015).
The regional analysis of construction and operational emissions, as shown above indicates that the Project would not exceed the SJVAPCD’s significance thresholds, and the Project is consistent with the applicable AQPs. Therefore, the Project’s emissions would not have a measurable effect on human health and would not result in significant cumulative health impacts from nonattainment pollutants and impacts would be less than significant.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.12 Conclusion
The proposed Project would not result in a cumulatively considerable net increase of any criteria pollutant for which the project region is non-attainment under an applicable federal or state ambient air quality standard.
Level of Significance Before Mitigation
Less Than Significant Impact.
Mitigation Measures
None are required.
Level of Significance After Mitigation
Less Than Significant Impact.
Impact AIR-3 Expose sensitive receptors to substantial pollutant concentrations?
Impact Analysis
This discussion addresses whether the proposed Project would expose sensitive receptors to Naturally Occurring Asbestos (NOA), construction-generated fugitive dust (PM10), ROG, NOX, PM2.5, Valley Fever, construction generated DPM and operational health risks from the proposed service station. A sensitive receptor is a person in a population who is particularly susceptible to health effects due to exposure to an air contaminant. The following are land uses (sensitive sites) where sensitive receptors are typically located:
• Long-term health care facilities
• Rehabilitation centers
• Convalescent centers
• Hospitals
• Retirement homes
• Residences
• Schools, playgrounds and childcare centers
The proposed Project is considered a sensitive receptor once operational, however there are not any nearby sources of TAC near the site and impact to these receptors
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.13 was not evaluated. The nearest off-site sensitive receptors are the residents adjacent to the project site.
Localized Impacts
Emissions occurring at or near the Project have the potential to create a localized impact also referred to as an air pollutant hotspot. Localized emissions are considered significant if when combined with background emissions, they would result in exceedance of any health-based air quality standard. In locations that already exceed standards for these pollutants, significance is based on a significant impact level (SIL) that represents the amount that is considered a cumulatively considerable contribution to an existing violation of an air quality standard. The pollutants of concern for localized impact in the SJVAB are NO2 and CO.
The SJVAPCD has provided guidance for screening localized impacts in the GAMAQI that establishes a screening threshold of 100 pounds per day of any criteria pollutant. If a project exceeds 100 pounds per day of any criteria pollutant, then ambient air quality modeling would be necessary. If the Project does not exceed 100 pounds per day of any criteria pollutant, then it can be assumed that it would not cause a violation of an ambient air quality standard.
Construction: Localized Concentrations of PM10, PM2.5, CO, and NO2 Local construction impacts would be short-term in nature lasting only during the duration of construction. Because of the short duration and limited amount of construction anticipated for the Project, application of best management practices through compliance with Regulation VIII Fugitive Dust Prohibitions to minimize construction emissions, and levels of emissions less than the SJVAPCD’s emission significance thresholds, localized construction concentrations are considered less than significant. It should also be noted that the on-site construction emissions would be less than 100 pounds per day for each of the criteria pollutants, as shown in Table 12 below. To present a conservative estimate, on-site emissions for on-road construction vehicles were included in the localized analysis. It should be noted that the estimates below do not include reductions associated with Rule 9510 compliance, which would reduce NOX and PM10 emissions. Based on the SJVAPCD’s guidance the construction emissions would not cause an ambient air quality standard violation. Impacts would be less than significant.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.14 Table 12: Localized Concentrations of PM10, PM2.5, CO, and NOX for Construction
Emissions Source Emissions (pounds per day)
NOX CO PM10 PM2.5
Phase One
2021
Site Preparation 40.50 21.15 21.70 11.98
Grading 46.40 30.88 11.19 5.48
Building Construction (2021) 17.43 16.58 0.96 0.90
2021 Maximum 46.40 30.88 21.70 11.98
2022
Building Construction (2022) 15.61 16.36 0.81 0.76
Paving 11.12 14.58 0.57 0.52
Architectural Coating 1.41 1.81 0.08 0.08
2022 Maximum 15.61 16.36 0.81 0.76
Phase Two
2023
Site Preparation 27.52 18.24 20.92 11.27
Grading 34.52 28.05 10.63 4.96
Building Construction 14.38 16.24 0.70 0.66
Paving 10.19 14.58 0.51 0.50
Architectural Coating 1.30 1.81 0.07 0.07
2023 Maximum 34.52 28.05 20.92 11.27
Total Construction Duration (Phase One and Phase Two)
Maximum in Any Calendar
Year 46.40 30.88 21.70 11.98
Significance Thresholds 100 100 100 100
Any Year Exceed
Significance Thresholds? No No No No
Notes: PM10 and PM2.5 emissions are from the unmitigated output and as a result are more conservative as they do not reflect compliance with Regulation VIII—Fugitive PM10 Prohibitions. The table only accounts for on-site construction emissions.
Source of Emissions: CalEEMod Output (Attachment A).
Source of Thresholds: San Joaquin Valley Air Pollution Control District (SJVAPCD). 2015. Guidance for Assessing and Mitigating Air Quality Impacts. February 19. Website: https://www.valleyair.org/transportation/GAMAQI2015/FINAL-DRAFT-GAMAQI.PDF. Accessed April 16, 2021.
Operation: Localized Concentrations of PM10, PM2.5, CO, and NO2 Localized impacts could occur in areas with a single large source of emissions such as a power plant or with multiple sources concentrated in a small area such as a
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.15 distribution center. Since the proposed project is proposing the develop 233 single family homes and a park on the project site localized levels of PM10, PM2.5, CO, and NO2 are not expected to exceed localized impacts.
Construction
ROG
During paving operations, ROG is emitted. The amount emitted is dependent on the amount of ROG (or VOC) in the paving materials. There are three types of asphalt that are typically used in paving: asphalt cements, cutback asphalts, and emulsified asphalts. However, SJVAPCD Rule 4641 prohibits the use of the following types of asphalt: rapid cure cutback asphalt; medium cure cutback asphalt; slow cure asphalt that contains more than one-half (0.5) percent of organic compounds that evaporate at 500 degrees Fahrenheit (°F) or lower; and emulsified asphalt containing organic compounds, in excess of 3 percent by volume, that evaporate at 500°F or lower. An exception to this is medium cure asphalt when the National Weather Service official forecast of the high temperature for the 24-hour period following application is below 50°F.
The acute (short-term) health effects from worker direct exposure to asphalt fumes include irritation of the eyes, nose, and throat. Other effects include respiratory tract symptoms and pulmonary function changes. The studies were based on occupational exposure of fumes. Sensitive receptors are not in the immediate vicinity of the fumes; therefore, they would not be subjected to concentrations high enough to evoke a negative response. In addition, the restrictions that are placed on asphalt in the San Joaquin Valley reduce ROG emissions from asphalt and exposure. The impact to sensitive receptors from ROG during construction is less than significant.
Naturally-Occurring Asbestos
According to a map of areas where naturally occurring asbestos in California are likely to occur (U.S. Geological Survey 2011), there are no such areas in the Project area.
Therefore, development of the project is not anticipated to expose receptors to naturally occurring asbestos. Impacts would be less than significant.
Fugitive Dust (PM10)
PM10 emissions would not exceed the thresholds of significance, nevertheless, the potential for localized PM10 health impacts are a concern, however, the Project would comply with the SJVAPCD’s Regulation VIII incorporating Best Management Practices for reducing fugitive dust, thus potential impacts are reduced to a less than significant level.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.16 Valley Fever
Valley fever, or coccidioidomycosis, is an infection caused by inhalation of the spores of the fungus, Coccidioides immitis (C. immitis). The spores live in soil and can live for an extended time in harsh environmental conditions. Activities or conditions that increase the amount of fugitive dust contribute to greater exposure, and they include dust storms, grading, and recreational off-road activities. The San Joaquin Valley is considered an endemic area for Valley fever.
Construction activities would generate fugitive dust that could contain C. immitis spores.
The Project will minimize the generation of fugitive dust during construction activities by complying with the SJVAPCD’s Regulation VIII. Therefore, this regulation would reduce Valley fever impacts to less than significant.
During operations, dust emissions are anticipated to be negligible, because most of the Project area would be occupied by buildings, pavement, and landscaped areas. This condition would preclude the possibility of the Project from generating fugitive dust that may contribute to Valley fever exposure. Impacts would be less than significant.
Health Risk Assessment
Construction
Construction activities have the potential to generate Diesel Particulate Matter (DPM) emissions related to the number and types of equipment typically associated with construction. Off-road, heavy-duty diesel equipment used for site grading, paving, and other construction activities result in the generation of DPM. For construction activity, DPM is the primary air toxic of concern. Particulate exhaust emissions from dieselfueled engines (i.e., DPM) were identified as a toxic air contaminant (TAC) by the California Air Resources Board (CARB) in 1998. Because of the proximity of sensitive receptors there is the potential for the DPM emissions to result in a health impact.
Accordingly, an analysis was prepared to determine if a potential health risk would occur.
A construction HRA was prepared in accordance with SJVAPCD and OEHHA guidance for the proposed project and is included as Appendix B. To assess the project’s total health risk impacts, impacts from both construction and operations were considered in this HRA; therefore, the construction HRA is summarized below.
The construction HRA evaluated DPM (represent as exhaust PM2.5) emissions generated during construction of the proposed project and the related health risk impacts for sensitive receptors located within 1,000 feet of the project boundary. A project would result in a significant impact if it would individually expose sensitive receptors to TACs resulting in an increased cancer risk greater than 20 in one million or
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.17 an increased non-cancer risk of greater than 1.0 on the hazard index. It should be noted that the SJVAPCD’s latest threshold of significance for TAC emissions is an increase in cancer risk for the maximally exposed individual of 20 in one million (formerly 10 in one million).
The project site is located within 1,000 feet from existing sensitive receptors that could be exposed to diesel emission exhaust during the construction and operational periods.
The nearest sensitive receptors are residents occupying the single-family houses adjacent to the project site to the north and east. Furthermore, there are existing are residences surrounding the project site on all sides (to the north, east, south, and west).
There is an existing commercial center west of the southern half of the project site. To estimate the potential cancer risk associated with construction of the proposed project from equipment exhaust (including DPM), a dispersion model was used to translate an emission rate from the source location to concentrations at the receptor locations of interest (i.e., receptors at nearby residences).
Figure 4: Project Site with a 1,000 Foot Buffer
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.18 The location of the maximally exposure individual receptor (MEIR) is located on Westwood Boulevard, immediately west of the project site. As discussed above, AERMOD dispersion model was used to predict concentrations of DPM and PM2.5 at sensitive receptors within 1,000 feet of the project site, as recommended by the SJVAPCD. To model emissions, a release height of 3 meters was chosen to represent the release height of construction equipment. Emissions from off-road construction equipment and on-road vehicle travel were distributed throughout the modeled area source.
The current OEHHA guidance recommends that cancer risks be calculated by age groups to account for different breathing rates and sensitivity to TACs. Specifically, it recommends evaluating the risks for the third trimester of pregnancy to age zero (third trimester exposure), ages zero to less than two (infant exposure), ages two to less than 16 (child exposure), and ages 16 to 70 (adult exposure). Age sensitivity factors (ASFs) associated with the different types of exposure are an ASF of 10 for the third trimester and infant exposure, an ASF of 3 for child exposure, and an ASF of 1 for an adult exposure. Also associated with each exposure type are different breathing rates, expressed as liters per kilograms of body weight per day (L/kg-day). As recommended, 95th percentile breathing rates are used for the third trimester and infant exposure, and 80th percentile breathing rates are used for child and adult exposure. These agespecific breathing rates are 361 L/kg-day for the third trimester receptor, 1,090 L/kg-day for the infant receptors, 572 L/kg-day for child receptors, and 233 L/kg-day for adult receptors (OEHHA 2015).. According to OEHHA, the cancer risk for a residential receptor is assumed to start in the third trimester of life.
Results of the construction health risk analysis for the unmitigated emissions are summarized in Table 13. The complete construction HRA prepared for the proposed project, including calculations and AERMOD output data used in the assessment are included in Appendix B.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.19 Table 13: Health Risks from Project Construction at the Maximally Exposed Sensitive Receptor (Unmitigated)
Health Impact Metric
Carcinogenic
Inhalation Health
Risk in One Million
Chronic Inhalation
Hazard Index
Risks and Hazards at the maximally exposed sensitive receptor1 Risks and Hazards: Infant 25.6 0.016
Risks and Hazards: Child 4.03 0.016
Risks and Hazards: Adult 0.61 0.016
Threshold 20 1
Exceeds Threshold? Yes No
Notes:
1 The maximally exposed sensitive receptor is located at an existing residence located approximately 100 feet west of the project site. 2 Chronic non-cancer hazard index was estimated by dividing the annual DPM concentration (as PM2.5 exhaust) by the REL of 5 µg/m3.
Source: Appendix B.
As shown in Table 13, mitigation would be required to reduce potential impacts from project construction. MM AIR-1 requires the applicant provide documentation to the City of Porterville demonstrating that all off-road diesel-powered construction equipment greater than 50 horsepower meets EPA or ARB Tier 4 off-road emissions standards.
Equipment tiers refer to a generation of emission standards established by the EPA and ARB that apply to diesel engines in off-road equipment. Since Tier 1 emission standards were established by the EPA in 1994, increasingly more stringent Tier 2, Tier 3, and Tier 4 (interim and final) standards were adopted by the EPA, as well as CARB. Results of the construction health risk analysis after the incorporation of MM AIR-1 are summarized in Table 14.
Table 14: Health Risks from Project Construction at the Maximally Exposed Sensitive Receptor (Mitigated)
Health Impact Metric
Carcinogenic
Inhalation Health
Risk in One Million
Chronic Inhalation
Hazard Index
Risks and Hazards at the maximally exposed sensitive receptor1 Risks and Hazards: Infant 3.63 0.002
Risks and Hazards: Child 0.57 0.002
Risks and Hazards: Adult 0.08 0.002
Threshold 20 1
Exceeds Threshold? No No
Notes:
1 The maximally exposed sensitive receptor is located at an existing residence located approximately 100 feet west of the project site. 2 Chronic non-cancer hazard index was estimated by dividing the annual DPM concentration (as PM2.5 exhaust) by the REL of 5 µg/m3.
Source: Appendix B.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.20 Operations
The greatest potential during long-term operations for exposure to TACs is from the use of heavy-duty diesel trucks and stationary generators that use diesel fuel. The proposed project is a 233-unit residential development with park uses. Once operational, the majority of vehicle trips to the project site will be from residents and, as a result, the proposed project would attract very few diesel truck trips. Additionally, the project does not propose any stationary generators on-site. For these reasons, once operational, the proposed project would not be expected to expose nearby sensitive receptors to substantial amounts of air toxics and the project would have a less than significant impact.
Conclusion
Sensitive receptors would not be exposed to substantial pollutant concentrations.
Level of Significance Before Mitigation
Less Than Significant Impact With Mitigation.
Mitigation Measures
MM AIR-1: Clean Construction Fleet. The Project Applicant and/or their respective contractors shall submit documentation to the City of Porterville demonstrating that all off-road diesel-powered construction equipment greater than 50 horsepower meets EPA or ARB Tier 5 off-road emission standards.
Level of Significance After Mitigation
Less Than Significant Impact.
Impact AIR-4 Result in other emissions (such as those leading to odors) affecting a substantial number of people?
Impact Analysis
While offensive odors rarely cause any physical harm, they can still be very unpleasant, leading to considerable distress among the public and often generating citizen complaints to local governments and the SJVAPCD. The occurrence and severity of odor impacts depends on numerous factors, including nature, frequency, and intensity of the source, the wind speed and direction, and the sensitivity of the receptor. The nearest sensitive receptor in the vicinity of the proposed Project site would be the
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Air Quality Impact Analysis
7.21 students and faculty at West Hills College, approximately 912 feet south of the Project site, the nearest residential receptor would be the single-family residence located 2,700 feet east of the Project site.
Construction activities associated with the proposed Project could result in short-term odorous emissions from diesel exhaust associated with construction equipment.
However, these emissions would be intermittent and would dissipate rapidly from the source. In addition, this diesel-powered equipment would only be present on site temporarily during construction activities. Therefore, construction would not create objectionable odors affecting a substantial number of people, and the impact would be less than significant.
Land uses typically considered associated with odors include wastewater treatment facilities, waste-disposal facilities, or agricultural operations. The proposed Project does not contain land uses typically associated with emitting objectionable odors and is not located within the screening distances to sources of odors recommended by the SJVAPCD. Therefore, the impact would be less than significant.
Conclusion
The proposed Project would not create objectionable odors affecting a substantial number of people.
Level of Significance Before Mitigation
Less Than Significant Impact.
Mitigation Measures
None.
Level of Significance After Mitigation
Less Than Significant Impact.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.1 8.0 GREENHOUSE GAS IMPACT ANALYSIS
8.1 CEQA GUIDELINES
The CEQA Guidelines define a significant effect on the environment as “a substantial, or potentially substantial, adverse change in the environment.” To determine if a project would have a significant impact on GHGs, the type, level, and impact of emissions generated by the project must be evaluated.
The following GHG significance thresholds are contained in Appendix G of the CEQA Guidelines:
a) Generate greenhouse gas emissions, either directly or indirectly, that may have a significant impact on the environment; or
b) Conflict with any applicable plan, policy or regulation of an agency adopted for the purpose of reducing the emissions of greenhouse gases.
This section discusses potential impacts concerning greenhouse gases associated with the proposed project and provides mitigation measures where necessary.
8.1.1 Thresholds
The State CEQA Guidelines indicate that a project would normally have a significant adverse GHG impact is the project would:
• Generate greenhouse gas emissions, either directly or indirectly, that may have a significant impact on the environment; or
• Conflict with an applicable plan, policy or regulation adopted for the purpose of reduction the emissions of greenhouse gases.
The SJVAPCD’s Guidance for Valley Land-use Agencies in Addressing GHG Emission Impacts for New Projects under CEQA presents a tiered approach to analyzing project significance with respect to GHG emissions. Project GHG emissions are considered less than significant if they can meet any of the following conditions, evaluated in the order presented:
• Project is exempt from CEQA requirements;
• Project complies with an approved GHG emission reduction plan or GHG mitigation program;
• Project implements Best Performance Standards (BPS); or
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.2 • Project demonstrates that specific GHG emissions would be reduced or mitigated by at least 29 percent compared to Business-as-Usual (BAU), including GHG emission reductions achieved since the 2002-2004 baseline period.
On November 20, 2015, the California Supreme Court (Court) issued its decision on the Center for Biological Diversity v. California Department of Fish and Wildlife on the Newhall Ranch project case. The Court determined that there is not substantial evidence to link a specific project’s achievement of CARB’s Scoping Plan’s statewide average reduction below BAU to the conclusion that the project’s reduction would meet AB 32’s 2020 goals. Furthermore, since the release of SJVAPCD’s guidance, SB32 has been issued that requires the state to further reduce GHG emissions beyond the goals laid out in AB32. As a result, the 29 percent reduction in emissions as compared to a BAU standard are outdated and were not used for this analysis.
CEQA Guidelines15064.4 provides guidance for determining the significance of impacts from GHGs as follows:
(a) The determination of the significance of greenhouse gas emissions calls for a careful judgment by the lead agency consistent with the provisions in section 15064. A lead agency shall make a good-faith effort, based to the extent possible on scientific and factual data, to describe, calculate or estimate the amount of greenhouse gas emissions resulting from a project. A lead agency shall have discretion to determine, in the context of a particular project, whether to:
(1) Quantify greenhouse gas emissions resulting from a project; and/or (2) Rely on a qualitative analysis or performance-based standards. (b) In determining the significance of a project’s greenhouse gas emissions, the lead agency should focus its analysis on the reasonably foreseeable incremental contribution of the project’s emissions to the effects of climate change. A project’s incremental contribution may be cumulatively considerable even if it appears relatively small compared to statewide, national or global emissions. The agency’s analysis should consider a timeframe that is appropriate for the project. The agency’s analysis also must reasonably reflect evolving scientific knowledge and state regulatory schemes. A lead agency should consider the following factors, among others, when determining the significance of impacts from greenhouse gas emissions on the environment:
(1) The extent to which the project may increase or reduce greenhouse gas emissions as compared to the existing environmental setting;
(2) Whether the project emissions exceed a threshold of significance that the lead agency determines applies to the project.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.3 (3) The extent to which the project complies with regulations or requirements adopted to implement a statewide, regional, or local plan for the reduction or mitigation of greenhouse gas emissions (see, e.g., section 15183.5(b)). Such requirements must be adopted by the relevant public agency through a public review process and must reduce or mitigate the project’s incremental contribution of greenhouse gas emissions. If there is substantial evidence that the possible effects of a particular project are still cumulatively considerable notwithstanding compliance with the adopted regulations or requirements, an EIR must be prepared for the project. In determining the significance of impacts, the lead agency may consider a project’s consistency with the State’s longterm climate goals or strategies, provided that substantial evidence supports the agency’s analysis of how those goals or strategies address the project’s incremental contribution to climate change and its conclusion that the project’s incremental contribution is not cumulatively considerable.
(c) A lead agency may use a model or methodology to estimate greenhouse gas emissions resulting from a project. The lead agency has discretion to select the model or methodology it considers most appropriate to enable decision makers to intelligently take into account the project’s incremental contribution to climate change. The lead agency must support its selection of a model or methodology with substantial evidence.
The lead agency should explain the limitations of the particular model or methodology selected for use.
Project Threshold
The City of Porterville does not have a qualified Climate Action Plan currently. However, the Project will be required to comply with a series of state and regional GHG reduction plans, including CARB’s 2017 Scoping Plan and SJVAPCD’s Climate Change Action Plan (CCAP) Measures. These plans include approved GHG emission reduction plans and Project’s consistent with these plans would also comply with SB32. Therefore, as SJVAPCD does not have a quantifiable emissions threshold, project significance was determined based on compliance with applicable plans to reduce GHG emissions in accordance with CEQA Guidelines 15064.4(b)(3).
8.2 GHG IMPACT ANALYSIS
Impact GHG-1 Generate greenhouse gas emissions, either directly or indirectly, that may have a significant impact on the environment?
Impact Analysis
The following emissions estimate is consistent with CEQA Guidelines 15064.4.
CalEEMod was used to estimate the Project’s GHG emissions. Modeling assumptions are described in Section 6:Modeling Parameters and Assumptions.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.4 Constructions Emission Inventory
Construction GHGs would be emitted by the off-road construction equipment and vehicle travel by workers and material deliveries to the project site. The estimated construction GHG emissions are shown in Table 15. Because construction GHG emissions are temporary and reduction measures are limited, a common professional practice is to amortize the construction emissions over the life of the project. A residential project is conservatively assumed to have a life of 30 years.
Table 15: Construction Greenhouse Gas Emissions
Construction Year MTCO2e
2021 (Phase One) 173
2022 (Phase One) 473
2023 (Phase Two) 696
Total 1,342
Amortized over 20 years1 44.7
Notes:
1. GHG emissions are amortized over the 30-year life of the proposed project.
Source: Stantec 2021, CalEEMod 2020.4.0.
Operational Emission Inventory
Operational or long-term emissions occur over the life of the project. Sources of emissions may include motor vehicles and trucks, energy usage, water usage, waste generation, and area sources, such as landscaping activities and residential woodburning. Operational GHG emissions associated with the project were estimated using CalEEMod 2020.4.0.
Operational GHG emissions are shown in Table 16.
Table 16: Operational Greenhouse Gas Emissions
Source Emissions (MTCO2e per year)
Phase One
Area 57.4
Energy 344
Mobile 1,294
Waste 66.3
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.5 Source Emissions (MTCO2e per year)
Water 22.7
Subtotal 1,785
Phase Two
Area 47.1
Energy 283
Mobile 987
Waste 54.5
Water 21.2
Subtotal 1,392
Amortized Construction Emissions 44.7
Total 3,222
Source: Stantec 2021, CalEEMod 2020.4.0 (Appendix A).
The proposed project’s GHG impact is determined by its consistency with applicable statewide and regional GHG reduction plans. As shown in Impact GHG-2, the proposed project would be consistent with the CARB’s 2017 Scoping Plan, Tulare COG’s RTP/SCS, and the City’s General Plan goals that aim to reduce air quality and energy (which in turn reduce GHG emissions), as such the Project will comply with applicable reduction plans and GHG emissions are less than significant.
The proposed project would not generate GHG emissions, either directly or indirectly, that may have a significant impact on the environment; the impact is less than significant.
Level of Significance Before Mitigation
Less Than Significant Impact.
Mitigation Measures
No mitigation is necessary.
Level of Significance After Mitigation
Less Than Significant Impact.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.6 Impact GHG-2 Conflict with an applicable plan, policy or regulation adopted for the purpose of reducing the emissions of greenhouse gases? The proposed project would have a significant impact with respect to GHG emissions and global climate change if it would substantially conflict with the provisions of Section 15064.4(b) of the CEQA Guidelines.
Pursuant to Appendix G of the CEQA Guidelines, a significant GHG impact is identified if the project could conflict with applicable GHG reduction plans, policies, or regulations.
Development projects would be subject to complying with SB 32, Tulare COG’s RTP/SCS, and the City’s applicable goals. SB 32 is a statewide reduction goal aimed at reducing emissions to 40% below 1990 levels by 2030. CARB’s 2017 Scoping Plan sets a framework for the State to meet the reduction targets of SB 32.
Consistency with the Final 2017 Scoping Plan Update
CARB issued the Final 2017 Scoping Plan Update in November 2017 and establishes emissions reduction strategies necessary to meet SB 32’s 2030 reduction goals. Table 17, identifies the Scoping Plan policies that are applicable to the proposed project. As shown, the proposed project would be consistent with the Scoping Plan.
Table 17: Project Consistency with Applicable 2017 Scoping Plan Greenhouse Gas Reduction Strategies
Measure Name Measure Description Consistency Determination SB 350 50%
Renewable
Mandate.
Utilities subject to the legislation will be
required to increase their renewable energy
mix from 33% in 2020 to 50% in 2030.
Consistent. The proposed project will
purchase electricity from a utility subject to
the SB 350 Renewable Mandate. In
addition, the proposed project includes
renewable energy through roof top solar
systems.
Low Carbon Fuel
Standard
This measure requires fuel providers to
meet an 18 percent reduction in carbon
content by 2030.
Consistent. Vehicles accessing the
proposed project site will use fuel
containing lower carbon content as the fuel
standard is implemented.
Mobile Source
Strategy (Cleaner
Technology and
Fuels Scenario)
Vehicle manufacturers will be required to
meet existing regulations mandated by the
LEV III and Heavy-Duty Vehicle programs.
The strategy includes a goal of having 4.2
million ZEVs on the road by 2030 and
increasing numbers of ZEV trucks and
buses.
Consistent. Future residents can be
expected to purchase increasing numbers
of more fuel efficient and zero emission
cars and trucks each year. The 2019
CalGreen Code requires electrical service
in new single-family housing to be EV
charger-ready. Home deliveries will be
made by increasing numbers of ZEV
delivery trucks.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.7 Measure Name Measure Description Consistency Determination Short-Lived Climate
Pollutant (SLCP)
Reduction Strategy
The strategy requires the reduction of
SLCPs by 40 percent from 2013 levels by
2030 and the reduction of black carbon by
50 percent from 2013 levels by 2030.
Consistent. SJVAPCD limits wood burning
devices in new homes. Therefore, the
proposed project will not generate black
carbon.
SB 375 Sustainable
Communities
Strategies
Requires Regional Transportation Plans to
include a sustainable communities’ strategy
for reduction of per capita vehicle miles
traveled.
Consistent. The proposed project would
provide housing in the region that is
consistent with the growth projections in
the 2018 Regional Transportation
Plan/Sustainable Communities Strategy
(SCS). The project is not within an SCS
priority area and so is not subject to
requirements applicable to those areas.
Furthermore, the project site lies along
Porterville Transit Line 2., which has
stations along Westfield Avenue.
Post-2020 Cap-andTrade ProgramThe Post 2020 Cap-and-Trade Program continues the existing program for another
10 years. The Cap-and-Trade Program
applies to large industrial sources such as
power plants, refineries, and cement
manufacturers.
Consistent. The post-2020 Cap-and-Trade
Program indirectly affects people who use
the products and services produced by the
regulated industrial sources when
increased cost of products or services
(such as electricity and fuel) are transferred
to the consumers. The Cap-and-Trade
Program covers the GHG emissions
associated with electricity consumed in
California, whether generated in-state or
imported. Accordingly, GHG emissions
associated with CEQA projects’ electricity
usage are covered by the Cap- and-Trade
Program. The Cap-and-Trade Program
also covers fuel suppliers (natural gas and
propane fuel providers and transportation
fuel providers) to address emissions from
such fuels and from combustion of other
fossil fuels not directly covered at large
sources in the program’s first compliance
period.
Source of Measures: CARB, 2017
Source of Consistency Determination: Stantec Consulting Services Inc, 2021 Based on this evaluation, this analysis finds the project would be consistent with all feasible and applicable strategies recommended in the 2017 Scoping Plan Update.
Consistency with SJVAPCD CCAP
The SJVAPCD has adopted a CCAP, which includes suggested BPS for proposed residential development projects. Appendix J of the SJVAPCD Final Staff Report for the CCAP contains GHG reduction measures that would be applicable to the proposed project. The proposed project’s consistency with these measures is included in Table 18 below. As shown in the table, the project would be consistent with applicable CCAP measures.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.8 Table 18: Project Consistency with Applicable SJVAPCD CCAP GHG Reduction Measures
Measure
Name Measure Description Project Consistency
Bicycle/Pedestrian Transit Measures
5 –
Pedestrian
Network
The project provides a pedestrian access network that
internally links all uses and connects to existing external streets and pedestrian facilities. Existing facilities are defined as those facilities that are physically constructed and ready for use prior to the first 20 percent of the projects occupancy permits being granted.
Consistent. The proposed project would
provide pedestrian accommodations throughout
the project site and connecting offsite
to existing external streets and pedestrian
facilities.
6 –
Pedestrian
barriers
minimized
Site design and building placement minimize barriers to pedestrian access and interconnectivity. Physical barriers such as walls, berms, landscaping, and slopes between residential and
nonresidential uses that impede bicycle or pedestrian
circulation
are eliminated. Barriers to pedestrian access of neighboring facilities and sites are minimized. This measure is not meant to prevent the limited use of barriers to ensure public safety by prohibiting access to hazardous areas, etc.
Consistent. The proposed project would
provide pedestrian accommodations throughout
the project site and connecting offsite to
existing external streets and pedestrian
facilities.
Site Design Measures
18 -
Residential
Density
with No
Transit (3-
6 Du/acre)
Project provides high-density residential development. Density is calculated by determined the number of units per acre within the residential portion of the project's net lot area.
Consistent. The Project is seeking a zone
change on APN 245-010-087 from Very Low
Density Residential to Low Density Residential.
The site will provide 233 housing units over 56
acres of development, a density of 4.16
Du/acre.
Building Component Measures
26 - Onsite
renewable
energy
system
Project provides onsite renewable energy system(s). Consistent. The 2019 California Building Energy Efficiency Standards requires that all
new single-family homes and multi-family
buildings under three stories must conform to
the new solar code that requires the installation
of rooftop solar photovoltaic systems be
equipped on all new homes after January 1,
2020. Therefore, the Project will be required to
comply with these standards.
Additional GHG Emission Reduction Measures Requiring Additional Investigation 8 - Open
Space
Preserve and create open space and parks. Preserve existing trees, and plant replacement trees at a set ratio.
Consistent. The Project will develop a 3.5-acre
park in the center of the Project site and will
plant at least one tree at each lot.
11- Vehicle
Idling
Limit idling for commercial vehicles, including delivery and construction vehicles.
Consistent. CARB limits idling of diesel
vehicles to 5 minutes. The Project will comply
as applicable.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.9 Measure
Name Measure Description Project Consistency
16-Energy
Efficient
Appliances
Install energy efficient heating and cooling systems, appliances and equipment, and control systems.
Consistent. The Project will be designed to be
compliant with the 2019 California Building
Standards and the California Energy
Commission's regulations on home appliances.
17 -
Renewable
Energy
Use
Install Photovoltaic roofing tiles for solar power. Consistent. The 2019 California Building Energy Efficiency Standards requires that all
new single-family homes and multi-family
buildings under three stories must conform to
the new solar code that requires the installation
of rooftop solar photovoltaic systems be
equipped on all new homes after January 1,
2020. Therefore, the Project will be required to
comply with these standards.
20 - Tree
Plants
Protect existing trees and encourage the planting of new trees.
Adopt a tree protection and replacement ordinance, e.g., requiring that trees larger than a specified diameter that are removed to accommodate development must be replaced at a set ratio.
Consistent. The existing land uses on site are
primarily agricultural and, as a result, few trees
are currently on the project site. The Project will
develop a 3.5-acre park in the center of the
Project site and will plant at least one tree at
each lot.
Source: Stantec 2021. SJVAPCD, 2009.
Consistency with Tulare COG RTP/SCS
The TCAG’s2018 RTP/SCS includes a series of goals for the region that would reduce GHG emissions based on the land use consistency and the reduction of vehicle trips.
The proposed project’s consistency with these measures is included in Table 19 below.
As shown in the table, the project would be consistent with applicable TCAG measures.
Table 19: Project Consistency with Applicable Tulare COG Goals Goals Consistency
Provide an efficient, integrated, multi-modal
transportation system for the movement of people
and goods that enhance the physical, economic,
and social environment in the Tulare County
Region.
Not Applicable. This goal is aimed at transportation systems and local jurisdictions. The Project will not interfere with this goal and will place new residents near an existing bus station.
Encourage and support an efficient, maintained,
and safe circulation network that maximizes
circulations, longevity, and fiscal responsibility
while minimizing environmental impacts.
Consistent. The Project will construct a new roadway network that will connect the new development to the existing roadways.
The new roadways will further connect Porterville and maximize the roadway circulation.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.10 Goals Consistency
Provide a safe, secure, coordinated and efficient
public transit system that can reasonably meet the
needs of the residents.
Not Applicable. This goal is aimed at transportation systems and local jurisdictions. The Project will not interfere with this goal and will place new residents near an existing bus station.
Support development of a regional system of
airports that meets the air commerce and general
aviation needs of the county.
Not Applicable. This goal is aimed at local and regional jurisdictions. The Project will not interfere with this goal.
Promote safe, economical, convenient rail systems
and schedules that meet the needs of passenger
and freight services in the region.
Not Applicable. This goal is aimed at local and regional jurisdictions. The Project will not interfere with this goal.
Provide a transportation system that efficiently and
effectively transports goods to, from, within, and
through Tulare County.
Not Applicable. This goal is aimed at local and regional jurisdictions. The Project will not interfere with this goal.
Improve goods movement within the region to
increase economic vitality, meet the growing
needs of frieght and passenger services, and
improve traffic safety, air quality, and overall
mobility.
Not Applicable. This goal is aimed at local and regional jurisdictions. The Project will not interfere with this goal.
Improve, enhance, and expand the region's bicycle
and pedestrian systems and connectivity to those
systems, while keeping them safe and convenient.
Consistent. The Project will add new roads through an existing agricultural area. The subdivision will connect existing roads and place new residences near existing schools. The increase in roadways and residential areas will result in more pedestrian accessible areas and walkways.
Preserve and enhance regional transportation
roads and corridors.
Consistent. The Project will add new roadways and expand Porterville's existing roadway system.
Promote the improvement of air quality and
greenhouse gas reductions through congestion
management, coordination of land use, housing,
and transportation systems, provision of alternative
modes of transportation, and provision of
incentives that reduce vehicle miles traveled.
Consistent. The Project will construct a new subdivision near existing single-family homes and near multiple schools. In addition, the site is adjacent to Porterville Transportation bus line 2 that will promote alternative modes of transportation and reduce vehicle miles traveled.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.11 Goals Consistency
Promote public health opportunities for residents to
bicycle and walk to destinations such as home,
work, school, medical facilities, and commercial
and service systems.
Consistent. The Project will add new roads through an existing agricultural area. The subdivision will connect existing roads and place new residences near existing schools. The increase in roadways and residential areas will result in more pedestrian accessible areas and walkways.
Improve transportation mobility and operations by
improving and utilizing TSM strategies, TDM
measures, TCMs, and ITS programs.
Not Applicable. This goal is aimed at transportation systems and local jurisdictions. The Project will not interfere with this goal and will place new residents near an existing bus station.
Ensure that transportation investments do not
discriminate on the basis of race, color, national
origin, sex, age, or disability.
Not Applicable. This goal is aimed at transportation systems and local jurisdictions. The Project will not interfere with this goal.
Support the development and implementation of
emerging technologies in the surface
transportation system.
Not Applicable. This goal is aimed at transportation systems and local jurisdictions. The Project will not interfere with this goal.
Source: Stantec 2021. TCAG 2018.
Conclusion
The Project proposes to increase the density of allowable residential development on the lot and build residences near existing schools and an existing residential community. Development will place 4.15 homes/acre and allow pedestrian access and increased housing opportunities in the area. The site lies along Porterville Transit Line 2, which runs along Westfield Ave. As a result, the site will place residences in walking distance of transit and serve to further connect the areas pedestrian access while bringing students within walking distance of several schools. Finally, the Project will be required to adhere to Title 24 and the latest California Building Standards, which will require each single-family home to include photovoltaic cells. The proposed project would not conflict with the goals and objectives of the SJVAPCD’s CCAP, with CARB’s 2017 Scoping Plan, or any other State or regional plan, policy, or regulation of an agency adopted for the purpose of reducing GHG emissions. As such, the proposed project would not conflict with an applicable plan; therefore, impacts would be considered less than significant.
Level of Significance Before Mitigation
Less Than Significant Impact.
Mitigation Measures
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Greenhouse Gas Impact Analysis
8.12 No mitigation is necessary.
Level of Significance After Mitigation
Less Than Significant Impact.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Energy
9.1 9.0 ENERGY
9.1 CEQA GUIDELINES
The CEQA Guidelines define a significant effect on the environment as “a substantial, or potentially substantial, adverse change in the environment.” To determine if a project would have a significant impact on energy the following must be evaluated.
Would the project:
a) Result in potentially significant environmental impact due to wasteful, inefficient, or unnecessary consumption of energy resources, during project construction or operation?
b) Conflict with or obstruct a state or local plan for renewable energy or energy efficiency?
9.2 ENERGY IMPACT ANALYSIS
This section discusses potential energy impacts associated with the proposed project and provides mitigation measures where necessary.
Impact ENERGY-1 Result in potentially significant environmental impact due to wasteful, inefficient, or unnecessary
consumption of energy resources, during project
construction or operation?
Impact Analysis
The energy requirements for the proposed project were determined using the construction and operational estimates generated from the Methodology and Modeling Assumptions. The calculation worksheets for energy consumption are provided in Appendix C.
This impact addresses the energy consumption from both the short-term construction and long-term operations and are discussed separately below.
Short-Term Construction
Off-Road Equipment
Table 20 provides estimates of the project’s construction fuel consumption from off-road construction equipment.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Energy
9.2 Table 20: Construction Off-Road Fuel Consumption
Project Component Total Annual Fuel Consumption (gallons) Phase One Construction Off-Road Equipment 15,637
Phase Two Construction Off-Road Equipment 15,631
Total 31,268
Source: Appendix C.
As shown in Table 19, construction activities associated with the proposed project would be estimated to consume 31,268 gallons of diesel fuel. There are no unusual project characteristics that would necessitate the use of construction equipment that would be less energy-efficient than at comparable construction sites in other parts of the state.
On-Road Vehicles
On-road vehicles for construction workers, vendors, and haulers would require fuel for travel to and from the site during construction. Table 21 provides an estimate of the total on-road vehicle fuel usage during construction. There are no unusual project characteristics that would necessitate the use of construction equipment that would be less energy-efficient than at comparable construction sites in other parts of the state.
Therefore, it is expected that construction fuel consumption associated with the proposed project would not be any more inefficient, wasteful, or unnecessary than at other construction sites in the region.
Table 21: Construction On-Road Fuel Consumption
Project
Component
Average Fuel
Economy
(miles/gallon) Total VMT
Total Fuel Consumption
(gallons)
Phase One
Worker Trips 26.95 437,558 17,570
Vendor Trips 9.34 115,340 12,348
Haul Trips 6.54 0 0
Phase Two
Worker Trips 26.95 569,408 21,126
Vendor Trips 9.34 140,160 15,006
Haul Trips 6.54 0 0
Total Construction On-Road
Trips 1,262,466 66,050
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Energy
9.3 Project
Component
Average Fuel
Economy
(miles/gallon) Total VMT
Total Fuel Consumption
(gallons)
Notes:
Calculations use unrounded numbers; totals may not appear to sum exactly due to rounding.
VMT = vehicle miles traveled
Source: Appendix C
Other Construction Energy Consumption
Other equipment could include construction lighting, field services (office trailers), and electrically driven equipment such as pumps and other tools. As on-site construction activities would be restricted to permissible construction hours, it is anticipated that the use of construction lighting would be minimal. Singlewide mobile office trailers, which are commonly used in construction staging areas, generally range in size from 160 square feet to 720 square feet. Table 22 shows the energy consumption estimated for a typical 720-square-foot trailer during construction over Phase One and Phase Two.
There is a gap between the end of Phase One and the start of Phase Two, it was conservatively assumed that the trailer would remain occupied and using energy during that time.
Table 22: Construction Trailer
Project Component Kilowatt hours per year (kWh/yr)
Construction 15,644
Source: Appendix C
There are no unusual project characteristics that would necessitate the use of construction vehicles or equipment that would be less energy efficient than at comparable construction sites in other parts of the state. Therefore, it is expected that construction energy consumption associated with the proposed project would not be any more inefficient, wasteful, or unnecessary than at other construction sites in the region.
Long-term Operations
Transportation Energy Demand
Table 23 provides an estimate of the daily and annual fuel consumed by vehicles traveling to and from the project site. These estimates were derived using the same assumptions used in the operational air quality analysis for the proposed project. For details relating assumptions used in the calculations, please refer to Appendix C.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Energy
9.4 Table 22: Long-Term Operational Vehicle Fuel Consumption Vehicle
Type
Percent
of
Vehicle
Trips
Daily VMT Annual
VMT
Average Fuel
Economy
(miles/gallon)1
Total Daily
Fuel
Consumption
(gallons)
Total Annual
Fuel
Consumption
(gallons)
Passenger
Cars (LDA) 51.0% 8,722 3,183,626 33.45 260.8 95,178
Light Trucks
and Medium
Duty
Vehicles
(LDT1,
LDT2, MDV)
39.3% 6,725 2,454,614 24.24 277.5 101,270
Light-Heavy
to HeavyHeavy Diesel
Trucks
(LHD1,
LHD2,
MHDT,
HHDT)
6.7% 1,151 420,234 8.66 119.7 43,704
Motorcycles
(MCY) 2.4% 403 147,037 37.84 10.6 3,885
Other
(OBUS,
UBUS,
SBUS, MH)
0.6% 104 38,117 6.89 14.6 5,332
Total 100% 17,106 6,243,629 — 683.2 249,369
Notes:
VMT = vehicle miles traveled
Percent of Vehicle Trips and VMT provided by CalEEMod.
“Other” consists of buses and motor homes.
Source: Appendix C
As shown in Table 25, annual vehicular fuel consumption is estimated to be 249,369 gallons of a combination of gasoline and diesel fuel.
Building Energy Demand
As shown in Appendix C the proposed project is estimated to demand 1,849,780 kilowatt hours of electricity and 3,048,506 kilo-British Thermal Units of natural gas, respectively, on an annual basis.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Energy
9.5 It would be expected that building energy consumption associated with the proposed project would not be any more inefficient, wasteful, or unnecessary than for any other similar buildings in the region. Current state regulatory requirements for new building construction contained in the 2019 CALGreen and Title 24 standards would increase energy efficiency and reduce energy demand in comparison to existing commercial structures, and therefore would reduce actual environmental effects associated with energy use from the proposed project. Additionally, the CALGreen and Title 24 standards have increased efficiency standards through each update. Further, the most recent CALGreen standards require single-family housing constructed after January 1, 2020 to include rooftop photovoltaic cells. The reductions from the energy generation was not accounted for in order to provide a conservative analysis.
Therefore, while the proposed project would result in increased electricity and natural gas demand, the electricity and natural gas would be consumed more efficiently and would be typical of residential development. Compliance with future building code standards would result in increased energy efficiency.
For the above reasons, energy impacts would be less than significant.
Level of Significance Before Mitigation
Less Than Significant Impact.
Mitigation Measures
None.
Level of Significance After Mitigation
Less Than Significant Impact.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT Energy
9.6 Impact ENERGY-2 Conflict with or obstruct a state or local plan for renewable energy or energy efficiency?
The proposed project would comply with federal, State, and local regulations aimed at reducing energy consumption. Local regulations have been developed in accordance with federal and State energy regulations, such as the California Energy Code Building Energy Efficiency Standards (CCR Title 24, Part 6), the CALGreen Code (CCR Title 24, Part 11), and SB 743, which are also aimed at reducing energy consumption.
The proposed project would not conflict with or obstruct a state or local plan for renewable energy or energy efficiency. The impact would be less than significant.
Level of Significance Before Mitigation
Less Than Significant Impact.
Mitigation Measures
None.
Level of Significance After Mitigation
Less Than Significant Impact.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT References
10.1 10.0 REFERENCES
Agency for Toxic Substances and Disease Registry. 2021. Lead. Website:
https://wwwn.cdc.gov/TSP/substances/ToxSubstance.aspx?toxid=22. Accessed June 22, 2021.
California Air Pollution Control Officers Association (CAPCOA). 2009. Health Risk Assessments for Proposed Land Use Projects. Website:
http://www.capcoa.org/wpcontent/uploads/2012/03/CAPCOA_HRA_LU_Guidelines_8-6-09.pdf. Accessed February 11, 2021.
California Air Resources Board (CARB). 2001. Staff Report: Ozone Transport: 2001 Review. Website: https://ww3.arb.ca.gov/research/apr/reports/l3067.pdf.
Accessed: February 10, 2021.
———. 2005. Air Quality and Land Use Handbook: A Community Health Perspective.
April 2005. Website: https://www.arb.ca.gov/ch/handbook.pdf. Accessed:
February 11, 2021.
———. 2013. California Almanac of Emissions & Air Quality. Website:
https://www.arb.ca.gov/aqd/almanac/almanac13/almanac2013all.pdf. Accessed:
February 10, 2021.
———. 2016a. Health Effects of Air Pollution. Website:
https://www.arb.ca.gov/research/health/health.htm. Accessed: February 10, 2021.
———. 2016b. Overview: Diesel Exhaust and Health. Website:
https://www.arb.ca.gov/research/diesel/diesel-health.htm. Accessed: July 22, 2021.
———. 2016c. Ambient Air Quality Standards. Website:
https://www.arb.ca.gov/research/aaqs/aaqs2.pdf. Accessed: February 10, 2021. ———. 2017b. California’s 2017 Climate Change Scoping Plan. Website:
https://www.arb.ca.gov/cc/scopingplan/scoping_plan_2017.pdf. Accessed February July 19, 2021.
———. 2018a. iADAM: Air Quality Data Statistics. Website:
https://www.arb.ca.gov/adam. Accessed July 16, 2021.
———. 2018b.California Greenhouse Gas Emission Inventory – 2018 Edition. Website:
https://www.arb.ca.gov/cc/inventory/data/data.htm. Accessed February 10, 2021.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT References
10.2 Centers for Disease Control and Prevention (CDC). 2020. Valley Fever (Coccidioidomycosis). Website:
https://www.cdc.gov/fungal/diseases/coccidioidomycosis/index.html. Accessed July 20, 2021.
City of Porterville. Planning Division – Porterville 2030 General Plan. Website:
www.ci.porterville.ca.us/depts/CommunityDevelopment/generalplan.cfm.
Accessed July 19, 2021.
SJVAPCD. 2015. Guidance for Assessing and Mitigating Air Quality Impacts. Website:
http://www.valleyair.org/transportation/GAMAQI_3-19-15.pdf. Accessed: July 19, 2021.
———.2015b. Amicus Curiae brief filed on Case S219783 in the Supreme Court of California, Sierra Club et. al. v. County of Fresno and Friant Ranch, L.P. April 13, 2015. Accessed July 20, 2021.
———. 2019. Ambient Air Quality Standards and Valley Attainment Status. Website:
https://www.valleyair.org/aqinfo/attainment.htm. Accessed July 19, 2021.
SCAQMD, 2015. Amicus Curiae Brief filed on Case S219783 in the Supreme Court of California, Sierra Club et. al. v County of Fresno and Friant Ranch, L.P. April 13, 2015. Accessed July 20, 2021.
SoCal Gas. 2021. Aspire 2045 Sustainability and Climate Commitment to Net Zero.
Website: https://www.socalgas.com/sites/default/files/2021- 03/SoCalGas_Climate_Commitment.pdf. Accessed July 19, 2021.
Tulare Council of Governments. 2018. Regional Transportation Plan Sustainable Communities Plan, Policy Element. Website:
https://tularecog.org/tcag/planning/rtp/rtp-20181/policy-element/. Accessed: July 23, 2021.
U.S. Environmental Protection Agency. 2019a. Criteria Air Pollutants. Website:
https://www.epa.gov/criteria-air-pollutants. Accessed: July 22, 2021. ———. 2019b. Greenhouse Gas Emissions. Website:
https://www.epa.gov/ghgemissions/overview-greenhouse-gases. Accessed: July 21, 2021.
———. 2021a. Health and Environmental Effects of Particulate Matter. Website:
https://www.epa.gov/pm-pollution/health-and-environmental-effects-particulatematter-pm. Accessed: July 22, 2021.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT References
10.3 ———. 2021b. Particulate Matter (PM) Basics. Website: https://www.epa.gov/pmpollution/particulate-matter-pm-basicsEPA. 2021b. Particulate Matter (PM) Basics. https://www.epa.gov/pm-pollution/particulate-matter-pm-basics.
Accessed July 19, 2021.
———2021c. Health Effects of Ozone Pollution. Website: https://www.epa.gov/groundlevel-ozone-pollution/health-effects-ozone-pollution, accessed July 20, 2021.
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT
APPENDIX A
CRITERIA AIR POLLUTANT AND GHG EMISSIONS RESULTS
Lombardi Development - Phase 1
Tulare County, Annual
Project Characteristics -
Land Use - Acreage adjusted to account for the project site.
Construction Phase - Construction will take place over one year (October 2021 to October 2022) Grading - Grading balanced on-site.
Sequestration - At least one tree will be planted at each lot.
Construction Off-road Equipment Mitigation - SJVAPCD Rule 8021.
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Other Asphalt Surfaces 9.08 Acre 9.08 395,524.80 0
Single Family Housing 128.00 Dwelling Unit 19.34 230,400.00 366
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
7 Wind Speed (m/s) 2.2 Precipitation Freq (Days) 51
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Southern California Edison
Operational Year 2022
CO2 Intensity
(lb/MWhr)
390.98 CH4 Intensity 0.033
(lb/MWhr)
N2O Intensity 0.004
(lb/MWhr)
Table Name Column Name Default Value New Value
tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 CalEEMod Version: CalEEMod.2020.4.0 Page 1 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 3.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 4.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 9.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstructionPhase NumDays 35.00 14.00
tblConstructionPhase NumDays 440.00 200.00
tblConstructionPhase NumDays 45.00 25.00
tblConstructionPhase NumDays 35.00 12.00
tblConstructionPhase NumDays 20.00 10.00
CalEEMod Version: CalEEMod.2020.4.0 Page 2 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
2.0 Emissions Summary
tblLandUse LotAcreage 41.56 19.34
tblSequestration NumberOfNewTrees 0.00 128.00
CalEEMod Version: CalEEMod.2020.4.0 Page 3 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
2.1 Overall Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year tons/yr MT/yr
2021 0.1210 1.1476 0.8933 1.9100e0030.2503 0.0516 0.3019 0.1062 0.0478 0.1540 0.0000 170.6025 170.6025 0.0373 4.7200e003172.9432 2022 2.4940 1.8204 2.1400 5.1400e0030.1899 0.0774 0.2673 0.0515 0.0728 0.1243 0.0000 464.6741 464.6741 0.0563 0.0244 473.3555 Maximum 2.4940 1.8204 2.1400 5.1400e0030.2503 0.0774 0.3019 0.1062 0.0728 0.1540 0.0000 464.6741 464.6741 0.0563 0.0244 473.3555 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 0.0441 0.5658 0.9955 1.9100e0030.2503 4.5600e0030.2549 0.1062 4.4800e0030.1107 0.0000 170.6023 170.6023 0.0373 4.7200e003172.9430 2022 2.3892 1.4140 2.2841 5.1400e0030.1899 0.0124 0.2023 0.0515 0.0122 0.0637 0.0000 464.6739 464.6739 0.0563 0.0244 473.3552 Maximum 2.3892 1.4140 2.2841 5.1400e0030.2503 0.0124 0.2549 0.1062 0.0122 0.1107 0.0000 464.6739 464.6739 0.0563 0.0244 473.3552 Mitigated Construction
CalEEMod Version: CalEEMod.2020.4.0 Page 4 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
6.95 33.30 -8.12 0.00 0.00 86.82 19.67 0.00 86.18 37.34 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 10-1-2021 12-31-2021 1.2679 0.6103
2 1-1-2022 3-31-2022 0.7549 0.5660
3 4-1-2022 6-30-2022 0.7547 0.5637
4 7-1-2022 9-30-2022 2.6305 2.4979
Highest 2.6305 2.4979
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Area 1.1842 0.0589 0.9719 3.6000e0049.1300e0039.1300e0039.1300e0039.1300e0030.0000 57.0032 57.0032 2.5600e0031.0200e00357.3702 Energy 0.0164 0.1402 0.0596 8.9000e0040.0113 0.0113 0.0113 0.0113 0.0000 342.5309 342.5309 0.0183 4.8200e003344.4252 Mobile 0.6939 1.2339 6.4478 0.0137 1.2573 0.0143 1.2717 0.3367 0.0135 0.3502 0.0000 1,270.933 0 1,270.933
0 0.0742 0.0713 1,294.030
8 Waste 0.0000 0.0000 0.0000 0.0000 26.7461 0.0000 26.7461 1.5807 0.0000 66.2623 Water 0.0000 0.0000 0.0000 0.0000 2.6458 11.2664 13.9122 0.2727 6.5300e00322.6762 Total 1.8946 1.4329 7.4793 0.0149 1.2573 0.0348 1.2921 0.3367 0.0340 0.3706 29.3919 1,681.733 5 1,711.125
4 1.9484 0.0837 1,784.764
6 Unmitigated Operational
CalEEMod Version: CalEEMod.2020.4.0 Page 5 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Area 1.1842 0.0589 0.9719 3.6000e0049.1300e0039.1300e0039.1300e0039.1300e0030.0000 57.0032 57.0032 2.5600e0031.0200e00357.3702 Energy 0.0164 0.1402 0.0596 8.9000e0040.0113 0.0113 0.0113 0.0113 0.0000 342.5309 342.5309 0.0183 4.8200e003344.4252 Mobile 0.6939 1.2339 6.4478 0.0137 1.2573 0.0143 1.2717 0.3367 0.0135 0.3502 0.0000 1,270.933 0 1,270.933
0 0.0742 0.0713 1,294.030
8 Waste 0.0000 0.0000 0.0000 0.0000 26.7461 0.0000 26.7461 1.5807 0.0000 66.2623 Water 0.0000 0.0000 0.0000 0.0000 2.6458 11.2664 13.9122 0.2727 6.5300e00322.6762 Total 1.8946 1.4329 7.4793 0.0149 1.2573 0.0348 1.2921 0.3367 0.0340 0.3706 29.3919 1,681.733 5 1,711.125
4 1.9484 0.0837 1,784.764
6 Mitigated 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 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2020.4.0 Page 6 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.0 Construction Detail
2.3 Vegetation
CO2e
Category MT
New Trees 90.6240
Total 90.6240
Vegetation
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Site Preparation Site Preparation 10/1/2021 10/14/2021 5 10 2 Grading Grading 10/15/2021 11/18/2021 5 25
3 Building Construction Building Construction 11/19/2021 8/25/2022 5 200 4 Paving Paving 8/26/2022 9/12/2022 5 12
5 Architectural Coating Architectural Coating 9/13/2022 9/30/2022 5 14 Residential Indoor: 466,560; Residential Outdoor: 155,520; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area:
23,731 (Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 15
Acres of Grading (Grading Phase): 75
Acres of Paving: 9.08
CalEEMod Version: CalEEMod.2020.4.0 Page 7 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.1 Mitigation Measures Construction
OffRoad Equipment
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 Coating 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 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Grading 8 20.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Building Construction 9 212.00 79.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Paving 6 15.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 42.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2020.4.0 Page 8 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 0.0983 0.0000 0.0983 0.0505 0.0000 0.0505 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0194 0.2025 0.1058 1.9000e0040.0102 0.0102 9.4000e0039.4000e0030.0000 16.7179 16.7179 5.4100e0030.0000 16.8530 Total 0.0194 0.2025 0.1058 1.9000e0040.0983 0.0102 0.1085 0.0505 9.4000e0030.0599 0.0000 16.7179 16.7179 5.4100e0030.0000 16.8530 Unmitigated Construction On-Site
Use Cleaner Engines for Construction Equipment
Reduce Vehicle Speed on Unpaved Roads
CalEEMod Version: CalEEMod.2020.4.0 Page 9 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 3.8000e0042.9000e0043.0000e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.6087 0.6087 2.0000e0052.0000e0050.6160 Total 3.8000e0042.9000e0043.0000e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.6087 0.6087 2.0000e0052.0000e0050.6160 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 0.0983 0.0000 0.0983 0.0505 0.0000 0.0505 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 3.4800e0030.0608 0.1148 1.9000e0043.1000e0043.1000e0043.1000e0043.1000e0040.0000 16.7178 16.7178 5.4100e0030.0000 16.8530 Total 3.4800e0030.0608 0.1148 1.9000e0040.0983 3.1000e0040.0986 0.0505 3.1000e0040.0508 0.0000 16.7178 16.7178 5.4100e0030.0000 16.8530 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 10 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 3.8000e0042.9000e0043.0000e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.6087 0.6087 2.0000e0052.0000e0050.6160 Total 3.8000e0042.9000e0043.0000e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.6087 0.6087 2.0000e0052.0000e0050.6160 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 0.1150 0.0000 0.1150 0.0457 0.0000 0.0457 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0524 0.5800 0.3860 7.8000e0040.0248 0.0248 0.0228 0.0228 0.0000 68.1187 68.1187 0.0220 0.0000 68.6695 Total 0.0524 0.5800 0.3860 7.8000e0040.1150 0.0248 0.1399 0.0457 0.0228 0.0685 0.0000 68.1187 68.1187 0.0220 0.0000 68.6695 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 11 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 1.0500e0038.1000e0048.3300e0032.0000e0051.9900e0031.0000e0052.0000e0035.3000e0041.0000e0055.4000e0040.0000 1.6909 1.6909 7.0000e0056.0000e0051.7110 Total 1.0500e0038.1000e0048.3300e0032.0000e0051.9900e0031.0000e0052.0000e0035.3000e0041.0000e0055.4000e0040.0000 1.6909 1.6909 7.0000e0056.0000e0051.7110 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 0.1150 0.0000 0.1150 0.0457 0.0000 0.0457 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0126 0.2409 0.4590 7.8000e0041.2700e0031.2700e0031.2700e0031.2700e0030.0000 68.1187 68.1187 0.0220 0.0000 68.6694 Total 0.0126 0.2409 0.4590 7.8000e0040.1150 1.2700e0030.1163 0.0457 1.2700e0030.0469 0.0000 68.1187 68.1187 0.0220 0.0000 68.6694 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 12 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 1.0500e0038.1000e0048.3300e0032.0000e0051.9900e0031.0000e0052.0000e0035.3000e0041.0000e0055.4000e0040.0000 1.6909 1.6909 7.0000e0056.0000e0051.7110 Total 1.0500e0038.1000e0048.3300e0032.0000e0051.9900e0031.0000e0052.0000e0035.3000e0041.0000e0055.4000e0040.0000 1.6909 1.6909 7.0000e0056.0000e0051.7110 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 0.0295 0.2702 0.2569 4.2000e0040.0149 0.0149 0.0140 0.0140 0.0000 35.9038 35.9038 8.6600e0030.0000 36.1203 Total 0.0295 0.2702 0.2569 4.2000e0040.0149 0.0149 0.0140 0.0140 0.0000 35.9038 35.9038 8.6600e0030.0000 36.1203 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 13 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 4.4800e0030.0832 0.0237 2.6000e0048.0900e0031.5000e0039.5900e0032.3400e0031.4300e0033.7700e0030.0000 25.3371 25.3371 2.5000e0043.8300e00326.4840 Worker 0.0138 0.0106 0.1095 2.4000e0040.0262 1.6000e0040.0263 6.9600e0031.4000e0047.1000e0030.0000 22.2254 22.2254 9.0000e0048.1000e00422.4894 Total 0.0183 0.0939 0.1333 5.0000e0040.0343 1.6600e0030.0359 9.3000e0031.5700e0030.0109 0.0000 47.5625 47.5625 1.1500e0034.6400e00348.9734 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 8.2700e0030.1691 0.2770 4.2000e0041.3100e0031.3100e0031.3100e0031.3100e0030.0000 35.9037 35.9037 8.6600e0030.0000 36.1203 Total 8.2700e0030.1691 0.2770 4.2000e0041.3100e0031.3100e0031.3100e0031.3100e0030.0000 35.9037 35.9037 8.6600e0030.0000 36.1203 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 14 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 4.4800e0030.0832 0.0237 2.6000e0048.0900e0031.5000e0039.5900e0032.3400e0031.4300e0033.7700e0030.0000 25.3371 25.3371 2.5000e0043.8300e00326.4840 Worker 0.0138 0.0106 0.1095 2.4000e0040.0262 1.6000e0040.0263 6.9600e0031.4000e0047.1000e0030.0000 22.2254 22.2254 9.0000e0048.1000e00422.4894 Total 0.0183 0.0939 0.1333 5.0000e0040.0343 1.6600e0030.0359 9.3000e0031.5700e0030.0109 0.0000 47.5625 47.5625 1.1500e0034.6400e00348.9734 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 0.1442 1.3195 1.3827 2.2800e0030.0684 0.0684 0.0643 0.0643 0.0000 195.8078 195.8078 0.0469 0.0000 196.9806 Total 0.1442 1.3195 1.3827 2.2800e0030.0684 0.0684 0.0643 0.0643 0.0000 195.8078 195.8078 0.0469 0.0000 196.9806 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 15 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 0.0149 0.3728 0.1065 1.4000e0030.0441 4.2300e0030.0484 0.0128 4.0500e0030.0168 0.0000 134.6687 134.6687 9.2000e0040.0203 140.7427 Worker 0.0685 0.0504 0.5391 1.2800e0030.1427 7.9000e0040.1435 0.0379 7.3000e0040.0387 0.0000 117.8672 117.8672 4.3600e0034.0200e003119.1737 Total 0.0834 0.4232 0.6456 2.6800e0030.1868 5.0200e0030.1919 0.0507 4.7800e0030.0555 0.0000 252.5359 252.5359 5.2800e0030.0243 259.9164 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 0.0451 0.9221 1.5103 2.2800e0037.1500e0037.1500e0037.1500e0037.1500e0030.0000 195.8076 195.8076 0.0469 0.0000 196.9804 Total 0.0451 0.9221 1.5103 2.2800e0037.1500e0037.1500e0037.1500e0037.1500e0030.0000 195.8076 195.8076 0.0469 0.0000 196.9804 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 16 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 0.0149 0.3728 0.1065 1.4000e0030.0441 4.2300e0030.0484 0.0128 4.0500e0030.0168 0.0000 134.6687 134.6687 9.2000e0040.0203 140.7427 Worker 0.0685 0.0504 0.5391 1.2800e0030.1427 7.9000e0040.1435 0.0379 7.3000e0040.0387 0.0000 117.8672 117.8672 4.3600e0034.0200e003119.1737 Total 0.0834 0.4232 0.6456 2.6800e0030.1868 5.0200e0030.1919 0.0507 4.7800e0030.0555 0.0000 252.5359 252.5359 5.2800e0030.0243 259.9164 Mitigated Construction Off-Site
3.5 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 6.6200e0030.0668 0.0875 1.4000e0043.4100e0033.4100e0033.1300e0033.1300e0030.0000 12.0165 12.0165 3.8900e0030.0000 12.1137 Paving 0.0119 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0185 0.0668 0.0875 1.4000e0043.4100e0033.4100e0033.1300e0033.1300e0030.0000 12.0165 12.0165 3.8900e0030.0000 12.1137 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 17 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.5 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 3.4000e0042.5000e0042.7100e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5922 0.5922 2.0000e0052.0000e0050.5987 Total 3.4000e0042.5000e0042.7100e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5922 0.5922 2.0000e0052.0000e0050.5987 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 2.0000e0030.0602 0.1038 1.4000e0042.2000e0042.2000e0042.2000e0042.2000e0040.0000 12.0165 12.0165 3.8900e0030.0000 12.1137 Paving 0.0119 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0139 0.0602 0.1038 1.4000e0042.2000e0042.2000e0042.2000e0042.2000e0040.0000 12.0165 12.0165 3.8900e0030.0000 12.1137 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 18 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.5 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 3.4000e0042.5000e0042.7100e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5922 0.5922 2.0000e0052.0000e0050.5987 Total 3.4000e0042.5000e0042.7100e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5922 0.5922 2.0000e0052.0000e0050.5987 Mitigated Construction Off-Site
3.6 Architectural Coating - 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 2.2450 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 1.4300e0039.8600e0030.0127 2.0000e0055.7000e0045.7000e0045.7000e0045.7000e0040.0000 1.7873 1.7873 1.2000e0040.0000 1.7902 Total 2.2464 9.8600e0030.0127 2.0000e0055.7000e0045.7000e0045.7000e0045.7000e0040.0000 1.7873 1.7873 1.2000e0040.0000 1.7902 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 19 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.6 Architectural Coating - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 1.1200e0038.3000e0048.8500e0032.0000e0052.3400e0031.0000e0052.3500e0036.2000e0041.0000e0056.3000e0040.0000 1.9344 1.9344 7.0000e0057.0000e0051.9559 Total 1.1200e0038.3000e0048.8500e0032.0000e0052.3400e0031.0000e0052.3500e0036.2000e0041.0000e0056.3000e0040.0000 1.9344 1.9344 7.0000e0057.0000e0051.9559 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 2.2450 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 3.8000e0047.4200e0030.0128 2.0000e0053.0000e0053.0000e0053.0000e0053.0000e0050.0000 1.7873 1.7873 1.2000e0040.0000 1.7902 Total 2.2454 7.4200e0030.0128 2.0000e0053.0000e0053.0000e0053.0000e0053.0000e0050.0000 1.7873 1.7873 1.2000e0040.0000 1.7902 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 20 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.6 Architectural Coating - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 1.1200e0038.3000e0048.8500e0032.0000e0052.3400e0031.0000e0052.3500e0036.2000e0041.0000e0056.3000e0040.0000 1.9344 1.9344 7.0000e0057.0000e0051.9559 Total 1.1200e0038.3000e0048.8500e0032.0000e0052.3400e0031.0000e0052.3500e0036.2000e0041.0000e0056.3000e0040.0000 1.9344 1.9344 7.0000e0057.0000e0051.9559 Mitigated Construction Off-Site
4.0 Operational Detail - Mobile
4.1 Mitigation Measures Mobile
CalEEMod Version: CalEEMod.2020.4.0 Page 21 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 0.6939 1.2339 6.4478 0.0137 1.2573 0.0143 1.2717 0.3367 0.0135 0.3502 0.0000 1,270.933 0 1,270.933
0 0.0742 0.0713 1,294.030
8 Unmitigated 0.6939 1.2339 6.4478 0.0137 1.2573 0.0143 1.2717 0.3367 0.0135 0.3502 0.0000 1,270.933 0 1,270.933
0 0.0742 0.0713 1,294.030
8 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
Single Family Housing 1,208.32 1,221.12 1094.40 3,365,214 3,365,214 Total 1,208.32 1,221.12 1,094.40 3,365,214 3,365,214
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 9.50 7.30 7.30 0.00 0.00 0.00 0 0 0 Single Family Housing 10.80 7.30 7.50 38.40 22.60 39.00 86 11 3
4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH Other Asphalt Surfaces 0.491968 0.051162 0.166648 0.188672 0.034593 0.008513 0.012315 0.015417 0.000659 0.000471 0.024128 0.001541 0.003914 Single Family Housing 0.491968 0.051162 0.166648 0.188672 0.034593 0.008513 0.012315 0.015417 0.000659 0.000471 0.024128 0.001541 0.003914
5.0 Energy Detail
CalEEMod Version: CalEEMod.2020.4.0 Page 22 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Electricity
Mitigated
0.0000 0.0000 0.0000 0.0000 0.0000 180.2160 180.2160 0.0152 1.8400e003181.1457 Electricity
Unmitigated
0.0000 0.0000 0.0000 0.0000 0.0000 180.2160 180.2160 0.0152 1.8400e003181.1457 NaturalGas
Mitigated
0.0164 0.1402 0.0596 8.9000e0040.0113 0.0113 0.0113 0.0113 0.0000 162.3149 162.3149 3.1100e0032.9800e003163.2795 NaturalGas
Unmitigated
0.0164 0.1402 0.0596 8.9000e0040.0113 0.0113 0.0113 0.0113 0.0000 162.3149 162.3149 3.1100e0032.9800e003163.2795
5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2020.4.0 Page 23 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr tons/yr MT/yr
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 Single Family
Housing
3.04167e
+006
0.0164 0.1402 0.0596 8.9000e0040.0113 0.0113 0.0113 0.0113 0.0000 162.3149 162.3149 3.1100e0032.9800e003163.2795 Total 0.0164 0.1402 0.0596 8.9000e0040.0113 0.0113 0.0113 0.0113 0.0000 162.3149 162.3149 3.1100e0032.9800e003163.2795 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 Single Family
Housing
3.04167e
+006
0.0164 0.1402 0.0596 8.9000e0040.0113 0.0113 0.0113 0.0113 0.0000 162.3149 162.3149 3.1100e0032.9800e003163.2795 Total 0.0164 0.1402 0.0596 8.9000e0040.0113 0.0113 0.0113 0.0113 0.0000 162.3149 162.3149 3.1100e0032.9800e003163.2795 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 24 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
6.0 Area Detail
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
Single Family
Housing
1.01619e
+006
180.2160 0.0152 1.8400e003181.1457
Total 180.2160 0.0152 1.8400e003181.1457
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
Single Family
Housing
1.01619e
+006
180.2160 0.0152 1.8400e003181.1457
Total 180.2160 0.0152 1.8400e003181.1457
Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 25 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
6.1 Mitigation Measures Area
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 1.1842 0.0589 0.9719 3.6000e0049.1300e0039.1300e0039.1300e0039.1300e0030.0000 57.0032 57.0032 2.5600e0031.0200e00357.3702 Unmitigated 1.1842 0.0589 0.9719 3.6000e0049.1300e0039.1300e0039.1300e0039.1300e0030.0000 57.0032 57.0032 2.5600e0031.0200e00357.3702 CalEEMod Version: CalEEMod.2020.4.0 Page 26 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory tons/yr MT/yr
Architectural
Coating
0.2245 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Consumer
Products
0.9254 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Hearth 5.6000e0030.0479 0.0204 3.1000e0043.8700e0033.8700e0033.8700e0033.8700e0030.0000 55.4506 55.4506 1.0600e0031.0200e00355.7801 Landscaping 0.0288 0.0110 0.9515 5.0000e0055.2600e0035.2600e0035.2600e0035.2600e0030.0000 1.5527 1.5527 1.5000e0030.0000 1.5901 Total 1.1842 0.0589 0.9719 3.6000e0049.1300e0039.1300e0039.1300e0039.1300e0030.0000 57.0032 57.0032 2.5600e0031.0200e00357.3702 Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 27 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
7.1 Mitigation Measures Water
7.0 Water Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory tons/yr MT/yr
Architectural
Coating
0.2245 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Consumer
Products
0.9254 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Hearth 5.6000e0030.0479 0.0204 3.1000e0043.8700e0033.8700e0033.8700e0033.8700e0030.0000 55.4506 55.4506 1.0600e0031.0200e00355.7801 Landscaping 0.0288 0.0110 0.9515 5.0000e0055.2600e0035.2600e0035.2600e0035.2600e0030.0000 1.5527 1.5527 1.5000e0030.0000 1.5901 Total 1.1842 0.0589 0.9719 3.6000e0049.1300e0039.1300e0039.1300e0039.1300e0030.0000 57.0032 57.0032 2.5600e0031.0200e00357.3702 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 28 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied Total CO2 CH4 N2O CO2e
Category MT/yr
Mitigated 13.9122 0.2727 6.5300e00322.6762
Unmitigated 13.9122 0.2727 6.5300e00322.6762
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
Single Family
Housing
8.33972 /
5.25765
13.9122 0.2727 6.5300e00322.6762
Total 13.9122 0.2727 6.5300e00322.6762
Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 29 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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
Single Family
Housing
8.33972 /
5.25765
13.9122 0.2727 6.5300e00322.6762
Total 13.9122 0.2727 6.5300e00322.6762
Mitigated
8.1 Mitigation Measures Waste
8.0 Waste Detail
Total CO2 CH4 N2O CO2e
MT/yr
Mitigated 26.7461 1.5807 0.0000 66.2623
Unmitigated 26.7461 1.5807 0.0000 66.2623
Category/Year
CalEEMod Version: CalEEMod.2020.4.0 Page 30 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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
Single Family
Housing
131.76 26.7461 1.5807 0.0000 66.2623
Total 26.7461 1.5807 0.0000 66.2623
Unmitigated
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
Other Asphalt
Surfaces
0 0.0000 0.0000 0.0000 0.0000
Single Family
Housing
131.76 26.7461 1.5807 0.0000 66.2623
Total 26.7461 1.5807 0.0000 66.2623
Mitigated
9.0 Operational Offroad
CalEEMod Version: CalEEMod.2020.4.0 Page 31 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
11.0 Vegetation
Total CO2 CH4 N2O CO2e
Category MT
Unmitigated 90.6240 0.0000 0.0000 90.6240
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type
10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2020.4.0 Page 32 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
11.2 Net New Trees
Number of
Trees
Total CO2 CH4 N2O CO2e
MT
Miscellaneous 128 90.6240 0.0000 0.0000 90.6240
Total 90.6240 0.0000 0.0000 90.6240
Species Class
CalEEMod Version: CalEEMod.2020.4.0 Page 33 of 33 Date: 7/21/2021 12:50 PM Lombardi Development - Phase 1 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied Lombardi Development - Phase 1
Tulare County, Summer
Project Characteristics -
Land Use - Acreage adjusted to account for the project site.
Construction Phase - Construction will take place over one year (October 2021 to October 2022) Grading - Grading balanced on-site.
Sequestration - At least one tree will be planted at each lot.
Construction Off-road Equipment Mitigation - SJVAPCD Rule 8021.
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Other Asphalt Surfaces 9.08 Acre 9.08 395,524.80 0
Single Family Housing 128.00 Dwelling Unit 19.34 230,400.00 366
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
7 Wind Speed (m/s) 2.2 Precipitation Freq (Days) 51
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Southern California Edison
Operational Year 2022
CO2 Intensity
(lb/MWhr)
390.98 CH4 Intensity 0.033
(lb/MWhr)
N2O Intensity 0.004
(lb/MWhr)
Table Name Column Name Default Value New Value
tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 CalEEMod Version: CalEEMod.2020.4.0 Page 1 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 3.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 4.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 9.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstructionPhase NumDays 35.00 14.00
tblConstructionPhase NumDays 440.00 200.00
tblConstructionPhase NumDays 45.00 25.00
tblConstructionPhase NumDays 35.00 12.00
tblConstructionPhase NumDays 20.00 10.00
CalEEMod Version: CalEEMod.2020.4.0 Page 2 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
2.0 Emissions Summary
tblLandUse LotAcreage 41.56 19.34
tblSequestration NumberOfNewTrees 0.00 128.00
CalEEMod Version: CalEEMod.2020.4.0 Page 3 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
2.1 Overall Construction (Maximum Daily Emission)
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2021 4.2894 46.4601 31.6597 0.0636 19.8049 2.0453 21.8502 10.1417 1.8817 12.0234 0.0000 6,169.441 9 6,169.441
9 1.9487 0.3271 6,219.707
4 2022 321.1067 20.3893 25.0590 0.0600 2.2771 0.8684 3.1455 0.6162 0.8176 1.4338 0.0000 5,984.572 0 5,984.572
0 0.7179 0.3148 6,095.354
8 Maximum 321.1067 46.4601 31.6597 0.0636 19.8049 2.0453 21.8502 10.1417 1.8817 12.0234 0.0000 6,169.441 9 6,169.441
9 1.9487 0.3271 6,219.707
4 Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2021 1.8660 19.3310 37.5038 0.0636 19.8049 0.1912 19.8678 10.1417 0.1862 10.2045 0.0000 6,169.441 9 6,169.441
9 1.9487 0.3271 6,219.707
4 2022 320.9567 15.6858 26.5694 0.0600 2.2771 0.1440 2.4211 0.6162 0.1411 0.7572 0.0000 5,984.572 0 5,984.572
0 0.7179 0.3148 6,095.354
8 Maximum 320.9567 19.3310 37.5038 0.0636 19.8049 0.1912 19.8678 10.1417 0.1862 10.2045 0.0000 6,169.441 9 6,169.441
9 1.9487 0.3271 6,219.707
4 Mitigated Construction
CalEEMod Version: CalEEMod.2020.4.0 Page 4 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.79 47.62 -12.97 0.00 0.00 88.50 10.83 0.00 87.87 18.54 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2020.4.0 Page 5 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 Energy 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Mobile 4.7205 6.5188 39.5462 0.0820 7.2845 0.0806 7.3651 1.9456 0.0759 2.0215 8,389.539 7 8,389.539
7 0.4401 0.4291 8,528.401
0 Total 11.5672 8.5765 50.9424 0.0949 7.2845 0.2955 7.5800 1.9456 0.2908 2.2364 0.0000 10,879.77 20 10,879.77
20 0.5059 0.4744 11,033.77
73 Unmitigated Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 Energy 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Mobile 4.7205 6.5188 39.5462 0.0820 7.2845 0.0806 7.3651 1.9456 0.0759 2.0215 8,389.539 7 8,389.539
7 0.4401 0.4291 8,528.401
0 Total 11.5672 8.5765 50.9424 0.0949 7.2845 0.2955 7.5800 1.9456 0.2908 2.2364 0.0000 10,879.77 20 10,879.77
20 0.5059 0.4744 11,033.77
73 Mitigated Operational
CalEEMod Version: CalEEMod.2020.4.0 Page 6 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Site Preparation Site Preparation 10/1/2021 10/14/2021 5 10 2 Grading Grading 10/15/2021 11/18/2021 5 25
3 Building Construction Building Construction 11/19/2021 8/25/2022 5 200 4 Paving Paving 8/26/2022 9/12/2022 5 12
5 Architectural Coating Architectural Coating 9/13/2022 9/30/2022 5 14 OffRoad Equipment
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
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Residential Indoor: 466,560; Residential Outdoor: 155,520; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area:
23,731 (Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 15
Acres of Grading (Grading Phase): 75
Acres of Paving: 9.08
CalEEMod Version: CalEEMod.2020.4.0 Page 7 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.1 Mitigation Measures Construction
Use Cleaner Engines for Construction Equipment
Reduce Vehicle Speed on Unpaved Roads
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 Coating 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 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Grading 8 20.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Building Construction 9 212.00 79.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Paving 6 15.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 42.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2020.4.0 Page 8 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Fugitive Dust 19.6570 0.0000 19.6570 10.1025 0.0000 10.1025 0.0000 0.0000 Off-Road 3.8882 40.4971 21.1543 0.0380 2.0445 2.0445 1.8809 1.8809 3,685.656 9 3,685.656
9 1.1920 3,715.457
3 Total 3.8882 40.4971 21.1543 0.0380 19.6570 2.0445 21.7015 10.1025 1.8809 11.9834 3,685.656 9 3,685.656
9 1.1920 3,715.457
3 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0884 0.0543 0.7031 1.4400e0030.1479 8.5000e0040.1487 0.0392 7.9000e0040.0400 146.1586 146.1586 5.2900e0034.6800e003147.6846 Total 0.0884 0.0543 0.7031 1.4400e0030.1479 8.5000e0040.1487 0.0392 7.9000e0040.0400 146.1586 146.1586 5.2900e0034.6800e003147.6846 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 9 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Fugitive Dust 19.6570 0.0000 19.6570 10.1025 0.0000 10.1025 0.0000 0.0000 Off-Road 0.6967 12.1620 22.9600 0.0380 0.0621 0.0621 0.0621 0.0621 0.0000 3,685.656 9 3,685.656
9 1.1920 3,715.457
3 Total 0.6967 12.1620 22.9600 0.0380 19.6570 0.0621 19.7191 10.1025 0.0621 10.1645 0.0000 3,685.656 9 3,685.656
9 1.1920 3,715.457
3 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0884 0.0543 0.7031 1.4400e0030.1479 8.5000e0040.1487 0.0392 7.9000e0040.0400 146.1586 146.1586 5.2900e0034.6800e003147.6846 Total 0.0884 0.0543 0.7031 1.4400e0030.1479 8.5000e0040.1487 0.0392 7.9000e0040.0400 146.1586 146.1586 5.2900e0034.6800e003147.6846 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 10 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Fugitive Dust 9.2036 0.0000 9.2036 3.6538 0.0000 3.6538 0.0000 0.0000 Off-Road 4.1912 46.3998 30.8785 0.0620 1.9853 1.9853 1.8265 1.8265 6,007.043 4 6,007.043
4 1.9428 6,055.613
4 Total 4.1912 46.3998 30.8785 0.0620 9.2036 1.9853 11.1889 3.6538 1.8265 5.4803 6,007.043 4 6,007.043
4 1.9428 6,055.613
4 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0982 0.0603 0.7812 1.6000e0030.1643 9.5000e0040.1652 0.0436 8.7000e0040.0445 162.3984 162.3984 5.8800e0035.2000e003164.0940 Total 0.0982 0.0603 0.7812 1.6000e0030.1643 9.5000e0040.1652 0.0436 8.7000e0040.0445 162.3984 162.3984 5.8800e0035.2000e003164.0940 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 11 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Fugitive Dust 9.2036 0.0000 9.2036 3.6538 0.0000 3.6538 0.0000 0.0000 Off-Road 1.0110 19.2707 36.7226 0.0620 0.1015 0.1015 0.1015 0.1015 0.0000 6,007.043 4 6,007.043
4 1.9428 6,055.613
4 Total 1.0110 19.2707 36.7226 0.0620 9.2036 0.1015 9.3051 3.6538 0.1015 3.7553 0.0000 6,007.043 4 6,007.043
4 1.9428 6,055.613
4 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0982 0.0603 0.7812 1.6000e0030.1643 9.5000e0040.1652 0.0436 8.7000e0040.0445 162.3984 162.3984 5.8800e0035.2000e003164.0940 Total 0.0982 0.0603 0.7812 1.6000e0030.1643 9.5000e0040.1652 0.0436 8.7000e0040.0445 162.3984 162.3984 5.8800e0035.2000e003164.0940 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 12 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Off-Road 1.9009 17.4321 16.5752 0.0269 0.9586 0.9586 0.9013 0.9013 2,553.363 9 2,553.363
9 0.6160 2,568.764
3 Total 1.9009 17.4321 16.5752 0.0269 0.9586 0.9586 0.9013 0.9013 2,553.363 9 2,553.363
9 0.6160 2,568.764
3 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.2917 5.1293 1.5103 0.0170 0.5356 0.0966 0.6321 0.1542 0.0924 0.2466 1,801.537 2 1,801.537
2 0.0176 0.2720 1,883.037
9 Worker 1.0409 0.6393 8.2807 0.0170 1.7415 0.0101 1.7516 0.4619 9.2600e0030.4712 1,721.423 4 1,721.423
4 0.0623 0.0551 1,739.396
5 Total 1.3325 5.7687 9.7910 0.0340 2.2771 0.1066 2.3837 0.6162 0.1016 0.7178 3,522.960 6 3,522.960
6 0.0798 0.3271 3,622.434
4 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 13 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Off-Road 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,553.363 9 2,553.363
9 0.6160 2,568.764
3 Total 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,553.363 9 2,553.363
9 0.6160 2,568.764
3 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.2917 5.1293 1.5103 0.0170 0.5356 0.0966 0.6321 0.1542 0.0924 0.2466 1,801.537 2 1,801.537
2 0.0176 0.2720 1,883.037
9 Worker 1.0409 0.6393 8.2807 0.0170 1.7415 0.0101 1.7516 0.4619 9.2600e0030.4712 1,721.423 4 1,721.423
4 0.0623 0.0551 1,739.396
5 Total 1.3325 5.7687 9.7910 0.0340 2.2771 0.1066 2.3837 0.6162 0.1016 0.7178 3,522.960 6 3,522.960
6 0.0798 0.3271 3,622.434
4 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 14 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Off-Road 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Total 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.1788 4.2171 1.2417 0.0166 0.5356 0.0500 0.5856 0.1542 0.0478 0.2021 1,756.147 5 1,756.147
5 0.0121 0.2647 1,835.317
3 Worker 0.9480 0.5566 7.4540 0.0165 1.7415 9.3900e0031.7509 0.4619 8.6500e0030.4706 1,674.090 9 1,674.090
9 0.0553 0.0501 1,690.405
3 Total 1.1268 4.7736 8.6956 0.0331 2.2771 0.0594 2.3365 0.6162 0.0565 0.6726 3,430.238 4 3,430.238
4 0.0674 0.3148 3,525.722
6 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 15 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Off-Road 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Total 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.1788 4.2171 1.2417 0.0166 0.5356 0.0500 0.5856 0.1542 0.0478 0.2021 1,756.147 5 1,756.147
5 0.0121 0.2647 1,835.317
3 Worker 0.9480 0.5566 7.4540 0.0165 1.7415 9.3900e0031.7509 0.4619 8.6500e0030.4706 1,674.090 9 1,674.090
9 0.0553 0.0501 1,690.405
3 Total 1.1268 4.7736 8.6956 0.0331 2.2771 0.0594 2.3365 0.6162 0.0565 0.6726 3,430.238 4 3,430.238
4 0.0674 0.3148 3,525.722
6 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 16 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.5 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 lb/day lb/day
Off-Road 1.1028 11.1249 14.5805 0.0228 0.5679 0.5679 0.5225 0.5225 2,207.660 3 2,207.660
3 0.7140 2,225.510
4 Paving 1.9825 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 3.0853 11.1249 14.5805 0.0228 0.5679 0.5679 0.5225 0.5225 2,207.660 3 2,207.660
3 0.7140 2,225.510
4 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0671 0.0394 0.5274 1.1600e0030.1232 6.6000e0040.1239 0.0327 6.1000e0040.0333 118.4498 118.4498 3.9100e0033.5500e003119.6042 Total 0.0671 0.0394 0.5274 1.1600e0030.1232 6.6000e0040.1239 0.0327 6.1000e0040.0333 118.4498 118.4498 3.9100e0033.5500e003119.6042 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 17 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.5 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 lb/day lb/day
Off-Road 0.3341 10.0395 17.2957 0.0228 0.0374 0.0374 0.0374 0.0374 0.0000 2,207.660 3 2,207.660
3 0.7140 2,225.510
4 Paving 1.9825 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 2.3166 10.0395 17.2957 0.0228 0.0374 0.0374 0.0374 0.0374 0.0000 2,207.660 3 2,207.660
3 0.7140 2,225.510
4 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0671 0.0394 0.5274 1.1600e0030.1232 6.6000e0040.1239 0.0327 6.1000e0040.0333 118.4498 118.4498 3.9100e0033.5500e003119.6042 Total 0.0671 0.0394 0.5274 1.1600e0030.1232 6.6000e0040.1239 0.0327 6.1000e0040.0333 118.4498 118.4498 3.9100e0033.5500e003119.6042 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 18 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.6 Architectural Coating - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 320.7144 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.2045 1.4085 1.8136 2.9700e0030.0817 0.0817 0.0817 0.0817 281.4481 281.4481 0.0183 281.9062 Total 320.9189 1.4085 1.8136 2.9700e0030.0817 0.0817 0.0817 0.0817 281.4481 281.4481 0.0183 281.9062 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.1878 0.1103 1.4767 3.2600e0030.3450 1.8600e0030.3469 0.0915 1.7100e0030.0932 331.6595 331.6595 0.0110 9.9300e003334.8916 Total 0.1878 0.1103 1.4767 3.2600e0030.3450 1.8600e0030.3469 0.0915 1.7100e0030.0932 331.6595 331.6595 0.0110 9.9300e003334.8916 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 19 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.6 Architectural Coating - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 320.7144 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0545 1.0598 1.8324 2.9700e0033.9600e0033.9600e0033.9600e0033.9600e0030.0000 281.4481 281.4481 0.0183 281.9062 Total 320.7688 1.0598 1.8324 2.9700e0033.9600e0033.9600e0033.9600e0033.9600e0030.0000 281.4481 281.4481 0.0183 281.9062 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.1878 0.1103 1.4767 3.2600e0030.3450 1.8600e0030.3469 0.0915 1.7100e0030.0932 331.6595 331.6595 0.0110 9.9300e003334.8916 Total 0.1878 0.1103 1.4767 3.2600e0030.3450 1.8600e0030.3469 0.0915 1.7100e0030.0932 331.6595 331.6595 0.0110 9.9300e003334.8916 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 20 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
4.0 Operational Detail - Mobile
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 4.7205 6.5188 39.5462 0.0820 7.2845 0.0806 7.3651 1.9456 0.0759 2.0215 8,389.539 7 8,389.539
7 0.4401 0.4291 8,528.401
0 Unmitigated 4.7205 6.5188 39.5462 0.0820 7.2845 0.0806 7.3651 1.9456 0.0759 2.0215 8,389.539 7 8,389.539
7 0.4401 0.4291 8,528.401
0 4.1 Mitigation Measures Mobile
4.2 Trip Summary Information
4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Other Asphalt Surfaces 0.00 0.00 0.00
Single Family Housing 1,208.32 1,221.12 1094.40 3,365,214 3,365,214 Total 1,208.32 1,221.12 1,094.40 3,365,214 3,365,214
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 9.50 7.30 7.30 0.00 0.00 0.00 0 0 0 Single Family Housing 10.80 7.30 7.50 38.40 22.60 39.00 86 11 3
4.4 Fleet Mix
CalEEMod Version: CalEEMod.2020.4.0 Page 21 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH Other Asphalt Surfaces 0.491968 0.051162 0.166648 0.188672 0.034593 0.008513 0.012315 0.015417 0.000659 0.000471 0.024128 0.001541 0.003914 Single Family Housing 0.491968 0.051162 0.166648 0.188672 0.034593 0.008513 0.012315 0.015417 0.000659 0.000471 0.024128 0.001541 0.003914
5.0 Energy Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
NaturalGas
Mitigated
0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 NaturalGas
Unmitigated
0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181
5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2020.4.0 Page 22 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
6.0 Area Detail
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
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 Single Family
Housing
8333.33 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Total 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Unmitigated
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
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 Single Family
Housing
8.33333 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Total 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 23 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
6.1 Mitigation Measures Area
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 Unmitigated 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 CalEEMod Version: CalEEMod.2020.4.0 Page 24 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
1.2301 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
5.0707 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.1367 1.1678 0.4969 7.4500e0030.0944 0.0944 0.0944 0.0944 0.0000 1,490.823 5 1,490.823
5 0.0286 0.0273 1,499.682
8 Landscaping 0.3194 0.1219 10.5725 5.6000e0040.0584 0.0584 0.0584 0.0584 19.0167 19.0167 0.0184 19.4754 Total 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 25 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
7.1 Mitigation Measures Water
7.0 Water Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
1.2301 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
5.0707 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.1367 1.1678 0.4969 7.4500e0030.0944 0.0944 0.0944 0.0944 0.0000 1,490.823 5 1,490.823
5 0.0286 0.0273 1,499.682
8 Landscaping 0.3194 0.1219 10.5725 5.6000e0040.0584 0.0584 0.0584 0.0584 19.0167 19.0167 0.0184 19.4754 Total 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 26 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
11.0 Vegetation
8.1 Mitigation Measures Waste
8.0 Waste Detail
9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type
10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2020.4.0 Page 27 of 27 Date: 7/21/2021 12:55 PM Lombardi Development - Phase 1 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied Lombardi Development - Phase 1
Tulare County, Winter
Project Characteristics -
Land Use - Acreage adjusted to account for the project site.
Construction Phase - Construction will take place over one year (October 2021 to October 2022) Grading - Grading balanced on-site.
Sequestration - At least one tree will be planted at each lot.
Construction Off-road Equipment Mitigation - SJVAPCD Rule 8021.
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Other Asphalt Surfaces 9.08 Acre 9.08 395,524.80 0
Single Family Housing 128.00 Dwelling Unit 19.34 230,400.00 366
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
7 Wind Speed (m/s) 2.2 Precipitation Freq (Days) 51
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Southern California Edison
Operational Year 2022
CO2 Intensity
(lb/MWhr)
390.98 CH4 Intensity 0.033
(lb/MWhr)
N2O Intensity 0.004
(lb/MWhr)
Table Name Column Name Default Value New Value
tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 CalEEMod Version: CalEEMod.2020.4.0 Page 1 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 3.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 4.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 9.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstructionPhase NumDays 35.00 14.00
tblConstructionPhase NumDays 440.00 200.00
tblConstructionPhase NumDays 45.00 25.00
tblConstructionPhase NumDays 35.00 12.00
tblConstructionPhase NumDays 20.00 10.00
CalEEMod Version: CalEEMod.2020.4.0 Page 2 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
2.0 Emissions Summary
tblLandUse LotAcreage 41.56 19.34
tblSequestration NumberOfNewTrees 0.00 128.00
CalEEMod Version: CalEEMod.2020.4.0 Page 3 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
2.1 Overall Construction (Maximum Daily Emission)
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2021 4.2767 46.4706 31.5268 0.0634 19.8049 2.0453 21.8502 10.1417 1.8817 12.0234 0.0000 6,150.778 3 6,150.778
3 1.9492 0.3337 6,201.231
5 2022 321.0829 20.7762 23.8680 0.0581 2.2771 0.8686 3.1457 0.6162 0.8178 1.4339 0.0000 5,794.272 1 5,794.272
1 0.7183 0.3208 5,906.992
7 Maximum 321.0829 46.4706 31.5268 0.0634 19.8049 2.0453 21.8502 10.1417 1.8817 12.0234 0.0000 6,150.778 3 6,150.778
3 1.9492 0.3337 6,201.231
5 Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2021 1.7280 19.3415 37.3709 0.0634 19.8049 0.1914 19.8678 10.1417 0.1864 10.2045 0.0000 6,150.778 2 6,150.778
2 1.9492 0.3337 6,201.231
5 2022 320.9328 16.0728 25.3784 0.0581 2.2771 0.1441 2.4213 0.6162 0.1412 0.7574 0.0000 5,794.272 1 5,794.272
1 0.7183 0.3208 5,906.992
7 Maximum 320.9328 19.3415 37.3709 0.0634 19.8049 0.1914 19.8678 10.1417 0.1864 10.2045 0.0000 6,150.778 2 6,150.778
2 1.9492 0.3337 6,201.231
5 Mitigated Construction
CalEEMod Version: CalEEMod.2020.4.0 Page 4 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.83 47.34 -13.28 0.00 0.00 88.48 10.83 0.00 87.86 18.54 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2020.4.0 Page 5 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 Energy 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Mobile 3.6919 7.2988 37.1618 0.0750 7.2845 0.0807 7.3652 1.9456 0.0760 2.0215 7,679.774 8 7,679.774
8 0.4907 0.4582 7,828.579
4 Total 10.5386 9.3565 48.5580 0.0879 7.2845 0.2956 7.5801 1.9456 0.2909 2.2364 0.0000 10,170.00 71 10,170.00
71 0.5564 0.5035 10,333.95
57 Unmitigated Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 Energy 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Mobile 3.6919 7.2988 37.1618 0.0750 7.2845 0.0807 7.3652 1.9456 0.0760 2.0215 7,679.774 8 7,679.774
8 0.4907 0.4582 7,828.579
4 Total 10.5386 9.3565 48.5580 0.0879 7.2845 0.2956 7.5801 1.9456 0.2909 2.2364 0.0000 10,170.00 71 10,170.00
71 0.5564 0.5035 10,333.95
57 Mitigated Operational
CalEEMod Version: CalEEMod.2020.4.0 Page 6 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Site Preparation Site Preparation 10/1/2021 10/14/2021 5 10 2 Grading Grading 10/15/2021 11/18/2021 5 25
3 Building Construction Building Construction 11/19/2021 8/25/2022 5 200 4 Paving Paving 8/26/2022 9/12/2022 5 12
5 Architectural Coating Architectural Coating 9/13/2022 9/30/2022 5 14 OffRoad Equipment
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
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Residential Indoor: 466,560; Residential Outdoor: 155,520; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area:
23,731 (Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 15
Acres of Grading (Grading Phase): 75
Acres of Paving: 9.08
CalEEMod Version: CalEEMod.2020.4.0 Page 7 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.1 Mitigation Measures Construction
Use Cleaner Engines for Construction Equipment
Reduce Vehicle Speed on Unpaved Roads
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 Coating 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 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Grading 8 20.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Building Construction 9 212.00 79.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Paving 6 15.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 42.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2020.4.0 Page 8 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Fugitive Dust 19.6570 0.0000 19.6570 10.1025 0.0000 10.1025 0.0000 0.0000 Off-Road 3.8882 40.4971 21.1543 0.0380 2.0445 2.0445 1.8809 1.8809 3,685.656 9 3,685.656
9 1.1920 3,715.457
3 Total 3.8882 40.4971 21.1543 0.0380 19.6570 2.0445 21.7015 10.1025 1.8809 11.9834 3,685.656 9 3,685.656
9 1.1920 3,715.457
3 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0770 0.0637 0.5835 1.2800e0030.1479 8.5000e0040.1487 0.0392 7.9000e0040.0400 129.3613 129.3613 5.7600e0035.2000e003131.0563 Total 0.0770 0.0637 0.5835 1.2800e0030.1479 8.5000e0040.1487 0.0392 7.9000e0040.0400 129.3613 129.3613 5.7600e0035.2000e003131.0563 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 9 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Fugitive Dust 19.6570 0.0000 19.6570 10.1025 0.0000 10.1025 0.0000 0.0000 Off-Road 0.6967 12.1620 22.9600 0.0380 0.0621 0.0621 0.0621 0.0621 0.0000 3,685.656 9 3,685.656
9 1.1920 3,715.457
3 Total 0.6967 12.1620 22.9600 0.0380 19.6570 0.0621 19.7191 10.1025 0.0621 10.1645 0.0000 3,685.656 9 3,685.656
9 1.1920 3,715.457
3 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0770 0.0637 0.5835 1.2800e0030.1479 8.5000e0040.1487 0.0392 7.9000e0040.0400 129.3613 129.3613 5.7600e0035.2000e003131.0563 Total 0.0770 0.0637 0.5835 1.2800e0030.1479 8.5000e0040.1487 0.0392 7.9000e0040.0400 129.3613 129.3613 5.7600e0035.2000e003131.0563 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 10 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Fugitive Dust 9.2036 0.0000 9.2036 3.6538 0.0000 3.6538 0.0000 0.0000 Off-Road 4.1912 46.3998 30.8785 0.0620 1.9853 1.9853 1.8265 1.8265 6,007.043 4 6,007.043
4 1.9428 6,055.613
4 Total 4.1912 46.3998 30.8785 0.0620 9.2036 1.9853 11.1889 3.6538 1.8265 5.4803 6,007.043 4 6,007.043
4 1.9428 6,055.613
4 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0856 0.0708 0.6483 1.4200e0030.1643 9.5000e0040.1652 0.0436 8.7000e0040.0445 143.7348 143.7348 6.4000e0035.7800e003145.6181 Total 0.0856 0.0708 0.6483 1.4200e0030.1643 9.5000e0040.1652 0.0436 8.7000e0040.0445 143.7348 143.7348 6.4000e0035.7800e003145.6181 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 11 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Fugitive Dust 9.2036 0.0000 9.2036 3.6538 0.0000 3.6538 0.0000 0.0000 Off-Road 1.0110 19.2707 36.7226 0.0620 0.1015 0.1015 0.1015 0.1015 0.0000 6,007.043 4 6,007.043
4 1.9428 6,055.613
4 Total 1.0110 19.2707 36.7226 0.0620 9.2036 0.1015 9.3051 3.6538 0.1015 3.7553 0.0000 6,007.043 4 6,007.043
4 1.9428 6,055.613
4 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0856 0.0708 0.6483 1.4200e0030.1643 9.5000e0040.1652 0.0436 8.7000e0040.0445 143.7348 143.7348 6.4000e0035.7800e003145.6181 Total 0.0856 0.0708 0.6483 1.4200e0030.1643 9.5000e0040.1652 0.0436 8.7000e0040.0445 143.7348 143.7348 6.4000e0035.7800e003145.6181 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 12 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Off-Road 1.9009 17.4321 16.5752 0.0269 0.9586 0.9586 0.9013 0.9013 2,553.363 9 2,553.363
9 0.6160 2,568.764
3 Total 1.9009 17.4321 16.5752 0.0269 0.9586 0.9586 0.9013 0.9013 2,553.363 9 2,553.363
9 0.6160 2,568.764
3 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.2876 5.4803 1.5560 0.0170 0.5356 0.0968 0.6323 0.1542 0.0926 0.2468 1,802.401 5 1,802.401
5 0.0173 0.2724 1,884.015
2 Worker 0.9069 0.7503 6.8719 0.0150 1.7415 0.0101 1.7516 0.4619 9.2600e0030.4712 1,523.589 0 1,523.589
0 0.0678 0.0613 1,543.551
6 Total 1.1945 6.2305 8.4280 0.0321 2.2771 0.1068 2.3839 0.6162 0.1018 0.7180 3,325.990 5 3,325.990
5 0.0852 0.3337 3,427.566
8 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 13 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Off-Road 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,553.363 9 2,553.363
9 0.6160 2,568.764
3 Total 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,553.363 9 2,553.363
9 0.6160 2,568.764
3 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.2876 5.4803 1.5560 0.0170 0.5356 0.0968 0.6323 0.1542 0.0926 0.2468 1,802.401 5 1,802.401
5 0.0173 0.2724 1,884.015
2 Worker 0.9069 0.7503 6.8719 0.0150 1.7415 0.0101 1.7516 0.4619 9.2600e0030.4712 1,523.589 0 1,523.589
0 0.0678 0.0613 1,543.551
6 Total 1.1945 6.2305 8.4280 0.0321 2.2771 0.1068 2.3839 0.6162 0.1018 0.7180 3,325.990 5 3,325.990
5 0.0852 0.3337 3,427.566
8 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 14 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Off-Road 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Total 1.7062 15.6156 16.3634 0.0269 0.8090 0.8090 0.7612 0.7612 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.1743 4.5078 1.2853 0.0166 0.5356 0.0502 0.5857 0.1542 0.0480 0.2022 1,757.630 7 1,757.630
7 0.0119 0.2651 1,836.932
8 Worker 0.8277 0.6528 6.2193 0.0146 1.7415 9.3900e0031.7509 0.4619 8.6500e0030.4706 1,482.307 8 1,482.307
8 0.0606 0.0557 1,500.427
7 Total 1.0019 5.1606 7.5046 0.0312 2.2771 0.0595 2.3367 0.6162 0.0566 0.6728 3,239.938 5 3,239.938
5 0.0725 0.3208 3,337.360
5 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 15 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
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 lb/day lb/day
Off-Road 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Total 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,554.333 6 2,554.333
6 0.6120 2,569.632
2 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.1743 4.5078 1.2853 0.0166 0.5356 0.0502 0.5857 0.1542 0.0480 0.2022 1,757.630 7 1,757.630
7 0.0119 0.2651 1,836.932
8 Worker 0.8277 0.6528 6.2193 0.0146 1.7415 9.3900e0031.7509 0.4619 8.6500e0030.4706 1,482.307 8 1,482.307
8 0.0606 0.0557 1,500.427
7 Total 1.0019 5.1606 7.5046 0.0312 2.2771 0.0595 2.3367 0.6162 0.0566 0.6728 3,239.938 5 3,239.938
5 0.0725 0.3208 3,337.360
5 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 16 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.5 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 lb/day lb/day
Off-Road 1.1028 11.1249 14.5805 0.0228 0.5679 0.5679 0.5225 0.5225 2,207.660 3 2,207.660
3 0.7140 2,225.510
4 Paving 1.9825 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 3.0853 11.1249 14.5805 0.0228 0.5679 0.5679 0.5225 0.5225 2,207.660 3 2,207.660
3 0.7140 2,225.510
4 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0586 0.0462 0.4400 1.0300e0030.1232 6.6000e0040.1239 0.0327 6.1000e0040.0333 104.8803 104.8803 4.2900e0033.9400e003106.1623 Total 0.0586 0.0462 0.4400 1.0300e0030.1232 6.6000e0040.1239 0.0327 6.1000e0040.0333 104.8803 104.8803 4.2900e0033.9400e003106.1623 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 17 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.5 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 lb/day lb/day
Off-Road 0.3341 10.0395 17.2957 0.0228 0.0374 0.0374 0.0374 0.0374 0.0000 2,207.660 3 2,207.660
3 0.7140 2,225.510
4 Paving 1.9825 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 2.3166 10.0395 17.2957 0.0228 0.0374 0.0374 0.0374 0.0374 0.0000 2,207.660 3 2,207.660
3 0.7140 2,225.510
4 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0586 0.0462 0.4400 1.0300e0030.1232 6.6000e0040.1239 0.0327 6.1000e0040.0333 104.8803 104.8803 4.2900e0033.9400e003106.1623 Total 0.0586 0.0462 0.4400 1.0300e0030.1232 6.6000e0040.1239 0.0327 6.1000e0040.0333 104.8803 104.8803 4.2900e0033.9400e003106.1623 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 18 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.6 Architectural Coating - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 320.7144 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.2045 1.4085 1.8136 2.9700e0030.0817 0.0817 0.0817 0.0817 281.4481 281.4481 0.0183 281.9062 Total 320.9189 1.4085 1.8136 2.9700e0030.0817 0.0817 0.0817 0.0817 281.4481 281.4481 0.0183 281.9062 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.1640 0.1293 1.2321 2.8900e0030.3450 1.8600e0030.3469 0.0915 1.7100e0030.0932 293.6648 293.6648 0.0120 0.0110 297.2546 Total 0.1640 0.1293 1.2321 2.8900e0030.3450 1.8600e0030.3469 0.0915 1.7100e0030.0932 293.6648 293.6648 0.0120 0.0110 297.2546 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 19 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
3.6 Architectural Coating - 2022
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 320.7144 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0545 1.0598 1.8324 2.9700e0033.9600e0033.9600e0033.9600e0033.9600e0030.0000 281.4481 281.4481 0.0183 281.9062 Total 320.7688 1.0598 1.8324 2.9700e0033.9600e0033.9600e0033.9600e0033.9600e0030.0000 281.4481 281.4481 0.0183 281.9062 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.1640 0.1293 1.2321 2.8900e0030.3450 1.8600e0030.3469 0.0915 1.7100e0030.0932 293.6648 293.6648 0.0120 0.0110 297.2546 Total 0.1640 0.1293 1.2321 2.8900e0030.3450 1.8600e0030.3469 0.0915 1.7100e0030.0932 293.6648 293.6648 0.0120 0.0110 297.2546 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 20 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
4.0 Operational Detail - Mobile
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 3.6919 7.2988 37.1618 0.0750 7.2845 0.0807 7.3652 1.9456 0.0760 2.0215 7,679.774 8 7,679.774
8 0.4907 0.4582 7,828.579
4 Unmitigated 3.6919 7.2988 37.1618 0.0750 7.2845 0.0807 7.3652 1.9456 0.0760 2.0215 7,679.774 8 7,679.774
8 0.4907 0.4582 7,828.579
4 4.1 Mitigation Measures Mobile
4.2 Trip Summary Information
4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
Other Asphalt Surfaces 0.00 0.00 0.00
Single Family Housing 1,208.32 1,221.12 1094.40 3,365,214 3,365,214 Total 1,208.32 1,221.12 1,094.40 3,365,214 3,365,214
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 9.50 7.30 7.30 0.00 0.00 0.00 0 0 0 Single Family Housing 10.80 7.30 7.50 38.40 22.60 39.00 86 11 3
4.4 Fleet Mix
CalEEMod Version: CalEEMod.2020.4.0 Page 21 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH Other Asphalt Surfaces 0.491968 0.051162 0.166648 0.188672 0.034593 0.008513 0.012315 0.015417 0.000659 0.000471 0.024128 0.001541 0.003914 Single Family Housing 0.491968 0.051162 0.166648 0.188672 0.034593 0.008513 0.012315 0.015417 0.000659 0.000471 0.024128 0.001541 0.003914
5.0 Energy Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
NaturalGas
Mitigated
0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 NaturalGas
Unmitigated
0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181
5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2020.4.0 Page 22 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
6.0 Area Detail
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
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 Single Family
Housing
8333.33 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Total 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Unmitigated
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
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 Single Family
Housing
8.33333 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Total 0.0899 0.7680 0.3268 4.9000e0030.0621 0.0621 0.0621 0.0621 980.3921 980.3921 0.0188 0.0180 986.2181 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 23 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
6.1 Mitigation Measures Area
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 Unmitigated 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 CalEEMod Version: CalEEMod.2020.4.0 Page 24 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
1.2301 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
5.0707 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.1367 1.1678 0.4969 7.4500e0030.0944 0.0944 0.0944 0.0944 0.0000 1,490.823 5 1,490.823
5 0.0286 0.0273 1,499.682
8 Landscaping 0.3194 0.1219 10.5725 5.6000e0040.0584 0.0584 0.0584 0.0584 19.0167 19.0167 0.0184 19.4754 Total 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 25 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
7.1 Mitigation Measures Water
7.0 Water Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
1.2301 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
5.0707 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.1367 1.1678 0.4969 7.4500e0030.0944 0.0944 0.0944 0.0944 0.0000 1,490.823 5 1,490.823
5 0.0286 0.0273 1,499.682
8 Landscaping 0.3194 0.1219 10.5725 5.6000e0040.0584 0.0584 0.0584 0.0584 19.0167 19.0167 0.0184 19.4754 Total 6.7568 1.2897 11.0694 8.0100e0030.1528 0.1528 0.1528 0.1528 0.0000 1,509.840 2 1,509.840
2 0.0469 0.0273 1,519.158
2 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 26 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied
11.0 Vegetation
8.1 Mitigation Measures Waste
8.0 Waste Detail
9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type
10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2020.4.0 Page 27 of 27 Date: 7/21/2021 12:57 PM Lombardi Development - Phase 1 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Applied Lombardi Development Phase 2
Tulare County, Annual
Project Characteristics -
Land Use - Acreage adjusted for the Project site.
Construction Phase - Construction will take place over one year (January 2023 to January 2024) Grading - Grading balanced on-site
Sequestration - At least one tree will be planted at each lot.
Construction Off-road Equipment Mitigation - SJVAPCD Rule 8021
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Other Asphalt Surfaces 8.43 Acre 8.43 367,210.80 0
City Park 3.51 Acre 3.51 152,895.60 0
Single Family Housing 105.00 Dwelling Unit 18.88 189,000.00 300
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
7 Wind Speed (m/s) 2.2 Precipitation Freq (Days) 51
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Southern California Edison
Operational Year 2024
CO2 Intensity
(lb/MWhr)
390.98 CH4 Intensity 0.033
(lb/MWhr)
N2O Intensity 0.004
(lb/MWhr)
Table Name Column Name Default Value New Value
tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 CalEEMod Version: CalEEMod.2020.4.0 Page 1 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 3.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 4.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 9.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstructionPhase NumDays 35.00 13.00
tblConstructionPhase NumDays 500.00 200.00
tblConstructionPhase NumDays 45.00 25.00
tblConstructionPhase NumDays 35.00 12.00
CalEEMod Version: CalEEMod.2020.4.0 Page 2 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
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
2023 2.1840 2.5743 3.0129 7.5800e0030.4868 0.1015 0.5883 0.1704 0.0950 0.2653 0.0000 683.7508 683.7508 0.0932 0.0335 696.0526 Maximum 2.1840 2.5743 3.0129 7.5800e0030.4868 0.1015 0.5883 0.1704 0.0950 0.2653 0.0000 683.7508 683.7508 0.0932 0.0335 696.0526 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
2023 2.0363 1.9571 3.3242 7.5800e0030.4868 0.0141 0.5009 0.1704 0.0139 0.1843 0.0000 683.7504 683.7504 0.0932 0.0335 696.0522 Maximum 2.0363 1.9571 3.3242 7.5800e0030.4868 0.0141 0.5009 0.1704 0.0139 0.1843 0.0000 683.7504 683.7504 0.0932 0.0335 696.0522 Mitigated Construction
tblConstructionPhase NumDays 20.00 10.00
tblLandUse LotAcreage 34.09 18.88
tblSequestration NumberOfNewTrees 0.00 105.00
CalEEMod Version: CalEEMod.2020.4.0 Page 3 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
6.76 23.97 -10.33 0.00 0.00 86.07 14.85 0.00 85.33 30.54 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 1-1-2023 3-31-2023 0.9466 0.5790
2 4-1-2023 6-30-2023 0.7095 0.5629
3 7-1-2023 9-30-2023 0.7173 0.5691
Highest 0.9466 0.5790
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Area 0.9764 0.0483 0.7961 2.9000e0047.5000e0037.5000e0037.5000e0037.5000e0030.0000 46.7605 46.7605 2.0900e0038.3000e00447.0614 Energy 0.0135 0.1150 0.0489 7.3000e0049.3000e0039.3000e0039.3000e0039.3000e0030.0000 280.9824 280.9824 0.0150 3.9500e003282.5363 Mobile 0.5015 0.8269 4.6448 0.0105 1.0339 9.1500e0031.0431 0.2767 8.5900e0030.2853 0.0000 970.1987 970.1987 0.0535 0.0526 987.2129 Waste 0.0000 0.0000 0.0000 0.0000 21.9839 0.0000 21.9839 1.2992 0.0000 54.4642 Water 0.0000 0.0000 0.0000 0.0000 2.1704 11.8378 14.0082 0.2239 5.3800e00321.2109 Total 1.4914 0.9901 5.4898 0.0115 1.0339 0.0260 1.0599 0.2767 0.0254 0.3021 24.1543 1,309.779 4 1,333.933
7 1.5938 0.0628 1,392.485
7 Unmitigated Operational
CalEEMod Version: CalEEMod.2020.4.0 Page 4 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Area 0.9764 0.0483 0.7961 2.9000e0047.5000e0037.5000e0037.5000e0037.5000e0030.0000 46.7605 46.7605 2.0900e0038.3000e00447.0614 Energy 0.0135 0.1150 0.0489 7.3000e0049.3000e0039.3000e0039.3000e0039.3000e0030.0000 280.9824 280.9824 0.0150 3.9500e003282.5363 Mobile 0.5015 0.8269 4.6448 0.0105 1.0339 9.1500e0031.0431 0.2767 8.5900e0030.2853 0.0000 970.1987 970.1987 0.0535 0.0526 987.2129 Waste 0.0000 0.0000 0.0000 0.0000 21.9839 0.0000 21.9839 1.2992 0.0000 54.4642 Water 0.0000 0.0000 0.0000 0.0000 2.1704 11.8378 14.0082 0.2239 5.3800e00321.2109 Total 1.4914 0.9901 5.4898 0.0115 1.0339 0.0260 1.0599 0.2767 0.0254 0.3021 24.1543 1,309.779 4 1,333.933
7 1.5938 0.0628 1,392.485
7 Mitigated 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 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2020.4.0 Page 5 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.0 Construction Detail
2.3 Vegetation
CO2e
Category MT
New Trees 74.3400
Total 74.3400
Vegetation
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Site Preparation Site Preparation 1/1/2023 1/13/2023 5 10 2 Grading Grading 1/14/2023 2/17/2023 5 25
3 Building Construction Building Construction 2/18/2023 11/24/2023 5 200 4 Paving Paving 11/25/2023 12/12/2023 5 12
5 Architectural Coating Architectural Coating 12/13/2023 12/31/2023 5 13 Residential Indoor: 382,725; Residential Outdoor: 127,575; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area:
22,033 (Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 15
Acres of Grading (Grading Phase): 75
Acres of Paving: 8.43
CalEEMod Version: CalEEMod.2020.4.0 Page 6 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.1 Mitigation Measures Construction
OffRoad Equipment
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 Coating 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 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Grading 8 20.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Building Construction 9 256.00 96.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Paving 6 15.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 51.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2020.4.0 Page 7 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.0983 0.0000 0.0983 0.0505 0.0000 0.0505 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0133 0.1376 0.0912 1.9000e0046.3300e0036.3300e0035.8200e0035.8200e0030.0000 16.7254 16.7254 5.4100e0030.0000 16.8606 Total 0.0133 0.1376 0.0912 1.9000e0040.0983 6.3300e0030.1046 0.0505 5.8200e0030.0563 0.0000 16.7254 16.7254 5.4100e0030.0000 16.8606 Unmitigated Construction On-Site
Use Cleaner Engines for Construction Equipment
Reduce Vehicle Speed on Unpaved Roads
CalEEMod Version: CalEEMod.2020.4.0 Page 8 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 3.1000e0042.2000e0042.4500e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5694 0.5694 2.0000e0052.0000e0050.5753 Total 3.1000e0042.2000e0042.4500e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5694 0.5694 2.0000e0052.0000e0050.5753 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 0.0983 0.0000 0.0983 0.0505 0.0000 0.0505 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 3.4800e0030.0608 0.1148 1.9000e0043.1000e0043.1000e0043.1000e0043.1000e0040.0000 16.7253 16.7253 5.4100e0030.0000 16.8606 Total 3.4800e0030.0608 0.1148 1.9000e0040.0983 3.1000e0040.0986 0.0505 3.1000e0040.0508 0.0000 16.7253 16.7253 5.4100e0030.0000 16.8606 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 9 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 3.1000e0042.2000e0042.4500e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5694 0.5694 2.0000e0052.0000e0050.5753 Total 3.1000e0042.2000e0042.4500e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5694 0.5694 2.0000e0052.0000e0050.5753 Mitigated Construction Off-Site
3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Fugitive Dust 0.1150 0.0000 0.1150 0.0457 0.0000 0.0457 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0415 0.4314 0.3506 7.8000e0040.0178 0.0178 0.0164 0.0164 0.0000 68.1690 68.1690 0.0221 0.0000 68.7202 Total 0.0415 0.4314 0.3506 7.8000e0040.1150 0.0178 0.1329 0.0457 0.0164 0.0621 0.0000 68.1690 68.1690 0.0221 0.0000 68.7202 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 10 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 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 8.7000e0046.1000e0046.8000e0032.0000e0051.9900e0031.0000e0052.0000e0035.3000e0041.0000e0055.4000e0040.0000 1.5816 1.5816 5.0000e0055.0000e0051.5982 Total 8.7000e0046.1000e0046.8000e0032.0000e0051.9900e0031.0000e0052.0000e0035.3000e0041.0000e0055.4000e0040.0000 1.5816 1.5816 5.0000e0055.0000e0051.5982 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 0.1150 0.0000 0.1150 0.0457 0.0000 0.0457 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0126 0.2409 0.4590 7.8000e0041.2700e0031.2700e0031.2700e0031.2700e0030.0000 68.1689 68.1689 0.0221 0.0000 68.7201 Total 0.0126 0.2409 0.4590 7.8000e0040.1150 1.2700e0030.1163 0.0457 1.2700e0030.0469 0.0000 68.1689 68.1689 0.0221 0.0000 68.7201 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 11 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 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 8.7000e0046.1000e0046.8000e0032.0000e0051.9900e0031.0000e0052.0000e0035.3000e0041.0000e0055.4000e0040.0000 1.5816 1.5816 5.0000e0055.0000e0051.5982 Total 8.7000e0046.1000e0046.8000e0032.0000e0051.9900e0031.0000e0052.0000e0035.3000e0041.0000e0055.4000e0040.0000 1.5816 1.5816 5.0000e0055.0000e0051.5982 Mitigated Construction Off-Site
3.4 Building Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 0.1573 1.4385 1.6244 2.6900e0030.0700 0.0700 0.0658 0.0658 0.0000 231.8048 231.8048 0.0551 0.0000 233.1833 Total 0.1573 1.4385 1.6244 2.6900e0030.0700 0.0700 0.0658 0.0658 0.0000 231.8048 231.8048 0.0551 0.0000 233.1833 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 12 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Building Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0108 0.4324 0.1305 1.9500e0030.0635 2.7600e0030.0662 0.0183 2.6400e0030.0210 0.0000 186.6075 186.6075 8.6000e0040.0281 194.9926 Worker 0.0894 0.0628 0.6961 1.7700e0030.2039 1.0600e0030.2050 0.0542 9.8000e0040.0552 0.0000 161.9511 161.9511 5.5600e0035.2400e003163.6525 Total 0.1002 0.4952 0.8266 3.7200e0030.2674 3.8200e0030.2712 0.0726 3.6200e0030.0762 0.0000 348.5585 348.5585 6.4200e0030.0333 358.6451 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 0.0534 1.0912 1.7874 2.6900e0038.4600e0038.4600e0038.4600e0038.4600e0030.0000 231.8045 231.8045 0.0551 0.0000 233.1830 Total 0.0534 1.0912 1.7874 2.6900e0038.4600e0038.4600e0038.4600e0038.4600e0030.0000 231.8045 231.8045 0.0551 0.0000 233.1830 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 13 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Building Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0108 0.4324 0.1305 1.9500e0030.0635 2.7600e0030.0662 0.0183 2.6400e0030.0210 0.0000 186.6075 186.6075 8.6000e0040.0281 194.9926 Worker 0.0894 0.0628 0.6961 1.7700e0030.2039 1.0600e0030.2050 0.0542 9.8000e0040.0552 0.0000 161.9511 161.9511 5.5600e0035.2400e003163.6525 Total 0.1002 0.4952 0.8266 3.7200e0030.2674 3.8200e0030.2712 0.0726 3.6200e0030.0762 0.0000 348.5585 348.5585 6.4200e0030.0333 358.6451 Mitigated Construction Off-Site
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 6.2000e0030.0612 0.0875 1.4000e0043.0600e0033.0600e0032.8200e0032.8200e0030.0000 12.0161 12.0161 3.8900e0030.0000 12.1133 Paving 0.0110 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0172 0.0612 0.0875 1.4000e0043.0600e0033.0600e0032.8200e0032.8200e0030.0000 12.0161 12.0161 3.8900e0030.0000 12.1133 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 14 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 3.1000e0042.2000e0042.4500e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5694 0.5694 2.0000e0052.0000e0050.5753 Total 3.1000e0042.2000e0042.4500e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5694 0.5694 2.0000e0052.0000e0050.5753 Unmitigated Construction Off-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Off-Road 2.0000e0030.0602 0.1038 1.4000e0042.2000e0042.2000e0042.2000e0042.2000e0040.0000 12.0161 12.0161 3.8900e0030.0000 12.1133 Paving 0.0110 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 0.0130 0.0602 0.1038 1.4000e0042.2000e0042.2000e0042.2000e0042.2000e0040.0000 12.0161 12.0161 3.8900e0030.0000 12.1133 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 15 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 3.1000e0042.2000e0042.4500e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5694 0.5694 2.0000e0052.0000e0050.5753 Total 3.1000e0042.2000e0042.4500e0031.0000e0057.2000e0040.0000 7.2000e0041.9000e0040.0000 1.9000e0040.0000 0.5694 0.5694 2.0000e0052.0000e0050.5753 Mitigated Construction Off-Site
3.6 Architectural Coating - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Archit. Coating 1.8505 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 1.2500e0038.4700e0030.0118 2.0000e0054.6000e0044.6000e0044.6000e0044.6000e0040.0000 1.6596 1.6596 1.0000e0040.0000 1.6621 Total 1.8518 8.4700e0030.0118 2.0000e0054.6000e0044.6000e0044.6000e0044.6000e0040.0000 1.6596 1.6596 1.0000e0040.0000 1.6621 Unmitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 16 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Architectural Coating - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 1.1600e0038.1000e0049.0100e0032.0000e0052.6400e0031.0000e0052.6500e0037.0000e0041.0000e0057.1000e0040.0000 2.0971 2.0971 7.0000e0057.0000e0052.1192 Total 1.1600e0038.1000e0049.0100e0032.0000e0052.6400e0031.0000e0052.6500e0037.0000e0041.0000e0057.1000e0040.0000 2.0971 2.0971 7.0000e0057.0000e0052.1192 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 1.8505 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 3.5000e0046.8900e0030.0119 2.0000e0053.0000e0053.0000e0053.0000e0053.0000e0050.0000 1.6596 1.6596 1.0000e0040.0000 1.6621 Total 1.8509 6.8900e0030.0119 2.0000e0053.0000e0053.0000e0053.0000e0053.0000e0050.0000 1.6596 1.6596 1.0000e0040.0000 1.6621 Mitigated Construction On-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 17 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Architectural Coating - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 1.1600e0038.1000e0049.0100e0032.0000e0052.6400e0031.0000e0052.6500e0037.0000e0041.0000e0057.1000e0040.0000 2.0971 2.0971 7.0000e0057.0000e0052.1192 Total 1.1600e0038.1000e0049.0100e0032.0000e0052.6400e0031.0000e0052.6500e0037.0000e0041.0000e0057.1000e0040.0000 2.0971 2.0971 7.0000e0057.0000e0052.1192 Mitigated Construction Off-Site
4.0 Operational Detail - Mobile
4.1 Mitigation Measures Mobile
CalEEMod Version: CalEEMod.2020.4.0 Page 18 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 0.5015 0.8269 4.6448 0.0105 1.0339 9.1500e0031.0431 0.2767 8.5900e0030.2853 0.0000 970.1987 970.1987 0.0535 0.0526 987.2129 Unmitigated 0.5015 0.8269 4.6448 0.0105 1.0339 9.1500e0031.0431 0.2767 8.5900e0030.2853 0.0000 970.1987 970.1987 0.0535 0.0526 987.2129
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
City Park 2.74 6.88 7.69 8,617 8,617
Other Asphalt Surfaces 0.00 0.00 0.00
Single Family Housing 991.20 1,001.70 897.75 2,760,527 2,760,527 Total 993.94 1,008.58 905.44 2,769,145 2,769,145
Miles Trip % Trip Purpose %
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C H-O or C-NW Primary Diverted Pass-by City Park 9.50 7.30 7.30 33.00 48.00 19.00 66 28 6
Other Asphalt Surfaces 9.50 7.30 7.30 0.00 0.00 0.00 0 0 0 Single Family Housing 10.80 7.30 7.50 38.40 22.60 39.00 86 11 3
4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH City Park 0.509869 0.051139 0.167106 0.174849 0.031609 0.007996 0.012006 0.015707 0.000636 0.000471 0.023554 0.001465 0.003592 Other Asphalt Surfaces 0.509869 0.051139 0.167106 0.174849 0.031609 0.007996 0.012006 0.015707 0.000636 0.000471 0.023554 0.001465 0.003592 CalEEMod Version: CalEEMod.2020.4.0 Page 19 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied Single Family Housing 0.509869 0.051139 0.167106 0.174849 0.031609 0.007996 0.012006 0.015707 0.000636 0.000471 0.023554 0.001465 0.003592
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 147.8334 147.8334 0.0125 1.5100e003148.5961 Electricity
Unmitigated
0.0000 0.0000 0.0000 0.0000 0.0000 147.8334 147.8334 0.0125 1.5100e003148.5961 NaturalGas
Mitigated
0.0135 0.1150 0.0489 7.3000e0049.3000e0039.3000e0039.3000e0039.3000e0030.0000 133.1490 133.1490 2.5500e0032.4400e003133.9402 NaturalGas
Unmitigated
0.0135 0.1150 0.0489 7.3000e0049.3000e0039.3000e0039.3000e0039.3000e0030.0000 133.1490 133.1490 2.5500e0032.4400e003133.9402
5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2020.4.0 Page 20 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr tons/yr MT/yr
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 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 Single Family
Housing
2.49512e
+006
0.0135 0.1150 0.0489 7.3000e0049.3000e0039.3000e0039.3000e0039.3000e0030.0000 133.1490 133.1490 2.5500e0032.4400e003133.9402 Total 0.0135 0.1150 0.0489 7.3000e0049.3000e0039.3000e0039.3000e0039.3000e0030.0000 133.1490 133.1490 2.5500e0032.4400e003133.9402 Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 21 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr tons/yr MT/yr
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 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 Single Family
Housing
2.49512e
+006
0.0135 0.1150 0.0489 7.3000e0049.3000e0039.3000e0039.3000e0039.3000e0030.0000 133.1490 133.1490 2.5500e0032.4400e003133.9402 Total 0.0135 0.1150 0.0489 7.3000e0049.3000e0039.3000e0039.3000e0039.3000e0030.0000 133.1490 133.1490 2.5500e0032.4400e003133.9402 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 22 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
5.3 Energy by Land Use - Electricity
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
City Park 0 0.0000 0.0000 0.0000 0.0000
Other Asphalt
Surfaces
0 0.0000 0.0000 0.0000 0.0000
Single Family
Housing
833590 147.8334 0.0125 1.5100e003148.5961
Total 147.8334 0.0125 1.5100e003148.5961
Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 23 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
6.1 Mitigation Measures Area
6.0 Area Detail
5.3 Energy by Land Use - Electricity
Electricity
Use
Total CO2 CH4 N2O CO2e
Land Use kWh/yr MT/yr
City Park 0 0.0000 0.0000 0.0000 0.0000
Other Asphalt
Surfaces
0 0.0000 0.0000 0.0000 0.0000
Single Family
Housing
833590 147.8334 0.0125 1.5100e003148.5961
Total 147.8334 0.0125 1.5100e003148.5961
Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 24 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category tons/yr MT/yr
Mitigated 0.9764 0.0483 0.7961 2.9000e0047.5000e0037.5000e0037.5000e0037.5000e0030.0000 46.7605 46.7605 2.0900e0038.3000e00447.0614 Unmitigated 0.9764 0.0483 0.7961 2.9000e0047.5000e0037.5000e0037.5000e0037.5000e0030.0000 46.7605 46.7605 2.0900e0038.3000e00447.0614
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
0.1851 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Consumer
Products
0.7633 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Hearth 4.6000e0030.0393 0.0167 2.5000e0043.1800e0033.1800e0033.1800e0033.1800e0030.0000 45.4868 45.4868 8.7000e0048.3000e00445.7571 Landscaping 0.0234 8.9800e0030.7794 4.0000e0054.3200e0034.3200e0034.3200e0034.3200e0030.0000 1.2737 1.2737 1.2200e0030.0000 1.3043 Total 0.9764 0.0483 0.7961 2.9000e0047.5000e0037.5000e0037.5000e0037.5000e0030.0000 46.7605 46.7605 2.0900e0038.3000e00447.0614 Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 25 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
7.1 Mitigation Measures Water
7.0 Water Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory tons/yr MT/yr
Architectural
Coating
0.1851 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Consumer
Products
0.7633 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Hearth 4.6000e0030.0393 0.0167 2.5000e0043.1800e0033.1800e0033.1800e0033.1800e0030.0000 45.4868 45.4868 8.7000e0048.3000e00445.7571 Landscaping 0.0234 8.9800e0030.7794 4.0000e0054.3200e0034.3200e0034.3200e0034.3200e0030.0000 1.2737 1.2737 1.2200e0030.0000 1.3043 Total 0.9764 0.0483 0.7961 2.9000e0047.5000e0037.5000e0037.5000e0037.5000e0030.0000 46.7605 46.7605 2.0900e0038.3000e00447.0614 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 26 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied Total CO2 CH4 N2O CO2e
Category MT/yr
Mitigated 14.0082 0.2239 5.3800e00321.2109
Unmitigated 14.0082 0.2239 5.3800e00321.2109
7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
City Park 0 / 4.1821 2.5959 2.2000e0043.0000e0052.6093 Other Asphalt
Surfaces
0 / 0 0.0000 0.0000 0.0000 0.0000
Single Family
Housing
6.84117 /
4.31291
11.4124 0.2237 5.3600e00318.6016
Total 14.0082 0.2239 5.3900e00321.2109
Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 27 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
7.2 Water by Land Use
Indoor/Out
door Use
Total CO2 CH4 N2O CO2e
Land Use Mgal MT/yr
City Park 0 / 4.1821 2.5959 2.2000e0043.0000e0052.6093 Other Asphalt
Surfaces
0 / 0 0.0000 0.0000 0.0000 0.0000
Single Family
Housing
6.84117 /
4.31291
11.4124 0.2237 5.3600e00318.6016
Total 14.0082 0.2239 5.3900e00321.2109
Mitigated
8.1 Mitigation Measures Waste
8.0 Waste Detail
CalEEMod Version: CalEEMod.2020.4.0 Page 28 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied Total CO2 CH4 N2O CO2e
MT/yr
Mitigated 21.9839 1.2992 0.0000 54.4642
Unmitigated 21.9839 1.2992 0.0000 54.4642
Category/Year
8.2 Waste by Land Use
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
City Park 0.3 0.0609 3.6000e0030.0000 0.1509
Other Asphalt
Surfaces
0 0.0000 0.0000 0.0000 0.0000
Single Family
Housing
108 21.9230 1.2956 0.0000 54.3134
Total 21.9839 1.2992 0.0000 54.4642
Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 29 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
8.2 Waste by Land Use
Waste
Disposed
Total CO2 CH4 N2O CO2e
Land Use tons MT/yr
City Park 0.3 0.0609 3.6000e0030.0000 0.1509
Other Asphalt
Surfaces
0 0.0000 0.0000 0.0000 0.0000
Single Family
Housing
108 21.9230 1.2956 0.0000 54.3134
Total 21.9839 1.2992 0.0000 54.4642
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.2020.4.0 Page 30 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
11.0 Vegetation
Total CO2 CH4 N2O CO2e
Category MT
Unmitigated 74.3400 0.0000 0.0000 74.3400
11.2 Net New Trees
Number of
Trees
Total CO2 CH4 N2O CO2e
MT
Miscellaneous 105 74.3400 0.0000 0.0000 74.3400
Total 74.3400 0.0000 0.0000 74.3400
Species Class
CalEEMod Version: CalEEMod.2020.4.0 Page 31 of 31 Date: 7/21/2021 4:25 PM Lombardi Development Phase 2 - Tulare County, Annual
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied Lombardi Development Phase 2
Tulare County, Summer
Project Characteristics -
Land Use - Acreage adjusted for the Project site.
Construction Phase - Construction will take place over one year (January 2023 to January 2024) Grading - Grading balanced on-site
Sequestration - At least one tree will be planted at each lot.
Construction Off-road Equipment Mitigation - SJVAPCD Rule 8021
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Other Asphalt Surfaces 8.43 Acre 8.43 367,210.80 0
City Park 3.51 Acre 3.51 152,895.60 0
Single Family Housing 105.00 Dwelling Unit 18.88 189,000.00 300
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
7 Wind Speed (m/s) 2.2 Precipitation Freq (Days) 51
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Southern California Edison
Operational Year 2024
CO2 Intensity
(lb/MWhr)
390.98 CH4 Intensity 0.033
(lb/MWhr)
N2O Intensity 0.004
(lb/MWhr)
Table Name Column Name Default Value New Value
tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 CalEEMod Version: CalEEMod.2020.4.0 Page 1 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 3.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 4.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 9.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstructionPhase NumDays 35.00 13.00
tblConstructionPhase NumDays 500.00 200.00
tblConstructionPhase NumDays 45.00 25.00
tblConstructionPhase NumDays 35.00 12.00
CalEEMod Version: CalEEMod.2020.4.0 Page 2 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.0 Emissions Summary
2.1 Overall Construction (Maximum Daily Emission)
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2023 285.0953 34.5614 28.6849 0.0656 19.8049 1.4253 21.0716 10.1417 1.3113 11.3071 0.0000 6,553.710 4 6,553.710
4 1.9489 0.3642 6,679.175
1 Maximum 285.0953 34.5614 28.6849 0.0656 19.8049 1.4253 21.0716 10.1417 1.3113 11.3071 0.0000 6,553.710 4 6,553.710
4 1.9489 0.3642 6,679.175
1 Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2023 284.9581 19.3165 37.3563 0.0656 19.8049 0.1227 19.8677 10.1417 0.1207 10.2044 0.0000 6,553.710 4 6,553.710
4 1.9489 0.3642 6,679.175
1 Maximum 284.9581 19.3165 37.3563 0.0656 19.8049 0.1227 19.8677 10.1417 0.1207 10.2044 0.0000 6,553.710 4 6,553.710
4 1.9489 0.3642 6,679.175
1 Mitigated Construction
tblConstructionPhase NumDays 20.00 10.00
tblLandUse LotAcreage 34.09 18.88
tblSequestration NumberOfNewTrees 0.00 105.00
CalEEMod Version: CalEEMod.2020.4.0 Page 3 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.05 44.11 -30.23 0.00 0.00 91.39 5.71 0.00 90.80 9.75 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2020.4.0 Page 4 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 Energy 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Mobile 3.4366 4.3777 28.4038 0.0631 6.0062 0.0516 6.0578 1.6035 0.0485 1.6519 6,420.259 5 6,420.259
5 0.3181 0.3178 6,522.908
1 Total 9.0794 6.0654 37.7397 0.0736 6.0062 0.2280 6.2341 1.6035 0.2249 1.8283 0.0000 8,463.029 2 8,463.029
2 0.3719 0.3549 8,578.098
6 Unmitigated Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 Energy 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Mobile 3.4366 4.3777 28.4038 0.0631 6.0062 0.0516 6.0578 1.6035 0.0485 1.6519 6,420.259 5 6,420.259
5 0.3181 0.3178 6,522.908
1 Total 9.0794 6.0654 37.7397 0.0736 6.0062 0.2280 6.2341 1.6035 0.2249 1.8283 0.0000 8,463.029 2 8,463.029
2 0.3719 0.3549 8,578.098
6 Mitigated Operational
CalEEMod Version: CalEEMod.2020.4.0 Page 5 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Site Preparation Site Preparation 1/1/2023 1/13/2023 5 10 2 Grading Grading 1/14/2023 2/17/2023 5 25
3 Building Construction Building Construction 2/18/2023 11/24/2023 5 200 4 Paving Paving 11/25/2023 12/12/2023 5 12
5 Architectural Coating Architectural Coating 12/13/2023 12/31/2023 5 13 OffRoad Equipment
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
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Residential Indoor: 382,725; Residential Outdoor: 127,575; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area:
22,033 (Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 15
Acres of Grading (Grading Phase): 75
Acres of Paving: 8.43
CalEEMod Version: CalEEMod.2020.4.0 Page 6 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.1 Mitigation Measures Construction
Use Cleaner Engines for Construction Equipment
Reduce Vehicle Speed on Unpaved Roads
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 Coating 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 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Grading 8 20.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Building Construction 9 256.00 96.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Paving 6 15.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 51.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2020.4.0 Page 7 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 19.6570 0.0000 19.6570 10.1025 0.0000 10.1025 0.0000 0.0000 Off-Road 2.6595 27.5242 18.2443 0.0381 1.2660 1.2660 1.1647 1.1647 3,687.308 1 3,687.308
1 1.1926 3,717.121
9 Total 2.6595 27.5242 18.2443 0.0381 19.6570 1.2660 20.9230 10.1025 1.1647 11.2672 3,687.308 1 3,687.308
1 1.1926 3,717.121
9 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0734 0.0412 0.5704 1.3500e0030.1479 7.4000e0040.1486 0.0392 6.9000e0040.0399 136.6267 136.6267 4.1700e0033.8900e003137.8891 Total 0.0734 0.0412 0.5704 1.3500e0030.1479 7.4000e0040.1486 0.0392 6.9000e0040.0399 136.6267 136.6267 4.1700e0033.8900e003137.8891 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 8 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 19.6570 0.0000 19.6570 10.1025 0.0000 10.1025 0.0000 0.0000 Off-Road 0.6967 12.1620 22.9600 0.0381 0.0621 0.0621 0.0621 0.0621 0.0000 3,687.308 1 3,687.308
1 1.1926 3,717.121
9 Total 0.6967 12.1620 22.9600 0.0381 19.6570 0.0621 19.7191 10.1025 0.0621 10.1645 0.0000 3,687.308 1 3,687.308
1 1.1926 3,717.121
9 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0734 0.0412 0.5704 1.3500e0030.1479 7.4000e0040.1486 0.0392 6.9000e0040.0399 136.6267 136.6267 4.1700e0033.8900e003137.8891 Total 0.0734 0.0412 0.5704 1.3500e0030.1479 7.4000e0040.1486 0.0392 6.9000e0040.0399 136.6267 136.6267 4.1700e0033.8900e003137.8891 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 9 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 9.2036 0.0000 9.2036 3.6538 0.0000 3.6538 0.0000 0.0000 Off-Road 3.3217 34.5156 28.0512 0.0621 1.4245 1.4245 1.3105 1.3105 6,011.477 7 6,011.477
7 1.9442 6,060.083
6 Total 3.3217 34.5156 28.0512 0.0621 9.2036 1.4245 10.6281 3.6538 1.3105 4.9643 6,011.477 7 6,011.477
7 1.9442 6,060.083
6 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0815 0.0458 0.6337 1.5000e0030.1643 8.3000e0040.1651 0.0436 7.6000e0040.0443 151.8074 151.8074 4.6400e0034.3200e003153.2101 Total 0.0815 0.0458 0.6337 1.5000e0030.1643 8.3000e0040.1651 0.0436 7.6000e0040.0443 151.8074 151.8074 4.6400e0034.3200e003153.2101 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 10 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 9.2036 0.0000 9.2036 3.6538 0.0000 3.6538 0.0000 0.0000 Off-Road 1.0110 19.2707 36.7226 0.0621 0.1015 0.1015 0.1015 0.1015 0.0000 6,011.477 7 6,011.477
7 1.9442 6,060.083
6 Total 1.0110 19.2707 36.7226 0.0621 9.2036 0.1015 9.3051 3.6538 0.1015 3.7553 0.0000 6,011.477 7 6,011.477
7 1.9442 6,060.083
6 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0815 0.0458 0.6337 1.5000e0030.1643 8.3000e0040.1651 0.0436 7.6000e0040.0443 151.8074 151.8074 4.6400e0034.3200e003153.2101 Total 0.0815 0.0458 0.6337 1.5000e0030.1643 8.3000e0040.1651 0.0436 7.6000e0040.0443 151.8074 151.8074 4.6400e0034.3200e003153.2101 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 11 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Building Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Total 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.1122 4.1327 1.2861 0.0194 0.6509 0.0275 0.6784 0.1874 0.0264 0.2138 2,055.365 5 2,055.365
5 9.6200e0030.3090 2,147.679
6 Worker 1.0433 0.5861 8.1118 0.0192 2.1030 0.0106 2.1136 0.5578 9.7500e0030.5676 1,943.135 0 1,943.135
0 0.0594 0.0553 1,961.089
4 Total 1.1556 4.7188 9.3979 0.0387 2.7538 0.0381 2.7920 0.7452 0.0361 0.7813 3,998.500 5 3,998.500
5 0.0690 0.3642 4,108.769
0 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 12 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Building Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Total 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.1122 4.1327 1.2861 0.0194 0.6509 0.0275 0.6784 0.1874 0.0264 0.2138 2,055.365 5 2,055.365
5 9.6200e0030.3090 2,147.679
6 Worker 1.0433 0.5861 8.1118 0.0192 2.1030 0.0106 2.1136 0.5578 9.7500e0030.5676 1,943.135 0 1,943.135
0 0.0594 0.0553 1,961.089
4 Total 1.1556 4.7188 9.3979 0.0387 2.7538 0.0381 2.7920 0.7452 0.0361 0.7813 3,998.500 5 3,998.500
5 0.0690 0.3642 4,108.769
0 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 13 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.0327 10.1917 14.5842 0.0228 0.5102 0.5102 0.4694 0.4694 2,207.584 1 2,207.584
1 0.7140 2,225.433
6 Paving 1.8406 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 2.8733 10.1917 14.5842 0.0228 0.5102 0.5102 0.4694 0.4694 2,207.584 1 2,207.584
1 0.7140 2,225.433
6 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0611 0.0343 0.4753 1.1300e0030.1232 6.2000e0040.1238 0.0327 5.7000e0040.0333 113.8556 113.8556 3.4800e0033.2400e003114.9076 Total 0.0611 0.0343 0.4753 1.1300e0030.1232 6.2000e0040.1238 0.0327 5.7000e0040.0333 113.8556 113.8556 3.4800e0033.2400e003114.9076 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 14 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.3341 10.0395 17.2957 0.0228 0.0374 0.0374 0.0374 0.0374 0.0000 2,207.584 1 2,207.584
1 0.7140 2,225.433
6 Paving 1.8406 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 2.1746 10.0395 17.2957 0.0228 0.0374 0.0374 0.0374 0.0374 0.0000 2,207.584 1 2,207.584
1 0.7140 2,225.433
6 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0611 0.0343 0.4753 1.1300e0030.1232 6.2000e0040.1238 0.0327 5.7000e0040.0333 113.8556 113.8556 3.4800e0033.2400e003114.9076 Total 0.0611 0.0343 0.4753 1.1300e0030.1232 6.2000e0040.1238 0.0327 5.7000e0040.0333 113.8556 113.8556 3.4800e0033.2400e003114.9076 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 15 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Architectural Coating - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 284.6958 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.1917 1.3030 1.8111 2.9700e0030.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690 Total 284.8874 1.3030 1.8111 2.9700e0030.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.2079 0.1168 1.6160 3.8300e0030.4190 2.1100e0030.4211 0.1111 1.9400e0030.1131 387.1089 387.1089 0.0118 0.0110 390.6858 Total 0.2079 0.1168 1.6160 3.8300e0030.4190 2.1100e0030.4211 0.1111 1.9400e0030.1131 387.1089 387.1089 0.0118 0.0110 390.6858 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 16 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Architectural Coating - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 284.6958 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0545 1.0598 1.8324 2.9700e0033.9600e0033.9600e0033.9600e0033.9600e0030.0000 281.4481 281.4481 0.0168 281.8690 Total 284.7503 1.0598 1.8324 2.9700e0033.9600e0033.9600e0033.9600e0033.9600e0030.0000 281.4481 281.4481 0.0168 281.8690 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.2079 0.1168 1.6160 3.8300e0030.4190 2.1100e0030.4211 0.1111 1.9400e0030.1131 387.1089 387.1089 0.0118 0.0110 390.6858 Total 0.2079 0.1168 1.6160 3.8300e0030.4190 2.1100e0030.4211 0.1111 1.9400e0030.1131 387.1089 387.1089 0.0118 0.0110 390.6858 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 17 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
4.0 Operational Detail - Mobile
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 3.4366 4.3777 28.4038 0.0631 6.0062 0.0516 6.0578 1.6035 0.0485 1.6519 6,420.259 5 6,420.259
5 0.3181 0.3178 6,522.908
1 Unmitigated 3.4366 4.3777 28.4038 0.0631 6.0062 0.0516 6.0578 1.6035 0.0485 1.6519 6,420.259 5 6,420.259
5 0.3181 0.3178 6,522.908
1 4.1 Mitigation Measures Mobile
4.2 Trip Summary Information
4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
City Park 2.74 6.88 7.69 8,617 8,617
Other Asphalt Surfaces 0.00 0.00 0.00
Single Family Housing 991.20 1,001.70 897.75 2,760,527 2,760,527 Total 993.94 1,008.58 905.44 2,769,145 2,769,145
Miles Trip % Trip Purpose %
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C H-O or C-NW Primary Diverted Pass-by City Park 9.50 7.30 7.30 33.00 48.00 19.00 66 28 6
Other Asphalt Surfaces 9.50 7.30 7.30 0.00 0.00 0.00 0 0 0 Single Family Housing 10.80 7.30 7.50 38.40 22.60 39.00 86 11 3 CalEEMod Version: CalEEMod.2020.4.0 Page 18 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH City Park 0.509869 0.051139 0.167106 0.174849 0.031609 0.007996 0.012006 0.015707 0.000636 0.000471 0.023554 0.001465 0.003592 Other Asphalt Surfaces 0.509869 0.051139 0.167106 0.174849 0.031609 0.007996 0.012006 0.015707 0.000636 0.000471 0.023554 0.001465 0.003592 Single Family Housing 0.509869 0.051139 0.167106 0.174849 0.031609 0.007996 0.012006 0.015707 0.000636 0.000471 0.023554 0.001465 0.003592
5.0 Energy Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
NaturalGas
Mitigated
0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 NaturalGas
Unmitigated
0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070
5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2020.4.0 Page 19 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 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 Single Family
Housing
6835.94 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Total 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 20 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
6.1 Mitigation Measures Area
6.0 Area Detail
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 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 Single Family
Housing
6.83594 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Total 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 21 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 Unmitigated 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
1.0140 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
4.1825 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.1121 0.9580 0.4077 6.1100e0030.0775 0.0775 0.0775 0.0775 0.0000 1,222.941 2 1,222.941
2 0.0234 0.0224 1,230.208
5 Landscaping 0.2605 0.0998 8.6602 4.6000e0040.0480 0.0480 0.0480 0.0480 15.6006 15.6006 0.0150 15.9749 Total 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 22 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
7.1 Mitigation Measures Water
7.0 Water Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
1.0140 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
4.1825 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.1121 0.9580 0.4077 6.1100e0030.0775 0.0775 0.0775 0.0775 0.0000 1,222.941 2 1,222.941
2 0.0234 0.0224 1,230.208
5 Landscaping 0.2605 0.0998 8.6602 4.6000e0040.0480 0.0480 0.0480 0.0480 15.6006 15.6006 0.0150 15.9749 Total 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 23 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
11.0 Vegetation
8.1 Mitigation Measures Waste
8.0 Waste Detail
9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type
10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2020.4.0 Page 24 of 24 Date: 7/21/2021 4:26 PM Lombardi Development Phase 2 - Tulare County, Summer
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied Lombardi Development Phase 2
Tulare County, Winter
Project Characteristics -
Land Use - Acreage adjusted for the Project site.
Construction Phase - Construction will take place over one year (January 2023 to January 2024) Grading - Grading balanced on-site
Sequestration - At least one tree will be planted at each lot.
Construction Off-road Equipment Mitigation - SJVAPCD Rule 8021
1.1 Land Usage
Land Uses Size Metric Lot Acreage Floor Surface Area Population Other Asphalt Surfaces 8.43 Acre 8.43 367,210.80 0
City Park 3.51 Acre 3.51 152,895.60 0
Single Family Housing 105.00 Dwelling Unit 18.88 189,000.00 300
1.2 Other Project Characteristics
Urbanization
Climate Zone
Urban
7 Wind Speed (m/s) 2.2 Precipitation Freq (Days) 51
1.3 User Entered Comments & Non-Default Data
1.0 Project Characteristics
Utility Company Southern California Edison
Operational Year 2024
CO2 Intensity
(lb/MWhr)
390.98 CH4 Intensity 0.033
(lb/MWhr)
N2O Intensity 0.004
(lb/MWhr)
Table Name Column Name Default Value New Value
tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 0 15 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 CalEEMod Version: CalEEMod.2020.4.0 Page 1 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 3.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 4.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 2.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 9.00 tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 1.00 tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstEquipMitigation Tier No Change Tier 4 Interim
tblConstructionPhase NumDays 35.00 13.00
tblConstructionPhase NumDays 500.00 200.00
tblConstructionPhase NumDays 45.00 25.00
tblConstructionPhase NumDays 35.00 12.00
CalEEMod Version: CalEEMod.2020.4.0 Page 2 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.0 Emissions Summary
2.1 Overall Construction (Maximum Daily Emission)
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2023 285.0694 34.5693 28.5826 0.0634 19.8049 1.4253 21.0716 10.1417 1.3113 11.3071 0.0000 6,335.681 9 6,335.681
9 1.9493 0.3713 6,463.381
1 Maximum 285.0694 34.5693 28.5826 0.0634 19.8049 1.4253 21.0716 10.1417 1.3113 11.3071 0.0000 6,335.681 9 6,335.681
9 1.9493 0.3713 6,463.381
1 Unmitigated Construction
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Year lb/day lb/day
2023 284.9322 19.3244 37.2540 0.0634 19.8049 0.1228 19.8677 10.1417 0.1208 10.2044 0.0000 6,335.681 9 6,335.681
9 1.9493 0.3713 6,463.381
1 Maximum 284.9322 19.3244 37.2540 0.0634 19.8049 0.1228 19.8677 10.1417 0.1208 10.2044 0.0000 6,335.681 9 6,335.681
9 1.9493 0.3713 6,463.381
1 Mitigated Construction
tblConstructionPhase NumDays 20.00 10.00
tblLandUse LotAcreage 34.09 18.88
tblSequestration NumberOfNewTrees 0.00 105.00
CalEEMod Version: CalEEMod.2020.4.0 Page 3 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.05 44.10 -30.34 0.00 0.00 91.38 5.71 0.00 90.79 9.75 0.00 0.00 0.00 0.00 0.00 0.00 CalEEMod Version: CalEEMod.2020.4.0 Page 4 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
2.2 Overall Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 Energy 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Mobile 2.6642 4.9082 26.9440 0.0577 6.0062 0.0516 6.0578 1.6035 0.0485 1.6520 5,879.184 2 5,879.184
2 0.3549 0.3387 5,988.990
5 Total 8.3071 6.5959 36.2799 0.0683 6.0062 0.2280 6.2342 1.6035 0.2249 1.8284 0.0000 7,921.953 9 7,921.953
9 0.4087 0.3759 8,044.180
9 Unmitigated Operational
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Area 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 Energy 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Mobile 2.6642 4.9082 26.9440 0.0577 6.0062 0.0516 6.0578 1.6035 0.0485 1.6520 5,879.184 2 5,879.184
2 0.3549 0.3387 5,988.990
5 Total 8.3071 6.5959 36.2799 0.0683 6.0062 0.2280 6.2342 1.6035 0.2249 1.8284 0.0000 7,921.953 9 7,921.953
9 0.4087 0.3759 8,044.180
9 Mitigated Operational
CalEEMod Version: CalEEMod.2020.4.0 Page 5 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.0 Construction Detail
Construction Phase
Phase
Number
Phase Name Phase Type Start Date End Date Num Days
Week
Num Days Phase Description
1 Site Preparation Site Preparation 1/1/2023 1/13/2023 5 10 2 Grading Grading 1/14/2023 2/17/2023 5 25
3 Building Construction Building Construction 2/18/2023 11/24/2023 5 200 4 Paving Paving 11/25/2023 12/12/2023 5 12
5 Architectural Coating Architectural Coating 12/13/2023 12/31/2023 5 13 OffRoad Equipment
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
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio-CO2 Total CO2 CH4 N20 CO2e
Percent
Reduction
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Residential Indoor: 382,725; Residential Outdoor: 127,575; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area:
22,033 (Architectural Coating – sqft)
Acres of Grading (Site Preparation Phase): 15
Acres of Grading (Grading Phase): 75
Acres of Paving: 8.43
CalEEMod Version: CalEEMod.2020.4.0 Page 6 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.1 Mitigation Measures Construction
Use Cleaner Engines for Construction Equipment
Reduce Vehicle Speed on Unpaved Roads
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 Coating 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 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Grading 8 20.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Building Construction 9 256.00 96.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Paving 6 15.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT Architectural Coating 1 51.00 0.00 0.00 10.80 7.30 20.00 LD_Mix HDT_Mix HHDT CalEEMod Version: CalEEMod.2020.4.0 Page 7 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 19.6570 0.0000 19.6570 10.1025 0.0000 10.1025 0.0000 0.0000 Off-Road 2.6595 27.5242 18.2443 0.0381 1.2660 1.2660 1.1647 1.1647 3,687.308 1 3,687.308
1 1.1926 3,717.121
9 Total 2.6595 27.5242 18.2443 0.0381 19.6570 1.2660 20.9230 10.1025 1.1647 11.2672 3,687.308 1 3,687.308
1 1.1926 3,717.121
9 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0642 0.0483 0.4782 1.2000e0030.1479 7.4000e0040.1486 0.0392 6.9000e0040.0399 121.0230 121.0230 4.6000e0034.3200e003122.4250 Total 0.0642 0.0483 0.4782 1.2000e0030.1479 7.4000e0040.1486 0.0392 6.9000e0040.0399 121.0230 121.0230 4.6000e0034.3200e003122.4250 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 8 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.2 Site Preparation - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 19.6570 0.0000 19.6570 10.1025 0.0000 10.1025 0.0000 0.0000 Off-Road 0.6967 12.1620 22.9600 0.0381 0.0621 0.0621 0.0621 0.0621 0.0000 3,687.308 1 3,687.308
1 1.1926 3,717.121
9 Total 0.6967 12.1620 22.9600 0.0381 19.6570 0.0621 19.7191 10.1025 0.0621 10.1645 0.0000 3,687.308 1 3,687.308
1 1.1926 3,717.121
9 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0642 0.0483 0.4782 1.2000e0030.1479 7.4000e0040.1486 0.0392 6.9000e0040.0399 121.0230 121.0230 4.6000e0034.3200e003122.4250 Total 0.0642 0.0483 0.4782 1.2000e0030.1479 7.4000e0040.1486 0.0392 6.9000e0040.0399 121.0230 121.0230 4.6000e0034.3200e003122.4250 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 9 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 9.2036 0.0000 9.2036 3.6538 0.0000 3.6538 0.0000 0.0000 Off-Road 3.3217 34.5156 28.0512 0.0621 1.4245 1.4245 1.3105 1.3105 6,011.477 7 6,011.477
7 1.9442 6,060.083
6 Total 3.3217 34.5156 28.0512 0.0621 9.2036 1.4245 10.6281 3.6538 1.3105 4.9643 6,011.477 7 6,011.477
7 1.9442 6,060.083
6 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0714 0.0537 0.5314 1.3300e0030.1643 8.3000e0040.1651 0.0436 7.6000e0040.0443 134.4700 134.4700 5.1100e0034.8000e003136.0278 Total 0.0714 0.0537 0.5314 1.3300e0030.1643 8.3000e0040.1651 0.0436 7.6000e0040.0443 134.4700 134.4700 5.1100e0034.8000e003136.0278 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 10 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.3 Grading - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Fugitive Dust 9.2036 0.0000 9.2036 3.6538 0.0000 3.6538 0.0000 0.0000 Off-Road 1.0110 19.2707 36.7226 0.0621 0.1015 0.1015 0.1015 0.1015 0.0000 6,011.477 7 6,011.477
7 1.9442 6,060.083
6 Total 1.0110 19.2707 36.7226 0.0621 9.2036 0.1015 9.3051 3.6538 0.1015 3.7553 0.0000 6,011.477 7 6,011.477
7 1.9442 6,060.083
6 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0714 0.0537 0.5314 1.3300e0030.1643 8.3000e0040.1651 0.0436 7.6000e0040.0443 134.4700 134.4700 5.1100e0034.8000e003136.0278 Total 0.0714 0.0537 0.5314 1.3300e0030.1643 8.3000e0040.1651 0.0436 7.6000e0040.0443 134.4700 134.4700 5.1100e0034.8000e003136.0278 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 11 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Building Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Total 1.5728 14.3849 16.2440 0.0269 0.6997 0.6997 0.6584 0.6584 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.1056 4.4305 1.3298 0.0195 0.6509 0.0276 0.6785 0.1874 0.0264 0.2139 2,059.256 1 2,059.256
1 9.3100e0030.3098 2,151.819
3 Worker 0.9132 0.6869 6.8016 0.0170 2.1030 0.0106 2.1136 0.5578 9.7500e0030.5676 1,721.215 8 1,721.215
8 0.0654 0.0614 1,741.155
8 Total 1.0188 5.1174 8.1314 0.0365 2.7538 0.0382 2.7921 0.7452 0.0362 0.7814 3,780.471 9 3,780.471
9 0.0747 0.3713 3,892.975
1 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 12 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.4 Building Construction - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Total 0.5335 10.9122 17.8738 0.0269 0.0846 0.0846 0.0846 0.0846 0.0000 2,555.209 9 2,555.209
9 0.6079 2,570.406
1 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.1056 4.4305 1.3298 0.0195 0.6509 0.0276 0.6785 0.1874 0.0264 0.2139 2,059.256 1 2,059.256
1 9.3100e0030.3098 2,151.819
3 Worker 0.9132 0.6869 6.8016 0.0170 2.1030 0.0106 2.1136 0.5578 9.7500e0030.5676 1,721.215 8 1,721.215
8 0.0654 0.0614 1,741.155
8 Total 1.0188 5.1174 8.1314 0.0365 2.7538 0.0382 2.7921 0.7452 0.0362 0.7814 3,780.471 9 3,780.471
9 0.0747 0.3713 3,892.975
1 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 13 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 1.0327 10.1917 14.5842 0.0228 0.5102 0.5102 0.4694 0.4694 2,207.584 1 2,207.584
1 0.7140 2,225.433
6 Paving 1.8406 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 2.8733 10.1917 14.5842 0.0228 0.5102 0.5102 0.4694 0.4694 2,207.584 1 2,207.584
1 0.7140 2,225.433
6 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0535 0.0403 0.3985 1.0000e0030.1232 6.2000e0040.1238 0.0327 5.7000e0040.0333 100.8525 100.8525 3.8300e0033.6000e003102.0209 Total 0.0535 0.0403 0.3985 1.0000e0030.1232 6.2000e0040.1238 0.0327 5.7000e0040.0333 100.8525 100.8525 3.8300e0033.6000e003102.0209 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 14 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.5 Paving - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Off-Road 0.3341 10.0395 17.2957 0.0228 0.0374 0.0374 0.0374 0.0374 0.0000 2,207.584 1 2,207.584
1 0.7140 2,225.433
6 Paving 1.8406 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Total 2.1746 10.0395 17.2957 0.0228 0.0374 0.0374 0.0374 0.0374 0.0000 2,207.584 1 2,207.584
1 0.7140 2,225.433
6 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.0535 0.0403 0.3985 1.0000e0030.1232 6.2000e0040.1238 0.0327 5.7000e0040.0333 100.8525 100.8525 3.8300e0033.6000e003102.0209 Total 0.0535 0.0403 0.3985 1.0000e0030.1232 6.2000e0040.1238 0.0327 5.7000e0040.0333 100.8525 100.8525 3.8300e0033.6000e003102.0209 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 15 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Architectural Coating - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 284.6958 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.1917 1.3030 1.8111 2.9700e0030.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690 Total 284.8874 1.3030 1.8111 2.9700e0030.0708 0.0708 0.0708 0.0708 281.4481 281.4481 0.0168 281.8690 Unmitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.1819 0.1369 1.3550 3.3900e0030.4190 2.1100e0030.4211 0.1111 1.9400e0030.1131 342.8985 342.8985 0.0130 0.0122 346.8709 Total 0.1819 0.1369 1.3550 3.3900e0030.4190 2.1100e0030.4211 0.1111 1.9400e0030.1131 342.8985 342.8985 0.0130 0.0122 346.8709 Unmitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 16 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
3.6 Architectural Coating - 2023
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Archit. Coating 284.6958 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Off-Road 0.0545 1.0598 1.8324 2.9700e0033.9600e0033.9600e0033.9600e0033.9600e0030.0000 281.4481 281.4481 0.0168 281.8690 Total 284.7503 1.0598 1.8324 2.9700e0033.9600e0033.9600e0033.9600e0033.9600e0030.0000 281.4481 281.4481 0.0168 281.8690 Mitigated Construction On-Site
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Hauling 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Vendor 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 Worker 0.1819 0.1369 1.3550 3.3900e0030.4190 2.1100e0030.4211 0.1111 1.9400e0030.1131 342.8985 342.8985 0.0130 0.0122 346.8709 Total 0.1819 0.1369 1.3550 3.3900e0030.4190 2.1100e0030.4211 0.1111 1.9400e0030.1131 342.8985 342.8985 0.0130 0.0122 346.8709 Mitigated Construction Off-Site
CalEEMod Version: CalEEMod.2020.4.0 Page 17 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
4.0 Operational Detail - Mobile
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 2.6642 4.9082 26.9440 0.0577 6.0062 0.0516 6.0578 1.6035 0.0485 1.6520 5,879.184 2 5,879.184
2 0.3549 0.3387 5,988.990
5 Unmitigated 2.6642 4.9082 26.9440 0.0577 6.0062 0.0516 6.0578 1.6035 0.0485 1.6520 5,879.184 2 5,879.184
2 0.3549 0.3387 5,988.990
5 4.1 Mitigation Measures Mobile
4.2 Trip Summary Information
4.3 Trip Type Information
Average Daily Trip Rate Unmitigated Mitigated
Land Use Weekday Saturday Sunday Annual VMT Annual VMT
City Park 2.74 6.88 7.69 8,617 8,617
Other Asphalt Surfaces 0.00 0.00 0.00
Single Family Housing 991.20 1,001.70 897.75 2,760,527 2,760,527 Total 993.94 1,008.58 905.44 2,769,145 2,769,145
Miles Trip % Trip Purpose %
Land Use H-W or C-W H-S or C-C H-O or C-NW H-W or C-W H-S or C-C H-O or C-NW Primary Diverted Pass-by City Park 9.50 7.30 7.30 33.00 48.00 19.00 66 28 6
Other Asphalt Surfaces 9.50 7.30 7.30 0.00 0.00 0.00 0 0 0 Single Family Housing 10.80 7.30 7.50 38.40 22.60 39.00 86 11 3 CalEEMod Version: CalEEMod.2020.4.0 Page 18 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
4.4 Fleet Mix
Land Use LDA LDT1 LDT2 MDV LHD1 LHD2 MHD HHD OBUS UBUS MCY SBUS MH City Park 0.509869 0.051139 0.167106 0.174849 0.031609 0.007996 0.012006 0.015707 0.000636 0.000471 0.023554 0.001465 0.003592 Other Asphalt Surfaces 0.509869 0.051139 0.167106 0.174849 0.031609 0.007996 0.012006 0.015707 0.000636 0.000471 0.023554 0.001465 0.003592 Single Family Housing 0.509869 0.051139 0.167106 0.174849 0.031609 0.007996 0.012006 0.015707 0.000636 0.000471 0.023554 0.001465 0.003592
5.0 Energy Detail
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
NaturalGas
Mitigated
0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 NaturalGas
Unmitigated
0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070
5.1 Mitigation Measures Energy
Historical Energy Use: N
CalEEMod Version: CalEEMod.2020.4.0 Page 19 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 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 Single Family
Housing
6835.94 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Total 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 20 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
6.1 Mitigation Measures Area
6.0 Area Detail
5.2 Energy by Land Use - NaturalGas
NaturalGa
s Use
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Land Use kBTU/yr lb/day lb/day
City Park 0 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 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 Single Family
Housing
6.83594 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Total 0.0737 0.6300 0.2681 4.0200e0030.0509 0.0509 0.0509 0.0509 804.2279 804.2279 0.0154 0.0147 809.0070 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 21 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
Category lb/day lb/day
Mitigated 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 Unmitigated 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
1.0140 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
4.1825 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.1121 0.9580 0.4077 6.1100e0030.0775 0.0775 0.0775 0.0775 0.0000 1,222.941 2 1,222.941
2 0.0234 0.0224 1,230.208
5 Landscaping 0.2605 0.0998 8.6602 4.6000e0040.0480 0.0480 0.0480 0.0480 15.6006 15.6006 0.0150 15.9749 Total 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 Unmitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 22 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
7.1 Mitigation Measures Water
7.0 Water Detail
6.2 Area by SubCategory
ROG NOx CO SO2 Fugitive
PM10
Exhaust
PM10
PM10
Total
Fugitive
PM2.5
Exhaust
PM2.5
PM2.5
Total
Bio- CO2 NBio- CO2 Total CO2 CH4 N2O CO2e
SubCategory lb/day lb/day
Architectural
Coating
1.0140 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Consumer
Products
4.1825 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000
Hearth 0.1121 0.9580 0.4077 6.1100e0030.0775 0.0775 0.0775 0.0775 0.0000 1,222.941 2 1,222.941
2 0.0234 0.0224 1,230.208
5 Landscaping 0.2605 0.0998 8.6602 4.6000e0040.0480 0.0480 0.0480 0.0480 15.6006 15.6006 0.0150 15.9749 Total 5.5691 1.0578 9.0679 6.5700e0030.1255 0.1255 0.1255 0.1255 0.0000 1,238.541 8 1,238.541
8 0.0384 0.0224 1,246.183
4 Mitigated
CalEEMod Version: CalEEMod.2020.4.0 Page 23 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
11.0 Vegetation
8.1 Mitigation Measures Waste
8.0 Waste Detail
9.0 Operational Offroad
Equipment Type Number Hours/Day Days/Year Horse Power Load Factor Fuel Type
10.0 Stationary Equipment
Fire Pumps and Emergency Generators
Equipment Type Number Hours/Day Hours/Year Horse Power Load Factor Fuel Type Boilers
Equipment Type Number Heat Input/Day Heat Input/Year Boiler Rating Fuel Type User Defined Equipment
Equipment Type Number
CalEEMod Version: CalEEMod.2020.4.0 Page 24 of 24 Date: 7/21/2021 4:27 PM Lombardi Development Phase 2 - Tulare County, Winter
EMFAC Off-Model Adjustment Factors for Gasoline Light Duty Vehicle to Account for the SAFE Vehicle Rule Not Applied
AIR QUALITY, GREENHOUSE GAS, AND ENERGY IMPACT ASSESSMENT
APPENDIX B
HEALTH RISK CALCULATIONS AND AERMOD OUTPUT FILES
**
****************************************
**
** AERMOD Input Produced by:
** AERMOD View Ver. 10.0.0
** Lakes Environmental Software Inc.
** Date: 7/23/2021
** File: C:\Lakes\AERMOD View\LombardiPorterville\LombardiPorterville.ADI **
****************************************
**
**
****************************************
** AERMOD Control Pathway
****************************************
**
**
CO STARTING
TITLEONE C:\Lakes\AERMOD View\LombardiPorterville\LombardiPorterville.isc
MODELOPT DFAULT CONC
AVERTIME 1 ANNUAL
URBANOPT 59988 Porterville,_CA
POLLUTID PM_2.5
RUNORNOT RUN
ERRORFIL LombardiPorterville.err
CO FINISHED
**
****************************************
** AERMOD Source Pathway
****************************************
**
**
SO STARTING
** Source Location **
** Source ID - Type - X Coord. - Y Coord. **
LOCATION PAREA1 AREAPOLY 313577.994 3996166.184 125.800 ** Source Parameters **
SRCPARAM PAREA1 1.4246E-08 3.000 13
AREAVERT PAREA1 313577.994 3996166.184 313563.335 3995657.628 AREAVERT PAREA1 313703.160 3995653.117 313704.288 3995698.222 AREAVERT PAREA1 313804.646 3995697.095 313802.390 3995655.373 AREAVERT PAREA1 313954.619 3995648.607 313955.747 3995897.811 AREAVERT PAREA1 313909.514 3995897.811 313911.769 3996035.380 AREAVERT PAREA1 313956.874 3996036.508 313961.385 3996256.394 AREAVERT PAREA1 313661.438 3996256.394
URBANSRC ALL
SRCGROUP ALL
SO FINISHED
**
****************************************
** AERMOD Receptor Pathway
****************************************
**
**
RE STARTING
INCLUDED LombardiPorterville.rou
RE FINISHED
**
****************************************
** AERMOD Meteorology Pathway
****************************************
**
**
ME STARTING
SURFFILE "C:\Users\kheck\Desktop\Porterville Met Data\Porterville_2006-2009.SFC" PROFFILE "C:\Users\kheck\Desktop\Porterville Met Data\Porterville_2006-2009.PFL" SURFDATA 23149 2006 Porterville
UAIRDATA 23230 2006 OAKLAND/WSO_AP
PROFBASE 135.0 METERS
ME FINISHED
**
****************************************
** AERMOD Output Pathway
****************************************
**
**
OU STARTING
RECTABLE ALLAVE 1ST
RECTABLE 1 1ST
** Auto-Generated Plotfiles
PLOTFILE 1 ALL 1ST LombardiPorterville.AD\01H1GALL.PLT 31 PLOTFILE ANNUAL ALL LombardiPorterville.AD\AN00GALL.PLT 32 SUMMFILE LombardiPorterville.sum
OU FINISHED
**
****************************************
** Project Parameters
****************************************
** PROJCTN CoordinateSystemUTM
** DESCPTN UTM: Universal Transverse Mercator
** DATUM World Geodetic System 1984
** DTMRGN Global Definition
** UNITS m
** ZONE 11
** ZONEINX 0
**
**
****************************************
**
** AERMOD Input Produced by:
** AERMOD View Ver. 10.0.0
** Lakes Environmental Software Inc.
** Date: 7/23/2021
** File: C:\Lakes\AERMOD View\LombardiPorterville\LombardiPorterville.ADI **
****************************************
**
**
****************************************
** AERMOD Control Pathway
****************************************
**
**
CO STARTING
TITLEONE C:\Lakes\AERMOD View\LombardiPorterville\LombardiPorterville.isc
MODELOPT DFAULT CONC
AVERTIME 1 ANNUAL
URBANOPT 59988 Porterville,_CA
POLLUTID PM_2.5
RUNORNOT RUN
ERRORFIL LombardiPorterville.err
CO FINISHED
**
****************************************
** AERMOD Source Pathway
****************************************
**
**
SO STARTING
** Source Location **
** Source ID - Type - X Coord. - Y Coord. **
LOCATION PAREA1 AREAPOLY 313577.994 3996166.184 125.800 ** Source Parameters **
SRCPARAM PAREA1 1.4246E-08 3.000 13
AREAVERT PAREA1 313577.994 3996166.184 313563.335 3995657.628 AREAVERT PAREA1 313703.160 3995653.117 313704.288 3995698.222 AREAVERT PAREA1 313804.646 3995697.095 313802.390 3995655.373 AREAVERT PAREA1 313954.619 3995648.607 313955.747 3995897.811 AREAVERT PAREA1 313909.514 3995897.811 313911.769 3996035.380 AREAVERT PAREA1 313956.874 3996036.508 313961.385 3996256.394 AREAVERT PAREA1 313661.438 3996256.394
URBANSRC ALL
SRCGROUP ALL
SO FINISHED
**
****************************************
** AERMOD Receptor Pathway
****************************************
**
**
RE STARTING
INCLUDED LombardiPorterville.rou
RE FINISHED
**
****************************************
** AERMOD Meteorology Pathway
****************************************
**
**
ME STARTING
SURFFILE "C:\Users\kheck\Desktop\Porterville Met Data\Porterville_2006-2009.SFC" PROFFILE "C:\Users\kheck\Desktop\Porterville Met Data\Porterville_2006-2009.PFL" SURFDATA 23149 2006 Porterville
UAIRDATA 23230 2006 OAKLAND/WSO_AP
PROFBASE 135.0 METERS
ME FINISHED
**
****************************************
** AERMOD Output Pathway
****************************************
**
**
OU STARTING
RECTABLE ALLAVE 1ST
RECTABLE 1 1ST
** Auto-Generated Plotfiles
PLOTFILE 1 ALL 1ST LombardiPorterville.AD\01H1GALL.PLT 31 PLOTFILE ANNUAL ALL LombardiPorterville.AD\AN00GALL.PLT 32 SUMMFILE LombardiPorterville.sum
OU FINISHED
*** Message Summary For AERMOD Model Setup ***
--------- Summary of Total Messages --------
A Total of 0 Fatal Error Message(s)
A Total of 1 Warning Message(s)
A Total of 0 Informational Message(s)
******** FATAL ERROR MESSAGES ********
*** NONE ***
******** WARNING MESSAGES ********
ME W187 70 MEOPEN: ADJ_U* Option for Stable Low Winds used in AERMET
***********************************
*** SETUP Finishes Successfully ***
***********************************
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 1
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** MODEL SETUP OPTIONS SUMMARY
***
- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -
**Model Is Setup For Calculation of Average CONCentration Values.
-- DEPOSITION LOGIC --
**NO GAS DEPOSITION Data Provided.
**NO PARTICLE DEPOSITION Data Provided.
**Model Uses NO DRY DEPLETION. DRYDPLT = F
**Model Uses NO WET DEPLETION. WETDPLT = F
**Model Uses URBAN Dispersion Algorithm for the SBL for 1 Source(s), for Total of 1 Urban Area(s):
Urban Population = 59988.0 ; Urban Roughness Length = 1.000 m
**Model Uses Regulatory DEFAULT Options:
1. Stack-tip Downwash.
2. Model Accounts for ELEVated Terrain Effects.
3. Use Calms Processing Routine.
4. Use Missing Data Processing Routine.
5. No Exponential Decay.
6. Urban Roughness Length of 1.0 Meter Assumed.
**Other Options Specified:
ADJ_U* - Use ADJ_U* option for SBL in AERMET
CCVR_Sub - Meteorological data includes CCVR substitutions TEMP_Sub - Meteorological data includes TEMP substitutions
**Model Assumes No FLAGPOLE Receptor Heights.
**The User Specified a Pollutant Type of: PM_2.5
**Model Calculates 1 Short Term Average(s) of: 1-HR
and Calculates ANNUAL Averages
**This Run Includes: 1 Source(s); 1 Source Group(s); and 1934 Receptor(s)
with: 0 POINT(s), including
0 POINTCAP(s) and 0 POINTHOR(s)
and: 0 VOLUME source(s)
and: 1 AREA type source(s)
and: 0 LINE source(s)
and: 0 RLINE/RLINEXT source(s)
and: 0 OPENPIT source(s)
and: 0 BUOYANT LINE source(s) with a total of 0 line(s)
**Model Set To Continue RUNning After the Setup Testing. **The AERMET Input Meteorological Data Version Date: 18081
**Output Options Selected:
Model Outputs Tables of ANNUAL Averages by Receptor
Model Outputs Tables of Highest Short Term Values by Receptor (RECTABLE Keyword)
Model Outputs External File(s) of High Values for Plotting (PLOTFILE Keyword)
Model Outputs Separate Summary File of High Ranked Values (SUMMFILE Keyword)
**NOTE: The Following Flags May Appear Following CONC Values: c for Calm Hours m for Missing Hours
b for Both Calm and
Missing Hours
**Misc. Inputs: Base Elev. for Pot. Temp. Profile (m MSL) = 135.00 ; Decay Coef. = 0.000 ; Rot. Angle = 0.0
Emission Units = GRAMS/SEC ;
Emission Rate Unit Factor = 0.10000E+07
Output Units = MICROGRAMS/M**3
**Approximate Storage Requirements of Model = 3.7 MB of RAM.
**Input Runstream File: aermod.inp
**Output Print File: aermod.out
**Detailed Error/Message File: LombardiPorterville.err
**File for Summary of Results: LombardiPorterville.sum
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 2
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** AREAPOLY SOURCE DATA ***
NUMBER EMISSION RATE LOCATION OF AREA BASE RELEASE NUMBER INIT. URBAN EMISSION RATE
SOURCE PART. (GRAMS/SEC X Y ELEV. HEIGHT OF VERTS.
SZ SOURCE SCALAR VARY
ID CATS. /METER**2) (METERS) (METERS) (METERS) (METERS) (METERS) BY
- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -
PAREA1 0 0.14246E-07 313578.0 3996166.2 125.8 3.00 13
0.00 YES
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 3
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** SOURCE IDs DEFINING SOURCE GROUPS ***
SRCGROUP ID SOURCE IDs
----------- ----------
ALL PAREA1 ,
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 4
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** SOURCE IDs DEFINED AS URBAN SOURCES
***
URBAN ID URBAN POP SOURCE IDs
-------- --------- ----------
59988. PAREA1 ,
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 5
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313271.5, 3995341.5, 126.0, 126.0, 0.0); ( 313291.5,
3995341.5, 126.0, 126.0, 0.0);
( 313311.5, 3995341.5, 126.1, 126.1, 0.0); ( 313331.5,
3995341.5, 126.1, 126.1, 0.0);
( 313351.5, 3995341.5, 126.1, 126.1, 0.0); ( 313371.5,
3995341.5, 126.1, 126.1, 0.0);
( 313391.5, 3995341.5, 126.2, 126.2, 0.0); ( 313411.5,
3995341.5, 126.2, 126.2, 0.0);
( 313431.5, 3995341.5, 126.2, 126.2, 0.0); ( 313451.5,
3995341.5, 126.3, 126.3, 0.0);
( 313471.5, 3995341.5, 126.3, 126.3, 0.0); ( 313491.5,
3995341.5, 126.3, 126.3, 0.0);
( 313511.5, 3995341.5, 126.4, 126.4, 0.0); ( 313531.5,
3995341.5, 126.4, 126.4, 0.0);
( 313551.5, 3995341.5, 126.4, 126.4, 0.0); ( 313571.5,
3995341.5, 126.5, 126.5, 0.0);
( 313591.5, 3995341.5, 126.5, 126.5, 0.0); ( 313611.5,
3995341.5, 126.5, 126.5, 0.0);
( 313631.5, 3995341.5, 126.5, 126.5, 0.0); ( 313651.5,
3995341.5, 126.6, 126.6, 0.0);
( 313671.5, 3995341.5, 126.6, 126.6, 0.0); ( 313691.5,
3995341.5, 126.6, 126.6, 0.0);
( 313711.5, 3995341.5, 126.7, 126.7, 0.0); ( 313731.5,
3995341.5, 126.7, 126.7, 0.0);
( 313751.5, 3995341.5, 126.7, 126.7, 0.0); ( 313771.5,
3995341.5, 126.7, 126.7, 0.0);
( 313791.5, 3995341.5, 126.8, 126.8, 0.0); ( 313811.5,
3995341.5, 126.8, 126.8, 0.0);
( 313831.5, 3995341.5, 126.8, 126.8, 0.0); ( 313851.5,
3995341.5, 126.8, 126.8, 0.0);
( 313871.5, 3995341.5, 126.9, 126.9, 0.0); ( 313891.5,
3995341.5, 126.9, 126.9, 0.0);
( 313911.5, 3995341.5, 126.9, 126.9, 0.0); ( 313931.5,
3995341.5, 127.0, 127.0, 0.0);
( 313951.5, 3995341.5, 127.0, 127.0, 0.0); ( 313971.5,
3995341.5, 127.0, 127.0, 0.0);
( 313991.5, 3995341.5, 127.0, 127.0, 0.0); ( 314011.5,
3995341.5, 127.0, 127.0, 0.0);
( 314031.5, 3995341.5, 127.0, 127.0, 0.0); ( 314051.5,
3995341.5, 127.0, 127.0, 0.0);
( 314071.5, 3995341.5, 127.1, 127.1, 0.0); ( 314091.5,
3995341.5, 127.1, 127.1, 0.0);
( 314111.5, 3995341.5, 127.1, 127.1, 0.0); ( 314131.5,
3995341.5, 127.1, 127.1, 0.0);
( 314151.5, 3995341.5, 127.1, 127.1, 0.0); ( 314171.5,
3995341.5, 127.1, 127.1, 0.0);
( 314191.5, 3995341.5, 127.1, 127.1, 0.0); ( 314211.5,
3995341.5, 127.2, 127.2, 0.0);
( 314231.5, 3995341.5, 127.2, 127.2, 0.0); ( 314251.5,
3995341.5, 127.2, 127.2, 0.0);
( 314271.5, 3995341.5, 127.2, 127.2, 0.0); ( 313271.5,
3995361.5, 126.0, 126.0, 0.0);
( 313291.5, 3995361.5, 126.0, 126.0, 0.0); ( 313311.5,
3995361.5, 126.0, 126.0, 0.0);
( 313331.5, 3995361.5, 126.1, 126.1, 0.0); ( 313351.5,
3995361.5, 126.1, 126.1, 0.0);
( 313371.5, 3995361.5, 126.1, 126.1, 0.0); ( 313391.5,
3995361.5, 126.1, 126.1, 0.0);
( 313411.5, 3995361.5, 126.2, 126.2, 0.0); ( 313431.5,
3995361.5, 126.2, 126.2, 0.0);
( 313451.5, 3995361.5, 126.2, 126.2, 0.0); ( 313471.5,
3995361.5, 126.3, 126.3, 0.0);
( 313491.5, 3995361.5, 126.3, 126.3, 0.0); ( 313511.5,
3995361.5, 126.3, 126.3, 0.0);
( 313531.5, 3995361.5, 126.3, 126.3, 0.0); ( 313551.5,
3995361.5, 126.4, 126.4, 0.0);
( 313571.5, 3995361.5, 126.4, 126.4, 0.0); ( 313591.5,
3995361.5, 126.4, 126.4, 0.0);
( 313611.5, 3995361.5, 126.5, 126.5, 0.0); ( 313631.5,
3995361.5, 126.5, 126.5, 0.0);
( 313651.5, 3995361.5, 126.5, 126.5, 0.0); ( 313671.5,
3995361.5, 126.5, 126.5, 0.0);
( 313691.5, 3995361.5, 126.6, 126.6, 0.0); ( 313711.5,
3995361.5, 126.6, 126.6, 0.0);
( 313731.5, 3995361.5, 126.6, 126.6, 0.0); ( 313751.5,
3995361.5, 126.7, 126.7, 0.0);
( 313771.5, 3995361.5, 126.7, 126.7, 0.0); ( 313791.5,
3995361.5, 126.7, 126.7, 0.0);
( 313811.5, 3995361.5, 126.8, 126.8, 0.0); ( 313831.5,
3995361.5, 126.8, 126.8, 0.0);
( 313851.5, 3995361.5, 126.8, 126.8, 0.0); ( 313871.5,
3995361.5, 126.8, 126.8, 0.0);
( 313891.5, 3995361.5, 126.9, 126.9, 0.0); ( 313911.5,
3995361.5, 126.9, 126.9, 0.0);
( 313931.5, 3995361.5, 126.9, 126.9, 0.0); ( 313951.5,
3995361.5, 126.9, 126.9, 0.0);
( 313971.5, 3995361.5, 126.9, 126.9, 0.0); ( 313991.5,
3995361.5, 127.0, 127.0, 0.0);
( 314011.5, 3995361.5, 127.0, 127.0, 0.0); ( 314031.5,
3995361.5, 127.0, 127.0, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 6
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 314051.5, 3995361.5, 127.0, 127.0, 0.0); ( 314071.5,
3995361.5, 127.0, 127.0, 0.0);
( 314091.5, 3995361.5, 127.0, 127.0, 0.0); ( 314111.5,
3995361.5, 127.1, 127.1, 0.0);
( 314131.5, 3995361.5, 127.1, 127.1, 0.0); ( 314151.5,
3995361.5, 127.1, 127.1, 0.0);
( 314171.5, 3995361.5, 127.1, 127.1, 0.0); ( 314191.5,
3995361.5, 127.1, 127.1, 0.0);
( 314211.5, 3995361.5, 127.1, 127.1, 0.0); ( 314231.5,
3995361.5, 127.2, 127.2, 0.0);
( 314251.5, 3995361.5, 127.2, 127.2, 0.0); ( 314271.5,
3995361.5, 127.2, 127.2, 0.0);
( 313271.5, 3995381.5, 126.0, 126.0, 0.0); ( 313291.5,
3995381.5, 126.0, 126.0, 0.0);
( 313311.5, 3995381.5, 126.0, 126.0, 0.0); ( 313331.5,
3995381.5, 126.0, 126.0, 0.0);
( 313351.5, 3995381.5, 126.0, 126.0, 0.0); ( 313371.5,
3995381.5, 126.1, 126.1, 0.0);
( 313391.5, 3995381.5, 126.1, 126.1, 0.0); ( 313411.5,
3995381.5, 126.1, 126.1, 0.0);
( 313431.5, 3995381.5, 126.2, 126.2, 0.0); ( 313451.5,
3995381.5, 126.2, 126.2, 0.0);
( 313471.5, 3995381.5, 126.2, 126.2, 0.0); ( 313491.5,
3995381.5, 126.2, 126.2, 0.0);
( 313511.5, 3995381.5, 126.3, 126.3, 0.0); ( 313531.5,
3995381.5, 126.3, 126.3, 0.0);
( 313551.5, 3995381.5, 126.3, 126.3, 0.0); ( 313571.5,
3995381.5, 126.4, 126.4, 0.0);
( 313591.5, 3995381.5, 126.4, 126.4, 0.0); ( 313611.5,
3995381.5, 126.4, 126.4, 0.0);
( 313631.5, 3995381.5, 126.5, 126.5, 0.0); ( 313651.5,
3995381.5, 126.5, 126.5, 0.0);
( 313671.5, 3995381.5, 126.5, 126.5, 0.0); ( 313691.5,
3995381.5, 126.5, 126.5, 0.0);
( 313711.5, 3995381.5, 126.6, 126.6, 0.0); ( 313731.5,
3995381.5, 126.6, 126.6, 0.0);
( 313751.5, 3995381.5, 126.6, 126.6, 0.0); ( 313771.5,
3995381.5, 126.7, 126.7, 0.0);
( 313791.5, 3995381.5, 126.7, 126.7, 0.0); ( 313811.5,
3995381.5, 126.7, 126.7, 0.0);
( 313831.5, 3995381.5, 126.7, 126.7, 0.0); ( 313851.5,
3995381.5, 126.8, 126.8, 0.0);
( 313871.5, 3995381.5, 126.8, 126.8, 0.0); ( 313891.5,
3995381.5, 126.8, 126.8, 0.0);
( 313911.5, 3995381.5, 126.8, 126.8, 0.0); ( 313931.5,
3995381.5, 126.8, 126.8, 0.0);
( 313951.5, 3995381.5, 126.9, 126.9, 0.0); ( 313971.5,
3995381.5, 126.9, 126.9, 0.0);
( 313991.5, 3995381.5, 126.9, 126.9, 0.0); ( 314011.5,
3995381.5, 126.9, 126.9, 0.0);
( 314031.5, 3995381.5, 127.0, 127.0, 0.0); ( 314051.5,
3995381.5, 127.0, 127.0, 0.0);
( 314071.5, 3995381.5, 127.0, 127.0, 0.0); ( 314091.5,
3995381.5, 127.0, 127.0, 0.0);
( 314111.5, 3995381.5, 127.0, 127.0, 0.0); ( 314131.5,
3995381.5, 127.0, 127.0, 0.0);
( 314151.5, 3995381.5, 127.1, 127.1, 0.0); ( 314171.5,
3995381.5, 127.1, 127.1, 0.0);
( 314191.5, 3995381.5, 127.1, 127.1, 0.0); ( 314211.5,
3995381.5, 127.1, 127.1, 0.0);
( 314231.5, 3995381.5, 127.1, 127.1, 0.0); ( 314251.5,
3995381.5, 127.2, 127.2, 0.0);
( 314271.5, 3995381.5, 127.2, 127.2, 0.0); ( 313271.5,
3995401.5, 125.9, 125.9, 0.0);
( 313291.5, 3995401.5, 125.9, 125.9, 0.0); ( 313311.5,
3995401.5, 126.0, 126.0, 0.0);
( 313331.5, 3995401.5, 126.0, 126.0, 0.0); ( 313351.5,
3995401.5, 126.0, 126.0, 0.0);
( 313371.5, 3995401.5, 126.0, 126.0, 0.0); ( 313391.5,
3995401.5, 126.1, 126.1, 0.0);
( 313411.5, 3995401.5, 126.1, 126.1, 0.0); ( 313431.5,
3995401.5, 126.1, 126.1, 0.0);
( 313451.5, 3995401.5, 126.1, 126.1, 0.0); ( 313471.5,
3995401.5, 126.2, 126.2, 0.0);
( 313491.5, 3995401.5, 126.2, 126.2, 0.0); ( 313511.5,
3995401.5, 126.2, 126.2, 0.0);
( 313531.5, 3995401.5, 126.3, 126.3, 0.0); ( 313551.5,
3995401.5, 126.3, 126.3, 0.0);
( 313571.5, 3995401.5, 126.3, 126.3, 0.0); ( 313591.5,
3995401.5, 126.4, 126.4, 0.0);
( 313611.5, 3995401.5, 126.4, 126.4, 0.0); ( 313631.5,
3995401.5, 126.4, 126.4, 0.0);
( 313651.5, 3995401.5, 126.4, 126.4, 0.0); ( 313671.5,
3995401.5, 126.5, 126.5, 0.0);
( 313691.5, 3995401.5, 126.5, 126.5, 0.0); ( 313711.5,
3995401.5, 126.5, 126.5, 0.0);
( 313731.5, 3995401.5, 126.6, 126.6, 0.0); ( 313751.5,
3995401.5, 126.6, 126.6, 0.0);
( 313771.5, 3995401.5, 126.6, 126.6, 0.0); ( 313791.5,
3995401.5, 126.6, 126.6, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 7
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313811.5, 3995401.5, 126.7, 126.7, 0.0); ( 313831.5,
3995401.5, 126.7, 126.7, 0.0);
( 313851.5, 3995401.5, 126.7, 126.7, 0.0); ( 313871.5,
3995401.5, 126.7, 126.7, 0.0);
( 313891.5, 3995401.5, 126.8, 126.8, 0.0); ( 313911.5,
3995401.5, 126.8, 126.8, 0.0);
( 313931.5, 3995401.5, 126.8, 126.8, 0.0); ( 313951.5,
3995401.5, 126.8, 126.8, 0.0);
( 313971.5, 3995401.5, 126.8, 126.8, 0.0); ( 313991.5,
3995401.5, 126.9, 126.9, 0.0);
( 314011.5, 3995401.5, 126.9, 126.9, 0.0); ( 314031.5,
3995401.5, 126.9, 126.9, 0.0);
( 314051.5, 3995401.5, 126.9, 126.9, 0.0); ( 314071.5,
3995401.5, 127.0, 127.0, 0.0);
( 314091.5, 3995401.5, 127.0, 127.0, 0.0); ( 314111.5,
3995401.5, 127.0, 127.0, 0.0);
( 314131.5, 3995401.5, 127.0, 127.0, 0.0); ( 314151.5,
3995401.5, 127.0, 127.0, 0.0);
( 314171.5, 3995401.5, 127.0, 127.0, 0.0); ( 314191.5,
3995401.5, 127.1, 127.1, 0.0);
( 314211.5, 3995401.5, 127.1, 127.1, 0.0); ( 314231.5,
3995401.5, 127.1, 127.1, 0.0);
( 314251.5, 3995401.5, 127.1, 127.1, 0.0); ( 314271.5,
3995401.5, 127.2, 127.2, 0.0);
( 313271.5, 3995421.5, 125.9, 125.9, 0.0); ( 313291.5,
3995421.5, 125.9, 125.9, 0.0);
( 313311.5, 3995421.5, 125.9, 125.9, 0.0); ( 313331.5,
3995421.5, 126.0, 126.0, 0.0);
( 313351.5, 3995421.5, 126.0, 126.0, 0.0); ( 313371.5,
3995421.5, 126.0, 126.0, 0.0);
( 313391.5, 3995421.5, 126.0, 126.0, 0.0); ( 313411.5,
3995421.5, 126.1, 126.1, 0.0);
( 313431.5, 3995421.5, 126.1, 126.1, 0.0); ( 313451.5,
3995421.5, 126.1, 126.1, 0.0);
( 313471.5, 3995421.5, 126.1, 126.1, 0.0); ( 313491.5,
3995421.5, 126.2, 126.2, 0.0);
( 313511.5, 3995421.5, 126.2, 126.2, 0.0); ( 313531.5,
3995421.5, 126.2, 126.2, 0.0);
( 313551.5, 3995421.5, 126.3, 126.3, 0.0); ( 313571.5,
3995421.5, 126.3, 126.3, 0.0);
( 313591.5, 3995421.5, 126.3, 126.3, 0.0); ( 313611.5,
3995421.5, 126.3, 126.3, 0.0);
( 313631.5, 3995421.5, 126.4, 126.4, 0.0); ( 313651.5,
3995421.5, 126.4, 126.4, 0.0);
( 313671.5, 3995421.5, 126.4, 126.4, 0.0); ( 313691.5,
3995421.5, 126.5, 126.5, 0.0);
( 313711.5, 3995421.5, 126.5, 126.5, 0.0); ( 313731.5,
3995421.5, 126.5, 126.5, 0.0);
( 313751.5, 3995421.5, 126.5, 126.5, 0.0); ( 313771.5,
3995421.5, 126.6, 126.6, 0.0);
( 313791.5, 3995421.5, 126.6, 126.6, 0.0); ( 313811.5,
3995421.5, 126.6, 126.6, 0.0);
( 313831.5, 3995421.5, 126.6, 126.6, 0.0); ( 313851.5,
3995421.5, 126.7, 126.7, 0.0);
( 313871.5, 3995421.5, 126.7, 126.7, 0.0); ( 313891.5,
3995421.5, 126.7, 126.7, 0.0);
( 313911.5, 3995421.5, 126.7, 126.7, 0.0); ( 313931.5,
3995421.5, 126.8, 126.8, 0.0);
( 313951.5, 3995421.5, 126.8, 126.8, 0.0); ( 313971.5,
3995421.5, 126.8, 126.8, 0.0);
( 313991.5, 3995421.5, 126.8, 126.8, 0.0); ( 314011.5,
3995421.5, 126.8, 126.8, 0.0);
( 314031.5, 3995421.5, 126.9, 126.9, 0.0); ( 314051.5,
3995421.5, 126.9, 126.9, 0.0);
( 314071.5, 3995421.5, 126.9, 126.9, 0.0); ( 314091.5,
3995421.5, 126.9, 126.9, 0.0);
( 314111.5, 3995421.5, 127.0, 127.0, 0.0); ( 314131.5,
3995421.5, 127.0, 127.0, 0.0);
( 314151.5, 3995421.5, 127.0, 127.0, 0.0); ( 314171.5,
3995421.5, 127.0, 127.0, 0.0);
( 314191.5, 3995421.5, 127.0, 127.0, 0.0); ( 314211.5,
3995421.5, 127.1, 127.1, 0.0);
( 314231.5, 3995421.5, 127.1, 127.1, 0.0); ( 314251.5,
3995421.5, 127.1, 127.1, 0.0);
( 314271.5, 3995421.5, 127.1, 127.1, 0.0); ( 313271.5,
3995441.5, 125.8, 125.8, 0.0);
( 313291.5, 3995441.5, 125.9, 125.9, 0.0); ( 313311.5,
3995441.5, 125.9, 125.9, 0.0);
( 313331.5, 3995441.5, 125.9, 125.9, 0.0); ( 313351.5,
3995441.5, 126.0, 126.0, 0.0);
( 313371.5, 3995441.5, 126.0, 126.0, 0.0); ( 313391.5,
3995441.5, 126.0, 126.0, 0.0);
( 313411.5, 3995441.5, 126.0, 126.0, 0.0); ( 313431.5,
3995441.5, 126.0, 126.0, 0.0);
( 313451.5, 3995441.5, 126.1, 126.1, 0.0); ( 313471.5,
3995441.5, 126.1, 126.1, 0.0);
( 313491.5, 3995441.5, 126.1, 126.1, 0.0); ( 313511.5,
3995441.5, 126.2, 126.2, 0.0);
( 313531.5, 3995441.5, 126.2, 126.2, 0.0); ( 313551.5,
3995441.5, 126.2, 126.2, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 8
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313571.5, 3995441.5, 126.2, 126.2, 0.0); ( 313591.5,
3995441.5, 126.3, 126.3, 0.0);
( 313611.5, 3995441.5, 126.3, 126.3, 0.0); ( 313631.5,
3995441.5, 126.3, 126.3, 0.0);
( 313651.5, 3995441.5, 126.4, 126.4, 0.0); ( 313671.5,
3995441.5, 126.4, 126.4, 0.0);
( 313691.5, 3995441.5, 126.4, 126.4, 0.0); ( 313711.5,
3995441.5, 126.4, 126.4, 0.0);
( 313731.5, 3995441.5, 126.5, 126.5, 0.0); ( 313751.5,
3995441.5, 126.5, 126.5, 0.0);
( 313771.5, 3995441.5, 126.5, 126.5, 0.0); ( 313791.5,
3995441.5, 126.5, 126.5, 0.0);
( 313811.5, 3995441.5, 126.6, 126.6, 0.0); ( 313831.5,
3995441.5, 126.6, 126.6, 0.0);
( 313851.5, 3995441.5, 126.6, 126.6, 0.0); ( 313871.5,
3995441.5, 126.6, 126.6, 0.0);
( 313891.5, 3995441.5, 126.7, 126.7, 0.0); ( 313911.5,
3995441.5, 126.7, 126.7, 0.0);
( 313931.5, 3995441.5, 126.7, 126.7, 0.0); ( 313951.5,
3995441.5, 126.7, 126.7, 0.0);
( 313971.5, 3995441.5, 126.8, 126.8, 0.0); ( 313991.5,
3995441.5, 126.8, 126.8, 0.0);
( 314011.5, 3995441.5, 126.8, 126.8, 0.0); ( 314031.5,
3995441.5, 126.8, 126.8, 0.0);
( 314051.5, 3995441.5, 126.8, 126.8, 0.0); ( 314071.5,
3995441.5, 126.9, 126.9, 0.0);
( 314091.5, 3995441.5, 126.9, 126.9, 0.0); ( 314111.5,
3995441.5, 126.9, 126.9, 0.0);
( 314131.5, 3995441.5, 126.9, 126.9, 0.0); ( 314151.5,
3995441.5, 127.0, 127.0, 0.0);
( 314171.5, 3995441.5, 127.0, 127.0, 0.0); ( 314191.5,
3995441.5, 127.0, 127.0, 0.0);
( 314211.5, 3995441.5, 127.0, 127.0, 0.0); ( 314231.5,
3995441.5, 127.1, 127.1, 0.0);
( 314251.5, 3995441.5, 127.1, 127.1, 0.0); ( 314271.5,
3995441.5, 127.1, 127.1, 0.0);
( 313271.5, 3995461.5, 125.8, 125.8, 0.0); ( 313291.5,
3995461.5, 125.8, 125.8, 0.0);
( 313311.5, 3995461.5, 125.9, 125.9, 0.0); ( 313331.5,
3995461.5, 125.9, 125.9, 0.0);
( 313351.5, 3995461.5, 125.9, 125.9, 0.0); ( 313371.5,
3995461.5, 125.9, 125.9, 0.0);
( 313391.5, 3995461.5, 126.0, 126.0, 0.0); ( 313411.5,
3995461.5, 126.0, 126.0, 0.0);
( 313431.5, 3995461.5, 126.0, 126.0, 0.0); ( 313451.5,
3995461.5, 126.0, 126.0, 0.0);
( 313471.5, 3995461.5, 126.1, 126.1, 0.0); ( 313491.5,
3995461.5, 126.1, 126.1, 0.0);
( 313511.5, 3995461.5, 126.1, 126.1, 0.0); ( 313531.5,
3995461.5, 126.1, 126.1, 0.0);
( 313551.5, 3995461.5, 126.2, 126.2, 0.0); ( 313571.5,
3995461.5, 126.2, 126.2, 0.0);
( 313591.5, 3995461.5, 126.2, 126.2, 0.0); ( 313611.5,
3995461.5, 126.3, 126.3, 0.0);
( 313631.5, 3995461.5, 126.3, 126.3, 0.0); ( 313651.5,
3995461.5, 126.3, 126.3, 0.0);
( 313671.5, 3995461.5, 126.3, 126.3, 0.0); ( 313691.5,
3995461.5, 126.4, 126.4, 0.0);
( 313711.5, 3995461.5, 126.4, 126.4, 0.0); ( 313731.5,
3995461.5, 126.4, 126.4, 0.0);
( 313751.5, 3995461.5, 126.5, 126.5, 0.0); ( 313771.5,
3995461.5, 126.5, 126.5, 0.0);
( 313791.5, 3995461.5, 126.5, 126.5, 0.0); ( 313811.5,
3995461.5, 126.5, 126.5, 0.0);
( 313831.5, 3995461.5, 126.6, 126.6, 0.0); ( 313851.5,
3995461.5, 126.6, 126.6, 0.0);
( 313871.5, 3995461.5, 126.6, 126.6, 0.0); ( 313891.5,
3995461.5, 126.6, 126.6, 0.0);
( 313911.5, 3995461.5, 126.6, 126.6, 0.0); ( 313931.5,
3995461.5, 126.7, 126.7, 0.0);
( 313951.5, 3995461.5, 126.7, 126.7, 0.0); ( 313971.5,
3995461.5, 126.7, 126.7, 0.0);
( 313991.5, 3995461.5, 126.7, 126.7, 0.0); ( 314011.5,
3995461.5, 126.8, 126.8, 0.0);
( 314031.5, 3995461.5, 126.8, 126.8, 0.0); ( 314051.5,
3995461.5, 126.8, 126.8, 0.0);
( 314071.5, 3995461.5, 126.8, 126.8, 0.0); ( 314091.5,
3995461.5, 126.9, 126.9, 0.0);
( 314111.5, 3995461.5, 126.9, 126.9, 0.0); ( 314131.5,
3995461.5, 126.9, 126.9, 0.0);
( 314151.5, 3995461.5, 126.9, 126.9, 0.0); ( 314171.5,
3995461.5, 127.0, 127.0, 0.0);
( 314191.5, 3995461.5, 127.0, 127.0, 0.0); ( 314211.5,
3995461.5, 127.0, 127.0, 0.0);
( 314231.5, 3995461.5, 127.0, 127.0, 0.0); ( 314251.5,
3995461.5, 127.1, 127.1, 0.0);
( 314271.5, 3995461.5, 127.1, 127.1, 0.0); ( 313271.5,
3995481.5, 125.8, 125.8, 0.0);
( 313291.5, 3995481.5, 125.8, 125.8, 0.0); ( 313311.5,
3995481.5, 125.8, 125.8, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 9
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313331.5, 3995481.5, 125.8, 125.8, 0.0); ( 313351.5,
3995481.5, 125.9, 125.9, 0.0);
( 313371.5, 3995481.5, 125.9, 125.9, 0.0); ( 313391.5,
3995481.5, 125.9, 125.9, 0.0);
( 313411.5, 3995481.5, 126.0, 126.0, 0.0); ( 313431.5,
3995481.5, 126.0, 126.0, 0.0);
( 313451.5, 3995481.5, 126.0, 126.0, 0.0); ( 313471.5,
3995481.5, 126.0, 126.0, 0.0);
( 313491.5, 3995481.5, 126.1, 126.1, 0.0); ( 313511.5,
3995481.5, 126.1, 126.1, 0.0);
( 313531.5, 3995481.5, 126.1, 126.1, 0.0); ( 313551.5,
3995481.5, 126.1, 126.1, 0.0);
( 313571.5, 3995481.5, 126.2, 126.2, 0.0); ( 313591.5,
3995481.5, 126.2, 126.2, 0.0);
( 313611.5, 3995481.5, 126.2, 126.2, 0.0); ( 313631.5,
3995481.5, 126.3, 126.3, 0.0);
( 313651.5, 3995481.5, 126.3, 126.3, 0.0); ( 313671.5,
3995481.5, 126.3, 126.3, 0.0);
( 313691.5, 3995481.5, 126.3, 126.3, 0.0); ( 313711.5,
3995481.5, 126.3, 126.3, 0.0);
( 313731.5, 3995481.5, 126.4, 126.4, 0.0); ( 313751.5,
3995481.5, 126.4, 126.4, 0.0);
( 313771.5, 3995481.5, 126.4, 126.4, 0.0); ( 313791.5,
3995481.5, 126.5, 126.5, 0.0);
( 313811.5, 3995481.5, 126.5, 126.5, 0.0); ( 313831.5,
3995481.5, 126.5, 126.5, 0.0);
( 313851.5, 3995481.5, 126.5, 126.5, 0.0); ( 313871.5,
3995481.5, 126.6, 126.6, 0.0);
( 313891.5, 3995481.5, 126.6, 126.6, 0.0); ( 313911.5,
3995481.5, 126.6, 126.6, 0.0);
( 313931.5, 3995481.5, 126.6, 126.6, 0.0); ( 313951.5,
3995481.5, 126.6, 126.6, 0.0);
( 313971.5, 3995481.5, 126.7, 126.7, 0.0); ( 313991.5,
3995481.5, 126.7, 126.7, 0.0);
( 314011.5, 3995481.5, 126.7, 126.7, 0.0); ( 314031.5,
3995481.5, 126.8, 126.8, 0.0);
( 314051.5, 3995481.5, 126.8, 126.8, 0.0); ( 314071.5,
3995481.5, 126.8, 126.8, 0.0);
( 314091.5, 3995481.5, 126.8, 126.8, 0.0); ( 314111.5,
3995481.5, 126.8, 126.8, 0.0);
( 314131.5, 3995481.5, 126.9, 126.9, 0.0); ( 314151.5,
3995481.5, 126.9, 126.9, 0.0);
( 314171.5, 3995481.5, 126.9, 126.9, 0.0); ( 314191.5,
3995481.5, 126.9, 126.9, 0.0);
( 314211.5, 3995481.5, 127.0, 127.0, 0.0); ( 314231.5,
3995481.5, 127.0, 127.0, 0.0);
( 314251.5, 3995481.5, 127.0, 127.0, 0.0); ( 314271.5,
3995481.5, 127.1, 127.1, 0.0);
( 313271.5, 3995501.5, 125.8, 125.8, 0.0); ( 313291.5,
3995501.5, 125.8, 125.8, 0.0);
( 313311.5, 3995501.5, 125.8, 125.8, 0.0); ( 313331.5,
3995501.5, 125.8, 125.8, 0.0);
( 313351.5, 3995501.5, 125.8, 125.8, 0.0); ( 313371.5,
3995501.5, 125.9, 125.9, 0.0);
( 313391.5, 3995501.5, 125.9, 125.9, 0.0); ( 313411.5,
3995501.5, 125.9, 125.9, 0.0);
( 313431.5, 3995501.5, 126.0, 126.0, 0.0); ( 313451.5,
3995501.5, 126.0, 126.0, 0.0);
( 313471.5, 3995501.5, 126.0, 126.0, 0.0); ( 313491.5,
3995501.5, 126.0, 126.0, 0.0);
( 313511.5, 3995501.5, 126.0, 126.0, 0.0); ( 313531.5,
3995501.5, 126.1, 126.1, 0.0);
( 313551.5, 3995501.5, 126.1, 126.1, 0.0); ( 313571.5,
3995501.5, 126.1, 126.1, 0.0);
( 313591.5, 3995501.5, 126.2, 126.2, 0.0); ( 313611.5,
3995501.5, 126.2, 126.2, 0.0);
( 313631.5, 3995501.5, 126.2, 126.2, 0.0); ( 313651.5,
3995501.5, 126.2, 126.2, 0.0);
( 313671.5, 3995501.5, 126.3, 126.3, 0.0); ( 313691.5,
3995501.5, 126.3, 126.3, 0.0);
( 313711.5, 3995501.5, 126.3, 126.3, 0.0); ( 313731.5,
3995501.5, 126.3, 126.3, 0.0);
( 313751.5, 3995501.5, 126.4, 126.4, 0.0); ( 313771.5,
3995501.5, 126.4, 126.4, 0.0);
( 313791.5, 3995501.5, 126.4, 126.4, 0.0); ( 313811.5,
3995501.5, 126.5, 126.5, 0.0);
( 313831.5, 3995501.5, 126.5, 126.5, 0.0); ( 313851.5,
3995501.5, 126.5, 126.5, 0.0);
( 313871.5, 3995501.5, 126.5, 126.5, 0.0); ( 313891.5,
3995501.5, 126.5, 126.5, 0.0);
( 313911.5, 3995501.5, 126.6, 126.6, 0.0); ( 313931.5,
3995501.5, 126.6, 126.6, 0.0);
( 313951.5, 3995501.5, 126.6, 126.6, 0.0); ( 313971.5,
3995501.5, 126.6, 126.6, 0.0);
( 313991.5, 3995501.5, 126.7, 126.7, 0.0); ( 314011.5,
3995501.5, 126.7, 126.7, 0.0);
( 314031.5, 3995501.5, 126.7, 126.7, 0.0); ( 314051.5,
3995501.5, 126.7, 126.7, 0.0);
( 314071.5, 3995501.5, 126.8, 126.8, 0.0); ( 314091.5,
3995501.5, 126.8, 126.8, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 10
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 314111.5, 3995501.5, 126.8, 126.8, 0.0); ( 314131.5,
3995501.5, 126.8, 126.8, 0.0);
( 314151.5, 3995501.5, 126.9, 126.9, 0.0); ( 314171.5,
3995501.5, 126.9, 126.9, 0.0);
( 314191.5, 3995501.5, 126.9, 126.9, 0.0); ( 314211.5,
3995501.5, 127.0, 127.0, 0.0);
( 314231.5, 3995501.5, 127.0, 127.0, 0.0); ( 314251.5,
3995501.5, 127.0, 127.0, 0.0);
( 314271.5, 3995501.5, 127.0, 127.0, 0.0); ( 313271.5,
3995521.5, 125.7, 125.7, 0.0);
( 313291.5, 3995521.5, 125.7, 125.7, 0.0); ( 313311.5,
3995521.5, 125.8, 125.8, 0.0);
( 313331.5, 3995521.5, 125.8, 125.8, 0.0); ( 313351.5,
3995521.5, 125.8, 125.8, 0.0);
( 313371.5, 3995521.5, 125.8, 125.8, 0.0); ( 313391.5,
3995521.5, 125.9, 125.9, 0.0);
( 313411.5, 3995521.5, 125.9, 125.9, 0.0); ( 313431.5,
3995521.5, 125.9, 125.9, 0.0);
( 313451.5, 3995521.5, 125.9, 125.9, 0.0); ( 313471.5,
3995521.5, 126.0, 126.0, 0.0);
( 313491.5, 3995521.5, 126.0, 126.0, 0.0); ( 313511.5,
3995521.5, 126.0, 126.0, 0.0);
( 313531.5, 3995521.5, 126.0, 126.0, 0.0); ( 313551.5,
3995521.5, 126.1, 126.1, 0.0);
( 313571.5, 3995521.5, 126.1, 126.1, 0.0); ( 313591.5,
3995521.5, 126.1, 126.1, 0.0);
( 313611.5, 3995521.5, 126.2, 126.2, 0.0); ( 313631.5,
3995521.5, 126.2, 126.2, 0.0);
( 313651.5, 3995521.5, 126.2, 126.2, 0.0); ( 313671.5,
3995521.5, 126.2, 126.2, 0.0);
( 313691.5, 3995521.5, 126.2, 126.2, 0.0); ( 313711.5,
3995521.5, 126.3, 126.3, 0.0);
( 313731.5, 3995521.5, 126.3, 126.3, 0.0); ( 313751.5,
3995521.5, 126.3, 126.3, 0.0);
( 313771.5, 3995521.5, 126.3, 126.3, 0.0); ( 313791.5,
3995521.5, 126.4, 126.4, 0.0);
( 313811.5, 3995521.5, 126.4, 126.4, 0.0); ( 313831.5,
3995521.5, 126.4, 126.4, 0.0);
( 313851.5, 3995521.5, 126.5, 126.5, 0.0); ( 313871.5,
3995521.5, 126.5, 126.5, 0.0);
( 313891.5, 3995521.5, 126.5, 126.5, 0.0); ( 313911.5,
3995521.5, 126.5, 126.5, 0.0);
( 313931.5, 3995521.5, 126.5, 126.5, 0.0); ( 313951.5,
3995521.5, 126.6, 126.6, 0.0);
( 313971.5, 3995521.5, 126.6, 126.6, 0.0); ( 313991.5,
3995521.5, 126.6, 126.6, 0.0);
( 314011.5, 3995521.5, 126.6, 126.6, 0.0); ( 314031.5,
3995521.5, 126.7, 126.7, 0.0);
( 314051.5, 3995521.5, 126.7, 126.7, 0.0); ( 314071.5,
3995521.5, 126.7, 126.7, 0.0);
( 314091.5, 3995521.5, 126.8, 126.8, 0.0); ( 314111.5,
3995521.5, 126.8, 126.8, 0.0);
( 314131.5, 3995521.5, 126.8, 126.8, 0.0); ( 314151.5,
3995521.5, 126.8, 126.8, 0.0);
( 314171.5, 3995521.5, 126.9, 126.9, 0.0); ( 314191.5,
3995521.5, 126.9, 126.9, 0.0);
( 314211.5, 3995521.5, 126.9, 126.9, 0.0); ( 314231.5,
3995521.5, 127.0, 127.0, 0.0);
( 314251.5, 3995521.5, 127.0, 127.0, 0.0); ( 314271.5,
3995521.5, 127.0, 127.0, 0.0);
( 313271.5, 3995541.5, 125.7, 125.7, 0.0); ( 313291.5,
3995541.5, 125.7, 125.7, 0.0);
( 313311.5, 3995541.5, 125.7, 125.7, 0.0); ( 313331.5,
3995541.5, 125.8, 125.8, 0.0);
( 313351.5, 3995541.5, 125.8, 125.8, 0.0); ( 313371.5,
3995541.5, 125.8, 125.8, 0.0);
( 313391.5, 3995541.5, 125.8, 125.8, 0.0); ( 313411.5,
3995541.5, 125.8, 125.8, 0.0);
( 313431.5, 3995541.5, 125.9, 125.9, 0.0); ( 313451.5,
3995541.5, 125.9, 125.9, 0.0);
( 313471.5, 3995541.5, 125.9, 125.9, 0.0); ( 313491.5,
3995541.5, 126.0, 126.0, 0.0);
( 313511.5, 3995541.5, 126.0, 126.0, 0.0); ( 313531.5,
3995541.5, 126.0, 126.0, 0.0);
( 313551.5, 3995541.5, 126.0, 126.0, 0.0); ( 313571.5,
3995541.5, 126.1, 126.1, 0.0);
( 313591.5, 3995541.5, 126.1, 126.1, 0.0); ( 313611.5,
3995541.5, 126.1, 126.1, 0.0);
( 313631.5, 3995541.5, 126.1, 126.1, 0.0); ( 313651.5,
3995541.5, 126.2, 126.2, 0.0);
( 313671.5, 3995541.5, 126.2, 126.2, 0.0); ( 313691.5,
3995541.5, 126.2, 126.2, 0.0);
( 313711.5, 3995541.5, 126.2, 126.2, 0.0); ( 313731.5,
3995541.5, 126.3, 126.3, 0.0);
( 313751.5, 3995541.5, 126.3, 126.3, 0.0); ( 313771.5,
3995541.5, 126.3, 126.3, 0.0);
( 313791.5, 3995541.5, 126.3, 126.3, 0.0); ( 313811.5,
3995541.5, 126.3, 126.3, 0.0);
( 313831.5, 3995541.5, 126.4, 126.4, 0.0); ( 313851.5,
3995541.5, 126.4, 126.4, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 11
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313871.5, 3995541.5, 126.4, 126.4, 0.0); ( 313891.5,
3995541.5, 126.4, 126.4, 0.0);
( 313911.5, 3995541.5, 126.5, 126.5, 0.0); ( 313931.5,
3995541.5, 126.5, 126.5, 0.0);
( 313951.5, 3995541.5, 126.5, 126.5, 0.0); ( 313971.5,
3995541.5, 126.5, 126.5, 0.0);
( 313991.5, 3995541.5, 126.6, 126.6, 0.0); ( 314011.5,
3995541.5, 126.6, 126.6, 0.0);
( 314031.5, 3995541.5, 126.6, 126.6, 0.0); ( 314051.5,
3995541.5, 126.7, 126.7, 0.0);
( 314071.5, 3995541.5, 126.7, 126.7, 0.0); ( 314091.5,
3995541.5, 126.7, 126.7, 0.0);
( 314111.5, 3995541.5, 126.8, 126.8, 0.0); ( 314131.5,
3995541.5, 126.8, 126.8, 0.0);
( 314151.5, 3995541.5, 126.8, 126.8, 0.0); ( 314171.5,
3995541.5, 126.8, 126.8, 0.0);
( 314191.5, 3995541.5, 126.9, 126.9, 0.0); ( 314211.5,
3995541.5, 126.9, 126.9, 0.0);
( 314231.5, 3995541.5, 126.9, 126.9, 0.0); ( 314251.5,
3995541.5, 127.0, 127.0, 0.0);
( 314271.5, 3995541.5, 127.0, 127.0, 0.0); ( 313271.5,
3995561.5, 125.7, 125.7, 0.0);
( 313291.5, 3995561.5, 125.7, 125.7, 0.0); ( 313311.5,
3995561.5, 125.7, 125.7, 0.0);
( 313331.5, 3995561.5, 125.7, 125.7, 0.0); ( 313351.5,
3995561.5, 125.8, 125.8, 0.0);
( 313371.5, 3995561.5, 125.8, 125.8, 0.0); ( 313391.5,
3995561.5, 125.8, 125.8, 0.0);
( 313411.5, 3995561.5, 125.8, 125.8, 0.0); ( 313431.5,
3995561.5, 125.8, 125.8, 0.0);
( 313451.5, 3995561.5, 125.9, 125.9, 0.0); ( 313471.5,
3995561.5, 125.9, 125.9, 0.0);
( 313491.5, 3995561.5, 125.9, 125.9, 0.0); ( 313511.5,
3995561.5, 126.0, 126.0, 0.0);
( 313531.5, 3995561.5, 126.0, 126.0, 0.0); ( 313551.5,
3995561.5, 126.0, 126.0, 0.0);
( 313571.5, 3995561.5, 126.0, 126.0, 0.0); ( 313591.5,
3995561.5, 126.1, 126.1, 0.0);
( 313611.5, 3995561.5, 126.1, 126.1, 0.0); ( 313631.5,
3995561.5, 126.1, 126.1, 0.0);
( 313651.5, 3995561.5, 126.1, 126.1, 0.0); ( 313671.5,
3995561.5, 126.1, 126.1, 0.0);
( 313691.5, 3995561.5, 126.2, 126.2, 0.0); ( 313711.5,
3995561.5, 126.2, 126.2, 0.0);
( 313731.5, 3995561.5, 126.2, 126.2, 0.0); ( 313751.5,
3995561.5, 126.2, 126.2, 0.0);
( 313771.5, 3995561.5, 126.2, 126.2, 0.0); ( 313791.5,
3995561.5, 126.3, 126.3, 0.0);
( 313811.5, 3995561.5, 126.3, 126.3, 0.0); ( 313831.5,
3995561.5, 126.3, 126.3, 0.0);
( 313851.5, 3995561.5, 126.3, 126.3, 0.0); ( 313871.5,
3995561.5, 126.4, 126.4, 0.0);
( 313891.5, 3995561.5, 126.4, 126.4, 0.0); ( 313911.5,
3995561.5, 126.4, 126.4, 0.0);
( 313931.5, 3995561.5, 126.4, 126.4, 0.0); ( 313951.5,
3995561.5, 126.5, 126.5, 0.0);
( 313971.5, 3995561.5, 126.5, 126.5, 0.0); ( 313991.5,
3995561.5, 126.5, 126.5, 0.0);
( 314011.5, 3995561.5, 126.6, 126.6, 0.0); ( 314031.5,
3995561.5, 126.6, 126.6, 0.0);
( 314051.5, 3995561.5, 126.6, 126.6, 0.0); ( 314071.5,
3995561.5, 126.6, 126.6, 0.0);
( 314091.5, 3995561.5, 126.7, 126.7, 0.0); ( 314111.5,
3995561.5, 126.7, 126.7, 0.0);
( 314131.5, 3995561.5, 126.7, 126.7, 0.0); ( 314151.5,
3995561.5, 126.8, 126.8, 0.0);
( 314171.5, 3995561.5, 126.8, 126.8, 0.0); ( 314191.5,
3995561.5, 126.8, 126.8, 0.0);
( 314211.5, 3995561.5, 126.8, 126.8, 0.0); ( 314231.5,
3995561.5, 126.9, 126.9, 0.0);
( 314251.5, 3995561.5, 126.9, 126.9, 0.0); ( 314271.5,
3995561.5, 127.0, 127.0, 0.0);
( 313271.5, 3995581.5, 125.6, 125.6, 0.0); ( 313291.5,
3995581.5, 125.7, 125.7, 0.0);
( 313311.5, 3995581.5, 125.7, 125.7, 0.0); ( 313331.5,
3995581.5, 125.7, 125.7, 0.0);
( 313351.5, 3995581.5, 125.7, 125.7, 0.0); ( 313371.5,
3995581.5, 125.8, 125.8, 0.0);
( 313391.5, 3995581.5, 125.8, 125.8, 0.0); ( 313411.5,
3995581.5, 125.8, 125.8, 0.0);
( 313431.5, 3995581.5, 125.8, 125.8, 0.0); ( 313451.5,
3995581.5, 125.8, 125.8, 0.0);
( 313471.5, 3995581.5, 125.9, 125.9, 0.0); ( 313491.5,
3995581.5, 125.9, 125.9, 0.0);
( 313511.5, 3995581.5, 125.9, 125.9, 0.0); ( 313531.5,
3995581.5, 126.0, 126.0, 0.0);
( 313551.5, 3995581.5, 126.0, 126.0, 0.0); ( 313571.5,
3995581.5, 126.0, 126.0, 0.0);
( 313591.5, 3995581.5, 126.0, 126.0, 0.0); ( 313611.5,
3995581.5, 126.0, 126.0, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 12
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313631.5, 3995581.5, 126.1, 126.1, 0.0); ( 313651.5,
3995581.5, 126.1, 126.1, 0.0);
( 313671.5, 3995581.5, 126.1, 126.1, 0.0); ( 313691.5,
3995581.5, 126.1, 126.1, 0.0);
( 313711.5, 3995581.5, 126.1, 126.1, 0.0); ( 313731.5,
3995581.5, 126.2, 126.2, 0.0);
( 313751.5, 3995581.5, 126.2, 126.2, 0.0); ( 313771.5,
3995581.5, 126.2, 126.2, 0.0);
( 313791.5, 3995581.5, 126.2, 126.2, 0.0); ( 313811.5,
3995581.5, 126.2, 126.2, 0.0);
( 313831.5, 3995581.5, 126.3, 126.3, 0.0); ( 313851.5,
3995581.5, 126.3, 126.3, 0.0);
( 313871.5, 3995581.5, 126.3, 126.3, 0.0); ( 313891.5,
3995581.5, 126.3, 126.3, 0.0);
( 313911.5, 3995581.5, 126.4, 126.4, 0.0); ( 313931.5,
3995581.5, 126.4, 126.4, 0.0);
( 313951.5, 3995581.5, 126.4, 126.4, 0.0); ( 313971.5,
3995581.5, 126.4, 126.4, 0.0);
( 313991.5, 3995581.5, 126.5, 126.5, 0.0); ( 314011.5,
3995581.5, 126.5, 126.5, 0.0);
( 314031.5, 3995581.5, 126.5, 126.5, 0.0); ( 314051.5,
3995581.5, 126.6, 126.6, 0.0);
( 314071.5, 3995581.5, 126.6, 126.6, 0.0); ( 314091.5,
3995581.5, 126.6, 126.6, 0.0);
( 314111.5, 3995581.5, 126.7, 126.7, 0.0); ( 314131.5,
3995581.5, 126.7, 126.7, 0.0);
( 314151.5, 3995581.5, 126.7, 126.7, 0.0); ( 314171.5,
3995581.5, 126.8, 126.8, 0.0);
( 314191.5, 3995581.5, 126.8, 126.8, 0.0); ( 314211.5,
3995581.5, 126.8, 126.8, 0.0);
( 314231.5, 3995581.5, 126.9, 126.9, 0.0); ( 314251.5,
3995581.5, 126.9, 126.9, 0.0);
( 314271.5, 3995581.5, 126.9, 126.9, 0.0); ( 313271.5,
3995601.5, 125.6, 125.6, 0.0);
( 313291.5, 3995601.5, 125.6, 125.6, 0.0); ( 313311.5,
3995601.5, 125.7, 125.7, 0.0);
( 313331.5, 3995601.5, 125.7, 125.7, 0.0); ( 313351.5,
3995601.5, 125.7, 125.7, 0.0);
( 313371.5, 3995601.5, 125.7, 125.7, 0.0); ( 313391.5,
3995601.5, 125.8, 125.8, 0.0);
( 313411.5, 3995601.5, 125.8, 125.8, 0.0); ( 313431.5,
3995601.5, 125.8, 125.8, 0.0);
( 313451.5, 3995601.5, 125.8, 125.8, 0.0); ( 313471.5,
3995601.5, 125.8, 125.8, 0.0);
( 313491.5, 3995601.5, 125.9, 125.9, 0.0); ( 313511.5,
3995601.5, 125.9, 125.9, 0.0);
( 313531.5, 3995601.5, 125.9, 125.9, 0.0); ( 313551.5,
3995601.5, 125.9, 125.9, 0.0);
( 313571.5, 3995601.5, 126.0, 126.0, 0.0); ( 313591.5,
3995601.5, 126.0, 126.0, 0.0);
( 313611.5, 3995601.5, 126.0, 126.0, 0.0); ( 313631.5,
3995601.5, 126.0, 126.0, 0.0);
( 313651.5, 3995601.5, 126.0, 126.0, 0.0); ( 313671.5,
3995601.5, 126.1, 126.1, 0.0);
( 313691.5, 3995601.5, 126.1, 126.1, 0.0); ( 313711.5,
3995601.5, 126.1, 126.1, 0.0);
( 313731.5, 3995601.5, 126.1, 126.1, 0.0); ( 313751.5,
3995601.5, 126.1, 126.1, 0.0);
( 313771.5, 3995601.5, 126.2, 126.2, 0.0); ( 313791.5,
3995601.5, 126.2, 126.2, 0.0);
( 313811.5, 3995601.5, 126.2, 126.2, 0.0); ( 313831.5,
3995601.5, 126.2, 126.2, 0.0);
( 313851.5, 3995601.5, 126.2, 126.2, 0.0); ( 313871.5,
3995601.5, 126.3, 126.3, 0.0);
( 313891.5, 3995601.5, 126.3, 126.3, 0.0); ( 313911.5,
3995601.5, 126.3, 126.3, 0.0);
( 313931.5, 3995601.5, 126.3, 126.3, 0.0); ( 313951.5,
3995601.5, 126.4, 126.4, 0.0);
( 313971.5, 3995601.5, 126.4, 126.4, 0.0); ( 313991.5,
3995601.5, 126.4, 126.4, 0.0);
( 314011.5, 3995601.5, 126.5, 126.5, 0.0); ( 314031.5,
3995601.5, 126.5, 126.5, 0.0);
( 314051.5, 3995601.5, 126.5, 126.5, 0.0); ( 314071.5,
3995601.5, 126.6, 126.6, 0.0);
( 314091.5, 3995601.5, 126.6, 126.6, 0.0); ( 314111.5,
3995601.5, 126.6, 126.6, 0.0);
( 314131.5, 3995601.5, 126.7, 126.7, 0.0); ( 314151.5,
3995601.5, 126.7, 126.7, 0.0);
( 314171.5, 3995601.5, 126.7, 126.7, 0.0); ( 314191.5,
3995601.5, 126.8, 126.8, 0.0);
( 314211.5, 3995601.5, 126.8, 126.8, 0.0); ( 314231.5,
3995601.5, 126.8, 126.8, 0.0);
( 314251.5, 3995601.5, 126.9, 126.9, 0.0); ( 314271.5,
3995601.5, 126.9, 126.9, 0.0);
( 313271.5, 3995621.5, 125.6, 125.6, 0.0); ( 313291.5,
3995621.5, 125.6, 125.6, 0.0);
( 313311.5, 3995621.5, 125.6, 125.6, 0.0); ( 313331.5,
3995621.5, 125.7, 125.7, 0.0);
( 313351.5, 3995621.5, 125.7, 125.7, 0.0); ( 313371.5,
3995621.5, 125.7, 125.7, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 13
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313391.5, 3995621.5, 125.7, 125.7, 0.0); ( 313411.5,
3995621.5, 125.8, 125.8, 0.0);
( 313431.5, 3995621.5, 125.8, 125.8, 0.0); ( 313451.5,
3995621.5, 125.8, 125.8, 0.0);
( 313471.5, 3995621.5, 125.8, 125.8, 0.0); ( 313491.5,
3995621.5, 125.8, 125.8, 0.0);
( 313511.5, 3995621.5, 125.9, 125.9, 0.0); ( 313531.5,
3995621.5, 125.9, 125.9, 0.0);
( 313551.5, 3995621.5, 125.9, 125.9, 0.0); ( 313571.5,
3995621.5, 125.9, 125.9, 0.0);
( 313591.5, 3995621.5, 126.0, 126.0, 0.0); ( 313611.5,
3995621.5, 126.0, 126.0, 0.0);
( 313631.5, 3995621.5, 126.0, 126.0, 0.0); ( 313651.5,
3995621.5, 126.0, 126.0, 0.0);
( 313671.5, 3995621.5, 126.0, 126.0, 0.0); ( 313691.5,
3995621.5, 126.0, 126.0, 0.0);
( 313711.5, 3995621.5, 126.1, 126.1, 0.0); ( 313731.5,
3995621.5, 126.1, 126.1, 0.0);
( 313751.5, 3995621.5, 126.1, 126.1, 0.0); ( 313771.5,
3995621.5, 126.1, 126.1, 0.0);
( 313791.5, 3995621.5, 126.1, 126.1, 0.0); ( 313811.5,
3995621.5, 126.1, 126.1, 0.0);
( 313831.5, 3995621.5, 126.2, 126.2, 0.0); ( 313851.5,
3995621.5, 126.2, 126.2, 0.0);
( 313871.5, 3995621.5, 126.2, 126.2, 0.0); ( 313891.5,
3995621.5, 126.2, 126.2, 0.0);
( 313911.5, 3995621.5, 126.3, 126.3, 0.0); ( 313931.5,
3995621.5, 126.3, 126.3, 0.0);
( 313951.5, 3995621.5, 126.3, 126.3, 0.0); ( 313971.5,
3995621.5, 126.3, 126.3, 0.0);
( 313991.5, 3995621.5, 126.4, 126.4, 0.0); ( 314011.5,
3995621.5, 126.4, 126.4, 0.0);
( 314031.5, 3995621.5, 126.5, 126.5, 0.0); ( 314051.5,
3995621.5, 126.5, 126.5, 0.0);
( 314071.5, 3995621.5, 126.5, 126.5, 0.0); ( 314091.5,
3995621.5, 126.5, 126.5, 0.0);
( 314111.5, 3995621.5, 126.6, 126.6, 0.0); ( 314131.5,
3995621.5, 126.6, 126.6, 0.0);
( 314151.5, 3995621.5, 126.7, 126.7, 0.0); ( 314171.5,
3995621.5, 126.7, 126.7, 0.0);
( 314191.5, 3995621.5, 126.7, 126.7, 0.0); ( 314211.5,
3995621.5, 126.8, 126.8, 0.0);
( 314231.5, 3995621.5, 126.8, 126.8, 0.0); ( 314251.5,
3995621.5, 126.8, 126.8, 0.0);
( 314271.5, 3995621.5, 126.9, 126.9, 0.0); ( 313271.5,
3995641.5, 125.6, 125.6, 0.0);
( 313291.5, 3995641.5, 125.6, 125.6, 0.0); ( 313311.5,
3995641.5, 125.6, 125.6, 0.0);
( 313331.5, 3995641.5, 125.6, 125.6, 0.0); ( 313351.5,
3995641.5, 125.7, 125.7, 0.0);
( 313371.5, 3995641.5, 125.7, 125.7, 0.0); ( 313391.5,
3995641.5, 125.7, 125.7, 0.0);
( 313411.5, 3995641.5, 125.7, 125.7, 0.0); ( 313431.5,
3995641.5, 125.8, 125.8, 0.0);
( 313451.5, 3995641.5, 125.8, 125.8, 0.0); ( 313471.5,
3995641.5, 125.8, 125.8, 0.0);
( 313491.5, 3995641.5, 125.8, 125.8, 0.0); ( 313511.5,
3995641.5, 125.8, 125.8, 0.0);
( 313531.5, 3995641.5, 125.9, 125.9, 0.0); ( 313551.5,
3995641.5, 125.9, 125.9, 0.0);
( 313571.5, 3995641.5, 125.9, 125.9, 0.0); ( 313591.5,
3995641.5, 125.9, 125.9, 0.0);
( 313611.5, 3995641.5, 125.9, 125.9, 0.0); ( 313631.5,
3995641.5, 126.0, 126.0, 0.0);
( 313651.5, 3995641.5, 126.0, 126.0, 0.0); ( 313671.5,
3995641.5, 126.0, 126.0, 0.0);
( 313691.5, 3995641.5, 126.0, 126.0, 0.0); ( 313711.5,
3995641.5, 126.0, 126.0, 0.0);
( 313731.5, 3995641.5, 126.1, 126.1, 0.0); ( 313751.5,
3995641.5, 126.1, 126.1, 0.0);
( 313771.5, 3995641.5, 126.1, 126.1, 0.0); ( 313791.5,
3995641.5, 126.1, 126.1, 0.0);
( 313811.5, 3995641.5, 126.1, 126.1, 0.0); ( 313971.5,
3995641.5, 126.3, 126.3, 0.0);
( 313991.5, 3995641.5, 126.3, 126.3, 0.0); ( 314011.5,
3995641.5, 126.4, 126.4, 0.0);
( 314031.5, 3995641.5, 126.4, 126.4, 0.0); ( 314051.5,
3995641.5, 126.4, 126.4, 0.0);
( 314071.5, 3995641.5, 126.5, 126.5, 0.0); ( 314091.5,
3995641.5, 126.5, 126.5, 0.0);
( 314111.5, 3995641.5, 126.5, 126.5, 0.0); ( 314131.5,
3995641.5, 126.6, 126.6, 0.0);
( 314151.5, 3995641.5, 126.6, 126.6, 0.0); ( 314171.5,
3995641.5, 126.7, 126.7, 0.0);
( 314191.5, 3995641.5, 126.7, 126.7, 0.0); ( 314211.5,
3995641.5, 126.7, 126.7, 0.0);
( 314231.5, 3995641.5, 126.8, 126.8, 0.0); ( 314251.5,
3995641.5, 126.8, 126.8, 0.0);
( 314271.5, 3995641.5, 126.8, 126.8, 0.0); ( 313271.5,
3995661.5, 125.5, 125.5, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 14
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313291.5, 3995661.5, 125.6, 125.6, 0.0); ( 313311.5,
3995661.5, 125.6, 125.6, 0.0);
( 313331.5, 3995661.5, 125.6, 125.6, 0.0); ( 313351.5,
3995661.5, 125.6, 125.6, 0.0);
( 313371.5, 3995661.5, 125.7, 125.7, 0.0); ( 313391.5,
3995661.5, 125.7, 125.7, 0.0);
( 313411.5, 3995661.5, 125.7, 125.7, 0.0); ( 313431.5,
3995661.5, 125.7, 125.7, 0.0);
( 313451.5, 3995661.5, 125.8, 125.8, 0.0); ( 313471.5,
3995661.5, 125.8, 125.8, 0.0);
( 313491.5, 3995661.5, 125.8, 125.8, 0.0); ( 313511.5,
3995661.5, 125.8, 125.8, 0.0);
( 313531.5, 3995661.5, 125.8, 125.8, 0.0); ( 313971.5,
3995661.5, 126.2, 126.2, 0.0);
( 313991.5, 3995661.5, 126.3, 126.3, 0.0); ( 314011.5,
3995661.5, 126.3, 126.3, 0.0);
( 314031.5, 3995661.5, 126.3, 126.3, 0.0); ( 314051.5,
3995661.5, 126.4, 126.4, 0.0);
( 314071.5, 3995661.5, 126.4, 126.4, 0.0); ( 314091.5,
3995661.5, 126.5, 126.5, 0.0);
( 314111.5, 3995661.5, 126.5, 126.5, 0.0); ( 314131.5,
3995661.5, 126.5, 126.5, 0.0);
( 314151.5, 3995661.5, 126.6, 126.6, 0.0); ( 314171.5,
3995661.5, 126.6, 126.6, 0.0);
( 314191.5, 3995661.5, 126.7, 126.7, 0.0); ( 314211.5,
3995661.5, 126.7, 126.7, 0.0);
( 314231.5, 3995661.5, 126.7, 126.7, 0.0); ( 314251.5,
3995661.5, 126.8, 126.8, 0.0);
( 314271.5, 3995661.5, 126.8, 126.8, 0.0); ( 313271.5,
3995681.5, 125.5, 125.5, 0.0);
( 313291.5, 3995681.5, 125.5, 125.5, 0.0); ( 313311.5,
3995681.5, 125.6, 125.6, 0.0);
( 313331.5, 3995681.5, 125.6, 125.6, 0.0); ( 313351.5,
3995681.5, 125.6, 125.6, 0.0);
( 313371.5, 3995681.5, 125.6, 125.6, 0.0); ( 313391.5,
3995681.5, 125.7, 125.7, 0.0);
( 313411.5, 3995681.5, 125.7, 125.7, 0.0); ( 313431.5,
3995681.5, 125.7, 125.7, 0.0);
( 313451.5, 3995681.5, 125.7, 125.7, 0.0); ( 313471.5,
3995681.5, 125.8, 125.8, 0.0);
( 313491.5, 3995681.5, 125.8, 125.8, 0.0); ( 313511.5,
3995681.5, 125.8, 125.8, 0.0);
( 313531.5, 3995681.5, 125.8, 125.8, 0.0); ( 313971.5,
3995681.5, 126.2, 126.2, 0.0);
( 313991.5, 3995681.5, 126.2, 126.2, 0.0); ( 314011.5,
3995681.5, 126.3, 126.3, 0.0);
( 314031.5, 3995681.5, 126.3, 126.3, 0.0); ( 314051.5,
3995681.5, 126.3, 126.3, 0.0);
( 314071.5, 3995681.5, 126.4, 126.4, 0.0); ( 314091.5,
3995681.5, 126.4, 126.4, 0.0);
( 314111.5, 3995681.5, 126.5, 126.5, 0.0); ( 314131.5,
3995681.5, 126.5, 126.5, 0.0);
( 314151.5, 3995681.5, 126.5, 126.5, 0.0); ( 314171.5,
3995681.5, 126.6, 126.6, 0.0);
( 314191.5, 3995681.5, 126.6, 126.6, 0.0); ( 314211.5,
3995681.5, 126.7, 126.7, 0.0);
( 314231.5, 3995681.5, 126.7, 126.7, 0.0); ( 314251.5,
3995681.5, 126.7, 126.7, 0.0);
( 314271.5, 3995681.5, 126.8, 126.8, 0.0); ( 313271.5,
3995701.5, 125.5, 125.5, 0.0);
( 313291.5, 3995701.5, 125.5, 125.5, 0.0); ( 313311.5,
3995701.5, 125.6, 125.6, 0.0);
( 313331.5, 3995701.5, 125.6, 125.6, 0.0); ( 313351.5,
3995701.5, 125.6, 125.6, 0.0);
( 313371.5, 3995701.5, 125.6, 125.6, 0.0); ( 313391.5,
3995701.5, 125.7, 125.7, 0.0);
( 313411.5, 3995701.5, 125.7, 125.7, 0.0); ( 313431.5,
3995701.5, 125.7, 125.7, 0.0);
( 313451.5, 3995701.5, 125.7, 125.7, 0.0); ( 313471.5,
3995701.5, 125.7, 125.7, 0.0);
( 313491.5, 3995701.5, 125.8, 125.8, 0.0); ( 313511.5,
3995701.5, 125.8, 125.8, 0.0);
( 313531.5, 3995701.5, 125.8, 125.8, 0.0); ( 313971.5,
3995701.5, 126.2, 126.2, 0.0);
( 313991.5, 3995701.5, 126.2, 126.2, 0.0); ( 314011.5,
3995701.5, 126.2, 126.2, 0.0);
( 314031.5, 3995701.5, 126.3, 126.3, 0.0); ( 314051.5,
3995701.5, 126.3, 126.3, 0.0);
( 314071.5, 3995701.5, 126.3, 126.3, 0.0); ( 314091.5,
3995701.5, 126.4, 126.4, 0.0);
( 314111.5, 3995701.5, 126.4, 126.4, 0.0); ( 314131.5,
3995701.5, 126.5, 126.5, 0.0);
( 314151.5, 3995701.5, 126.5, 126.5, 0.0); ( 314171.5,
3995701.5, 126.5, 126.5, 0.0);
( 314191.5, 3995701.5, 126.6, 126.6, 0.0); ( 314211.5,
3995701.5, 126.6, 126.6, 0.0);
( 314231.5, 3995701.5, 126.7, 126.7, 0.0); ( 314251.5,
3995701.5, 126.7, 126.7, 0.0);
( 314271.5, 3995701.5, 126.8, 126.8, 0.0); ( 313271.5,
3995721.5, 125.5, 125.5, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 15
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313291.5, 3995721.5, 125.5, 125.5, 0.0); ( 313311.5,
3995721.5, 125.5, 125.5, 0.0);
( 313331.5, 3995721.5, 125.6, 125.6, 0.0); ( 313351.5,
3995721.5, 125.6, 125.6, 0.0);
( 313371.5, 3995721.5, 125.6, 125.6, 0.0); ( 313391.5,
3995721.5, 125.6, 125.6, 0.0);
( 313411.5, 3995721.5, 125.7, 125.7, 0.0); ( 313431.5,
3995721.5, 125.7, 125.7, 0.0);
( 313451.5, 3995721.5, 125.7, 125.7, 0.0); ( 313471.5,
3995721.5, 125.7, 125.7, 0.0);
( 313491.5, 3995721.5, 125.7, 125.7, 0.0); ( 313511.5,
3995721.5, 125.8, 125.8, 0.0);
( 313531.5, 3995721.5, 125.8, 125.8, 0.0); ( 313971.5,
3995721.5, 126.1, 126.1, 0.0);
( 313991.5, 3995721.5, 126.1, 126.1, 0.0); ( 314011.5,
3995721.5, 126.2, 126.2, 0.0);
( 314031.5, 3995721.5, 126.2, 126.2, 0.0); ( 314051.5,
3995721.5, 126.2, 126.2, 0.0);
( 314071.5, 3995721.5, 126.3, 126.3, 0.0); ( 314091.5,
3995721.5, 126.3, 126.3, 0.0);
( 314111.5, 3995721.5, 126.4, 126.4, 0.0); ( 314131.5,
3995721.5, 126.4, 126.4, 0.0);
( 314151.5, 3995721.5, 126.5, 126.5, 0.0); ( 314171.5,
3995721.5, 126.5, 126.5, 0.0);
( 314191.5, 3995721.5, 126.5, 126.5, 0.0); ( 314211.5,
3995721.5, 126.6, 126.6, 0.0);
( 314231.5, 3995721.5, 126.6, 126.6, 0.0); ( 314251.5,
3995721.5, 126.7, 126.7, 0.0);
( 314271.5, 3995721.5, 126.7, 126.7, 0.0); ( 313271.5,
3995741.5, 125.5, 125.5, 0.0);
( 313291.5, 3995741.5, 125.5, 125.5, 0.0); ( 313311.5,
3995741.5, 125.5, 125.5, 0.0);
( 313331.5, 3995741.5, 125.5, 125.5, 0.0); ( 313351.5,
3995741.5, 125.6, 125.6, 0.0);
( 313371.5, 3995741.5, 125.6, 125.6, 0.0); ( 313391.5,
3995741.5, 125.6, 125.6, 0.0);
( 313411.5, 3995741.5, 125.7, 125.7, 0.0); ( 313431.5,
3995741.5, 125.7, 125.7, 0.0);
( 313451.5, 3995741.5, 125.7, 125.7, 0.0); ( 313471.5,
3995741.5, 125.7, 125.7, 0.0);
( 313491.5, 3995741.5, 125.7, 125.7, 0.0); ( 313511.5,
3995741.5, 125.7, 125.7, 0.0);
( 313531.5, 3995741.5, 125.8, 125.8, 0.0); ( 313971.5,
3995741.5, 126.1, 126.1, 0.0);
( 313991.5, 3995741.5, 126.1, 126.1, 0.0); ( 314011.5,
3995741.5, 126.1, 126.1, 0.0);
( 314031.5, 3995741.5, 126.2, 126.2, 0.0); ( 314051.5,
3995741.5, 126.2, 126.2, 0.0);
( 314071.5, 3995741.5, 126.2, 126.2, 0.0); ( 314091.5,
3995741.5, 126.3, 126.3, 0.0);
( 314111.5, 3995741.5, 126.3, 126.3, 0.0); ( 314131.5,
3995741.5, 126.4, 126.4, 0.0);
( 314151.5, 3995741.5, 126.4, 126.4, 0.0); ( 314171.5,
3995741.5, 126.5, 126.5, 0.0);
( 314191.5, 3995741.5, 126.5, 126.5, 0.0); ( 314211.5,
3995741.5, 126.6, 126.6, 0.0);
( 314231.5, 3995741.5, 126.6, 126.6, 0.0); ( 314251.5,
3995741.5, 126.6, 126.6, 0.0);
( 314271.5, 3995741.5, 126.7, 126.7, 0.0); ( 313271.5,
3995761.5, 125.5, 125.5, 0.0);
( 313291.5, 3995761.5, 125.5, 125.5, 0.0); ( 313311.5,
3995761.5, 125.5, 125.5, 0.0);
( 313331.5, 3995761.5, 125.5, 125.5, 0.0); ( 313351.5,
3995761.5, 125.6, 125.6, 0.0);
( 313371.5, 3995761.5, 125.6, 125.6, 0.0); ( 313391.5,
3995761.5, 125.6, 125.6, 0.0);
( 313411.5, 3995761.5, 125.7, 125.7, 0.0); ( 313431.5,
3995761.5, 125.7, 125.7, 0.0);
( 313451.5, 3995761.5, 125.7, 125.7, 0.0); ( 313471.5,
3995761.5, 125.7, 125.7, 0.0);
( 313491.5, 3995761.5, 125.7, 125.7, 0.0); ( 313511.5,
3995761.5, 125.7, 125.7, 0.0);
( 313531.5, 3995761.5, 125.7, 125.7, 0.0); ( 313971.5,
3995761.5, 126.0, 126.0, 0.0);
( 313991.5, 3995761.5, 126.1, 126.1, 0.0); ( 314011.5,
3995761.5, 126.1, 126.1, 0.0);
( 314031.5, 3995761.5, 126.1, 126.1, 0.0); ( 314051.5,
3995761.5, 126.2, 126.2, 0.0);
( 314071.5, 3995761.5, 126.2, 126.2, 0.0); ( 314091.5,
3995761.5, 126.2, 126.2, 0.0);
( 314111.5, 3995761.5, 126.3, 126.3, 0.0); ( 314131.5,
3995761.5, 126.3, 126.3, 0.0);
( 314151.5, 3995761.5, 126.4, 126.4, 0.0); ( 314171.5,
3995761.5, 126.4, 126.4, 0.0);
( 314191.5, 3995761.5, 126.5, 126.5, 0.0); ( 314211.5,
3995761.5, 126.5, 126.5, 0.0);
( 314231.5, 3995761.5, 126.6, 126.6, 0.0); ( 314251.5,
3995761.5, 126.6, 126.6, 0.0);
( 314271.5, 3995761.5, 126.7, 126.7, 0.0); ( 313271.5,
3995781.5, 125.4, 125.4, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 16
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313291.5, 3995781.5, 125.5, 125.5, 0.0); ( 313311.5,
3995781.5, 125.5, 125.5, 0.0);
( 313331.5, 3995781.5, 125.5, 125.5, 0.0); ( 313351.5,
3995781.5, 125.6, 125.6, 0.0);
( 313371.5, 3995781.5, 125.6, 125.6, 0.0); ( 313391.5,
3995781.5, 125.6, 125.6, 0.0);
( 313411.5, 3995781.5, 125.6, 125.6, 0.0); ( 313431.5,
3995781.5, 125.7, 125.7, 0.0);
( 313451.5, 3995781.5, 125.7, 125.7, 0.0); ( 313471.5,
3995781.5, 125.7, 125.7, 0.0);
( 313491.5, 3995781.5, 125.7, 125.7, 0.0); ( 313511.5,
3995781.5, 125.7, 125.7, 0.0);
( 313531.5, 3995781.5, 125.7, 125.7, 0.0); ( 313971.5,
3995781.5, 126.0, 126.0, 0.0);
( 313991.5, 3995781.5, 126.0, 126.0, 0.0); ( 314011.5,
3995781.5, 126.1, 126.1, 0.0);
( 314031.5, 3995781.5, 126.1, 126.1, 0.0); ( 314051.5,
3995781.5, 126.1, 126.1, 0.0);
( 314071.5, 3995781.5, 126.2, 126.2, 0.0); ( 314091.5,
3995781.5, 126.2, 126.2, 0.0);
( 314111.5, 3995781.5, 126.3, 126.3, 0.0); ( 314131.5,
3995781.5, 126.3, 126.3, 0.0);
( 314151.5, 3995781.5, 126.3, 126.3, 0.0); ( 314171.5,
3995781.5, 126.4, 126.4, 0.0);
( 314191.5, 3995781.5, 126.5, 126.5, 0.0); ( 314211.5,
3995781.5, 126.5, 126.5, 0.0);
( 314231.5, 3995781.5, 126.5, 126.5, 0.0); ( 314251.5,
3995781.5, 126.6, 126.6, 0.0);
( 314271.5, 3995781.5, 126.6, 126.6, 0.0); ( 313271.5,
3995801.5, 125.4, 125.4, 0.0);
( 313291.5, 3995801.5, 125.5, 125.5, 0.0); ( 313311.5,
3995801.5, 125.5, 125.5, 0.0);
( 313331.5, 3995801.5, 125.5, 125.5, 0.0); ( 313351.5,
3995801.5, 125.6, 125.6, 0.0);
( 313371.5, 3995801.5, 125.6, 125.6, 0.0); ( 313391.5,
3995801.5, 125.6, 125.6, 0.0);
( 313411.5, 3995801.5, 125.6, 125.6, 0.0); ( 313431.5,
3995801.5, 125.7, 125.7, 0.0);
( 313451.5, 3995801.5, 125.7, 125.7, 0.0); ( 313471.5,
3995801.5, 125.7, 125.7, 0.0);
( 313491.5, 3995801.5, 125.7, 125.7, 0.0); ( 313511.5,
3995801.5, 125.7, 125.7, 0.0);
( 313531.5, 3995801.5, 125.7, 125.7, 0.0); ( 313971.5,
3995801.5, 126.0, 126.0, 0.0);
( 313991.5, 3995801.5, 126.0, 126.0, 0.0); ( 314011.5,
3995801.5, 126.0, 126.0, 0.0);
( 314031.5, 3995801.5, 126.1, 126.1, 0.0); ( 314051.5,
3995801.5, 126.1, 126.1, 0.0);
( 314071.5, 3995801.5, 126.1, 126.1, 0.0); ( 314091.5,
3995801.5, 126.2, 126.2, 0.0);
( 314111.5, 3995801.5, 126.2, 126.2, 0.0); ( 314131.5,
3995801.5, 126.3, 126.3, 0.0);
( 314151.5, 3995801.5, 126.3, 126.3, 0.0); ( 314171.5,
3995801.5, 126.4, 126.4, 0.0);
( 314191.5, 3995801.5, 126.4, 126.4, 0.0); ( 314211.5,
3995801.5, 126.5, 126.5, 0.0);
( 314231.5, 3995801.5, 126.5, 126.5, 0.0); ( 314251.5,
3995801.5, 126.5, 126.5, 0.0);
( 314271.5, 3995801.5, 126.6, 126.6, 0.0); ( 313271.5,
3995821.5, 125.4, 125.4, 0.0);
( 313291.5, 3995821.5, 125.5, 125.5, 0.0); ( 313311.5,
3995821.5, 125.5, 125.5, 0.0);
( 313331.5, 3995821.5, 125.5, 125.5, 0.0); ( 313351.5,
3995821.5, 125.5, 125.5, 0.0);
( 313371.5, 3995821.5, 125.6, 125.6, 0.0); ( 313391.5,
3995821.5, 125.6, 125.6, 0.0);
( 313411.5, 3995821.5, 125.6, 125.6, 0.0); ( 313431.5,
3995821.5, 125.6, 125.6, 0.0);
( 313451.5, 3995821.5, 125.7, 125.7, 0.0); ( 313471.5,
3995821.5, 125.7, 125.7, 0.0);
( 313491.5, 3995821.5, 125.7, 125.7, 0.0); ( 313511.5,
3995821.5, 125.7, 125.7, 0.0);
( 313531.5, 3995821.5, 125.7, 125.7, 0.0); ( 313971.5,
3995821.5, 125.9, 125.9, 0.0);
( 313991.5, 3995821.5, 126.0, 126.0, 0.0); ( 314011.5,
3995821.5, 126.0, 126.0, 0.0);
( 314031.5, 3995821.5, 126.0, 126.0, 0.0); ( 314051.5,
3995821.5, 126.1, 126.1, 0.0);
( 314071.5, 3995821.5, 126.1, 126.1, 0.0); ( 314091.5,
3995821.5, 126.1, 126.1, 0.0);
( 314111.5, 3995821.5, 126.2, 126.2, 0.0); ( 314131.5,
3995821.5, 126.2, 126.2, 0.0);
( 314151.5, 3995821.5, 126.3, 126.3, 0.0); ( 314171.5,
3995821.5, 126.3, 126.3, 0.0);
( 314191.5, 3995821.5, 126.4, 126.4, 0.0); ( 314211.5,
3995821.5, 126.4, 126.4, 0.0);
( 314231.5, 3995821.5, 126.5, 126.5, 0.0); ( 314251.5,
3995821.5, 126.5, 126.5, 0.0);
( 314271.5, 3995821.5, 126.6, 126.6, 0.0); ( 313271.5,
3995841.5, 125.4, 125.4, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 17
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313291.5, 3995841.5, 125.4, 125.4, 0.0); ( 313311.5,
3995841.5, 125.5, 125.5, 0.0);
( 313331.5, 3995841.5, 125.5, 125.5, 0.0); ( 313351.5,
3995841.5, 125.5, 125.5, 0.0);
( 313371.5, 3995841.5, 125.6, 125.6, 0.0); ( 313391.5,
3995841.5, 125.6, 125.6, 0.0);
( 313411.5, 3995841.5, 125.6, 125.6, 0.0); ( 313431.5,
3995841.5, 125.6, 125.6, 0.0);
( 313451.5, 3995841.5, 125.7, 125.7, 0.0); ( 313471.5,
3995841.5, 125.7, 125.7, 0.0);
( 313491.5, 3995841.5, 125.7, 125.7, 0.0); ( 313511.5,
3995841.5, 125.7, 125.7, 0.0);
( 313531.5, 3995841.5, 125.7, 125.7, 0.0); ( 313971.5,
3995841.5, 125.9, 125.9, 0.0);
( 313991.5, 3995841.5, 125.9, 125.9, 0.0); ( 314011.5,
3995841.5, 126.0, 126.0, 0.0);
( 314031.5, 3995841.5, 126.0, 126.0, 0.0); ( 314051.5,
3995841.5, 126.0, 126.0, 0.0);
( 314071.5, 3995841.5, 126.1, 126.1, 0.0); ( 314091.5,
3995841.5, 126.1, 126.1, 0.0);
( 314111.5, 3995841.5, 126.2, 126.2, 0.0); ( 314131.5,
3995841.5, 126.2, 126.2, 0.0);
( 314151.5, 3995841.5, 126.3, 126.3, 0.0); ( 314171.5,
3995841.5, 126.3, 126.3, 0.0);
( 314191.5, 3995841.5, 126.4, 126.4, 0.0); ( 314211.5,
3995841.5, 126.4, 126.4, 0.0);
( 314231.5, 3995841.5, 126.5, 126.5, 0.0); ( 314251.5,
3995841.5, 126.5, 126.5, 0.0);
( 314271.5, 3995841.5, 126.5, 126.5, 0.0); ( 313271.5,
3995861.5, 125.4, 125.4, 0.0);
( 313291.5, 3995861.5, 125.4, 125.4, 0.0); ( 313311.5,
3995861.5, 125.5, 125.5, 0.0);
( 313331.5, 3995861.5, 125.5, 125.5, 0.0); ( 313351.5,
3995861.5, 125.5, 125.5, 0.0);
( 313371.5, 3995861.5, 125.6, 125.6, 0.0); ( 313391.5,
3995861.5, 125.6, 125.6, 0.0);
( 313411.5, 3995861.5, 125.6, 125.6, 0.0); ( 313431.5,
3995861.5, 125.6, 125.6, 0.0);
( 313451.5, 3995861.5, 125.7, 125.7, 0.0); ( 313471.5,
3995861.5, 125.7, 125.7, 0.0);
( 313491.5, 3995861.5, 125.7, 125.7, 0.0); ( 313511.5,
3995861.5, 125.7, 125.7, 0.0);
( 313531.5, 3995861.5, 125.7, 125.7, 0.0); ( 313991.5,
3995861.5, 125.9, 125.9, 0.0);
( 314011.5, 3995861.5, 125.9, 125.9, 0.0); ( 314031.5,
3995861.5, 126.0, 126.0, 0.0);
( 314051.5, 3995861.5, 126.0, 126.0, 0.0); ( 314071.5,
3995861.5, 126.0, 126.0, 0.0);
( 314091.5, 3995861.5, 126.1, 126.1, 0.0); ( 314111.5,
3995861.5, 126.1, 126.1, 0.0);
( 314131.5, 3995861.5, 126.2, 126.2, 0.0); ( 314151.5,
3995861.5, 126.2, 126.2, 0.0);
( 314171.5, 3995861.5, 126.3, 126.3, 0.0); ( 314191.5,
3995861.5, 126.3, 126.3, 0.0);
( 314211.5, 3995861.5, 126.4, 126.4, 0.0); ( 314231.5,
3995861.5, 126.4, 126.4, 0.0);
( 314251.5, 3995861.5, 126.5, 126.5, 0.0); ( 314271.5,
3995861.5, 126.5, 126.5, 0.0);
( 313271.5, 3995881.5, 125.4, 125.4, 0.0); ( 313291.5,
3995881.5, 125.4, 125.4, 0.0);
( 313311.5, 3995881.5, 125.5, 125.5, 0.0); ( 313331.5,
3995881.5, 125.5, 125.5, 0.0);
( 313351.5, 3995881.5, 125.5, 125.5, 0.0); ( 313371.5,
3995881.5, 125.6, 125.6, 0.0);
( 313391.5, 3995881.5, 125.6, 125.6, 0.0); ( 313411.5,
3995881.5, 125.6, 125.6, 0.0);
( 313431.5, 3995881.5, 125.6, 125.6, 0.0); ( 313451.5,
3995881.5, 125.7, 125.7, 0.0);
( 313471.5, 3995881.5, 125.7, 125.7, 0.0); ( 313491.5,
3995881.5, 125.7, 125.7, 0.0);
( 313511.5, 3995881.5, 125.7, 125.7, 0.0); ( 313531.5,
3995881.5, 125.7, 125.7, 0.0);
( 313991.5, 3995881.5, 125.8, 125.8, 0.0); ( 314011.5,
3995881.5, 125.9, 125.9, 0.0);
( 314031.5, 3995881.5, 125.9, 125.9, 0.0); ( 314051.5,
3995881.5, 126.0, 126.0, 0.0);
( 314071.5, 3995881.5, 126.0, 126.0, 0.0); ( 314091.5,
3995881.5, 126.1, 126.1, 0.0);
( 314111.5, 3995881.5, 126.1, 126.1, 0.0); ( 314131.5,
3995881.5, 126.2, 126.2, 0.0);
( 314151.5, 3995881.5, 126.2, 126.2, 0.0); ( 314171.5,
3995881.5, 126.2, 126.2, 0.0);
( 314191.5, 3995881.5, 126.3, 126.3, 0.0); ( 314211.5,
3995881.5, 126.3, 126.3, 0.0);
( 314231.5, 3995881.5, 126.4, 126.4, 0.0); ( 314251.5,
3995881.5, 126.4, 126.4, 0.0);
( 314271.5, 3995881.5, 126.5, 126.5, 0.0); ( 313291.5,
3995901.5, 125.4, 125.4, 0.0);
( 313311.5, 3995901.5, 125.5, 125.5, 0.0); ( 313331.5,
3995901.5, 125.5, 125.5, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 18
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313351.5, 3995901.5, 125.5, 125.5, 0.0); ( 313371.5,
3995901.5, 125.6, 125.6, 0.0);
( 313391.5, 3995901.5, 125.6, 125.6, 0.0); ( 313411.5,
3995901.5, 125.6, 125.6, 0.0);
( 313431.5, 3995901.5, 125.6, 125.6, 0.0); ( 313451.5,
3995901.5, 125.7, 125.7, 0.0);
( 313471.5, 3995901.5, 125.7, 125.7, 0.0); ( 313491.5,
3995901.5, 125.7, 125.7, 0.0);
( 313511.5, 3995901.5, 125.7, 125.7, 0.0); ( 313531.5,
3995901.5, 125.7, 125.7, 0.0);
( 313991.5, 3995901.5, 125.8, 125.8, 0.0); ( 314011.5,
3995901.5, 125.9, 125.9, 0.0);
( 314031.5, 3995901.5, 125.9, 125.9, 0.0); ( 314051.5,
3995901.5, 126.0, 126.0, 0.0);
( 314071.5, 3995901.5, 126.0, 126.0, 0.0); ( 314091.5,
3995901.5, 126.0, 126.0, 0.0);
( 314111.5, 3995901.5, 126.1, 126.1, 0.0); ( 314131.5,
3995901.5, 126.1, 126.1, 0.0);
( 314151.5, 3995901.5, 126.2, 126.2, 0.0); ( 314171.5,
3995901.5, 126.2, 126.2, 0.0);
( 314191.5, 3995901.5, 126.3, 126.3, 0.0); ( 314211.5,
3995901.5, 126.3, 126.3, 0.0);
( 314231.5, 3995901.5, 126.3, 126.3, 0.0); ( 314251.5,
3995901.5, 126.4, 126.4, 0.0);
( 314271.5, 3995901.5, 126.4, 126.4, 0.0); ( 313311.5,
3995921.5, 125.5, 125.5, 0.0);
( 313331.5, 3995921.5, 125.5, 125.5, 0.0); ( 313351.5,
3995921.5, 125.5, 125.5, 0.0);
( 313371.5, 3995921.5, 125.6, 125.6, 0.0); ( 313391.5,
3995921.5, 125.6, 125.6, 0.0);
( 313411.5, 3995921.5, 125.6, 125.6, 0.0); ( 313431.5,
3995921.5, 125.6, 125.6, 0.0);
( 313451.5, 3995921.5, 125.7, 125.7, 0.0); ( 313471.5,
3995921.5, 125.7, 125.7, 0.0);
( 313491.5, 3995921.5, 125.7, 125.7, 0.0); ( 313511.5,
3995921.5, 125.7, 125.7, 0.0);
( 313531.5, 3995921.5, 125.7, 125.7, 0.0); ( 313991.5,
3995921.5, 125.8, 125.8, 0.0);
( 314011.5, 3995921.5, 125.8, 125.8, 0.0); ( 314031.5,
3995921.5, 125.9, 125.9, 0.0);
( 314051.5, 3995921.5, 125.9, 125.9, 0.0); ( 314071.5,
3995921.5, 126.0, 126.0, 0.0);
( 314091.5, 3995921.5, 126.0, 126.0, 0.0); ( 314111.5,
3995921.5, 126.1, 126.1, 0.0);
( 314131.5, 3995921.5, 126.1, 126.1, 0.0); ( 314151.5,
3995921.5, 126.1, 126.1, 0.0);
( 314171.5, 3995921.5, 126.2, 126.2, 0.0); ( 314191.5,
3995921.5, 126.2, 126.2, 0.0);
( 314211.5, 3995921.5, 126.3, 126.3, 0.0); ( 314231.5,
3995921.5, 126.3, 126.3, 0.0);
( 314251.5, 3995921.5, 126.3, 126.3, 0.0); ( 314271.5,
3995921.5, 126.4, 126.4, 0.0);
( 313331.5, 3995941.5, 125.5, 125.5, 0.0); ( 313351.5,
3995941.5, 125.5, 125.5, 0.0);
( 313371.5, 3995941.5, 125.5, 125.5, 0.0); ( 313391.5,
3995941.5, 125.6, 125.6, 0.0);
( 313411.5, 3995941.5, 125.6, 125.6, 0.0); ( 313431.5,
3995941.5, 125.6, 125.6, 0.0);
( 313451.5, 3995941.5, 125.7, 125.7, 0.0); ( 313471.5,
3995941.5, 125.7, 125.7, 0.0);
( 313491.5, 3995941.5, 125.7, 125.7, 0.0); ( 313511.5,
3995941.5, 125.7, 125.7, 0.0);
( 313531.5, 3995941.5, 125.7, 125.7, 0.0); ( 313991.5,
3995941.5, 125.8, 125.8, 0.0);
( 314011.5, 3995941.5, 125.8, 125.8, 0.0); ( 314031.5,
3995941.5, 125.9, 125.9, 0.0);
( 314051.5, 3995941.5, 125.9, 125.9, 0.0); ( 314071.5,
3995941.5, 126.0, 126.0, 0.0);
( 314091.5, 3995941.5, 126.0, 126.0, 0.0); ( 314111.5,
3995941.5, 126.0, 126.0, 0.0);
( 314131.5, 3995941.5, 126.1, 126.1, 0.0); ( 314151.5,
3995941.5, 126.1, 126.1, 0.0);
( 314171.5, 3995941.5, 126.2, 126.2, 0.0); ( 314191.5,
3995941.5, 126.2, 126.2, 0.0);
( 314211.5, 3995941.5, 126.2, 126.2, 0.0); ( 314231.5,
3995941.5, 126.3, 126.3, 0.0);
( 314251.5, 3995941.5, 126.3, 126.3, 0.0); ( 314271.5,
3995941.5, 126.4, 126.4, 0.0);
( 313351.5, 3995961.5, 125.5, 125.5, 0.0); ( 313371.5,
3995961.5, 125.5, 125.5, 0.0);
( 313391.5, 3995961.5, 125.6, 125.6, 0.0); ( 313411.5,
3995961.5, 125.6, 125.6, 0.0);
( 313431.5, 3995961.5, 125.6, 125.6, 0.0); ( 313451.5,
3995961.5, 125.7, 125.7, 0.0);
( 313471.5, 3995961.5, 125.7, 125.7, 0.0); ( 313491.5,
3995961.5, 125.7, 125.7, 0.0);
( 313511.5, 3995961.5, 125.8, 125.8, 0.0); ( 313531.5,
3995961.5, 125.8, 125.8, 0.0);
( 313991.5, 3995961.5, 125.8, 125.8, 0.0); ( 314011.5,
3995961.5, 125.8, 125.8, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 19
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 314031.5, 3995961.5, 125.8, 125.8, 0.0); ( 314051.5,
3995961.5, 125.9, 125.9, 0.0);
( 314071.5, 3995961.5, 125.9, 125.9, 0.0); ( 314091.5,
3995961.5, 126.0, 126.0, 0.0);
( 314111.5, 3995961.5, 126.0, 126.0, 0.0); ( 314131.5,
3995961.5, 126.1, 126.1, 0.0);
( 314151.5, 3995961.5, 126.1, 126.1, 0.0); ( 314171.5,
3995961.5, 126.1, 126.1, 0.0);
( 314191.5, 3995961.5, 126.2, 126.2, 0.0); ( 314211.5,
3995961.5, 126.2, 126.2, 0.0);
( 314231.5, 3995961.5, 126.2, 126.2, 0.0); ( 314251.5,
3995961.5, 126.3, 126.3, 0.0);
( 314271.5, 3995961.5, 126.3, 126.3, 0.0); ( 313371.5,
3995981.5, 125.5, 125.5, 0.0);
( 313391.5, 3995981.5, 125.6, 125.6, 0.0); ( 313411.5,
3995981.5, 125.6, 125.6, 0.0);
( 313431.5, 3995981.5, 125.6, 125.6, 0.0); ( 313451.5,
3995981.5, 125.7, 125.7, 0.0);
( 313471.5, 3995981.5, 125.7, 125.7, 0.0); ( 313491.5,
3995981.5, 125.7, 125.7, 0.0);
( 313511.5, 3995981.5, 125.8, 125.8, 0.0); ( 313531.5,
3995981.5, 125.8, 125.8, 0.0);
( 313991.5, 3995981.5, 125.8, 125.8, 0.0); ( 314011.5,
3995981.5, 125.8, 125.8, 0.0);
( 314031.5, 3995981.5, 125.8, 125.8, 0.0); ( 314051.5,
3995981.5, 125.9, 125.9, 0.0);
( 314071.5, 3995981.5, 125.9, 125.9, 0.0); ( 314091.5,
3995981.5, 126.0, 126.0, 0.0);
( 314111.5, 3995981.5, 126.0, 126.0, 0.0); ( 314131.5,
3995981.5, 126.0, 126.0, 0.0);
( 314151.5, 3995981.5, 126.1, 126.1, 0.0); ( 314171.5,
3995981.5, 126.1, 126.1, 0.0);
( 314191.5, 3995981.5, 126.2, 126.2, 0.0); ( 314211.5,
3995981.5, 126.2, 126.2, 0.0);
( 314231.5, 3995981.5, 126.2, 126.2, 0.0); ( 314251.5,
3995981.5, 126.3, 126.3, 0.0);
( 314271.5, 3995981.5, 126.3, 126.3, 0.0); ( 313391.5,
3996001.5, 125.6, 125.6, 0.0);
( 313411.5, 3996001.5, 125.6, 125.6, 0.0); ( 313431.5,
3996001.5, 125.6, 125.6, 0.0);
( 313451.5, 3996001.5, 125.7, 125.7, 0.0); ( 313471.5,
3996001.5, 125.7, 125.7, 0.0);
( 313491.5, 3996001.5, 125.7, 125.7, 0.0); ( 313511.5,
3996001.5, 125.8, 125.8, 0.0);
( 313531.5, 3996001.5, 125.8, 125.8, 0.0); ( 313991.5,
3996001.5, 125.8, 125.8, 0.0);
( 314011.5, 3996001.5, 125.8, 125.8, 0.0); ( 314031.5,
3996001.5, 125.8, 125.8, 0.0);
( 314051.5, 3996001.5, 125.9, 125.9, 0.0); ( 314071.5,
3996001.5, 125.9, 125.9, 0.0);
( 314091.5, 3996001.5, 126.0, 126.0, 0.0); ( 314111.5,
3996001.5, 126.0, 126.0, 0.0);
( 314131.5, 3996001.5, 126.0, 126.0, 0.0); ( 314151.5,
3996001.5, 126.1, 126.1, 0.0);
( 314171.5, 3996001.5, 126.1, 126.1, 0.0); ( 314191.5,
3996001.5, 126.1, 126.1, 0.0);
( 314211.5, 3996001.5, 126.2, 126.2, 0.0); ( 314231.5,
3996001.5, 126.2, 126.2, 0.0);
( 314251.5, 3996001.5, 126.2, 126.2, 0.0); ( 314271.5,
3996001.5, 126.3, 126.3, 0.0);
( 313411.5, 3996021.5, 125.6, 125.6, 0.0); ( 313431.5,
3996021.5, 125.6, 125.6, 0.0);
( 313451.5, 3996021.5, 125.7, 125.7, 0.0); ( 313471.5,
3996021.5, 125.7, 125.7, 0.0);
( 313491.5, 3996021.5, 125.7, 125.7, 0.0); ( 313511.5,
3996021.5, 125.8, 125.8, 0.0);
( 313531.5, 3996021.5, 125.8, 125.8, 0.0); ( 313991.5,
3996021.5, 125.7, 125.7, 0.0);
( 314011.5, 3996021.5, 125.8, 125.8, 0.0); ( 314031.5,
3996021.5, 125.8, 125.8, 0.0);
( 314051.5, 3996021.5, 125.8, 125.8, 0.0); ( 314071.5,
3996021.5, 125.9, 125.9, 0.0);
( 314091.5, 3996021.5, 125.9, 125.9, 0.0); ( 314111.5,
3996021.5, 126.0, 126.0, 0.0);
( 314131.5, 3996021.5, 126.0, 126.0, 0.0); ( 314151.5,
3996021.5, 126.0, 126.0, 0.0);
( 314171.5, 3996021.5, 126.1, 126.1, 0.0); ( 314191.5,
3996021.5, 126.1, 126.1, 0.0);
( 314211.5, 3996021.5, 126.1, 126.1, 0.0); ( 314231.5,
3996021.5, 126.2, 126.2, 0.0);
( 314251.5, 3996021.5, 126.2, 126.2, 0.0); ( 314271.5,
3996021.5, 126.3, 126.3, 0.0);
( 313431.5, 3996041.5, 125.6, 125.6, 0.0); ( 313451.5,
3996041.5, 125.7, 125.7, 0.0);
( 313471.5, 3996041.5, 125.7, 125.7, 0.0); ( 313491.5,
3996041.5, 125.7, 125.7, 0.0);
( 313511.5, 3996041.5, 125.8, 125.8, 0.0); ( 313531.5,
3996041.5, 125.8, 125.8, 0.0);
( 313991.5, 3996041.5, 125.7, 125.7, 0.0); ( 314011.5,
3996041.5, 125.8, 125.8, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 20
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 314031.5, 3996041.5, 125.8, 125.8, 0.0); ( 314051.5,
3996041.5, 125.8, 125.8, 0.0);
( 314071.5, 3996041.5, 125.9, 125.9, 0.0); ( 314091.5,
3996041.5, 125.9, 125.9, 0.0);
( 314111.5, 3996041.5, 126.0, 126.0, 0.0); ( 314131.5,
3996041.5, 126.0, 126.0, 0.0);
( 314151.5, 3996041.5, 126.0, 126.0, 0.0); ( 314171.5,
3996041.5, 126.0, 126.0, 0.0);
( 314191.5, 3996041.5, 126.1, 126.1, 0.0); ( 314211.5,
3996041.5, 126.1, 126.1, 0.0);
( 314231.5, 3996041.5, 126.2, 126.2, 0.0); ( 314251.5,
3996041.5, 126.2, 126.2, 0.0);
( 314271.5, 3996041.5, 126.2, 126.2, 0.0); ( 313991.5,
3996061.5, 125.7, 125.7, 0.0);
( 314011.5, 3996061.5, 125.7, 125.7, 0.0); ( 314031.5,
3996061.5, 125.8, 125.8, 0.0);
( 314051.5, 3996061.5, 125.8, 125.8, 0.0); ( 314071.5,
3996061.5, 125.9, 125.9, 0.0);
( 314091.5, 3996061.5, 125.9, 125.9, 0.0); ( 314111.5,
3996061.5, 125.9, 125.9, 0.0);
( 314131.5, 3996061.5, 126.0, 126.0, 0.0); ( 314151.5,
3996061.5, 126.0, 126.0, 0.0);
( 314171.5, 3996061.5, 126.0, 126.0, 0.0); ( 314191.5,
3996061.5, 126.1, 126.1, 0.0);
( 314211.5, 3996061.5, 126.1, 126.1, 0.0); ( 314231.5,
3996061.5, 126.1, 126.1, 0.0);
( 314251.5, 3996061.5, 126.2, 126.2, 0.0); ( 314271.5,
3996061.5, 126.2, 126.2, 0.0);
( 313991.5, 3996081.5, 125.7, 125.7, 0.0); ( 314011.5,
3996081.5, 125.7, 125.7, 0.0);
( 314031.5, 3996081.5, 125.8, 125.8, 0.0); ( 314051.5,
3996081.5, 125.8, 125.8, 0.0);
( 314071.5, 3996081.5, 125.8, 125.8, 0.0); ( 314091.5,
3996081.5, 125.9, 125.9, 0.0);
( 314111.5, 3996081.5, 125.9, 125.9, 0.0); ( 314131.5,
3996081.5, 126.0, 126.0, 0.0);
( 314151.5, 3996081.5, 126.0, 126.0, 0.0); ( 314171.5,
3996081.5, 126.0, 126.0, 0.0);
( 314191.5, 3996081.5, 126.1, 126.1, 0.0); ( 314211.5,
3996081.5, 126.1, 126.1, 0.0);
( 314231.5, 3996081.5, 126.1, 126.1, 0.0); ( 314251.5,
3996081.5, 126.2, 126.2, 0.0);
( 314271.5, 3996081.5, 126.2, 126.2, 0.0); ( 313991.5,
3996101.5, 125.7, 125.7, 0.0);
( 314011.5, 3996101.5, 125.7, 125.7, 0.0); ( 314031.5,
3996101.5, 125.8, 125.8, 0.0);
( 314051.5, 3996101.5, 125.8, 125.8, 0.0); ( 314071.5,
3996101.5, 125.8, 125.8, 0.0);
( 314091.5, 3996101.5, 125.9, 125.9, 0.0); ( 314111.5,
3996101.5, 125.9, 125.9, 0.0);
( 314131.5, 3996101.5, 125.9, 125.9, 0.0); ( 314151.5,
3996101.5, 126.0, 126.0, 0.0);
( 314171.5, 3996101.5, 126.0, 126.0, 0.0); ( 314191.5,
3996101.5, 126.0, 126.0, 0.0);
( 314211.5, 3996101.5, 126.1, 126.1, 0.0); ( 314231.5,
3996101.5, 126.1, 126.1, 0.0);
( 314251.5, 3996101.5, 126.1, 126.1, 0.0); ( 314271.5,
3996101.5, 126.2, 126.2, 0.0);
( 313991.5, 3996121.5, 125.6, 125.6, 0.0); ( 314011.5,
3996121.5, 125.7, 125.7, 0.0);
( 314031.5, 3996121.5, 125.7, 125.7, 0.0); ( 314051.5,
3996121.5, 125.8, 125.8, 0.0);
( 314071.5, 3996121.5, 125.8, 125.8, 0.0); ( 314091.5,
3996121.5, 125.8, 125.8, 0.0);
( 314111.5, 3996121.5, 125.9, 125.9, 0.0); ( 314131.5,
3996121.5, 125.9, 125.9, 0.0);
( 314151.5, 3996121.5, 125.9, 125.9, 0.0); ( 314171.5,
3996121.5, 126.0, 126.0, 0.0);
( 314191.5, 3996121.5, 126.0, 126.0, 0.0); ( 314211.5,
3996121.5, 126.0, 126.0, 0.0);
( 314231.5, 3996121.5, 126.1, 126.1, 0.0); ( 314251.5,
3996121.5, 126.1, 126.1, 0.0);
( 314271.5, 3996121.5, 126.1, 126.1, 0.0); ( 313991.5,
3996141.5, 125.6, 125.6, 0.0);
( 314011.5, 3996141.5, 125.7, 125.7, 0.0); ( 314031.5,
3996141.5, 125.7, 125.7, 0.0);
( 314051.5, 3996141.5, 125.7, 125.7, 0.0); ( 314071.5,
3996141.5, 125.8, 125.8, 0.0);
( 314091.5, 3996141.5, 125.8, 125.8, 0.0); ( 314111.5,
3996141.5, 125.8, 125.8, 0.0);
( 314131.5, 3996141.5, 125.9, 125.9, 0.0); ( 314151.5,
3996141.5, 125.9, 125.9, 0.0);
( 314171.5, 3996141.5, 126.0, 126.0, 0.0); ( 314191.5,
3996141.5, 126.0, 126.0, 0.0);
( 314211.5, 3996141.5, 126.0, 126.0, 0.0); ( 314231.5,
3996141.5, 126.1, 126.1, 0.0);
( 314251.5, 3996141.5, 126.1, 126.1, 0.0); ( 314271.5,
3996141.5, 126.1, 126.1, 0.0);
( 313991.5, 3996161.5, 125.6, 125.6, 0.0); ( 314011.5,
3996161.5, 125.6, 125.6, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 21
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 314031.5, 3996161.5, 125.7, 125.7, 0.0); ( 314051.5,
3996161.5, 125.7, 125.7, 0.0);
( 314071.5, 3996161.5, 125.8, 125.8, 0.0); ( 314091.5,
3996161.5, 125.8, 125.8, 0.0);
( 314111.5, 3996161.5, 125.8, 125.8, 0.0); ( 314131.5,
3996161.5, 125.9, 125.9, 0.0);
( 314151.5, 3996161.5, 125.9, 125.9, 0.0); ( 314171.5,
3996161.5, 125.9, 125.9, 0.0);
( 314191.5, 3996161.5, 126.0, 126.0, 0.0); ( 314211.5,
3996161.5, 126.0, 126.0, 0.0);
( 314231.5, 3996161.5, 126.0, 126.0, 0.0); ( 314251.5,
3996161.5, 126.1, 126.1, 0.0);
( 314271.5, 3996161.5, 126.1, 126.1, 0.0); ( 313991.5,
3996181.5, 125.6, 125.6, 0.0);
( 314011.5, 3996181.5, 125.6, 125.6, 0.0); ( 314031.5,
3996181.5, 125.7, 125.7, 0.0);
( 314051.5, 3996181.5, 125.7, 125.7, 0.0); ( 314071.5,
3996181.5, 125.7, 125.7, 0.0);
( 314091.5, 3996181.5, 125.8, 125.8, 0.0); ( 314111.5,
3996181.5, 125.8, 125.8, 0.0);
( 314131.5, 3996181.5, 125.8, 125.8, 0.0); ( 314151.5,
3996181.5, 125.9, 125.9, 0.0);
( 314171.5, 3996181.5, 125.9, 125.9, 0.0); ( 314191.5,
3996181.5, 126.0, 126.0, 0.0);
( 314211.5, 3996181.5, 126.0, 126.0, 0.0); ( 314231.5,
3996181.5, 126.0, 126.0, 0.0);
( 314251.5, 3996181.5, 126.0, 126.0, 0.0); ( 314271.5,
3996181.5, 126.1, 126.1, 0.0);
( 313991.5, 3996201.5, 125.6, 125.6, 0.0); ( 314011.5,
3996201.5, 125.6, 125.6, 0.0);
( 314031.5, 3996201.5, 125.6, 125.6, 0.0); ( 314051.5,
3996201.5, 125.7, 125.7, 0.0);
( 314071.5, 3996201.5, 125.7, 125.7, 0.0); ( 314091.5,
3996201.5, 125.7, 125.7, 0.0);
( 314111.5, 3996201.5, 125.8, 125.8, 0.0); ( 314131.5,
3996201.5, 125.8, 125.8, 0.0);
( 314151.5, 3996201.5, 125.8, 125.8, 0.0); ( 314171.5,
3996201.5, 125.9, 125.9, 0.0);
( 314191.5, 3996201.5, 125.9, 125.9, 0.0); ( 314211.5,
3996201.5, 126.0, 126.0, 0.0);
( 314231.5, 3996201.5, 126.0, 126.0, 0.0); ( 314251.5,
3996201.5, 126.0, 126.0, 0.0);
( 314271.5, 3996201.5, 126.1, 126.1, 0.0); ( 313991.5,
3996221.5, 125.5, 125.5, 0.0);
( 314011.5, 3996221.5, 125.6, 125.6, 0.0); ( 314031.5,
3996221.5, 125.6, 125.6, 0.0);
( 314051.5, 3996221.5, 125.6, 125.6, 0.0); ( 314071.5,
3996221.5, 125.7, 125.7, 0.0);
( 314091.5, 3996221.5, 125.7, 125.7, 0.0); ( 314111.5,
3996221.5, 125.8, 125.8, 0.0);
( 314131.5, 3996221.5, 125.8, 125.8, 0.0); ( 314151.5,
3996221.5, 125.8, 125.8, 0.0);
( 314171.5, 3996221.5, 125.9, 125.9, 0.0); ( 314191.5,
3996221.5, 125.9, 125.9, 0.0);
( 314211.5, 3996221.5, 125.9, 125.9, 0.0); ( 314231.5,
3996221.5, 126.0, 126.0, 0.0);
( 314251.5, 3996221.5, 126.0, 126.0, 0.0); ( 314271.5,
3996221.5, 126.0, 126.0, 0.0);
( 313991.5, 3996241.5, 125.5, 125.5, 0.0); ( 314011.5,
3996241.5, 125.6, 125.6, 0.0);
( 314031.5, 3996241.5, 125.6, 125.6, 0.0); ( 314051.5,
3996241.5, 125.6, 125.6, 0.0);
( 314071.5, 3996241.5, 125.7, 125.7, 0.0); ( 314091.5,
3996241.5, 125.7, 125.7, 0.0);
( 314111.5, 3996241.5, 125.7, 125.7, 0.0); ( 314131.5,
3996241.5, 125.8, 125.8, 0.0);
( 314151.5, 3996241.5, 125.8, 125.8, 0.0); ( 314171.5,
3996241.5, 125.8, 125.8, 0.0);
( 314191.5, 3996241.5, 125.9, 125.9, 0.0); ( 314211.5,
3996241.5, 125.9, 125.9, 0.0);
( 314231.5, 3996241.5, 125.9, 125.9, 0.0); ( 314251.5,
3996241.5, 126.0, 126.0, 0.0);
( 314271.5, 3996241.5, 126.0, 126.0, 0.0); ( 313991.5,
3996261.5, 125.5, 125.5, 0.0);
( 314011.5, 3996261.5, 125.5, 125.5, 0.0); ( 314031.5,
3996261.5, 125.6, 125.6, 0.0);
( 314051.5, 3996261.5, 125.6, 125.6, 0.0); ( 314071.5,
3996261.5, 125.6, 125.6, 0.0);
( 314091.5, 3996261.5, 125.7, 125.7, 0.0); ( 314111.5,
3996261.5, 125.7, 125.7, 0.0);
( 314131.5, 3996261.5, 125.7, 125.7, 0.0); ( 314151.5,
3996261.5, 125.8, 125.8, 0.0);
( 314171.5, 3996261.5, 125.8, 125.8, 0.0); ( 314191.5,
3996261.5, 125.8, 125.8, 0.0);
( 314211.5, 3996261.5, 125.9, 125.9, 0.0); ( 314231.5,
3996261.5, 125.9, 125.9, 0.0);
( 314251.5, 3996261.5, 126.0, 126.0, 0.0); ( 314271.5,
3996261.5, 126.0, 126.0, 0.0);
( 313991.5, 3996281.5, 125.5, 125.5, 0.0); ( 314011.5,
3996281.5, 125.5, 125.5, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 22
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 314031.5, 3996281.5, 125.5, 125.5, 0.0); ( 314051.5,
3996281.5, 125.6, 125.6, 0.0);
( 314071.5, 3996281.5, 125.6, 125.6, 0.0); ( 314091.5,
3996281.5, 125.6, 125.6, 0.0);
( 314111.5, 3996281.5, 125.7, 125.7, 0.0); ( 314131.5,
3996281.5, 125.7, 125.7, 0.0);
( 314151.5, 3996281.5, 125.8, 125.8, 0.0); ( 314171.5,
3996281.5, 125.8, 125.8, 0.0);
( 314191.5, 3996281.5, 125.8, 125.8, 0.0); ( 314211.5,
3996281.5, 125.9, 125.9, 0.0);
( 314231.5, 3996281.5, 125.9, 125.9, 0.0); ( 314251.5,
3996281.5, 125.9, 125.9, 0.0);
( 314271.5, 3996281.5, 126.0, 126.0, 0.0); ( 313811.5,
3996301.5, 125.2, 125.2, 0.0);
( 313831.5, 3996301.5, 125.2, 125.2, 0.0); ( 313851.5,
3996301.5, 125.2, 125.2, 0.0);
( 313871.5, 3996301.5, 125.3, 125.3, 0.0); ( 313891.5,
3996301.5, 125.3, 125.3, 0.0);
( 313911.5, 3996301.5, 125.3, 125.3, 0.0); ( 313931.5,
3996301.5, 125.4, 125.4, 0.0);
( 313951.5, 3996301.5, 125.4, 125.4, 0.0); ( 313971.5,
3996301.5, 125.4, 125.4, 0.0);
( 313991.5, 3996301.5, 125.5, 125.5, 0.0); ( 314011.5,
3996301.5, 125.5, 125.5, 0.0);
( 314031.5, 3996301.5, 125.5, 125.5, 0.0); ( 314051.5,
3996301.5, 125.6, 125.6, 0.0);
( 314071.5, 3996301.5, 125.6, 125.6, 0.0); ( 314091.5,
3996301.5, 125.6, 125.6, 0.0);
( 314111.5, 3996301.5, 125.7, 125.7, 0.0); ( 314131.5,
3996301.5, 125.7, 125.7, 0.0);
( 314151.5, 3996301.5, 125.7, 125.7, 0.0); ( 314171.5,
3996301.5, 125.8, 125.8, 0.0);
( 314191.5, 3996301.5, 125.8, 125.8, 0.0); ( 314211.5,
3996301.5, 125.8, 125.8, 0.0);
( 314231.5, 3996301.5, 125.9, 125.9, 0.0); ( 314251.5,
3996301.5, 125.9, 125.9, 0.0);
( 314271.5, 3996301.5, 125.9, 125.9, 0.0); ( 313811.5,
3996321.5, 125.2, 125.2, 0.0);
( 313831.5, 3996321.5, 125.2, 125.2, 0.0); ( 313851.5,
3996321.5, 125.2, 125.2, 0.0);
( 313871.5, 3996321.5, 125.2, 125.2, 0.0); ( 313891.5,
3996321.5, 125.3, 125.3, 0.0);
( 313911.5, 3996321.5, 125.3, 125.3, 0.0); ( 313931.5,
3996321.5, 125.3, 125.3, 0.0);
( 313951.5, 3996321.5, 125.4, 125.4, 0.0); ( 313971.5,
3996321.5, 125.4, 125.4, 0.0);
( 313991.5, 3996321.5, 125.4, 125.4, 0.0); ( 314011.5,
3996321.5, 125.5, 125.5, 0.0);
( 314031.5, 3996321.5, 125.5, 125.5, 0.0); ( 314051.5,
3996321.5, 125.5, 125.5, 0.0);
( 314071.5, 3996321.5, 125.6, 125.6, 0.0); ( 314091.5,
3996321.5, 125.6, 125.6, 0.0);
( 314111.5, 3996321.5, 125.6, 125.6, 0.0); ( 314131.5,
3996321.5, 125.7, 125.7, 0.0);
( 314151.5, 3996321.5, 125.7, 125.7, 0.0); ( 314171.5,
3996321.5, 125.7, 125.7, 0.0);
( 314191.5, 3996321.5, 125.8, 125.8, 0.0); ( 314211.5,
3996321.5, 125.8, 125.8, 0.0);
( 314231.5, 3996321.5, 125.8, 125.8, 0.0); ( 314251.5,
3996321.5, 125.9, 125.9, 0.0);
( 314271.5, 3996321.5, 125.9, 125.9, 0.0); ( 313811.5,
3996341.5, 125.1, 125.1, 0.0);
( 313831.5, 3996341.5, 125.2, 125.2, 0.0); ( 313851.5,
3996341.5, 125.2, 125.2, 0.0);
( 313871.5, 3996341.5, 125.2, 125.2, 0.0); ( 313891.5,
3996341.5, 125.3, 125.3, 0.0);
( 313911.5, 3996341.5, 125.3, 125.3, 0.0); ( 313931.5,
3996341.5, 125.3, 125.3, 0.0);
( 313951.5, 3996341.5, 125.4, 125.4, 0.0); ( 313971.5,
3996341.5, 125.4, 125.4, 0.0);
( 313991.5, 3996341.5, 125.4, 125.4, 0.0); ( 314011.5,
3996341.5, 125.5, 125.5, 0.0);
( 314031.5, 3996341.5, 125.5, 125.5, 0.0); ( 314051.5,
3996341.5, 125.5, 125.5, 0.0);
( 314071.5, 3996341.5, 125.5, 125.5, 0.0); ( 314091.5,
3996341.5, 125.6, 125.6, 0.0);
( 314111.5, 3996341.5, 125.6, 125.6, 0.0); ( 314131.5,
3996341.5, 125.6, 125.6, 0.0);
( 314151.5, 3996341.5, 125.7, 125.7, 0.0); ( 314171.5,
3996341.5, 125.7, 125.7, 0.0);
( 314191.5, 3996341.5, 125.7, 125.7, 0.0); ( 314211.5,
3996341.5, 125.8, 125.8, 0.0);
( 314231.5, 3996341.5, 125.8, 125.8, 0.0); ( 314251.5,
3996341.5, 125.8, 125.8, 0.0);
( 314271.5, 3996341.5, 125.9, 125.9, 0.0); ( 313811.5,
3996361.5, 125.1, 125.1, 0.0);
( 313831.5, 3996361.5, 125.1, 125.1, 0.0); ( 313851.5,
3996361.5, 125.2, 125.2, 0.0);
( 313871.5, 3996361.5, 125.2, 125.2, 0.0); ( 313891.5,
3996361.5, 125.2, 125.2, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 23
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313911.5, 3996361.5, 125.3, 125.3, 0.0); ( 313931.5,
3996361.5, 125.3, 125.3, 0.0);
( 313951.5, 3996361.5, 125.3, 125.3, 0.0); ( 313971.5,
3996361.5, 125.4, 125.4, 0.0);
( 313991.5, 3996361.5, 125.4, 125.4, 0.0); ( 314011.5,
3996361.5, 125.4, 125.4, 0.0);
( 314031.5, 3996361.5, 125.5, 125.5, 0.0); ( 314051.5,
3996361.5, 125.5, 125.5, 0.0);
( 314071.5, 3996361.5, 125.5, 125.5, 0.0); ( 314091.5,
3996361.5, 125.6, 125.6, 0.0);
( 314111.5, 3996361.5, 125.6, 125.6, 0.0); ( 314131.5,
3996361.5, 125.6, 125.6, 0.0);
( 314151.5, 3996361.5, 125.6, 125.6, 0.0); ( 314171.5,
3996361.5, 125.7, 125.7, 0.0);
( 314191.5, 3996361.5, 125.7, 125.7, 0.0); ( 314211.5,
3996361.5, 125.7, 125.7, 0.0);
( 314231.5, 3996361.5, 125.8, 125.8, 0.0); ( 314251.5,
3996361.5, 125.8, 125.8, 0.0);
( 314271.5, 3996361.5, 125.8, 125.8, 0.0); ( 313731.5,
3996381.5, 125.0, 125.0, 0.0);
( 313751.5, 3996381.5, 125.0, 125.0, 0.0); ( 313771.5,
3996381.5, 125.0, 125.0, 0.0);
( 313791.5, 3996381.5, 125.0, 125.0, 0.0); ( 313811.5,
3996381.5, 125.1, 125.1, 0.0);
( 313831.5, 3996381.5, 125.1, 125.1, 0.0); ( 313851.5,
3996381.5, 125.1, 125.1, 0.0);
( 313871.5, 3996381.5, 125.2, 125.2, 0.0); ( 313891.5,
3996381.5, 125.2, 125.2, 0.0);
( 313911.5, 3996381.5, 125.2, 125.2, 0.0); ( 313931.5,
3996381.5, 125.3, 125.3, 0.0);
( 313951.5, 3996381.5, 125.3, 125.3, 0.0); ( 313971.5,
3996381.5, 125.3, 125.3, 0.0);
( 313991.5, 3996381.5, 125.4, 125.4, 0.0); ( 314011.5,
3996381.5, 125.4, 125.4, 0.0);
( 314031.5, 3996381.5, 125.4, 125.4, 0.0); ( 314051.5,
3996381.5, 125.5, 125.5, 0.0);
( 314071.5, 3996381.5, 125.5, 125.5, 0.0); ( 314091.5,
3996381.5, 125.5, 125.5, 0.0);
( 314111.5, 3996381.5, 125.6, 125.6, 0.0); ( 314131.5,
3996381.5, 125.6, 125.6, 0.0);
( 314151.5, 3996381.5, 125.6, 125.6, 0.0); ( 314171.5,
3996381.5, 125.6, 125.6, 0.0);
( 314191.5, 3996381.5, 125.7, 125.7, 0.0); ( 314211.5,
3996381.5, 125.7, 125.7, 0.0);
( 314231.5, 3996381.5, 125.8, 125.8, 0.0); ( 314251.5,
3996381.5, 125.8, 125.8, 0.0);
( 314271.5, 3996381.5, 125.8, 125.8, 0.0); ( 313731.5,
3996401.5, 125.0, 125.0, 0.0);
( 313751.5, 3996401.5, 125.0, 125.0, 0.0); ( 313771.5,
3996401.5, 125.0, 125.0, 0.0);
( 313791.5, 3996401.5, 125.0, 125.0, 0.0); ( 313811.5,
3996401.5, 125.0, 125.0, 0.0);
( 313831.5, 3996401.5, 125.1, 125.1, 0.0); ( 313851.5,
3996401.5, 125.1, 125.1, 0.0);
( 313871.5, 3996401.5, 125.1, 125.1, 0.0); ( 313891.5,
3996401.5, 125.2, 125.2, 0.0);
( 313911.5, 3996401.5, 125.2, 125.2, 0.0); ( 313931.5,
3996401.5, 125.2, 125.2, 0.0);
( 313951.5, 3996401.5, 125.3, 125.3, 0.0); ( 313971.5,
3996401.5, 125.3, 125.3, 0.0);
( 313991.5, 3996401.5, 125.3, 125.3, 0.0); ( 314011.5,
3996401.5, 125.4, 125.4, 0.0);
( 314031.5, 3996401.5, 125.4, 125.4, 0.0); ( 314051.5,
3996401.5, 125.4, 125.4, 0.0);
( 314071.5, 3996401.5, 125.5, 125.5, 0.0); ( 314091.5,
3996401.5, 125.5, 125.5, 0.0);
( 314111.5, 3996401.5, 125.5, 125.5, 0.0); ( 314131.5,
3996401.5, 125.6, 125.6, 0.0);
( 314151.5, 3996401.5, 125.6, 125.6, 0.0); ( 314171.5,
3996401.5, 125.6, 125.6, 0.0);
( 314191.5, 3996401.5, 125.6, 125.6, 0.0); ( 314211.5,
3996401.5, 125.7, 125.7, 0.0);
( 314231.5, 3996401.5, 125.7, 125.7, 0.0); ( 314251.5,
3996401.5, 125.8, 125.8, 0.0);
( 314271.5, 3996401.5, 125.8, 125.8, 0.0); ( 313731.5,
3996421.5, 124.9, 124.9, 0.0);
( 313751.5, 3996421.5, 124.9, 124.9, 0.0); ( 313771.5,
3996421.5, 125.0, 125.0, 0.0);
( 313791.5, 3996421.5, 125.0, 125.0, 0.0); ( 313811.5,
3996421.5, 125.0, 125.0, 0.0);
( 313831.5, 3996421.5, 125.1, 125.1, 0.0); ( 313851.5,
3996421.5, 125.1, 125.1, 0.0);
( 313871.5, 3996421.5, 125.1, 125.1, 0.0); ( 313891.5,
3996421.5, 125.1, 125.1, 0.0);
( 313911.5, 3996421.5, 125.2, 125.2, 0.0); ( 313931.5,
3996421.5, 125.2, 125.2, 0.0);
( 313951.5, 3996421.5, 125.2, 125.2, 0.0); ( 313971.5,
3996421.5, 125.3, 125.3, 0.0);
( 313991.5, 3996421.5, 125.3, 125.3, 0.0); ( 314011.5,
3996421.5, 125.3, 125.3, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 24
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 314031.5, 3996421.5, 125.4, 125.4, 0.0); ( 314051.5,
3996421.5, 125.4, 125.4, 0.0);
( 314071.5, 3996421.5, 125.5, 125.5, 0.0); ( 314091.5,
3996421.5, 125.5, 125.5, 0.0);
( 314111.5, 3996421.5, 125.5, 125.5, 0.0); ( 314131.5,
3996421.5, 125.5, 125.5, 0.0);
( 314151.5, 3996421.5, 125.6, 125.6, 0.0); ( 314171.5,
3996421.5, 125.6, 125.6, 0.0);
( 314191.5, 3996421.5, 125.6, 125.6, 0.0); ( 314211.5,
3996421.5, 125.7, 125.7, 0.0);
( 314231.5, 3996421.5, 125.7, 125.7, 0.0); ( 314251.5,
3996421.5, 125.7, 125.7, 0.0);
( 314271.5, 3996421.5, 125.8, 125.8, 0.0); ( 313751.5,
3996441.5, 124.9, 124.9, 0.0);
( 313771.5, 3996441.5, 124.9, 124.9, 0.0); ( 313791.5,
3996441.5, 125.0, 125.0, 0.0);
( 313811.5, 3996441.5, 125.0, 125.0, 0.0); ( 313831.5,
3996441.5, 125.0, 125.0, 0.0);
( 313851.5, 3996441.5, 125.1, 125.1, 0.0); ( 313871.5,
3996441.5, 125.1, 125.1, 0.0);
( 313891.5, 3996441.5, 125.1, 125.1, 0.0); ( 313911.5,
3996441.5, 125.2, 125.2, 0.0);
( 313931.5, 3996441.5, 125.2, 125.2, 0.0); ( 313951.5,
3996441.5, 125.2, 125.2, 0.0);
( 313971.5, 3996441.5, 125.3, 125.3, 0.0); ( 313991.5,
3996441.5, 125.3, 125.3, 0.0);
( 314011.5, 3996441.5, 125.3, 125.3, 0.0); ( 314031.5,
3996441.5, 125.3, 125.3, 0.0);
( 314051.5, 3996441.5, 125.4, 125.4, 0.0); ( 314071.5,
3996441.5, 125.4, 125.4, 0.0);
( 314091.5, 3996441.5, 125.5, 125.5, 0.0); ( 314111.5,
3996441.5, 125.5, 125.5, 0.0);
( 314131.5, 3996441.5, 125.5, 125.5, 0.0); ( 314151.5,
3996441.5, 125.5, 125.5, 0.0);
( 314171.5, 3996441.5, 125.6, 125.6, 0.0); ( 314191.5,
3996441.5, 125.6, 125.6, 0.0);
( 314211.5, 3996441.5, 125.6, 125.6, 0.0); ( 314231.5,
3996441.5, 125.7, 125.7, 0.0);
( 314251.5, 3996441.5, 125.7, 125.7, 0.0); ( 314271.5,
3996441.5, 125.7, 125.7, 0.0);
( 313751.5, 3996461.5, 124.9, 124.9, 0.0); ( 313771.5,
3996461.5, 124.9, 124.9, 0.0);
( 313791.5, 3996461.5, 124.9, 124.9, 0.0); ( 313811.5,
3996461.5, 125.0, 125.0, 0.0);
( 313831.5, 3996461.5, 125.0, 125.0, 0.0); ( 313851.5,
3996461.5, 125.0, 125.0, 0.0);
( 313871.5, 3996461.5, 125.1, 125.1, 0.0); ( 313891.5,
3996461.5, 125.1, 125.1, 0.0);
( 313911.5, 3996461.5, 125.1, 125.1, 0.0); ( 313931.5,
3996461.5, 125.2, 125.2, 0.0);
( 313951.5, 3996461.5, 125.2, 125.2, 0.0); ( 313971.5,
3996461.5, 125.2, 125.2, 0.0);
( 313991.5, 3996461.5, 125.3, 125.3, 0.0); ( 314011.5,
3996461.5, 125.3, 125.3, 0.0);
( 314031.5, 3996461.5, 125.3, 125.3, 0.0); ( 314051.5,
3996461.5, 125.3, 125.3, 0.0);
( 314071.5, 3996461.5, 125.4, 125.4, 0.0); ( 314091.5,
3996461.5, 125.4, 125.4, 0.0);
( 314111.5, 3996461.5, 125.5, 125.5, 0.0); ( 314131.5,
3996461.5, 125.5, 125.5, 0.0);
( 314151.5, 3996461.5, 125.5, 125.5, 0.0); ( 314171.5,
3996461.5, 125.5, 125.5, 0.0);
( 314191.5, 3996461.5, 125.6, 125.6, 0.0); ( 314211.5,
3996461.5, 125.6, 125.6, 0.0);
( 314231.5, 3996461.5, 125.6, 125.6, 0.0); ( 314251.5,
3996461.5, 125.7, 125.7, 0.0);
( 314271.5, 3996461.5, 125.7, 125.7, 0.0); ( 313751.5,
3996481.5, 124.8, 124.8, 0.0);
( 313771.5, 3996481.5, 124.9, 124.9, 0.0); ( 313791.5,
3996481.5, 124.9, 124.9, 0.0);
( 313811.5, 3996481.5, 124.9, 124.9, 0.0); ( 313831.5,
3996481.5, 125.0, 125.0, 0.0);
( 313851.5, 3996481.5, 125.0, 125.0, 0.0); ( 313871.5,
3996481.5, 125.0, 125.0, 0.0);
( 313891.5, 3996481.5, 125.1, 125.1, 0.0); ( 313911.5,
3996481.5, 125.1, 125.1, 0.0);
( 313931.5, 3996481.5, 125.1, 125.1, 0.0); ( 313951.5,
3996481.5, 125.2, 125.2, 0.0);
( 313971.5, 3996481.5, 125.2, 125.2, 0.0); ( 313991.5,
3996481.5, 125.2, 125.2, 0.0);
( 314011.5, 3996481.5, 125.3, 125.3, 0.0); ( 314031.5,
3996481.5, 125.3, 125.3, 0.0);
( 314051.5, 3996481.5, 125.3, 125.3, 0.0); ( 314071.5,
3996481.5, 125.4, 125.4, 0.0);
( 314091.5, 3996481.5, 125.4, 125.4, 0.0); ( 314111.5,
3996481.5, 125.4, 125.4, 0.0);
( 314131.5, 3996481.5, 125.5, 125.5, 0.0); ( 314151.5,
3996481.5, 125.5, 125.5, 0.0);
( 314171.5, 3996481.5, 125.5, 125.5, 0.0); ( 314191.5,
3996481.5, 125.5, 125.5, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 25
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 314211.5, 3996481.5, 125.6, 125.6, 0.0); ( 314231.5,
3996481.5, 125.6, 125.6, 0.0);
( 314251.5, 3996481.5, 125.6, 125.6, 0.0); ( 314271.5,
3996481.5, 125.7, 125.7, 0.0);
( 313771.5, 3996501.5, 124.8, 124.8, 0.0); ( 313791.5,
3996501.5, 124.9, 124.9, 0.0);
( 313811.5, 3996501.5, 124.9, 124.9, 0.0); ( 313831.5,
3996501.5, 125.0, 125.0, 0.0);
( 313851.5, 3996501.5, 125.0, 125.0, 0.0); ( 313871.5,
3996501.5, 125.0, 125.0, 0.0);
( 313891.5, 3996501.5, 125.0, 125.0, 0.0); ( 313911.5,
3996501.5, 125.1, 125.1, 0.0);
( 313931.5, 3996501.5, 125.1, 125.1, 0.0); ( 313951.5,
3996501.5, 125.1, 125.1, 0.0);
( 313971.5, 3996501.5, 125.2, 125.2, 0.0); ( 313991.5,
3996501.5, 125.2, 125.2, 0.0);
( 314011.5, 3996501.5, 125.2, 125.2, 0.0); ( 314031.5,
3996501.5, 125.3, 125.3, 0.0);
( 314051.5, 3996501.5, 125.3, 125.3, 0.0); ( 314071.5,
3996501.5, 125.3, 125.3, 0.0);
( 314091.5, 3996501.5, 125.4, 125.4, 0.0); ( 314111.5,
3996501.5, 125.4, 125.4, 0.0);
( 314131.5, 3996501.5, 125.4, 125.4, 0.0); ( 314151.5,
3996501.5, 125.5, 125.5, 0.0);
( 314171.5, 3996501.5, 125.5, 125.5, 0.0); ( 314191.5,
3996501.5, 125.5, 125.5, 0.0);
( 314211.5, 3996501.5, 125.6, 125.6, 0.0); ( 314231.5,
3996501.5, 125.6, 125.6, 0.0);
( 314251.5, 3996501.5, 125.6, 125.6, 0.0); ( 314271.5,
3996501.5, 125.6, 125.6, 0.0);
( 313771.5, 3996521.5, 124.8, 124.8, 0.0); ( 313791.5,
3996521.5, 124.8, 124.8, 0.0);
( 313811.5, 3996521.5, 124.9, 124.9, 0.0); ( 313831.5,
3996521.5, 124.9, 124.9, 0.0);
( 313851.5, 3996521.5, 125.0, 125.0, 0.0); ( 313871.5,
3996521.5, 125.0, 125.0, 0.0);
( 313891.5, 3996521.5, 125.0, 125.0, 0.0); ( 313911.5,
3996521.5, 125.0, 125.0, 0.0);
( 313931.5, 3996521.5, 125.1, 125.1, 0.0); ( 313951.5,
3996521.5, 125.1, 125.1, 0.0);
( 313971.5, 3996521.5, 125.1, 125.1, 0.0); ( 313991.5,
3996521.5, 125.2, 125.2, 0.0);
( 314011.5, 3996521.5, 125.2, 125.2, 0.0); ( 314031.5,
3996521.5, 125.2, 125.2, 0.0);
( 314051.5, 3996521.5, 125.3, 125.3, 0.0); ( 314071.5,
3996521.5, 125.3, 125.3, 0.0);
( 314091.5, 3996521.5, 125.3, 125.3, 0.0); ( 314111.5,
3996521.5, 125.4, 125.4, 0.0);
( 314131.5, 3996521.5, 125.4, 125.4, 0.0); ( 314151.5,
3996521.5, 125.4, 125.4, 0.0);
( 314171.5, 3996521.5, 125.5, 125.5, 0.0); ( 314191.5,
3996521.5, 125.5, 125.5, 0.0);
( 314211.5, 3996521.5, 125.5, 125.5, 0.0); ( 314231.5,
3996521.5, 125.6, 125.6, 0.0);
( 314251.5, 3996521.5, 125.6, 125.6, 0.0); ( 314271.5,
3996521.5, 125.6, 125.6, 0.0);
( 313791.5, 3996541.5, 124.8, 124.8, 0.0); ( 313811.5,
3996541.5, 124.9, 124.9, 0.0);
( 313831.5, 3996541.5, 124.9, 124.9, 0.0); ( 313851.5,
3996541.5, 124.9, 124.9, 0.0);
( 313871.5, 3996541.5, 125.0, 125.0, 0.0); ( 313891.5,
3996541.5, 125.0, 125.0, 0.0);
( 313911.5, 3996541.5, 125.0, 125.0, 0.0); ( 313931.5,
3996541.5, 125.1, 125.1, 0.0);
( 313951.5, 3996541.5, 125.1, 125.1, 0.0); ( 313971.5,
3996541.5, 125.1, 125.1, 0.0);
( 313991.5, 3996541.5, 125.1, 125.1, 0.0); ( 314011.5,
3996541.5, 125.2, 125.2, 0.0);
( 314031.5, 3996541.5, 125.2, 125.2, 0.0); ( 314051.5,
3996541.5, 125.2, 125.2, 0.0);
( 314071.5, 3996541.5, 125.3, 125.3, 0.0); ( 314091.5,
3996541.5, 125.3, 125.3, 0.0);
( 314111.5, 3996541.5, 125.3, 125.3, 0.0); ( 314131.5,
3996541.5, 125.4, 125.4, 0.0);
( 314151.5, 3996541.5, 125.4, 125.4, 0.0); ( 314171.5,
3996541.5, 125.5, 125.5, 0.0);
( 314191.5, 3996541.5, 125.5, 125.5, 0.0); ( 314211.5,
3996541.5, 125.5, 125.5, 0.0);
( 314231.5, 3996541.5, 125.5, 125.5, 0.0); ( 314251.5,
3996541.5, 125.6, 125.6, 0.0);
( 314271.5, 3996541.5, 125.6, 125.6, 0.0); ( 313791.5,
3996561.5, 124.8, 124.8, 0.0);
( 313811.5, 3996561.5, 124.8, 124.8, 0.0); ( 313831.5,
3996561.5, 124.9, 124.9, 0.0);
( 313851.5, 3996561.5, 124.9, 124.9, 0.0); ( 313871.5,
3996561.5, 124.9, 124.9, 0.0);
( 313891.5, 3996561.5, 125.0, 125.0, 0.0); ( 313911.5,
3996561.5, 125.0, 125.0, 0.0);
( 313931.5, 3996561.5, 125.0, 125.0, 0.0); ( 313951.5,
3996561.5, 125.1, 125.1, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 26
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** DISCRETE CARTESIAN RECEPTORS ***
(X-COORD, Y-COORD, ZELEV, ZHILL, ZFLAG)
(METERS)
( 313971.5, 3996561.5, 125.1, 125.1, 0.0); ( 313991.5,
3996561.5, 125.1, 125.1, 0.0);
( 314011.5, 3996561.5, 125.2, 125.2, 0.0); ( 314031.5,
3996561.5, 125.2, 125.2, 0.0);
( 314051.5, 3996561.5, 125.2, 125.2, 0.0); ( 314071.5,
3996561.5, 125.2, 125.2, 0.0);
( 314091.5, 3996561.5, 125.3, 125.3, 0.0); ( 314111.5,
3996561.5, 125.3, 125.3, 0.0);
( 314131.5, 3996561.5, 125.3, 125.3, 0.0); ( 314151.5,
3996561.5, 125.4, 125.4, 0.0);
( 314171.5, 3996561.5, 125.4, 125.4, 0.0); ( 314191.5,
3996561.5, 125.5, 125.5, 0.0);
( 314211.5, 3996561.5, 125.5, 125.5, 0.0); ( 314231.5,
3996561.5, 125.5, 125.5, 0.0);
( 314251.5, 3996561.5, 125.5, 125.5, 0.0); ( 314271.5,
3996561.5, 125.6, 125.6, 0.0);
( 313791.5, 3996581.5, 124.8, 124.8, 0.0); ( 313811.5,
3996581.5, 124.8, 124.8, 0.0);
( 313831.5, 3996581.5, 124.9, 124.9, 0.0); ( 313851.5,
3996581.5, 124.9, 124.9, 0.0);
( 313871.5, 3996581.5, 124.9, 124.9, 0.0); ( 313891.5,
3996581.5, 125.0, 125.0, 0.0);
( 313911.5, 3996581.5, 125.0, 125.0, 0.0); ( 313931.5,
3996581.5, 125.0, 125.0, 0.0);
( 313951.5, 3996581.5, 125.0, 125.0, 0.0); ( 313971.5,
3996581.5, 125.1, 125.1, 0.0);
( 313991.5, 3996581.5, 125.1, 125.1, 0.0); ( 314011.5,
3996581.5, 125.1, 125.1, 0.0);
( 314031.5, 3996581.5, 125.2, 125.2, 0.0); ( 314051.5,
3996581.5, 125.2, 125.2, 0.0);
( 314071.5, 3996581.5, 125.2, 125.2, 0.0); ( 314091.5,
3996581.5, 125.3, 125.3, 0.0);
( 314111.5, 3996581.5, 125.3, 125.3, 0.0); ( 314131.5,
3996581.5, 125.3, 125.3, 0.0);
( 314151.5, 3996581.5, 125.3, 125.3, 0.0); ( 314171.5,
3996581.5, 125.4, 125.4, 0.0);
( 314191.5, 3996581.5, 125.4, 125.4, 0.0); ( 314211.5,
3996581.5, 125.5, 125.5, 0.0);
( 314231.5, 3996581.5, 125.5, 125.5, 0.0); ( 314251.5,
3996581.5, 125.5, 125.5, 0.0);
( 314271.5, 3996581.5, 125.5, 125.5, 0.0); ( 313529.1,
3996060.3, 125.8, 125.8, 0.0);
( 313510.2, 3996059.1, 125.8, 125.8, 0.0); ( 313491.4,
3996062.8, 125.8, 125.8, 0.0);
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 27
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** METEOROLOGICAL DAYS SELECTED FOR
PROCESSING ***
(1=YES; 0=NO)
1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1
1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1
1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1
1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1
1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1
1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1
1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1
1 1 1 1 1 1 1 1 1 1 1 1 1 1 1
NOTE: METEOROLOGICAL DATA ACTUALLY PROCESSED WILL ALSO DEPEND ON WHAT IS INCLUDED IN THE DATA FILE.
*** UPPER BOUND OF FIRST THROUGH FIFTH WIND SPEED
CATEGORIES ***
(METERS/SEC)
1.54, 3.09, 5.14, 8.23,
10.80,
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 28
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** UP TO THE FIRST 24 HOURS OF METEOROLOGICAL
DATA ***
Surface file: C:\Users\kheck\Desktop\Porterville Met
Data\Porterville_2006-2009.SFC Met Version: 18081
Profile file: C:\Users\kheck\Desktop\Porterville Met
Data\Porterville_2006-2009.PFL
Surface format: FREE
Profile format: FREE
Surface station no.: 23149 Upper air station no.: 23230 Name: PORTERVILLE Name:
OAKLAND/WSO_AP
Year: 2006 Year: 2006
First 24 hours of scalar data
YR MO DY JDY HR H0 U* W* DT/DZ ZICNV ZIMCH M-O LEN Z0 BOWEN
ALBEDO REF WS WD HT REF TA HT
- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -
06 01 01 1 01 -24.8 0.249 -9.000 -9.000 -999. 297. 68.0 0.03 0.76
1.00 3.86 101. 10.0 280.1 2.0
06 01 01 1 02 -24.7 0.249 -9.000 -9.000 -999. 298. 68.0 0.03 0.76
1.00 3.86 108. 10.0 281.1 2.0
06 01 01 1 03 -21.4 0.215 -9.000 -9.000 -999. 240. 50.9 0.03 0.76
1.00 3.36 104. 10.0 280.1 2.0
06 01 01 1 04 -24.7 0.249 -9.000 -9.000 -999. 297. 68.0 0.03 0.76
1.00 3.86 113. 10.0 281.1 2.0
06 01 01 1 05 -24.7 0.249 -9.000 -9.000 -999. 298. 68.0 0.03 0.76
1.00 3.86 113. 10.0 281.1 2.0
06 01 01 1 06 -25.0 0.252 -9.000 -9.000 -999. 303. 69.7 0.03 0.76
1.00 3.86 132. 10.0 281.1 2.0
06 01 01 1 07 -28.4 0.286 -9.000 -9.000 -999. 366. 89.8 0.03 0.76
1.00 4.36 145. 10.0 281.1 2.0
06 01 01 1 08 -18.7 0.205 -9.000 -9.000 -999. 225. 46.2 0.02 0.76
0.61 3.36 163. 10.0 280.1 2.0
06 01 01 1 09 11.0 -9.000 -9.000 -9.000 95. -999. -99999.0 0.03 0.76
0.34 0.00 0. 10.0 282.1 2.0
06 01 01 1 10 48.2 -9.000 -9.000 -9.000 186. -999. -99999.0 0.03 0.76
0.25 0.00 0. 10.0 284.1 2.0
06 01 01 1 11 81.6 0.277 0.863 0.005 280. 350. -23.1 0.04 0.76
0.22 3.36 4. 10.0 284.1 2.0
06 01 01 1 12 96.6 0.230 0.994 0.005 360. 265. -11.1 0.02 0.76
0.21 2.86 306. 10.0 284.1 2.0
06 01 01 1 13 101.2 -9.000 -9.000 -9.000 608. -999. -99999.0 0.03 0.76
0.21 0.00 0. 10.0 284.1 2.0
06 01 01 1 14 17.7 0.212 0.685 0.005 644. 234. -47.5 0.03 0.76
0.22 2.86 119. 10.0 284.1 2.0
06 01 01 1 15 10.3 0.274 0.579 0.005 666. 344. -176.6 0.03 0.76
0.25 3.86 142. 10.0 284.1 2.0
06 01 01 1 16 0.1 0.263 0.123 0.005 668. 323. -8888.0 0.03 0.76
0.35 3.86 104. 10.0 284.1 2.0
06 01 01 1 17 -11.7 0.144 -9.000 -9.000 -999. 139. 22.8 0.02 0.76
0.62 2.36 41. 10.0 283.1 2.0
06 01 01 1 18 -6.7 0.108 -9.000 -9.000 -999. 85. 16.3 0.03 0.76
1.00 1.76 97. 10.0 284.1 2.0
06 01 01 1 19 -6.5 0.105 -9.000 -9.000 -999. 81. 15.7 0.02 0.76
1.00 1.76 44. 10.0 284.1 2.0
06 01 01 1 20 -17.2 0.177 -9.000 -9.000 -999. 178. 34.3 0.02 0.76
1.00 2.86 317. 10.0 284.1 2.0
06 01 01 1 21 -999.0 -9.000 -9.000 -9.000 -999. -999. -99999.0 0.03 0.76
1.00 0.00 0. 10.0 284.1 2.0
06 01 01 1 22 -11.9 0.144 -9.000 -9.000 -999. 131. 22.7 0.02 0.76
1.00 2.36 32. 10.0 284.1 2.0
06 01 01 1 23 -18.8 0.192 -9.000 -9.000 -999. 202. 40.6 0.04 0.76
1.00 2.86 20. 10.0 284.1 2.0
06 01 01 1 24 -17.2 0.177 -9.000 -9.000 -999. 178. 34.3 0.02 0.76
1.00 2.86 50. 10.0 285.1 2.0
First hour of profile data
YR MO DY HR HEIGHT F WDIR WSPD AMB_TMP sigmaA sigmaW sigmaV 06 01 01 01 10.0 1 101. 3.86 280.2 99.0 -99.00 -99.00
F indicates top of profile (=1) or below (=0)
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 29
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** THE ANNUAL AVERAGE CONCENTRATION VALUES AVERAGED OVER 4 YEARS FOR SOURCE GROUP: ALL ***
INCLUDING SOURCE(S): PAREA1 ,
*** DISCRETE CARTESIAN RECEPTOR POINTS
***
** CONC OF PM_2.5 IN MICROGRAMS/M**3
**
X-COORD (M) Y-COORD (M) CONC X-COORD (M)
Y-COORD (M) CONC
- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -
313271.45 3995341.55 0.00111 313291.45
3995341.55 0.00114
313311.45 3995341.55 0.00118 313331.45
3995341.55 0.00121
313351.45 3995341.55 0.00125 313371.45
3995341.55 0.00130
313391.45 3995341.55 0.00135 313411.45
3995341.55 0.00141
313431.45 3995341.55 0.00148 313451.45
3995341.55 0.00155
313471.45 3995341.55 0.00163 313491.45
3995341.55 0.00172
313511.45 3995341.55 0.00182 313531.45
3995341.55 0.00194
313551.45 3995341.55 0.00207 313571.45
3995341.55 0.00222
313591.45 3995341.55 0.00239 313611.45
3995341.55 0.00258
313631.45 3995341.55 0.00279 313651.45
3995341.55 0.00303
313671.45 3995341.55 0.00330 313691.45
3995341.55 0.00358
313711.45 3995341.55 0.00388 313731.45
3995341.55 0.00419
313751.45 3995341.55 0.00451 313771.45
3995341.55 0.00483
313791.45 3995341.55 0.00515 313811.45
3995341.55 0.00547
313831.45 3995341.55 0.00578 313851.45
3995341.55 0.00609
313871.45 3995341.55 0.00638 313891.45
3995341.55 0.00667
313911.45 3995341.55 0.00694 313931.45
3995341.55 0.00719
313951.45 3995341.55 0.00742 313971.45
3995341.55 0.00762
313991.45 3995341.55 0.00779 314011.45
3995341.55 0.00792
314031.45 3995341.55 0.00801 314051.45
3995341.55 0.00806
314071.45 3995341.55 0.00808 314091.45
3995341.55 0.00806
314111.45 3995341.55 0.00801 314131.45
3995341.55 0.00792
314151.45 3995341.55 0.00781 314171.45
3995341.55 0.00768
314191.45 3995341.55 0.00754 314211.45
3995341.55 0.00737
314231.45 3995341.55 0.00720 314251.45
3995341.55 0.00702
314271.45 3995341.55 0.00683 313271.45
3995361.55 0.00117
313291.45 3995361.55 0.00120 313311.45
3995361.55 0.00124
313331.45 3995361.55 0.00127 313351.45
3995361.55 0.00132
313371.45 3995361.55 0.00136 313391.45
3995361.55 0.00142
313411.45 3995361.55 0.00148 313431.45
3995361.55 0.00155
313451.45 3995361.55 0.00162 313471.45
3995361.55 0.00171
313491.45 3995361.55 0.00181 313511.45
3995361.55 0.00192
313531.45 3995361.55 0.00204 313551.45
3995361.55 0.00219
313571.45 3995361.55 0.00235 313591.45
3995361.55 0.00254
313611.45 3995361.55 0.00275 313631.45
3995361.55 0.00299
313651.45 3995361.55 0.00326 313671.45
3995361.55 0.00355
313691.45 3995361.55 0.00387 313711.45
3995361.55 0.00420
313731.45 3995361.55 0.00454 313751.45
3995361.55 0.00490
313771.45 3995361.55 0.00525 313791.45
3995361.55 0.00560
313811.45 3995361.55 0.00594 313831.45
3995361.55 0.00628
*** AERMOD - VERSION 21112 *** *** C:\Lakes\AERMOD
View\LombardiPorterville\LombardiPorterville.isc *** 07/23/21 *** AERMET - VERSION 18081 *** ***
*** 09:19:05
PAGE 30
*** MODELOPTs: RegDFAULT CONC ELEV URBAN ADJ_U*
*** THE ANNUAL AVERAGE CONCENTRATION VALUES AVERAGED OVER 4 YEARS FOR SOURCE GROUP: ALL ***
INCLUDING SOURCE(S): PAREA1 ,
*** DISCRETE CARTESIAN RECEPTOR POINTS
***
** CONC OF PM_2.5 IN MICROGRAMS/M**3
**