ATT 2.b.xix - HRA Report — Murrieta City Council, May 20, 2025

Whitewood I

CONSTRUCTION HEALTH RISK ASSESSMENT

CITY OF MURRIETA

PREPARED BY:

Haseeb Qureshi
[email protected]

Michael Tirohn
[email protected]

F
EBRUARY 29, 2024

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TABLE OF CONTENTS
TABLE OF CONTENTS ............................................................................................................................. I APPENDICES .......................................................................................................................................... I LIST OF EXHIBITS .................................................................................................................................. II LIST OF TABLES .................................................................................................................................... II LIST OF ABBREVIATED TERMS ............................................................................................................. III EXECUTIVE SUMMARY ......................................................................................................................... 1 1 INTRODUCTION ........................................................................................................................... 3

1.1 Site Location .................................................................................................................................. 3

1.2 Project Description ........................................................................................................................ 4 2 BACKGROUND............................................................................................................................. 8

2.1 Background on Recommended Methodology .............................................................................. 8

2.2 Construction Health Risk Assessment ........................................................................................... 8

2.3 Exposure Quantification.............................................................................................................. 11

2.4 Carcinogenic Chemical Risk ......................................................................................................... 12

2.5 Non-carcinogenic Exposures ....................................................................................................... 13

2.6 Potential Project DPM-Source Cancer and Non-Cancer Risks .................................................... 14 3 REFERENCES .............................................................................................................................. 18 4 CERTIFICATIONS ........................................................................................................................ 20

APPENDICES
APPENDIX 2.1: CALEEMOD OUTPUTS AND EMISSION CALCULATIONS APPENDIX 2.2: AERMOD MODEL INPUT/OUTPUT
APPENDIX 2.3: RISK CALCULATIONS

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LIST OF EXHIBITS
EXHIBIT 1-A: LOCATION MAP .............................................................................................................. 5 EXHIBIT 1-B: SITE PLAN........................................................................................................................ 6 EXHIBIT 2-A: MODELED CONSTRUCTION EMISSION SOURCES ............................................................ 10 EXHIBIT 2-B: RECEPTOR LOCATIONS .................................................................................................. 16

LIST OF TABLES
TABLE ES-1: SUMMARY OF CONSTRUCTION CANCER AND NON-CANCER RISKS ................................... 2 TABLE 2-1: CONSTRUCTION DURATION ................................................................................................ 9 TABLE 2-2: CONSTRUCTION EQUIPMENT ASSUMPTIONS ...................................................................... 9 TABLE 2-5: AERMOD MODEL PARAMETERS ........................................................................................ 11 TABLE 2-3: EXPOSURE ASSUMPTIONS FOR INDIVIDUAL CANCER RISK ................................................ 12 TABLE 2-4: EXPOSURE ASSUMPTIONS FOR INDIVIDUAL CANCER RISK (9 YEAR SCHOOL CHILD) .......... 12

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LIST OF ABBREVIATED TERMS
(1) Reference
µg Microgram
AERMOD American Meteorological Society/Environmental
Protection Agency Regulatory Model
AQMD Air Quality Management District
ARB Air Resources Board
CEQA California Environmental Quality Act
CPF Cancer Potency Factor
DPM Diesel Particulate Matter
EMFAC Emission Factor Model
EPA Environmental Protection Agency
HHD Heavy Heavy-Duty
HI Hazard Index
HRA Health Risk Assessment
LHD Light Heavy-Duty
MEIR Maximally Exposed Individual Receptor
MEISC Maximally Exposed Individual School Child
MHD Medium Heavy-Duty
NAD North American Datum
OEHHA Office of Environmental Health Hazard Assessment
PM10 Particulate Matter 10 microns in diameter or less
Project Whitewood I
REL Reference Exposure Level
RM Recommended Measures
SCAQMD South Coast Air Quality Management District
SRA Source Receptor Area
TAC Toxic Air Contaminant
TA Traffic Analysis
TRU Transport Refrigeration Unit
URF Unit Risk Factor
UTM Universal Transverse Mercator
VMT Vehicle Miles Traveled
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1 EXECUTIVE SUMMARY
This report evaluates the potential health risk impacts to sensitive receptors (which are residents) associated with the development of the Project, more specifically, health risk impacts as a result of exposure to Toxic Air Contaminants (TACs) including diesel particulate mat ter (DPM) as a result of heavy-duty diesel trucks and construction equipment used during construction of the proposed Project. This section summarizes the significance criteria and Project health risks.

The results of the health risk assessment from Project construction-generated DPM emissions are provided in Table ES- 1 below for the Project. Because the proposed Project would not generate TAC emissions during long-term operation, an operational HRA is not required.

CONSTRUCTION IMPACTS
Residential Exposure Scenario:

The land use with the greatest potential exposure to Project construction-source DPM emissions is Location R 3 which is located approximately 64 feet north of the Project site at an existing residence located at 35842 Meadowlark Lane . R3 is placed in the private outdoor living areas (backyard) facing the Project site. At the maximally exposed individual receptor (MEIR), the maximum incremental cancer risk attributable to Project construction -source DPM emissions is estimated at 4.08 in one million, which is less than the SCAQMD’s significance threshold of 10 in one million. At this same location, non-cancer risks were estimated to be <0.01, which would not exceed the applicable threshold of 1.0. While Location R 3 is not the nearest receptor to the Project site, it would experience the highest concentrations of DPM during Project construction due to meteorological co nditions at the site . Because all other modeled receptors would experience lower concentrations of DPM during Project construction, all other receptors in the vicinity of the Project would be exposed to less emissions and therefore less risk than the MEI R identified herein. As such, the Project will not cause a significant human health or cancer risk to adjacent land uses and would not have impacts beyond what was studied in the City of Murrieta General Plan EIR as a result of Project construction activity. All other receptors during construction activity would experience less risk than what is identified for this location. The modeled receptors are illustrated on Exhibit 2-B.

School Child Exposure Scenario:

The nearest school is Vista Murrieta High School , located approximately 551 feet southwest of the Project site. The maximally exposed individual school child (MEISC) is the school receptor that would experience the highest modeled concentrations of DPM, and thus the highest risk. At the MEISC, the maximum incremental cancer risk impact attributable to the Project is calculated to be 0.04 in one million, which is less than the significance threshold of 10 in one million. At this same location, non -cancer risks attributable to the Project were calculated to be ≤ 0.01, which would not exceed the applicable significance threshold of 1.0. As such, the Project will not cause a significant human health or cancer risk to nearby school children and would not have impacts beyond what was studied in the City of Murrieta General Plan EIR.

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2 TABLE ES-1: SUMMARY OF CONSTRUCTION CANCER AND NON-CANCER RISKS Time Period Location
Maximum
Lifetime
Cancer Risk
(Risk per
Million)
Significance
Threshold
(Risk per
Million)
Exceeds
Significance
Threshold

1.00 Year
Exposure Maximum Exposed Sensitive Receptor 4.08 10 NO

1.00 Year
Exposure Maximum Exposed Individual School Child 0.04 10 NO Time Period Location
Maximum
Hazard
Index
Significance
Threshold
Exceeds
Significance
Threshold
Annual
Average Maximum Exposed Sensitive Receptor ≤0.01 1.0 NO Annual
Average Maximum Exposed Individual School Child ≤0.01 1.0 NO Whitewood I Construction Health Risk Assessment
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3 1 INTRODUCTION
This HRA has been prepared in accordance with the document Health Risk Assessment Guidance for Analyzing Cancer Risk from Mobile Source Diesel Idling Emissions for CEQA Air Quality Analysis (1) and is comprised of all relevant and appropriate procedures presented by the United States Environmental Protection Agency (U.S. EPA), California EPA and SCAQMD. Cancer risk is expressed in terms of expected incremental incidence per million population. The SCAQMD has established an incidence rate of ten ( 10) persons per million as the maximum acceptable incremental cancer risk due to TAC exposure from a project such as the proposed Project. This threshold serves to determine whether or not a given project has a potentially significant development-specific and cumulatively considerable impact.

The AQMD has published a report on how to address cumulative impacts from air pollution: White Paper on Potential Control Strategies to Address Cumulative Impacts from Air Pollution (2). In this report the AQMD states (Page D-3):
“…the AQMD uses the same significance thresholds for project specific and cumulative impacts for all environmental topics analyzed in an Environmental Assessment or EIR. The only case where the significance thresholds for project specific and cumulative impacts differ is the Hazard Index (HI) significance threshold for toxic air contaminant (TAC) emissions. The project specific (project increment) significance threshold is HI > 1.0 while the cumulative (facility-wide) is HI > 3.0. It should be noted that th e HI is only one of three TAC emission significance thresholds considered (when applicable) in a CEQA analysis. The other two are the maximum individual cancer risk (MICR) and the cancer burden, both of which use the same significance thresholds (MICR of 10 in 1 million and cancer burden of 0.5) for project specific and cumulative impacts.

Projects that exceed the project-specific significance thresholds are considered by the SCAQMD to be cumulatively considerable. This is the reason project-specific and cumulative significance thresholds are the same. Conversely, projects that do not exceed the project-specific thresholds are generally not considered to be cumulatively significant.” The SCAQMD has also established non- carcinogenic risk parameters for use in HRAs. Non - carcinogenic risks are quantified by calculating a "hazard index," expressed as the ratio between the ambient pollutant concentration and its toxicity or Reference Exposure Level (REL). A REL is a concentration at or below which health effects are not likely to occur. A hazard index less of than one (1.0) means that adverse health effects are not expected. In this HRA, non-carcinogenic exposures of less than 1.0 are consi dered less-than-significant. Both the cancer risk and non- carcinogenic risk thresholds are applied to the nearest sensitive receptors below.

1.1 SITE LOCATION
The Project is located north of Clinton Keith Road, east of Whitewood Road, and west of Arendt Lane in the City of Murrieta. The Project’s location in relation to the surrounding area is shown on Exhibit 1-A. The surrounding land use designations are Multi-Family Residential to the north, south, and west, Single-Family Residential to the east, and Civic/Institutional to the southwest.

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4 1.2 PROJECT DESCRIPTION
The Project consists of a Development Plan Permit and Tentative Tract Map for a 17.26-acre site.

The Project would provide for the development of 243 1 multi-family residential homes at a density of 15.1 dwelling units per acre. The Project also includes construction of a recreational pool area with a ± 900sf restroom and pool equipment building, tot lot and 65,120 SF of total common open space areas throughout the site. A preliminary site plan for the proposed Project is shown on Exhibit 1-B.

The proposed 243 dwelling units comprise 2 - and 3 -story townhomes. A total of 629 parking spaces would be provided with 10% of spaces designated as future electric vehicle (EV) spaces.

Access to the Project would be provided by two (2) full access driveways, one located on Arendt Lane, and the other located on Whitewood Road.

Grading proposed by the Project would result in disturbance to 16.64 acres of the Project with the balance of the site remaining undisturbed. The project will preserve 0.62 acres of sensitive area including 33 mature Oaks and 0.35 acres of County of Riverside riparian/riverine features.

The project will construct a ±12” offsite EMWD master plan sewer line within Arendt Lane, continuing easterly within Clinton Keith Road and terminating near the northwest corner of Clinton Keith Road and Menifee Road.

1 It should be noted, since the time this health risk assessment has been prepared, the site plan has been updated: the single family attached residential dwelling units has been reduced from 257 dwelling units to 243 dwelling units. In an effort to provide flexibility for minor changes to the site plan during final preparation, the Whitewood I Traffic Analysis evaluated the higher single family attached resident ial dwelling units in an effort to provide a conservative analysis. As such, the emissions presented in this health risk assessment as well represent a conservative analysis and no new health impacts are anticipated.

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5 EXHIBIT 1-A: LOCATION MAP

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6 EXHIBIT 1-B: SITE PLAN

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8 2 BACKGROUND

2.1 BACKGROUND ON RECOMMENDED METHODOLOGY
This HRA is based on applicable guidelines to produce conservative estimates of human health risk posed by exposure to DPM. The conservative nature of this analysis is due primarily to the following factors:
• The ARB-adopted diesel exhaust Unit Risk Factor (URF) of 300 in one million per µg/m3 is based upon the upper 95 percentile of estimated risk for each of the epidemiological studies utilized to develop the URF. Using the 95th percentile URF represents a very conservative (health-protective) risk posed by DPM because it represents breathing rates that are high for the human body (95% higher than the average population).

2.2 CONSTRUCTION HEALTH RISK ASSESSMENT

2.2.1 EMISSIONS CALCULATIONS
The emissions calculations for the construction HRA component are based on an assumed mix of construction equipment and hauling activity as presented in the Whitewood I Air Quality & Energy Assessment (“technical study”) prepared by Urban Crossroads, Inc. (3).

Construction related DPM emissions are expected to occur primarily as a function of the operation of heavy-duty construction equipment.

To support the Project development, there will be grading, trenching, and paving for off- site improvements associated with roadway construction and utility installation for the Project.

However, it is expected that the off -site construction activities woul d not take place at one location throughout a single day or for the entire duration of construction. Construction emissions from this off-site work would, therefore, be relatively short term, not concentrated in one area, and would be reduced at any given location as construction work moves linearly along the existing public right- of-way and farther from sensitive uses. The physical constraints would limit the amount of construction equipment that could be used, and any off- site and utility infrastructure construction would not use equipment totals that would exceed the equipment totals on Table 2-2. Because off-site construction activity would be located near existing homes on an intermittent and short-term basis, no health risk impacts beyond what has alre ady been identified in this report are expected to occur.

As discussed in the technical study, the Project would result in approximately 261 total working- days of construction activity. The construction duration by phase is shown on Table 2 -1. A detailed summary of construction equipment assumptions by phase is provided at Table 2-2. The CalEEMod emissions outputs are presented in Appendix 2.1 . The modeled emission sources for construction activity are illustrated on Exhibit 2 -A. It should be noted that emissions from overlapping construction activities is accounted for in the analysis.

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9 TABLE 2-1: CONSTRUCTION DURATION
Construction Activity Start Date End Date Days
Demolition 1/1/2024 1/19/2024 15
Site Preparation 1/22/2024 1/31/2024 8
Grading 2/1/2024 3/1/2024 22
Building Construction 3/4/2024 12/30/2024 216
Paving 12/9/2024 12/30/2024 16
Architectural Coating 11/1/2024 12/30/2024 42
TABLE 2-2: CONSTRUCTION EQUIPMENT ASSUMPTIONS
Construction Activity Equipment Amount Hours Per Day
Demolition
Concrete/Industrial Saws 1 8
Excavators 3 8
Rubber Tired Dozers 2 8
Site Preparation
Rubber Tired Dozers 3 8
Crawler Tractors 4 8
Grading
Excavators 2 8
Graders 1 8
Rubber Tired Dozers 1 8
Scrapers 2 8
Crawler Tractors 2 8
Building Construction
Cranes 1 8
Forklifts 3 8
Generator Sets 1 8
Welders 1 8
Tractors/Loaders/Backhoes 3 8
Paving
Pavers 2 8
Paving Equipment 2 8
Rollers 2 8
Architectural Coating Air Compressors 1 8

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10 EXHIBIT 2-A: MODELED CONSTRUCTION EMISSION SOURCES

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11 2.3 EXPOSURE QUANTIFICATION
The analysis herein has been conducted in accordance with the guidelines in the Health Risk Assessment Guidance for Analyzing Cancer Risks from Mobile Source Diesel Idling Emissions for CEQA Air Quality Analysis (1). The Environmental Protection Agency’s (U.S. EPA’s) AERMOD model has been utilized. For purposes of this analysis, the Lakes AERMOD View (Version 11.2.0) was used to calculate annual average particulate concentrations associated with site operations.

Lakes AERMOD View was utilized to incorporate the U.S. EPA’s latest AERMOD Version 22112 (4).

The model offers additional flexibility by allowing the user to assign an initial release height and vertical dispersion parameters for mobile sources representative of a roadway. For this HRA, the roadways were modeled as adjacent volume sources. Roadways were modeled using the U.S.

EPA’s haul route methodology for modeling construction haul truck and vendor truck movement.

More specifically, the Haul Road Volume Source Calculator in Lakes AERMOD View has been utilized to determine the release height param eters. Based on the US EPA methodology, the Project’s modeled sources would result in a release height of 3.49 meters and an initial lateral dimension of 4.0 meters, and an initial vertical dimension of 3.25 meters.

Model parameters are presented in Table 2 -5 (5). The model requires additional input parameters including emission data and local meteorology. Meteorological data from the SCAQMD’s Lake Elsinore monitoring station was used to represent local weather conditions and prevailing winds (6).

TABLE 2-5: AERMOD MODEL PARAMETERS
Dispersion Coefficient (Urban/Rural) Urban (population 2,189,641) Terrain (Flat/Elevated) Elevated (Regulatory Default)
Averaging Time 1 year (5-year Meteorological Data Set)
Receptor Height 0 meters (Regulatory Default)
Universal Transverse Mercator (UTM) coordinates for World Geodetic System (WGS) 84 were used to locate the Project site boundaries, each volume source location, and receptor locations in the Project vicinity. The AERMOD dispersion model summary output files for the Project are presented in Appendix 2.2. Modeled sensitive receptors were placed at residential and non- residential locations.

Receptors may be placed at applicable structure locations for residential property and not necessarily the boundaries of the properties containing these uses because the human receptors spend a majority of their time at the residence’s building, and not on the property line. It should be noted that the primary purpose of receptor placement is focused on long -term exposure.

Notwithstanding, as a conservative measure, receptors were placed at either the outdoor living area or the building façade, whichever is closer to the Project site.

For purposes of this HRA, receptors include residential land uses in the vicinity of the Project.

These receptors are included in the HRA since residents may be exposed at these locations over the course of Project construction. This methodology is consistent with SC AQMD and OEHHA recommended guidance.

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12 Any impacts to residents or workers located further away from the Project site than the modeled residential and workers would have a lesser impact than what has already been disclosed in the HRA at the MEIR and MEISC because concentrations dissipate with distance.

All receptors were set to existing elevation height so that only ground- level concentrations are analyzed. United States Geological Survey (USGS) Digital Elevation Model (DEM) terrain data based on a 7.5-minute topographic quadrangle map series using AERMAP was utilized in the HRA modeling to set elevations (7).

Discrete variants for daily breathing rates, exposure frequency, and exposure duration were obtained from relevant distribution profiles presented in the 2015 OEHHA Guidelines. Table s 2- 3 and 2-4 summarize the e xposure parameters for residents and school children, respectively, based on 2015 OEHHA Guidelines. Appendix 2.3 includes the detailed risk calculation.

TABLE 2-3: EXPOSURE ASSUMPTIONS FOR INDIVIDUAL CANCER RISK Age Daily
Breathing
Rate (L/kg-
day)
Age
Specific
Factor
Exposure
Duration
(years)
Fraction
of Time
at Home
Exposure
Frequency
(days/year)
Exposure
Time
(hours/day)
0 to 2 1,090 10 2.00 1.00 260 8
2 to 16 572 3 1.29 1.00 260 8
TABLE 2-4: EXPOSURE ASSUMPTIONS FOR INDIVIDUAL CANCER RISK (9 YEAR SCHOOL CHILD) Age Daily
Breathing
Rate (L/kg-
day)
Age
Specific
Factor
Exposure
Duration
(years)
Exposure
Frequency
(days/year)
a
Exposure
Time
(hours/day)
4 to 13 631 3 9 180 12
a To represent the unique characteristics of the school-based population, the assessment employed the U.S.

Environmental Protection Agency’s guidance to develop viable dose estimates based on reasonable maximum exposures (RME). RME’s are defined as the “highest exposure that is reasonably expected to occur” for a given receptor population. As a result, lifetime risk values for the student population were adjusted to account for an exposure duration of 180 days per year for nine (9) years. The 9 year exposure duration is also consistent with OEHHA Recommendations and consistent with the exposure duration utilized in school-based risk assessments for various schools within the Los Angeles County Unified School District (LAUSD) that have been accepted by the SCAQMD.

2.4 CARCINOGENIC CHEMICAL RISK
Excess cancer risks are estimated as the upper-bound incremental probability that an individual will develop cancer over a lifetime as a direct result of exposure to potential carcinogens over a specified exposure duration. The estimated risk is expressed as a unitless probability. The cancer risk attributed to a chemical is calculated by multiplying the chemical intake or dose at the human exchange boundaries (e.g., lungs) by the chemical-specific cancer potency factor (CPF). A risk level of 10 in one million implies a likelihood that up to 10 people, out of one million equally exposed Whitewood I Construction Health Risk Assessment
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13 people would contract cancer if exposed continuously (24 hours per day) to the levels of toxic air contaminants over a specified duration of time.

Guidance from CARB and the California Environmental Protection Agency, Office of Environmental Health Hazard Assessment (OEHHA) recommends a refinement to the standard point estimate approach when alternate human body weights and breathing rates are utilized to assess risk for susc eptible subpopulations such as children. For the inhalation pathway, the procedure requires the incorporation of several discrete variates to effectively quantify dose.

Once determined, contaminant dose is multiplied by the canc er potency factor (CPF) in units of inverse dose expressed in milligrams per kilogram per day (mg/kg/day) -1 to derive the cancer risk
estimate. Therefore, to assess exposures, the following dose algorithm was utilized.

𝐷𝐷𝐷𝐷𝐷𝐷𝐷𝐷𝐴𝐴𝐴𝐴𝐴𝐴 = �𝐶𝐶𝐴𝐴𝐴𝐴𝐴𝐴 × 𝐵𝐵𝐵𝐵
𝐵𝐵𝐵𝐵 × 𝐴𝐴 × 𝐷𝐷𝐸𝐸� × (1 × 10−6)
Where:

𝐷𝐷𝐷𝐷𝐷𝐷𝐷𝐷𝐴𝐴𝐴𝐴𝐴𝐴 = chronic daily intake (mg/kg/day)
𝐶𝐶𝐴𝐴𝐴𝐴𝐴𝐴 = concentration of contaminant in air (µg/m3) 𝐵𝐵𝐴𝐴
𝐵𝐵𝐵𝐵 = daily breathing rate normalized to body weight
(L/kg BW-day)
𝐴𝐴 = inhalation absorption factor
𝐷𝐷𝐸𝐸 = exposure frequency (days/365 days)
𝐵𝐵𝐵𝐵 = body weight (kg)
1 × 10−6 = conversion factors (µg to mg, L to m3)

𝐵𝐵𝑅𝑅𝐷𝐷𝑅𝑅𝐴𝐴𝐴𝐴𝐴𝐴 = 𝐷𝐷𝐷𝐷𝐷𝐷𝐷𝐷𝐴𝐴𝐴𝐴𝐴𝐴 × 𝐶𝐶𝐶𝐶𝐸𝐸 × 𝐴𝐴𝐷𝐷𝐸𝐸 × 𝐸𝐸𝐴𝐴𝐹𝐹 × 𝐷𝐷𝐷𝐷 𝐴𝐴𝐴𝐴
Where:

𝐷𝐷𝐷𝐷𝐷𝐷𝐷𝐷𝐴𝐴𝐴𝐴𝐴𝐴 = chronic daily intake (mg/kg/day)
𝐶𝐶𝐶𝐶𝐸𝐸 = cancer potency factor
𝐷𝐷𝐷𝐷 = number of years within particular age group
𝐴𝐴𝐴𝐴 = averaging time

2.5 NON-CARCINOGENIC EXPOSURES
An evaluation of the potential noncarcinogenic effects of chronic exposures was also conducted.

Adverse health effects are evaluated by comparing a compound’s annual concentration with its Whitewood I Construction Health Risk Assessment
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14 toxicity factor or Reference Exposure Level (REL). The REL for diesel particulates was obtained from OEHHA for this analysis. The chronic reference exposure level (REL) for DPM was established by OEHHA as 5 μg/m
3 (8).

Non-cancer health effects are expressed as a hazard index (HI), which is calculated using the following equation:

𝐹𝐹𝑅𝑅𝐷𝐷𝐷𝐷𝐷𝐷 = 𝐶𝐶𝐷𝐷𝐷𝐷𝐷𝐷
𝐵𝐵𝐷𝐷𝑅𝑅𝐷𝐷𝐷𝐷𝐷𝐷

Where:

𝐹𝐹𝑅𝑅𝐷𝐷𝐷𝐷𝐷𝐷 = Hazard index (unitless)
𝐶𝐶𝐷𝐷𝐷𝐷𝐷𝐷 = Annual average DPM concentration (μg/m3)
𝐵𝐵𝐷𝐷𝑅𝑅𝐷𝐷𝐷𝐷𝐷𝐷 = REL for DPM ( the DPM concentration at which no adverse health effects are anticipated).

For purposes of this analysis the hazard index for the respiratory endpoint totaled less than one for all receptors in the project vicinity, and thus is less than significant.

2.6 POTENTIAL PROJECT DPM-SOURCE CANCER AND NON-CANCER RISKS

CONSTRUCTION IMPACTS
Residential Exposure Scenario:

Because all other modeled receptors would experience lower concentrations of DPM during Project construction, all other receptors in the vicinity of the Project would be exposed to less emissions and therefore less risk than the MEI R identified herein. As such, the Project will not cause a significant human health or cancer risk to adjacent land uses and would not have impacts beyond what was studied in the City of Murrieta General Plan EIR as a result of Project construction activity. All other receptors during construction activity would experience less risk than what is identified for this location. The modeled receptors are illustrated on Exhibit 2-B.

School Child Exposure Scenario:

The nearest school is Vista Murrieta High School, located approximately 551 feet southwest of the Project site. At the MEISC, the maximum incremental cancer risk impact attributable to the Whitewood I Construction Health Risk Assessment
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15 Project is calculated to be 0.04 in one million, which is less than the significance threshold of 10 in one million. At this same location, non-cancer risks attributable to the Project were calculated to be ≤ 0.01, which would not exceed the applicable significance threshold of 1.0. As such, the Project will not cause a significant human health or cancer risk to nearby school children and would not have impacts beyond what was studied in the City of Murrieta General Plan EIR.

It should be noted that the receptors presented in Exhibit 2 -B do not represent all modeled receptors.

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16 EXHIBIT 2-B: RECEPTOR LOCATIONS

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18 3 REFERENCES

1. South Coast Air Quality Managment District. Mobile Source Toxics Analysis. [Online] 2003. http://www.aqmd.gov/ceqa/handbook/mobile_toxic/mobile_toxic.html.

2. Goss, Tracy A and Kroeger, Amy. White Paper on Potential Control Strategies to Address Cumulative Impacts from Air Pollution. [Online] South Coast Air Quality Management District, 2003. [Cited: June 6, 2019.] http://www.aqmd.gov/docs/default -source/Agendas/Environmental-Justice/cumulative- impacts-working-group/cumulative-impacts-white-paper.pdf?sfvrsn=2.

3. Urban Crossroads, Inc. Whitewood I Air Quality & Energy Assessment. 2023.

4. Environmental Protection Agency. User's Guide for the AMS/EPA Regulatory Model (AERMOD). [Online] June 2022.
https://gaftp.epa.gov/Air/aqmg/SCRAM/models/preferred/aermod/aermod_userguide.pdf.

5. —. User's Guide for the AMS/EPA Regulatory Model (AERMOD). [Online] April 2018. https://www3.epa.gov/ttn/scram/models/aermod/aermod_userguide.pdf.

6. South Coast Air Quality Management District. Data for AERMOD. [Online] [Cited: May 9, 2022.] https://www.aqmd.gov/home/air-quality/air-quality-data-studies/meteorological-data/data-for- aermod.

7. Environmental Protection Agency. User's Guide for the AERMOD Terrain Preprocessor (AERMAP). [Online] 2018.
https://gaftp.epa.gov/Air/aqmg/SCRAM/models/related/aermap/aermap_userguide_v18081.pdf.

8. Office of Environmental Health Hazard Assessment. Chemical Toxicity Database. [Online] https://oehha.ca.gov/chemicals.

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20 4 CERTIFICATIONS
The contents of this health risk assessment represent an accurate depiction of the impacts to sensitive receptors associated with the proposed Whitewood I Project. The information contained in this health risk assessment report is based on the best available data at the time of preparation. If you have any questions, please contact me at (949) 660-1994.

Haseeb Qureshi
Principal
URBAN CROSSROADS, INC.
(949) 660-1994
[email protected]

EDUCATION
Master of Science in Environmental Studies
California State University, Fullerton • May 2010
Bachelor of Arts in Environmental Analysis and Design
University of California, Irvine • June 2006

ROFESSIONAL AFFILIATIONS
AEP – Association of Environmental Planners
AWMA – Air and Waste Management Association
ASTM – American Society for Testing and Materials

ROFESSIONAL CERTIFICATIONS
Environmental Site Assessment – American Society for Testing and Materials • June 2013 Planned Communities and Urban Infill – Urban Land Institute • June 2011 Indoor Air Quality and Industrial Hygiene – EMSL Analytical • April 2008 Principles of Ambient Air Monitoring – California Air Resources Board • August 2007 AB2588 Regulatory Standards – Trinity Consultants • November 2006 Air Dispersion Modeling – Lakes Environmental • June 2006

Whitewood I Construction Health Risk Assessment
14984-06 HRA Report
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Whitewood I Construction Health Risk Assessment
14984-06 HRA Report
APPENDIX 2.1:

CALEEMOD OUTPUTS AND EMISSION CALCULATIONS

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14984 - Whitewood Detailed Report
Table of Contents

1. Basic Project Information

1.1. Basic Project Information

1.2. Land Use Types

1.3. User-Selected Emission Reduction Measures by Emissions Sector

2. Emissions Summary

2.1. Construction Emissions Compared Against Thresholds

2.2. Construction Emissions by Y ear, Unmitigated

2.4. Operations Emissions Compared Against Thresholds

2.5. Operations Emissions by Sector, Unmitigated

3. Construction Emissions Details

3.1. Demolition (2024) - Unmitigated

3.3. Site Preparation (2024) - Unmitigated

3.5. Grading (2024) - Unmitigated

3.7. Building Construction (2024) - Unmitigated
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3.9. Paving (2024) - Unmitigated

3.11. Architectural Coating (2024) - Unmitigated

4. Operations Emissions Details

4.1. Mobile Emissions by Land Use

4.1.1. Unmitigated

4.2. Energy

4.2.1. Electricity Emissions By Land Use - Unmitigated

4.2.3. Natural Gas Emissions By Land Use - Unmitigated

4.3. Area Emissions by Source

4.3.2. Unmitigated

4.4. Water Emissions by Land Use

4.4.2. Unmitigated

4.5. Waste Emissions by Land Use

4.5.2. Unmitigated

4.6. Refrigerant Emissions by Land Use

4.6.1. Unmitigated

4.7. Offroad Emissions By Equipment Type
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4.7.1. Unmitigated

4.8. Stationary Emissions By Equipment Type

4.8.1. Unmitigated

4.9. User Defined Emissions By Equipment Type

4.9.1. Unmitigated

4.10. Soil Carbon Accumulation By Vegetation Type

4.10.1. Soil Carbon Accumulation By Vegetation Type - Unmitigated

4.10.2. Above and Belowground Carbon Accumulation by Land Use Type - Unmitigated

4.10.3. Avoided and Sequestered Emissions by Species - Unmitigated

5. Activity Data

5.1. Construction Schedule

5.2. Off-Road Equipment

5.2.1. Unmitigated

5.3. Construction Vehicles

5.3.1. Unmitigated

5.4. Vehicles

5.4.1. Construction Vehicle Control Strategies
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5.5. Architectural Coatings

5.6. Dust Mitigation

5.6.1. Construction Earthmoving Activities

5.6.2. Construction Earthmoving Control Strategies

5.7. Construction Paving

5.8. Construction Electricity Consumption and Emissions Factors

5.9. Operational Mobile Sources

5.9.1. Unmitigated

5.10. Operational Area Sources

5.10.1. Hearths

5.10.1.1. Unmitigated

5.10.2. Architectural Coatings

5.10.3. Landscape Equipment

5.11. Operational Energy Consumption

5.11.1. Unmitigated

5.12. Operational Water and Wastewater Consumption

5.12.1. Unmitigated
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5.13. Operational Waste Generation

5.13.1. Unmitigated

5.14. Operational Refrigeration and Air Conditioning Equipment

5.14.1. Unmitigated

5.15. Operational Off-Road Equipment

5.15.1. Unmitigated

5.16. Stationary Sources

5.16.1. Emergency Generators and Fire Pumps

5.16.2. Process Boilers

5.17. User Defined

5.18. Vegetation

5.18.1. Land Use Change

5.18.1.1. Unmitigated

5.18.1. Biomass Cover Type

5.18.1.1. Unmitigated

5.18.2. Sequestration

5.18.2.1. Unmitigated
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6. Climate Risk Detailed Report

6.1. Climate Risk Summary

6.2. Initial Climate Risk Scores

6.3. Adjusted Climate Risk Scores

6.4. Climate Risk Reduction Measures

7. Health and Equity Details

7.1. CalEnviroScreen 4.0 Scores

7.2. Healthy Places Index Scores

7.3. Overall Health & Equity Scores

7.4. Health & Equity Measures

7.5. Evaluation Scorecard

7.6. Health & Equity Custom Measures

8. User Changes to Default Data
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1. Basic Project Information

1.1. Basic Project Information
Data Field Value
Project Name 14984 - Whitewood
Lead Agency —
Land Use Scale Project/site
Analysis Level for Defaults County
Windspeed (m/s) 2.50
Precipitation (days) 18.6
Location 33.598655677467576, -117.16191006740195
County Riverside-South Coast
City Murrieta
Air District South Coast AQMD
Air Basin South Coast
TAZ 5545
EDFZ 11
Electric Utility Southern California Edison
Gas Utility Southern California Gas

1.2. Land Use Types
Land Use Subtype Size Unit Lot Acreage Building Area (sq ft) Landscape Area (sq ft)
Special Landscape
Area (sq ft)
Population Description
Condo/Townhouse 130 Dwelling Unit 5.14 223,690 0.00 — 420 — Apartments Low
Rise
132 Dwelling Unit 4.46 194,436 0.00 — 426 —
Parking Lot 680 Space 2.52 0.00 0.00 — — —
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Other Asphalt
Surfaces

5.82 Acre 5.82 0.00 0.00 — — —

1.3. User-Selected Emission Reduction Measures by Emissions Sector No measures selected

2. Emissions Summary

2.1. Construction Emissions Compared Against Thresholds Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Un/Mit. TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 2.64 2.28 13.9 30.2 0.03 0.55 2.66 3.21 0.51 0.63 1.14 — 6,065 6,065 0.24 0.22 12.8 6,150 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 5.44 69.6 42.6 41.3 0.06 2.25 5.90 8.15 2.07 2.74 4.81 — 8,233 8,233 0.34 0.26 0.41 8,320 Average
Daily
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 2.16 9.36 13.1 20.6 0.03 0.55 1.95 2.49 0.50 0.51 1.02 — 4,342 4,342 0.18 0.14 3.46 4,392 Annual
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 0.40 1.71 2.39 3.77 < 0.005 0.10 0.36 0.46 0.09 0.09 0.19 — 719 719 0.03 0.02 0.57 727

2.2. Construction Emissions by Y ear, Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Y ear TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e 14984 - Whitewood Detailed Report, 12/8/2022
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Daily -
Summer
(Max)
— — — — — — — — — — — — — — — — — —
2024 2.64 2.28 13.9 30.2 0.03 0.55 2.66 3.21 0.51 0.63 1.14 — 6,065 6,065 0.24 0.22 12.8 6,150 Daily -
Winter
(Max)
— — — — — — — — — — — — — — — — — —
2024 5.44 69.6 42.6 41.3 0.06 2.25 5.90 8.15 2.07 2.74 4.81 — 8,233 8,233 0.34 0.26 0.41 8,320 Average
Daily
— — — — — — — — — — — — — — — — — —
2024 2.16 9.36 13.1 20.6 0.03 0.55 1.95 2.49 0.50 0.51 1.02 — 4,342 4,342 0.18 0.14 3.46 4,392 Annual — — — — — — — — — — — — — — — — — —
2024 0.40 1.71 2.39 3.77 < 0.005 0.10 0.36 0.46 0.09 0.09 0.19 — 719 719 0.03 0.02 0.57 727

2.4. Operations Emissions Compared Against Thresholds
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Un/Mit. TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 12.0 20.5 14.0 94.8 0.21 0.56 5.88 6.44 0.56 1.04 1.60 125 26,925 27,050 13.7 0.91 77.2 27,740 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 9.91 18.5 14.4 67.6 0.20 0.56 5.88 6.43 0.55 1.04 1.59 125 25,762 25,887 13.7 0.94 4.92 26,514 Average
Daily
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 9.17 18.1 9.81 69.6 0.16 0.25 5.09 5.34 0.24 0.91 1.15 125 19,006 19,131 13.6 0.82 30.8 19,745 Annual
(Max)
— — — — — — — — — — — — — — — — — —
Unmit. 1.67 3.29 1.79 12.7 0.03 0.05 0.93 0.97 0.04 0.17 0.21 20.7 3,147 3,167 2.24 0.14 5.09 3,269 14984 - Whitewood Detailed Report, 12/8/2022
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2.5. Operations Emissions by Sector, Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Sector TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Mobile 9.96 9.17 8.64 77.8 0.18 0.14 5.88 6.01 0.13 1.04 1.17 — 18,399 18,399 0.77 0.82 74.2 18,738 Area 1.89 11.3 4.06 16.5 0.03 0.32 — 0.32 0.32 — 0.32 0.00 5,005 5,005 0.10 0.01 — 5,010 Energy 0.15 0.07 1.25 0.53 0.01 0.10 — 0.10 0.10 — 0.10 — 3,452 3,452 0.32 0.02 — 3,467 Water — — — — — — — — — — — 20.4 69.3 89.7 2.10 0.05 — 157 Waste — — — — — — — — — — — 104 0.00 104 10.4 0.00 — 365 Refrig. — — — — — — — — — — — — — — — — 2.99 2.99
Total 12.0 20.5 14.0 94.8 0.21 0.56 5.88 6.44 0.56 1.04 1.60 125 26,925 27,050 13.7 0.91 77.2 27,740 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Mobile 9.30 8.50 9.27 65.4 0.17 0.14 5.88 6.01 0.13 1.04 1.17 — 17,276 17,276 0.80 0.85 1.92 17,552 Area 0.46 9.95 3.91 1.66 0.02 0.32 — 0.32 0.32 — 0.32 0.00 4,965 4,965 0.09 0.01 — 4,970 Energy 0.15 0.07 1.25 0.53 0.01 0.10 — 0.10 0.10 — 0.10 — 3,452 3,452 0.32 0.02 — 3,467 Water — — — — — — — — — — — 20.4 69.3 89.7 2.10 0.05 — 157 Waste — — — — — — — — — — — 104 0.00 104 10.4 0.00 — 365 Refrig. — — — — — — — — — — — — — — — — 2.99 2.99
Total 9.91 18.5 14.4 67.6 0.20 0.56 5.88 6.43 0.55 1.04 1.59 125 25,762 25,887 13.7 0.94 4.92 26,514 Average
Daily
— — — — — — — — — — — — — — — — — —
Mobile 8.01 7.31 8.20 58.8 0.15 0.12 5.09 5.21 0.11 0.91 1.02 — 15,118 15,118 0.69 0.75 27.8 15,385 Area 1.01 10.7 0.37 10.3 < 0.005 0.03 — 0.03 0.03 — 0.03 0.00 367 367 0.01 < 0.005 — 368 Energy 0.15 0.07 1.25 0.53 0.01 0.10 — 0.10 0.10 — 0.10 — 3,452 3,452 0.32 0.02 — 3,467 Water — — — — — — — — — — — 20.4 69.3 89.7 2.10 0.05 — 157 14984 - Whitewood Detailed Report, 12/8/2022
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Waste — — — — — — — — — — — 104 0.00 104 10.4 0.00 — 365 Refrig. — — — — — — — — — — — — — — — — 2.99 2.99
Total 9.17 18.1 9.81 69.6 0.16 0.25 5.09 5.34 0.24 0.91 1.15 125 19,006 19,131 13.6 0.82 30.8 19,745 Annual — — — — — — — — — — — — — — — — — —
Mobile 1.46 1.33 1.50 10.7 0.03 0.02 0.93 0.95 0.02 0.17 0.19 — 2,503 2,503 0.11 0.12 4.60 2,547 Area 0.18 1.95 0.07 1.87 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 0.00 60.8 60.8 < 0.005 < 0.005 — 60.9 Energy 0.03 0.01 0.23 0.10 < 0.005 0.02 — 0.02 0.02 — 0.02 — 571 571 0.05 < 0.005 — 574 Water — — — — — — — — — — — 3.38 11.5 14.9 0.35 0.01 — 26.0 Waste — — — — — — — — — — — 17.3 0.00 17.3 1.73 0.00 — 60.5 Refrig. — — — — — — — — — — — — — — — — 0.50 0.50
Total 1.67 3.29 1.79 12.7 0.03 0.05 0.93 0.97 0.04 0.17 0.21 20.7 3,147 3,167 2.24 0.14 5.09 3,269

3. Construction Emissions Details

3.1. Demolition (2024) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

3.12 2.62 24.9 21.7 0.03 1.06 — 1.06 0.98 — 0.98 — 3,425 3,425 0.14 0.03 — 3,437 Demolitio
n
— — — — — — 0.20 0.20 — 0.03 0.03 — — — — — — —
Onsite
truck

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Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

0.13 0.11 1.02 0.89 < 0.005 0.04 — 0.04 0.04 — 0.04 — 141 141 0.01 < 0.005 — 141 Demolitio
n
— — — — — — 0.01 0.01 — < 0.005 < 0.005 — — — — — — —
Onsite
truck

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 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment

0.02 0.02 0.19 0.16 < 0.005 0.01 — 0.01 0.01 — 0.01 — 23.3 23.3 < 0.005 < 0.005 — 23.4 Demolitio
n
— — — — — — < 0.005 < 0.005 — < 0.005 < 0.005 — — — — — — — Onsite
truck

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 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.08 0.07 0.09 0.95 0.00 0.00 0.01 0.01 0.00 0.00 0.00 — 198 198 0.01 0.01 0.02 201 Vendor < 0.005 < 0.005 0.06 0.02 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — 50.0 50.0 < 0.005 0.01 < 0.005 52.3 Hauling 0.01 < 0.005 0.19 0.05 < 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 0.01 — 164 164 < 0.005 0.03 0.01 171 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.04 0.00 0.00 < 0.005 < 0.005 0.00 0.00 0.00 — 8.26 8.26 < 0.005 < 0.005 0.02 8.37 Vendor < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — 2.05 2.05 < 0.005 < 0.005 < 0.005 2.15 Hauling < 0.005 < 0.005 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — 6.72 6.72 < 0.005 < 0.005 0.01 7.05 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.01 0.00 0.00 < 0.005 < 0.005 0.00 0.00 0.00 — 1.37 1.37 < 0.005 < 0.005 < 0.005 1.39 14984 - Whitewood Detailed Report, 12/8/2022
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Vendor < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — 0.34 0.34 < 0.005 < 0.005 < 0.005 0.36 Hauling < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — 1.11 1.11 < 0.005 < 0.005 < 0.005 1.17

3.3. Site Preparation (2024) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

5.35 4.49 42.5 35.3 0.05 2.25 — 2.25 2.07 — 2.07 — 5,529 5,529 0.22 0.04 — 5,548 Dust
From
Material
Movement
— — — — — — 5.66 5.66 — 2.69 2.69 — — — — — — —
Onsite
truck

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 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

0.12 0.10 0.93 0.77 < 0.005 0.05 — 0.05 0.05 — 0.05 — 121 121 < 0.005 < 0.005 — 122 Dust
From
Material
Movement
— — — — — — 0.12 0.12 — 0.06 0.06 — — — — — — —
Onsite
truck

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 0.00 Annual — — — — — — — — — — — — — — — — — —
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20.1—< 0.005< 0.00520.120.1—0.01—0.010.01—0.01< 0.0050.140.170.020.02Off-Road Equipment
Dust
From
Material
Movement
— — — — — — 0.02 0.02 — 0.01 0.01 — — — — — — —
Onsite
truck

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 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.09 0.08 0.10 1.10 0.00 0.00 0.01 0.01 0.00 0.00 0.00 — 231 231 0.01 0.01 0.03 234 Vendor < 0.005 < 0.005 0.03 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — 26.7 26.7 < 0.005 < 0.005 < 0.005 27.9 Hauling 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 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.03 0.00 0.00 < 0.005 < 0.005 0.00 0.00 0.00 — 5.14 5.14 < 0.005 < 0.005 0.01 5.21 Vendor < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — 0.59 0.59 < 0.005 < 0.005 < 0.005 0.61 Hauling 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 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 < 0.005 0.00 0.00 < 0.005 < 0.005 0.00 0.00 0.00 — 0.85 0.85 < 0.005 < 0.005 < 0.005 0.86 Vendor < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — 0.10 0.10 < 0.005 < 0.005 < 0.005 0.10 Hauling 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 0.00

3.5. Grading (2024) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e 14984 - Whitewood Detailed Report, 12/8/2022
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Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

4.69 3.94 37.6 31.4 0.06 1.77 — 1.77 1.63 — 1.63 — 6,715 6,715 0.27 0.05 — 6,738 Dust
From
Material
Movement
— — — — — — 2.67 2.67 — 0.98 0.98 — — — — — — —
Onsite
truck

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 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

0.28 0.24 2.26 1.89 < 0.005 0.11 — 0.11 0.10 — 0.10 — 405 405 0.02 < 0.005 — 406 Dust
From
Material
Movement
— — — — — — 0.16 0.16 — 0.06 0.06 — — — — — — —
Onsite
truck

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 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment

0.05 0.04 0.41 0.35 < 0.005 0.02 — 0.02 0.02 — 0.02 — 67.0 67.0 < 0.005 < 0.005 — 67.2 Dust
From
Material
Movement
— — — — — — 0.03 0.03 — 0.01 0.01 — — — — — — —
Onsite
truck

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 0.00 Offsite — — — — — — — — — — — — — — — — — —
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Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.11 0.10 0.11 1.26 0.00 0.00 0.02 0.02 0.00 0.00 0.00 — 265 265 0.01 0.01 0.03 268 Vendor < 0.005 < 0.005 0.09 0.03 < 0.005 < 0.005 < 0.005 0.01 < 0.005 < 0.005 < 0.005 — 73.3 73.3 < 0.005 0.01 0.01 76.7 Hauling 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 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.01 0.01 0.01 0.08 0.00 0.00 < 0.005 < 0.005 0.00 0.00 0.00 — 16.1 16.1 < 0.005 < 0.005 0.03 16.4 Vendor < 0.005 < 0.005 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — 4.42 4.42 < 0.005 < 0.005 0.01 4.62 Hauling 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 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.01 0.00 0.00 < 0.005 < 0.005 0.00 0.00 0.00 — 2.67 2.67 < 0.005 < 0.005 < 0.005 2.71 Vendor < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — 0.73 0.73 < 0.005 < 0.005 < 0.005 0.77 Hauling 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 0.00

3.7. Building Construction (2024) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

1.55 1.30 12.2 14.2 0.03 0.54 — 0.54 0.49 — 0.49 — 2,630 2,630 0.11 0.02 — 2,639 Onsite
truck

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 0.00 14984 - Whitewood Detailed Report, 12/8/2022
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Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

1.55 1.30 12.2 14.2 0.03 0.54 — 0.54 0.49 — 0.49 — 2,630 2,630 0.11 0.02 — 2,639 Onsite
truck

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 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

0.92 0.77 7.20 8.42 0.02 0.32 — 0.32 0.29 — 0.29 — 1,557 1,557 0.06 0.01 — 1,562 Onsite
truck

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 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment

0.17 0.14 1.31 1.54 < 0.005 0.06 — 0.06 0.05 — 0.05 — 258 258 0.01 < 0.005 — 259 Onsite
truck

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 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Worker 1.06 0.97 0.91 15.7 0.00 0.00 0.15 0.15 0.00 0.00 0.00 — 2,715 2,715 0.11 0.09 10.8 2,757 Vendor 0.03 0.02 0.82 0.25 0.01 0.01 0.04 0.05 0.01 0.02 0.03 — 719 719 0.02 0.11 2.03 754 Hauling 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 0.00 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 1.01 0.91 1.07 11.9 0.00 0.00 0.15 0.15 0.00 0.00 0.00 — 2,495 2,495 0.12 0.09 0.28 2,526 Vendor 0.03 0.02 0.85 0.26 0.01 0.01 0.04 0.05 0.01 0.02 0.03 — 720 720 0.02 0.11 0.05 753 Hauling 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 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
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Worker 0.59 0.54 0.63 7.42 0.00 0.00 0.09 0.09 0.00 0.00 0.00 — 1,496 1,496 0.07 0.06 2.75 1,517 Vendor 0.02 0.01 0.50 0.15 < 0.005 0.01 0.02 0.03 0.01 0.01 0.02 — 426 426 0.01 0.06 0.52 446 Hauling 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 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker 0.11 0.10 0.12 1.35 0.00 0.00 0.02 0.02 0.00 0.00 0.00 — 248 248 0.01 0.01 0.46 251 Vendor < 0.005 < 0.005 0.09 0.03 < 0.005 < 0.005 < 0.005 0.01 < 0.005 < 0.005 < 0.005 — 70.5 70.5 < 0.005 0.01 0.09 73.8 Hauling 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 0.00

3.9. Paving (2024) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

1.01 0.85 7.81 10.0 0.01 0.39 — 0.39 0.36 — 0.36 — 1,512 1,512 0.06 0.01 — 1,517 Paving — 1.37 — — — — — — — — — — — — — — — —
Onsite
truck

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 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

0.04 0.04 0.34 0.44 < 0.005 0.02 — 0.02 0.02 — 0.02 — 66.3 66.3 < 0.005 < 0.005 — 66.5 Paving — 0.06 — — — — — — — — — — — — — — — —
Onsite
truck

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 0.00 14984 - Whitewood Detailed Report, 12/8/2022
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Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment

0.01 0.01 0.06 0.08 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 11.0 11.0 < 0.005 < 0.005 — 11.0 Paving — 0.01 — — — — — — — — — — — — — — — —
Onsite
truck

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 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Worker 0.08 0.07 0.09 0.95 0.00 0.00 0.01 0.01 0.00 0.00 0.00 — 198 198 0.01 0.01 0.02 201 Vendor 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 0.00 Hauling 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 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.04 0.00 0.00 < 0.005 < 0.005 0.00 0.00 0.00 — 8.81 8.81 < 0.005 < 0.005 0.02 8.93 Vendor 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 0.00 Hauling 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 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.01 0.00 0.00 < 0.005 < 0.005 0.00 0.00 0.00 — 1.46 1.46 < 0.005 < 0.005 < 0.005 1.48 Vendor 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 0.00 Hauling 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 0.00

3.11. Architectural Coating (2024) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Onsite — — — — — — — — — — — — — — — — — —
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Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

0.22 0.18 1.21 1.53 < 0.005 0.04 — 0.04 0.04 — 0.04 — 178 178 0.01 < 0.005 — 179 Architect
ural
Coatings
— 64.7 — — — — — — — — — — — — — — — —
Onsite
truck

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 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Off-Road
Equipment

0.03 0.02 0.14 0.18 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 20.5 20.5 < 0.005 < 0.005 — 20.6 Architect
ural
Coatings
— 7.45 — — — — — — — — — — — — — — — —
Onsite
truck

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 0.00 Annual — — — — — — — — — — — — — — — — — —
Off-Road
Equipment
< 0.005 < 0.005 0.03 0.03 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 3.39 3.39 < 0.005 < 0.005 — 3.40 Architect
ural
Coatings
— 1.36 — — — — — — — — — — — — — — — —
Onsite
truck

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 0.00 Offsite — — — — — — — — — — — — — — — — — —
Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
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——————————————————Daily,
Winter
(Max)
Worker 0.20 0.18 0.21 2.38 0.00 0.00 0.03 0.03 0.00 0.00 0.00 — 499 499 0.02 0.02 0.06 505 Vendor 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 0.00 Hauling 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 0.00 Average
Daily
— — — — — — — — — — — — — — — — — —
Worker 0.02 0.02 0.02 0.29 0.00 0.00 < 0.005 < 0.005 0.00 0.00 0.00 — 58.2 58.2 < 0.005 < 0.005 0.11 59.0 Vendor 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 0.00 Hauling 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 0.00 Annual — — — — — — — — — — — — — — — — — —
Worker < 0.005 < 0.005 < 0.005 0.05 0.00 0.00 < 0.005 < 0.005 0.00 0.00 0.00 — 9.63 9.63 < 0.005 < 0.005 0.02 9.76 Vendor 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 0.00 Hauling 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 0.00

4. Operations Emissions Details

4.1. Mobile Emissions by Land Use

4.1.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e

5.59 5.15 4.85 43.7 0.10 0.08 3.30 3.38 0.07 0.59 0.66 — 10,329 10,329 0.43 0.46 41.7 10,519 14984 - Whitewood Detailed Report, 12/8/2022
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Apartme
Low Rise

4.37 4.02 3.79 34.1 0.08 0.06 2.58 2.64 0.06 0.46 0.51 — 8,070 8,070 0.34 0.36 32.5 8,218 Parking
Lot

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 0.00 Other
Asphalt
Surfaces

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 0.00 Total 9.96 9.17 8.64 77.8 0.18 0.14 5.88 6.01 0.13 1.04 1.17 — 18,399 18,399 0.77 0.82 74.2 18,738 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e

5.22 4.77 5.21 36.7 0.09 0.08 3.30 3.38 0.07 0.59 0.66 — 9,699 9,699 0.45 0.48 1.08 9,854 Apartme
nts
Low Rise

4.08 3.73 4.07 28.7 0.07 0.06 2.58 2.64 0.06 0.46 0.51 — 7,577 7,577 0.35 0.37 0.84 7,698 Parking
Lot

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 0.00 Other
Asphalt
Surfaces

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 0.00 Total 9.30 8.50 9.27 65.4 0.17 0.14 5.88 6.01 0.13 1.04 1.17 — 17,276 17,276 0.80 0.85 1.92 17,552 Annual — — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e

0.80 0.73 0.82 5.88 0.01 0.01 0.51 0.52 0.01 0.09 0.10 — 1,373 1,373 0.06 0.07 2.52 1,397 Apartme
nts
Low Rise

0.66 0.60 0.68 4.84 0.01 0.01 0.42 0.43 0.01 0.07 0.08 — 1,130 1,130 0.05 0.06 2.08 1,150 Parking
Lot

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 0.00 Other
Asphalt
Surfaces

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 0.00 14984 - Whitewood Detailed Report, 12/8/2022
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Total 1.46 1.33 1.50 10.7 0.03 0.02 0.93 0.95 0.02 0.17 0.19 — 2,503 2,503 0.11 0.12 4.60 2,547

4.2. Energy

4.2.1. Electricity Emissions By Land Use - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e
— — — — — — — — — — — — 910 910 0.09 0.01 — 915
Apartme
nts
Low Rise
— — — — — — — — — — — — 863 863 0.08 0.01 — 868
Parking
Lot
— — — — — — — — — — — — 91.8 91.8 0.01 < 0.005 — 92.4
Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 1,865 1,865 0.18 0.02 — 1,876 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e
— — — — — — — — — — — — 910 910 0.09 0.01 — 915
Apartme
nts
Low Rise
— — — — — — — — — — — — 863 863 0.08 0.01 — 868
Parking
Lot
— — — — — — — — — — — — 91.8 91.8 0.01 < 0.005 — 92.4
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Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 1,865 1,865 0.18 0.02 — 1,876 Annual — — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e
— — — — — — — — — — — — 151 151 0.01 < 0.005 — 152
Apartme
nts
Low Rise
— — — — — — — — — — — — 143 143 0.01 < 0.005 — 144
Parking
Lot
— — — — — — — — — — — — 15.2 15.2 < 0.005 < 0.005 — 15.3 Other
Asphalt
Surfaces
— — — — — — — — — — — — 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — — 309 309 0.03 < 0.005 — 311

4.2.3. Natural Gas Emissions By Land Use - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e

0.08 0.04 0.68 0.29 < 0.005 0.06 — 0.06 0.06 — 0.06 — 869 869 0.08 < 0.005 — 871 Apartme
nts
Low Rise

0.07 0.03 0.57 0.24 < 0.005 0.05 — 0.05 0.05 — 0.05 — 718 718 0.06 < 0.005 — 720 Parking
Lot

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 14984 - Whitewood Detailed Report, 12/8/2022
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0.00—0.000.000.000.00—0.00—0.000.00—0.000.000.000.000.000.00Other Asphalt
Surfaces
Total 0.15 0.07 1.25 0.53 0.01 0.10 — 0.10 0.10 — 0.10 — 1,587 1,587 0.14 < 0.005 — 1,591 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e

0.08 0.04 0.68 0.29 < 0.005 0.06 — 0.06 0.06 — 0.06 — 869 869 0.08 < 0.005 — 871 Apartme
nts
Low Rise

0.07 0.03 0.57 0.24 < 0.005 0.05 — 0.05 0.05 — 0.05 — 718 718 0.06 < 0.005 — 720 Parking
Lot

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 Other
Asphalt
Surfaces

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 Total 0.15 0.07 1.25 0.53 0.01 0.10 — 0.10 0.10 — 0.10 — 1,587 1,587 0.14 < 0.005 — 1,591 Annual — — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e

0.01 0.01 0.12 0.05 < 0.005 0.01 — 0.01 0.01 — 0.01 — 144 144 0.01 < 0.005 — 144 Apartme
nts
Low Rise

0.01 0.01 0.10 0.04 < 0.005 0.01 — 0.01 0.01 — 0.01 — 119 119 0.01 < 0.005 — 119 Parking
Lot

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 Other
Asphalt
Surfaces

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 Total 0.03 0.01 0.23 0.10 < 0.005 0.02 — 0.02 0.02 — 0.02 — 263 263 0.02 < 0.005 — 263

4.3. Area Emissions by Source
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4.3.2. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Source TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Hearths 0.46 0.23 3.91 1.66 0.02 0.32 — 0.32 0.32 — 0.32 0.00 4,965 4,965 0.09 0.01 — 4,970 Consum
er
Products
— 8.98 — — — — — — — — — — — — — — — —
Architect
ural
Coatings
— 0.74 — — — — — — — — — — — — — — — —
Landsca
pe
Equipme
nt

1.43 1.36 0.15 14.8 < 0.005 0.01 — 0.01 0.01 — 0.01 — 39.7 39.7 < 0.005 < 0.005 — 39.9 Total 1.89 11.3 4.06 16.5 0.03 0.32 — 0.32 0.32 — 0.32 0.00 5,005 5,005 0.10 0.01 — 5,010 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Hearths 0.46 0.23 3.91 1.66 0.02 0.32 — 0.32 0.32 — 0.32 0.00 4,965 4,965 0.09 0.01 — 4,970 Consum
er
Products
— 8.98 — — — — — — — — — — — — — — — —
Architect
ural
Coatings
— 0.74 — — — — — — — — — — — — — — — —
Total 0.46 9.95 3.91 1.66 0.02 0.32 — 0.32 0.32 — 0.32 0.00 4,965 4,965 0.09 0.01 — 4,970 Annual — — — — — — — — — — — — — — — — — —
Hearths 0.01 < 0.005 0.05 0.02 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 0.00 56.3 56.3 < 0.005 < 0.005 — 56.4 14984 - Whitewood Detailed Report, 12/8/2022
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————————————————1.64—Consum
er
Products
Architect
ural
Coatings
— 0.14 — — — — — — — — — — — — — — — —
Landsca
pe
Equipme
nt

0.18 0.17 0.02 1.85 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 4.51 4.51 < 0.005 < 0.005 — 4.52 Total 0.18 1.95 0.07 1.87 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 0.00 60.8 60.8 < 0.005 < 0.005 — 60.9

4.4. Water Emissions by Land Use

4.4.2. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e
— — — — — — — — — — — 10.1 34.4 44.5 1.04 0.03 — 78.0
Apartme
nts
Low Rise
— — — — — — — — — — — 10.3 34.9 45.2 1.06 0.03 — 79.2
Parking
Lot
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Other
Asphalt
Surfaces
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — 20.4 69.3 89.7 2.10 0.05 — 157 14984 - Whitewood Detailed Report, 12/8/2022
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——————————————————Daily,
Winter
(Max)
Condo/T
ownhous
e
— — — — — — — — — — — 10.1 34.4 44.5 1.04 0.03 — 78.0
Apartme
nts
Low Rise
— — — — — — — — — — — 10.3 34.9 45.2 1.06 0.03 — 79.2
Parking
Lot
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Other
Asphalt
Surfaces
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — 20.4 69.3 89.7 2.10 0.05 — 157 Annual — — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e
— — — — — — — — — — — 1.68 5.69 7.37 0.17 < 0.005 — 12.9 Apartme
nts
Low Rise
— — — — — — — — — — — 1.70 5.78 7.48 0.18 < 0.005 — 13.1 Parking
Lot
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Other
Asphalt
Surfaces
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — 3.38 11.5 14.9 0.35 0.01 — 26.0

4.5. Waste Emissions by Land Use

4.5.2. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) 14984 - Whitewood Detailed Report, 12/8/2022
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Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e
— — — — — — — — — — — 51.8 0.00 51.8 5.18 0.00 — 181
Apartme
nts
Low Rise
— — — — — — — — — — — 52.6 0.00 52.6 5.25 0.00 — 184
Parking
Lot
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Other
Asphalt
Surfaces
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — 104 0.00 104 10.4 0.00 — 365 Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e
— — — — — — — — — — — 51.8 0.00 51.8 5.18 0.00 — 181
Apartme
nts
Low Rise
— — — — — — — — — — — 52.6 0.00 52.6 5.25 0.00 — 184
Parking
Lot
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Other
Asphalt
Surfaces
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — 104 0.00 104 10.4 0.00 — 365 Annual — — — — — — — — — — — — — — — — — —
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30.0—0.000.868.580.008.58———————————Condo/T
ownhous
e
Apartme
nts
Low Rise
— — — — — — — — — — — 8.70 0.00 8.70 0.87 0.00 — 30.4
Parking
Lot
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Other
Asphalt
Surfaces
— — — — — — — — — — — 0.00 0.00 0.00 0.00 0.00 — 0.00
Total — — — — — — — — — — — 17.3 0.00 17.3 1.73 0.00 — 60.5

4.6. Refrigerant Emissions by Land Use

4.6.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e
— — — — — — — — — — — — — — — — 1.60 1.60
Apartme
nts
Low Rise
— — — — — — — — — — — — — — — — 1.39 1.39
Total — — — — — — — — — — — — — — — — 2.99 2.99
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
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1.601.60————————————————Condo/T
ownhous
e
Apartme
nts
Low Rise
— — — — — — — — — — — — — — — — 1.39 1.39
Total — — — — — — — — — — — — — — — — 2.99 2.99
Annual — — — — — — — — — — — — — — — — — —
Condo/T
ownhous
e
— — — — — — — — — — — — — — — — 0.27 0.27
Apartme
nts
Low Rise
— — — — — — — — — — — — — — — — 0.23 0.23
Total — — — — — — — — — — — — — — — — 0.50 0.50

4.7. Offroad Emissions By Equipment Type

4.7.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Equipme
nt
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
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4.8. Stationary Emissions By Equipment Type

4.8.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Equipme
nt
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —

4.9. User Defined Emissions By Equipment Type

4.9.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Equipme
nt
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
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Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —

4.10. Soil Carbon Accumulation By Vegetation Type

4.10.1. Soil Carbon Accumulation By Vegetation Type - Unmitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Vegetatio
n
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —

4.10.2. Above and Belowground Carbon Accumulation by Land Use Type - Unmitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —
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——————————————————Daily,
Winter
(Max)
Total — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Total — — — — — — — — — — — — — — — — — —

4.10.3. Avoided and Sequestered Emissions by Species - Unmitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Species TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
— — — — — — — — — — — — — — — — — —
Avoided — — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Sequest
ered
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Remove
d
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
— — — — — — — — — — — — — — — — — — —
Daily,
Winter
(Max)
— — — — — — — — — — — — — — — — — —
Avoided — — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Sequest
ered
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
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——————————————————Remove
d
Subtotal — — — — — — — — — — — — — — — — — —
— — — — — — — — — — — — — — — — — — —
Annual — — — — — — — — — — — — — — — — — —
Avoided — — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Sequest
ered
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
Remove
d
— — — — — — — — — — — — — — — — — —
Subtotal — — — — — — — — — — — — — — — — — —
— — — — — — — — — — — — — — — — — — —

5. Activity Data

5.1. Construction Schedule
Phase Name Phase Type Start Date End Date Days Per Week Work Days per Phase Phase Description Demolition Demolition 1/1/2024 1/19/2024 5.00 15.0 —
Site Preparation Site Preparation 1/22/2024 1/31/2024 5.00 8.00 — Grading Grading 2/1/2024 3/1/2024 5.00 22.0 —
Building Construction Building Construction 3/4/2024 12/30/2024 5.00 216 — Paving Paving 12/9/2024 12/30/2024 5.00 16.0 —
Architectural Coating Architectural Coating 11/1/2024 12/30/2024 5.00 42.0 —

5.2. Off-Road Equipment
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5.2.1. Unmitigated
Phase Name Equipment Type Fuel Type Engine Tier Number per Day Hours Per Day Horsepower Load Factor Demolition Rubber Tired Dozers Diesel Average 2.00 8.00 367 0.40 Demolition Excavators Diesel Average 3.00 8.00 36.0 0.38 Demolition Concrete/Industrial
Saws
Diesel Average 1.00 8.00 33.0 0.73
Site Preparation Rubber Tired Dozers Diesel Average 3.00 8.00 367 0.40 Site Preparation Crawler Tractors Diesel Average 4.00 8.00 87.0 0.43 Grading Graders Diesel Average 1.00 8.00 148 0.41
Grading Excavators Diesel Average 2.00 8.00 36.0 0.38
Grading Crawler Tractors Diesel Average 2.00 8.00 87.0 0.43 Grading Scrapers Diesel Average 2.00 8.00 423 0.48
Grading Rubber Tired Dozers Diesel Average 1.00 8.00 367 0.40 Building Construction Forklifts Diesel Average 3.00 8.00 82.0 0.20 Building Construction Generator Sets Diesel Average 1.00 8.00 14.0 0.74 Building Construction Cranes Diesel Average 1.00 8.00 367 0.29 Building Construction Welders Diesel Average 1.00 8.00 46.0 0.45 Building Construction Tractors/Loaders/Backh
oes
Diesel Average 3.00 8.00 84.0 0.37
Paving Pavers Diesel Average 2.00 8.00 81.0 0.42
Paving Paving Equipment Diesel Average 2.00 8.00 89.0 0.36 Paving Rollers Diesel Average 2.00 8.00 36.0 0.38
Architectural Coating Air Compressors Diesel Average 1.00 8.00 37.0 0.48

5.3. Construction Vehicles

5.3.1. Unmitigated
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Phase Name Trip Type One-Way Trips per Day Miles per Trip Vehicle Mix Demolition — — — —
Demolition Worker 15.0 18.5 LDA,LDT1,LDT2
Demolition Vendor 1.61 10.2 HHDT,MHDT
Demolition Hauling 2.33 20.0 HHDT
Demolition Onsite truck — — HHDT
Site Preparation — — — —
Site Preparation Worker 17.5 18.5 LDA,LDT1,LDT2
Site Preparation Vendor 0.86 10.2 HHDT,MHDT
Site Preparation Hauling 0.00 20.0 HHDT
Site Preparation Onsite truck — — HHDT
Grading — — — —
Grading Worker 20.0 18.5 LDA,LDT1,LDT2
Grading Vendor 2.36 10.2 HHDT,MHDT
Grading Hauling 0.00 20.0 HHDT
Grading Onsite truck — — HHDT
Building Construction — — — —
Building Construction Worker 189 18.5 LDA,LDT1,LDT2
Building Construction Vendor 23.2 10.2 HHDT,MHDT
Building Construction Hauling 0.00 20.0 HHDT
Building Construction Onsite truck — — HHDT
Paving — — — —
Paving Worker 15.0 18.5 LDA,LDT1,LDT2
Paving Vendor — 10.2 HHDT,MHDT
Paving Hauling 0.00 20.0 HHDT
Paving Onsite truck — — HHDT
Architectural Coating — — — —
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Architectural Coating Worker 37.7 18.5 LDA,LDT1,LDT2
Architectural Coating Vendor — 10.2 HHDT,MHDT
Architectural Coating Hauling 0.00 20.0 HHDT
Architectural Coating Onsite truck — — HHDT

5.4. Vehicles

5.4.1. Construction Vehicle Control Strategies
Non-applicable. No control strategies activated by user.

5.5. Architectural Coatings
Phase Name Residential Interior Area Coated
(sq ft)
Residential Exterior Area Coated
(sq ft)
Non-Residential Interior Area
Coated (sq ft)
Non-Residential Exterior Area
Coated (sq ft)
Parking Area Coated (sq ft)
Architectural Coating 846,705 282,235 0.00 0.00 21,797

5.6. Dust Mitigation

5.6.1. Construction Earthmoving Activities
Phase Name Material Imported (cy) Material Exported (cy) Acres Graded (acres) Material Demolished (Building Square Footage)
Acres Paved (acres)
Demolition 0.00 0.00 0.00 2,976 —
Site Preparation — — 28.0 0.00 —
Grading — — 88.0 0.00 —
Paving 0.00 0.00 0.00 0.00 8.34

5.6.2. Construction Earthmoving Control Strategies
Control Strategies Applied Frequency (per day) PM10 Reduction PM2.5 Reduction Water Exposed Area 3 74% 74%
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5.7. Construction Paving
Land Use Area Paved (acres) % Asphalt
Condo/Townhouse — 0%
Apartments Low Rise — 0%
Parking Lot 2.52 100%
Other Asphalt Surfaces 5.82 100%

5.8. Construction Electricity Consumption and Emissions Factors kWh per Y ear and Emission Factor (lb/MWh)
Y ear kWh per Y ear CO2 CH4 N2O
2024 0.00 349 0.03 < 0.005

5.9. Operational Mobile Sources

5.9.1. Unmitigated
Land Use Type Trips/Weekday Trips/Saturday Trips/Sunday Trips/Y ear VMT/Weekday VMT/Saturday VMT/Sunday VMT/Y ear Condo/Townhouse 936 1,139 932 352,011 9,751 11,864 9,710 3,667,177 Apartments Low
Rise
890 601 510 289,837 9,268 6,257 5,308 3,019,461
Parking Lot 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Other Asphalt
Surfaces

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

5.10. Operational Area Sources

5.10.1. Hearths
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5.10.1.1. Unmitigated
Hearth Type Unmitigated (number)
Condo/Townhouse —
Wood Fireplaces 0
Gas Fireplaces 117
Propane Fireplaces 0
Electric Fireplaces 0
No Fireplaces 13
Apartments Low Rise —
Wood Fireplaces 0
Gas Fireplaces 119
Propane Fireplaces 0
Electric Fireplaces 0
No Fireplaces 13

5.10.2. Architectural Coatings
Residential Interior Area Coated (sq ft) Residential Exterior Area Coated (sq ft) Non-Residential Interior Area Coated (sq ft)
Non-Residential Exterior Area Coated
(sq ft)
Parking Area Coated (sq ft)
846705.1499999999 282,235 0.00 0.00 21,797

5.10.3. Landscape Equipment
Season Unit Value
Snow Days day/yr 0.00
Summer Days day/yr 250

5.11. Operational Energy Consumption
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5.11.1. Unmitigated
Electricity (kWh/yr) and CO2 and CH4 and N2O and Natural Gas (kBTU/yr) Land Use Electricity (kWh/yr) CO2 CH4 N2O Natural Gas (kBTU/yr) Condo/Townhouse 952,788 349 0.0330 0.0040 2,710,588
Apartments Low Rise 903,776 349 0.0330 0.0040 2,240,069 Parking Lot 96,160 349 0.0330 0.0040 0.00
Other Asphalt Surfaces 0.00 349 0.0330 0.0040 0.00

5.12. Operational Water and Wastewater Consumption

5.12.1. Unmitigated
Land Use Indoor Water (gal/year) Outdoor Water (gal/year) Condo/Townhouse 5,287,591 0.00
Apartments Low Rise 5,368,938 0.00
Parking Lot 0.00 0.00
Other Asphalt Surfaces 0.00 0.00

5.13. Operational Waste Generation

5.13.1. Unmitigated
Land Use Waste (ton/year) Cogeneration (kWh/year)
Condo/Townhouse 29.8 0.00
Apartments Low Rise 30.2 0.00
Parking Lot 0.00 0.00
Other Asphalt Surfaces 0.00 0.00
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5.14. Operational Refrigeration and Air Conditioning Equipment

5.14.1. Unmitigated
Land Use Type Equipment Type Refrigerant GWP Quantity (kg) Operations Leak Rate Service Leak Rate Times Serviced Condo/Townhouse Average room A/C &
Other residential A/C
and heat pumps
R-410A 2,088 < 0.005 2.50 2.50 10.0
Condo/Townhouse Household refrigerators
and/or freezers
R-134a 1,430 0.12 0.60 0.00 1.00
Apartments Low Rise Average room A/C &
Other residential A/C
and heat pumps
R-410A 2,088 < 0.005 2.50 2.50 10.0
Apartments Low Rise Household refrigerators
and/or freezers
R-134a 1,430 0.12 0.60 0.00 1.00

5.15. Operational Off-Road Equipment

5.15.1. Unmitigated
Equipment Type Fuel Type Engine Tier Number per Day Hours Per Day Horsepower Load Factor

5.16. Stationary Sources

5.16.1. Emergency Generators and Fire Pumps
Equipment Type Fuel Type Number per Day Hours per Day Hours per Y ear Horsepower Load Factor

5.16.2. Process Boilers
Equipment Type Fuel Type Number Boiler Rating (MMBtu/hr) Daily Heat Input (MMBtu/day) Annual Heat Input (MMBtu/yr) 14984 - Whitewood Detailed Report, 12/8/2022
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5.17. User Defined
Equipment Type Fuel Type
— —

5.18. Vegetation

5.18.1. Land Use Change

5.18.1.1. Unmitigated
Vegetation Land Use Type Vegetation Soil Type Initial Acres Final Acres

5.18.1. Biomass Cover Type

5.18.1.1. Unmitigated
Biomass Cover Type Initial Acres Final Acres

5.18.2. Sequestration

5.18.2.1. Unmitigated
Tree Type Number Electricity Saved (kWh/year) Natural Gas Saved (btu/year)

6. Climate Risk Detailed Report

6.1. Climate Risk Summary
Cal-Adapt midcentury 2040–2059 average projections for four hazards are reported below for your project location. These are under Representation Concentration Pathway (RCP) 8.5 which assumes GHG emissions will continue to rise strongly through 2050 and then plateau around 2100.

Climate Hazard Result for Project Location Unit
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Temperature and Extreme Heat 28.6 annual days of extreme heat Extreme Precipitation 3.45 annual days with precipitation above 20 mm Sea Level Rise 0.00 meters of inundation depth
Wildfire 16.5 annual hectares burned
Temperature and Extreme Heat data are for grid cell in which your project are located. The projection is based on the 98th historical percentile of daily maximum/minimum temperatures from observed historical data (32 climate model ensemble from Cal-Adapt, 2040–2059 average under RCP 8.5). Each grid cell is 6 kilometers (km) by 6 km, or 3.7 miles (mi) by 3.7 mi.

Extreme Precipitation data are for the grid cell in which your project are located. The threshold of 20 mm is equivalent to about ¾ an inch of rain, which would be light to moderate rainfall if received over a full day or heavy rain if received over a period of 2 to 4 hours. Each grid cell is 6 kilometers (km) by 6 km, or 3.7 miles (mi) by 3.7 mi.

Sea Level Rise data are for the grid cell in which your project are located. The projections are from Radke et al. (2017), as reported in Cal-Adapt (2040–2059 average under RCP 8.5), and consider different increments of sea level rise coupled with extreme storm events. Users may select from four model simulations to view the range in potential inundation depth for the grid cell. The four simulations make different assumptions about expected rainfall and temperature are: Warmer/drier (HadGEM2-ES), Cooler/wetter (CNRM-CM5), Average conditions (CanESM2), Range of different rainfall and temperature possibilities (MIROC5). Each grid cell is 50 meters (m) by 50 m, or about 164 feet (ft) by 164 ft.

Wildfire data are for the grid cell in which your project are located. The projections are from UC Davis, as reported in Cal-Adapt (2040–2059 average under RCP 8.5), and consider historical data of climate, vegetation, population density, and large (> 400 ha) fire history. Users may select from four model simulations to view the range in potential wildfire probabilities for the grid cell. The four simulations make different assumptions about expected rainfall and temperature are: Warmer/drier (HadGEM2-ES), Cooler/wetter (CNRM-CM5), Average conditions (CanESM2), Range of different rainfall and temperature possibilities (MIROC5). Each grid cell is 6 kilometers (km) by 6 km, or 3.7 miles (mi) by 3.7 mi.

6.2. Initial Climate Risk Scores
Climate Hazard Exposure Score Sensitivity Score Adaptive Capacity Score Vulnerability Score Temperature and Extreme Heat 3 0 0 N/A
Extreme Precipitation N/A N/A N/A N/A
Sea Level Rise 1 0 0 N/A
Wildfire 1 0 0 N/A
Flooding N/A N/A N/A N/A
Drought N/A N/A N/A N/A
Snowpack Reduction N/A N/A N/A N/A
Air Quality Degradation 0 0 0 N/A
The sensitivity score reflects the extent to which a project would be adversely affected by exposure to a climate hazard. Exposure is rated on a scale of 1 to 5, with a score of 5 representing the greatest exposure.

The adaptive capacity of a project refers to its ability to manage and reduce vulnerabilities from projected climate hazards. Adaptive capacity is rated on a scale of 1 to 5, with a score of 5 representing the greatest ability to adapt.

The overall vulnerability scores are calculated based on the potential impacts and adaptive capacity assessments for each hazard. Scores do not include implementation of climate risk reduction measures. 14984 - Whitewood Detailed Report, 12/8/2022
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6.3. Adjusted Climate Risk Scores
Climate Hazard Exposure Score Sensitivity Score Adaptive Capacity Score Vulnerability Score Temperature and Extreme Heat 3 1 1 3
Extreme Precipitation N/A N/A N/A N/A
Sea Level Rise 1 1 1 2
Wildfire 1 1 1 2
Flooding N/A N/A N/A N/A
Drought N/A N/A N/A N/A
Snowpack Reduction N/A N/A N/A N/A
Air Quality Degradation 1 1 1 2
The sensitivity score reflects the extent to which a project would be adversely affected by exposure to a climate hazard. Exposure is rated on a scale of 1 to 5, with a score of 5 representing the greatest exposure.

The overall vulnerability scores are calculated based on the potential impacts and adaptive capacity assessments for each hazard. Scores include implementation of climate risk reduction measures.

6.4. Climate Risk Reduction Measures

7. Health and Equity Details

7.1. CalEnviroScreen 4.0 Scores
The maximum CalEnviroScreen score is 100. A high score (i.e., greater than 50) reflects a higher pollution burden compared to other census tracts in the state.

Indicator Result for Project Census Tract
Exposure Indicators —
AQ-Ozone 80.0
AQ-PM 40.4
AQ-DPM 31.3
Drinking Water 11.0
Lead Risk Housing 4.06
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Pesticides 13.6
Toxic Releases 14.3
Traffic 81.3
Effect Indicators —
CleanUp Sites 0.00
Groundwater 0.00
Haz Waste Facilities/Generators 73.6
Impaired Water Bodies 58.7
Solid Waste 0.00
Sensitive Population —
Asthma 31.6
Cardio-vascular 76.0
Low Birth Weights 56.6
Socioeconomic Factor Indicators —
Education 40.1
Housing 12.8
Linguistic 8.49
Poverty 34.9
Unemployment 48.3

7.2. Healthy Places Index Scores
The maximum Health Places Index score is 100. A high score (i.e., greater than 50) reflects healthier community conditions compared to other census tracts in the state.

Indicator Result for Project Census Tract
Economic —
Above Poverty 70.31951752
Employed 39.30450404
Median HI 80.88027717
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Education —
Bachelor's or higher 58.29590658
High school enrollment 100
Preschool enrollment 64.72475298
Transportation —
Auto Access 89.83703323
Active commuting 12.60105223
Social —
2-parent households 73.95098165
Voting 49.22366226
Neighborhood —
Alcohol availability 89.3750802
Park access 2.194276915
Retail density 10.31695111
Supermarket access 18.61927371
Tree canopy 4.38855383
Housing —
Homeownership 67.93276017
Housing habitability 86.16707301
Low-inc homeowner severe housing cost burden 69.34428333 Low-inc renter severe housing cost burden 80.27717182
Uncrowded housing 68.66418581
Health Outcomes —
Insured adults 89.59322469
Arthritis 10.7
Asthma ER Admissions 78.7
High Blood Pressure 18.2
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Cancer (excluding skin) 10.4
Asthma 46.1
Coronary Heart Disease 23.5
Chronic Obstructive Pulmonary Disease 33.2
Diagnosed Diabetes 68.9
Life Expectancy at Birth 83.5
Cognitively Disabled 29.3
Physically Disabled 73.0
Heart Attack ER Admissions 38.4
Mental Health Not Good 64.8
Chronic Kidney Disease 45.1
Obesity 48.4
Pedestrian Injuries 39.7
Physical Health Not Good 61.7
Stroke 51.7
Health Risk Behaviors —
Binge Drinking 19.3
Current Smoker 59.6
No Leisure Time for Physical Activity 72.6
Climate Change Exposures —
Wildfire Risk 18.1
SLR Inundation Area 0.0
Children 5.7
Elderly 87.4
English Speaking 95.5
Foreign-born 16.2
Outdoor Workers 58.6
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Climate Change Adaptive Capacity —
Impervious Surface Cover 74.9
Traffic Density 62.3
Traffic Access 23.0
Other Indices —
Hardship 29.8
Other Decision Support —
2016 Voting 55.2

7.3. Overall Health & Equity Scores
Metric Result for Project Census Tract
CalEnviroScreen 4.0 Score for Project Location (a) 30.0 Healthy Places Index Score for Project Location (b) 67.0 Project Located in a Designated Disadvantaged Community (Senate Bill 535) No Project Located in a Low-Income Community (Assembly Bill 1550) No Project Located in a Community Air Protection Program Community (Assembly Bill 617) No a: The maximum CalEnviroScreen score is 100. A high score (i.e., greater than 50) reflects a higher pollution burden compared to other census tracts in the state. b: The maximum Health Places Index score is 100. A high score (i.e., greater than 50) reflects healthier community conditions compared to other census tracts in the state.

7.4. Health & Equity Measures
No Health & Equity Measures selected.

7.5. Evaluation Scorecard
Health & Equity Evaluation Scorecard not completed.

7.6. Health & Equity Custom Measures
No Health & Equity Custom Measures created.

8. User Changes to Default Data
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Screen Justification
Land Use Taken from site plan
Construction: Construction Phases Building, Paving, and Architectural Coating overlap to present a conservative analysis Construction schedule compressed to account for 2024 Opening Y ear Construction: Off-Road Equipment T/L/B replaced with Crawler Tractor to accurately calculate disturbance for Site Preparation and Grading phases
Standard 8 hours work days
Operations: Vehicle Data Trip Characteristics based on information provided in the Traffic Analysis Operations: Hearths SCAQMD Rule 445 no wood burning devices, Wood burning devices added to gas devices Construction: Trips and VMT Vendor Trips adjusted based on CalEEMod defaults for Building Construction and number of days for Demolition, Site Preparation, Grading, and Building Construction Emissions Phase Lb/Day # Days Emissions Avg/Lb Day Avg/Hourly On-Site Demolition 1.06 15 15.9 1.06 0.1325
Exhaust PM-10 Site Preparation 2.25 8 18.000 2.250 0.281 Grading 1.77 22 38.940 1.770 0.221
Building Construction 0.54 216 116.640 0.540 0.068
Paving 0.39 16 6.240 0.390 0.049
Architectural Coating 0.04 42 1.680 0.040 0.005

6.05 261 197.4 0.756321839 0.09454023
Off-Site Demolition 5.00E-03 15 0.075 0.005 0.001
Exhaust PM-10 Site Preparation 5.00E-03 8 0.040 0.005 0.001 Grading 5.00E-03 22 0.110 0.005 0.001
Building Construction 1.00E-02 216 2.160 0.010 0.001
Paving 0.00E+00 16 0.000 0.000 0.000
Architectural Coating 0.00E+00 42 0.000 0.000 0.000

2.50E-02 261 2.385 0.009137931 0.001142241
No. Days
15 8
22 216
16 42
261Total Days of Construction
3/4/2024 12/30/2024
12/9/2024 12/30/2024
Building Construction
Paving
Architectural Coating 11/1/2024 12/30/2024
1/19/2024
2/1/2024 3/1/2024
Phase
Demolition
Grading
1/1/2024
Site Preparation 1/22/2024 1/31/2024
Start Date End Date
Whitewood I Construction Health Risk Assessment
14984-06 HRA Report
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Whitewood I Construction Health Risk Assessment
14984-06 HRA Report
APPENDIX 2.2:

AERMOD MODEL INPUT/OUTPUT

**
****************************************
**
** AERMOD Input Produced by:
** AERMOD View Ver. 11.2.0
** Lakes Environmental Software Inc.
** Date: 5/9/2023
** File: C:\Users\Michael Tirohn\Desktop\HRAs\14984 Whitewood\14984 Cons\14984 Cons.ADI **
****************************************
**
**
****************************************
** AERMOD Control Pathway
****************************************
**
**

CO STARTING
TITLEONE C:\Users\Michael Tirohn\Desktop\HRAs\14984 Whitewood\14984 Cons\1498

MODELOPT DFAULT CONC

AVERTIME PERIOD
URBANOPT 2189641 Riverside_County

POLLUTID DPM

RUNORNOT RUN
ERRORFIL "14984 Cons.err"

CO FINISHED
**
****************************************
** AERMOD Source Pathway
****************************************
**
**

SO STARTING
** Source Location **
** Source ID - Type - X Coord. - Y Coord. **
** --------------------------------------------------------------------- ** Line Source Represented by Adjacent Volume Sources
** LINE VOLUME Source ID = SLINE1
** DESCRSRC
** PREFIX
** Length of Side = 14.00
** Configuration = Adjacent
** Emission Rate = 0.0001203946
** Vertical Dimension = 6.99
** SZINIT = 3.25
** Nodes = 9
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** 484641.101, 3717579.570, 462.09, 3.49, 6.51
** 484082.434, 3717583.002, 464.93, 3.49, 6.51
** 484053.452, 3717584.909, 465.77, 3.49, 6.51
** 484008.072, 3717594.442, 464.11, 3.49, 6.51
** 483837.231, 3717648.593, 459.48, 3.49, 6.51
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0.000001056 3.49 6.51 3.25 SRCPARAM L0000046 0.000001056 3.49 6.51 3.25 SRCPARAM L0000047 0.000001056 3.49 6.51 3.25 SRCPARAM L0000048 0.000001056 3.49 6.51 3.25 SRCPARAM L0000049 0.000001056 3.49 6.51 3.25 SRCPARAM L0000050 0.000001056 3.49 6.51 3.25 SRCPARAM L0000051 0.000001056 3.49 6.51 3.25 SRCPARAM L0000052 0.000001056 3.49 6.51 3.25 SRCPARAM L0000053 0.000001056 3.49 6.51 3.25 SRCPARAM L0000054 0.000001056 3.49 6.51 3.25 SRCPARAM L0000055 0.000001056 3.49 6.51 3.25 SRCPARAM L0000056 0.000001056 3.49 6.51 3.25 SRCPARAM L0000057 0.000001056 3.49 6.51 3.25 SRCPARAM L0000058 0.000001056 3.49 6.51 3.25 SRCPARAM L0000059 0.000001056 3.49 6.51 3.25 SRCPARAM L0000060 0.000001056 3.49 6.51 3.25 SRCPARAM L0000061 0.000001056 3.49 6.51 3.25 SRCPARAM L0000062 0.000001056 3.49 6.51 3.25 SRCPARAM L0000063 0.000001056 3.49 6.51 3.25 SRCPARAM L0000064 0.000001056 3.49 6.51 3.25 SRCPARAM L0000065 0.000001056 3.49 6.51 3.25 SRCPARAM L0000066 0.000001056 3.49 6.51 3.25 SRCPARAM L0000067 0.000001056 3.49 6.51 3.25 SRCPARAM L0000068 0.000001056 3.49 6.51 3.25 SRCPARAM L0000069 0.000001056 3.49 6.51 3.25 SRCPARAM L0000070 0.000001056 3.49 6.51 3.25 SRCPARAM L0000071 0.000001056 3.49 6.51 3.25 SRCPARAM L0000072 0.000001056 3.49 6.51 3.25 SRCPARAM L0000073 0.000001056 3.49 6.51 3.25 SRCPARAM L0000074 0.000001056 3.49 6.51 3.25 SRCPARAM L0000075 0.000001056 3.49 6.51 3.25 SRCPARAM L0000076 0.000001056 3.49 6.51 3.25 SRCPARAM L0000077 0.000001056 3.49 6.51 3.25 SRCPARAM L0000078 0.000001056 3.49 6.51 3.25 SRCPARAM L0000079 0.000001056 3.49 6.51 3.25 SRCPARAM L0000080 0.000001056 3.49 6.51 3.25 SRCPARAM L0000081 0.000001056 3.49 6.51 3.25 SRCPARAM L0000082 0.000001056 3.49 6.51 3.25 SRCPARAM L0000083 0.000001056 3.49 6.51 3.25 SRCPARAM L0000084 0.000001056 3.49 6.51 3.25 SRCPARAM L0000085 0.000001056 3.49 6.51 3.25 SRCPARAM L0000086 0.000001056 3.49 6.51 3.25 SRCPARAM L0000087 0.000001056 3.49 6.51 3.25 SRCPARAM L0000088 0.000001056 3.49 6.51 3.25 SRCPARAM L0000089 0.000001056 3.49 6.51 3.25 SRCPARAM L0000090 0.000001056 3.49 6.51 3.25 SRCPARAM L0000091 0.000001056 3.49 6.51 3.25 SRCPARAM L0000092 0.000001056 3.49 6.51 3.25 SRCPARAM L0000093 0.000001056 3.49 6.51 3.25 SRCPARAM L0000094 0.000001056 3.49 6.51 3.25 SRCPARAM L0000095 0.000001056 3.49 6.51 3.25 SRCPARAM L0000096 0.000001056 3.49 6.51 3.25 SRCPARAM L0000097 0.000001056 3.49 6.51 3.25 SRCPARAM L0000098 0.000001056 3.49 6.51 3.25 SRCPARAM L0000099 0.000001056 3.49 6.51 3.25 SRCPARAM L0000100 0.000001056 3.49 6.51 3.25 SRCPARAM L0000101 0.000001056 3.49 6.51 3.25 SRCPARAM L0000102 0.000001056 3.49 6.51 3.25 SRCPARAM L0000103 0.000001056 3.49 6.51 3.25 SRCPARAM L0000104 0.000001056 3.49 6.51 3.25 SRCPARAM L0000105 0.000001056 3.49 6.51 3.25 SRCPARAM L0000106 0.000001056 3.49 6.51 3.25 SRCPARAM L0000107 0.000001056 3.49 6.51 3.25 SRCPARAM L0000108 0.000001056 3.49 6.51 3.25 SRCPARAM L0000109 0.000001056 3.49 6.51 3.25 SRCPARAM L0000110 0.000001056 3.49 6.51 3.25 SRCPARAM L0000111 0.000001056 3.49 6.51 3.25 SRCPARAM L0000112 0.000001056 3.49 6.51 3.25 SRCPARAM L0000113 0.000001056 3.49 6.51 3.25 SRCPARAM L0000114 0.000001056 3.49 6.51 3.25 ** --------------------------------------------------------------------- SRCPARAM VOL1 0.0049823681 5.000 44.023 1.400 SRCPARAM VOL2 0.0049823681 5.000 44.023 1.400

URBANSRC ALL
** Variable Emissions Type: "By Hour / Day (HRDOW)"
** Variable Emission Scenario: "Scenario 1"
** WeekDays:

EMISFACT L0000001 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000001 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000001 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000001 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000002 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000002 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000002 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000002 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000003 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000003 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000003 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000003 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000004 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000004 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000004 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000004 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000005 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000005 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000005 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000005 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000006 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000006 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000006 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000006 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000007 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000007 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000007 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000007 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000008 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000008 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000008 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000008 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000009 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000009 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000009 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000009 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000010 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000010 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000010 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000010 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000011 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000011 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000011 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000011 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000012 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000012 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000012 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000012 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000013 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000013 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000013 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000013 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000014 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000014 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000014 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000014 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000015 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000015 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000015 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000015 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000016 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000016 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000016 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000016 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000017 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000017 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000017 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000017 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000018 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000018 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000018 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000018 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000019 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000019 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000019 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000019 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000020 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000020 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000020 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000020 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000021 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000021 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000021 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000021 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000022 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000022 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000022 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000022 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000023 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000023 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000023 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000023 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000024 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000024 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000024 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000024 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000025 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000025 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000025 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000025 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000026 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000026 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000026 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000026 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000027 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000027 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000027 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000027 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000028 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000028 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000028 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000028 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000029 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000029 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000029 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000029 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000030 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000030 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000030 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000030 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000031 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000031 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000031 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000031 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000032 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000032 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000032 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000032 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000033 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000033 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000033 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000033 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000034 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000034 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000034 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000034 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000035 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000035 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000035 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000035 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000036 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000036 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000036 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000036 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000037 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000037 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000037 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000037 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000038 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000038 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000038 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000038 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000039 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000039 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000039 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000039 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000040 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000040 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000040 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000040 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000041 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000041 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000041 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000041 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000042 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000042 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000042 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000042 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000043 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000043 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000043 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000043 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000044 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000044 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000044 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000044 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000045 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000045 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000045 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000045 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000046 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000046 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000046 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000046 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000047 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000047 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000047 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000047 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000048 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000048 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000048 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000048 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000049 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000049 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000049 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000049 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000050 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000050 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000050 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000050 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000051 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000051 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000051 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000051 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000052 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000052 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000052 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000052 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000053 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000053 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000053 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000053 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000054 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000054 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000054 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000054 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000055 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000055 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000055 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000055 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000056 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000056 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000056 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000056 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000057 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000057 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000057 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000057 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000058 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000058 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000058 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000058 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000059 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000059 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000059 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000059 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000060 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000060 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000060 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000060 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000061 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000061 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000061 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000061 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000062 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000062 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000062 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000062 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000063 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000063 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000063 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000063 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000064 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000064 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000064 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000064 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000065 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000065 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000065 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000065 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000066 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000066 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000066 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000066 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000067 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000067 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000067 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000067 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000068 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000068 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000068 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000068 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000069 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000069 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000069 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000069 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000070 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000070 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000070 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000070 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000071 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000071 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000071 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000071 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000072 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000072 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000072 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000072 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000073 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000073 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000073 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000073 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000074 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000074 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000074 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000074 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000075 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000075 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000075 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000075 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000076 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000076 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000076 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000076 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000077 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000077 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000077 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000077 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000078 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000078 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000078 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000078 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000079 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000079 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000079 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000079 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000080 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000080 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000080 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000080 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000081 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000081 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000081 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000081 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000082 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000082 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000082 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000082 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000083 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000083 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000083 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000083 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000084 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000084 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000084 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000084 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000085 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000085 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000085 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000085 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000086 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000086 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000086 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000086 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000087 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000087 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000087 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000087 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000088 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000088 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000088 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000088 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000089 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000089 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000089 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000089 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000090 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000090 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000090 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000090 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000091 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000091 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000091 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000091 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000092 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000092 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000092 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000092 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000093 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000093 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000093 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000093 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000094 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000094 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000094 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000094 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000095 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000095 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000095 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000095 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000096 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000096 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000096 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000096 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000097 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000097 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000097 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000097 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000098 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000098 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000098 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000098 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000099 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000099 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000099 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000099 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000100 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000100 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000100 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000100 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000101 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000101 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000101 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000101 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000102 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000102 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000102 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000102 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000103 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000103 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000103 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000103 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000104 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000104 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000104 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000104 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000105 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000105 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000105 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000105 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000106 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000106 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000106 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000106 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000107 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000107 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000107 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000107 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000108 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000108 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000108 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000108 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000109 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000109 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000109 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000109 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000110 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000110 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000110 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000110 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000111 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000111 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000111 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000111 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000112 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000112 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000112 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000112 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000113 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000113 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000113 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000113 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000114 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000114 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT L0000114 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT L0000114 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
** Saturday:

EMISFACT L0000001 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000001 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000001 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000001 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000002 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000002 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000002 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000002 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000003 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000003 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000003 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000003 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000004 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000004 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000004 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000004 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000005 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000005 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000005 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000005 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000006 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000006 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000006 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000006 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000007 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000007 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000007 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000007 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000008 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000008 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000008 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000008 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000009 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000009 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000009 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000009 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000010 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
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EMISFACT L0000077 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000077 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000078 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000078 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000078 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000078 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000079 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000079 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000079 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000079 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000080 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000080 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000080 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000080 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000081 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000081 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000081 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000081 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000082 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000082 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000082 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000082 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000083 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000083 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000083 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000083 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000084 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000084 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000084 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000084 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000085 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000085 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000085 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000085 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000086 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000086 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000086 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000086 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000087 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000087 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000087 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000087 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000088 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000088 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000088 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000088 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000089 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000089 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000089 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000089 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000090 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000090 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000090 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000090 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000091 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000091 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000091 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000091 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000092 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000092 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000092 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000092 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000093 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000093 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000093 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000093 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000094 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000094 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000094 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000094 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000095 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000095 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000095 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000095 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000096 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000096 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000096 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000096 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000097 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000097 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000097 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000097 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000098 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000098 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000098 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000098 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000099 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000099 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000099 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000099 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000100 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000100 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000100 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000100 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000101 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000101 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000101 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000101 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000102 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000102 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000102 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000102 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000103 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000103 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000103 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000103 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000104 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000104 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000104 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000104 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000105 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000105 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000105 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000105 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000106 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000106 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000106 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000106 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000107 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000107 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000107 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000107 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000108 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000108 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000108 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000108 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000109 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000109 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000109 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000109 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000110 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000110 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000110 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000110 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000111 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000111 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000111 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000111 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000112 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000112 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000112 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000112 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000113 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000113 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000113 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000113 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000114 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000114 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000114 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT L0000114 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
** Sunday:

EMISFACT VOL1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL1 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT VOL1 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT VOL1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
** Saturday:

EMISFACT VOL1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
** Sunday:

EMISFACT VOL1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
** WeekDays:

EMISFACT VOL2 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL2 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0
EMISFACT VOL2 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0
EMISFACT VOL2 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
** Saturday:

EMISFACT VOL2 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL2 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL2 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL2 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
** Sunday:

EMISFACT VOL2 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL2 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL2 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0
EMISFACT VOL2 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0

SRCGROUP ALL

SO FINISHED
**
****************************************
** AERMOD Receptor Pathway
****************************************
**
**

RE STARTING
INCLUDED "14984 Cons.rou"

RE FINISHED
**
****************************************
** AERMOD Meteorology Pathway
****************************************
**
**

ME STARTING
SURFFILE ELSI_V9_ADJU\ELSI_v9.SFC
PROFFILE ELSI_V9_ADJU\ELSI_v9.PFL
SURFDATA 3171 2012
UAIRDATA 3190 2012
SITEDATA 99999 2012
PROFBASE 406.0 METERS

ME FINISHED
**
****************************************
** AERMOD Output Pathway
****************************************
**
**

OU STARTING
** Auto-Generated Plotfiles
PLOTFILE PERIOD ALL "14984 Cons.AD\PE00GALL.PLT" 31
SUMMFILE "14984 Cons.sum"

OU FINISHED
**
****************************************
** Project Parameters
****************************************
** PROJCTN CoordinateSystemUTM
** DESCPTN UTM: Universal Transverse Mercator
** DATUM North American Datum 1983
** DTMRGN CONUS
** UNITS m
** ZONE 11
** ZONEINX 0
**
** Lakes Environmental AERMOD MPI
**
****************************************
**
** AERMOD Input Produced by:
** AERMOD View Ver. 11.2.0
** Lakes Environmental Software Inc.
** Date: 5/9/2023
** File: C:\Users\Michael Tirohn\Desktop\HRAs\14984 Whitewood\14984 Cons\14984 Cons.ADI **
****************************************
**
**
****************************************
** AERMOD Control Pathway
****************************************
**
**