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Home My WebLink AboutAppendix B - Air Quality and Greenhouse Gas AssessmentTECHNICAL MEMORANDUM 20341 SW Birch Street | Suite 230 | Newport Beach, CA 92660 | (949) 660-1994 | urbanxroads.com DATE: February 16, 2026 FROM: Haseeb Qureshi, Ali Dadabhoy, Urban Crossroads, Inc. JOB NO: 16758-03 AQ & GHG Assessment SUBJECT: ALMOND AVENUE TRAILER YARD (MCN25-0059) AIR QUALITY AND GREENHOUSE GAS ASSESSMENT Urban Crossroads, Inc. is pleased to provide the following Air Quality and Greenhouse Gas Assessment for the Almond Avenue Trailer Yard (MCN25-0059) (Project), which is located at 9882 Almond Avenue (west of Almond Avenue and approximately 1,220 feet south of San Bernardino Avenue) within the Southwest Industrial Park Speciﬁc Plan (SWIP) in the City of Fontana. PROJECT OVERVIEW It is our understanding that the Project is to consist of a 9.49-acre trailer yard with a 1,248 square foot pre-fabricated oﬃce building and 294 12-foot by 53-foot trailer stalls. It is anticipated that the project will be processed as a California Environmental Quality Act (CEQA) Addendum to the SWIP Environmental Impact Report (EIR), as such, a comparative assessment of what is allowed under the SWIP EIR for the subject site will be included, as applicable. Exhibit 1 shows the location map and Exhibit 2 shows the preliminary site plan. The Project proposes a single access point on Almond Avenue. The Project’s anticipated Opening Year is 2028. SUMMARY OF FINDINGS Results of the assessment indicate that the Project would result in a less than signiﬁcant impact with respect to air quality and greenhouse gases (GHG). 16758-03 AQ & GHG Assessment 2 Almond Avenue Trailer Yard (MCN25-0059) EXHIBIT 2: LOCATION MAP 16758-03 AQ & GHG Assessment 3 Almond Avenue Trailer Yard (MCN25-0059) EXHIBIT 1: SITE PLAN 16758-03 AQ & GHG Assessment 4 Almond Avenue Trailer Yard (MCN25-0059) PROJECT AIR QUALITY IMPACTS AIR QUALITY SETTING South Coast Air Basin (SCAB) The Project site is located in the SCAB within the jurisdiction of South Coast Air Quality Management District (SCAQMD) (1). The SCAQMD was created by the 1977 Lewis-Presley Air Quality Management Act, which merged four county air pollution control bodies into one regional district. Under the Act, the SCAQMD is responsible for bringing air quality in areas under its jurisdiction into conformity with federal and state air quality standards. As stated, the Project site is located within the SCAB, a 6,745-square-mile subregion of the SCAQMD, which includes portions of Los Angeles, Riverside, and San Bernardino Counties, and all of Orange County. The SCAB is bounded by the Paciﬁc Ocean to the west and the San Gabriel, San Bernardino, and San Jacinto Mountains to the north and east. The Los Angeles County portion of the Mojave Desert Air Basin is bounded by the San Gabriel Mountains to the south and west, the Los Angeles / Kern County border to the north, and the Los Angeles / San Bernardino County border to the east. The Riverside County portion of the Salton Sea Air Basin is bounded by the San Jacinto Mountains in the west and spans eastward up to the Palo Verde Valley. Regional Climate The regional climate has a substantial inﬂuence on air quality in the SCAB. In addition, the temperature, wind, humidity, precipitation, and amount of sunshine inﬂuence the air quality. The annual average temperatures throughout the SCAB vary from the low to mid 60s (degrees Fahrenheit [°F]). Due to a decreased marine inﬂuence, the eastern portion of the SCAB shows greater variability in average annual minimum and maximum temperatures. January is the coldest month throughout the SCAB, with average minimum temperatures of 47°F in downtown Los Angeles and 36°F in San Bernardino. All portions of the SCAB have recorded maximum temperatures above 100°F. Although the climate of the SCAB can be characterized as semi-arid, the air near the land surface is quite moist on most days because of the presence of a marine layer. This shallow layer of sea air is an important modiﬁer of SCAB climate. Humidity restricts visibility in the SCAB, and the conversion of sulfur dioxide (SO2) to sulfates (SO4) is heightened in air with high relative humidity. The marine layer provides an environment for that conversion process, especially during the spring and summer months. The annual average relative humidity within the SCAB is 71 percent (%) along the coast and 59% inland. Since the ocean eﬀect is dominant, periods of heavy early morning fog are frequent and low stratus clouds are a characteristic feature. These eﬀects decrease with distance from the coast. More than 90% of the SCAB’s rainfall occurs from November through April. The annual average rainfall varies from approximately nine inches in Riverside to fourteen inches in downtown Los Angeles. Monthly and yearly rainfall totals are extremely variable. Summer rainfall usually consists of widely scattered thunderstorms near the coast and slightly heavier shower activity in the eastern portion of the SCAB with frequency being higher near the coast. Due to its generally clear weather, about three-quarters of available sunshine is received in the SCAB. The remaining one-quarter is absorbed by clouds. The ultraviolet portion of this abundant radiation 16758-03 AQ & GHG Assessment 5 Almond Avenue Trailer Yard (MCN25-0059) is a key factor in photochemical reactions. On the shortest day of the year there are approximately 10 hours of possible sunshine, and on the longest day of the year there are approximately 14½ hours of possible sunshine. The importance of wind to air pollution is considerable. The direction and speed of the wind determines the horizontal dispersion and transport of the air pollutants. During the late autumn to early spring rainy season, the SCAB is subjected to wind ﬂows associated with the traveling storms moving through the region from the northwest. This period also brings ﬁve to ten periods of strong, dry oﬀshore winds, locally termed “Santa Anas” each year. During the dry season, which coincides with the months of maximum photochemical smog concentrations, the wind ﬂow is bimodal, typiﬁed by a daytime onshore sea breeze and a nighttime oﬀshore drainage wind. Summer wind ﬂows are created by the pressure diﬀerences between the relatively cold ocean and the unevenly heated and cooled land surfaces that modify the general northwesterly wind circulation over southern California. Nighttime drainage begins with the tradiational cooling of the mountain slopes. Heavy, cool air descends the slopes and ﬂows through the mountain passes and canyons as it follows the lowering terrain toward the ocean. Another characteristic wind regime in the SCAB is the “Catalina Eddy,” a low level cyclonic (counterclockwise) ﬂow centered over Santa Catalina Island which results in an oﬀshore ﬂow to the southwest. On most spring and summer days, some indication of an eddy is apparent in coastal sections. In the SCAB, there are two distinct temperature inversion structures that control vertical mixing of air pollution. During the summer, warm high-pressure descending (subsiding) air is undercut by a shallow layer of cool marine air. The boundary between these two layers of air is a persistent marine subsidence/inversion. This boundary prevents vertical mixing which eﬀectively acts as an impervious lid to pollutants over the entire SCAB. The mixing height for the inversion structure is normally situated 1,000 to 1,500 feet above mean sea level. A second inversion-type forms in conjunction with the drainage of cool air oﬀ the surrounding mountains at night followed by the seaward drift of this pool of cool air. The top of this layer forms a sharp boundary with the warmer air aloft and creates nocturnal radiation inversions. These inversions occur primarily in the winter when nights are longer and onshore ﬂow is weakest. They are typically only a few hundred feet above mean sea level. These inversions eﬀectively trap pollutants, such as nitrogen oxides (NOX) and carbon monoxide (CO) from vehicles, as the pool of cool air drifts seaward. Winter is therefore a period of high levels of primary pollutants along the coastline. Wind Patterns and Project Location The distinctive climate of the Project area and the SCAB is determined by its terrain and geographical location. The SCAB is located in a coastal plain with connecting broad valleys and low hills, bounded by the Paciﬁc Ocean in the southwest quadrant with high mountains forming the remainder of the perimeter. Wind patterns across the south coastal region are characterized by westerly and southwesterly onshore winds during the day and easterly or northeasterly breezes at night. Winds are characteristically light although the speed is somewhat greater during the dry summer months than during the rainy winter season. 16758-03 AQ & GHG Assessment 6 Almond Avenue Trailer Yard (MCN25-0059) Criteria Pollutants Both the U.S. Environmental Protection Agency (EPA) and the California Air Resources Board (CARB) have established ambient air quality standards for common pollutants. These ambient air quality standards are levels of contaminants representing safe levels that avoid speciﬁc adverse health eﬀects associated with each pollutant. The ambient air quality standards cover what are called “criteria” pollutants because the health and other eﬀects of each pollutant are described in criteria documents. The six criteria pollutants are ozone (O3) (precursor emissions include NOX and reactive organic gases (ROG), CO, particulate matter (PM), nitrogen dioxide (NO2), sulfur dioxide (SO2), and lead. Areas that meet ambient air quality standards are classiﬁed as attainment areas, while areas that do not meet these standards are classiﬁed as nonattainment areas. The Riverside County portion of the SCAB is designated as a nonattainment area for the federal O3 and PM2.5 standards and is also a nonattainment area for the state standards for O3, PM10, and PM2.5. Toxic Air Contaminants (TAC) Trend In 1984, as a result of public concern for exposure to airborne carcinogens, CARB adopted regulations to reduce the amount of TAC emissions resulting from mobile and area sources, such as cars, trucks, stationary products, and consumer products. According to the Ambient and Emission Trends of Toxic Air Contaminants in California journal article (2) which was prepared for CARB, results show that between 1990-2012, ambient concentration and emission trends for the seven TACs responsible for most of the known cancer risk associated with airborne exposure in California have declined signiﬁcantly (between 1990 and 2012). The seven TACs studied include those that are derived from mobile sources: diesel particulate matter (DPM), benzene (C6H6), and 1,3-butadiene (C4H6); those that are derived from stationary sources: perchloroethylene (C2Cl4) and hexavalent chromium (Cr(VI)); and those derived from photochemical reactions of emitted VOCs: formaldehyde (CH2O) and acetaldehyde (C2H4O).1 The decline in ambient concentration and emission trends of these TACs are a result of various regulations CARB has implemented to address cancer risk. REGULATORY BACKGROUND FEDERAL REGULATIONS The EPA is responsible for setting and enforcing the national ambient air quality standards (NAAQS) for O3, CO, NOX, SO2, PM10, and lead (Pb) (3). The EPA has jurisdiction over emissions sources that are under the authority of the federal government including aircraft, locomotives, and emissions sources outside state waters (Outer Continental Shelf). The EPA also establishes emission standards for vehicles sold in states other than California. Automobiles sold in California must meet the stricter emission requirements of CARB. The Federal Clean Air Act (CAA) was ﬁrst enacted in 1955 and has been amended numerous times in subsequent years (1963, 1965, 1967, 1970, 1977, and 1990). The CAA establishes the federal air quality standards, the NAAQS, and speciﬁes future dates for achieving compliance (4). The CAA also mandates that each state submit and implement state implementation plans (SIPs) for local areas 1 It should be noted that ambient DPM concentrations are not measured directly. Rather, a surrogate method using the coefficient of haze (COH) and elemental carbon (EC) is used to estimate DPM concentrations. 16758-03 AQ & GHG Assessment 7 Almond Avenue Trailer Yard (MCN25-0059) not meeting these standards. These plans must include pollution control measures that demonstrate how the standards will be met. The 1990 amendments to the CAA that identify speciﬁc emission reduction goals for areas not meeting the NAAQS require a demonstration of reasonable further progress toward attainment and incorporate additional sanctions for failure to attain or to meet interim milestones. The sections of the CAA most directly applicable to the development of the Project site include Title I (Non- Attainment Provisions) and Title II (Mobile Source Provisions) (5) (6). Title I provisions were established with the goal of attaining the NAAQS for the following criteria pollutants O3, NO2, SO2, PM10, CO, PM2.5, and Pb. The NAAQS were amended in July 1997 to include an additional standard for O3 and to adopt a NAAQS for PM2.5. Mobile source emissions are regulated in accordance with Title II provisions. These provisions require the use of cleaner burning gasoline and other cleaner burning fuels such as methanol and natural gas. Automobile manufacturers are also required to reduce tailpipe emissions of hydrocarbons and NOX. NOX is a collective term that includes all forms of NOX which are emitted as byproducts of the combustion process. CALIFORNIA REGULATIONS CARB The CARB, which became part of the California EPA (CalEPA) in 1991, is responsible for ensuring implementation of the California Clean Air Act (AB 2595), responding to the federal CAA, and for regulating emissions from consumer products and motor vehicles. AB 2595 mandates achievement of the maximum degree of emissions reductions possible from vehicular and other mobile sources in order to attain the state ambient air quality standards by the earliest practical date. The CARB established the California ambient air quality standards (CAAQS) for all pollutants for which the federal government has NAAQS and, in addition, establishes standards for SO4, visibility, hydrogen sulﬁde (H2S), and vinyl chloride (C2H3Cl). However, at this time, H2S and C2H3Cl are not measured at any monitoring stations in the SCAB because they are not considered to be a regional air quality problem. Generally, the CAAQS are more stringent than the NAAQS (7) (8). Local air quality management districts, such as the SCAQMD, regulate air emissions from stationary sources such as commercial and industrial facilities. All air pollution control districts have been formally designated as attainment or non-attainment for each CAAQS. Serious non-attainment areas are required to prepare Air Quality Management Plans (AQMP) that include speciﬁed emission reduction strategies in an eﬀort to meet clean air goals. These plans are required to include: • Application of Best Available Retrofit Control Technology to existing sources; • Developing control programs for area sources (e.g., architectural coatings and solvents) and indirect sources (e.g., motor vehicle use generated by residential and commercial development); • A District permitting system designed to allow no net increase in emissions from any new or modified permitted sources of emissions; • Implementing reasonably available transportation control measures and assuring a substantial reduction in growth rate of vehicle trips and miles traveled; • Significant use of low emissions vehicles by fleet operators; 16758-03 AQ & GHG Assessment 8 Almond Avenue Trailer Yard (MCN25-0059) • Sufficient control strategies to achieve a 5% or more annual reduction in emissions or 15% or more in a period of three years for ROGs, NOX, CO and PM10. However, air basins may use an alternative emission reduction strategy that achieves a reduction of less than 5% per year under certain circumstances. AQMP Currently, the NAAQS and CAAQS are exceeded in most parts of the SCAB. In response, the SCAQMD has adopted a series of AQMP to meet the state and federal ambient air quality standards (9). AQMPs are updated regularly in order to more eﬀectively reduce emissions, accommodate growth, and to minimize any negative ﬁscal impacts of air pollution control on the economy. APPLICABLE REGULATORY REQUIREMENTS SCAQMD Rules that are currently applicable during construction activity for this Project include but are not limited to Rule 403 (Fugitive Dust) and Rule 1113 (Architectural Coatings) (10) (11). SCAQMD RULE 403 This rule is intended to reduce the amount of particulate matter entrained in the ambient air as a result of anthropogenic (human-made) fugitive dust sources by requiring actions to prevent and reduce fugitive dust emissions. Rule 403 applies to any activity or human-made condition capable of generating fugitive dust and requires best available control measures to be applied to earth moving and grading activities. This rule is intended to reduce PM10 emissions from any transportation, handling, construction, or storage activity that has the potential to generate fugitive dust. PM10 suppression techniques are summarized below. • Portions of a construction site to remain inactive longer than a period of three months will be seeded and watered until grass cover is grown or otherwise stabilized. • All on-site roads will be paved as soon as feasible or watered periodically or chemically stabilized. • All material transported off-site will be either sufficiently watered or securely covered to prevent excessive amounts of dust. • The area disturbed by clearing, grading, earthmoving, or excavation operations will be minimized at all times. • Where vehicles leave a construction site and enter adjacent public streets, the streets will be swept daily or washed down at the end of the workday to remove soil tracked onto the paved surface. SCAQMD RULE 1113 This rule serves to limit the volatile organic compound (VOC) content of architectural coatings used on projects in the SCAQMD. Any person who supplies, sells, oﬀers for sale, or manufactures any architectural coating for use on projects in the SCAQMD must comply with the current VOC standards set in this rule. METHODOLOGY The California Air Pollution Control Oﬃcers Association (CAPCOA) in conjunction with other California air districts, including SCAQMD, released CalEEMod 2022 in May 2022. CalEEMod periodically releases updates, as such the latest version available at the time of this report has been 16758-03 AQ & GHG Assessment 9 Almond Avenue Trailer Yard (MCN25-0059) utilized in this analysis. The purpose of this model is to calculate construction-source and operational-source criteria pollutant (VOCs, NOX, SOX, CO, PM10, and PM2.5) and GHG emissions from direct and indirect sources; and quantify applicable air quality and GHG reductions achieved from mitigation measures (12). Accordingly, the latest version of CalEEMod has been used for this Project to determine construction and operational air quality and greenhouse gas emissions. STANDARDS OF SIGNIFICANCE The criteria used to determine the signiﬁcance of potential Project-related air quality impacts are taken from the California Environmental Quality Act Guidelines (CEQA Guidelines) (14 CCR §§15000, et seq.). Based on these thresholds, a project would result in a signiﬁcant impact related to air quality if it would (13): • Threshold 1: Conflict with or obstruct implementation of the applicable air quality plan. • Threshold 2: Result in a cumulatively considerable net increase of any criteria pollutant for which the project region is in non-attainment under an applicable federal or state ambient air quality standard. • Threshold 3: Expose sensitive receptors to substantial pollutant concentrations. • Threshold 4: Result in other emissions (such as those leading to odors) adversely affecting a substantial number of people. AIR QUALITY REGIONAL AND LOCALIZED EMISSIONS THRESHOLDS The SCAQMD has developed regional and localized signiﬁcance thresholds for criteria pollutants, as summarized at Tables 1 and 2 (14). The SCAQMD’s CEQA Air Quality Signiﬁcance Thresholds (March 2023) indicate that any projects in the SCAB with daily emissions that exceed any of the indicated thresholds should be considered as having an individually and cumulatively signiﬁcant air quality impact. TABLE 1: REGIONAL EMISSIONS SIGNIFICANCE THRESHOLDS Pollutant Construction Operations NOX 100 lbs/day 55 lbs/day VOC 75 lbs/day 55 lbs/day PM10 150 lbs/day 150 lbs/day PM2.5 55 lbs/day 55 lbs/day SOX 150 lbs/day 150 lbs/day CO 550 lbs/day 550 lbs/day Pb 3 lbs/day 3 lbs/day lbs/day = Pounds Per Day 16758-03 AQ & GHG Assessment 10 Almond Avenue Trailer Yard (MCN25-0059) TABLE 2: LOCALIZED EMISSIONS SIGNIFICANCE THRESHOLDS Pollutant Construction Operations NOX 0.18 ppm 0.18 ppm CO (1-hour average) 20 ppm 20 ppm CO (8-hour average) 9 ppm 9 ppm PM10 10.4 µg/m3 2.5 µg/m3 PM2.5 10.4 µg/m3 2.5 µg/m3 ppm = Parts Per Million µg/m3 = Micrograms Per Cubic Meter CONSTRUCTION ACTIVITIES Construction activities associated with the Project would result in emissions of VOCs, NOX, SOX, CO, PM10, and PM2.5. Construction related emissions are expected from the following construction activities: • Demolition • Site Preparation • Grading • Building Construction • Paving • Architectural Coating DEMOLITION ACTIVITIES The site is currently developed with existing uses/structures and asphalt/concrete which total approximately 100 tons. Demolished material associated with demolition will be hauled oﬀ-site. GRADING ACTIVITIES Dust is typically a major concern during grading activities. Because such emissions are not amenable to collection and discharge through a controlled source, they are called “fugitive emissions.” Fugitive dust emissions rates vary as a function of many parameters (soil silt, soil moisture, wind speed, area disturbed, number of vehicles, depth of disturbance or excavation, etc.). CalEEMod was utilized to calculate fugitive dust emissions resulting from this phase of activity. Based on consultation with the project team, the Project site has been designed to balance (will not require import/export of soil). ON-ROAD TRIPS Construction generates on-road vehicle emissions from vehicle usage for workers, vendors, and haul trucks commuting to and from the site. The number of worker and hauling trips per phase is presented below in Table 3. Worker and hauling trips are based on CalEEMod defaults. 16758-03 AQ & GHG Assessment 11 Almond Avenue Trailer Yard (MCN25-0059) TABLE 3: CONSTRUCTION TRIP ASSUMPTIONS Construction Activity Worker Trips Per Day Hauling Trips Per Day Demolition 15 1 Site Preparation 18 0 Grading 15 0 Building Construction 0 0 Paving 15 0 Architectural Coating 0 0 CONSTRUCTION DURATION For purposes of analysis, Project construction will begin in March 2027 and would last through March 2028. The construction schedule utilized in the analysis, as shown in Table 4, represents a “worst- case” analysis scenario should construction occur any time after the respective dates since emission factors for construction decrease as time passes and the analysis year increases due to emission regulations becoming more stringent2. The duration of construction activity and associated equipment represents a reasonable approximation of the expected construction ﬂeet as required per CEQA Guidelines (15). TABLE 4: CONSTRUCTION DURATION Construction Activity Start Date End Date Days Demolition 3/1/2027 3/26/2027 20 Site Preparation 3/29/2027 4/9/2027 10 Grading 4/12/2027 5/7/2027 20 Building Construction 5/10/2027 3/24/2028 230 Paving 2/28/2028 3/24/2028 20 Architectural Coating 2/28/2028 3/24/2028 20 CONSTRUCTION EQUIPMENT Equipment used for construction of the Project is shown in Table 5. CalEEMod default parameters for equipment has been used. Consistent with industry standards and typical construction practices, each piece of equipment will operate up to a total of eight (8) hours per day, or more than two-thirds of the period during which construction activities are allowed pursuant to the code. 2 As shown in the CalEEMod User’s Guide Version 2022, Appendix G “Table G-11. Statewide Average Annual Offroad Equipment Emission Factors” as the analysis year increases, emission factors for the same equipment pieces decrease due to the natural turnover of older equipment being replaced by newer less polluting equipment and new regulatory requirements. 16758-03 AQ & GHG Assessment 12 Almond Avenue Trailer Yard (MCN25-0059) TABLE 5: CONSTRUCTION EQUIPMENT Construction Activity Equipment1 Quantity Hours Demolition Rubber Tired Dozers 2 8 Excavators 3 8 Concrete/Industrial Saws 1 8 Site Preparation Rubber Tired Dozers 3 8 Crawler Tractors 4 8 Grading Graders 1 8 Excavators 1 8 Crawler Tractors 3 8 Rubber Tired Dozers 1 8 Building Construction Forklifts 3 8 Generator Sets 1 8 Cranes 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 1 In order to account for fugitive dust emissions, Crawler Tractors were used in lieu of Tractors/Loaders/Backhoes. REGIONAL CONSTRUCTION EMISSIONS SUMMARY The estimated maximum daily construction emissions without mitigation are summarized in Table 6. Detailed construction model outputs are presented in Appendix 1. Under the assumed scenarios, emissions resulting from the Project construction will not exceed thresholds established by the SCAQMD for emissions of any criteria pollutant and no mitigation is required. 16758-03 AQ & GHG Assessment 13 Almond Avenue Trailer Yard (MCN25-0059) TABLE 6: REGIONAL CONSTRUCTION EMISSIONS SUMMARY Year Emissions (lbs/day) ROG NOX CO SO2 PM10T PM2.5T Summer 2027 3.72 32.81 31.55 0.05 7.51 4.23 Winter 2027 3.71 32.81 31.26 0.05 7.51 4.23 2028 9.22 17.43 26.16 0.04 0.81 0.60 Maximum Daily Emissions 9.22 32.81 31.55 0.05 7.51 4.23 SCAQMD Regional Thresholds 75 100 550 150 150 55 Threshold Exceeded? NO NO NO NO NO NO 1 PM10 and PM2.5 source emissions reﬂect 3x daily watering per SCAQMD Rule 403 for fugitive dust. VOC source emissions reﬂect SCAQMD Rule 1113 for Architectural Coatings. REGIONAL OPERATIONAL EMISSIONS Operational activities associated with the Project would result in emissions of CO, VOCs, NOX, SOX, PM10, and PM2.5. Operational related emissions are expected from the following primary sources: area source emissions, mobile source emissions, stationary source emissions, and cargo handling equipment emissions. The Project related operational air quality emissions derived primarily from vehicle trips generated by the Project. Trip characteristics available from the Almond Avenue Trailer Yard (MCN25-0059) Trip Generation Assessment were utilized in this analysis (16). To determine emissions from trucks for the proposed industrial uses, the analysis incorporated the SCAQMD recommended truck trip length 15.3 miles for 2-axle (LHDT1, LHDT2) trucks, 14.2 miles 3- axle (MHDT) trucks and 39.9 miles for 4+-axle (HHDT) trucks and weighting the average trip lengths using the following SCAQMD recommended truck mix: 2-Axle = 16.7%; 3-Axle = 20.7%; 4+-Axle = 62.6%. The trip length function for trucks in CalEEMod has been revised to 27.33 miles, with an assumption of 100% primary trips for the proposed truck trailer lot land use. The estimated operation-source emissions from the Project are summarized in Table 7. Detailed operation model outputs are presented in Appendix 1. As shown in Table 7, operational-source emissions would not exceed the applicable SCAQMD regional thresholds for emissions of any criteria pollutant. 16758-03 AQ & GHG Assessment 14 Almond Avenue Trailer Yard (MCN25-0059) TABLE 7: TOTAL PROJECT REGIONAL OPERATIONAL EMISSIONS Source Emissions (lbs/day) ROG NOX CO SO2 PM10T PM2.5T Summer Mobile 0.81 12.17 13.44 0.13 6.09 1.74 Area 0.10 0.00 0.05 0.00 0.00 0.00 Maximum Daily Emissions 0.91 12.17 13.50 0.13 6.09 1.74 SCAQMD Regional Thresholds 55 55 550 150 150 55 Threshold Exceeded? NO NO NO NO NO NO Winter Mobile 0.78 12.73 12.25 0.13 6.09 1.74 Area 0.09 0.00 0.00 0.00 0.00 0.00 Maximum Daily Emissions 0.87 12.73 12.25 0.13 6.09 1.74 SCAQMD Regional Thresholds 55 55 550 150 150 55 Threshold Exceeded? NO NO NO NO NO NO LOCALIZED CONSTRUCTION EMISSIONS The analysis makes use of methodology included in the SCAQMD Final Localized Signiﬁcance Threshold Methodology (LST Methodology). The SCAQMD has established that impacts to air quality are signiﬁcant if there is a potential to contribute or cause localized exceedances of the federal and/or state ambient air quality standards (NAAQS/CAAQS). Collectively, these are referred to as Localized Signiﬁcance Thresholds (LSTs). The SCAQMD established LSTs in response to the SCAQMD Governing Board’s Environmental Justice Initiative I-4.3 LSTs represent the maximum emissions from a project that would not cause or contribute to an exceedance of the most stringent applicable federal or state ambient air quality standard at the nearest residence or sensitive receptor. The SCAQMD states that lead agencies can use the LSTs as another indicator of signiﬁcance in its air quality impact analyses. LSTs were developed in response to environmental justice and health concerns raised by the public regarding exposure of individuals to criteria pollutants in local communities. To address the issue of localized signiﬁcance, the SCAQMD adopted LSTs that show whether a project would cause or contribute to localized air quality impacts and thereby cause or contribute to potential localized adverse health eﬀects. The analysis makes use of methodology included in the LST Methodology (17). Emissions Considered Based on SCAQMD’s LST Methodology, emissions for concern during construction activities are on- site NOX, CO, PM2.5, and PM10. The LST Methodology clearly states that “oﬀ-site mobile emissions from the Project should not be included in the emissions compared to LSTs (18).” As such, for 3 The purpose of SCAQMD’s Environmental Justice program is to ensure that everyone has the right to equal protection from air pollution and fair access to the decision-making process that works to improve the quality of air within their communities. Further, the SCAQMD deﬁnes Environmental Justice as “…equitable environmental policymaking and enforcement to protect the health of all residents, regardless of age, culture, ethnicity, gender, race, socioeconomic status, or geographic location, from the health effects of air pollution.” 16758-03 AQ & GHG Assessment 15 Almond Avenue Trailer Yard (MCN25-0059) purposes of the construction LST analysis, only emissions included in the CalEEMod “on-site” emissions outputs were considered. Dispersion Modeling In order to estimate localized pollutant concentrations resulting from Project construction, the SCAQMD-approved American Meteorological Society/EPA Regulatory Model (AERMOD) dispersion model was utilized. The modeling approach utilized is discussed as follows. Sources It should be noted that in order to model worst-case conditions, the highest daily peak on-site emissions resulting from overlapping construction activity were modeled. A ground level release height and a 1 meter (approximately 3.28 feet) initial vertical dimension (sigma z) were utilized for fugitive dust emissions of PM10 and PM2.5 consistent with SCAQMD’s LST guidance. In order to account for equipment exhaust emissions from NO2, CO, PM10, and PM2.5 a release height of 5.0 meters was utilized consistent with SCAQMD’s LST guidance. Meteorological Data and Model Options In order to account for meteorological conditions at the Project site, meteorological data from the SCAQMD’s Fontana monitoring station was utilized, as this is the nearest station to the Project site for which meteorological data is available. Additionally, a receptor height of 2 meters and regulatory default options were utilized consistent with SCAQMD’s LST guidance. Receptors As previously stated, LSTs represent the maximum emissions from a project that would not cause or contribute to an exceedance of the most stringent applicable NAAQS and CAAQS at the nearest residence or sensitive receptor. Receptor locations are oﬀ-site locations where individuals may be exposed to emissions from Project activities. Some people are especially sensitive to air pollution and are given special consideration when evaluating air quality impacts from projects. These groups of people include children, the elderly, and individuals with pre-existing respiratory or cardiovascular illness. Structures that house these persons or places where they gather are deﬁned as “sensitive receptors”. These structures typically include uses such as residences, hotels, and hospitals where an individual can remain for 24 hours. Consistent with the LST Methodology, the nearest land use to the Project site where an individual could remain for 24 hours has been used to determine construction and operational air quality impacts for emissions of PM10 and PM2.5, since PM10 and PM2.5 thresholds are based on a 24-hour averaging time. Per the LST Methodology, commercial and industrial facilities are not included in the deﬁnition of sensitive receptor because employees and patrons do not typically remain onsite for a full 24 hours but are typically on-site for 8 hours or less. However, LST Methodology explicitly states that “LSTs based on shorter averaging periods, such as the NO2 and CO LSTs, could also be applied to receptors such as industrial or commercial facilities since it is reasonable to assume that a worker at these sites could be present for periods of one to eight hours (18).” Therefore, any adjacent land use where an individual could remain for 1 or 8 hours, that is located at a closer distance to the Project site than the receptor used for PM10 and PM2.5 analysis, must be considered to determine construction and operational LST air impacts for emissions of NO2 and CO since these pollutants have an averaging time of 1 and 8 hours. 16758-03 AQ & GHG Assessment 16 Almond Avenue Trailer Yard (MCN25-0059) Project-related Receptors Receptors in the Project study area are described below and shown in Exhibit 2. Localized air quality impacts were evaluated at sensitive receptor land uses nearest the Project site. All distances are measured from the Project site boundary to the outdoor living areas (e.g., backyards) or at the building façade, whichever is closer to the Project site. R1: Location R1 represents the Kaiser Park at 9550 Cherry Ave, approximately 2,107 feet north of the Project site. Receptor R1 is placed in the park area facing the Project site. R2: Location R2 represents the existing residence at 9933 Cherry Ave, approximately 1,400 feet east of the Project site. Receptor R2 is placed in the private outdoor living area (backyard) facing the Project site. R3: Location R3 represents the existing residence at 10141 Walmac Ave, approximately 907 feet south of the Project site. Receptor R3 is placed in the private outdoor living area (backyard) facing the Project site. R4: Location R4 represents the existing residence at 14037 Rosemary Dr., approximately 1,054 feet west of the Project site. Receptor R4 is placed in the private outdoor living area (backyard) facing the Project site. R5: Location R5 represents the Detail Center at 14226 Valley Blvd, adjacent south of the Project site. Receptor R5 is placed at the at the building façade, facing the Project site. R6: Location R6 represents the Live Oak Elementary School at 9522 Live Oak Ave., approximately 3,950 feet northeast of the Project site. Receptor R6 is placed in the soccer ﬁeld facing the Project site. The SCAQMD recommends that the nearest sensitive receptor be considered when determining a Project’s impact. The nearest land use where an individual could remain for 24 hours to the Project site has been used to determine localized construction and operational air quality impacts for emissions of PM10 and PM2.5 (since PM10 and PM2.5 thresholds are based on a 24-hour averaging time). As previously stated, and consistent with LST Methodology, the nearest industrial/commercial use to the Project site is used to determine construction and operational LST air impacts for emissions of NOX and CO as the averaging periods for these pollutants are shorter (8 hours or less) and it is reasonable to assume that an individual could be present at these sites for periods of one to 8 hours. 16758-03 AQ & GHG Assessment 17 Almond Avenue Trailer Yard (MCN25-0059) EXHIBIT 1: SITE PLAN 16758-03 AQ & GHG Assessment 18 Almond Avenue Trailer Yard (MCN25-0059) LOCALIZED CONSTRUCTION EMISSIONS Emissions during the peak construction activity will not exceed the SCAQMD’s localized signiﬁcance thresholds at the maximally exposed receptor location, as illustrated in Table 8. All other modeled locations in the study area would experience lower concentrations, resulting in a reduced impact. As such, the Project’s localized impacts during construction activity would be less than signiﬁcant. Outputs from the CalEEMod model runs for construction LSTs are provided in Appendix 1 and 3. TABLE 8: CONSTRUCTION LOCALIZED SIGNIFICANCE SUMMARY CONSTRUCTION Peak Construction CO NO2 PM10 PM2.5 Averaging Time 1-Hour 8-Hours 1-Hour 24-Hours 24-Hours Peak Day Localized Emissions 0.12 0.04 7.96E-02 0.58 0.33 Background Concentration A 1.6 1.1 0.080 Total Concentration 1.72 1.14 0.16 0.58 0.33 SCAQMD Localized Signiﬁcance Threshold 20 9 0.18 10.4 10.4 Threshold Exceeded? NO NO NO NO NO A Highest concentration from the last three years of available data. Notes: PM10 and PM2.5 concentrations are expressed in µg/m3. All others are expressed in ppm. Based on SCAQMD’s LST Methodology, background concentrations are considered only for CO and NO2. LOCALIZED OPERATIONAL EMISSIONS The LST analysis generally includes on-site sources (area, energy, mobile, and on-site cargo handling equipment). However, it should be noted that the CalEEMod outputs do not separate on-site and oﬀ-site emissions from mobile sources. As such, to establish a maximum potential impact scenario for analytic purposes, the modeled emissions include all on-site Project-related stationary (area) sources and on-site Project-related mobile emissions. In order to account for on-site mobile emissions, a trip length of 0.17 miles was utilized for both trucks and passenger cars. In order to account for any potential impacts to on-site receptors as a result of operational activity, a scenario conservatively assuming 2028 emissions was analyzed. Outputs from the model runs for operational LSTs are provided in Appendix 3. As shown in Table 9, emissions would not exceed SCAQMD’s localized signiﬁcance thresholds at the maximally exposed on-site receptors as a result of operational activities. 16758-03 AQ & GHG Assessment 19 Almond Avenue Trailer Yard (MCN25-0059) TABLE 9: OPERATIONAL LOCALIZED SIGNIFICANCE SUMMARY PEAK OPERATIONS Peak Operations CO NO2 PM10 PM2.5 Averaging Time 1-Hour 8-Hours 1-Hour 24-Hours 24-Hours Peak Day Localized Emissions 4.82E-03 2.43E-03 2.16E-03 0.01 0.00 Background Concentration 1.6 1.1 0.080 Total Concentration 1.60 1.10 0.08 0.01 0.00 SCAQMD Localized Signiﬁcance Threshold 20 9 0.18 2.5 2.5 Threshold Exceeded? NO NO NO NO NO A Highest concentration from the last three years of available data. Notes: PM10 and PM2.5 concentrations are expressed in µg/m3. All others are expressed in ppm. Based on SCAQMD’s LST Methodology, background concentrations are considered only for CO and NO2. AIR QUALITY IMPACTS – CONSISTENCY WITH THRESHOLD NO. 1 Would the Project conﬂict with or obstruct implementation of the applicable air quality plan? The Project site is located within the SCAB, which is characterized by relatively poor air quality. The SCAQMD has jurisdiction over an approximately 10,743 square-mile area consisting of the four- county Basin and the Los Angeles County and Riverside County portions of what used to be referred to as the Southeast Desert Air Basin. In these areas, the SCAQMD is principally responsible for air pollution control, and works directly with the Southern California Association of Governments (SCAG), county transportation commissions, local governments, as well as state and federal agencies to reduce emissions from stationary, mobile, and indirect sources to meet state and federal ambient air quality standards. Currently, these state and federal air quality standards are exceeded in most parts of the SCAB. In response, the SCAQMD has adopted a series of AQMPs to meet the state and federal ambient air quality standards. AQMPs are updated regularly in order to more eﬀectively reduce emissions, accommodate growth, and to minimize any negative ﬁscal impacts of air pollution control on the economy. In December 2022, the SCAQMD released the Final 2022 AQMP (2022 AQMP). The 2022 AQMP continues to evaluate current integrated strategies and control measures to meet the CAAQS, as well as explore new and innovative methods to reach its goals. Some of these approaches include utilizing incentive programs, recognizing existing co-beneﬁt programs from other sectors, and developing a strategy with fair-share reductions at the federal, state, and local levels (19). Similar to the 2016 AQMP, the 2022 AQMP incorporates scientiﬁc and technological information and planning assumptions, including the 2020-2045 RTP/SCS, a planning document that supports the integration of land use and transportation to help the region meet the federal CAA requirements (20). The Project’s consistency with the AQMP will be determined using the 2022 AQMP as discussed below. SCAG adopted the 2020-2045 Regional Transportation Plan/Sustainable Communities Strategy (2020- 2045 RTP/SCS), a planning document that supports the integration of land use and transportation to help the region meet the federal metropolitan planning organization (MPO) requirements under the Sustainable communities and Climate Protection Act. The proposed Project would be developed in accordance with all applicable rules and regulations contained in those plans. It should be noted 16758-03 AQ & GHG Assessment 20 Almond Avenue Trailer Yard (MCN25-0059) that although the 2024-2050 RTP was released after approval of the 2022 AQMP, the 2022 AQMP is reliant in part upon the general plan land use designations. Criteria for determining consistency with the AQMP are deﬁned in Chapter 12, Section 12.2 and Section 12.3 of the 1993 CEQA Handbook (21). These indicators are discussed below. The proposed Project will not result in an increase in the frequency or severity of existing air quality violations or cause or contribute to new violations or delay the timely attainment of air quality standards or the interim emissions reductions speciﬁed in the AQMP. The violations that under this criterion refer to are the CAAQS and NAAQS. CAAQS and NAAQS violations would occur if regional or localized signiﬁcance thresholds were exceeded. CAAQS and NAAQS violations would occur if regional or localized signiﬁcance thresholds were exceeded. As evaluated, the Project’s regional and localized construction and net operational-source emissions would not exceed applicable regional signiﬁcance thresholds. As such, a less than signiﬁcant impact is expected. On the basis of the preceding discussion, the Project is determined to be consistent with the ﬁrst criterion. The Project will not exceed the assumptions in the AQMP based on the years of Project build-out phase. The 2022 AQMP demonstrates that the applicable ambient air quality standards can be achieved within the timeframes required under federal law. Growth projections from local general plans adopted by cities in the district are provided to the SCAG, which develops regional growth forecasts, which are then used to develop future air quality forecasts for the AQMP. Development consistent with the growth projections in City of Fontana General Plan is considered to be consistent with the AQMP. Peak day emissions generated by construction activities are largely independent of land use assignments, but rather are a function of development scope and maximum area of disturbance. Irrespective of the site’s land use designation, development of the site to its maximum potential would likely occur, with disturbance of the entire site occurring during construction activities. As such, when considering that no emissions thresholds will be exceeded, a less than signiﬁcant impact would result. The City of Fontana General Plan designates the Project site within the Southwest Industrial Park Speciﬁc Plan (SWIP) speciﬁcally, the Project is located within the Speedway Industrial District (SID) of the SWIP. The Speedway Industrial District (SID) is intended to encourage uses that complement and support the Auto Club Speedway of Southern California. This district will provide opportunities for a mixture of uses, including service commercial, entertainment, small businesses, research and development, restaurants, and hospitality uses. Light manufacturing will be allowed in the district. General features of this District include: Auto-related uses, Entertainment-oriented uses, Speedway theme, Landscape/Streetscape Enhancement, Edge conditions that are compatible with surrounding uses, Establishment of uses that capitalize on regional market potential, Facade Improvements that enhance the I-10 Corridor, Promotion of lot consolidation (22). As previously stated, the Project is to consist of a 9.49-acre trailer yard with a 1,248 square foot pre- fabricated oﬃce building and 294 12-foot by 53-foot trailer stalls. 16758-03 AQ & GHG Assessment 21 Almond Avenue Trailer Yard (MCN25-0059) The Project is consistent with the current land use and zoning designation and would not require a General Plan and Zone Change Amendment. As such, the Project on an individual basis does not have an impact and as such, the proposed Project would not conﬂict with the goals and objectives of the AQMP. Furthermore, the Project, as evaluated herein would not exceed the regional or localized air quality signiﬁcance thresholds. On the basis of the preceding discussion, the Project is determined to be consistent with the AQMP and a less than signiﬁcant impact is expected. AIR QUALITY IMPACTS – CONSISTENCY WITH THRESHOLD NO. 2 Would the Project result in a cumulatively considerable net increase of any criteria pollutant for which the project region is in non-attainment under an applicable federal or state ambient air quality standard? The CAAQS designates the Project site as nonattainment for O3, PM10, and PM2.5 while the NAAQS designates the Project site as nonattainment for O3 and PM2.5. The SCAQMD 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 (23). In this report the SCAQMD clearly states (Page D-3): “…the SCAQMD 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 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 the 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.” Therefore, this analysis assumes that individual projects that do not generate operational or construction emissions that exceed the SCAQMD’s recommended daily thresholds for project- speciﬁc impacts would also not cause a cumulatively considerable increase in emissions for those pollutants for which SCAB is in nonattainment, and, therefore, would not be considered to have a signiﬁcant, adverse air quality impact. Alternatively, individual project-related construction and operational emissions that exceed SCAQMD thresholds for project-speciﬁc impacts would be considered cumulatively considerable. CONSTRUCTION IMPACTS The Project-speciﬁc evaluation of emissions presented in the preceding analysis demonstrates that proposed Project construction-source air pollutant emissions would not result in exceedances of 16758-03 AQ & GHG Assessment 22 Almond Avenue Trailer Yard (MCN25-0059) regional thresholds. Therefore, proposed Project construction-source emissions would be considered less than signiﬁcant on a project-speciﬁc and cumulative basis. OPERATIONAL IMPACTS The Project-speciﬁc evaluation of emissions presented in the preceding analysis demonstrates that proposed Project’s net operational-source air pollutant emissions would not result in exceedances of regional thresholds. Therefore, the proposed Project operational-source emissions would be considered less than signiﬁcant on a project-speciﬁc and cumulative basis. AIR QUALITY IMPACTS – CONSISTENCY WITH THRESHOLD NO. 3 Would they expose sensitive receptors to substantial pollutant concentrations? The potential impact of Project-generated air pollutant emissions at sensitive receptors has also been considered. Results of the LST analysis indicate that the Project will not exceed the SCAQMD localized signiﬁcance thresholds during construction. Therefore, sensitive receptors would not be exposed to substantial pollutant concentrations during Project construction. Additionally, the Project will not exceed the SCAQMD localized signiﬁcance thresholds during operational activity. Therefore, sensitive receptors would not be exposed to substantial pollutant concentrations as the result of Project operations. CO “HOT SPOT” ANALYSIS A CO hotspot is deﬁned as a localized concentration of carbon monoxide exceeding the state one- hour standard of 20 ppm or the eight-hour standard of 9 ppm. At the time the most recent CEQA Air Quality Handbook (1993) was published by SCAQMD, the air basin was designated as non- attainment, requiring projects to perform hotspot analyses to ensure they did not worsen the existing conditions. Over the last two decades, background CO concentrations have been signiﬁcantly reduced due to regulatory controls on tailpipe emissions, which have culminated in the air basin achieving attainment status for CO. The 2003 AQMP’s ﬁndings underscore that CO hotspots are highly unlikely due to the reduced background concentrations and the eﬀectiveness of California's air quality management strategies. The substantial reduction in CO levels from the vehicle ﬂeet and the state’s attainment status for CO further diminish the need for detailed microscale hotspot analyses, reinforcing that existing monitoring and regulatory frameworks adequately address potential air quality concerns. As summarized in the 2003 AQMP, even at one of the busiest intersections at that time, only 0.7 ppm of CO is attributable to vehicular traﬃc and the remaining 7.7 ppm were due to ambient background conditions. Within the Project vicinity, the background air quality 1-hour and 8-hour concentrations are well below the applicable AAQS. As such, Project-related traﬃc at any intersections within the air basin would not cause or contribute to a CO hotspot since the background concentrations are low and any contribution from project traﬃc would be negligible. The project would not signiﬁcantly contribute to the formation of a CO hotspot. AIR QUALITY IMPACTS – CONSISTENCY WITH THRESHOLD NO. 4 Would the Project result in other emissions (such as those leading to odors) adversely aﬀecting a substantial number of people? 16758-03 AQ & GHG Assessment 23 Almond Avenue Trailer Yard (MCN25-0059) The potential for the Project to generate objectionable odors has also been considered. Land uses generally associated with odor complaints include: • Agricultural uses (livestock and farming) • Wastewater treatment plants • Food processing plants • Chemical plants • Composting operations • Refineries • Landfills • Dairies • Fiberglass molding facilities The Project does not contain land uses typically associated with emitting objectionable odors. Potential odor sources associated with the proposed Project may result from construction equipment exhaust and the application of asphalt and architectural coatings during construction activities and the temporary storage of typical solid waste (refuse) associated with the proposed Project’s (long-term operational) uses. Standard construction requirements would minimize odor impacts from construction. The construction odor emissions would be temporary, short-term, and intermittent in nature and would cease upon completion of the respective phase of construction and is thus considered less than signiﬁcant. It is expected that Project-generated refuse would be stored in covered containers and removed at regular intervals in compliance with the solid waste regulations. The proposed Project would also be required to comply with SCAQMD Rule 402 to prevent occurrences of public nuisances. Therefore, odors associated with the proposed Project construction and operations would be less than signiﬁcant and no mitigation is required (24). PROJECT GHG ANALYSIS CLIMATE CHANGE SETTING Global climate change (GCC) is the change in average meteorological conditions on the earth with respect to temperature, precipitation, and storms. The majority of scientists believe that the climate shift taking place since the Industrial Revolution is occurring at a quicker rate and magnitude than in the past. Scientiﬁc evidence suggests that GCC is the result of increased concentrations of GHGs in the earth’s atmosphere, including carbon dioxide (CO2), methane (CH4), nitrous oxide (N2O), and ﬂuorinated gases. The majority of scientists believe that this increased rate of climate change is the result of GHGs resulting from human activity and industrialization over the past 200 years. An individual project like the proposed Project evaluated in this memo cannot generate enough GHG emissions to aﬀect a discernible change in global climate. However, the proposed Project may participate in the potential for GCC by its incremental contribution of GHGs combined with the cumulative increase of all other sources of GHGs, which when taken together constitute potential inﬂuences on GCC. Because these changes may have serious environmental consequences, this memo will evaluate the potential for the proposed Project to have a signiﬁcant eﬀect upon the environment as a result of its potential contribution to the greenhouse eﬀect. GCC refers to the change in average meteorological conditions on the earth with respect to temperature, wind patterns, precipitation and storms. Global temperatures are regulated by naturally occurring atmospheric gases such as water vapor, CO2, N2O, CH4, hydroﬂuorocarbons 16758-03 AQ & GHG Assessment 24 Almond Avenue Trailer Yard (MCN25-0059) (HFCs), perﬂuorocarbons (PFCs), and sulfur hexaﬂuoride (SF6). These particular gases are important due to their residence time (duration they stay) in the atmosphere, which ranges from 10 years to more than 100 years. These gases allow solar radiation into the earth’s atmosphere, but prevent radiative heat from escaping, thus warming the earth’s atmosphere. GCC can occur naturally as it has in the past with the previous ice ages. Gases that trap heat in the atmosphere are often referred to as GHGs. GHGs are released into the atmosphere by both natural and anthropogenic activity. Without the natural GHG eﬀect, the earth’s average temperature would be approximately 61 degrees Fahrenheit (°F) cooler than it is currently. The cumulative accumulation of these gases in the earth’s atmosphere is considered to be the cause for the observed increase in the earth’s temperature. For the purposes of this analysis, emissions of CO2, CH4, and N2O were evaluated because these gases are the primary contributors to GCC from development projects. Although there are other substances such as ﬂuorinated gases that also contribute to GCC, these ﬂuorinated gases were not evaluated as their sources are not well-deﬁned and do not contain accepted emissions factors or methodology to accurately calculate these gases. REGULATORY SETTING Executive Order S-3-05 Former California Governor Arnold Schwarzenegger announced on June 1, 2005, through Executive Order S-3-05, the following reduction targets for GHG emissions: • By 2010, reduce GHG emissions to 2000 levels. • By 2020, reduce GHG emissions to 1990 levels. • By 2050, reduce GHG emissions to 80% below 1990 levels. The 2050 reduction goal represents what some scientists believe is necessary to reach levels that will stabilize the climate. The 2020 goal was established to be a mid-term target. Because this is an executive order, the goals are not legally enforceable for local governments or the private sector. Assembly Bill (AB) 32 The California State Legislature enacted AB 32, which requires that GHGs emitted in California be reduced to 1990 levels by the year 2020. “GHGs” as deﬁned under AB 32 include CO2, CH4, N2O, hydroﬂuorocarbons (HFCs), perﬂuorocarbons (PFCs), and sulfur hexaﬂuoride (SF6). Since AB 32 was enacted, a seventh chemical, nitrogen triﬂuoride, has also been added to the list of GHGs. CARB is the state agency charged with monitoring and regulating sources of GHGs. Pursuant to AB 32, CARB adopted regulations to achieve the maximum technologically feasible and cost-eﬀective GHG emission reductions. AB 32 states the following: “Global warming poses a serious threat to the economic well-being, public health, natural resources, and the environment of California. The potential adverse impacts of global warming include the exacerbation of air quality problems, a reduction in the quality and supply of water to the state from the Sierra snowpack, a rise in sea levels resulting in the displacement of thousands of coastal businesses and residences, damage to marine ecosystems and the natural environment, and an increase in the incidences of infectious diseases, asthma, and other human health-related problems.” 16758-03 AQ & GHG Assessment 25 Almond Avenue Trailer Yard (MCN25-0059) CARB approved the 1990 GHG emissions level of 427 million metric tons of CO2 equivalent per year (MMTCO2e) on December 6, 2007 (25). Therefore, emissions generated in California in 2020 are required to be equal to or less than 427 MMTCO2e. Emissions in 2020 in a “business as usual” (BAU) scenario were estimated to be 596 MMTCO2e, which do not account for reductions from AB 32 regulations (26). At that level, a 28.4% reduction was required to achieve the 427 MMTCO2e 1990 inventory. In October 2010, CARB prepared an updated BAU 2020 forecast to account for the recession and slower forecasted growth. The forecasted inventory without the beneﬁts of adopted regulation is now estimated at 545 MMTCO2e. Therefore, under the updated forecast, a 21.7% reduction from BAU is required to achieve 1990 levels (27). Progress in Achieving AB 32 Targets and Remaining Reductions Required The State has made steady progress in implementing AB 32 and achieving targets included in Executive Order S-3-05. The progress is shown in updated emission inventories prepared by CARB for 2000 through 2012 (28). The State has achieved the Executive Order S-3-05 target for 2010 of reducing GHG emissions to 2000 levels. As shown below, the 2010 emission inventory achieved this target. • 1990: 427 MMTCO2e (AB 32 2020 target) • 2000: 463 MMTCO2e (an average 8% reduction needed to achieve 1990 base) • 2010: 450 MMTCO2e (an average 5% reduction needed to achieve 1990 base) CARB has also made substantial progress in achieving its goal of achieving 1990 emissions levels by 2020. As described earlier in this section, CARB revised the 2020 BAU inventory forecast to account for new lower growth projections, which resulted in a new lower reduction from BAU to achieve the 1990 base. The previous reduction from 2020 BAU needed to achieve 1990 levels was 28.4% and the latest reduction from 2020 BAU is 21.7%. • 2020: 545 MMTCO2e BAU (an average 21.7% reduction from BAU needed to achieve 1990 base) Senate Bill (SB) 32 On September 8, 2016, Governor Jerry Brown signed SB 32 and its companion bill, AB 197. SB 32 requires the state to reduce statewide GHG emissions to 40% below 1990 levels by 2030, a reduction target that was ﬁrst introduced in Executive Order B-30-15. The new legislation builds upon the AB 32 goal of 1990 levels by 2020 and provides an intermediate goal to achieving S-3-05, which sets a statewide GHG reduction target of 80% below 1990 levels by 2050. AB 197 creates a legislative committee to oversee regulators to ensure that CARB not only responds to the Governor, but also the Legislature (29). AB 197 A condition of approval for SB 32 was the passage of AB 197. AB 197 requires that CARB consider the social costs of GHG emissions and prioritize direct reductions in GHG emissions at mobile sources and large stationary sources. AB 197 also gives the California legislature more oversight over CARB through the addition of two legislatively appointed members to the CARB Board and the establishment of a legislative committee to make recommendations about CARB programs to the legislature. 16758-03 AQ & GHG Assessment 26 Almond Avenue Trailer Yard (MCN25-0059) Executive Order B-55-18 and SB 100 Executive Order B-55-18 and SB 100. SB 100 and Executive Order B-55-18 were signed by Governor Brown on September 10, 2018. Under the existing RPS, 25% of retail sales are required to be from renewable sources by December 31, 2016, 33% by December 31, 2020, 40% by December 31, 2024, 45% by December 31, 2027, and 50% by December 31, 2030. SB 100 raises California’s RPS requirement to 50% renewable resources target by December 31, 2026, and to achieve a 60% target by December 31, 2030. SB 100 also requires that retail sellers and local publicly owned electric utilities procure a minimum quantity of electricity products from eligible renewable energy resources so that the total kilowatt hours of those products sold to their retail end-use customers achieve 44% of retail sales by December 31, 2024, 52% by December 31, 2027, and 60% by December 31, 2030. In addition to targets under AB 32 and SB 32, Executive Order B-55-18 establishes a carbon neutrality goal for the state of California by 2045; and sets a goal to maintain net negative emissions thereafter. The Executive Order directs the California Natural Resources Agency (CNRA), California Environmental Protection Agency (CalEPA), the Department of Food and Agriculture (CDFA), and CARB to include sequestration targets in the Natural and Working Lands Climate Change Implementation Plan consistent with the carbon neutrality goal. Title 24 California Code of Regulations (CCR) California Code of Regulations (CCR) Title 24 Part 6: The California Energy Code was ﬁrst adopted in 1978 in response to a legislative mandate to reduce California’s energy consumption. The standards are updated periodically to allow consideration and possible incorporation of new energy eﬃcient technologies and methods. CCR, Title 24, Part 11: California Green Building Standards Code (CALGreen) is a comprehensive and uniform regulatory code for all residential, industrial, commercial, and school buildings that went in eﬀect on August 1, 2009, and is administered by the California Building Standards Commission. CALGreen is updated on a regular basis, with the most recent approved update consisting of the 2022 California Green Building Code Standards that became eﬀective on January 1, 2023 4. As construction of the Project is anticipated to be completed in 2027, the Project would be required to comply with the Title 24 standards in place at that time. SCAQMD SCAQMD is the agency responsible for air quality planning and regulation in the SCAB. The SCAQMD addresses the impacts to climate change of projects subject to SCAQMD permit as a lead agency if they are the only agency having discretionary approval for the project and acts as a responsible agency when a land use agency must also approve discretionary permits for the project. The SCAQMD acts as an expert commenting agency for impacts to air quality. This expertise carries over to GHG emissions, so the agency helps local land use agencies through the development of models and emission thresholds that can be used to address GHG emissions. 4 The 2022 California Green Building Standard Code became effective on January 1, 2023, however; it has since been amended on July 1, 2024 with the Intervening Code Cycle Update which is reﬂected in this report. Additionally, it should be noted that CALGreen is currently being updated, with the most recent draft update consisting of the 2025 California Green Building Code Standards that will be effective on January 1, 2025. As construction of the Project is anticipated to be completed in 2027, it is presumed that the Project would be required to comply with the Title 24 standards in place at that time. 16758-03 AQ & GHG Assessment 27 Almond Avenue Trailer Yard (MCN25-0059) In 2008, SCAQMD formed a Working Group to identify GHG emissions thresholds for land use projects that could be used by local lead agencies in the SCAB. The Working Group developed several diﬀerent options that are contained in the SCAQMD Draft Guidance Document – Interim CEQA GHG Signiﬁcance Threshold, that could be applied by lead agencies. The working group has not provided additional guidance since the release of the interim guidance in 2008. The SCAQMD Board has not approved the thresholds; however, the Guidance Document provides substantial evidence supporting the approaches to signiﬁcance of GHG emissions that can be considered by the lead agency in adopting its own threshold. The current interim thresholds consist of the following tiered approach: • Tier 1 consists of evaluating whether or not the project qualifies for any applicable exemption under CEQA. • Tier 2 consists of determining whether the project is consistent with a GHG reduction plan. If a project is consistent with a qualifying local GHG reduction plan, it does not have significant GHG emissions. • Tier 3 consists of screening values, which the lead agency can choose, but must be consistent with all projects within its jurisdiction. A project’s construction emissions are averaged over 30 years and are added to the project’s operational emissions. If a project’s emissions are below one of the following screening thresholds, then the project is less than significant: o Residential and commercial land use: 3,000 metric ton of CO2 equivalent (MTCO2e/yr) o Industrial land use: 10,000 MTCO2e/yr o Based on land use type: residential: 3,500 MTCO2e/yr; commercial: 1,400 MTCO2e/yr; or mixed use: 3,000 MTCO2e/yr • Tier 4 has the following options: o Option 1: Reduce Business-as-Usual (BAU) emissions by a certain percentage; this percentage is currently undeﬁned. o Option 2: Early implementation of applicable AB 32 Scoping Plan measures o Option 3: 2020 target for service populations (SP), which includes residents and employees: 4.8 MTCO2e per SP per year for projects and 6.6 MTCO2e per SP per year for plans; o Option 3, 2035 target: 3.0 MTCO2e per SP per year for projects and 4.1 MTCO2e per SP per year for plans • Tier 5 involves mitigation offsets to achieve target significance threshold. The SCAQMD’s interim thresholds used the Executive Order S-3-05-year 2050 goal as the basis for the Tier 3 screening level. Achieving the Executive Order’s objective would contribute to worldwide eﬀorts to cap CO2 concentrations at 450 ppm, thus stabilizing global climate. SCAQMD only has authority over GHG emissions from development projects that include air quality permits. At this time, it is unknown if the project would include stationary sources of emissions subject to SCAQMD permits. Notwithstanding, if the Project requires a stationary permit, it would be subject to the applicable SCAQMD regulations. SCAQMD Regulation XXVII, adopted in 2009 includes the following rules: • Rule 2700 defines terms and post global warming potentials. 16758-03 AQ & GHG Assessment 28 Almond Avenue Trailer Yard (MCN25-0059) • Rule 2701, Southern California (SoCal) Climate Solutions Exchange, establishes a voluntary program to encourage, quantify, and certify voluntary, high quality certified GHG emission reductions in the SCAQMD. • Rule 2702, GHG Reduction Program created a program to produce GHG emission reductions within the SCAQMD. The SCAQMD will fund projects through contracts in response to requests for proposals or purchase reductions from other parties. SCAQMD is the agency responsible for air quality planning and regulation in the SCAB. The SCAQMD addresses the impacts to climate change of projects subject to SCAQMD permit as a lead agency if they are the only agency having discretionary approval for the project and acts as a responsible agency when a land use agency must also approve discretionary permits for the project. The SCAQMD acts as an expert commenting agency for impacts to air quality. This expertise carries over to GHG emissions, so the agency helps local land use agencies through the development of models and emission thresholds that can be used to address GHG emissions. GHG IMPACTS STANDARDS OF SIGNIFICANCE According to the CEQA Guidelines Appendix G thresholds, to determine whether impacts from GHG emissions are signiﬁcant. Would the project: • Threshold 1: Generate GHG emissions, either directly or indirectly, that may have a significant impact on the environment? • Threshold 2: Conflict with an applicable plan, policy or regulation adopted for the purpose of reducing the emissions of GHGs? The evaluation of an impact under CEQA requires measuring data from a project against both existing conditions and a “threshold of signiﬁcance.” For establishing signiﬁcance thresholds, the Oﬃce of Planning and Research’s amendments to the CEQA Guidelines Section 15064.7(c) state “[w]hen adopting thresholds of signiﬁcance, a lead agency may consider thresholds of signiﬁcance previously adopted or recommended by other public agencies, or recommended by experts, provided the decision of the lead agency to adopt such thresholds is supported by substantial evidence.” CEQA Guidelines Section 15064.4(a) further states, “. . . A lead agency shall have discretion to determine, in the context of a particular project, whether to: (1) Use a model or methodology to quantify greenhouse gas emissions resulting from a project, and which model or methodology to use . . .; or (2) Rely on a qualitative analysis or performance-based standards.” CEQA Guidelines Section 15064.4 provides that a lead agency should consider the following factors, among others, in assessing the signiﬁcance of impacts from greenhouse gas emissions: • Consideration #1: The extent to which the project may increase or reduce greenhouse gas emissions as compared to the existing environmental setting. • Consideration #2: Whether the project emissions exceed a threshold of significance that the lead agency determines applies to the project. • Consideration #3: The extent to which the project complies with regulations or requirements adopted to implement a statewide, regional, or local plan for the reduction or mitigation of greenhouse gas emissions. Such regulations or requirements must be adopted by the relevant 16758-03 AQ & GHG Assessment 29 Almond Avenue Trailer Yard (MCN25-0059) public agency through a public review process and must reduce or mitigate the project’s incremental contribution of greenhouse gas emissions. In determining the significance of impacts, the lead agency may consider a project’s consistency with the State’s long-term climate goals or strategies, provided that substantial evidence supports the agency’s analysis of how those goals or strategies address the project’s incremental contribution to climate change and its conclusion that the project’s incremental contribution is not cumulatively considerable. DISCUSSION ON ESTABLISHMENT OF SIGNIFICANCE THRESHOLDS The City of Fontana has determined the development size that would be too small to be able to provide GHG emission reductions. To do this the City determined the GHG emissions allowed by a project such that 90 percent of the emissions on average from all projects would exceed that level and be “captured” and exceed this level and require further mitigation. A 90 percent emission capture rate means that 90 percent of total emissions from all projects would be subject to a CEQA analysis, including a negative declaration, a mitigated negative declaration, or an environmental impact report, which includes analyzing feasible alternatives and imposing feasible mitigation measures. A GHG significance threshold based on a 90 percent emission capture rate may be more appropriate to address the long-term adverse impacts associated with global climate change because most projects will be required to implement GHG reduction measures. Further, a 90 percent emission capture rate sets the emission threshold low enough to capture a substantial fraction of future stationary source projects that will be constructed to accommodate future statewide population and economic growth, while setting the emission threshold high enough to exclude small projects that will in aggregate contribute a relatively small fraction of the cumulative statewide GHG emissions. In determining this level of emissions, data available from SCAQMD was utilized. SCAQMD used a database of projects kept by the Governor’s Office of Planning and Research (OPR). That database contained 798 projects, 60 of which were extremely large General Plan Updates, Master Plans, or Specific Plan Projects. The 60 very large projects were removed from the database in order not to skew the emissions value, leaving a net of 738 projects. In addition, 27 projects were found to be outliers that would skew the emission value too high, leaving 711 as the sample population to use in determining the 90th percentile capture rate. The SCAQMD analysis of the 711 projects within the sample population combined commercial, residential, and mixed-use projects. It should be noted that the sample of projects included warehouses and other light industrial land uses but did not include industrial processes (i.e., oil refineries, heavy manufacturing, electric generating stations, mining operations, etc.). Emissions from each of these projects were calculated by SCAQMD to provide a consistent method of emissions calculations across the sample population and from projects within the sample population, construction period GHG emissions were amortized over 30 years (the average economic life of a development project). further reduce potential errors in the statistical analysis. In calculating the emissions The SCAQMD analysis determined that the 90th percentile ranged from 2,983 to 3,143 MT CO2e per year. Therefore, a 3,000 MT CO2e per year value is the low-end value within that range rounded to the nearest hundred tons of emissions and is used in defining small projects that are considered less than significant and do not need to provide further analysis. 16758-03 AQ & GHG Assessment 30 Almond Avenue Trailer Yard (MCN25-0059) Lastly, we understand that the 3,000 MT CO2e per year threshold for residential/commercial uses was proposed a decade ago and was never adopted. However, the 3,000 MT CO2e per year threshold was developed and recommended by SCAQMD, an expert agency, based on substantial evidence as provided in the Draft Guidance Document – Interim CEQA Greenhouse Gas Significance Threshold (2008) document and subsequent Working Group meetings (latest in 2010). This threshold uses the Executive Order S-3-05 goal as the basis, so it is not tied to only the 2020 target year and is thus not outdated. This threshold is also based on the 90% capture rate methodology, which means that 90% of total emissions from all new or modified projects would be subject to some type of CEQA analysis, which was the approach taken by SCAQMD to establish the stationary/industrial source threshold, as well as by the California Air Resources Board (for interim threshold for stationary source projects) and one of the options suggested by the California Air Pollution Control Officers Association (quantitative threshold based on market capture). Further, this threshold has been used for hundreds, if not thousands of GHG analyses performed for projects located within the SCAQMD jurisdiction. Thus, for purposes of analysis in this analysis, if Project-related GHG emissions do not exceed the 3,000 MTCO2e/yr threshold, then Project-related GHG emissions would clearly have a less-than- signiﬁcant impact pursuant to Threshold GHG-1. On the other hand, if Project-related GHG emissions exceed 3,000 MTCO2e/yr, the Project would be considered a substantial source of GHG emissions. GHG IMPACTS – CONSISTENCY WITH THRESHOLD NO. 1 Would the Project have the potential to generate direct or indirect GHG emissions that would result in a signiﬁcant impact on the environment? Project GHG Emissions The estimated GHG emissions for the Project land use are summarized in Table 10. The estimated GHG emission includes emissions from CO2, CH4, N2O, and Refrigerants (R). As shown in Table 10, the Project would generate a total of approximately 2,002.77 MTCO2e/yr. Detailed operation model outputs for the proposed Project are presented in Appendix 1. TABLE 10: TOTAL PROJECT GHG EMISSIONS Source Emissions (MT/yr) CO2T CH4 N2O R Total CO2e Annual construction emissions amortized over 30 years 12.69 5.11E-04 1.16E-04 3.57E-04 12.74 Mobile 1,850.12 0.11 0.25 2.21 1,928.65 Area 0.03 0.00 0.00 0.00 0.03 Energy 60.11 0.01 0.00 0.00 60.46 Water 0.31 0.01 0.00 0.00 0.54 Waste 0.10 0.01 0.00 0.00 0.36 Total CO2e (All Sources) 2,002.77 A numerical threshold for determining the signiﬁcance of GHG emissions in the SCAB has not been established by the SCAQMD for Projects where it is not the lead agency. As an interim threshold 16758-03 AQ & GHG Assessment 31 Almond Avenue Trailer Yard (MCN25-0059) based on guidance provided in the CAPCOA CEQA and Climate Change handbook, the City has opted to use a non-zero threshold approach based on Approach 2 of the handbook. Threshold 2.5 (Unit-Based Thresholds Based on Market Capture) establishes a numerical threshold based on capture of approximately 90% of emissions from future development. The latest threshold developed by SCAQMD using this method is 3,000 MTCO2e/yr for all projects (30). The Project would result in approximately 2,002.77 MTCO2e/yr; the proposed Project would not exceed the SCAQMD’s numeric threshold of 3,000 MTCO2e/yr. Thus, the Project would result in a less than signiﬁcant impact with respect to GHG emissions. GHG IMPACTS – CONSISTENCY WITH THRESHOLD NO. 2 Would the Project have the potential to conﬂict with any applicable plan, policy or regulation of an agency adopted for the purpose of reducing the emissions of GHGs? Pursuant to 15604.4 of the CEQA Guidelines, a lead agency may rely on qualitative analysis or performance-based standards to determine the signiﬁcance of impacts from GHG emissions (31). The 2022 Scoping Plan for Achieving Carbon Neutrality (2022 Scoping Plan) lays out a path to achieve targets for carbon neutrality and reduce anthropogenic greenhouse gas (GHG) emissions by 85 percent below 1990 levels no later than 2045, as directed by Assembly Bill 1279. The actions and outcomes in the plan will achieve signiﬁcant reductions in fossil fuel combustion by deploying clean technologies and fuels, further reductions in short-lived climate pollutants, support for sustainable development, increased action on natural and working lands to reduce emissions and sequester carbon, and the capture and storage of carbon (32). Finally, the Project is consistent with the general plan land use designation, density, building intensity, and applicable policies speciﬁed for the Project area in SCAG's Sustainable Community Strategy/Regional Transportation Plan, which pursuant to SB 375 calls for the integration of transportation, land-use and housing policies to plan for achievement of the GHG-emissions target for the region. Thus, a less than signiﬁcant impact related to GHG emissions from Project construction and operation would occur and no mitigation is required. CONCLUSION In summary, results of the assessment indicate that the Project would result in a less than signiﬁcant impact with respect to air quality and greenhouse gases. If you have any questions, please contact me directly at hqureshi@urbanxroads.com. 16758-03 AQ & GHG Assessment 32 Almond Avenue Trailer Yard (MCN25-0059) REFERENCES 1. South Coast Air Quality Management District. Southern California Air Basins. [Online] https://www.arb.ca.gov/msprog/onroad/porttruck/maps/scabc7map.pdf. 2. Ralph Propper, Patrick Wong, Son Bui, Jeff Austin, William Vance, Alvaro Alvarado, Bart Croes, and Dongmin Luo. Ambient and Emission Trends of Toxic Air Contaminants in California. American Chemical Society: Environmental Science & Technology. 2015. 3. United States Environmental Protection Agency. National Ambient Air Quality Standards (NAAQS). [Online] 1990. https://www.epa.gov/environmental-topics/air-topics. 4. Environmental Protection Agency. Air Pollution and the Clean Air Act. [Online] http://www.epa.gov/air/caa/. 5. 1990 Clean Air Act Amendment Summary: Title I. [Online] https://www.epa.gov/clean-air- act-overview/1990-clean-air-act-amendment-summary-title-i. 6. United States Environmental Protection Agency. 1990 Clean Air Act Amendment Summary: Title II. [Online] https://www.epa.gov/clean-air-act-overview/1990-clean-air-act- amendment-summary-title-ii. 7. Air Resources Board. California Ambient Air Quality Standards (CAAQS). [Online] 2009. [Cited: April 16, 2018.] http://www.arb.ca.gov/research/aaqs/caaqs/caaqs.htm. 8. Environmental Protection Agency. National Ambient Air Quality Standards (NAAQS). [Online] 1990. https://www.epa.gov/environmental-topics/air-topics. 9. Southern California Association of Governments. 2016-2040 Regional Transportation Plan/Sustainable Communities Strategy. [Online] April 2016. http://scagrtpscs.net/Documents/2016/final/f2016RTPSCS.pdf. 10. South Coast Air Quality Management District. RULE 403. FUGITIVE DUST. [Online] https://www.aqmd.gov/docs/default-source/rule-book/rule-iv/rule-403.pdf?sfvrsn=4. 11. —. RULE 1113. Architectural Coatings. [Online] http://www.aqmd.gov/docs/default- source/rule-book/reg-xi/r1113.pdf. 12. California Air Pollution Control Officers Association (CAPCOA). California Emissions Estimator Model (CalEEMod). [Online] May 2022. www.caleemod.com. 13. State of California. 2020 CEQA California Environmental Quality Act. 2020. 14. South Coast Air Quality Management District (SCAQMD). SCAQMD Air Quality Significance Thresholds. [Online] https://www.aqmd.gov/docs/default- source/ceqa/handbook/south-coast-aqmd-air-quality-significance-thresholds.pdf. 15. State of California. 2020 CEQA California Environmental Quality Act. 2020. 16. Urban Crossroads, Inc. Almond Avenue Trailer Yard (MCN25-0059) Trip Generation Assessment. 2025. 17. Lake Environmental. US EPA Models. Lake Environmental. [Online] http://www.weblakes.com/download/us_epa.html. 16758-03 AQ & GHG Assessment 33 Almond Avenue Trailer Yard (MCN25-0059) 18. South Coast Air Quality Management District. Localized Significance Thresholds Methodology. s.l. : South Coast Air Quality Managment District, 2008. 19. —. Final 2016 Air Quality Management Plan (AQMP). [Online] March 2017. http://www.aqmd.gov/docs/default-source/clean-air-plans/air-quality-management- plans/2016-air-quality-management-plan/final-2016- aqmp/final2016aqmp.pdf?sfvrsn=11. 20. Southern California Association of Governments. 2020-2045 Regional Transportation Plan/Sustainable Communities Strategy. [Online] September 2020. https://scag.ca.gov/sites/main/files/file-attachments/0903fconnectsocal- plan_0.pdf?1606001176. 21. South Coast Air Quality Management District. CEQA Air Quality Handbook (1993). 1993. 22. City of Fontana. City of Fontana Southwest Industrial Park Specific Plan. [Online] 2012. https://www.fontanaca.gov/DocumentCenter/View/29312/Southwest-Industrial- Specific-Plan---Combined-Document. 23. 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. http://www.aqmd.gov/rules/ciwg/final_white_paper.pdf. 24. South Coast Air Quality Management District. RULE 402 NUISANCE. [Online] http://www.aqmd.gov/docs/default-source/rule-book/rule-iv/rule-402.pdf. 25. California Air Resources Board. GHG 1990 Emissions Level & 2020 Limit. California Air Resources Board. [Online] https://ww2.arb.ca.gov/ghg-2020-limit. 26. —. Climate Change Draft Scoping Plan. 2008. 27. —. STATUS OF SCOPING PLAN RECOMMENDED MEASURES. [Online] [Cited: September 19, 2019.] https://ww3.arb.ca.gov/cc/scopingplan/status_of_scoping_plan_measures.pdf. 28. —. First Update to the Climate Change Scoping Plan. 2014. 29. California Legislative Information. Senate Bill No. 32. [Online] September 8, 2016. https://leginfo.legislature.ca.gov/faces/billNavClient.xhtml?bill_id=201520160SB32. 30. South Coast Air Quality Management District. Interim CEQA GHG Threshold for Stationary Sources, Rules and Plans. [Online] December 5, 2008. http://www.aqmd.gov/docs/default-source/ceqa/handbook/greenhouse-gases-(ghg)- ceqa-significance-thresholds/ghgboardsynopsis.pdf. 31. Association of Environmental Professionals. 2018 CEQA California Environmental Quality Act. 2018. 32. California Air Resources Board. 2022 Scopuing Plan Documents. [Online] https://ww2.arb.ca.gov/our-work/programs/ab-32-climate-change-scoping- plan/2022-scoping-plan-documents. 16758-03 AQ & GHG Assessment 34 Almond Avenue Trailer Yard (MCN25-0059) APPENDIX 1: CALEEMOD PROPOSED PROJECT EMISSIONS MODEL OUTPUTS 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 1 / 49 16758 - Fontana Trailer Yard Detailed Report Table of Contents 1. Basic Project Information 1.1. Basic Project Information 1.2. Land Use Types 1.3. User-Selected Emission Reduction Measures by Emissions Sector 2. Emissions Summary 2.1. Construction Emissions Compared Against Thresholds 2.2. Construction Emissions by Year, Unmitigated 2.4. Operations Emissions Compared Against Thresholds 2.5. Operations Emissions by Sector, Unmitigated 3. Construction Emissions Details 3.1. Demolition (2027) - Unmitigated 3.3. Site Preparation (2027) - Unmitigated 3.5. Grading (2027) - Unmitigated 3.7. Building Construction (2027) - Unmitigated 3.9. Building Construction (2028) - Unmitigated 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 2 / 49 3.11. Paving (2028) - Unmitigated 3.13. Architectural Coating (2028) - 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 4.3.1. Unmitigated 4.4. Water Emissions by Land Use 4.4.1. Unmitigated 4.5. Waste Emissions by Land Use 4.5.1. Unmitigated 4.6. Refrigerant Emissions by Land Use 4.6.1. Unmitigated 4.7. Offroad Emissions By Equipment Type 4.7.1. Unmitigated 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 3 / 49 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 5.5. Architectural Coatings 5.6. Dust Mitigation 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 4 / 49 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 5.13. Operational Waste Generation 5.13.1. Unmitigated 5.14. Operational Refrigeration and Air Conditioning Equipment 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 5 / 49 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 6. Climate Risk Detailed Report 6.1. Climate Risk Summary 6.2. Initial Climate Risk Scores 6.3. Adjusted Climate Risk Scores 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 6 / 49 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 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 7 / 49 1. Basic Project Information 1.1. Basic Project Information Data Field Value Project Name 16758 - Fontana Trailer Yard Construction Start Date 3/1/2027 Operational Year 2028 Lead Agency — Land Use Scale Project/site Analysis Level for Defaults County Windspeed (m/s)2.80 Precipitation (days)6.40 Location 9822 Almond Ave, Fontana, CA 92335, USA County San Bernardino-South Coast City Fontana Air District South Coast AQMD Air Basin South Coast TAZ 5286 EDFZ 10 Electric Utility Southern California Edison Gas Utility Southern California Gas App Version 2022.1.1.30 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 General Office Building 1.25 1000sqft 0.03 1,248 0.00 ——— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 8 / 49 Parking Lot 299 Space 9.46 0.00 0.00 ——— User Defined Parking 9.49 User Defined Unit 0.00 0.00 0.00 ——PC Trips User Defined Parking 9.49 User Defined Unit 0.00 0.00 0.00 ——Truck Trips 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.4.42 3.72 32.8 31.5 0.05 1.62 5.89 7.51 1.49 2.74 4.23 —5,769 5,769 0.23 0.05 0.74 5,792 Daily, Winter (Max) —————————————————— Unmit.9.59 9.22 32.8 31.3 0.05 1.62 5.89 7.51 1.49 2.74 4.23 —5,750 5,750 0.23 0.05 0.02 5,771 Average Daily (Max) —————————————————— Unmit.1.02 0.86 7.68 9.50 0.02 0.31 0.32 0.62 0.28 0.13 0.42 —1,762 1,762 0.07 0.02 0.05 1,769 Annual (Max) —————————————————— Unmit.0.19 0.16 1.40 1.73 < 0.005 0.06 0.06 0.11 0.05 0.02 0.08 —292 292 0.01 < 0.005 0.01 293 2.2. Construction Emissions by Year, Unmitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 9 / 49 Year TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily - Summer (Max) —————————————————— 2027 4.42 3.72 32.8 31.5 0.05 1.62 5.89 7.51 1.49 2.74 4.23 —5,769 5,769 0.23 0.05 0.74 5,792 Daily - Winter (Max) —————————————————— 2027 4.41 3.71 32.8 31.3 0.05 1.62 5.89 7.51 1.49 2.74 4.23 —5,750 5,750 0.23 0.05 0.02 5,771 2028 9.59 9.22 17.4 26.2 0.04 0.60 0.20 0.81 0.55 0.05 0.60 —4,514 4,514 0.18 0.04 0.02 4,531 Average Daily —————————————————— 2027 1.02 0.86 7.68 9.50 0.02 0.31 0.32 0.62 0.28 0.13 0.42 —1,762 1,762 0.07 0.02 0.05 1,769 2028 0.67 0.62 2.01 2.98 0.01 0.07 0.01 0.08 0.06 < 0.005 0.07 —537 537 0.02 < 0.005 0.02 539 Annual —————————————————— 2027 0.19 0.16 1.40 1.73 < 0.005 0.06 0.06 0.11 0.05 0.02 0.08 —292 292 0.01 < 0.005 0.01 293 2028 0.12 0.11 0.37 0.54 < 0.005 0.01 < 0.005 0.01 0.01 < 0.005 0.01 —88.9 88.9 < 0.005 < 0.005 < 0.005 89.2 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.1.77 0.91 12.2 13.5 0.13 0.19 5.91 6.09 0.18 1.56 1.74 1.05 14,388 14,389 0.96 1.86 38.4 15,005 Daily, Winter (Max) —————————————————— Unmit.1.73 0.87 12.7 12.2 0.13 0.19 5.91 6.09 0.18 1.56 1.74 1.05 14,273 14,274 0.96 1.86 1.00 14,854 Average Daily (Max) —————————————————— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 10 / 49 Unmit.1.41 0.72 10.3 10.0 0.10 0.15 4.72 4.87 0.14 1.25 1.39 1.05 11,539 11,540 0.80 1.50 13.3 12,020 Annual (Max) —————————————————— Unmit.0.26 0.13 1.88 1.83 0.02 0.03 0.86 0.89 0.03 0.23 0.25 0.17 1,910 1,911 0.13 0.25 2.21 1,990 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 1.67 0.81 12.2 13.4 0.13 0.19 5.91 6.09 0.18 1.56 1.74 —14,023 14,023 0.82 1.85 38.4 14,635 Area 0.10 0.10 < 0.005 0.05 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.22 0.22 < 0.005 < 0.005 —0.22 Energy 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —363 363 0.03 < 0.005 —365 Water ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Waste ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Refrig.————————————————< 0.005 < 0.005 Total 1.77 0.91 12.2 13.5 0.13 0.19 5.91 6.09 0.18 1.56 1.74 1.05 14,388 14,389 0.96 1.86 38.4 15,005 Daily, Winter (Max) —————————————————— Mobile 1.64 0.78 12.7 12.2 0.13 0.19 5.91 6.09 0.18 1.56 1.74 —13,908 13,908 0.82 1.86 1.00 14,483 Area 0.09 0.09 ———————————————— Energy 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —363 363 0.03 < 0.005 —365 Water ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Waste ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Refrig.————————————————< 0.005 < 0.005 Total 1.73 0.87 12.7 12.2 0.13 0.19 5.91 6.09 0.18 1.56 1.74 1.05 14,273 14,274 0.96 1.86 1.00 14,854 Average Daily —————————————————— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 11 / 49 Mobile 1.31 0.63 10.3 9.98 0.10 0.15 4.72 4.87 0.14 1.25 1.39 —11,175 11,175 0.66 1.49 13.3 11,649 Area 0.10 0.10 < 0.005 0.04 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.15 0.15 < 0.005 < 0.005 —0.15 Energy 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —363 363 0.03 < 0.005 —365 Water ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Waste ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Refrig.————————————————< 0.005 < 0.005 Total 1.41 0.72 10.3 10.0 0.10 0.15 4.72 4.87 0.14 1.25 1.39 1.05 11,539 11,540 0.80 1.50 13.3 12,020 Annual —————————————————— Mobile 0.24 0.11 1.88 1.82 0.02 0.03 0.86 0.89 0.03 0.23 0.25 —1,850 1,850 0.11 0.25 2.21 1,929 Area 0.02 0.02 < 0.005 0.01 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.03 0.03 < 0.005 < 0.005 —0.03 Energy 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —60.1 60.1 0.01 < 0.005 —60.5 Water ———————————0.07 0.24 0.31 0.01 < 0.005 —0.54 Waste ———————————0.10 0.00 0.10 0.01 0.00 —0.36 Refrig.————————————————< 0.005 < 0.005 Total 0.26 0.13 1.88 1.83 0.02 0.03 0.86 0.89 0.03 0.23 0.25 0.17 1,910 1,911 0.13 0.25 2.21 1,990 3. Construction Emissions Details 3.1. Demolition (2027) - 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) —————————————————— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 12 / 49 3,439—0.030.143,4273,427—0.73—0.730.80—0.800.0318.619.92.212.64Off-Roa d Equipm Demoliti on ——————0.11 0.11 —0.02 0.02 ——————— 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-Roa d Equipm ent 0.14 0.12 1.09 1.02 < 0.005 0.04 —0.04 0.04 —0.04 —188 188 0.01 < 0.005 —188 Demoliti on ——————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-Roa d Equipm ent 0.03 0.02 0.20 0.19 < 0.005 0.01 —0.01 0.01 —0.01 —31.1 31.1 < 0.005 < 0.005 —31.2 Demoliti on ——————< 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 0.07 0.06 0.06 0.76 0.00 0.00 0.20 0.20 0.00 0.05 0.05 —186 186 < 0.005 0.01 0.02 188 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 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 13 / 49 Hauling 0.01 < 0.005 0.10 0.06 < 0.005 < 0.005 0.02 0.02 < 0.005 0.01 0.01 —83.2 83.2 0.01 0.01 < 0.005 87.4 Average Daily —————————————————— Worker < 0.005 < 0.005 < 0.005 0.04 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 —10.3 10.3 < 0.005 < 0.005 0.02 10.5 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 < 0.005 < 0.005 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 —4.56 4.56 < 0.005 < 0.005 < 0.005 4.79 Annual —————————————————— Worker < 0.005 < 0.005 < 0.005 0.01 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 —1.71 1.71 < 0.005 < 0.005 < 0.005 1.73 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 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 —0.75 0.75 < 0.005 < 0.005 < 0.005 0.79 3.3. Site Preparation (2027) - 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-Roa d Equipm ent 4.34 3.65 32.7 30.4 0.05 1.62 —1.62 1.49 —1.49 —5,533 5,533 0.22 0.04 —5,552 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 Daily, Winter (Max) —————————————————— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 14 / 49 5,552—0.040.225,5335,533—1.49—1.491.62—1.620.0530.432.73.654.34Off-Roa d Equipm 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-Roa d Equipm ent 0.12 0.10 0.90 0.83 < 0.005 0.04 —0.04 0.04 —0.04 —152 152 0.01 < 0.005 —152 Dust From Material Movement ——————0.16 0.16 —0.07 0.07 ——————— 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-Roa d Equipm ent 0.02 0.02 0.16 0.15 < 0.005 0.01 —0.01 0.01 —0.01 —25.1 25.1 < 0.005 < 0.005 —25.2 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 —————————————————— Daily, Summer (Max) —————————————————— Worker 0.08 0.07 0.06 1.17 0.00 0.00 0.23 0.23 0.00 0.05 0.05 —237 237 < 0.005 0.01 0.74 240 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 15 / 49 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 Daily, Winter (Max) —————————————————— Worker 0.08 0.07 0.07 0.88 0.00 0.00 0.23 0.23 0.00 0.05 0.05 —217 217 < 0.005 0.01 0.02 220 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 0.03 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 —6.03 6.03 < 0.005 < 0.005 0.01 6.11 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 < 0.005 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 —1.00 1.00 < 0.005 < 0.005 < 0.005 1.01 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 3.5. Grading (2027) - 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-Roa d Equipm ent 2.42 2.03 17.8 18.8 0.03 0.93 —0.93 0.86 —0.86 —3,136 3,136 0.13 0.03 —3,147 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 16 / 49 ———————0.940.94—2.262.26——————Dust From Material Movement 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 Daily, Winter (Max) —————————————————— Average Daily —————————————————— Off-Roa d Equipm ent 0.13 0.11 0.98 1.03 < 0.005 0.05 —0.05 0.05 —0.05 —172 172 0.01 < 0.005 —172 Dust From Material Movement ——————0.12 0.12 —0.05 0.05 ——————— 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-Roa d Equipm ent 0.02 0.02 0.18 0.19 < 0.005 0.01 —0.01 0.01 —0.01 —28.5 28.5 < 0.005 < 0.005 —28.5 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) —————————————————— Worker 0.07 0.06 0.05 1.01 0.00 0.00 0.20 0.20 0.00 0.05 0.05 —203 203 < 0.005 0.01 0.64 206 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 17 / 49 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 Daily, Winter (Max) —————————————————— Average Daily —————————————————— Worker < 0.005 < 0.005 < 0.005 0.04 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 —10.3 10.3 < 0.005 < 0.005 0.02 10.5 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 < 0.005 < 0.005 —1.71 1.71 < 0.005 < 0.005 < 0.005 1.73 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 3.7. Building Construction (2027) - 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-Roa d Equipm ent 1.33 1.11 10.2 14.0 0.03 0.36 —0.36 0.34 —0.34 —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 Daily, Winter (Max) —————————————————— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 18 / 49 2,639—0.020.112,6302,630—0.34—0.340.36—0.360.0314.010.21.111.33Off-Roa d 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-Roa d Equipm ent 0.61 0.51 4.70 6.48 0.01 0.17 —0.17 0.15 —0.15 —1,215 1,215 0.05 0.01 —1,219 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-Roa d Equipm ent 0.11 0.09 0.86 1.18 < 0.005 0.03 —0.03 0.03 —0.03 —201 201 0.01 < 0.005 —202 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 < 0.005 < 0.005 < 0.005 0.03 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 —5.40 5.40 < 0.005 < 0.005 0.02 5.48 Vendor < 0.005 < 0.005 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 —6.09 6.09 < 0.005 < 0.005 0.01 6.39 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 < 0.005 < 0.005 < 0.005 0.02 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 —4.95 4.95 < 0.005 < 0.005 < 0.005 5.01 Vendor < 0.005 < 0.005 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 —6.09 6.09 < 0.005 < 0.005 < 0.005 6.37 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 —————————————————— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 19 / 49 Worker < 0.005 < 0.005 < 0.005 0.01 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 —2.32 2.32 < 0.005 < 0.005 < 0.005 2.35 Vendor < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 —2.81 2.81 < 0.005 < 0.005 < 0.005 2.95 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 < 0.005 < 0.005 —0.38 0.38 < 0.005 < 0.005 < 0.005 0.39 Vendor < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 —0.47 0.47 < 0.005 < 0.005 < 0.005 0.49 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. Building Construction (2028) - 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-Roa d Equipm ent 1.28 1.07 9.66 14.0 0.03 0.33 —0.33 0.30 —0.30 —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-Roa d Equipm ent 0.21 0.18 1.59 2.31 < 0.005 0.05 —0.05 0.05 —0.05 —432 432 0.02 < 0.005 —434 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 —————————————————— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 20 / 49 Off-Roa Equipment 0.04 0.03 0.29 0.42 < 0.005 0.01 —0.01 0.01 —0.01 —71.6 71.6 < 0.005 < 0.005 —71.8 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 < 0.005 < 0.005 < 0.005 0.02 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 —4.86 4.86 < 0.005 < 0.005 < 0.005 4.92 Vendor < 0.005 < 0.005 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 —5.95 5.95 < 0.005 < 0.005 < 0.005 6.23 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 < 0.005 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 —0.81 0.81 < 0.005 < 0.005 < 0.005 0.82 Vendor < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 —0.98 0.98 < 0.005 < 0.005 < 0.005 1.03 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 < 0.005 < 0.005 —0.13 0.13 < 0.005 < 0.005 < 0.005 0.14 Vendor < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 —0.16 0.16 < 0.005 < 0.005 < 0.005 0.17 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. Paving (2028) - 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) —————————————————— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 21 / 49 Daily, Winter (Max) —————————————————— Off-Roa d Equipm ent 0.82 0.69 6.63 9.91 0.01 0.26 —0.26 0.24 —0.24 —1,511 1,511 0.06 0.01 —1,516 Paving 1.24 1.24 ———————————————— 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-Roa d Equipm ent 0.04 0.04 0.36 0.54 < 0.005 0.01 —0.01 0.01 —0.01 —82.8 82.8 < 0.005 < 0.005 —83.1 Paving 0.07 0.07 ———————————————— 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-Roa d Equipm ent 0.01 0.01 0.07 0.10 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —13.7 13.7 < 0.005 < 0.005 —13.8 Paving 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 0.06 0.06 0.05 0.70 0.00 0.00 0.20 0.20 0.00 0.05 0.05 —183 183 < 0.005 0.01 0.01 185 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 22 / 49 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 0.01 0.01 0.00 < 0.005 < 0.005 —10.1 10.1 < 0.005 < 0.005 0.01 10.3 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 < 0.005 < 0.005 —1.68 1.68 < 0.005 < 0.005 < 0.005 1.70 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 3.13. Architectural Coating (2028) - 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-Roa d Equipm ent 0.17 0.14 1.08 1.49 < 0.005 0.02 —0.02 0.02 —0.02 —178 178 0.01 < 0.005 —179 Architect ural Coating s 6.02 6.02 ———————————————— 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 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 23 / 49 Average Daily —————————————————— Off-Roa d Equipm ent 0.01 0.01 0.06 0.08 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —9.75 9.75 < 0.005 < 0.005 —9.79 Architect ural Coating s 0.33 0.33 ———————————————— 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-Roa d Equipm ent < 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —1.61 1.61 < 0.005 < 0.005 —1.62 Architect ural Coating s 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 Offsite —————————————————— Daily, Summer (Max) —————————————————— Daily, Winter (Max) —————————————————— Worker < 0.005 < 0.005 < 0.005 < 0.005 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 —0.97 0.97 < 0.005 < 0.005 < 0.005 0.98 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 < 0.005 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 —0.05 0.05 < 0.005 < 0.005 < 0.005 0.05 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 24 / 49 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 < 0.005 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 —0.01 0.01 < 0.005 < 0.005 < 0.005 0.01 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) —————————————————— General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 0.00 0.00 0.00 0.00 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 User Defined Parking 1.67 0.81 12.2 13.4 0.13 0.19 5.91 6.09 0.18 1.56 1.74 —14,023 14,023 0.82 1.85 38.4 14,635 Total 1.67 0.81 12.2 13.4 0.13 0.19 5.91 6.09 0.18 1.56 1.74 —14,023 14,023 0.82 1.85 38.4 14,635 Daily, Winter (Max) —————————————————— General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 0.00 0.00 0.00 0.00 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 25 / 49 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 User Defined Parking 1.64 0.78 12.7 12.2 0.13 0.19 5.91 6.09 0.18 1.56 1.74 —13,908 13,908 0.82 1.86 1.00 14,483 Total 1.64 0.78 12.7 12.2 0.13 0.19 5.91 6.09 0.18 1.56 1.74 —13,908 13,908 0.82 1.86 1.00 14,483 Annual —————————————————— General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 0.00 0.00 0.00 0.00 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 User Defined Parking 0.24 0.11 1.88 1.82 0.02 0.03 0.86 0.89 0.03 0.23 0.25 —1,850 1,850 0.11 0.25 2.21 1,929 Total 0.24 0.11 1.88 1.82 0.02 0.03 0.86 0.89 0.03 0.23 0.25 —1,850 1,850 0.11 0.25 2.21 1,929 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) —————————————————— General Office Building ————————————20.7 20.7 < 0.005 < 0.005 —20.8 Parking Lot ————————————342 342 0.03 < 0.005 —344 User Defined Parking ————————————0.00 0.00 0.00 0.00 —0.00 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 26 / 49 Total ————————————363 363 0.03 < 0.005 —365 Daily, Winter (Max) —————————————————— General Office Building ————————————20.7 20.7 < 0.005 < 0.005 —20.8 Parking Lot ————————————342 342 0.03 < 0.005 —344 User Defined Parking ————————————0.00 0.00 0.00 0.00 —0.00 Total ————————————363 363 0.03 < 0.005 —365 Annual —————————————————— General Office Building ————————————3.42 3.42 < 0.005 < 0.005 —3.44 Parking Lot ————————————56.7 56.7 0.01 < 0.005 —57.0 User Defined Parking ————————————0.00 0.00 0.00 0.00 —0.00 Total ————————————60.1 60.1 0.01 < 0.005 —60.5 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) —————————————————— General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —0.00 0.00 0.00 0.00 —0.00 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 27 / 49 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 User Defined Parking 0.00 0.00 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 0.00 0.00 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) —————————————————— General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —0.00 0.00 0.00 0.00 —0.00 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 User Defined Parking 0.00 0.00 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 0.00 0.00 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 —————————————————— General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —0.00 0.00 0.00 0.00 —0.00 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 User Defined Parking 0.00 0.00 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 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —0.00 0.00 0.00 0.00 —0.00 4.3. Area Emissions by Source 4.3.1. 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 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 28 / 49 Daily, Summer (Max) —————————————————— Consum er Product s 0.06 0.06 ———————————————— Architect ural Coating s 0.03 0.03 ———————————————— Landsca pe Equipm ent 0.01 0.01 < 0.005 0.05 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.22 0.22 < 0.005 < 0.005 —0.22 Total 0.10 0.10 < 0.005 0.05 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.22 0.22 < 0.005 < 0.005 —0.22 Daily, Winter (Max) —————————————————— Consum er Product s 0.06 0.06 ———————————————— Architect ural Coating s 0.03 0.03 ———————————————— Total 0.09 0.09 ———————————————— Annual —————————————————— Consum er Product s 0.01 0.01 ———————————————— Architect ural Coating s 0.01 0.01 ———————————————— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 29 / 49 0.03—< 0.005< 0.0050.030.03—< 0.005—< 0.005< 0.005—< 0.005< 0.0050.01< 0.005< 0.005< 0.005Landsca pe Total 0.02 0.02 < 0.005 0.01 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.03 0.03 < 0.005 < 0.005 —0.03 4.4. Water Emissions by Land Use 4.4.1. 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) —————————————————— General Office Building ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Daily, Winter (Max) —————————————————— General Office Building ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 30 / 49 Annual —————————————————— General Office Building ———————————0.07 0.24 0.31 0.01 < 0.005 —0.54 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.07 0.24 0.31 0.01 < 0.005 —0.54 4.5. Waste Emissions by Land Use 4.5.1. 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) —————————————————— General Office Building ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Daily, Winter (Max) —————————————————— General Office Building ———————————0.63 0.00 0.63 0.06 0.00 —2.19 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 31 / 49 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Annual —————————————————— General Office Building ———————————0.10 0.00 0.10 0.01 0.00 —0.36 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.10 0.00 0.10 0.01 0.00 —0.36 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) —————————————————— General Office Building ————————————————< 0.005 < 0.005 Total ————————————————< 0.005 < 0.005 Daily, Winter (Max) —————————————————— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 32 / 49 < 0.005< 0.005————————————————General Office Building Total ————————————————< 0.005 < 0.005 Annual —————————————————— General Office Building ————————————————< 0.005 < 0.005 Total ————————————————< 0.005 < 0.005 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) Equipm ent 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 —————————————————— 4.8. 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) 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 33 / 49 Equipm 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) Equipm ent 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 —————————————————— 4.10. Soil Carbon Accumulation By Vegetation Type 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 34 / 49 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) Vegetati on 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 —————————————————— Daily, Winter (Max) —————————————————— Total —————————————————— Annual —————————————————— Total —————————————————— 4.10.3. Avoided and Sequestered Emissions by Species - Unmitigated 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 35 / 49 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 —————————————————— Remove d —————————————————— Subtotal —————————————————— ——————————————————— Annual —————————————————— Avoided —————————————————— Subtotal —————————————————— Sequest ered —————————————————— Subtotal —————————————————— 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 36 / 49 Remove —————————————————— 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 3/1/2027 3/26/2027 5.00 20.0 — Site Preparation Site Preparation 3/29/2027 4/9/2027 5.00 10.0 — Grading Grading 4/12/2027 5/7/2027 5.00 20.0 — Building Construction Building Construction 5/10/2027 3/24/2028 5.00 230 — Paving Paving 2/28/2028 3/24/2028 5.00 20.0 — Architectural Coating Architectural Coating 2/28/2028 3/24/2028 5.00 20.0 — 5.2. Off-Road Equipment 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 1.00 8.00 36.0 0.38 Grading Crawler Tractors Diesel Average 3.00 8.00 87.0 0.43 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 37 / 49 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/Back hoes 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 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 —10.2 HHDT,MHDT Demolition Hauling 1.25 20.0 HHDT Demolition Onsite truck ——HHDT Site Preparation ———— Site Preparation Worker 17.5 18.5 LDA,LDT1,LDT2 Site Preparation Vendor —10.2 HHDT,MHDT Site Preparation Hauling 0.00 20.0 HHDT Site Preparation Onsite truck ——HHDT Grading ———— Grading Worker 15.0 18.5 LDA,LDT1,LDT2 Grading Vendor —10.2 HHDT,MHDT 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 38 / 49 Grading Hauling 0.00 20.0 HHDT Grading Onsite truck ——HHDT Building Construction ———— Building Construction Worker 0.40 18.5 LDA,LDT1,LDT2 Building Construction Vendor 0.20 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 ———— Architectural Coating Worker 0.08 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 0.00 0.00 1,872 624 24,725 5.6. Dust Mitigation 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 39 / 49 5.6.1. Construction Earthmoving Activities Phase Name Material Imported (cy)Material Exported (cy)Acres Graded (acres)Material Demolished (Ton of Debris) Acres Paved (acres) Demolition 0.00 0.00 0.00 100 — Site Preparation ——35.0 0.00 — Grading ——50.0 0.00 — Paving 0.00 0.00 0.00 0.00 9.46 5.6.2. Construction Earthmoving Control Strategies Control Strategies Applied Frequency (per day)PM10 Reduction PM2.5 Reduction Water Exposed Area 3 74%74% 5.7. Construction Paving Land Use Area Paved (acres)% Asphalt General Office Building 0.00 0% Parking Lot 9.46 100% User Defined Parking 0.00 100% User Defined Parking 0.00 100% 5.8. Construction Electricity Consumption and Emissions Factors kWh per Year and Emission Factor (lb/MWh) Year kWh per Year CO2 CH4 N2O 2027 0.00 346 0.03 < 0.005 2028 0.00 346 0.03 < 0.005 5.9. Operational Mobile Sources 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 40 / 49 5.9.1. Unmitigated Land Use Type Trips/Weekday Trips/Saturday Trips/Sunday Trips/Year VMT/Weekday VMT/Saturday VMT/Sunday VMT/Year General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Parking Lot 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 User Defined Parking 100.0 135 125 39,670 1,602 2,170 2,009 635,577 User Defined Parking 136 184 171 53,953 3,717 5,034 4,660 1,474,534 5.10. Operational Area Sources 5.10.1. Hearths 5.10.1.1. Unmitigated 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) 0 0.00 1,872 624 24,725 5.10.3. Landscape Equipment Season Unit Value Snow Days day/yr 0.00 Summer Days day/yr 250 5.11. Operational Energy Consumption 5.11.1. Unmitigated Electricity (kWh/yr) and CO2 and CH4 and N2O and Natural Gas (kBTU/yr) 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 41 / 49 Land Use Electricity (kWh/yr)CO2 CH4 N2O Natural Gas (kBTU/yr) General Office Building 21,780 346 0.0330 0.0040 0.00 Parking Lot 360,980 346 0.0330 0.0040 0.00 User Defined Parking 0.00 346 0.0330 0.0040 0.00 User Defined Parking 0.00 346 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) General Office Building 221,812 0.00 Parking Lot 0.00 0.00 User Defined Parking 0.00 0.00 User Defined Parking 0.00 0.00 5.13. Operational Waste Generation 5.13.1. Unmitigated Land Use Waste (ton/year)Cogeneration (kWh/year) General Office Building 1.16 — Parking Lot 0.00 — User Defined Parking 0.00 — User Defined Parking 0.00 — 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 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 42 / 49 General Office Building Household refrigerators and/or freezers R-134a 1,430 0.02 0.60 0.00 1.00 General Office Building Other commercial A/C and heat pumps User Defined 750 < 0.005 4.00 4.00 18.0 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 Year 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) 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 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 43 / 49 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 Temperature and Extreme Heat 21.7 annual days of extreme heat Extreme Precipitation 5.25 annual days with precipitation above 20 mm Sea Level Rise —meters of inundation depth Wildfire 0.00 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 (Radke et al., 2017, CEC-500-2017-008), and consider inundation location and depth for the San Francisco Bay, the Sacramento-San Joaquin River Delta and California coast resulting different increments of sea level rise coupled with extreme storm events. Users may select from four scenarios to view the range in potential inundation depth for the grid cell. The four scenarios are: No rise, 0.5 meter, 1.0 meter, 1.41 meters 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. 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 44 / 49 6.2. Initial Climate Risk Scores Climate Hazard Exposure Score Sensitivity Score Adaptive Capacity Score Vulnerability Score Temperature and Extreme Heat 2 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. 6.3. Adjusted Climate Risk Scores Climate Hazard Exposure Score Sensitivity Score Adaptive Capacity Score Vulnerability Score Temperature and Extreme Heat 2 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. 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 45 / 49 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 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 95.3 AQ-PM 93.5 AQ-DPM 89.8 Drinking Water 66.7 Lead Risk Housing 48.2 Pesticides 0.00 Toxic Releases 75.3 Traffic 70.0 Effect Indicators — CleanUp Sites 86.3 Groundwater 30.9 Haz Waste Facilities/Generators 97.5 Impaired Water Bodies 0.00 Solid Waste 95.4 Sensitive Population — Asthma 72.1 Cardio-vascular 85.8 Low Birth Weights 31.5 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 46 / 49 Socioeconomic Factor Indicators — Education 79.1 Housing 48.1 Linguistic 73.7 Poverty 73.3 Unemployment 85.8 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 19.81265238 Employed 14.93648146 Median HI 31.91325549 Education — Bachelor's or higher 4.824842808 High school enrollment 17.87501604 Preschool enrollment 64.42961632 Transportation — Auto Access 92.6344155 Active commuting 46.54176825 Social — 2-parent households 66.99602207 Voting 15.74489927 Neighborhood — Alcohol availability 51.89272424 Park access 21.5193122 Retail density 38.36776594 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 47 / 49 Supermarket access 40.97266778 Tree canopy 5.51777236 Housing — Homeownership 52.16219684 Housing habitability 24.6888233 Low-inc homeowner severe housing cost burden 17.34890286 Low-inc renter severe housing cost burden 82.47144874 Uncrowded housing 10.95855255 Health Outcomes — Insured adults 8.392146798 Arthritis 41.4 Asthma ER Admissions 18.4 High Blood Pressure 53.6 Cancer (excluding skin)68.9 Asthma 21.6 Coronary Heart Disease 40.3 Chronic Obstructive Pulmonary Disease 27.0 Diagnosed Diabetes 27.5 Life Expectancy at Birth 23.5 Cognitively Disabled 24.2 Physically Disabled 50.9 Heart Attack ER Admissions 7.0 Mental Health Not Good 19.7 Chronic Kidney Disease 27.1 Obesity 22.5 Pedestrian Injuries 90.7 Physical Health Not Good 21.1 Stroke 34.3 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 48 / 49 Health Risk Behaviors — Binge Drinking 50.7 Current Smoker 20.8 No Leisure Time for Physical Activity 23.4 Climate Change Exposures — Wildfire Risk 0.0 SLR Inundation Area 0.0 Children 39.2 Elderly 91.2 English Speaking 19.9 Foreign-born 77.9 Outdoor Workers 50.5 Climate Change Adaptive Capacity — Impervious Surface Cover 77.1 Traffic Density 71.4 Traffic Access 46.8 Other Indices — Hardship 86.0 Other Decision Support — 2016 Voting 29.4 7.3. Overall Health & Equity Scores Metric Result for Project Census Tract CalEnviroScreen 4.0 Score for Project Location (a)93.0 Healthy Places Index Score for Project Location (b)19.0 Project Located in a Designated Disadvantaged Community (Senate Bill 535)Yes Project Located in a Low-Income Community (Assembly Bill 1550)Yes Project Located in a Community Air Protection Program Community (Assembly Bill 617)No 16758 - Fontana Trailer Yard Detailed Report, 10/16/2025 49 / 49 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 Screen Justification Land Use Based on site plan, total Project site is 9.49 acres. Construction: Construction Phases Building Construction, Paving, and Architectural Coating overlap to present a conservative analysis Construction: Off-Road Equipment T/L/B replaced with Crawler Tractor to accurately calculate disturbance for Site Preparation and Grading phases Standard 8-hour work days Construction: Architectural Coatings SCAQMD Rule 1113 Operations: Vehicle Data Trip Characteristics taken from the Traffic Analysis Operations: Fleet Mix Passenger Car Mix estimated based on CalEEMod default fleet mix and the ratio of the vehicle classes (LDA, LDT1, LDT2, MDV, MCY). Truck Fleet Mix based on 2, 3 and 4 axle trucks Operations: Architectural Coatings SCAQMD Rule 1113 Operations: Energy Use Natural Gas will not be utilized Operations: Refrigerants Beginning 1 January 2025, all new air conditioning equipment may not use refrigerants with a GWP of 750 or greater. 16758-03 AQ & GHG Assessment 35 Almond Avenue Trailer Yard (MCN25-0059) APPENDIX 2: CALEEMOD OPERATIONAL LST EMISSIONS MODEL OUTPUTS 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 1 / 31 16758 - Fontana Trailer Yard (Operational LSTs) 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 2.4. Operations Emissions Compared Against Thresholds 2.5. Operations Emissions by Sector, 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 4.3.1. Unmitigated 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 2 / 31 4.4. Water Emissions by Land Use 4.4.1. Unmitigated 4.5. Waste Emissions by Land Use 4.5.1. Unmitigated 4.6. Refrigerant Emissions by Land Use 4.6.1. Unmitigated 4.7. Offroad Emissions By Equipment Type 4.7.1. Unmitigated 4.8. Stationary Emissions By Equipment Type 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 5.9. Operational Mobile Sources 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 3 / 31 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 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 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 4 / 31 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 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 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 5 / 31 7.4. Health & Equity Measures 7.5. Evaluation Scorecard 7.6. Health & Equity Custom Measures 8. User Changes to Default Data 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 6 / 31 1. Basic Project Information 1.1. Basic Project Information Data Field Value Project Name 16758 - Fontana Trailer Yard (Operational LSTs) Operational Year 2028 Lead Agency — Land Use Scale Project/site Analysis Level for Defaults County Windspeed (m/s)2.80 Precipitation (days)6.40 Location 9822 Almond Ave, Fontana, CA 92335, USA County San Bernardino-South Coast City Fontana Air District South Coast AQMD Air Basin South Coast TAZ 5286 EDFZ 10 Electric Utility Southern California Edison Gas Utility Southern California Gas App Version 2022.1.1.30 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 General Office Building 1.25 1000sqft 0.03 1,248 0.00 ——— Parking Lot 299 Space 9.46 0.00 0.00 ——— 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 7 / 31 User Defined Parking 9.49 User Defined Unit 0.00 0.00 0.00 ——PC Trips User Defined Parking 9.49 User Defined Unit 0.00 0.00 0.00 ——Truck Trips 1.3. User-Selected Emission Reduction Measures by Emissions Sector No measures selected 2. Emissions Summary 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.0.66 0.55 1.61 2.20 < 0.005 < 0.005 0.04 0.05 < 0.005 0.01 0.01 1.05 655 656 0.26 0.06 0.26 680 Daily, Winter (Max) —————————————————— Unmit.0.62 0.51 1.69 2.30 < 0.005 < 0.005 0.04 0.05 < 0.005 0.01 0.01 1.05 656 657 0.26 0.06 0.01 681 Average Daily (Max) —————————————————— Unmit.0.52 0.43 1.33 1.87 < 0.005 < 0.005 0.03 0.04 < 0.005 0.01 0.01 1.05 598 599 0.24 0.05 0.09 619 Annual (Max) —————————————————— Unmit.0.10 0.08 0.24 0.34 < 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 < 0.005 0.17 98.9 99.1 0.04 0.01 0.02 102 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 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 8 / 31 Daily, Summer (Max) —————————————————— Mobile 0.56 0.45 1.61 2.15 < 0.005 < 0.005 0.04 0.05 < 0.005 0.01 0.01 —290 290 0.12 0.05 0.26 309 Area 0.10 0.10 < 0.005 0.05 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.22 0.22 < 0.005 < 0.005 —0.22 Energy 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —363 363 0.03 < 0.005 —365 Water ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Waste ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Refrig.————————————————< 0.005 < 0.005 Total 0.66 0.55 1.61 2.20 < 0.005 < 0.005 0.04 0.05 < 0.005 0.01 0.01 1.05 655 656 0.26 0.06 0.26 680 Daily, Winter (Max) —————————————————— Mobile 0.53 0.42 1.69 2.30 < 0.005 < 0.005 0.04 0.05 < 0.005 0.01 0.01 —292 292 0.12 0.05 0.01 311 Area 0.09 0.09 ———————————————— Energy 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —363 363 0.03 < 0.005 —365 Water ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Waste ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Refrig.————————————————< 0.005 < 0.005 Total 0.62 0.51 1.69 2.30 < 0.005 < 0.005 0.04 0.05 < 0.005 0.01 0.01 1.05 656 657 0.26 0.06 0.01 681 Average Daily —————————————————— Mobile 0.43 0.33 1.33 1.83 < 0.005 < 0.005 0.03 0.04 < 0.005 0.01 0.01 —233 233 0.10 0.04 0.09 248 Area 0.10 0.10 < 0.005 0.04 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.15 0.15 < 0.005 < 0.005 —0.15 Energy 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —363 363 0.03 < 0.005 —365 Water ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Waste ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Refrig.————————————————< 0.005 < 0.005 Total 0.52 0.43 1.33 1.87 < 0.005 < 0.005 0.03 0.04 < 0.005 0.01 0.01 1.05 598 599 0.24 0.05 0.09 619 Annual —————————————————— 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 9 / 31 Mobile 0.08 0.06 0.24 0.33 < 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 < 0.005 —38.6 38.6 0.02 0.01 0.01 41.1 Area 0.02 0.02 < 0.005 0.01 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.03 0.03 < 0.005 < 0.005 —0.03 Energy 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —60.1 60.1 0.01 < 0.005 —60.5 Water ———————————0.07 0.24 0.31 0.01 < 0.005 —0.54 Waste ———————————0.10 0.00 0.10 0.01 0.00 —0.36 Refrig.————————————————< 0.005 < 0.005 Total 0.10 0.08 0.24 0.34 < 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 < 0.005 0.17 98.9 99.1 0.04 0.01 0.02 102 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) —————————————————— General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 0.00 0.00 0.00 0.00 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 User Defined Parking 0.56 0.45 1.61 2.15 < 0.005 < 0.005 0.04 0.05 < 0.005 0.01 0.01 —290 290 0.12 0.05 0.26 309 Total 0.56 0.45 1.61 2.15 < 0.005 < 0.005 0.04 0.05 < 0.005 0.01 0.01 —290 290 0.12 0.05 0.26 309 Daily, Winter (Max) —————————————————— 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 10 / 31 0.000.000.000.000.000.00—0.000.000.000.000.000.000.000.000.000.000.00General Office Building 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 User Defined Parking 0.53 0.42 1.69 2.30 < 0.005 < 0.005 0.04 0.05 < 0.005 0.01 0.01 —292 292 0.12 0.05 0.01 311 Total 0.53 0.42 1.69 2.30 < 0.005 < 0.005 0.04 0.05 < 0.005 0.01 0.01 —292 292 0.12 0.05 0.01 311 Annual —————————————————— General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 0.00 0.00 0.00 0.00 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 User Defined Parking 0.08 0.06 0.24 0.33 < 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 < 0.005 —38.6 38.6 0.02 0.01 0.01 41.1 Total 0.08 0.06 0.24 0.33 < 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 < 0.005 —38.6 38.6 0.02 0.01 0.01 41.1 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) —————————————————— General Office Building ————————————20.7 20.7 < 0.005 < 0.005 —20.8 Parking Lot ————————————342 342 0.03 < 0.005 —344 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 11 / 31 User Defined Parking ————————————0.00 0.00 0.00 0.00 —0.00 Total ————————————363 363 0.03 < 0.005 —365 Daily, Winter (Max) —————————————————— General Office Building ————————————20.7 20.7 < 0.005 < 0.005 —20.8 Parking Lot ————————————342 342 0.03 < 0.005 —344 User Defined Parking ————————————0.00 0.00 0.00 0.00 —0.00 Total ————————————363 363 0.03 < 0.005 —365 Annual —————————————————— General Office Building ————————————3.42 3.42 < 0.005 < 0.005 —3.44 Parking Lot ————————————56.7 56.7 0.01 < 0.005 —57.0 User Defined Parking ————————————0.00 0.00 0.00 0.00 —0.00 Total ————————————60.1 60.1 0.01 < 0.005 —60.5 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) —————————————————— 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 12 / 31 General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —0.00 0.00 0.00 0.00 —0.00 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 User Defined Parking 0.00 0.00 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 0.00 0.00 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) —————————————————— General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —0.00 0.00 0.00 0.00 —0.00 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 User Defined Parking 0.00 0.00 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 0.00 0.00 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 —————————————————— General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —0.00 0.00 0.00 0.00 —0.00 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 User Defined Parking 0.00 0.00 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 0.00 0.00 0.00 0.00 0.00 0.00 —0.00 0.00 —0.00 —0.00 0.00 0.00 0.00 —0.00 4.3. Area Emissions by Source 4.3.1. Unmitigated 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 13 / 31 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) —————————————————— Consum er Product s 0.06 0.06 ———————————————— Architect ural Coating s 0.03 0.03 ———————————————— Landsca pe Equipm ent 0.01 0.01 < 0.005 0.05 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.22 0.22 < 0.005 < 0.005 —0.22 Total 0.10 0.10 < 0.005 0.05 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.22 0.22 < 0.005 < 0.005 —0.22 Daily, Winter (Max) —————————————————— Consum er Product s 0.06 0.06 ———————————————— Architect ural Coating s 0.03 0.03 ———————————————— Total 0.09 0.09 ———————————————— Annual —————————————————— Consum er Product s 0.01 0.01 ———————————————— 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 14 / 31 ————————————————0.010.01Architect ural Coating Landsca pe Equipm ent < 0.005 < 0.005 < 0.005 0.01 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.03 0.03 < 0.005 < 0.005 —0.03 Total 0.02 0.02 < 0.005 0.01 < 0.005 < 0.005 —< 0.005 < 0.005 —< 0.005 —0.03 0.03 < 0.005 < 0.005 —0.03 4.4. Water Emissions by Land Use 4.4.1. 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) —————————————————— General Office Building ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Daily, Winter (Max) —————————————————— General Office Building ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 15 / 31 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.43 1.43 1.86 0.04 < 0.005 —3.26 Annual —————————————————— General Office Building ———————————0.07 0.24 0.31 0.01 < 0.005 —0.54 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.07 0.24 0.31 0.01 < 0.005 —0.54 4.5. Waste Emissions by Land Use 4.5.1. 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) —————————————————— General Office Building ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.63 0.00 0.63 0.06 0.00 —2.19 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 16 / 31 ——————————————————Daily, Winter (Max) General Office Building ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.63 0.00 0.63 0.06 0.00 —2.19 Annual —————————————————— General Office Building ———————————0.10 0.00 0.10 0.01 0.00 —0.36 Parking Lot ———————————0.00 0.00 0.00 0.00 0.00 —0.00 User Defined Parking ———————————0.00 0.00 0.00 0.00 0.00 —0.00 Total ———————————0.10 0.00 0.10 0.01 0.00 —0.36 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) —————————————————— General Office Building ————————————————< 0.005 < 0.005 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 17 / 31 Total ————————————————< 0.005 < 0.005 Daily, Winter (Max) —————————————————— General Office Building ————————————————< 0.005 < 0.005 Total ————————————————< 0.005 < 0.005 Annual —————————————————— General Office Building ————————————————< 0.005 < 0.005 Total ————————————————< 0.005 < 0.005 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) Equipm ent 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 —————————————————— 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 18 / 31 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) Equipm ent 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) Equipm ent 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 —————————————————— 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 19 / 31 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) Vegetati on 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 —————————————————— Daily, Winter (Max) —————————————————— Total —————————————————— 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 20 / 31 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 —————————————————— Remove d —————————————————— Subtotal —————————————————— ——————————————————— Annual —————————————————— 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 21 / 31 Avoided —————————————————— Subtotal —————————————————— Sequest ered —————————————————— Subtotal —————————————————— Remove d —————————————————— Subtotal —————————————————— ——————————————————— 5. Activity Data 5.9. Operational Mobile Sources 5.9.1. Unmitigated Land Use Type Trips/Weekday Trips/Saturday Trips/Sunday Trips/Year VMT/Weekday VMT/Saturday VMT/Sunday VMT/Year General Office Building 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Parking Lot 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 User Defined Parking 100.0 135 125 39,670 17.0 23.0 21.3 6,744 User Defined Parking 136 184 171 53,953 23.1 31.3 29.0 9,172 5.10. Operational Area Sources 5.10.1. Hearths 5.10.1.1. Unmitigated 5.10.2. Architectural Coatings 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 22 / 31 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) 0 0.00 1,872 624 24,725 5.10.3. Landscape Equipment Season Unit Value Snow Days day/yr 0.00 Summer Days day/yr 250 5.11. Operational Energy Consumption 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) General Office Building 21,780 346 0.0330 0.0040 0.00 Parking Lot 360,980 346 0.0330 0.0040 0.00 User Defined Parking 0.00 346 0.0330 0.0040 0.00 User Defined Parking 0.00 346 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) General Office Building 221,812 0.00 Parking Lot 0.00 0.00 User Defined Parking 0.00 0.00 User Defined Parking 0.00 0.00 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 23 / 31 5.13. Operational Waste Generation 5.13.1. Unmitigated Land Use Waste (ton/year)Cogeneration (kWh/year) General Office Building 1.16 — Parking Lot 0.00 — User Defined Parking 0.00 — User Defined Parking 0.00 — 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 General Office Building Household refrigerators and/or freezers R-134a 1,430 0.02 0.60 0.00 1.00 General Office Building Other commercial A/C and heat pumps User Defined 750 < 0.005 4.00 4.00 18.0 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 Year Horsepower Load Factor 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 24 / 31 5.16.2. Process Boilers Equipment Type Fuel Type Number Boiler Rating (MMBtu/hr)Daily Heat Input (MMBtu/day)Annual Heat Input (MMBtu/yr) 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. 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 25 / 31 Climate Hazard Result for Project Location Unit Temperature and Extreme Heat 21.7 annual days of extreme heat Extreme Precipitation 5.25 annual days with precipitation above 20 mm Sea Level Rise —meters of inundation depth Wildfire 0.00 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 (Radke et al., 2017, CEC-500-2017-008), and consider inundation location and depth for the San Francisco Bay, the Sacramento-San Joaquin River Delta and California coast resulting different increments of sea level rise coupled with extreme storm events. Users may select from four scenarios to view the range in potential inundation depth for the grid cell. The four scenarios are: No rise, 0.5 meter, 1.0 meter, 1.41 meters 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 2 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. 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 26 / 31 6.3. Adjusted Climate Risk Scores Climate Hazard Exposure Score Sensitivity Score Adaptive Capacity Score Vulnerability Score Temperature and Extreme Heat 2 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 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 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 95.3 AQ-PM 93.5 AQ-DPM 89.8 Drinking Water 66.7 Lead Risk Housing 48.2 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 27 / 31 Pesticides 0.00 Toxic Releases 75.3 Traffic 70.0 Effect Indicators — CleanUp Sites 86.3 Groundwater 30.9 Haz Waste Facilities/Generators 97.5 Impaired Water Bodies 0.00 Solid Waste 95.4 Sensitive Population — Asthma 72.1 Cardio-vascular 85.8 Low Birth Weights 31.5 Socioeconomic Factor Indicators — Education 79.1 Housing 48.1 Linguistic 73.7 Poverty 73.3 Unemployment 85.8 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 19.81265238 Employed 14.93648146 Median HI 31.91325549 Education — 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 28 / 31 Bachelor's or higher 4.824842808 High school enrollment 17.87501604 Preschool enrollment 64.42961632 Transportation — Auto Access 92.6344155 Active commuting 46.54176825 Social — 2-parent households 66.99602207 Voting 15.74489927 Neighborhood — Alcohol availability 51.89272424 Park access 21.5193122 Retail density 38.36776594 Supermarket access 40.97266778 Tree canopy 5.51777236 Housing — Homeownership 52.16219684 Housing habitability 24.6888233 Low-inc homeowner severe housing cost burden 17.34890286 Low-inc renter severe housing cost burden 82.47144874 Uncrowded housing 10.95855255 Health Outcomes — Insured adults 8.392146798 Arthritis 41.4 Asthma ER Admissions 18.4 High Blood Pressure 53.6 Cancer (excluding skin)68.9 Asthma 21.6 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 29 / 31 Coronary Heart Disease 40.3 Chronic Obstructive Pulmonary Disease 27.0 Diagnosed Diabetes 27.5 Life Expectancy at Birth 23.5 Cognitively Disabled 24.2 Physically Disabled 50.9 Heart Attack ER Admissions 7.0 Mental Health Not Good 19.7 Chronic Kidney Disease 27.1 Obesity 22.5 Pedestrian Injuries 90.7 Physical Health Not Good 21.1 Stroke 34.3 Health Risk Behaviors — Binge Drinking 50.7 Current Smoker 20.8 No Leisure Time for Physical Activity 23.4 Climate Change Exposures — Wildfire Risk 0.0 SLR Inundation Area 0.0 Children 39.2 Elderly 91.2 English Speaking 19.9 Foreign-born 77.9 Outdoor Workers 50.5 Climate Change Adaptive Capacity — Impervious Surface Cover 77.1 Traffic Density 71.4 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 30 / 31 Traffic Access 46.8 Other Indices — Hardship 86.0 Other Decision Support — 2016 Voting 29.4 7.3. Overall Health & Equity Scores Metric Result for Project Census Tract CalEnviroScreen 4.0 Score for Project Location (a)93.0 Healthy Places Index Score for Project Location (b)19.0 Project Located in a Designated Disadvantaged Community (Senate Bill 535)Yes Project Located in a Low-Income Community (Assembly Bill 1550)Yes 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 Screen Justification Land Use Based on site plan, total Project site is 9.49 acres. Construction: Construction Phases Building Construction, Paving, and Architectural Coating overlap to present a conservative analysis 16758 - Fontana Trailer Yard (Operational LSTs) Detailed Report, 10/23/2025 31 / 31 Construction: Off-Road Equipment T/L/B replaced with Crawler Tractor to accurately calculate disturbance for Site Preparation and Grading phases Standard 8-hour work days Construction: Architectural Coatings SCAQMD Rule 1113 Operations: Vehicle Data Trip Characteristics taken from the Traffic Analysis Operations: Fleet Mix Passenger Car Mix estimated based on CalEEMod default fleet mix and the ratio of the vehicle classes (LDA, LDT1, LDT2, MDV, MCY). Truck Fleet Mix based on 2, 3 and 4 axle trucks Operations: Architectural Coatings SCAQMD Rule 1113 Operations: Energy Use Natural Gas will not be utilized Operations: Refrigerants Beginning 1 January 2025, all new air conditioning equipment may not use refrigerants with a GWP of 750 or greater. 16758-03 AQ & GHG Assessment 36 Almond Avenue Trailer Yard (MCN25-0059) APPENDIX 3: AERMOD LOCALIZED EMISSIONS MODEL OUTPUTS ** Lakes Environmental AERMOD MPI ** **************************************** ** ** AERMOD Input Produced by: ** AERMOD View Ver. 13.0.0 ** Lakes Environmental Software Inc. ** Date: 10/23/2025 ** File: C:\Users\adadabhoy\Desktop\AERMOD\16758‐Fontana Trailer Yard\16758‐Cons LSTs\16758‐Cons LSTs.ADI ** **************************************** ** ** **************************************** ** AERMOD Control Pathway **************************************** ** ** CO STARTING TITLEONE C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 MODELOPT DFAULT CONC AVERTIME 1 8 24 URBANOPT 2195611 County_of_San_Bernardino POLLUTID DPM FLAGPOLE 2.00 RUNORNOT RUN ERRORFIL "16758‐Cons LSTs.err" CO FINISHED ** **************************************** ** AERMOD Source Pathway **************************************** ** ** SO STARTING ** Source Location ** ** Source ID ‐ Type ‐ X Coord. ‐ Y Coord. ** LOCATION VOL1 VOLUME 454390.655 3770343.585 320.560 LOCATION PAREA1 AREAPOLY 454291.840 3770443.314 321.430 ** Source Parameters ** SRCPARAM VOL1 1.0 1.524 46.737 1.400 SRCPARAM PAREA1 0.0000260615 0.000 4 1.000 AREAVERT PAREA1 454291.840 3770443.314 454290.433 3770242.896 AREAVERT PAREA1 454481.805 3770242.293 454482.609 3770443.515 URBANSRC ALL ** Variable Emissions Type: "By Hour / Day (HRDOW)" ** Variable Emission Scenario: "Scenario 1" ** WeekDays: 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 PAREA1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0 EMISFACT PAREA1 HRDOW 0.0 0.0 1.0 1.0 1.0 1.0 EMISFACT PAREA1 HRDOW 1.0 1.0 1.0 1.0 0.0 0.0 EMISFACT PAREA1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0 ** Saturday: EMISFACT PAREA1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0 EMISFACT PAREA1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0 EMISFACT PAREA1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0 EMISFACT PAREA1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0 ** Sunday: EMISFACT PAREA1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0 EMISFACT PAREA1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0 EMISFACT PAREA1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0 EMISFACT PAREA1 HRDOW 0.0 0.0 0.0 0.0 0.0 0.0 SRCGROUP Dust PAREA1 SRCGROUP Exhuast VOL1 SRCGROUP ALL SO FINISHED ** **************************************** ** AERMOD Receptor Pathway **************************************** ** ** RE STARTING INCLUDED "16758‐Cons LSTs.rou" RE FINISHED ** **************************************** ** AERMOD Meteorology Pathway **************************************** ** ** ME STARTING SURFFILE FONT_V11_trimmed.sfc PROFFILE FONT_V11_trimmed.pfl SURFDATA 3102 2016 UAIRDATA 3190 2016 SITEDATA 60712002 2016 PROFBASE 363.0 METERS ME FINISHED ** **************************************** ** AERMOD Output Pathway **************************************** ** ** OU STARTING RECTABLE ALLAVE 1ST RECTABLE 1 1ST RECTABLE 8 1ST RECTABLE 24 1ST PLOTFILE 24 Dust 1ST "16758‐CONS LSTS.AD\Dust 24hr.PLT" 31 PLOTFILE 1 Exhuast 1ST "16758‐CONS LSTS.AD\Exhaust 1hr.PLT" 32 PLOTFILE 8 Exhuast 1ST "16758‐CONS LSTS.AD\Exhaust 8hr.PLT" 33 PLOTFILE 24 Exhuast 1ST "16758‐CONS LSTS.AD\Exhaust 24hr.PLT" 34 SUMMFILE "16758‐Cons LSTs.sum" OU FINISHED *** Message Summary For AERMOD Model Setup *** ‐‐‐‐‐‐‐‐‐ Summary of Total Messages ‐‐‐‐‐‐‐‐ A Total of 0 Fatal Error Message(s) A Total of 2 Warning Message(s) A Total of 0 Informational Message(s) ******** FATAL ERROR MESSAGES ******** *** NONE *** ******** WARNING MESSAGES ******** ME W186 104 MEOPEN: THRESH_1MIN 1‐min ASOS wind speed threshold used 0.50 ME W187 104 MEOPEN: ADJ_U* Option for Stable Low Winds used in AERMET *********************************** *** SETUP Finishes Successfully *** *********************************** *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 1 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** MODEL SETUP OPTIONS SUMMARY *** ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ** Model Options Selected: * Model Uses Regulatory DEFAULT Options * Model Is Setup For Calculation of Average CONCentration Values. * NO GAS DEPOSITION Data Provided. * NO PARTICLE DEPOSITION Data Provided. * Model Uses NO DRY DEPLETION. DDPLETE = F * Model Uses NO WET DEPLETION. WETDPLT = F * Stack‐tip Downwash. * Model Accounts for ELEVated Terrain Effects. * Use Calms Processing Routine. * Use Missing Data Processing Routine. * No Exponential Decay. * Model Uses URBAN Dispersion Algorithm for the SBL for 2 Source(s), for Total of 1 Urban Area(s): Urban Population = 2195611.0 ; Urban Roughness Length = 1.000 m * Urban Roughness Length of 1.0 Meter Used. * ADJ_U* ‐ Use ADJ_U* option for SBL in AERMET * CCVR_Sub ‐ Meteorological data includes CCVR substitutions * TEMP_Sub ‐ Meteorological data includes TEMP substitutions * Model Accepts FLAGPOLE Receptor . Heights. * The User Specified a Pollutant Type of: DPM **Model Calculates 3 Short Term Average(s) of: 1‐HR 8‐HR 24‐HR **This Run Includes: 2 Source(s); 3 Source Group(s); and 129 Receptor(s) with: 0 POINT(s), including 0 POINTCAP(s) and 0 POINTHOR(s) and: 1 VOLUME source(s) and: 1 AREA type source(s) and: 0 LINE source(s) and: 0 RLINE/RLINEXT source(s) and: 0 OPENPIT source(s) and: 0 BUOYANT LINE source(s) with a total of 0 line(s) and: 0 SWPOINT source(s) **Model Set To Continue RUNning After the Setup Testing. **The AERMET Input Meteorological Data Version Date: 22112 **Output Options Selected: Model Outputs Tables of Highest Short Term Values by Receptor (RECTABLE Keyword) Model Outputs External File(s) of High Values for Plotting (PLOTFILE Keyword) Model Outputs Separate Summary File of High Ranked Values (SUMMFILE Keyword) **NOTE: The Following Flags May Appear Following CONC Values: c for Calm Hours m for Missing Hours b for Both Calm and Missing Hours **Misc. Inputs: Base Elev. for Pot. Temp. Profile (m MSL) = 363.00 ; Decay Coef. = 0.000 ; Rot. Angle = 0.0 Emission Units = GRAMS/SEC ; Emission Rate Unit Factor = 0.10000E+07 Output Units = MICROGRAMS/M**3 **Approximate Storage Requirements of Model = 3.6 MB of RAM. **Input Runstream File: aermod.inp **Output Print File: aermod.out **Detailed Error/Message File: 16758‐Cons LSTs.err **File for Summary of Results: 16758‐Cons LSTs.sum *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 2 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** VOLUME SOURCE DATA *** NUMBER EMISSION RATE BASE RELEASE INIT. INIT. URBAN EMISSION RATE AIRCRAFT SOURCE PART. (GRAMS/SEC) X Y ELEV. HEIGHT SY SZ SOURCE SCALAR VARY ID CATS. (METERS) (METERS) (METERS) (METERS) (METERS) (METERS) BY ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ VOL1 0 0.10000E+01 454390.7 3770343.6 320.6 1.52 46.74 1.40 YES HRDOW NO *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 3 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** AREAPOLY SOURCE DATA *** NUMBER EMISSION RATE LOCATION OF AREA BASE RELEASE NUMBER INIT. URBAN EMISSION RATE AIRCRAFT SOURCE PART. (GRAMS/SEC X Y ELEV. HEIGHT OF VERTS. SZ SOURCE SCALAR VARY ID CATS. /METER**2) (METERS) (METERS) (METERS) (METERS) (METERS) BY ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ PAREA1 0 0.26062E‐04 454291.8 3770443.3 321.4 0.00 4 1.00 YES HRDOW NO *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 4 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** SOURCE IDs DEFINING SOURCE GROUPS *** SRCGROUP ID SOURCE IDs ‐‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ DUST PAREA1 , EXHUAST VOL1 , ALL VOL1 , PAREA1 , *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 5 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** SOURCE IDs DEFINED AS URBAN SOURCES *** URBAN ID URBAN POP SOURCE IDs ‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ 2195611. VOL1 , PAREA1 , *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 6 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* * SOURCE EMISSION RATE SCALARS WHICH VARY DIURNALLY AND BY DAY OF WEEK (HRDOW) * SOURCE ID = VOL1 ; SOURCE TYPE = VOLUME : HOUR SCALAR HOUR SCALAR HOUR SCALAR HOUR SCALAR HOUR SCALAR HOUR SCALAR HOUR SCALAR HOUR SCALAR ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ DAY OF WEEK = WEEKDAY 1 .0000E+00 2 .0000E+00 3 .0000E+00 4 .0000E+00 5 .0000E+00 6 .0000E+00 7 .0000E+00 8 .0000E+00 9 .1000E+01 10 .1000E+01 11 .1000E+01 12 .1000E+01 13 .1000E+01 14 .1000E+01 15 .1000E+01 16 .1000E+01 17 .0000E+00 18 .0000E+00 19 .0000E+00 20 .0000E+00 21 .0000E+00 22 .0000E+00 23 .0000E+00 24 .0000E+00 DAY OF WEEK = SATURDAY 1 .0000E+00 2 .0000E+00 3 .0000E+00 4 .0000E+00 5 .0000E+00 6 .0000E+00 7 .0000E+00 8 .0000E+00 9 .0000E+00 10 .0000E+00 11 .0000E+00 12 .0000E+00 13 .0000E+00 14 .0000E+00 15 .0000E+00 16 .0000E+00 17 .0000E+00 18 .0000E+00 19 .0000E+00 20 .0000E+00 21 .0000E+00 22 .0000E+00 23 .0000E+00 24 .0000E+00 DAY OF WEEK = SUNDAY 1 .0000E+00 2 .0000E+00 3 .0000E+00 4 .0000E+00 5 .0000E+00 6 .0000E+00 7 .0000E+00 8 .0000E+00 9 .0000E+00 10 .0000E+00 11 .0000E+00 12 .0000E+00 13 .0000E+00 14 .0000E+00 15 .0000E+00 16 .0000E+00 17 .0000E+00 18 .0000E+00 19 .0000E+00 20 .0000E+00 21 .0000E+00 22 .0000E+00 23 .0000E+00 24 .0000E+00 *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 7 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* * SOURCE EMISSION RATE SCALARS WHICH VARY DIURNALLY AND BY DAY OF WEEK (HRDOW) * SOURCE ID = PAREA1 ; SOURCE TYPE = AREAPOLY : HOUR SCALAR HOUR SCALAR HOUR SCALAR HOUR SCALAR HOUR SCALAR HOUR SCALAR HOUR SCALAR HOUR SCALAR ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ DAY OF WEEK = WEEKDAY 1 .0000E+00 2 .0000E+00 3 .0000E+00 4 .0000E+00 5 .0000E+00 6 .0000E+00 7 .0000E+00 8 .0000E+00 9 .1000E+01 10 .1000E+01 11 .1000E+01 12 .1000E+01 13 .1000E+01 14 .1000E+01 15 .1000E+01 16 .1000E+01 17 .0000E+00 18 .0000E+00 19 .0000E+00 20 .0000E+00 21 .0000E+00 22 .0000E+00 23 .0000E+00 24 .0000E+00 DAY OF WEEK = SATURDAY 1 .0000E+00 2 .0000E+00 3 .0000E+00 4 .0000E+00 5 .0000E+00 6 .0000E+00 7 .0000E+00 8 .0000E+00 9 .0000E+00 10 .0000E+00 11 .0000E+00 12 .0000E+00 13 .0000E+00 14 .0000E+00 15 .0000E+00 16 .0000E+00 17 .0000E+00 18 .0000E+00 19 .0000E+00 20 .0000E+00 21 .0000E+00 22 .0000E+00 23 .0000E+00 24 .0000E+00 DAY OF WEEK = SUNDAY 1 .0000E+00 2 .0000E+00 3 .0000E+00 4 .0000E+00 5 .0000E+00 6 .0000E+00 7 .0000E+00 8 .0000E+00 9 .0000E+00 10 .0000E+00 11 .0000E+00 12 .0000E+00 13 .0000E+00 14 .0000E+00 15 .0000E+00 16 .0000E+00 17 .0000E+00 18 .0000E+00 19 .0000E+00 20 .0000E+00 21 .0000E+00 22 .0000E+00 23 .0000E+00 24 .0000E+00 *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 8 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** DISCRETE CARTESIAN RECEPTORS *** (X‐COORD, Y‐COORD, ZELEV, ZHILL, ZFLAG) (METERS) ( 454512.8, 3770712.4, 326.3, 2731.4, 0.0); ( 454514.9, 3770786.1, 326.9, 2731.4, 0.0); ( 454034.3, 3770517.3, 321.0, 3066.9, 0.0); ( 454048.7, 3770385.9, 318.5, 2731.4, 0.0); ( 454182.3, 3770421.8, 320.2, 2731.4, 0.0); ( 454142.5, 3770420.6, 319.8, 2731.4, 0.0); ( 454625.6, 3770785.7, 327.0, 2731.4, 0.0); ( 454827.1, 3770784.5, 327.9, 2731.4, 0.0); ( 454752.6, 3770566.5, 324.7, 2731.4, 0.0); ( 454835.6, 3770558.6, 325.7, 2731.4, 0.0); ( 454812.4, 3770415.1, 323.3, 2731.4, 0.0); ( 454913.8, 3770480.5, 324.9, 2731.4, 0.0); ( 454925.3, 3770700.8, 327.6, 2731.4, 0.0); ( 454694.0, 3770943.2, 329.2, 2731.4, 0.0); ( 454368.0, 3770918.8, 328.2, 3066.9, 0.0); ( 453794.8, 3770744.2, 324.2, 3066.9, 0.0); ( 453971.9, 3770386.8, 319.4, 2731.4, 0.0); ( 453937.6, 3770445.0, 320.4, 3066.9, 0.0); ( 453953.9, 3770386.8, 319.5, 2731.4, 0.0); ( 453992.1, 3770444.7, 320.3, 2731.4, 0.0); ( 453912.3, 3770386.5, 319.4, 2731.4, 0.0); ( 453880.1, 3770440.5, 320.4, 3066.9, 0.0); ( 453864.7, 3770444.0, 320.4, 3066.9, 0.0); ( 453892.0, 3770343.4, 318.6, 2731.4, 0.0); ( 453845.5, 3770381.3, 319.2, 3066.9, 0.0); ( 453756.1, 3770381.8, 319.0, 3066.9, 0.0); ( 453736.6, 3770343.9, 318.5, 3066.9, 0.0); ( 453828.9, 3770443.9, 320.4, 3066.9, 0.0); ( 453791.0, 3770279.8, 317.6, 2731.4, 0.0); ( 453771.8, 3770281.4, 317.5, 2731.4, 0.0); ( 453656.8, 3770594.1, 322.0, 3066.9, 0.0); ( 453650.8, 3770437.0, 318.6, 3066.9, 0.0); ( 453730.4, 3770758.2, 324.2, 3066.9, 0.0); ( 454061.4, 3770113.9, 314.8, 2731.4, 0.0); ( 453983.2, 3770162.6, 316.1, 2731.4, 0.0); ( 453983.9, 3770095.4, 315.2, 2731.4, 0.0); ( 454129.9, 3770114.5, 315.6, 2731.4, 0.0); ( 454390.9, 3770146.1, 318.0, 2731.4, 0.0); ( 454378.1, 3770242.6, 319.1, 2731.4, 0.0); ( 453628.0, 3770153.7, 315.6, 2731.4, 0.0); ( 453331.2, 3770122.8, 314.9, 3066.9, 0.0); ( 453296.7, 3770270.8, 316.5, 3066.9, 0.0); ( 454635.8, 3770147.2, 318.2, 2731.4, 0.0); ( 454745.0, 3770120.0, 318.6, 2731.4, 0.0); ( 454639.8, 3770088.1, 317.9, 2731.4, 0.0); ( 454856.7, 3770082.3, 319.1, 2731.4, 0.0); ( 454787.6, 3770075.3, 318.5, 2731.4, 0.0); ( 454853.5, 3770149.9, 320.0, 2731.4, 0.0); ( 454867.6, 3770221.9, 321.0, 2731.4, 0.0); ( 454867.3, 3770294.3, 322.2, 2731.4, 0.0); ( 454699.0, 3770289.5, 320.4, 2731.4, 0.0); ( 454630.1, 3770001.8, 316.6, 2731.4, 0.0); ( 454859.7, 3770001.8, 318.2, 2731.4, 0.0); ( 454928.7, 3770010.3, 318.6, 2731.4, 0.0); ( 454545.2, 3770002.4, 316.3, 2731.4, 0.0); ( 454376.7, 3770010.3, 315.8, 2731.4, 0.0); ( 454040.2, 3769981.6, 312.9, 2731.4, 0.0); ( 454914.1, 3770171.5, 320.7, 2731.4, 0.0); ( 454913.5, 3770232.0, 321.5, 2731.4, 0.0); ( 453614.7, 3770780.3, 322.7, 3066.9, 0.0); ( 453305.8, 3770765.1, 322.7, 3066.9, 0.0); ( 454195.5, 3770945.2, 327.2, 3066.9, 0.0); ( 454923.5, 3770771.0, 328.4, 2731.4, 0.0); ( 454923.5, 3771039.0, 332.1, 2731.4, 0.0); ( 454924.0, 3771278.3, 335.5, 3066.9, 0.0); ( 454933.3, 3771200.4, 334.2, 3066.9, 0.0); ( 454799.2, 3771302.4, 335.1, 3066.9, 0.0); ( 454613.3, 3771299.0, 334.7, 3066.9, 0.0); ( 454087.5, 3771276.2, 332.9, 3066.9, 0.0); ( 455732.1, 3771151.8, 338.7, 2731.4, 0.0); ( 455146.8, 3770887.2, 331.8, 2731.4, 0.0); ( 455330.8, 3770872.1, 332.3, 2731.4, 0.0); ( 455325.7, 3770924.5, 332.9, 2731.4, 0.0); ( 455350.2, 3770868.5, 332.5, 2731.4, 0.0); ( 455124.6, 3770415.9, 324.8, 2731.4, 0.0); ( 454838.8, 3769931.0, 316.5, 2731.4, 0.0); ( 454961.0, 3769945.6, 318.1, 2731.4, 0.0); ( 454849.8, 3769882.7, 316.1, 2731.4, 0.0); ( 455044.0, 3769898.6, 317.6, 2731.4, 0.0); ( 455185.2, 3769966.4, 318.8, 2731.4, 0.0); ( 454949.8, 3769855.1, 316.2, 2731.4, 0.0); ( 455121.0, 3769660.8, 314.2, 2731.4, 0.0); ( 455144.0, 3769654.6, 314.4, 2731.4, 0.0); ( 455057.7, 3769795.1, 315.5, 2731.4, 0.0); ( 454950.5, 3769483.4, 311.4, 2731.4, 0.0); ( 455047.1, 3769487.1, 311.8, 2731.4, 0.0); ( 455186.0, 3769487.4, 312.9, 2731.4, 0.0); ( 455228.6, 3769489.3, 313.3, 2731.4, 0.0); ( 454670.6, 3769665.0, 311.7, 2731.4, 0.0); ( 454442.9, 3769677.5, 311.5, 2731.4, 0.0); *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 9 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** DISCRETE CARTESIAN RECEPTORS *** (X‐COORD, Y‐COORD, ZELEV, ZHILL, ZFLAG) (METERS) ( 454817.2, 3769446.6, 309.6, 2731.4, 0.0); ( 457073.4, 3771679.1, 353.7, 2731.4, 0.0); ( 457180.8, 3771676.9, 354.6, 2731.4, 0.0); ( 453294.0, 3769817.9, 310.4, 2731.4, 0.0); ( 453163.5, 3770000.2, 315.1, 3066.9, 0.0); ( 453419.5, 3770001.3, 313.1, 2731.4, 0.0); ( 453310.3, 3770010.7, 313.4, 2731.4, 0.0); ( 452792.8, 3769973.0, 316.3, 3066.9, 0.0); ( 452613.0, 3770098.2, 320.2, 3066.9, 0.0); ( 452566.2, 3770175.9, 319.2, 3066.9, 0.0); ( 452402.2, 3770197.5, 317.9, 3066.9, 0.0); ( 452395.0, 3770047.9, 316.1, 3066.9, 0.0); ( 452636.0, 3769852.9, 316.8, 3066.9, 0.0); ( 452269.8, 3770197.5, 317.6, 3066.9, 0.0); ( 452087.8, 3770201.1, 317.4, 3066.9, 0.0); ( 452365.5, 3769988.9, 315.6, 3066.9, 0.0); ( 452053.2, 3769889.6, 315.2, 3066.9, 0.0); ( 454290.1, 3769974.8, 315.3, 2731.4, 0.0); ( 454539.0, 3769826.6, 313.5, 2731.4, 0.0); ( 452423.7, 3769682.9, 305.6, 3066.9, 0.0); ( 452154.2, 3769692.2, 305.9, 3066.9, 0.0); ( 454912.8, 3770375.1, 323.5, 2731.4, 0.0); ( 454946.7, 3770523.9, 325.9, 2731.4, 0.0); ( 454913.4, 3770360.4, 323.3, 2731.4, 0.0); ( 455329.0, 3770822.7, 331.4, 2731.4, 0.0); ( 455107.7, 3770816.1, 330.1, 2731.4, 0.0); ( 454999.8, 3770834.1, 329.8, 2731.4, 0.0); ( 455329.8, 3770804.8, 331.3, 2731.4, 0.0); ( 455325.1, 3770415.6, 325.9, 2731.4, 0.0); ( 455325.1, 3770367.0, 325.2, 2731.4, 0.0); ( 455322.6, 3770267.3, 323.8, 2731.4, 0.0); ( 455327.6, 3770519.1, 327.5, 2731.4, 0.0); ( 455322.9, 3770561.4, 328.0, 2731.4, 0.0); ( 455330.7, 3770603.2, 328.5, 2731.4, 0.0); ( 454959.0, 3770572.5, 326.7, 2731.4, 0.0); ( 455127.1, 3770559.5, 327.0, 2731.4, 0.0); ( 453158.7, 3770937.9, 327.8, 3066.9, 0.0); ( 452421.7, 3770910.5, 322.7, 3066.9, 0.0); ( 454556.7, 3771053.1, 330.2, 3066.9, 0.0); *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 10 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** METEOROLOGICAL DAYS SELECTED FOR PROCESSING *** (1=YES; 0=NO) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 NOTE: METEOROLOGICAL DATA ACTUALLY PROCESSED WILL ALSO DEPEND ON WHAT IS INCLUDED IN THE DATA FILE. *** UPPER BOUND OF FIRST THROUGH FIFTH WIND SPEED CATEGORIES *** (METERS/SEC) 1.54, 3.09, 5.14, 8.23, 10.80, *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 11 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** UP TO THE FIRST 24 HOURS OF METEOROLOGICAL DATA *** Surface file: FONT_V11_trimmed.sfc Met Version: 22112 Profile file: FONT_V11_trimmed.pfl Surface format: FREE Profile format: FREE Surface station no.: 3102 Upper air station no.: 3190 Name: UNKNOWN Name: UNKNOWN Year: 2016 Year: 2016 First 24 hours of scalar data YR MO DY JDY HR H0 U* W* DT/DZ ZICNV ZIMCH M‐O LEN Z0 BOWEN ALBEDO REF WS WD HT REF TA HT ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 16 01 01 1 01 ‐33.6 0.350 ‐9.000 ‐9.000 ‐999. 500. 135.0 0.09 1.19 1.00 4.31 38. 10.0 284.3 9.0 16 01 01 1 02 ‐45.1 0.469 ‐9.000 ‐9.000 ‐999. 771. 242.2 0.09 1.19 1.00 5.71 44. 10.0 284.1 9.0 16 01 01 1 03 ‐36.8 0.383 ‐9.000 ‐9.000 ‐999. 574. 161.1 0.09 1.19 1.00 4.69 43. 10.0 284.1 9.0 16 01 01 1 04 ‐35.3 0.367 ‐9.000 ‐9.000 ‐999. 535. 148.5 0.09 1.19 1.00 4.52 41. 10.0 283.9 9.0 16 01 01 1 05 ‐20.4 0.212 ‐9.000 ‐9.000 ‐999. 251. 49.2 0.09 1.19 1.00 2.66 30. 10.0 283.6 9.0 16 01 01 1 06 ‐4.3 0.090 ‐9.000 ‐9.000 ‐999. 79. 15.1 0.09 1.19 1.00 1.18 346. 10.0 282.2 9.0 16 01 01 1 07 ‐1.7 0.067 ‐9.000 ‐9.000 ‐999. 42. 15.9 0.12 1.19 1.00 0.59 194. 10.0 280.6 9.0 16 01 01 1 08 ‐1.3 0.059 ‐9.000 ‐9.000 ‐999. 34. 13.4 0.08 1.19 0.53 0.69 14. 10.0 280.7 9.0 16 01 01 1 09 35.0 0.124 0.432 0.007 80. 105. ‐4.7 0.07 1.19 0.31 1.08 255. 10.0 282.7 9.0 16 01 01 1 10 86.7 0.127 0.917 0.005 310. 108. ‐2.0 0.07 1.19 0.24 0.95 253. 10.0 284.6 9.0 16 01 01 1 11 122.7 0.147 1.230 0.005 530. 136. ‐2.3 0.12 1.19 0.21 0.98 215. 10.0 286.4 9.0 16 01 01 1 12 140.5 0.207 1.381 0.005 653. 226. ‐5.5 0.16 1.19 0.20 1.44 135. 10.0 288.6 9.0 16 01 01 1 13 138.6 0.230 1.623 0.005 1076. 264. ‐7.6 0.10 1.19 0.20 1.94 90. 10.0 289.0 9.0 16 01 01 1 14 96.7 0.230 1.524 0.010 1276. 265. ‐11.0 0.10 1.19 0.22 2.04 80. 10.0 289.4 9.0 16 01 01 1 15 66.0 0.204 1.376 0.011 1375. 221. ‐11.1 0.10 1.19 0.25 1.81 86. 10.0 289.8 9.0 16 01 01 1 16 23.8 0.193 0.983 0.012 1392. 204. ‐26.4 0.10 1.19 0.34 1.89 82. 10.0 289.8 9.0 16 01 01 1 17 ‐8.6 0.134 ‐9.000 ‐9.000 ‐999. 119. 24.5 0.09 1.19 0.62 1.73 58. 10.0 289.0 9.0 16 01 01 1 18 ‐7.3 0.119 ‐9.000 ‐9.000 ‐999. 98. 19.8 0.09 1.19 1.00 1.55 34. 10.0 287.0 9.0 16 01 01 1 19 ‐8.1 0.124 ‐9.000 ‐9.000 ‐999. 105. 20.5 0.08 1.19 1.00 1.66 20. 10.0 285.1 9.0 16 01 01 1 20 ‐4.0 0.089 ‐9.000 ‐9.000 ‐999. 64. 15.6 0.13 1.19 1.00 1.05 91. 10.0 284.6 9.0 16 01 01 1 21 ‐3.4 0.082 ‐9.000 ‐9.000 ‐999. 56. 14.0 0.09 1.19 1.00 1.04 56. 10.0 283.6 9.0 16 01 01 1 22 ‐2.5 0.073 ‐9.000 ‐9.000 ‐999. 47. 13.5 0.09 1.19 1.00 0.84 53. 10.0 282.8 9.0 16 01 01 1 23 ‐4.2 0.089 ‐9.000 ‐9.000 ‐999. 64. 14.9 0.09 1.19 1.00 1.16 44. 10.0 282.7 9.0 16 01 01 1 24 ‐2.4 0.072 ‐9.000 ‐9.000 ‐999. 47. 13.6 0.09 1.19 1.00 0.83 59. 10.0 282.1 9.0 First hour of profile data YR MO DY HR HEIGHT F WDIR WSPD AMB_TMP sigmaA sigmaW sigmaV 16 01 01 01 9.0 0 ‐999. ‐99.00 284.3 99.0 ‐99.00 ‐99.00 16 01 01 01 10.0 1 38. 4.31 ‐999.0 99.0 ‐99.00 ‐99.00 F indicates top of profile (=1) or below (=0) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 12 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 1‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: DUST *** INCLUDING SOURCE(S): PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 60.44773 (17011216) 454514.86 3770786.06 48.38435 (17011216) 454034.35 3770517.35 30.59295 (19122516) 454048.71 3770385.92 77.11021 (20122416) 454182.29 3770421.75 116.76158 (20122416) 454142.55 3770420.62 91.39896 (20122416) 454625.62 3770785.69 28.69761 (17010316) 454827.07 3770784.47 30.18914 (19120516) 454752.59 3770566.53 64.25292 (19120516) 454835.61 3770558.60 49.12695 (16121216) 454812.42 3770415.14 59.34161 (16121216) 454913.75 3770480.46 49.83501 (16121216) 454925.35 3770700.83 37.40260 (19120516) 454693.99 3770943.18 15.65962 (16010516) 454368.01 3770918.76 18.95541 (16010515) 453794.80 3770744.18 11.82861 (19122516) 453971.91 3770386.76 58.49252 (20122416) 453937.64 3770444.98 25.55804 (20122416) 453953.91 3770386.77 55.21246 (20122416) 453992.13 3770444.71 30.05779 (20122416) 453912.32 3770386.53 48.75628 (20122416) 453880.11 3770440.50 24.06756 (20122416) 453864.72 3770443.99 21.69560 (20122416) 453892.00 3770343.38 51.70810 (20122416) 453845.52 3770381.27 41.72369 (20122416) 453756.12 3770381.81 33.50218 (20122416) 453736.62 3770343.88 35.94102 (20122416) 453828.86 3770443.92 20.00400 (20122416) 453790.96 3770279.76 34.79904 (20122416) 453771.85 3770281.37 33.69811 (20122416) 453656.79 3770594.13 10.77779 (19120309) 453650.82 3770437.04 15.64825 (20122416) 453730.36 3770758.17 10.36927 (19122516) 454061.44 3770113.91 34.58195 (17020315) 453983.24 3770162.63 24.28242 (17010416) 453983.88 3770095.38 26.47842 (16112416) 454129.86 3770114.50 71.15756 (19011416) 454390.90 3770146.06 190.36758 (22120216) 454378.15 3770242.63 709.76799 (22120216) 453628.04 3770153.73 10.89534 (19122616) 453331.19 3770122.83 7.04542 (17111609) 453296.71 3770270.82 14.25442 (20122416) 454635.77 3770147.25 61.57492 (19122015) 454744.96 3770119.96 36.21583 (19122015) 454639.83 3770088.09 47.85479 (19011615) 454856.74 3770082.33 26.08679 (16011816) 454787.57 3770075.32 29.42355 (19122015) 454853.55 3770149.91 48.68309 (16122116) 454867.57 3770221.95 52.03981 (16122116) 454867.26 3770294.31 31.50729 (22121516) 454698.95 3770289.53 79.17400 (16122116) 454630.12 3770001.75 33.49491 (19122016) 454859.72 3770001.75 21.03054 (19122015) 454928.73 3770010.30 17.22143 (19122015) 454545.24 3770002.36 97.72199 (22120216) 454376.71 3770010.30 83.02916 (19122316) 454040.24 3769981.60 46.40330 (19011416) 454914.07 3770171.51 48.43654 (16122116) 454913.46 3770231.96 42.77503 (16122116) 453614.68 3770780.33 9.65686 (19120309) 453305.84 3770765.12 8.67419 (19120309) 454195.51 3770945.23 35.00894 (22123016) 454923.46 3770771.03 39.56901 (19120516) 454923.46 3771038.97 21.02678 (17010316) 454924.00 3771278.30 8.67542 (16010516) 454933.34 3771200.44 9.00169 (17010316) 454799.23 3771302.36 7.29236 (16112809) 454613.27 3771298.98 15.27791 (17011216) 454087.50 3771276.16 18.23550 (22123016) 455732.13 3771151.77 8.21066 (22122916) 455146.83 3770887.16 23.10441 (19120516) 455330.77 3770872.07 14.70915 (22122916) 455325.74 3770924.52 14.82939 (22122916) 455350.18 3770868.48 13.66090 (22122916) 455124.63 3770415.95 29.09273 (22121516) 454838.81 3769930.96 21.05756 (17103016) 454960.97 3769945.62 15.65397 (19122015) 454849.81 3769882.70 17.26017 (17103016) 455044.03 3769898.59 12.68119 (19122015) 455185.16 3769966.42 13.40271 (16122116) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 13 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 1‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: DUST *** INCLUDING SOURCE(S): PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 15.53558 (17103016) 455120.97 3769660.75 9.29963 (19011615) 455143.99 3769654.61 9.06141 (19011615) 455057.73 3769795.12 11.68987 (17103016) 454950.48 3769483.39 7.55910 (17111314) 455047.08 3769487.06 7.83573 (17111309) 455186.02 3769487.43 7.88610 (20020509) 455228.61 3769489.33 7.66646 (20020509) 454670.56 3769664.99 39.30846 (22120216) 454442.93 3769677.47 43.83739 (19122316) 454817.24 3769446.56 12.92767 (22120216) 457073.40 3771679.08 3.98500 (17022709) 457180.76 3771676.87 3.77770 (17010912) 453293.96 3769817.93 6.68592 (22012509) 453163.51 3770000.16 6.33939 (17111609) 453419.51 3770001.32 6.88078 (22012509) 453310.35 3770010.68 6.70421 (17111609) 452792.85 3769973.03 5.39137 (17111609) 452612.97 3770098.22 5.94969 (17020209) 452566.21 3770175.93 6.37763 (17020209) 452402.16 3770197.51 6.07456 (17020209) 452394.97 3770047.86 5.24885 (17020209) 452636.00 3769852.88 4.97217 (17111609) 452269.78 3770197.51 5.81271 (17020209) 452087.75 3770201.11 5.49041 (17020209) 452365.47 3769988.86 4.64324 (17020209) 452053.21 3769889.57 4.01046 (17111609) 454290.08 3769974.82 62.70226 (20122816) 454539.03 3769826.60 76.55966 (22120216) 452423.72 3769682.87 4.11216 (17111609) 452154.23 3769692.25 4.08839 (17111609) 454912.82 3770375.11 43.63106 (22121516) 454946.69 3770523.91 47.08437 (16121216) 454913.41 3770360.45 42.81945 (22121516) 455329.00 3770822.74 12.13419 (22122916) 455107.72 3770816.10 21.85402 (19120516) 454999.84 3770834.08 32.10798 (19120516) 455329.83 3770804.76 10.68607 (22122916) 455325.06 3770415.64 21.68639 (22121516) 455325.06 3770367.01 19.02844 (22121516) 455322.57 3770267.26 8.03471 (19092716) 455327.56 3770519.13 14.27755 (16120616) 455322.94 3770561.45 15.48755 (16121216) 455330.69 3770603.23 18.12058 (16121216) 454959.01 3770572.49 40.54288 (16121216) 455127.10 3770559.48 29.16837 (16121216) 453158.66 3770937.93 7.90983 (19120309) 452421.67 3770910.46 4.69023 (16122216) 454556.71 3771053.14 24.10272 (17011216) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 14 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 1‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: EXHUAST *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 47.07626 (17011216) 454514.86 3770786.06 37.44704 (17011216) 454034.35 3770517.35 20.58110 (17012013) 454048.71 3770385.92 66.98768 (20122416) 454182.29 3770421.75 65.73728 (20122416) 454142.55 3770420.62 57.19451 (20122416) 454625.62 3770785.69 24.47208 (17010316) 454827.07 3770784.47 26.17182 (19120516) 454752.59 3770566.53 58.55970 (19120516) 454835.61 3770558.60 38.97239 (16121216) 454812.42 3770415.14 52.23299 (22121516) 454913.75 3770480.46 39.98146 (16121216) 454925.35 3770700.83 32.23492 (19120516) 454693.99 3770943.18 13.83839 (16010516) 454368.01 3770918.76 15.59072 (16010515) 453794.80 3770744.18 7.32628 (19122516) 453971.91 3770386.76 50.70681 (20122416) 453937.64 3770444.98 20.46817 (20122416) 453953.91 3770386.77 47.85534 (20122416) 453992.13 3770444.71 22.88494 (20122416) 453912.32 3770386.53 42.23595 (20122416) 453880.11 3770440.50 19.86291 (20122416) 453864.72 3770443.99 18.22006 (20122416) 453892.00 3770343.38 48.50165 (20122416) 453845.52 3770381.27 36.36148 (20122416) 453756.12 3770381.81 28.80337 (20122416) 453736.62 3770343.88 31.56739 (20122416) 453828.86 3770443.92 17.12261 (20122416) 453790.96 3770279.76 29.39417 (20122416) 453771.85 3770281.37 28.51483 (20122416) 453656.79 3770594.13 5.54068 (20011712) 453650.82 3770437.04 13.94070 (20122416) 453730.36 3770758.17 6.34520 (19122516) 454061.44 3770113.91 25.71093 (19011416) 453983.24 3770162.63 19.72323 (19022116) 453983.88 3770095.38 20.05500 (16112416) 454129.86 3770114.50 60.31843 (19011416) 454390.90 3770146.06 120.14512 (19011516) 454378.15 3770242.63 290.36389 (19011616) 453628.04 3770153.73 8.74452 (19122616) 453331.19 3770122.83 3.93612 (19122616) 453296.71 3770270.82 11.54572 (20122416) 454635.77 3770147.25 47.41813 (17103016) 454744.96 3770119.96 27.76845 (16011816) 454639.83 3770088.09 37.08141 (17103016) 454856.74 3770082.33 21.68529 (16011816) 454787.57 3770075.32 20.32703 (16011815) 454853.55 3770149.91 28.50341 (16011816) 454867.57 3770221.95 21.91214 (16122116) 454867.26 3770294.31 24.85555 (22121516) 454698.95 3770289.53 42.59144 (22121516) 454630.12 3770001.75 22.29870 (19122016) 454859.72 3770001.75 16.00573 (17103016) 454928.73 3770010.30 12.22164 (16011816) 454545.24 3770002.36 52.02545 (19011616) 454376.71 3770010.30 56.02168 (19011516) 454040.24 3769981.60 38.72954 (19011416) 454914.07 3770171.51 19.95082 (16011816) 454913.46 3770231.96 17.94209 (16122116) 453614.68 3770780.33 4.82439 (19122516) 453305.84 3770765.12 2.88092 (20011712) 454195.51 3770945.23 30.30743 (22123016) 454923.46 3770771.03 32.18336 (19120516) 454923.46 3771038.97 15.49503 (17010316) 454924.00 3771278.30 7.14622 (16010516) 454933.34 3771200.44 7.94153 (17010316) 454799.23 3771302.36 4.52498 (19021412) 454613.27 3771298.98 10.64784 (17011216) 454087.50 3771276.16 14.57946 (22123016) 455732.13 3771151.77 6.13146 (22122916) 455146.83 3770887.16 18.50712 (19120516) 455330.77 3770872.07 11.80691 (22122916) 455325.74 3770924.52 11.61759 (22122916) 455350.18 3770868.48 11.12710 (22122916) 455124.63 3770415.95 27.73301 (22121516) 454838.81 3769930.96 16.49244 (17103016) 454960.97 3769945.62 10.60348 (17103016) 454849.81 3769882.70 13.58680 (17103016) 455044.03 3769898.59 8.04826 (16011815) 455185.16 3769966.42 10.67143 (16011816) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 15 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 1‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: EXHUAST *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 11.90983 (17103016) 455120.97 3769660.75 6.75757 (17103016) 455143.99 3769654.61 6.62605 (17103016) 455057.73 3769795.12 8.95740 (17103016) 454950.48 3769483.39 3.98411 (19122014) 455047.08 3769487.06 4.08557 (19122016) 455186.02 3769487.43 3.75523 (19011615) 455228.61 3769489.33 4.08966 (17103016) 454670.56 3769664.99 16.82543 (19011616) 454442.93 3769677.47 20.04281 (19011516) 454817.24 3769446.56 7.74438 (19011616) 457073.40 3771679.08 1.56653 (17112716) 457180.76 3771676.87 1.45524 (17112716) 453293.96 3769817.93 3.80590 (19022116) 453163.51 3770000.16 3.79780 (19122616) 453419.51 3770001.32 5.26493 (19122616) 453310.35 3770010.68 4.77055 (19122616) 452792.85 3769973.03 2.11226 (20040909) 452612.97 3770098.22 1.83843 (20122416) 452566.21 3770175.93 3.46619 (20122416) 452402.16 3770197.51 3.57825 (20122416) 452394.97 3770047.86 1.63100 (16120909) 452636.00 3769852.88 2.05729 (19122616) 452269.78 3770197.51 3.31886 (20122416) 452087.75 3770201.11 3.04800 (20122416) 452365.47 3769988.86 1.54518 (17020609) 452053.21 3769889.57 1.42290 (17020609) 454290.08 3769974.82 40.71062 (20122816) 454539.03 3769826.60 27.74143 (19011616) 452423.72 3769682.87 1.58137 (19122616) 452154.23 3769692.25 1.39184 (19122616) 454912.82 3770375.11 45.74468 (22121516) 454946.69 3770523.91 36.49467 (16121216) 454913.41 3770360.45 43.61897 (22121516) 455329.00 3770822.74 10.47099 (22122916) 455107.72 3770816.10 18.70911 (19120516) 454999.84 3770834.08 25.62514 (19120516) 455329.83 3770804.76 9.60338 (22122916) 455325.06 3770415.64 19.58226 (22121516) 455325.06 3770367.01 16.92446 (22121516) 455322.57 3770267.26 6.03224 (19111916) 455327.56 3770519.13 10.48438 (22121516) 455322.94 3770561.45 12.20938 (16121216) 455330.69 3770603.23 13.30657 (16121216) 454959.01 3770572.49 31.17364 (16121216) 455127.10 3770559.48 21.76844 (16121216) 453158.66 3770937.93 2.25770 (17012013) 452421.67 3770910.46 1.66536 (16121309) 454556.71 3771053.14 17.49464 (17011216) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 16 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 1‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 107.52399 (17011216) 454514.86 3770786.06 85.83139 (17011216) 454034.35 3770517.35 50.40990 (19122516) 454048.71 3770385.92 144.09789 (20122416) 454182.29 3770421.75 182.49886 (20122416) 454142.55 3770420.62 148.59348 (20122416) 454625.62 3770785.69 53.16969 (17010316) 454827.07 3770784.47 56.36096 (19120516) 454752.59 3770566.53 122.81261 (19120516) 454835.61 3770558.60 88.09934 (16121216) 454812.42 3770415.14 109.29279 (16121216) 454913.75 3770480.46 89.81646 (16121216) 454925.35 3770700.83 69.63751 (19120516) 454693.99 3770943.18 29.49801 (16010516) 454368.01 3770918.76 34.54613 (16010515) 453794.80 3770744.18 19.15489 (19122516) 453971.91 3770386.76 109.19933 (20122416) 453937.64 3770444.98 46.02622 (20122416) 453953.91 3770386.77 103.06779 (20122416) 453992.13 3770444.71 52.94274 (20122416) 453912.32 3770386.53 90.99223 (20122416) 453880.11 3770440.50 43.93048 (20122416) 453864.72 3770443.99 39.91566 (20122416) 453892.00 3770343.38 100.20974 (20122416) 453845.52 3770381.27 78.08517 (20122416) 453756.12 3770381.81 62.30555 (20122416) 453736.62 3770343.88 67.50841 (20122416) 453828.86 3770443.92 37.12661 (20122416) 453790.96 3770279.76 64.19321 (20122416) 453771.85 3770281.37 62.21294 (20122416) 453656.79 3770594.13 14.46688 (20011712) 453650.82 3770437.04 29.58895 (20122416) 453730.36 3770758.17 16.71448 (19122516) 454061.44 3770113.91 59.33570 (16112416) 453983.24 3770162.63 43.14478 (19022116) 453983.88 3770095.38 46.53341 (16112416) 454129.86 3770114.50 131.47599 (19011416) 454390.90 3770146.06 245.72684 (19122316) 454378.15 3770242.63 861.14001 (19011616) 453628.04 3770153.73 19.63986 (19122616) 453331.19 3770122.83 9.41213 (20040909) 453296.71 3770270.82 25.80014 (20122416) 454635.77 3770147.25 102.32749 (17103016) 454744.96 3770119.96 62.19542 (16011816) 454639.83 3770088.09 82.48965 (17103016) 454856.74 3770082.33 47.77208 (16011816) 454787.57 3770075.32 48.58760 (19122015) 454853.55 3770149.91 68.16902 (16122116) 454867.57 3770221.95 73.95195 (16122116) 454867.26 3770294.31 56.36284 (22121516) 454698.95 3770289.53 117.06720 (16122116) 454630.12 3770001.75 55.79361 (19122016) 454859.72 3770001.75 34.90963 (17103016) 454928.73 3770010.30 28.50658 (19122015) 454545.24 3770002.36 116.89517 (19011616) 454376.71 3770010.30 114.80946 (19011516) 454040.24 3769981.60 85.13284 (19011416) 454914.07 3770171.51 67.62870 (16122116) 454913.46 3770231.96 60.71712 (16122116) 453614.68 3770780.33 12.63755 (19122516) 453305.84 3770765.12 9.34220 (19120309) 454195.51 3770945.23 65.31637 (22123016) 454923.46 3770771.03 71.75237 (19120516) 454923.46 3771038.97 36.52181 (17010316) 454924.00 3771278.30 15.82164 (16010516) 454933.34 3771200.44 16.94322 (17010316) 454799.23 3771302.36 10.92581 (19021412) 454613.27 3771298.98 25.92575 (17011216) 454087.50 3771276.16 32.81496 (22123016) 455732.13 3771151.77 14.34212 (22122916) 455146.83 3770887.16 41.61153 (19120516) 455330.77 3770872.07 26.51606 (22122916) 455325.74 3770924.52 26.44698 (22122916) 455350.18 3770868.48 24.78800 (22122916) 455124.63 3770415.95 56.82575 (22121516) 454838.81 3769930.96 37.55000 (17103016) 454960.97 3769945.62 25.49802 (19122015) 454849.81 3769882.70 30.84698 (17103016) 455044.03 3769898.59 20.58254 (19122015) 455185.16 3769966.42 24.04572 (16011816) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 17 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 1‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 27.44541 (17103016) 455120.97 3769660.75 15.83103 (17103016) 455143.99 3769654.61 15.60021 (17103016) 455057.73 3769795.12 20.64727 (17103016) 454950.48 3769483.39 11.39909 (19122014) 455047.08 3769487.06 10.59923 (19122016) 455186.02 3769487.43 9.61623 (19011615) 455228.61 3769489.33 10.58251 (19011615) 454670.56 3769664.99 41.99716 (22120216) 454442.93 3769677.47 56.49448 (19122316) 454817.24 3769446.56 16.61220 (19011616) 457073.40 3771679.08 4.21474 (17010912) 457180.76 3771676.87 4.17887 (19011109) 453293.96 3769817.93 8.97338 (19022116) 453163.51 3770000.16 8.91079 (19122616) 453419.51 3770001.32 12.04927 (19122616) 453310.35 3770010.68 11.17427 (19122616) 452792.85 3769973.03 6.16476 (17020609) 452612.97 3770098.22 6.35891 (17020209) 452566.21 3770175.93 7.08203 (20122416) 452402.16 3770197.51 7.70880 (20122416) 452394.97 3770047.86 5.61012 (17020209) 452636.00 3769852.88 5.35090 (17111609) 452269.78 3770197.51 7.21859 (20122416) 452087.75 3770201.11 6.74615 (20122416) 452365.47 3769988.86 5.20594 (17020609) 452053.21 3769889.57 4.86767 (17020609) 454290.08 3769974.82 103.41289 (20122816) 454539.03 3769826.60 81.25997 (22120216) 452423.72 3769682.87 4.80630 (16010510) 452154.23 3769692.25 4.41261 (17122209) 454912.82 3770375.11 89.37574 (22121516) 454946.69 3770523.91 83.57904 (16121216) 454913.41 3770360.45 86.43842 (22121516) 455329.00 3770822.74 22.60519 (22122916) 455107.72 3770816.10 40.56313 (19120516) 454999.84 3770834.08 57.73312 (19120516) 455329.83 3770804.76 20.28945 (22122916) 455325.06 3770415.64 41.26866 (22121516) 455325.06 3770367.01 35.95290 (22121516) 455322.57 3770267.26 14.01702 (19092716) 455327.56 3770519.13 23.63446 (16120616) 455322.94 3770561.45 27.69693 (16121216) 455330.69 3770603.23 31.42715 (16121216) 454959.01 3770572.49 71.71652 (16121216) 455127.10 3770559.48 50.93681 (16121216) 453158.66 3770937.93 8.47254 (19120309) 452421.67 3770910.46 5.04712 (16122216) 454556.71 3771053.14 41.59736 (17011216) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 18 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 8‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: DUST *** INCLUDING SOURCE(S): PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 14.34364 (17011016) 454514.86 3770786.06 11.33925 (17011016) 454034.35 3770517.35 8.14007 (22021516) 454048.71 3770385.92 14.64033 (19122616) 454182.29 3770421.75 27.31545 (16122016) 454142.55 3770420.62 19.94470 (16122016) 454625.62 3770785.69 8.88447 (17010316) 454827.07 3770784.47 6.63059 (19122416) 454752.59 3770566.53 18.43500 (20012116) 454835.61 3770558.60 13.43900 (20012116) 454812.42 3770415.14 14.76328 (19120916) 454913.75 3770480.46 10.55050 (19051516) 454925.35 3770700.83 7.51627 (20012116) 454693.99 3770943.18 5.11648 (22110816) 454368.01 3770918.76 5.62438 (16010616) 453794.80 3770744.18 3.13908 (19122516) 453971.91 3770386.76 10.00831 (19122616) 453937.64 3770444.98 6.37161 (19013116) 453953.91 3770386.77 9.26977 (19122616) 453992.13 3770444.71 7.91135 (16122016) 453912.32 3770386.53 7.88164 (19122616) 453880.11 3770440.50 5.44663 (19013116) 453864.72 3770443.99 5.13733 (19013116) 453892.00 3770343.38 9.30959 (19122616) 453845.52 3770381.27 6.47197 (19122616) 453756.12 3770381.81 4.95681 (19122616) 453736.62 3770343.88 5.62536 (19122616) 453828.86 3770443.92 4.64246 (19013116) 453790.96 3770279.76 7.26796 (19122616) 453771.85 3770281.37 6.84957 (19122616) 453656.79 3770594.13 2.51707 (19120316) 453650.82 3770437.04 2.92089 (19013116) 453730.36 3770758.17 2.68248 (19122516) 454061.44 3770113.91 11.64620 (16102416) 453983.24 3770162.63 8.96072 (22121216) 453983.88 3770095.38 8.09245 (22121216) 454129.86 3770114.50 18.84571 (19101116) 454390.90 3770146.06 57.51724 (22120216) 454378.15 3770242.63 373.24288 (22120216) 453628.04 3770153.73 3.44569 (19122616) 453331.19 3770122.83 2.07177 (19122616) 453296.71 3770270.82 2.65608 (19122616) 454635.77 3770147.25 19.37329 (19122016) 454744.96 3770119.96 12.28080 (16012716) 454639.83 3770088.09 15.09301 (19122016) 454856.74 3770082.33 8.15188 (16012716) 454787.57 3770075.32 9.25779 (16012716) 454853.55 3770149.91 8.91945 (16012716) 454867.57 3770221.95 9.09301 (17112116) 454867.26 3770294.31 10.56348 (22122916) 454698.95 3770289.53 24.25235 (19092716) 454630.12 3770001.75 10.46411 (19052316) 454859.72 3770001.75 6.24624 (16012716) 454928.73 3770010.30 5.92120 (16012716) 454545.24 3770002.36 16.78177 (22120216) 454376.71 3770010.30 15.49156 (22120216) 454040.24 3769981.60 10.27001 (19101116) 454914.07 3770171.51 7.10401 (17112116) 454913.46 3770231.96 7.75826 (17121316) 453614.68 3770780.33 2.02481 (19120316) 453305.84 3770765.12 1.64763 (19120316) 454195.51 3770945.23 5.90021 (22123016) 454923.46 3770771.03 6.86777 (19122416) 454923.46 3771038.97 4.43994 (17010316) 454924.00 3771278.30 3.09603 (16120516) 454933.34 3771200.44 3.28756 (17010316) 454799.23 3771302.36 2.43446 (17010316) 454613.27 3771298.98 2.72693 (17011016) 454087.50 3771276.16 2.69027 (22123016) 455732.13 3771151.77 1.67863 (22122916) 455146.83 3770887.16 3.62742 (19122416) 455330.77 3770872.07 3.05542 (20012116) 455325.74 3770924.52 2.84689 (19030816) 455350.18 3770868.48 3.04810 (19021516) 455124.63 3770415.95 5.72734 (19120916) 454838.81 3769930.96 4.42204 (16012716) 454960.97 3769945.62 4.77072 (16012716) 454849.81 3769882.70 3.76827 (19122016) 455044.03 3769898.59 4.02377 (16012716) 455185.16 3769966.42 3.87250 (16012716) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 19 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 8‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: DUST *** INCLUDING SOURCE(S): PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 3.39273 (16012716) 455120.97 3769660.75 2.29108 (19011616) 455143.99 3769654.61 2.26474 (19011616) 455057.73 3769795.12 2.95379 (16012716) 454950.48 3769483.39 1.87576 (17111316) 455047.08 3769487.06 1.69268 (17111316) 455186.02 3769487.43 1.53815 (19011616) 455228.61 3769489.33 1.70674 (19011616) 454670.56 3769664.99 6.15545 (22120216) 454442.93 3769677.47 5.47967 (19122316) 454817.24 3769446.56 2.71503 (22120216) 457073.40 3771679.08 0.82298 (19012316) 457180.76 3771676.87 0.82295 (19012316) 453293.96 3769817.93 1.42071 (22121216) 453163.51 3770000.16 1.43447 (19122616) 453419.51 3770001.32 1.53186 (19122616) 453310.35 3770010.68 1.59074 (19122616) 452792.85 3769973.03 1.04967 (19122616) 452612.97 3770098.22 1.09565 (19122616) 452566.21 3770175.93 1.26984 (19122616) 452402.16 3770197.51 1.21870 (19122616) 452394.97 3770047.86 0.90023 (19122616) 452636.00 3769852.88 0.88834 (19122616) 452269.78 3770197.51 1.14894 (19122616) 452087.75 3770201.11 1.07117 (19122616) 452365.47 3769988.86 0.80375 (19122616) 452053.21 3769889.57 0.68389 (16021616) 454290.08 3769974.82 13.72642 (19123016) 454539.03 3769826.60 10.96938 (22120216) 452423.72 3769682.87 0.69287 (16012216) 452154.23 3769692.25 0.64443 (19122616) 454912.82 3770375.11 10.44111 (19120916) 454946.69 3770523.91 9.25673 (17032216) 454913.41 3770360.45 10.09389 (19120916) 455329.00 3770822.74 3.34757 (19021516) 455107.72 3770816.10 4.30180 (19030816) 454999.84 3770834.08 5.38771 (19122416) 455329.83 3770804.76 3.32498 (19021516) 455325.06 3770415.64 3.60080 (19120916) 455325.06 3770367.01 3.27950 (17121816) 455322.57 3770267.26 3.02135 (22122916) 455327.56 3770519.13 3.31671 (19051516) 455322.94 3770561.45 3.41614 (19051516) 455330.69 3770603.23 3.18538 (19051516) 454959.01 3770572.49 8.75754 (17032216) 455127.10 3770559.48 5.34379 (17032216) 453158.66 3770937.93 1.36047 (19120316) 452421.67 3770910.46 0.97568 (19120316) 454556.71 3771053.14 4.94393 (17011016) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 20 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 8‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: EXHUAST *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 13.10689 (17011016) 454514.86 3770786.06 10.24311 (17011016) 454034.35 3770517.35 5.16569 (20041016) 454048.71 3770385.92 9.94904 (19122616) 454182.29 3770421.75 14.88729 (20041016) 454142.55 3770420.62 11.92922 (19013116) 454625.62 3770785.69 7.20623 (22110816) 454827.07 3770784.47 4.88917 (19122416) 454752.59 3770566.53 13.60579 (20012116) 454835.61 3770558.60 10.51594 (20012116) 454812.42 3770415.14 13.11364 (19051516) 454913.75 3770480.46 9.05656 (19051516) 454925.35 3770700.83 5.84599 (19011716) 454693.99 3770943.18 4.11632 (22110816) 454368.01 3770918.76 4.66448 (16010616) 453794.80 3770744.18 1.84827 (19122516) 453971.91 3770386.76 7.02889 (20122416) 453937.64 3770444.98 4.38689 (19013116) 453953.91 3770386.77 6.60834 (20122416) 453992.13 3770444.71 5.25238 (19013116) 453912.32 3770386.53 5.78978 (20122416) 453880.11 3770440.50 3.73790 (19013116) 453864.72 3770443.99 3.52345 (19013116) 453892.00 3770343.38 6.53249 (20122416) 453845.52 3770381.27 4.93127 (20122416) 453756.12 3770381.81 3.89438 (20122416) 453736.62 3770343.88 4.22895 (20122416) 453828.86 3770443.92 3.17854 (19013116) 453790.96 3770279.76 4.75223 (19122616) 453771.85 3770281.37 4.47977 (19122616) 453656.79 3770594.13 1.45225 (20041016) 453650.82 3770437.04 2.01139 (19013116) 453730.36 3770758.17 1.57921 (19122516) 454061.44 3770113.91 9.61339 (19101116) 453983.24 3770162.63 6.46336 (22121216) 453983.88 3770095.38 5.94611 (19103016) 454129.86 3770114.50 14.96594 (19101116) 454390.90 3770146.06 32.95427 (19022016) 454378.15 3770242.63 101.77808 (19022016) 453628.04 3770153.73 2.48325 (19122616) 453331.19 3770122.83 1.46240 (19122616) 453296.71 3770270.82 1.66960 (19122616) 454635.77 3770147.25 13.55755 (19122016) 454744.96 3770119.96 7.07908 (16011816) 454639.83 3770088.09 10.60391 (19122016) 454856.74 3770082.33 4.77571 (16011816) 454787.57 3770075.32 5.46988 (17103016) 454853.55 3770149.91 5.67359 (19092716) 454867.57 3770221.95 6.99766 (19092716) 454867.26 3770294.31 8.37062 (19092716) 454698.95 3770289.53 19.76916 (19092716) 454630.12 3770001.75 6.53422 (19122016) 454859.72 3770001.75 3.88070 (17103016) 454928.73 3770010.30 3.13226 (16011816) 454545.24 3770002.36 8.43958 (19011616) 454376.71 3770010.30 14.06112 (22011416) 454040.24 3769981.60 8.09653 (19101116) 454914.07 3770171.51 4.96209 (19092716) 454913.46 3770231.96 6.07158 (19092716) 453614.68 3770780.33 1.18543 (19122516) 453305.84 3770765.12 0.66841 (20041016) 454195.51 3770945.23 5.63298 (22123016) 454923.46 3770771.03 4.98098 (19122416) 454923.46 3771038.97 2.72551 (22022116) 454924.00 3771278.30 1.74890 (22110816) 454933.34 3771200.44 1.84566 (22110816) 454799.23 3771302.36 1.38963 (22110816) 454613.27 3771298.98 2.33293 (17011016) 454087.50 3771276.16 2.63145 (22123016) 455732.13 3771151.77 1.23869 (16011916) 455146.83 3770887.16 3.00175 (19011716) 455330.77 3770872.07 2.40286 (19021516) 455325.74 3770924.52 2.17433 (19020516) 455350.18 3770868.48 2.39311 (19021516) 455124.63 3770415.95 3.98060 (22121516) 454838.81 3769930.96 3.48099 (17103016) 454960.97 3769945.62 2.62162 (17103016) 454849.81 3769882.70 2.98988 (19122016) 455044.03 3769898.59 1.96161 (17103016) 455185.16 3769966.42 1.86587 (16011816) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 21 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 8‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: EXHUAST *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 2.48824 (17103016) 455120.97 3769660.75 1.32296 (17103016) 455143.99 3769654.61 1.30331 (17103016) 455057.73 3769795.12 1.89736 (17103016) 454950.48 3769483.39 1.03474 (19122016) 455047.08 3769487.06 1.08972 (19122016) 455186.02 3769487.43 0.95829 (19122016) 455228.61 3769489.33 0.90406 (19122016) 454670.56 3769664.99 2.47049 (19011616) 454442.93 3769677.47 3.43481 (19022016) 454817.24 3769446.56 1.21563 (19011616) 457073.40 3771679.08 0.46581 (17050516) 457180.76 3771676.87 0.45984 (17050516) 453293.96 3769817.93 1.00237 (22121216) 453163.51 3770000.16 0.99996 (19122616) 453419.51 3770001.32 1.15211 (19122616) 453310.35 3770010.68 1.13482 (19122616) 452792.85 3769973.03 0.73497 (19122616) 452612.97 3770098.22 0.73993 (19122616) 452566.21 3770175.93 0.79283 (19122616) 452402.16 3770197.51 0.73823 (19122616) 452394.97 3770047.86 0.61707 (19122616) 452636.00 3769852.88 0.58701 (19122616) 452269.78 3770197.51 0.69011 (19122616) 452087.75 3770201.11 0.63661 (19122616) 452365.47 3769988.86 0.57017 (19122616) 452053.21 3769889.57 0.45287 (19122616) 454290.08 3769974.82 12.40065 (19123016) 454539.03 3769826.60 4.39597 (19022016) 452423.72 3769682.87 0.41044 (16012216) 452154.23 3769692.25 0.40222 (19122616) 454912.82 3770375.11 7.33211 (19092616) 454946.69 3770523.91 7.36765 (19051516) 454913.41 3770360.45 7.12752 (19092616) 455329.00 3770822.74 2.61454 (19021516) 455107.72 3770816.10 3.43369 (19011716) 454999.84 3770834.08 3.89195 (19122416) 455329.83 3770804.76 2.61266 (19021516) 455325.06 3770415.64 2.71809 (22121516) 455325.06 3770367.01 2.32937 (22121516) 455322.57 3770267.26 2.14742 (19092716) 455327.56 3770519.13 2.79995 (19051516) 455322.94 3770561.45 2.88012 (19051516) 455330.69 3770603.23 2.71533 (19051516) 454959.01 3770572.49 6.64538 (17032216) 455127.10 3770559.48 4.40809 (19051516) 453158.66 3770937.93 0.58681 (19011116) 452421.67 3770910.46 0.35725 (19011116) 454556.71 3771053.14 4.25309 (17011016) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 22 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 8‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 27.45054 (17011016) 454514.86 3770786.06 21.58237 (17011016) 454034.35 3770517.35 12.98063 (22021516) 454048.71 3770385.92 24.58937 (19122616) 454182.29 3770421.75 40.70015 (19013116) 454142.55 3770420.62 31.28828 (19013116) 454625.62 3770785.69 15.90753 (22110816) 454827.07 3770784.47 11.51976 (19122416) 454752.59 3770566.53 32.04079 (20012116) 454835.61 3770558.60 23.95494 (20012116) 454812.42 3770415.14 27.69941 (19051516) 454913.75 3770480.46 19.60706 (19051516) 454925.35 3770700.83 13.05057 (20012116) 454693.99 3770943.18 9.23280 (22110816) 454368.01 3770918.76 10.28886 (16010616) 453794.80 3770744.18 4.98735 (19122516) 453971.91 3770386.76 16.99061 (19122616) 453937.64 3770444.98 10.75850 (19013116) 453953.91 3770386.77 15.75895 (19122616) 453992.13 3770444.71 12.90472 (19013116) 453912.32 3770386.53 13.42223 (19122616) 453880.11 3770440.50 9.18454 (19013116) 453864.72 3770443.99 8.66078 (19013116) 453892.00 3770343.38 15.68381 (19122616) 453845.52 3770381.27 11.00858 (19122616) 453756.12 3770381.81 8.61174 (20122416) 453736.62 3770343.88 9.42142 (20122416) 453828.86 3770443.92 7.82100 (19013116) 453790.96 3770279.76 12.02019 (19122616) 453771.85 3770281.37 11.32934 (19122616) 453656.79 3770594.13 3.62656 (20041016) 453650.82 3770437.04 4.93228 (19013116) 453730.36 3770758.17 4.26169 (19122516) 454061.44 3770113.91 21.24979 (19101116) 453983.24 3770162.63 15.42409 (22121216) 453983.88 3770095.38 13.84050 (22121216) 454129.86 3770114.50 33.81165 (19101116) 454390.90 3770146.06 77.26863 (22120216) 454378.15 3770242.63 448.47286 (22120216) 453628.04 3770153.73 5.92894 (19122616) 453331.19 3770122.83 3.53417 (19122616) 453296.71 3770270.82 4.32568 (19122616) 454635.77 3770147.25 32.93084 (19122016) 454744.96 3770119.96 17.17533 (16012716) 454639.83 3770088.09 25.69692 (19122016) 454856.74 3770082.33 11.25698 (16012716) 454787.57 3770075.32 12.89009 (16012716) 454853.55 3770149.91 12.69086 (19102516) 454867.57 3770221.95 15.09659 (19092716) 454867.26 3770294.31 18.58030 (19092716) 454698.95 3770289.53 44.02151 (19092716) 454630.12 3770001.75 16.99787 (19052316) 454859.72 3770001.75 8.62811 (16012716) 454928.73 3770010.30 8.09596 (16012716) 454545.24 3770002.36 20.33130 (22120216) 454376.71 3770010.30 29.10501 (22011416) 454040.24 3769981.60 18.36653 (19101116) 454914.07 3770171.51 11.49804 (17112116) 454913.46 3770231.96 13.18288 (19092716) 453614.68 3770780.33 3.15067 (19122516) 453305.84 3770765.12 2.19504 (19011116) 454195.51 3770945.23 11.53319 (22123016) 454923.46 3770771.03 11.84875 (19122416) 454923.46 3771038.97 7.11931 (17010316) 454924.00 3771278.30 4.01788 (22110816) 454933.34 3771200.44 4.85034 (17010316) 454799.23 3771302.36 3.14966 (16120516) 454613.27 3771298.98 5.05987 (17011016) 454087.50 3771276.16 5.32172 (22123016) 455732.13 3771151.77 2.84511 (16011916) 455146.83 3770887.16 6.44282 (19011716) 455330.77 3770872.07 5.42600 (19021516) 455325.74 3770924.52 4.96532 (16011916) 455350.18 3770868.48 5.44122 (19021516) 455124.63 3770415.95 9.48840 (19120916) 454838.81 3769930.96 7.77030 (17103016) 454960.97 3769945.62 6.49974 (16012716) 454849.81 3769882.70 6.75815 (19122016) 455044.03 3769898.59 5.41250 (16012716) 455185.16 3769966.42 5.18625 (16012716) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 23 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 8‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 5.66367 (17103016) 455120.97 3769660.75 3.18629 (19011616) 455143.99 3769654.61 3.13674 (19011616) 455057.73 3769795.12 4.36797 (17103016) 454950.48 3769483.39 2.51398 (19122016) 455047.08 3769487.06 2.64303 (19122016) 455186.02 3769487.43 2.18981 (19011616) 455228.61 3769489.33 2.38042 (19011616) 454670.56 3769664.99 7.11733 (22120216) 454442.93 3769677.47 7.85001 (19022016) 454817.24 3769446.56 3.36286 (22120216) 457073.40 3771679.08 1.08554 (19012316) 457180.76 3771676.87 1.08106 (19012316) 453293.96 3769817.93 2.42309 (22121216) 453163.51 3770000.16 2.43443 (19122616) 453419.51 3770001.32 2.68398 (19122616) 453310.35 3770010.68 2.72555 (19122616) 452792.85 3769973.03 1.78464 (19122616) 452612.97 3770098.22 1.83557 (19122616) 452566.21 3770175.93 2.06267 (19122616) 452402.16 3770197.51 1.95693 (19122616) 452394.97 3770047.86 1.51730 (19122616) 452636.00 3769852.88 1.47535 (19122616) 452269.78 3770197.51 1.83904 (19122616) 452087.75 3770201.11 1.70777 (19122616) 452365.47 3769988.86 1.37392 (19122616) 452053.21 3769889.57 1.08488 (19122616) 454290.08 3769974.82 26.12707 (19123016) 454539.03 3769826.60 12.57035 (22120216) 452423.72 3769682.87 1.10332 (16012216) 452154.23 3769692.25 1.04665 (19122616) 454912.82 3770375.11 17.53145 (19120916) 454946.69 3770523.91 16.42483 (17032216) 454913.41 3770360.45 17.02064 (19120916) 455329.00 3770822.74 5.96211 (19021516) 455107.72 3770816.10 7.58063 (19030816) 454999.84 3770834.08 9.27966 (19122416) 455329.83 3770804.76 5.93764 (19021516) 455325.06 3770415.64 5.96631 (19120916) 455325.06 3770367.01 5.46268 (19120916) 455322.57 3770267.26 5.03987 (22122916) 455327.56 3770519.13 6.11666 (19051516) 455322.94 3770561.45 6.29627 (19051516) 455330.69 3770603.23 5.90071 (19051516) 454959.01 3770572.49 15.40291 (17032216) 455127.10 3770559.48 9.59679 (19051516) 453158.66 3770937.93 1.84107 (19011116) 452421.67 3770910.46 1.21331 (19120316) 454556.71 3771053.14 9.19702 (17011016) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 24 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 24‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: DUST *** INCLUDING SOURCE(S): PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 4.78121 (17011024) 454514.86 3770786.06 3.77975 (17011024) 454034.35 3770517.35 2.71336 (22021524) 454048.71 3770385.92 4.88011 (19122624) 454182.29 3770421.75 9.10515 (16122024) 454142.55 3770420.62 6.64823 (16122024) 454625.62 3770785.69 2.96149 (17010324) 454827.07 3770784.47 2.21020 (19122424) 454752.59 3770566.53 6.14500 (20012124) 454835.61 3770558.60 4.47967 (20012124) 454812.42 3770415.14 4.92109 (19120924) 454913.75 3770480.46 3.51683 (19051524) 454925.35 3770700.83 2.50542 (20012124) 454693.99 3770943.18 1.70549 (22110824) 454368.01 3770918.76 1.87479 (16010624) 453794.80 3770744.18 1.04636 (19122524) 453971.91 3770386.76 3.33610 (19122624) 453937.64 3770444.98 2.12387 (19013124) 453953.91 3770386.77 3.08992 (19122624) 453992.13 3770444.71 2.63712 (16122024) 453912.32 3770386.53 2.62721 (19122624) 453880.11 3770440.50 1.81554 (19013124) 453864.72 3770443.99 1.71244 (19013124) 453892.00 3770343.38 3.10320 (19122624) 453845.52 3770381.27 2.15732 (19122624) 453756.12 3770381.81 1.65227 (19122624) 453736.62 3770343.88 1.87512 (19122624) 453828.86 3770443.92 1.54749 (19013124) 453790.96 3770279.76 2.42265 (19122624) 453771.85 3770281.37 2.28319 (19122624) 453656.79 3770594.13 0.83902 (19120324) 453650.82 3770437.04 0.97363 (19013124) 453730.36 3770758.17 0.89416 (19122524) 454061.44 3770113.91 3.88207 (16102424) 453983.24 3770162.63 2.98691 (22121224) 453983.88 3770095.38 2.69748 (22121224) 454129.86 3770114.50 6.28190 (19101124) 454390.90 3770146.06 19.17241 (22120224) 454378.15 3770242.63 124.41429 (22120224) 453628.04 3770153.73 1.14856 (19122624) 453331.19 3770122.83 0.69059 (19122624) 453296.71 3770270.82 0.88536 (19122624) 454635.77 3770147.25 6.45776 (19122024) 454744.96 3770119.96 4.09360 (16012724) 454639.83 3770088.09 5.03100 (19122024) 454856.74 3770082.33 2.71729 (16012724) 454787.57 3770075.32 3.08593 (16012724) 454853.55 3770149.91 2.97315 (16012724) 454867.57 3770221.95 3.03100 (17112124) 454867.26 3770294.31 3.52116 (22122924) 454698.95 3770289.53 8.08412 (19092724) 454630.12 3770001.75 3.48804 (19052324) 454859.72 3770001.75 2.08208 (16012724) 454928.73 3770010.30 1.97373 (16012724) 454545.24 3770002.36 5.59392 (22120224) 454376.71 3770010.30 5.16385 (22120224) 454040.24 3769981.60 3.42334 (19101124) 454914.07 3770171.51 2.36800 (17112124) 454913.46 3770231.96 2.58609 (17121324) 453614.68 3770780.33 0.67494 (19120324) 453305.84 3770765.12 0.54921 (19120324) 454195.51 3770945.23 1.96674 (22123024) 454923.46 3770771.03 2.28926 (19122424) 454923.46 3771038.97 1.47998 (17010324) 454924.00 3771278.30 1.03201 (16120524) 454933.34 3771200.44 1.09585 (17010324) 454799.23 3771302.36 0.81149 (17010324) 454613.27 3771298.98 0.90898 (17011024) 454087.50 3771276.16 0.89676 (22123024) 455732.13 3771151.77 0.58415c (16011924) 455146.83 3770887.16 1.20914 (19122424) 455330.77 3770872.07 1.01847 (20012124) 455325.74 3770924.52 1.01502c (16011924) 455350.18 3770868.48 1.01603 (19021524) 455124.63 3770415.95 1.90911 (19120924) 454838.81 3769930.96 1.47401 (16012724) 454960.97 3769945.62 1.59024 (16012724) 454849.81 3769882.70 1.25609 (19122024) 455044.03 3769898.59 1.34126 (16012724) 455185.16 3769966.42 1.29083 (16012724) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 25 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 24‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: DUST *** INCLUDING SOURCE(S): PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 1.13091 (16012724) 455120.97 3769660.75 0.76369 (19011624) 455143.99 3769654.61 0.75491 (19011624) 455057.73 3769795.12 0.98460 (16012724) 454950.48 3769483.39 0.62525 (17111324) 455047.08 3769487.06 0.56423 (17111324) 455186.02 3769487.43 0.51272 (19011624) 455228.61 3769489.33 0.56891 (19011624) 454670.56 3769664.99 2.05182 (22120224) 454442.93 3769677.47 1.82656 (19122324) 454817.24 3769446.56 0.90501 (22120224) 457073.40 3771679.08 0.27433 (19012324) 457180.76 3771676.87 0.27432 (19012324) 453293.96 3769817.93 0.47357 (22121224) 453163.51 3770000.16 0.47816 (19122624) 453419.51 3770001.32 0.51062 (19122624) 453310.35 3770010.68 0.53025 (19122624) 452792.85 3769973.03 0.34989 (19122624) 452612.97 3770098.22 0.36522 (19122624) 452566.21 3770175.93 0.42328 (19122624) 452402.16 3770197.51 0.40623 (19122624) 452394.97 3770047.86 0.30008 (19122624) 452636.00 3769852.88 0.29611 (19122624) 452269.78 3770197.51 0.38298 (19122624) 452087.75 3770201.11 0.35706 (19122624) 452365.47 3769988.86 0.26792 (19122624) 452053.21 3769889.57 0.22796 (16021624) 454290.08 3769974.82 4.57547 (19123024) 454539.03 3769826.60 3.65646 (22120224) 452423.72 3769682.87 0.23096 (16012224) 452154.23 3769692.25 0.21481 (19122624) 454912.82 3770375.11 3.48037 (19120924) 454946.69 3770523.91 3.08558 (17032224) 454913.41 3770360.45 3.36463 (19120924) 455329.00 3770822.74 1.11586 (19021524) 455107.72 3770816.10 1.48708c (16011924) 454999.84 3770834.08 1.79590 (19122424) 455329.83 3770804.76 1.10833 (19021524) 455325.06 3770415.64 1.20027 (19120924) 455325.06 3770367.01 1.09317 (17121824) 455322.57 3770267.26 1.00712 (22122924) 455327.56 3770519.13 1.10557 (19051524) 455322.94 3770561.45 1.13871 (19051524) 455330.69 3770603.23 1.06179 (19051524) 454959.01 3770572.49 2.91918 (17032224) 455127.10 3770559.48 1.78126 (17032224) 453158.66 3770937.93 0.45349 (19120324) 452421.67 3770910.46 0.32523 (19120324) 454556.71 3771053.14 1.64798 (17011024) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 26 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 24‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: EXHUAST *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 4.36896 (17011024) 454514.86 3770786.06 3.41437 (17011024) 454034.35 3770517.35 1.72190 (20041024) 454048.71 3770385.92 3.31635 (19122624) 454182.29 3770421.75 4.96243 (20041024) 454142.55 3770420.62 3.97641 (19013124) 454625.62 3770785.69 2.40208 (22110824) 454827.07 3770784.47 1.62972 (19122424) 454752.59 3770566.53 4.53526 (20012124) 454835.61 3770558.60 3.50531 (20012124) 454812.42 3770415.14 4.37121 (19051524) 454913.75 3770480.46 3.01885 (19051524) 454925.35 3770700.83 1.94866 (19011724) 454693.99 3770943.18 1.37211 (22110824) 454368.01 3770918.76 1.55483 (16010624) 453794.80 3770744.18 0.61609 (19122524) 453971.91 3770386.76 2.34296 (20122424) 453937.64 3770444.98 1.46230 (19013124) 453953.91 3770386.77 2.20278 (20122424) 453992.13 3770444.71 1.75079 (19013124) 453912.32 3770386.53 1.92993 (20122424) 453880.11 3770440.50 1.24597 (19013124) 453864.72 3770443.99 1.17448 (19013124) 453892.00 3770343.38 2.17750 (20122424) 453845.52 3770381.27 1.64376 (20122424) 453756.12 3770381.81 1.29813 (20122424) 453736.62 3770343.88 1.40965 (20122424) 453828.86 3770443.92 1.05951 (19013124) 453790.96 3770279.76 1.58408 (19122624) 453771.85 3770281.37 1.49326 (19122624) 453656.79 3770594.13 0.48408 (20041024) 453650.82 3770437.04 0.67046 (19013124) 453730.36 3770758.17 0.52640 (19122524) 454061.44 3770113.91 3.20446 (19101124) 453983.24 3770162.63 2.15445 (22121224) 453983.88 3770095.38 1.98204 (19103024) 454129.86 3770114.50 4.98865 (19101124) 454390.90 3770146.06 10.98476 (19022024) 454378.15 3770242.63 33.92603 (19022024) 453628.04 3770153.73 0.82775 (19122624) 453331.19 3770122.83 0.48747 (19122624) 453296.71 3770270.82 0.55653 (19122624) 454635.77 3770147.25 4.51918 (19122024) 454744.96 3770119.96 2.35969 (16011824) 454639.83 3770088.09 3.53464 (19122024) 454856.74 3770082.33 1.59190 (16011824) 454787.57 3770075.32 1.82329 (17103024) 454853.55 3770149.91 1.89120 (19092724) 454867.57 3770221.95 2.33255 (19092724) 454867.26 3770294.31 2.79021 (19092724) 454698.95 3770289.53 6.58972 (19092724) 454630.12 3770001.75 2.17807 (19122024) 454859.72 3770001.75 1.29357 (17103024) 454928.73 3770010.30 1.04409 (16011824) 454545.24 3770002.36 2.81319 (19011624) 454376.71 3770010.30 4.68704 (22011424) 454040.24 3769981.60 2.69884 (19101124) 454914.07 3770171.51 1.65403 (19092724) 454913.46 3770231.96 2.02386 (19092724) 453614.68 3770780.33 0.39514 (19122524) 453305.84 3770765.12 0.22280 (20041024) 454195.51 3770945.23 1.87766 (22123024) 454923.46 3770771.03 1.66033 (19122424) 454923.46 3771038.97 0.90850 (22022124) 454924.00 3771278.30 0.58297 (22110824) 454933.34 3771200.44 0.61522 (22110824) 454799.23 3771302.36 0.46321 (22110824) 454613.27 3771298.98 0.77764 (17011024) 454087.50 3771276.16 0.87715 (22123024) 455732.13 3771151.77 0.45043c (16011924) 455146.83 3770887.16 1.00058 (19011724) 455330.77 3770872.07 0.80095 (19021524) 455325.74 3770924.52 0.79056c (16011924) 455350.18 3770868.48 0.79770 (19021524) 455124.63 3770415.95 1.32687 (22121524) 454838.81 3769930.96 1.16033 (17103024) 454960.97 3769945.62 0.87387 (17103024) 454849.81 3769882.70 0.99663 (19122024) 455044.03 3769898.59 0.65387 (17103024) 455185.16 3769966.42 0.62196 (16011824) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 27 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 24‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: EXHUAST *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 0.82941 (17103024) 455120.97 3769660.75 0.44099 (17103024) 455143.99 3769654.61 0.43444 (17103024) 455057.73 3769795.12 0.63245 (17103024) 454950.48 3769483.39 0.34491 (19122024) 455047.08 3769487.06 0.36324 (19122024) 455186.02 3769487.43 0.31943 (19122024) 455228.61 3769489.33 0.30135 (19122024) 454670.56 3769664.99 0.82350 (19011624) 454442.93 3769677.47 1.14494 (19022024) 454817.24 3769446.56 0.40521 (19011624) 457073.40 3771679.08 0.15527 (17050524) 457180.76 3771676.87 0.15328 (17050524) 453293.96 3769817.93 0.33412 (22121224) 453163.51 3770000.16 0.33332 (19122624) 453419.51 3770001.32 0.38404 (19122624) 453310.35 3770010.68 0.37827 (19122624) 452792.85 3769973.03 0.24499 (19122624) 452612.97 3770098.22 0.24664 (19122624) 452566.21 3770175.93 0.26428 (19122624) 452402.16 3770197.51 0.24608 (19122624) 452394.97 3770047.86 0.20569 (19122624) 452636.00 3769852.88 0.19567 (19122624) 452269.78 3770197.51 0.23004 (19122624) 452087.75 3770201.11 0.21220 (19122624) 452365.47 3769988.86 0.19006 (19122624) 452053.21 3769889.57 0.15096 (19122624) 454290.08 3769974.82 4.13355 (19123024) 454539.03 3769826.60 1.46532 (19022024) 452423.72 3769682.87 0.13681 (16012224) 452154.23 3769692.25 0.13407 (19122624) 454912.82 3770375.11 2.44404 (19092624) 454946.69 3770523.91 2.45588 (19051524) 454913.41 3770360.45 2.37584 (19092624) 455329.00 3770822.74 0.87151 (19021524) 455107.72 3770816.10 1.17937c (16011924) 454999.84 3770834.08 1.29732 (19122424) 455329.83 3770804.76 0.87089 (19021524) 455325.06 3770415.64 0.90603 (22121524) 455325.06 3770367.01 0.77646 (22121524) 455322.57 3770267.26 0.71581 (19092724) 455327.56 3770519.13 0.93332 (19051524) 455322.94 3770561.45 0.96004 (19051524) 455330.69 3770603.23 0.90511 (19051524) 454959.01 3770572.49 2.21513 (17032224) 455127.10 3770559.48 1.46936 (19051524) 453158.66 3770937.93 0.19560 (19011124) 452421.67 3770910.46 0.11908 (19011124) 454556.71 3771053.14 1.41770 (17011024) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 28 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 24‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 9.15018 (17011024) 454514.86 3770786.06 7.19412 (17011024) 454034.35 3770517.35 4.32688 (22021524) 454048.71 3770385.92 8.19646 (19122624) 454182.29 3770421.75 13.56672 (19013124) 454142.55 3770420.62 10.42943 (19013124) 454625.62 3770785.69 5.30251 (22110824) 454827.07 3770784.47 3.83992 (19122424) 454752.59 3770566.53 10.68026 (20012124) 454835.61 3770558.60 7.98498 (20012124) 454812.42 3770415.14 9.23314 (19051524) 454913.75 3770480.46 6.53569 (19051524) 454925.35 3770700.83 4.35019 (20012124) 454693.99 3770943.18 3.07760 (22110824) 454368.01 3770918.76 3.42962 (16010624) 453794.80 3770744.18 1.66245 (19122524) 453971.91 3770386.76 5.66354 (19122624) 453937.64 3770444.98 3.58617 (19013124) 453953.91 3770386.77 5.25298 (19122624) 453992.13 3770444.71 4.30157 (19013124) 453912.32 3770386.53 4.47408 (19122624) 453880.11 3770440.50 3.06151 (19013124) 453864.72 3770443.99 2.88693 (19013124) 453892.00 3770343.38 5.22794 (19122624) 453845.52 3770381.27 3.66953 (19122624) 453756.12 3770381.81 2.87058 (20122424) 453736.62 3770343.88 3.14047 (20122424) 453828.86 3770443.92 2.60700 (19013124) 453790.96 3770279.76 4.00673 (19122624) 453771.85 3770281.37 3.77645 (19122624) 453656.79 3770594.13 1.20885 (20041024) 453650.82 3770437.04 1.64409 (19013124) 453730.36 3770758.17 1.42056 (19122524) 454061.44 3770113.91 7.08326 (19101124) 453983.24 3770162.63 5.14136 (22121224) 453983.88 3770095.38 4.61350 (22121224) 454129.86 3770114.50 11.27055 (19101124) 454390.90 3770146.06 25.75621 (22120224) 454378.15 3770242.63 149.49095 (22120224) 453628.04 3770153.73 1.97631 (19122624) 453331.19 3770122.83 1.17806 (19122624) 453296.71 3770270.82 1.44189 (19122624) 454635.77 3770147.25 10.97695 (19122024) 454744.96 3770119.96 5.72511 (16012724) 454639.83 3770088.09 8.56564 (19122024) 454856.74 3770082.33 3.75233 (16012724) 454787.57 3770075.32 4.29670 (16012724) 454853.55 3770149.91 4.23029 (19102524) 454867.57 3770221.95 5.03220 (19092724) 454867.26 3770294.31 6.19343 (19092724) 454698.95 3770289.53 14.67384 (19092724) 454630.12 3770001.75 5.66596 (19052324) 454859.72 3770001.75 2.87604 (16012724) 454928.73 3770010.30 2.69865 (16012724) 454545.24 3770002.36 6.77710 (22120224) 454376.71 3770010.30 9.70167 (22011424) 454040.24 3769981.60 6.12218 (19101124) 454914.07 3770171.51 3.83268 (17112124) 454913.46 3770231.96 4.39429 (19092724) 453614.68 3770780.33 1.05022 (19122524) 453305.84 3770765.12 0.73168 (19011124) 454195.51 3770945.23 3.84440 (22123024) 454923.46 3770771.03 3.94958 (19122424) 454923.46 3771038.97 2.37310 (17010324) 454924.00 3771278.30 1.33929 (22110824) 454933.34 3771200.44 1.61678 (17010324) 454799.23 3771302.36 1.04989 (16120524) 454613.27 3771298.98 1.68662 (17011024) 454087.50 3771276.16 1.77391 (22123024) 455732.13 3771151.77 1.03458c (16011924) 455146.83 3770887.16 2.14761 (19011724) 455330.77 3770872.07 1.80867 (19021524) 455325.74 3770924.52 1.80557c (16011924) 455350.18 3770868.48 1.81374 (19021524) 455124.63 3770415.95 3.16280 (19120924) 454838.81 3769930.96 2.59010 (17103024) 454960.97 3769945.62 2.16658 (16012724) 454849.81 3769882.70 2.25272 (19122024) 455044.03 3769898.59 1.80417 (16012724) 455185.16 3769966.42 1.72875 (16012724) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 29 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 24‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , PAREA1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 1.88789 (17103024) 455120.97 3769660.75 1.06210 (19011624) 455143.99 3769654.61 1.04558 (19011624) 455057.73 3769795.12 1.45599 (17103024) 454950.48 3769483.39 0.83799 (19122024) 455047.08 3769487.06 0.88101 (19122024) 455186.02 3769487.43 0.72994 (19011624) 455228.61 3769489.33 0.79347 (19011624) 454670.56 3769664.99 2.37244 (22120224) 454442.93 3769677.47 2.61667 (19022024) 454817.24 3769446.56 1.12095 (22120224) 457073.40 3771679.08 0.36185 (19012324) 457180.76 3771676.87 0.36035 (19012324) 453293.96 3769817.93 0.80770 (22121224) 453163.51 3770000.16 0.81148 (19122624) 453419.51 3770001.32 0.89466 (19122624) 453310.35 3770010.68 0.90852 (19122624) 452792.85 3769973.03 0.59488 (19122624) 452612.97 3770098.22 0.61186 (19122624) 452566.21 3770175.93 0.68756 (19122624) 452402.16 3770197.51 0.65231 (19122624) 452394.97 3770047.86 0.50577 (19122624) 452636.00 3769852.88 0.49178 (19122624) 452269.78 3770197.51 0.61301 (19122624) 452087.75 3770201.11 0.56926 (19122624) 452365.47 3769988.86 0.45797 (19122624) 452053.21 3769889.57 0.36163 (19122624) 454290.08 3769974.82 8.70902 (19123024) 454539.03 3769826.60 4.19012 (22120224) 452423.72 3769682.87 0.36777 (16012224) 452154.23 3769692.25 0.34888 (19122624) 454912.82 3770375.11 5.84382 (19120924) 454946.69 3770523.91 5.47494 (17032224) 454913.41 3770360.45 5.67355 (19120924) 455329.00 3770822.74 1.98737 (19021524) 455107.72 3770816.10 2.66645c (16011924) 454999.84 3770834.08 3.09322 (19122424) 455329.83 3770804.76 1.97921 (19021524) 455325.06 3770415.64 1.98877 (19120924) 455325.06 3770367.01 1.82089 (19120924) 455322.57 3770267.26 1.67996 (22122924) 455327.56 3770519.13 2.03889 (19051524) 455322.94 3770561.45 2.09876 (19051524) 455330.69 3770603.23 1.96690 (19051524) 454959.01 3770572.49 5.13430 (17032224) 455127.10 3770559.48 3.19893 (19051524) 453158.66 3770937.93 0.61369 (19011124) 452421.67 3770910.46 0.40444 (19120324) 454556.71 3771053.14 3.06567 (17011024) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 30 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE SUMMARY OF HIGHEST 1‐HR RESULTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** DATE NETWORK GROUP ID AVERAGE CONC (YYMMDDHH) RECEPTOR (XR, YR, ZELEV, ZHILL, ZFLAG) OF TYPE GRID‐ID ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ DUST HIGH 1ST HIGH VALUE IS 709.76799 ON 22120216: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC EXHUAST HIGH 1ST HIGH VALUE IS 290.36389 ON 19011616: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC ALL HIGH 1ST HIGH VALUE IS 861.14001 ON 19011616: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC *** RECEPTOR TYPES: GC = GRIDCART GP = GRIDPOLR DC = DISCCART DP = DISCPOLR *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 31 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE SUMMARY OF HIGHEST 8‐HR RESULTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** DATE NETWORK GROUP ID AVERAGE CONC (YYMMDDHH) RECEPTOR (XR, YR, ZELEV, ZHILL, ZFLAG) OF TYPE GRID‐ID ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ DUST HIGH 1ST HIGH VALUE IS 373.24288 ON 22120216: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC EXHUAST HIGH 1ST HIGH VALUE IS 101.77808 ON 19022016: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC ALL HIGH 1ST HIGH VALUE IS 448.47286 ON 22120216: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC *** RECEPTOR TYPES: GC = GRIDCART GP = GRIDPOLR DC = DISCCART DP = DISCPOLR *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 32 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE SUMMARY OF HIGHEST 24‐HR RESULTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** DATE NETWORK GROUP ID AVERAGE CONC (YYMMDDHH) RECEPTOR (XR, YR, ZELEV, ZHILL, ZFLAG) OF TYPE GRID‐ID ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ DUST HIGH 1ST HIGH VALUE IS 124.41429 ON 22120224: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC EXHUAST HIGH 1ST HIGH VALUE IS 33.92603 ON 19022024: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC ALL HIGH 1ST HIGH VALUE IS 149.49095 ON 22120224: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC *** RECEPTOR TYPES: GC = GRIDCART GP = GRIDPOLR DC = DISCCART DP = DISCPOLR *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:46:27 PAGE 33 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** Message Summary : AERMOD Model Execution *** ‐‐‐‐‐‐‐‐‐ Summary of Total Messages ‐‐‐‐‐‐‐‐ A Total of 0 Fatal Error Message(s) A Total of 73 Warning Message(s) A Total of 348 Informational Message(s) A Total of 43848 Hours Were Processed A Total of 22 Calm Hours Identified A Total of 326 Missing Hours Identified ( 0.74 Percent) ******** FATAL ERROR MESSAGES ******** *** NONE *** ******** WARNING MESSAGES ******** ME W186 104 MEOPEN: THRESH_1MIN 1‐min ASOS wind speed threshold used 0.50 ME W187 104 MEOPEN: ADJ_U* Option for Stable Low Winds used in AERMET CN W733 1744 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2016031316 CN W732 1752 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2016031324 CN W733 1768 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2016031416 CN W732 1776 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2016031424 CN W733 9952 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2017021816 CN W732 9960 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2017021824 MX W450 17545 CHKDAT: Record Out of Sequence in Meteorological File at: 19010101 MX W450 17545 CHKDAT: Record Out of Sequence in Meteorological File at: 1 year gap CN W733 22112 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2019071008 CN W733 22864 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2019081016 CN W732 22872 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2019081024 CN W733 28048 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020031316 CN W732 28056 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020031324 CN W733 28072 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020031416 CN W732 28080 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020031424 CN W733 28096 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020031516 CN W732 28104 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020031524 CN W733 28120 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020031616 CN W732 28128 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020031624 CN W733 28528 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020040216 CN W732 28536 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020040224 CN W733 28552 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020040316 CN W732 28560 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020040324 CN W733 28648 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020040716 CN W732 28656 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020040724 CN W733 28960 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020042016 CN W732 28968 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020042024 CN W733 33040 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020100716 CN W732 33048 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020100724 CN W733 33112 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020101016 CN W732 33120 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020101024 CN W733 33904 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020111216 CN W732 33912 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020111224 CN W733 34048 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020111816 CN W732 34056 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020111824 CN W733 34096 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112016 CN W732 34104 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112024 CN W733 34120 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112116 CN W732 34128 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112124 CN W733 34144 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112216 CN W732 34152 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112224 CN W733 34168 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112316 CN W732 34176 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112324 CN W733 34192 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112416 CN W732 34200 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112424 CN W733 34216 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112516 CN W732 34224 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112524 CN W733 34696 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020121516 CN W732 34704 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020121524 CN W733 34840 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020122116 CN W732 34848 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020122124 MX W450 35089 CHKDAT: Record Out of Sequence in Meteorological File at: 22010101 MX W450 35089 CHKDAT: Record Out of Sequence in Meteorological File at: 1 year gap CN W733 38296 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022051416 CN W732 38304 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022051424 CN W733 39016 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022061316 CN W732 39024 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022061324 CN W733 40432 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022081116 CN W732 40440 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022081124 CN W733 41128 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022090916 CN W732 41136 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022090924 CN W733 42664 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022111216 CN W732 42672 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022111224 CN W733 42688 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022111316 CN W732 42696 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022111324 CN W733 42712 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022111416 CN W732 42720 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022111424 CN W733 42736 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022111516 CN W732 42744 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022111524 CN W733 43168 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022120316 CN W732 43176 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022120324 ************************************ *** AERMOD Finishes Successfully *** ************************************ ** Lakes Environmental AERMOD MPI ** **************************************** ** ** AERMOD Input Produced by: ** AERMOD View Ver. 13.0.0 ** Lakes Environmental Software Inc. ** Date: 10/23/2025 ** File: C:\Users\adadabhoy\Desktop\AERMOD\16758‐Fontana Trailer Yard\16758‐Ops LSTs\16758‐Ops LSTs.ADI ** **************************************** ** ** **************************************** ** AERMOD Control Pathway **************************************** ** ** CO STARTING TITLEONE C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 MODELOPT DFAULT CONC AVERTIME 1 8 24 URBANOPT 2195611 County_of_San_Bernardino POLLUTID DPM FLAGPOLE 2.00 RUNORNOT RUN ERRORFIL "16758‐Ops LSTs.err" CO FINISHED ** **************************************** ** AERMOD Source Pathway **************************************** ** ** SO STARTING ** Source Location ** ** Source ID ‐ Type ‐ X Coord. ‐ Y Coord. ** LOCATION VOL1 VOLUME 454390.655 3770343.585 320.560 ** Source Parameters ** SRCPARAM VOL1 1.0 1.524 46.737 1.400 URBANSRC ALL SRCGROUP ALL SO FINISHED ** **************************************** ** AERMOD Receptor Pathway **************************************** ** ** RE STARTING INCLUDED "16758‐Ops LSTs.rou" RE FINISHED ** **************************************** ** AERMOD Meteorology Pathway **************************************** ** ** ME STARTING SURFFILE FONT_V11_trimmed.sfc PROFFILE FONT_V11_trimmed.pfl SURFDATA 3102 2016 UAIRDATA 3190 2016 SITEDATA 60712002 2016 PROFBASE 363.0 METERS ME FINISHED ** **************************************** ** AERMOD Output Pathway **************************************** ** ** OU STARTING RECTABLE ALLAVE 1ST RECTABLE 1 1ST RECTABLE 8 1ST RECTABLE 24 1ST ** Auto‐Generated Plotfiles PLOTFILE 1 ALL 1ST "16758‐OPS LSTS.AD\01H1GALL.PLT" 31 PLOTFILE 8 ALL 1ST "16758‐OPS LSTS.AD\08H1GALL.PLT" 32 PLOTFILE 24 ALL 1ST "16758‐OPS LSTS.AD\24H1GALL.PLT" 33 SUMMFILE "16758‐Ops LSTs.sum" OU FINISHED *** Message Summary For AERMOD Model Setup *** ‐‐‐‐‐‐‐‐‐ Summary of Total Messages ‐‐‐‐‐‐‐‐ A Total of 0 Fatal Error Message(s) A Total of 2 Warning Message(s) A Total of 0 Informational Message(s) ******** FATAL ERROR MESSAGES ******** *** NONE *** ******** WARNING MESSAGES ******** ME W186 65 MEOPEN: THRESH_1MIN 1‐min ASOS wind speed threshold used 0.50 ME W187 65 MEOPEN: ADJ_U* Option for Stable Low Winds used in AERMET *********************************** *** SETUP Finishes Successfully *** *********************************** *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 1 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** MODEL SETUP OPTIONS SUMMARY *** ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ** Model Options Selected: * Model Uses Regulatory DEFAULT Options * Model Is Setup For Calculation of Average CONCentration Values. * NO GAS DEPOSITION Data Provided. * NO PARTICLE DEPOSITION Data Provided. * Model Uses NO DRY DEPLETION. DDPLETE = F * Model Uses NO WET DEPLETION. WETDPLT = F * Stack‐tip Downwash. * Model Accounts for ELEVated Terrain Effects. * Use Calms Processing Routine. * Use Missing Data Processing Routine. * No Exponential Decay. * Model Uses URBAN Dispersion Algorithm for the SBL for 1 Source(s), for Total of 1 Urban Area(s): Urban Population = 2195611.0 ; Urban Roughness Length = 1.000 m * Urban Roughness Length of 1.0 Meter Used. * ADJ_U* ‐ Use ADJ_U* option for SBL in AERMET * CCVR_Sub ‐ Meteorological data includes CCVR substitutions * TEMP_Sub ‐ Meteorological data includes TEMP substitutions * Model Accepts FLAGPOLE Receptor . Heights. * The User Specified a Pollutant Type of: DPM **Model Calculates 3 Short Term Average(s) of: 1‐HR 8‐HR 24‐HR **This Run Includes: 1 Source(s); 1 Source Group(s); and 129 Receptor(s) with: 0 POINT(s), including 0 POINTCAP(s) and 0 POINTHOR(s) and: 1 VOLUME source(s) and: 0 AREA type source(s) and: 0 LINE source(s) and: 0 RLINE/RLINEXT source(s) and: 0 OPENPIT source(s) and: 0 BUOYANT LINE source(s) with a total of 0 line(s) and: 0 SWPOINT source(s) **Model Set To Continue RUNning After the Setup Testing. **The AERMET Input Meteorological Data Version Date: 22112 **Output Options Selected: Model Outputs Tables of Highest Short Term Values by Receptor (RECTABLE Keyword) Model Outputs External File(s) of High Values for Plotting (PLOTFILE Keyword) Model Outputs Separate Summary File of High Ranked Values (SUMMFILE Keyword) **NOTE: The Following Flags May Appear Following CONC Values: c for Calm Hours m for Missing Hours b for Both Calm and Missing Hours **Misc. Inputs: Base Elev. for Pot. Temp. Profile (m MSL) = 363.00 ; Decay Coef. = 0.000 ; Rot. Angle = 0.0 Emission Units = GRAMS/SEC ; Emission Rate Unit Factor = 0.10000E+07 Output Units = MICROGRAMS/M**3 **Approximate Storage Requirements of Model = 3.5 MB of RAM. **Input Runstream File: aermod.inp **Output Print File: aermod.out **Detailed Error/Message File: 16758‐Ops LSTs.err **File for Summary of Results: 16758‐Ops LSTs.sum *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 2 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** VOLUME SOURCE DATA *** NUMBER EMISSION RATE BASE RELEASE INIT. INIT. URBAN EMISSION RATE AIRCRAFT SOURCE PART. (GRAMS/SEC) X Y ELEV. HEIGHT SY SZ SOURCE SCALAR VARY ID CATS. (METERS) (METERS) (METERS) (METERS) (METERS) (METERS) BY ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ VOL1 0 0.10000E+01 454390.7 3770343.6 320.6 1.52 46.74 1.40 YES NO *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 3 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** SOURCE IDs DEFINING SOURCE GROUPS *** SRCGROUP ID SOURCE IDs ‐‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ALL VOL1 , *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 4 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** SOURCE IDs DEFINED AS URBAN SOURCES *** URBAN ID URBAN POP SOURCE IDs ‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ 2195611. VOL1 , *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 5 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** DISCRETE CARTESIAN RECEPTORS *** (X‐COORD, Y‐COORD, ZELEV, ZHILL, ZFLAG) (METERS) ( 454512.8, 3770712.4, 326.3, 2731.4, 0.0); ( 454514.9, 3770786.1, 326.9, 2731.4, 0.0); ( 454034.3, 3770517.3, 321.0, 3066.9, 0.0); ( 454048.7, 3770385.9, 318.5, 2731.4, 0.0); ( 454182.3, 3770421.8, 320.2, 2731.4, 0.0); ( 454142.5, 3770420.6, 319.8, 2731.4, 0.0); ( 454625.6, 3770785.7, 327.0, 2731.4, 0.0); ( 454827.1, 3770784.5, 327.9, 2731.4, 0.0); ( 454752.6, 3770566.5, 324.7, 2731.4, 0.0); ( 454835.6, 3770558.6, 325.7, 2731.4, 0.0); ( 454812.4, 3770415.1, 323.3, 2731.4, 0.0); ( 454913.8, 3770480.5, 324.9, 2731.4, 0.0); ( 454925.3, 3770700.8, 327.6, 2731.4, 0.0); ( 454694.0, 3770943.2, 329.2, 2731.4, 0.0); ( 454368.0, 3770918.8, 328.2, 3066.9, 0.0); ( 453794.8, 3770744.2, 324.2, 3066.9, 0.0); ( 453971.9, 3770386.8, 319.4, 2731.4, 0.0); ( 453937.6, 3770445.0, 320.4, 3066.9, 0.0); ( 453953.9, 3770386.8, 319.5, 2731.4, 0.0); ( 453992.1, 3770444.7, 320.3, 2731.4, 0.0); ( 453912.3, 3770386.5, 319.4, 2731.4, 0.0); ( 453880.1, 3770440.5, 320.4, 3066.9, 0.0); ( 453864.7, 3770444.0, 320.4, 3066.9, 0.0); ( 453892.0, 3770343.4, 318.6, 2731.4, 0.0); ( 453845.5, 3770381.3, 319.2, 3066.9, 0.0); ( 453756.1, 3770381.8, 319.0, 3066.9, 0.0); ( 453736.6, 3770343.9, 318.5, 3066.9, 0.0); ( 453828.9, 3770443.9, 320.4, 3066.9, 0.0); ( 453791.0, 3770279.8, 317.6, 2731.4, 0.0); ( 453771.8, 3770281.4, 317.5, 2731.4, 0.0); ( 453656.8, 3770594.1, 322.0, 3066.9, 0.0); ( 453650.8, 3770437.0, 318.6, 3066.9, 0.0); ( 453730.4, 3770758.2, 324.2, 3066.9, 0.0); ( 454061.4, 3770113.9, 314.8, 2731.4, 0.0); ( 453983.2, 3770162.6, 316.1, 2731.4, 0.0); ( 453983.9, 3770095.4, 315.2, 2731.4, 0.0); ( 454129.9, 3770114.5, 315.6, 2731.4, 0.0); ( 454390.9, 3770146.1, 318.0, 2731.4, 0.0); ( 454378.1, 3770242.6, 319.1, 2731.4, 0.0); ( 453628.0, 3770153.7, 315.6, 2731.4, 0.0); ( 453331.2, 3770122.8, 314.9, 3066.9, 0.0); ( 453296.7, 3770270.8, 316.5, 3066.9, 0.0); ( 454635.8, 3770147.2, 318.2, 2731.4, 0.0); ( 454745.0, 3770120.0, 318.6, 2731.4, 0.0); ( 454639.8, 3770088.1, 317.9, 2731.4, 0.0); ( 454856.7, 3770082.3, 319.1, 2731.4, 0.0); ( 454787.6, 3770075.3, 318.5, 2731.4, 0.0); ( 454853.5, 3770149.9, 320.0, 2731.4, 0.0); ( 454867.6, 3770221.9, 321.0, 2731.4, 0.0); ( 454867.3, 3770294.3, 322.2, 2731.4, 0.0); ( 454699.0, 3770289.5, 320.4, 2731.4, 0.0); ( 454630.1, 3770001.8, 316.6, 2731.4, 0.0); ( 454859.7, 3770001.8, 318.2, 2731.4, 0.0); ( 454928.7, 3770010.3, 318.6, 2731.4, 0.0); ( 454545.2, 3770002.4, 316.3, 2731.4, 0.0); ( 454376.7, 3770010.3, 315.8, 2731.4, 0.0); ( 454040.2, 3769981.6, 312.9, 2731.4, 0.0); ( 454914.1, 3770171.5, 320.7, 2731.4, 0.0); ( 454913.5, 3770232.0, 321.5, 2731.4, 0.0); ( 453614.7, 3770780.3, 322.7, 3066.9, 0.0); ( 453305.8, 3770765.1, 322.7, 3066.9, 0.0); ( 454195.5, 3770945.2, 327.2, 3066.9, 0.0); ( 454923.5, 3770771.0, 328.4, 2731.4, 0.0); ( 454923.5, 3771039.0, 332.1, 2731.4, 0.0); ( 454924.0, 3771278.3, 335.5, 3066.9, 0.0); ( 454933.3, 3771200.4, 334.2, 3066.9, 0.0); ( 454799.2, 3771302.4, 335.1, 3066.9, 0.0); ( 454613.3, 3771299.0, 334.7, 3066.9, 0.0); ( 454087.5, 3771276.2, 332.9, 3066.9, 0.0); ( 455732.1, 3771151.8, 338.7, 2731.4, 0.0); ( 455146.8, 3770887.2, 331.8, 2731.4, 0.0); ( 455330.8, 3770872.1, 332.3, 2731.4, 0.0); ( 455325.7, 3770924.5, 332.9, 2731.4, 0.0); ( 455350.2, 3770868.5, 332.5, 2731.4, 0.0); ( 455124.6, 3770415.9, 324.8, 2731.4, 0.0); ( 454838.8, 3769931.0, 316.5, 2731.4, 0.0); ( 454961.0, 3769945.6, 318.1, 2731.4, 0.0); ( 454849.8, 3769882.7, 316.1, 2731.4, 0.0); ( 455044.0, 3769898.6, 317.6, 2731.4, 0.0); ( 455185.2, 3769966.4, 318.8, 2731.4, 0.0); ( 454949.8, 3769855.1, 316.2, 2731.4, 0.0); ( 455121.0, 3769660.8, 314.2, 2731.4, 0.0); ( 455144.0, 3769654.6, 314.4, 2731.4, 0.0); ( 455057.7, 3769795.1, 315.5, 2731.4, 0.0); ( 454950.5, 3769483.4, 311.4, 2731.4, 0.0); ( 455047.1, 3769487.1, 311.8, 2731.4, 0.0); ( 455186.0, 3769487.4, 312.9, 2731.4, 0.0); ( 455228.6, 3769489.3, 313.3, 2731.4, 0.0); ( 454670.6, 3769665.0, 311.7, 2731.4, 0.0); ( 454442.9, 3769677.5, 311.5, 2731.4, 0.0); *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 6 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** DISCRETE CARTESIAN RECEPTORS *** (X‐COORD, Y‐COORD, ZELEV, ZHILL, ZFLAG) (METERS) ( 454817.2, 3769446.6, 309.6, 2731.4, 0.0); ( 457073.4, 3771679.1, 353.7, 2731.4, 0.0); ( 457180.8, 3771676.9, 354.6, 2731.4, 0.0); ( 453294.0, 3769817.9, 310.4, 2731.4, 0.0); ( 453163.5, 3770000.2, 315.1, 3066.9, 0.0); ( 453419.5, 3770001.3, 313.1, 2731.4, 0.0); ( 453310.3, 3770010.7, 313.4, 2731.4, 0.0); ( 452792.8, 3769973.0, 316.3, 3066.9, 0.0); ( 452613.0, 3770098.2, 320.2, 3066.9, 0.0); ( 452566.2, 3770175.9, 319.2, 3066.9, 0.0); ( 452402.2, 3770197.5, 317.9, 3066.9, 0.0); ( 452395.0, 3770047.9, 316.1, 3066.9, 0.0); ( 452636.0, 3769852.9, 316.8, 3066.9, 0.0); ( 452269.8, 3770197.5, 317.6, 3066.9, 0.0); ( 452087.8, 3770201.1, 317.4, 3066.9, 0.0); ( 452365.5, 3769988.9, 315.6, 3066.9, 0.0); ( 452053.2, 3769889.6, 315.2, 3066.9, 0.0); ( 454290.1, 3769974.8, 315.3, 2731.4, 0.0); ( 454539.0, 3769826.6, 313.5, 2731.4, 0.0); ( 452423.7, 3769682.9, 305.6, 3066.9, 0.0); ( 452154.2, 3769692.2, 305.9, 3066.9, 0.0); ( 454912.8, 3770375.1, 323.5, 2731.4, 0.0); ( 454946.7, 3770523.9, 325.9, 2731.4, 0.0); ( 454913.4, 3770360.4, 323.3, 2731.4, 0.0); ( 455329.0, 3770822.7, 331.4, 2731.4, 0.0); ( 455107.7, 3770816.1, 330.1, 2731.4, 0.0); ( 454999.8, 3770834.1, 329.8, 2731.4, 0.0); ( 455329.8, 3770804.8, 331.3, 2731.4, 0.0); ( 455325.1, 3770415.6, 325.9, 2731.4, 0.0); ( 455325.1, 3770367.0, 325.2, 2731.4, 0.0); ( 455322.6, 3770267.3, 323.8, 2731.4, 0.0); ( 455327.6, 3770519.1, 327.5, 2731.4, 0.0); ( 455322.9, 3770561.4, 328.0, 2731.4, 0.0); ( 455330.7, 3770603.2, 328.5, 2731.4, 0.0); ( 454959.0, 3770572.5, 326.7, 2731.4, 0.0); ( 455127.1, 3770559.5, 327.0, 2731.4, 0.0); ( 453158.7, 3770937.9, 327.8, 3066.9, 0.0); ( 452421.7, 3770910.5, 322.7, 3066.9, 0.0); ( 454556.7, 3771053.1, 330.2, 3066.9, 0.0); *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 7 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** METEOROLOGICAL DAYS SELECTED FOR PROCESSING *** (1=YES; 0=NO) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 NOTE: METEOROLOGICAL DATA ACTUALLY PROCESSED WILL ALSO DEPEND ON WHAT IS INCLUDED IN THE DATA FILE. *** UPPER BOUND OF FIRST THROUGH FIFTH WIND SPEED CATEGORIES *** (METERS/SEC) 1.54, 3.09, 5.14, 8.23, 10.80, *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 8 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** UP TO THE FIRST 24 HOURS OF METEOROLOGICAL DATA *** Surface file: FONT_V11_trimmed.sfc Met Version: 22112 Profile file: FONT_V11_trimmed.pfl Surface format: FREE Profile format: FREE Surface station no.: 3102 Upper air station no.: 3190 Name: UNKNOWN Name: UNKNOWN Year: 2016 Year: 2016 First 24 hours of scalar data YR MO DY JDY HR H0 U* W* DT/DZ ZICNV ZIMCH M‐O LEN Z0 BOWEN ALBEDO REF WS WD HT REF TA HT ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 16 01 01 1 01 ‐33.6 0.350 ‐9.000 ‐9.000 ‐999. 500. 135.0 0.09 1.19 1.00 4.31 38. 10.0 284.3 9.0 16 01 01 1 02 ‐45.1 0.469 ‐9.000 ‐9.000 ‐999. 771. 242.2 0.09 1.19 1.00 5.71 44. 10.0 284.1 9.0 16 01 01 1 03 ‐36.8 0.383 ‐9.000 ‐9.000 ‐999. 574. 161.1 0.09 1.19 1.00 4.69 43. 10.0 284.1 9.0 16 01 01 1 04 ‐35.3 0.367 ‐9.000 ‐9.000 ‐999. 535. 148.5 0.09 1.19 1.00 4.52 41. 10.0 283.9 9.0 16 01 01 1 05 ‐20.4 0.212 ‐9.000 ‐9.000 ‐999. 251. 49.2 0.09 1.19 1.00 2.66 30. 10.0 283.6 9.0 16 01 01 1 06 ‐4.3 0.090 ‐9.000 ‐9.000 ‐999. 79. 15.1 0.09 1.19 1.00 1.18 346. 10.0 282.2 9.0 16 01 01 1 07 ‐1.7 0.067 ‐9.000 ‐9.000 ‐999. 42. 15.9 0.12 1.19 1.00 0.59 194. 10.0 280.6 9.0 16 01 01 1 08 ‐1.3 0.059 ‐9.000 ‐9.000 ‐999. 34. 13.4 0.08 1.19 0.53 0.69 14. 10.0 280.7 9.0 16 01 01 1 09 35.0 0.124 0.432 0.007 80. 105. ‐4.7 0.07 1.19 0.31 1.08 255. 10.0 282.7 9.0 16 01 01 1 10 86.7 0.127 0.917 0.005 310. 108. ‐2.0 0.07 1.19 0.24 0.95 253. 10.0 284.6 9.0 16 01 01 1 11 122.7 0.147 1.230 0.005 530. 136. ‐2.3 0.12 1.19 0.21 0.98 215. 10.0 286.4 9.0 16 01 01 1 12 140.5 0.207 1.381 0.005 653. 226. ‐5.5 0.16 1.19 0.20 1.44 135. 10.0 288.6 9.0 16 01 01 1 13 138.6 0.230 1.623 0.005 1076. 264. ‐7.6 0.10 1.19 0.20 1.94 90. 10.0 289.0 9.0 16 01 01 1 14 96.7 0.230 1.524 0.010 1276. 265. ‐11.0 0.10 1.19 0.22 2.04 80. 10.0 289.4 9.0 16 01 01 1 15 66.0 0.204 1.376 0.011 1375. 221. ‐11.1 0.10 1.19 0.25 1.81 86. 10.0 289.8 9.0 16 01 01 1 16 23.8 0.193 0.983 0.012 1392. 204. ‐26.4 0.10 1.19 0.34 1.89 82. 10.0 289.8 9.0 16 01 01 1 17 ‐8.6 0.134 ‐9.000 ‐9.000 ‐999. 119. 24.5 0.09 1.19 0.62 1.73 58. 10.0 289.0 9.0 16 01 01 1 18 ‐7.3 0.119 ‐9.000 ‐9.000 ‐999. 98. 19.8 0.09 1.19 1.00 1.55 34. 10.0 287.0 9.0 16 01 01 1 19 ‐8.1 0.124 ‐9.000 ‐9.000 ‐999. 105. 20.5 0.08 1.19 1.00 1.66 20. 10.0 285.1 9.0 16 01 01 1 20 ‐4.0 0.089 ‐9.000 ‐9.000 ‐999. 64. 15.6 0.13 1.19 1.00 1.05 91. 10.0 284.6 9.0 16 01 01 1 21 ‐3.4 0.082 ‐9.000 ‐9.000 ‐999. 56. 14.0 0.09 1.19 1.00 1.04 56. 10.0 283.6 9.0 16 01 01 1 22 ‐2.5 0.073 ‐9.000 ‐9.000 ‐999. 47. 13.5 0.09 1.19 1.00 0.84 53. 10.0 282.8 9.0 16 01 01 1 23 ‐4.2 0.089 ‐9.000 ‐9.000 ‐999. 64. 14.9 0.09 1.19 1.00 1.16 44. 10.0 282.7 9.0 16 01 01 1 24 ‐2.4 0.072 ‐9.000 ‐9.000 ‐999. 47. 13.6 0.09 1.19 1.00 0.83 59. 10.0 282.1 9.0 First hour of profile data YR MO DY HR HEIGHT F WDIR WSPD AMB_TMP sigmaA sigmaW sigmaV 16 01 01 01 9.0 0 ‐999. ‐99.00 284.3 99.0 ‐99.00 ‐99.00 16 01 01 01 10.0 1 38. 4.31 ‐999.0 99.0 ‐99.00 ‐99.00 F indicates top of profile (=1) or below (=0) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 9 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 1‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 59.77726 (17012001) 454514.86 3770786.06 50.89053 (19011622) 454034.35 3770517.35 39.67242 (16011021) 454048.71 3770385.92 66.98768 (20122416) 454182.29 3770421.75 84.87035 (20123120) 454142.55 3770420.62 68.86955 (17011219) 454625.62 3770785.69 46.02654 (19020407) 454827.07 3770784.47 38.77929 (22120317) 454752.59 3770566.53 58.55970 (19120516) 454835.61 3770558.60 55.61861 (19012919) 454812.42 3770415.14 57.79139 (16022518) 454913.75 3770480.46 42.52147 (16021118) 454925.35 3770700.83 41.81988 (19010417) 454693.99 3770943.18 38.82783 (17010901) 454368.01 3770918.76 42.57939 (19011706) 453794.80 3770744.18 17.03331 (16011021) 453971.91 3770386.76 50.70681 (20122416) 453937.64 3770444.98 32.18550 (22021104) 453953.91 3770386.77 47.85534 (20122416) 453992.13 3770444.71 37.20503 (17011219) 453912.32 3770386.53 42.23595 (20122416) 453880.11 3770440.50 27.86230 (22021104) 453864.72 3770443.99 26.78374 (22021104) 453892.00 3770343.38 48.50165 (20122416) 453845.52 3770381.27 36.36148 (20122416) 453756.12 3770381.81 28.80337 (20122416) 453736.62 3770343.88 31.56739 (20122416) 453828.86 3770443.92 24.52623 (22021104) 453790.96 3770279.76 29.39417 (20122416) 453771.85 3770281.37 28.51483 (20122416) 453656.79 3770594.13 16.57763 (20123120) 453650.82 3770437.04 17.23008 (17012507) 453730.36 3770758.17 16.01860 (16011021) 454061.44 3770113.91 58.64989 (22120416) 453983.24 3770162.63 43.06531 (16020921) 453983.88 3770095.38 42.74776 (20022619) 454129.86 3770114.50 86.90649 (22120416) 454390.90 3770146.06 187.69141 (22012917) 454378.15 3770242.63 456.66951 (16012717) 453628.04 3770153.73 19.88447 (16012120) 453331.19 3770122.83 13.32758 (22022820) 453296.71 3770270.82 12.80923 (19012404) 454635.77 3770147.25 86.30849 (22100702) 454744.96 3770119.96 64.88955 (19040906) 454639.83 3770088.09 73.09080 (19051105) 454856.74 3770082.33 50.21145 (19040906) 454787.57 3770075.32 51.53772 (19040906) 454853.55 3770149.91 51.73057 (19060302) 454867.57 3770221.95 52.63256 (17040305) 454867.26 3770294.31 60.64826 (17010221) 454698.95 3770289.53 97.49747 (17040305) 454630.12 3770001.75 61.79604 (19051105) 454859.72 3770001.75 40.41771 (20050422) 454928.73 3770010.30 38.91530 (19040906) 454545.24 3770002.36 93.65987 (16012717) 454376.71 3770010.30 70.83920 (17121122) 454040.24 3769981.60 45.29387 (22120416) 454914.07 3770171.51 45.37151 (17060203) 454913.46 3770231.96 50.32457 (17040305) 453614.68 3770780.33 13.81885 (16011021) 453305.84 3770765.12 9.65242 (20123120) 454195.51 3770945.23 33.80167 (16010704) 454923.46 3770771.03 35.62534 (22012418) 454923.46 3771038.97 32.84339 (17120324) 454924.00 3771278.30 30.95555 (16021319) 454933.34 3771200.44 30.87778 (19121504) 454799.23 3771302.36 31.50222 (22122821) 454613.27 3771298.98 33.02211 (22013121) 454087.50 3771276.16 30.28093 (17021706) 455732.13 3771151.77 24.64560 (22120617) 455146.83 3770887.16 29.86942 (16011505) 455330.77 3770872.07 32.26138 (22010722) 455325.74 3770924.52 30.76022 (22011822) 455350.18 3770868.48 32.12530 (22120818) 455124.63 3770415.95 28.20022 (17051202) 454838.81 3769930.96 35.83814 (22100702) 454960.97 3769945.62 31.85163 (20050422) 454849.81 3769882.70 31.39486 (19051105) 455044.03 3769898.59 26.61706 (20050422) 455185.16 3769966.42 25.25566 (20070802) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 10 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 1‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 28.84450 (22100702) 455120.97 3769660.75 17.64970 (22100702) 455143.99 3769654.61 17.76650 (22100702) 455057.73 3769795.12 24.25953 (22100702) 454950.48 3769483.39 17.93175 (16021721) 455047.08 3769487.06 18.98681 (19051105) 455186.02 3769487.43 15.35867 (19051105) 455228.61 3769489.33 13.39073 (22022518) 454670.56 3769664.99 31.23869 (16012717) 454442.93 3769677.47 29.21497 (22012917) 454817.24 3769446.56 15.54644 (22022602) 457073.40 3771679.08 14.65036 (22122218) 457180.76 3771676.87 14.38093 (17020318) 453293.96 3769817.93 11.22898 (16020921) 453163.51 3770000.16 10.08310 (16010406) 453419.51 3770001.32 13.54610 (16010323) 453310.35 3770010.68 11.97689 (16010406) 452792.85 3769973.03 7.43548 (16012120) 452612.97 3770098.22 6.52526 (22012221) 452566.21 3770175.93 6.24436 (19012404) 452402.16 3770197.51 5.65435 (19012404) 452394.97 3770047.86 5.57261 (22012221) 452636.00 3769852.88 6.16192 (16010406) 452269.78 3770197.51 5.18170 (19012404) 452087.75 3770201.11 4.62461 (19012404) 452365.47 3769988.86 5.50012 (22022820) 452053.21 3769889.57 4.55107 (22022820) 454290.08 3769974.82 60.78842 (16021005) 454539.03 3769826.60 50.60031 (16012717) 452423.72 3769682.87 5.04390 (16010406) 452154.23 3769692.25 4.38435 (16010406) 454912.82 3770375.11 50.51691 (17010221) 454946.69 3770523.91 47.12254 (16021118) 454913.41 3770360.45 54.19208 (17010221) 455329.00 3770822.74 32.58927 (16022519) 455107.72 3770816.10 34.24858 (22011822) 454999.84 3770834.08 32.80313 (22012418) 455329.83 3770804.76 32.47619 (16022519) 455325.06 3770415.64 26.09603 (17051202) 455325.06 3770367.01 25.28729 (17010221) 455322.57 3770267.26 26.25735 (17010221) 455327.56 3770519.13 28.53504 (16021619) 455322.94 3770561.45 29.45883 (16022919) 455330.69 3770603.23 29.42929 (16120120) 454959.01 3770572.49 46.74313 (16022620) 455127.10 3770559.48 36.60404 (16021118) 453158.66 3770937.93 11.82888 (17011218) 452421.67 3770910.46 4.21779 (17011219) 454556.71 3771053.14 36.99658 (22020521) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 11 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 8‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 37.42511 (17011108) 454514.86 3770786.06 28.66910 (17110508) 454034.35 3770517.35 19.27716m (20040724) 454048.71 3770385.92 24.61827 (16030724) 454182.29 3770421.75 48.59801 (16011024) 454142.55 3770420.62 38.63354 (16011024) 454625.62 3770785.69 28.30026 (19020408) 454827.07 3770784.47 26.02501m (16031408) 454752.59 3770566.53 36.67098 (22121024) 454835.61 3770558.60 36.51491 (17012124) 454812.42 3770415.14 40.14783 (16120624) 454913.75 3770480.46 32.28173 (16120624) 454925.35 3770700.83 26.24123 (22121024) 454693.99 3770943.18 19.49855 (19020408) 454368.01 3770918.76 20.16045 (22123024) 453794.80 3770744.18 7.83264m (20040724) 453971.91 3770386.76 18.37063 (16030724) 453937.64 3770444.98 14.94987 (16011024) 453953.91 3770386.77 17.28876 (16030724) 453992.13 3770444.71 18.42738 (16011024) 453912.32 3770386.53 15.16874 (16030724) 453880.11 3770440.50 12.23256 (16011024) 453864.72 3770443.99 11.63338 (16011024) 453892.00 3770343.38 16.55366 (16030724) 453845.52 3770381.27 12.80304 (16030724) 453756.12 3770381.81 10.19824 (16030724) 453736.62 3770343.88 10.87082 (16030724) 453828.86 3770443.92 10.42274 (17012508) 453790.96 3770279.76 13.26569 (16030724) 453771.85 3770281.37 12.66369 (16030724) 453656.79 3770594.13 6.39932 (16011024) 453650.82 3770437.04 7.22513 (17012508) 453730.36 3770758.17 7.04341m (20040724) 454061.44 3770113.91 35.82900 (19122124) 453983.24 3770162.63 26.56932 (19122124) 453983.88 3770095.38 28.24737 (19122124) 454129.86 3770114.50 39.99835 (19122124) 454390.90 3770146.06 89.26734 (22020508) 454378.15 3770242.63 230.29162 (16021008) 453628.04 3770153.73 8.51937 (16010724) 453331.19 3770122.83 5.04348 (16010724) 453296.71 3770270.82 5.26177 (16030724) 454635.77 3770147.25 33.58813 (19122308) 454744.96 3770119.96 22.51534 (20040824) 454639.83 3770088.09 27.31077 (22122108) 454856.74 3770082.33 15.36385 (20040824) 454787.57 3770075.32 18.27065 (19122308) 454853.55 3770149.91 22.00380 (20041224) 454867.57 3770221.95 29.14239 (20041224) 454867.26 3770294.31 33.55496 (19111924) 454698.95 3770289.53 56.26802 (20041224) 454630.12 3770001.75 22.23559 (22122108) 454859.72 3770001.75 13.56732 (19122308) 454928.73 3770010.30 11.92817 (19122308) 454545.24 3770002.36 26.79152 (20120124) 454376.71 3770010.30 42.73007 (22020508) 454040.24 3769981.60 22.47870 (19110824) 454914.07 3770171.51 22.39107 (20041224) 454913.46 3770231.96 26.33863 (20041224) 453614.68 3770780.33 5.78633m (20040724) 453305.84 3770765.12 3.32371 (16011024) 454195.51 3770945.23 12.41803 (22121108) 454923.46 3770771.03 25.29160 (16013024) 454923.46 3771038.97 19.99827m (16031408) 454924.00 3771278.30 12.84012 (22082108) 454933.34 3771200.44 16.25574 (22072408) 454799.23 3771302.36 12.87850 (17011108) 454613.27 3771298.98 11.56354 (20031908) 454087.50 3771276.16 8.02918 (22121108) 455732.13 3771151.77 14.33155m (20100724) 455146.83 3770887.16 19.60143m (20100724) 455330.77 3770872.07 19.59581m (20100724) 455325.74 3770924.52 19.40012m (20100724) 455350.18 3770868.48 19.21963m (20100724) 455124.63 3770415.95 18.38162 (20010824) 454838.81 3769930.96 11.00933 (19122308) 454960.97 3769945.62 10.37696 (19122308) 454849.81 3769882.70 10.47089 (22122108) 455044.03 3769898.59 8.55352 (19122308) 455185.16 3769966.42 7.08516 (20041224) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 12 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 8‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 8.26326 (19122308) 455120.97 3769660.75 4.67075 (22122108) 455143.99 3769654.61 4.60938 (19122308) 455057.73 3769795.12 6.75724 (19122308) 454950.48 3769483.39 5.75214 (17112808) 455047.08 3769487.06 5.65841 (22122108) 455186.02 3769487.43 4.50552 (22122108) 455228.61 3769489.33 4.01082 (22122108) 454670.56 3769664.99 10.19215 (20120124) 454442.93 3769677.47 15.07460 (22020508) 454817.24 3769446.56 5.87267 (20120124) 457073.40 3771679.08 8.40874 (20092524) 457180.76 3771676.87 7.73480 (20092524) 453293.96 3769817.93 5.78886 (19122124) 453163.51 3770000.16 4.21093 (16010324) 453419.51 3770001.32 6.28800 (16010324) 453310.35 3770010.68 5.28371 (16010324) 452792.85 3769973.03 2.71082 (16010724) 452612.97 3770098.22 2.42498 (16030724) 452566.21 3770175.93 2.38560 (16030724) 452402.16 3770197.51 2.07461 (16030724) 452394.97 3770047.86 1.98887 (16030724) 452636.00 3769852.88 2.41296 (16010324) 452269.78 3770197.51 1.86990 (16030724) 452087.75 3770201.11 1.63508 (16030724) 452365.47 3769988.86 1.86080 (16030724) 452053.21 3769889.57 1.41705 (16030724) 454290.08 3769974.82 43.02626 (16021008) 454539.03 3769826.60 20.36928 (22013008) 452423.72 3769682.87 2.16211 (16010324) 452154.23 3769692.25 1.67230 (16010324) 454912.82 3770375.11 28.90298 (17103024) 454946.69 3770523.91 34.40451 (17012124) 454913.41 3770360.45 28.57657 (17103024) 455329.00 3770822.74 18.30548m (20100724) 455107.72 3770816.10 22.28013m (20100724) 454999.84 3770834.08 21.82205 (16013024) 455329.83 3770804.76 17.63817m (20100724) 455325.06 3770415.64 16.55088 (20010824) 455325.06 3770367.01 12.24620 (17103024) 455322.57 3770267.26 13.17720 (19111924) 455327.56 3770519.13 19.56182 (20010824) 455322.94 3770561.45 18.24792 (20010824) 455330.69 3770603.23 19.21472 (17012124) 454959.01 3770572.49 33.76103 (17012124) 455127.10 3770559.48 25.40531 (17012124) 453158.66 3770937.93 4.27702m (20040724) 452421.67 3770910.46 1.29907 (17011224) 454556.71 3771053.14 15.97593 (20031908) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 13 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 24‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454512.78 3770712.38 16.64208 (17110524) 454514.86 3770786.06 13.11282 (22123024) 454034.35 3770517.35 11.99100m (20040724) 454048.71 3770385.92 14.92642 (19013124) 454182.29 3770421.75 30.37580 (16011024) 454142.55 3770420.62 23.68499 (16011024) 454625.62 3770785.69 13.30556 (17011024) 454827.07 3770784.47 14.00624m (16031424) 454752.59 3770566.53 23.45791 (19020524) 454835.61 3770558.60 23.04454 (17012124) 454812.42 3770415.14 24.92713 (16051524) 454913.75 3770480.46 17.50598 (17012124) 454925.35 3770700.83 14.94699 (22033124) 454693.99 3770943.18 9.10528 (17011124) 454368.01 3770918.76 10.14884 (22123024) 453794.80 3770744.18 4.65930m (20040724) 453971.91 3770386.76 10.68389 (19013124) 453937.64 3770444.98 8.95490 (16011024) 453953.91 3770386.77 9.96300 (19013124) 453992.13 3770444.71 11.02356 (16011024) 453912.32 3770386.53 8.56277 (19013124) 453880.11 3770440.50 7.35921 (16011024) 453864.72 3770443.99 6.99834 (16011024) 453892.00 3770343.38 8.23186 (19013124) 453845.52 3770381.27 6.90965 (19013124) 453756.12 3770381.81 5.34064 (19013124) 453736.62 3770343.88 5.14421 (19013124) 453828.86 3770443.92 6.26975 (16011024) 453790.96 3770279.76 5.88033 (19013124) 453771.85 3770281.37 5.57939 (19013124) 453656.79 3770594.13 3.82025 (16011024) 453650.82 3770437.04 3.96717 (16011024) 453730.36 3770758.17 4.13182m (20040724) 454061.44 3770113.91 22.96149 (19122124) 453983.24 3770162.63 15.92608 (19122124) 453983.88 3770095.38 17.24191 (19122124) 454129.86 3770114.50 27.87973 (19122124) 454390.90 3770146.06 52.63474 (20120424) 454378.15 3770242.63 156.32149 (16012724) 453628.04 3770153.73 3.78199 (16010724) 453331.19 3770122.83 2.22922 (16010724) 453296.71 3770270.82 2.10075 (19013124) 454635.77 3770147.25 17.92214 (19122324) 454744.96 3770119.96 11.45182 (19122324) 454639.83 3770088.09 13.89109 (22122124) 454856.74 3770082.33 7.63743 (19122324) 454787.57 3770075.32 9.33944 (19122324) 454853.55 3770149.91 11.81715 (20041224) 454867.57 3770221.95 16.17205 (20041224) 454867.26 3770294.31 19.32146 (16051524) 454698.95 3770289.53 33.99470 (20041224) 454630.12 3770001.75 11.52951 (17112824) 454859.72 3770001.75 6.87057 (19122324) 454928.73 3770010.30 6.00695 (19122324) 454545.24 3770002.36 13.86930 (20120124) 454376.71 3770010.30 24.54586 (20120424) 454040.24 3769981.60 14.86078 (19012424) 454914.07 3770171.51 12.04424 (20041224) 454913.46 3770231.96 14.76750 (20041224) 453614.68 3770780.33 3.35689m (20040724) 453305.84 3770765.12 1.97891 (16011024) 454195.51 3770945.23 7.44663 (22123124) 454923.46 3770771.03 12.69779 (19030824) 454923.46 3771038.97 10.38452 (17011024) 454924.00 3771278.30 5.98368 (22082124) 454933.34 3771200.44 7.83175 (22072424) 454799.23 3771302.36 5.84630 (17011124) 454613.27 3771298.98 4.65680 (20031924) 454087.50 3771276.16 4.88615 (22123124) 455732.13 3771151.77 6.12635 (19073024) 455146.83 3770887.16 9.67554 (22033124) 455330.77 3770872.07 9.49426 (22033124) 455325.74 3770924.52 9.07272 (22033124) 455350.18 3770868.48 9.35920 (22033124) 455124.63 3770415.95 11.33528 (16051524) 454838.81 3769930.96 5.82956 (19122324) 454960.97 3769945.62 5.19270 (19122324) 454849.81 3769882.70 5.14584 (22122124) 455044.03 3769898.59 4.25041 (19122324) 455185.16 3769966.42 3.81609 (19050824) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 14 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE 1ST HIGHEST 24‐HR AVERAGE CONCENTRATION VALUES FOR SOURCE GROUP: ALL *** INCLUDING SOURCE(S): VOL1 , *** DISCRETE CARTESIAN RECEPTOR POINTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) X‐COORD (M) Y‐COORD (M) CONC (YYMMDDHH) ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 454949.80 3769855.15 4.30514 (19122324) 455120.97 3769660.75 2.49850 (19122324) 455143.99 3769654.61 2.44845 (19122324) 455057.73 3769795.12 3.45730 (19122324) 454950.48 3769483.39 2.82824 (17112824) 455047.08 3769487.06 2.60310 (22122124) 455186.02 3769487.43 2.11344 (22122124) 455228.61 3769489.33 1.92375 (22122124) 454670.56 3769664.99 4.92015 (20120124) 454442.93 3769677.47 7.81190 (22020524) 454817.24 3769446.56 2.84593 (20120124) 457073.40 3771679.08 2.96064 (17060524) 457180.76 3771676.87 2.90733 (17060524) 453293.96 3769817.93 3.24280 (19122124) 453163.51 3770000.16 1.81857 (19121824) 453419.51 3770001.32 3.00666 (19122124) 453310.35 3770010.68 2.23400 (16121724) 452792.85 3769973.03 1.16763 (19121824) 452612.97 3770098.22 0.92374 (19010824) 452566.21 3770175.93 0.93331 (19010824) 452402.16 3770197.51 0.82324 (19010824) 452394.97 3770047.86 0.75550 (17010724) 452636.00 3769852.88 1.06170 (19121824) 452269.78 3770197.51 0.74539 (19010824) 452087.75 3770201.11 0.65625 (19010824) 452365.47 3769988.86 0.74222 (16010724) 452053.21 3769889.57 0.60205 (16010724) 454290.08 3769974.82 26.12606 (22011024) 454539.03 3769826.60 8.88408 (22011224) 452423.72 3769682.87 0.87917 (16010324) 452154.23 3769692.25 0.73478 (19121824) 454912.82 3770375.11 20.21300 (16051524) 454946.69 3770523.91 20.74831 (17012124) 454913.41 3770360.45 20.23347 (16051524) 455329.00 3770822.74 9.39604 (22033124) 455107.72 3770816.10 11.35946 (22033124) 454999.84 3770834.08 10.95952 (22050224) 455329.83 3770804.76 9.96325 (17012124) 455325.06 3770415.64 8.97532 (16051524) 455325.06 3770367.01 8.08069 (16051524) 455322.57 3770267.26 6.72307 (16051524) 455327.56 3770519.13 9.22237 (16051724) 455322.94 3770561.45 9.72771 (17012124) 455330.69 3770603.23 11.04370 (17012124) 454959.01 3770572.49 20.63087 (17012124) 455127.10 3770559.48 14.93052 (17012124) 453158.66 3770937.93 2.12100m (20040724) 452421.67 3770910.46 0.72354 (17011224) 454556.71 3771053.14 7.08854 (22123024) *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 15 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE SUMMARY OF HIGHEST 1‐HR RESULTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** DATE NETWORK GROUP ID AVERAGE CONC (YYMMDDHH) RECEPTOR (XR, YR, ZELEV, ZHILL, ZFLAG) OF TYPE GRID‐ID ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ALL HIGH 1ST HIGH VALUE IS 456.66951 ON 16012717: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC *** RECEPTOR TYPES: GC = GRIDCART GP = GRIDPOLR DC = DISCCART DP = DISCPOLR *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 16 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE SUMMARY OF HIGHEST 8‐HR RESULTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** DATE NETWORK GROUP ID AVERAGE CONC (YYMMDDHH) RECEPTOR (XR, YR, ZELEV, ZHILL, ZFLAG) OF TYPE GRID‐ID ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ALL HIGH 1ST HIGH VALUE IS 230.29162 ON 16021008: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC *** RECEPTOR TYPES: GC = GRIDCART GP = GRIDPOLR DC = DISCCART DP = DISCPOLR *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 17 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** THE SUMMARY OF HIGHEST 24‐HR RESULTS *** ** CONC OF DPM IN MICROGRAMS/M**3 ** DATE NETWORK GROUP ID AVERAGE CONC (YYMMDDHH) RECEPTOR (XR, YR, ZELEV, ZHILL, ZFLAG) OF TYPE GRID‐ID ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ALL HIGH 1ST HIGH VALUE IS 156.32149 ON 16012724: AT ( 454378.15, 3770242.63, 319.05, 2731.43, 0.00) DC *** RECEPTOR TYPES: GC = GRIDCART GP = GRIDPOLR DC = DISCCART DP = DISCPOLR *** AERMOD ‐ VERSION 24142 *** *** C:\Users\adadabhoy\Desktop\AERMOD\16586‐Jensen Precast Industrial\16 *** 10/23/25 *** AERMET ‐ VERSION 22112 *** *** *** 09:59:15 PAGE 18 *** MODELOPTs: RegDFAULT CONC ELEV FLGPOL URBAN ADJ_U* *** Message Summary : AERMOD Model Execution *** ‐‐‐‐‐‐‐‐‐ Summary of Total Messages ‐‐‐‐‐‐‐‐ A Total of 0 Fatal Error Message(s) A Total of 73 Warning Message(s) A Total of 348 Informational Message(s) A Total of 43848 Hours Were Processed A Total of 22 Calm Hours Identified A Total of 326 Missing Hours Identified ( 0.74 Percent) ******** FATAL ERROR MESSAGES ******** *** NONE *** ******** WARNING MESSAGES ******** ME W186 65 MEOPEN: THRESH_1MIN 1‐min ASOS wind speed threshold used 0.50 ME W187 65 MEOPEN: ADJ_U* Option for Stable Low Winds used in AERMET CN W733 1744 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2016031316 CN W732 1752 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2016031324 CN W733 1768 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2016031416 CN W732 1776 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2016031424 CN W733 9952 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2017021816 CN W732 9960 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2017021824 MX W450 17545 CHKDAT: Record Out of Sequence in Meteorological File at: 19010101 MX W450 17545 CHKDAT: Record Out of Sequence in Meteorological File at: 1 year gap CN W733 22112 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2019071008 CN W733 22864 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2019081016 CN W732 22872 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2019081024 CN W733 28048 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020031316 CN W732 28056 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020031324 CN W733 28072 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020031416 CN W732 28080 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020031424 CN W733 28096 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020031516 CN W732 28104 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020031524 CN W733 28120 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020031616 CN W732 28128 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020031624 CN W733 28528 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020040216 CN W732 28536 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020040224 CN W733 28552 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020040316 CN W732 28560 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020040324 CN W733 28648 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020040716 CN W732 28656 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020040724 CN W733 28960 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020042016 CN W732 28968 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020042024 CN W733 33040 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020100716 CN W732 33048 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020100724 CN W733 33112 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020101016 CN W732 33120 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020101024 CN W733 33904 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020111216 CN W732 33912 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020111224 CN W733 34048 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020111816 CN W732 34056 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020111824 CN W733 34096 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112016 CN W732 34104 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112024 CN W733 34120 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112116 CN W732 34128 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112124 CN W733 34144 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112216 CN W732 34152 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112224 CN W733 34168 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112316 CN W732 34176 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112324 CN W733 34192 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112416 CN W732 34200 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112424 CN W733 34216 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020112516 CN W732 34224 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020112524 CN W733 34696 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020121516 CN W732 34704 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020121524 CN W733 34840 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2020122116 CN W732 34848 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2020122124 MX W450 35089 CHKDAT: Record Out of Sequence in Meteorological File at: 22010101 MX W450 35089 CHKDAT: Record Out of Sequence in Meteorological File at: 1 year gap CN W733 38296 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022051416 CN W732 38304 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022051424 CN W733 39016 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022061316 CN W732 39024 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022061324 CN W733 40432 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022081116 CN W732 40440 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022081124 CN W733 41128 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022090916 CN W732 41136 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022090924 CN W733 42664 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022111216 CN W732 42672 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022111224 CN W733 42688 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022111316 CN W732 42696 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022111324 CN W733 42712 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022111416 CN W732 42720 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022111424 CN W733 42736 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022111516 CN W732 42744 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022111524 CN W733 43168 AVER: 8‐hr avg, < 6 hours of data, calms policy used. 2022120316 CN W732 43176 AVER: 24‐hr avg, < 18 hours of data, calms policy used. 2022120324 ************************************ *** AERMOD Finishes Successfully *** ************************************