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4 Environmental Analysis <br /> 4.3 Air Quality <br /> Table 4.3-11. Estimated Maximum Daily Operational Criteria Air Pollutants Emissions <br /> ROG NOxCO sox PM10 <br /> PoundsEmission Source <br /> Area,,Mobile,and Off-road 1.45 8.60 9.72 0.04 0.32 0.29 <br /> SJVAPCD Threshold 100 100 100 100 100 100 <br /> Threshold Exceeded? No No No No No No <br /> CO-carbon monoxide;M-nitrogen oxide;PM,o-particulate matter between 2.5 and 10 micrometers in diameter;PM2.5-particulate matter 2.5 micrometers <br /> in diameter or smaller;ROG—reactive organic gas;SJVAPCD—San Joaquin Valley Air Pollution Control District;SO,—sulfur oxide <br /> As shown in Tables 4.3-10 and 4.3-11, operational emissions would not exceed the SJVAPCD <br /> thresholds for ROG, NO, CO, SO, PM1o, and PM2.5. Since operational activities would be <br /> minimal, including only routine inspection and maintenance, ambient air quality modeling was not <br /> required. Additionally, traffic associated with operations would be negligible and would not result <br /> in CO hotspots at intersections. Therefore, the operational impacts would be less than significant. <br /> Mitigation: None required; however, the Applicant-proposed compliance with Rule 9510 and <br /> preparation of a Dust Control Plan have been included as Mitigation Measures AQ-1 and AQ- <br /> 2, respectively to ensure their implementation. <br /> IMPACT 4.3-3: Would the project expose sensitive receptors to substantial pollutant <br /> concentrations? (Less than Significant Impact) <br /> Sensitive receptors for air quality include facilities or land uses that serve or house members of <br /> the population that are particularly sensitive to the effects of air pollutants, such as children, the <br /> elderly, and people with illnesses. Examples of sensitive receptors include schools, hospitals, and <br /> residential areas. The nearest rural residences on land not owned by the current property owner <br /> are located approximately 1,000 feet north of the Project site on the other side of West Patterson <br /> Pass and 1,000 feet southwest of the Project site at the southern terminus of Midway Road to the <br /> west of the onsite substation, to the east of Midway Road. <br /> In addition to the significance thresholds for criteria pollutants, the SJVPACD has established <br /> significance thresholds for TAC emissions. According to Section 39655 of the California Health <br /> and Safety Code, a TAC is "an air pollutant which may cause or contribute to an increase in <br /> mortality or an increase in serious illness, or which may pose a present or potential hazard to <br /> human health." TACs consist of a variety of compounds, including metals, minerals, soot, and <br /> hydrocarbon-based chemicals. Sources of TACs include industrial processes, such as petroleum <br /> refining and chrome-plating operations; commercial operations, such as gasoline stations and dry <br /> cleaners; and motor vehicle exhaust. <br /> Impacts to sensitive receptors are typically evaluated by analyzing the potential for health effects <br /> to result from exposure to project-related TACs. In addition, the analysis evaluates the potential <br /> for project construction to result in exposure of workers and other receptors to the dust-borne <br /> spores that cause Valley Fever. Impact 4.3-2 describes the analysis conducted for air contaminant <br /> emissions from construction and operation of the Project. <br /> The Project consists of construction of a battery energy storage facility that may have the potential <br /> to affect nearby sensitive receptors. The use of combustion equipment in Project construction <br /> activities could result in elevated concentrations of DPM,which could lead to an increase in cancer <br /> risk or chronic health impacts. <br /> Griffith Energy Storage Project 4.3-27 Tetra Tech/SCH 2022120675 <br /> Draft Environmental Impact Report August 2023 <br />