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Draft Environmental Impact Report - California Off Highway Vehicle ...

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3.2 Air Quality<br />

3.2 Air Quality<br />

This section presents details about the existing setting and regulatory setting for air quality. It also<br />

presents an analysis of the air quality impacts that would result from implementing the Clay Pit<br />

SVRA General Plan, including constructing and operating the headquarters facilities.<br />

3.2.1 Existing Setting<br />

The information in this section supplements the existing climate and air quality discussion for the<br />

project area provided in Section 2.3.1, “Physical Resources,” of the Clay Pit SVRA General Plan.<br />

Clay Pit SVRA is located within the Sacramento Valley Air Basin (SVAB), located in the northern<br />

portion of the Central Valley. The SVAB includes Butte, Colusa, Glenn, Sacramento, Shasta, Sutter,<br />

Tehama, Yolo, and Yuba Counties; the western urbanized portion of Placer County; and the<br />

northeastern portion of Solano County.<br />

Because of its inland location, the SVAB’s climate is more extreme than that of the San Francisco<br />

Bay Area or South Coast Air Basins. The winters are generally cool and wet, while the summers<br />

are hot and dry. Primary sources of air emissions in the nonurban areas are from fossil fuel<br />

combustion, on‐road vehicles and OHVs, agricultural tilling, fertilizer, livestock, and road dust.<br />

The City of Oroville is the closest population center to Clay Pit SVRA (approximately 2.5 miles<br />

northeast). Oroville has approximately 15,000 people and the greater Oroville area has a<br />

population of approximately 55,000 people. Much of the Oroville area’s economy is based on<br />

outdoor recreation, with about 1 million visitors per year (City of Oroville 2010).<br />

Butte County Ambient Air Quality<br />

As discussed in the General Plan, Section 2.7.3, “Regulatory Influences,” criteria air pollutants<br />

include ozone, carbon monoxide (CO), nitrogen dioxide (NO2), sulfur dioxide (SO2), respirable<br />

particulate matter with an aerodynamic resistance diameter of 10 micrometers or less (PM10), fine<br />

particulate matter with an aerodynamic resistance diameter of 2.5 micrometers or less (PM2.5),<br />

and lead. The <strong>California</strong> Air Resources Board (CARB) monitors criteria air pollutants within the<br />

SVAB using a number of monitoring stations. The monitoring station closest to the project site<br />

with complete monitoring data is in Chico approximately 22 miles to the north. This monitoring<br />

station measures ozone, CO, NO2, PM10, and PM2.5. In general, the measurements at this station<br />

represent the air quality near the SVRA. Table 3.2‐1 summarizes concentrations and exceedances<br />

of the <strong>California</strong> Ambient Air Quality Standards (CAAQS) and National Ambient Air Quality<br />

Standards (NAAQS) from the most recent 3 years (2008–2010) at the Chico station (CARB 2011a).<br />

Clay Pit State Vehicular Recreation Area<br />

<strong>Draft</strong> EIR 3.2-1 February 2012

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