Draft Environmental Impact Report - California Off Highway Vehicle ...
Draft Environmental Impact Report - California Off Highway Vehicle ...
Draft Environmental Impact Report - California Off Highway Vehicle ...
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3.2 Air Quality<br />
Rule 205, “Fugitive Dust Emissions,” was developed to reduce ambient concentrations and<br />
limit fugitive emissions of PM10 from construction activities; bulk material handling and<br />
storage; carryout/trackout (i.e., any bulk materials that adhere to the exterior surfaces of<br />
motor vehicles and/or equipment [including tires] and fall out or track onto a paved road,<br />
creating visible roadway dust) and similar activities; weed abatement activities; unpaved<br />
parking lots, staging areas, and roads; inactive disturbed land; disturbed open areas; and<br />
windblown dust.<br />
Rule 221: Phase I Vapor Recovery Requirements, which requires installation of an CARB‐<br />
certified Phase I vapor recovery system at the time of tank installation. Rule 222, Phase I<br />
Vapor Recovery Requirements, would not apply to the SVRA because it would not be<br />
dispensing gasoline for retail purposes.<br />
3.2.3 Thresholds of Significance<br />
The significance criteria for this analysis are based on the Butte County AQMD’s CEQA Air Quality<br />
Handbook. Under Butte County AQMD’s CEQA Air Quality Handbook (Butte County AQMD 2008:<br />
Section 2), a programmatic evaluation of a general plan, specific plan, or area plan can generally be<br />
done qualitatively. However this assumes that the plan being evaluated will involve different types<br />
of land use and can include measures/policies to reduce urban sprawl and dependence on motor<br />
vehicles, which is not the case with the Clay Pit SVRA General Plan. For this reason, a largely<br />
quantitative analysis was undertaken to evaluate the potential environmental impacts of<br />
implementing the General Plan related to air quality. Implementation of the General Plan,<br />
including construction and operation of the headquarters facilities, would have significant<br />
environmental impacts related to air quality if:<br />
the project construction or operations would generate regional emissions of ROG, NOX, and<br />
PM10 that exceed the thresholds in Table 3.2‐4;<br />
TABLE 3.24. THRESHOLDS OF SIGNIFICANCE FOR CRITERIA POLLUTANTS OF CONCERN<br />
Pollutant<br />
Daily Threshold for Project Emissions 1<br />
Level B Level C<br />
NOX 25 lbs/day 137 lbs/day<br />
ROG 25 lbs/day 137 lbs/day<br />
PM10 80 lbs/day 137 lbs/day<br />
Notes:<br />
1 Emissions that do not exceed Level B thresholds would require the use of Butte County AQMD’s standard<br />
mitigation measures. Emissions in excess of Level B thresholds but less than Level C would require, in addition to<br />
Butte County AQMD’s standard mitigation measures, incorporation of Butte County AQMD’s best available<br />
mitigation measures, to the extent feasible, to reduce project‐related emissions.<br />
Source: Butte County AQMD 2008:2‐2<br />
Clay Pit State Vehicular Recreation Area<br />
<strong>Draft</strong> EIR 3.2-7 February 2012