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

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3.2 Air Quality<br />

the project would be inconsistent with Butte County AQMD’s air quality attainment plan;<br />

the project would generate emissions such that exceedance of a CAAQS or NAAQS could<br />

occur and potentially affect public health/welfare;<br />

the project would generate toxic or hazardous air pollutants such that potential impacts to<br />

human health/welfare would occur; or<br />

the project would create objectionable odors that could affect a substantial number of<br />

people (Butte County AQMD 2008:Section 2.4).<br />

3.2.4 <strong>Environmental</strong> Evaluation<br />

Evaluation Methodology<br />

Air quality impacts were assessed in accordance with methodologies recommended by CARB and<br />

Butte County AQMD in its CEQA Air Quality Handbook.<br />

Temporary (construction) and permanent (operational) criteria pollutant emissions were<br />

calculated using the URBEMIS2007 Version 9.2.4 computer modeling program, data from the<br />

URBEMIS2007 Version 9.2.4 Users Guide (Rimpo and Associates 2008), and OFFROAD2007 (CARB<br />

2007). Predicted construction and operational emissions were then compared with applicable<br />

Butte County AQMD significance thresholds. Mobile sources of criteria pollutants calculated using<br />

URBEMIS2007 include passenger vehicles; light‐, medium‐, and heavy‐duty trucks; buses;<br />

motorcycles; and motor homes. URBEMIS2007 includes exhaust emissions and road dust from<br />

vehicles traveling on roadways.<br />

For on‐road mobile source emissions, URBEMIS2007 relies on CARB’s EMFAC2007, Version 2.3,<br />

computer modeling program. EMFAC calculates emissions from on‐road motor vehicles, including<br />

passenger vehicles; light‐, medium‐, and heavy‐duty trucks; buses; motorcycles; and motor homes.<br />

For scenarios where large material would be hauled, stand‐alone EMFAC modeling was<br />

performed.<br />

Estimates of on‐road vehicle trips by visitors and staff members traveling to and from the SVRA<br />

were derived from estimates of existing visitor numbers and from projections of visits following<br />

implementation of the Clay Pit SVRA General Plan. (Refer to Section 3.1, “Transportation and<br />

Traffic,” in this DEIR and Appendix C in the Clay Pit SVRA General Plan.) The construction of new<br />

visitor facilities envisioned in the General Plan would be expected to increase visitor trips to and<br />

from the project site by 50 average daily trips (ADT), with another 12 ADT by employees for a<br />

total of 62 on‐road vehicle trips attributable to implementing the General Plan. Increases in<br />

regional population and associated increases in the number of Clay Pit SVRA visitors would be<br />

expected to increase this estimate to 69 ADT in 2017 and 85 ADT in 2030.<br />

Clay Pit State Vehicular Recreation Area<br />

February 2012 3.2-8 <strong>Draft</strong> EIR

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