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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3.3 Noise<br />
The extent to which noise‐sensitive receptors in the project area are affected by traffic noise<br />
depends on their respective proximity to the roadways and their individual sensitivity to traffic<br />
noise. The primary roadway of concern for traffic noise is Larkin Road because Larkin Road<br />
provides primary access to Clay Pit SVRA. The receptor nearest to the SVRA along Larkin Road is a<br />
residence located approximately 115 feet west of Larkin Road, just south of Airport Park. This<br />
residence is approximately 130 feet from the Larkin Road centerline; thus, existing traffic noise<br />
levels at this residence are estimated to be approximately 60 dBA Ldn.<br />
Future traffic levels were projected based on the existing number of vehicles entering the SVRA,<br />
future population growth in Butte County, and improvements at the SVRA (e.g., new tracks, trails,<br />
entrance facilities). Implementation of the General Plan, including construction and operation of<br />
the headquarters facilities, is projected to result in 19,837 total vehicles accessing Clay Pit SVRA<br />
annually (approximately 55 vehicles daily). As shown in Table 3.3‐4, future increases in traffic<br />
noise levels would range from 0 dBA to 11 dBA Ldn. The greatest increase would occur along the<br />
SVRA access road from Larkin Road and to the south. However, no noise‐sensitive receptors are<br />
adjacent to this roadway segment. In areas where larger increases in traffic noise are accountable<br />
to the project, low traffic volumes currently exist, so although increases may occur in these areas,<br />
the overall noise level would remain well below 60 dBA Ldn following project implementation.<br />
Where noise‐sensitive receptors are located on Larkin Road between Airport Park and Hamilton<br />
Road, future increases in traffic would result in no increase in noise levels (Table 3.3‐4).<br />
Construction activities are anticipated to result in a short‐term, temporary addition of<br />
approximately 60 haul trucks per day for 42 days along Larkin Road and SR 162. The existing<br />
peak‐hour traffic volume along Larkin Road between the SVRA access road and SR 162 is 426 trips<br />
per day, and the existing peak‐hour traffic volume along SR 162 between SR 99 and Larkin Road is<br />
280 trips per day. Additional traffic volumes generated by construction activities would be less<br />
than 15% of peak hour traffic along Larkin Road and would be less than 22% of peak hour traffic<br />
along SR 162. For construction activities to create a significant increase (+3 dBA) in traffic noise,<br />
the number of trips would need to double (i.e., increase 100%). The increase in traffic from<br />
construction activities would be substantially less than 100%.<br />
Because implementing the Clay Pit SVRA General Plan, including constructing and operating the<br />
headquarters facilities, would not increase off‐site traffic noise levels at noise‐sensitive receptors,<br />
and because construction activities would increase off‐site traffic noise levels by an insubstantial<br />
amount (less than 3 dBA), off‐site noise levels related to traffic would be a lessthansignificant<br />
impact.<br />
Mitigation Measures: No mitigation is required.<br />
IMPACT<br />
3.3-3<br />
Exposure of Sensitive Receptors to Groundborne Noise and Vibration Levels from SVRA<br />
Operations<br />
Clay Pit State Vehicular Recreation Area<br />
<strong>Draft</strong> EIR 3.3-19 February 2012