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residential project, and residential projects are not considered significant stationary noise <br />sources, as are industrial facilities and specific service commercial uses such as <br />automotive repair facilities, salvage yards, and car washes, among others (San Joaquin <br />County 2016a). Project impacts related to noise increases would be less than significant <br />with implementation of mitigation for construction noise. <br />Level of Significance: Potentially significant <br />Mitiaation Measures: <br />NOISE -1: Project contractors shall use newer equipment with improved muffling <br />and ensure that all equipment items have intact and operational the <br />manufacturers' recommended noise abatement measures, such as <br />mufflers, engine enclosures, and engine vibration isolators. All <br />construction equipment shall be inspected at periodic intervals to <br />ensure proper maintenance and presence of noise control devices (e.g., <br />mufflers, shrouding, etc.). In accordance with the California Air <br />Resources Board's Regulation for In -Use Off -Road Diesel -Fueled <br />Fleets, idling of construction equipment for more than five minutes <br />shall be prohibited unless an activity is specifically exempted by the <br />Regulation. <br />Significance After Miti ag tion: Less than significant <br />b) Groundborne Vibration. <br />Groundborne vibration is not a common environmental problem. Some common sources <br />are trains, buses on rough roads, and construction activities such as blasting, pile driving, <br />and operating heavy earth -moving equipment. Construction vibration impacts include <br />human annoyance and building structural damage. However, construction impacts on the <br />project site would be temporary and short-term. The main source of vibrations is <br />anticipated to be grading equipment, which would no longer be used once the grading <br />portion of construction work is completed. The project would not generate groundborne <br />vibrations once work is completed. Project impacts related to groundborne vibrations <br />would be less than significant. <br />c) Exposure to Airport/Airstrip Noise. <br />As noted in Section 3.9, Hazards and Hazardous Materials, Stockton Metropolitan <br />Airport is approximately 2.25 miles south of the project site. Noise contours for the <br />airport were developed based on the Community Noise Equivalent Level (CNEL), which <br />is the same as the Lan but with an additional +5 -dB weighting applied to noise occurring <br />between 7:00 p.m. and 10:00 p.m. Based on the noise contour maps related to the <br />Stockton Metropolitan Airport, the projected 60 dBA CNEL contour extends no more <br />than 1.52 miles to the northwest of the airport facility and the 65 dBA CNEL contour <br />extends approximately 0.79 miles from the airport (both distances are with respect to the <br />end of the runway). Thus, noise from Stockton Metropolitan Airport operations would <br />not lead to ambient noise at the project site exceeding County noise standards. The <br />project site is beyond both noise contours. There are no private airstrips in the vicinity. <br />Pock Lane Public Review Draft IS/MND 3-55 May 2022 <br />