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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 /> Mitigation 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 />