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Reso13 PC 13-09 2859 Initial Study Mitigated Negative Declaration Kensington
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Reso13 PC 13-09 2859 Initial Study Mitigated Negative Declaration Kensington
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Last modified
6/6/2013 4:26:34 PM
Creation date
5/28/2013 9:28:11 AM
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CC Index
CC Index - Document Type
Resolution
Meeting Type
Regular
Agency Type
Planning Commission
Date
5/21/2013
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4.12 NOISE <br /> The following discussion is based,in part, on a noise assessment prepared by Illingworth& Rodkin <br /> in September 2012. The noise assessment can be found in Appendix F. <br /> 4.12.1 Setting <br /> 4.12.1.1 Methodology <br /> Noise is defined as unwanted sound. Sound levels are usually measured in decibels (dB)with 0 dB <br /> corresponding roughly to the threshold of hearing. Most of the sounds which we hear in the <br /> environment do not consist of a single frequency,but rather a broad band of frequencies,with each <br /> frequency differing in sound level. The intensities of each frequency add together to generate a <br /> sound. The method commonly used to quantify environmental sounds consists of evaluating all of <br /> the frequencies of a sound in accordance with a weighting that reflects the fact that human hearing is <br /> less sensitive at low frequencies and extreme high frequencies than in the frequency mid-range. This <br /> is called"A"weighting, and the decibel level so measured is called the A-weighted sound level <br /> (dBA). In practice,the level of a sound is conveniently measured using a sound level meter that <br /> includes an electrical filter corresponding to the A-weighting curve. Typical A-weighted levels <br /> measured in the environment are shown in Appendix F for different types of noise. <br /> Although the A-weighted noise level may adequately indicate the level of environmental noise at any <br /> instant in time, community noise levels vary continuously. Most environmental noise includes a <br /> conglomeration of noise from distant sources which create a relatively steady background noise in <br /> which no particular source is identifiable. To describe the time-varying character of environmental <br /> noise,the statistical noise descriptors, Lo1, LIO, Lso, and Lgo, are commonly used. They are the A- <br /> weighted noise levels equaled or exceeded during 1%, 10%, 50%, and 90% of a stated time period. <br /> A single number descriptor called the Leq is also widely used. The Leq is the average A-weighted <br /> noise level during a stated period of time. <br /> In determining the daily level of environmental noise,it is important to account for the difference in <br /> response of people to daytime and nighttime noises. During the nighttime, exterior background <br /> noises are generally lower than daytime levels. However, most household noise also decreases at <br /> night and exterior noises become very noticeable. Further, most people sleep at night and are very <br /> sensitive to noise intrusion. To account for human sensitivity to nighttime noise levels, a descriptor, <br /> DNL (day/night average sound level),was developed. The DNL divides the 24-hour day into the <br /> daytime of 7:00 AM to 10:00 PM and the nighttime of 10:00 PM to 7:00 AM. The nighttime noise <br /> level is weighted to 10 dB higher than the daytime noise level. The Community Noise Equivalent <br /> Level(CNEL)is another 24-hour average which includes both an evening and nighttime weighting. <br /> 4.12.1.2 Noise Standards <br /> Based on the City's General Plan, Table 4 shows the noise levels considered consistent with specific <br /> land uses. For mixed-use districts,including the proposed project, outdoor noise levels of up to 60 <br /> decibels are considered acceptable and up to 75 decibels are permitted only after a detailed analysis <br /> of noise reduction requirements are made. <br /> Kensington Assisted Living Facility Project 65 Initial Study <br /> Redwood City Apri12013 <br />
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