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2009-034 (2) - Final Supplemental Environmental Impact Report for Fairhaven/Lincoln
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2009-034 (2) - Final Supplemental Environmental Impact Report for Fairhaven/Lincoln
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Last modified
4/7/2015 1:21:03 PM
Creation date
7/20/2009 5:23:52 PM
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City Clerk
Doc Type
Resolution
Doc #
2009-034
Date
7/6/2009
Destruction Year
Perm
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S. Environmental A nalysis <br />NOISE <br />• om u ity Noise Equivalent Level 111EL). The energy average of the A- weighted hte <br />occurring during a 24 -Jour period with d6 9 9 � sound bevels <br />p added to the sound levels occurring during the period <br />from 7 Phi to 10 P M and 10 dB added to the sound levels occurring durir the period from <br />7 <br />A1. 9 R 1 PM to <br />L.d, and CNEL values rarely differ by more than 1 dB. As a matter of practice, and NEL <br />considered to bee equivalent and are treated �, values are <br />q eated as such �r� this assessment, <br />Eloise Descriptors <br />Noise i s most often defined as unwan ed sound, Although soun d can be easily measured, the erne ticn <br />noise and the physical response to sound complicate the anal P p of <br />p +s of its impact an popre, People fudge the <br />relative magnitude of sound sensation in subjective terms such as "noisiness" or "loudness." <br />Characteristics of Sound <br />When are object vibrates, it radiates part of its energy as acoustical pressure in the form of a sound wave. <br />Sound can be described in terms of amplitude (loudness), frequency (pitch), or duration (time). The human <br />hearing system is not equally sensitive to sound at all frequencies. Therefore, to appro orate this human <br />frequency - dependent response, the - weighted filter system is used to adjust measured sound levels. The <br />normal range of human hearing extends from approximately 0 dBA to 140 dB A. <br />Unlike linear units such as inches or pounds, decibels are measured on a logarithmic scale, representing <br />points on a sharply rising curve. Because of the physical characteristics of noise transmission and noise <br />perception, the relative loudness of sound does not closely match the actual amounts of sound energy. <br />Table ,2 -1, Change in Sound Pressure Level, Presents the subjective effect of chap <br />levels. <br />� gas �n sound pressure <br />Table 5.2-1 <br />Chan a in Sound Pressure ILevel <br />lra a in Apparent Loudness <br />± 3 dB Threshold of human perceptibility <br />± 5 dB Cleanly nofteable change in noise level <br />10 dB Half or trice as laud <br />± 0 dB Much quieter or ruder <br />Source. Bies and Hansen 2003 <br />Bound is generated from a source and dissipates exponentially with distance from that source. When sound <br />is measured for distinct time intervals, the statistical distri bution of the overall sound level durin that eriod <br />can be obtained. The sound level equivalent L is the most cone 9 p <br />g �� commonly the parameter associated with such <br />measurements. L,,, is the average sound level over a given period of time. For example, the L.50 noise level is <br />the level that is exceeded 50 percent of the time; half the time the noise exceeds this level and half the time it <br />is less than this level. This level is also exceeded 30 minutes in an hour. Similarly, the L-02, L ,,and L values <br />are the noise levels that are exceeded 2, 8, and 25 percent of the time or 1, 3, and 15 minutes per Dour. <br />Other values typically noted during a noise survey are the and P <br />�,�� L. These are the minimum and <br />maximum noise levels obtained over the measurement period. <br />Page 5.2-2 he Planning Venter <br />Resolution No. 2009 -034 <br />Page 68 of 130 <br />March 2009 <br />
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