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Staff Recommendation <br /> Docket #SU-81-20 <br /> November 13, 1981 <br /> Page Three <br /> Noise <br /> Noise, although not specifically listed in the Planning Commission con- <br /> cerns and suggestions, is obviously an overriding concern as far as <br /> impacts to the residential areas of Tantra Subdivision, Hyview Subdivision <br /> and the Coliday Mobile Home Park. The latest acoustics report from <br /> Charles M. Salter Associates of San Francisco utilizes current state of <br /> the art techniques in establishing the ambient (existing) sound levels <br /> at four (4) sites, including the Coliday Mobile Home Park, two (2) sites <br /> in Hy-View Subdivision and one (1) site on the Tantra area. Minimum and <br /> maximum dBA levels were 40 and 60, respectively. The L level , which <br /> represents an average level exceeded 50% of the time, rNged from 45 to <br /> 47 dBA, with the L level (exceeded only 10% of the time) ranging from <br /> 49-53 dBA. Thus , 1Y is safe to say that average daytime ambient level in <br /> the residential areas is 45-50 dBA. <br /> There are basically three (3) factors that reduce sound levels, and these <br /> are listed from the 1st, which requires no action by the applicant, to <br /> the last, which requires .the most action by the applicant: <br /> 1) Masking by ambient levels <br /> 2) Attenuation by distance (conservatively 6 decibel loss for <br /> each doubling of distance) by moving noise sources further <br /> away from noise receivers <br /> 3) Construction of sound barriers which depending on height, <br /> bulk and location can reduce sound levels by 5 to 20 decibels. <br /> General Goals of Noise Impact Mitigation <br /> The optimum goal of mitigation measures is to assure that whenever pos- <br /> sible noise levels from the site do not exceed ambient levels in the <br /> residential areas. The secondary goal is to assure that any noise level <br /> increases are so minimal that there is very little or no impact. Finally, <br /> at points in time and locations where noise increases will have noticeable <br /> impact, operations should be scheduled and otherwise tailored so as to <br /> minimize the impact as much as possible. There are a number of sources <br /> which estimate expected reactions to noise increases or set standards <br /> for maximum daytime noise levels in residental areas. These are listed as <br /> follows: <br /> Source Noise Level Expected Response, etc. <br /> CRS 73 25-12-103 55dBA Higher Level Constitutes <br /> _ 5OdBA impulse Nuisance <br /> EPA 55dBA outdoor Higher Level interferes <br /> 45dBA indoor with normal conversation, <br /> activities <br /> ISO Recommendation ambient +OdBA No observed reaction <br /> R-1996 ambient +5dBA Sporadic complaints <br /> (as cited by ambient +10dBA Threats of community <br /> Salter Associates) action <br /> ambient +15dBA Vigorous community action <br /> EPA 50-6OdBA Noise becomes noticeable, <br /> may be a few complaints <br /> 60-7OdBA Widespread complaints , <br /> threat of legal action <br /> 70-8OdBA Several threats of legal <br /> action, appeals for <br /> government intervention <br />