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change in Community response (i.e. complaints) would be ex- <br />pected. <br />l <br />Recent studies have shown that changes in long -term noise levels, <br />measured in units of Ldn or CNEL, are noticeable and that people <br />respond. About 10 percent of the people exposed to traffic noise <br />of 50 Ldn will report being highly annoyed with the noise, and <br />each increase of one Ldn is associated with approximately 2 <br />percent more people being highly annoyed. When traffic noise <br />exceeds 60 Ldn or aircraft noise exceeds 55 Ldn, people begin <br />complaining. Group and legal actions to stop the noise should be <br />expected to begin at traffic raise levels near 70 Ldn and air- <br />craft noise levels near 55 Ldn. <br />Land Use Compatibility with Noise <br />Some land uses are more tolerant of noise than others. For <br />example, schools, hospitals, churches and residences are more <br />sensitive to noise intrusion than commercial or industrial <br />I activities. As ambient noise levels affect the perceived amenity <br />noise impacts impair the economic health and growth potential, of <br />a community by reducing the area's desirability as a place to <br />live, shop, and work. For this reason, land use compatibility <br />with the noise environment is an important consideration in the <br />planning and design process. <br />There are two sets of noise criteria that apply to the Bristol <br />Street widening project. These include the federal noise stan- <br />dards (promulgated by the Federal Highway Administration) and the <br />City of Santa Ana noise standards established in the Noise Ele- <br />ment of the General Plan. Each set of criteria uses a different <br />noise metric and a unique methodology to assess noise impacts. <br />Federal Standards: The Federal Highway Administration (FHWA) has <br />developed a series of design noise levels for various activity <br />categories which are expressed in terms of equivalent sound <br />levels (Leq) or Llp values.3 These design noise levels are <br />commonly used on federally funded projects or projects for which <br />federal review or CalTrans review is anticipated. <br />The FHWA. design noise levels represent maximum values and incor- <br />porate trade -offs between desirable and feasible noise levels <br />(recognizing that in many cases lower noise exposures would <br />I. "Noise Manual ": Caltrans, 1980 and "National Cooperative <br />Highway Research Program Report 117 ", HRB, 1971. <br />2. State of California, Department of Health Services, Dr. <br />Jerome Lukas, Memo dated July 11, 1984. <br />3. LI0 values are noise levels exceeded ten percent of the <br />time. They are commonly used to express peak hour noise <br />levels (since peak hour traffic volumes are typically 10 <br />percent of the daily traffic volume). <br />4 -3 <br />