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Appendix H <br /> NOISE TECHNICAL DATA <br /> This appendix presents background information on noise to aid the EIR reader in <br /> understanding noise assessment, a description of the applicable noise standards, and a <br /> description of the existing noise environment in the study area. <br /> Noise is defined as unwanted sound. Airborne sound is a rapid fluctuation of air <br /> pressure above and below atmospheric pressure. Sound levels are usually measured <br /> and expressed in decibels (dB) with 0 dB corresponding roughly to the threshold of <br /> hearing. Decibels and other technical terms are defined in Table H-1. <br /> Most of the sounds which we hear in the environment do not consist of a single <br /> frequency, but rather a broad band of frequencies, with each frequency differing in <br /> sound level. The intensities of each frequency add together to generate a sound. The <br /> method commonlyused to quantify environmental sounds consists of evaluating all o <br /> the frequencies of a sound in accordance with a weighting that reflects the facts that <br /> human hearing is less sensitive at low frequencies and extreme high frequencies than in <br /> the frequency mid-range. This is called "'A" weigghting , and the decibel level so <br /> measured is called the A-weighted sound level (dBA). In practice, the level of sound <br /> source is conveniently measured using a sound level meter that includes an electrical <br /> filter corresponding to the A-weighting curve. Typical A-levels measure in the <br /> environment and in industry are shown in Table H-2 for different types of noise. <br /> Although the A-weighted noise level may adequately indicate the level of <br /> environmental noise at any instant in time, community noise levels varcontinuously. <br /> Most environmental noise includes a conglomeration of noise from istnt sources <br /> which create a relatively steady background noise i which o particular source is <br /> identifiable. To describe the time-varying character of environmental noise, the <br /> statistical noise descriptors, Llo, L50, and Lo, are commonly used. They are the A- <br /> weighted noise levels equaled or exceeded during 10%,.50%, and 90%of a stated time <br /> period. A single number descriptor called the L is now also widely used. The Leq is <br /> the average A-weighted noise level during a stateaPperiod of time. <br /> 1 In determining the daily level of environmental nose, it is important to account for the <br /> difference in response of people to daytime and nighttime noises. During the <br /> nighttime, exterior background noises are generally lower than the daytime levels. <br /> However, most household noise also decreases at night and exterior noise becomes very <br /> noticeable. Further, most people sleep at night and are very sensitive to noise intrusion. <br /> To account for human sensitivity to nighttime nose levels, a descriptor,Ldn (day/night <br /> average sound level),was developed. The L divides the 24-hour a into the daytime <br /> of 7:00 AM to 10:00 PM and the nighttime t7odT0:00 PM to 7:00 AM. The nighttime noise <br /> level is weighted 10 dB higher than the daytime noise level. The Community Noise <br /> Equivalent Level (CNEL) is another 24-hour average which includes both an evening <br /> and nighttime weighting. <br /> The effects of noise on people can be listed in three general categories: <br /> • <br /> subjective effects of annoyance,nuisance, dissatisfaction <br /> • interference with activities such as speech,sleep,learning <br /> physiological effects such as startling,hearing loss <br /> H-1 <br />