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I <br />4 6NQISE................ . ......... ...... <br />. <br />ENVIRONMENTAL SETTING <br />The Environmental Setting section presents background information on community noise to aid the reader <br />in understanding the noise assessment, a description of the applicable noise guidelines and standards, <br />and a description of the existing noise environment in the study area. <br />Background Information on Noise <br />FUNDAMENTAL CONCEPTS OF ENVIRONMENTAL ACOUSTICS <br />Noise is defined as unwanted sound. Airborne sound is a rapid fluctuation of air pressure above and <br />below atmospheric pressure. Sound levels are usually measured and expressed in decibels (dB) with 0 <br />dB corresponding roughly to the threshold of hearing. Decibels and other technical terms are defined <br />in Table 1. <br />Most of the sounds which we hear in the environment do not consist of a single frequency, but rather a <br />broad band of frequencies, with each frequency differing in sound level. The intensities of each frequency <br />add together to generate a sound. The method commonly used to quantify environmental sounds <br />consists of evaluating all of the frequencies of a sound in accordance with a weighting that reflects the <br />facts that human hearing is less sensitive at low frequencies and extreme high frequencies than in the <br />frequency mid-range. This is called "A" weighting, and the decibel level so measured is called the A - <br />weighted sound level (dBA). In practice, the level of a sound source is conveniently measured using a <br />sound level meter that includes an electrical filter corresponding to the A -weighting curve. Typical A-levels <br />measured in the environment and in industry are shown in Table 2 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 which <br />no particular source is identifiable. To describe the time -varying character of environmental noise, the <br />statistical noise descriptors, Lt0- L501 and L90, are commonly used. They are the A -weighted noise levels <br />equaled or exceeded during 10%, 50%, and 90% of a stated time period. A single number descriptor <br />called the Leq is now also widely used. The Leq is the average A -weighted noise level during a stated <br />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 noises <br />are generally lower than the daytime levels. However, most household noise also decreases at night and <br />exterior noise becomes very noticeable. Further, most people sleep at night and are very sensitive to <br />noise intrusion. To account for human sensitivity to nighttime noise levels, a descriptor, Ldp (day/night <br />average sound level), was developed. The Ldn divides the 24-hour day into the daytime of 7:00 AM to <br />10:00 PM and the nighttime of 10:00 PM to 7:00 AM. The nighttime noise level is weighted 10 dB higher <br />than the daytime noise level. The Community Noise Equivalent Level (CNEL) is another 24-hour average <br />which includes both an evening and nighttime weighting. <br />The effects of noise on people can be listed in three general categories: <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 />ER -93-1 -74- (9-27-93) <br />