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Pam Hazdy <br />Apri19, 2008 <br />Page 2 <br />the vibrations by which it is produced. Higher pitched signals sound louder to humans than <br />sounds with a lower pitch. Loudness is amplitude of sound waves combined with the reception <br />characteristics of the ear. Amplitude may be compazed with the height of an ocean wave. <br />In addition to the concepts of pitch and loudness, there are several noise measurement scales <br />which are used to describe noise in a particulaz location. A decibel (dB) is a unit of measurement <br />which indicates the relative amplitude of a sound. The zero on the decibel scale is based on the <br />lowest sound level that the healthy, unimpaired human ear can detect. Sound levels in decibels <br />are calculated on a logarithmic basis. An increase of 10 decibels represents aten-fold increase in <br />acoustic energy, while 20 decibels is 100 times more intense, 30 decibels is 1,000 times more <br />intense, etc. There is a relationship between the subjective noisiness or loudness of a sound and <br />its level. Each 10 decibel increase in sound level is perceived as approximately a doubling of <br />loudness over a fairly wide range of intensities. Technical terms are defined in Table 1. <br />There are several methods of characterizing sound. The most common in California is the A- <br />weighted sound level or dBA. This scale gives greater weight to the frequencies of sound to <br />which the human ear is most sensitive. Representative outdoor and indoor noise levels in units <br />of dBA are shown in Table 2. Because sound levels can vary markedly over a short period of <br />time, a method for describing either the average character of the sound or the statistical behavior <br />of the variations must be utilized. Most commonly, environmental sounds aze described in terms <br />of an average level that has the same acoustical energy as the summation of all the time-varying <br />events. This energy-equivalent sound/noise descriptor is called Lam. The most common <br />averaging period is hourly, but Ley can describe any series of noise events of arbitrary duration. <br />The scientific instrument used to measure noise is the sound level meter. Sound level meters can <br />accurately measure environmental noise levels to within about plus or minus 1 dBA. Various <br />computer models are used to predict environmental noise levels from sources, such as roadways <br />and airports. The accuracy of the predicted models depends upon the distance the receptor is <br />from the noise source. Close to the noise source, the models are accurate to within about plus or <br />minus 1 to 2 dBA. <br />Since the sensitivity to noise increases during the evening and at night --because excessive noise <br />interferes with the ability to sleep -- 24-hour descriptors have been developed that incorporate <br />artificial noise penalties added to quiet-time noise events. The Community Noise Equivalent <br />Level, CNEL, is a measure of the cumulative noise exposure in a community, with a 5 dB penalty <br />added to evening (7:00 pm - 10:00 pm) and a 10 dB addition to nocturnal (10:00 pm - 7:00 am) <br />noise levels. The Day/Night Average Sound Level, Ld„, is essentially the same as CNEL, with the <br />exception that the evening time period is dropped and all occurrences during this three-hour <br />period are grouped into the daytime period. <br />