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Introduction <br /> A continued and growing concern for the community environment has <br /> prompted the Johnson Kart Manufacturing Company of Milwaukee, Wisconsin <br /> to undertake an evaluation of noise levels resulting from operation <br /> of a commercial go-kart track. This report summarizes results of that <br /> evaluation. <br /> Sound, Noise, and Decibels <br /> Sound is a disturbance in air that travels as a wave having a frequency <br /> of between 20 and 20,000 hertz and having an amplitude great enough <br /> to be heard. Noise is merely a sound that is, subjectively, unwanted <br /> because of intensity, frequency, or location. Just as grass becomes a <br /> weed when growing in a garden, even music becomes "noise" if it disturbs <br /> one's sleep. <br /> Sound is sensed by a microphone which converts the pressure fluctuations <br /> of the sound wave to an electrical signal. This signal is conditioned <br /> by the circuitry of a sound level meter and the intensity is indicated <br /> in units of decibels (dB). The term decibel is defined to be equal to <br /> 10 times the logarithm to the base 10 of the ratio of two power <br /> quantities. Power can be in watts, horsepower, or, in the case of sound, <br /> pressure squared. The advantage of a decibel scale is that smaller <br /> numbers can be used in calculations. A disadvantage with this definition, <br /> as it relates to sound measurement and analysis, is that sound power <br /> cannot be measured directly. The"decibels" indicated on a sound level <br /> meter relate to the sound pressure level and not power level. <br /> It was noted that, in addition to intensity, sound is further charac- <br /> terized by frequency of the sound wave. Since response of the human <br /> ear is not the same for all frequencies, various weighting systems <br /> have been devised to correlate the sound level meter readings to human <br /> response to sound. The "A" weighted scale is presently accepted as <br /> resulting in the closest correlation. Table 1 shows the amount of <br /> attenuation or amplification of sound pressure level over the audible <br /> frequency range for the A weighted scale. Table 2 shows average noise <br /> levels for some sources typically encountered in a community enviro- <br /> nment. An interesting point of Table 2 is the human response to loudness. <br /> Technically, doubling the sound pressure level causes a 3dB increase <br /> in reading or a 6dB increase in sound power level. However as shown in <br /> Table 2, the human ear doesn't perceive a sound as being twice as loud <br /> until the difference in sound pressure level approaches 10dB. <br /> Test Program <br /> Test procedures followed were in general accord with accepted industry <br /> standards as defined by the Society of Automotive Engineers in SAE J 331 <br /> and SAE J 986. The sound level meter was a Bruel & Kjoerr Type 2209 <br /> equipped with a condensor microphone (Bruel & Kjoerr Type 4165). <br /> Instrument calibration was accomplished on site at the time of test <br /> using a General Radio Model 1562-Acalibrator. Accuracy of calibration <br /> is traceable to the National Bureau of Standards. Instruments conform <br /> to requirements of SAE J 184 and American National Standards Institute <br /> Specifications ANSI S1.4 - 1971 and ANSI S1.11 - 1966. <br /> The test sit chosen was the kart track of Johnson Park, Milwaukee, Wiscon- <br /> sin. Track layout and microphone positions are shown in figure 1. Nine <br />