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Grand Avenue Widening Project Environmental Impact Report Section 3.0 <br />3.6.3 METHODOLOGY RELATED TO NOISE <br />Noise Assessment Metrics <br />Community noise is generally not steady state and varies with time. Under conditions of non -steady <br />state noise, some type of statistical metric is necessary to quantify human response to noise. There <br />are several rating scales for the analysis of adverse effects of community noise on people. They are <br />designed, to account for the lmown effects of noise on people. Based on these effects, the <br />observation has been made that the potential for a noise to impact people is dependent on the total <br />acoustical energy content of the noise. A number of noise scales have been developed to account <br />for this observation. <br />The description, analysis and reporting of community noise levels around communities is made <br />difficult by the complexity of human response to noise and the number of noise metrics that have <br />been developed for describing noise impacts. Each metric attempts to quantify noise levels with <br />respect to community response. Most metrics use the A -weighted noise level to quantify noise <br />impacts on humans. A -weighting is a frequency correction that correlates the overall sound <br />pressure levels with the frequency response of the human ear. <br />Noise metrics can be divided into two categories: single event and cumulative. Single event metrics <br />describe the noise levels from an individual event such as an aircraft flyover or perhaps a heavy <br />equipment pass -by. Cumulative metrics average the total noise over a specific time period, which is <br />typically 1 -hour or 24 -hours for community noise assessments. For the proposed Grand Avenue <br />widening, cumulative noise metrics, described below, were used. <br />Cumulative Noise Metrics <br />There are several rating scales for the measurement of community noise. These rating scales <br />account for the parameters of noise that have been shown to contribute to the effects of noise on <br />humans; the variety of noises found in the environment; the variations in noise levels that occur as a <br />person moves through the environment; and the variations associated with the time of day. They <br />are designed to account for the known health effects of noise on humans described earlier. Based <br />on these effects, the observation has been made that the potential for a noise to impact people is <br />dependent on the total acoustical energy content of the noise. A number of noise scales have been <br />developed to account for this observation. Two predominate noise scales are the Equivalent Noise <br />Level (LEQ) and the CNEL, which are described as follows: <br />LEQ is the sound level corresponding to a steady-state sound level containing the same total <br />energy as a time -varying signal over a given sample period. LEQ is the "energy" average <br />noise level during the time period of the sample. LEQ can be measured for any time period, <br />but is typically measured for 15 minutes, one hour or 24 -hours. The noise measurement <br />survey for the Grand Avenue widening project was conducted in terms of the LEQ metric. <br />CNEL is similar to LEQ but it is for 24 hours, and applies a weighting factor which places <br />greater importance on noise events occurring during the evening and night hours when sleep <br />disturbance is a concern. CNEL is a 24-hour, time -weighted annual average noise level. <br />F: WROJ-ENMGrand eirlNew Text - GrandlSection 3 SplitlSection 3.6.doc Page 3.6-18 <br />