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Noise monitoring was performed using a Quest Technologies Model 2900 Type 2 IntegratingAogging Sound Level <br />Meter- The unit meets the American National Standards Institute (ANSI) Standard S1.4-1983 for Type 2, <br />1 International Electrotechnical Commission (IEC) Standazd 651 - 1979 for Type 2, and IEC Standazd 65I - 1979 for <br />Type 2 sound level meters. The unit was field calibrated at 10:52 am. using a Quest 'T'echnologies (ZC-10 <br />calibrator immediately prior to the fast set of readings. The calibration was then rechecked at 12:26 p.m. after the <br />four "spot" readings and prior to an "in-room" 24-hour measurement and no meter `<driR" was noted. The accuracy <br />of the cahbrator is maintained through a program established through the manuficturer and is traceable to the <br />National Bureau of Standazds. The unit meets the requiremeirts of ANSI Standard 81.4-1984 and IEC Standard <br />942: 1988 for Class 1 equipment. <br />j The study included four 15-minute, "spot" readings and one 24-hour "in-room" reading at the project site. For the <br />four spat readings, the I,eq, Lorin, Lmax, Loz> Los, Lzs, and Lro values were recorded. As discussed above, the Leq <br />~ value is representative of the equivalent noise level or logarithmic average noise level obtained over the <br />measurement period. The Lorin and Lmax represent the minimum and maximum root-mean-square noise levels <br />obtained over a period of 1 second. The Loz, Los,. Lu, and Lso represent the values that aze exceeded 2, 8, 25, and 50 <br />percent of the tune, or alternatively, 1, 5, 15, and 30 minutes per hour if the readings were extrapolated out to an <br />hour's duration. The 24-hour measurement actually. consisted of 24 1-hour measurements. These 24 readings <br />include the Leq, the Lio, the L9o, and the Lmax. The L <br />recorded. The readin obtained alo ~' Loz, Los, Ins> and Lro for the entire 24-hour period are also <br />g ng Harbor Boulevard (NR-3) was supplememed with simultaneous vehicle <br />counts. These coums were obtained for modeling purposes (discussed below). Monitoring locations are shown in <br />Figure 2 and the readings are included. in Table 3. Each reading is summarized below. <br />TABLE3 <br />NOISELEVEL MF 9.SUREMLc1yTS'' <br />Monitoring L <br />Location ~4 (d&4) Loz(d$.4) (dTilAl Las(di3A) Lso(dBA) Lorin Lmax <br />1.1 58.8 57.1 <br />NR-2 56.0 59.7 58.1 56.7 55.7 50.9 63.8 <br />NR-3 67.9 74.8 71.7 68.8 65.3 50.2 80.3 <br />NR-4 61.2 65.7 63.9 62..1 60.4 56.7 70,3 <br />NR-5 46.4 53.3 50.3 47.4 43.8 23.8 67.4 <br />The Leq represems the equivalent sound level and is the muneric value of a constant level that over the given <br />period of time transmits the same amrnmt of acoustic energy as the actual time-varying sound level. The Loz, <br />Los, Lss, and Lso are the levels that are exceeded 2, 8, 25, and 50 percern of the time, respectively. Alternatively, <br />these values represenrt the noise level that would be exceeded for 1, 5, 15, and 30 minutes during a 1-hour <br />period. The Lorin and Lmax represent the minimum and maximum root-mean_squaze noise levels obtained <br />over a period of 1 second. <br />z Represents a cominuous, 24-hour reading. <br />7 <br />75D-127 <br />