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SU0004098
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SU0004098
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Last modified
5/7/2020 11:30:31 AM
Creation date
9/6/2019 10:43:12 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0004098
PE
2605
FACILITY_NAME
PA-0300550
STREET_NUMBER
35775
Direction
S
STREET_NAME
KOSTER
STREET_TYPE
RD
City
TRACY
ENTERED_DATE
5/12/2004 12:00:00 AM
SITE_LOCATION
35775 S KOSTER RD
RECEIVED_DATE
3/10/2004 12:00:00 AM
QC Status
Approved
Scanner
SJGOV\rtan
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\MIGRATIONS\K\KOSTER\35775\PA-0300550\SU0004098\APPL.PDF \MIGRATIONS\K\KOSTER\35775\PA-0300550\SU0004098\CDD OK.PDF \MIGRATIONS\K\KOSTER\35775\PA-0300550\SU0004098\EH COND.PDF \MIGRATIONS\K\KOSTER\35775\PA-0300550\SU0004098\CORRESPOND.PDF
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EHD - Public
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San Joaquin County Community Environmental Setting, Impacts,and Mitigation Measures <br /> Development Department Noise <br /> acoustic calibrator and complies with applicable requirements of the American <br /> National Standards Institute(ANSI)for Type 2 sound level meters. <br /> The existing noise environment in the vicinity of the project site was <br /> characterized by conducting continuous noise monitoring at three locations for <br /> seven days, starting at 12:00 p.m.Monday, October 3,2005,and ending at 12:00 <br /> p.m. Monday,October 10,2005. These locations are shown on Figure 3.J-1. <br /> Long-Term Site LT-1: near Koster Ranch—This noise monitor was located at <br /> the eastern fence line of the Koster Ranch near the Delta-Mendota Canal and was <br /> used to represent the residence on the ranch property. Primary noise sources <br /> affecting the site include distant traffic from 1-5, traffic crossing the canal bridge, <br /> and aircraft overflights. <br /> Long-Term Site LT-2: Near Koster Road across from Residence—The Site 2 <br /> .. monitor was located near the intersection of the orchard road with Koster Road, <br /> across from the residence on the eastern side of the intersection, which the <br /> monitor is intended to represent. Primary noise sources affecting the site include <br /> traffic on SR 132,and local traffic on Koster Road and the orchard road. <br /> Long-Term Site LT-3: North of SR-132—The Site 3 monitor was located near <br /> i residences located north of SR-132. Primary noise sources affecting the site <br /> include traffic on SR 132. <br /> The LD Model 700 sound level meters at Sites LT-1 and LT-2 ran continuously <br /> over the seven-day period. At Site LT-3,the meter ran for 4 days. Statistical <br /> descriptors are calculated for each 1-hour interval of the overall sample period. <br /> Statistical descriptors include the Lam,Lte, L33, and L90. The Lq represents the <br /> energy-average noise level for each interval period(see Introduction). The Lle, <br /> L33, and L90 describe the noise levels exceeded 10%, 33%and 90%of the time, <br /> respectively, during each sample interval. The Lgo is often used to describe the <br /> background(or ambient) sound level for a given area, or the sound level that <br /> characterizes periods during which typical noise sources in the area(such as <br /> traffic and aircraft overflights)are not contributing significantly to the sound <br /> level. <br /> Table 3.J-1 summarizes the results of the long-term ambient noise level <br /> monitoring. On average,the loudest sound levels at the long-term sites occurred <br /> between the hours of 6:00 a.m. and 10:00 a.m. The quietest sound levels <br /> occurred during the hours of 11:00 p.m. and 3:00 a.m. <br /> DeSilva Gates Quarry Project <br /> Draft Environmental Impact Report 3.J-3 <br /> J85 05105.05 <br />
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