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SU0007300
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2600 - Land Use Program
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QX-89-0002
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SU0007300
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Last modified
10/29/2020 3:08:38 PM
Creation date
9/9/2019 9:06:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0007300
PE
2656
FACILITY_NAME
QX-89-0002
STREET_NUMBER
26292
Direction
E
STREET_NAME
RIVER
STREET_TYPE
RD
City
ESCALON
APN
24722019
ENTERED_DATE
7/29/2008 12:00:00 AM
SITE_LOCATION
26292 E RIVER RD
RECEIVED_DATE
7/28/2008 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\wng
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\MIGRATIONS\R\RIVER\26292\QX-890002\SU0007300\CORRESPOND.PDF
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EHD - Public
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J <br /> i <br /> of proper speeds and gear selection is extremely difficult to enforce as a <br /> mitigation measure. The BAC report indicates that the analysis of truck noise <br /> impacts will assume that truck drivers are operating vehicles in the "quietest <br /> manner possible". This analysis is not a conservative approach to evaluating <br /> noise impacts. This would seem to indicate that there has been an identified <br /> significant impact,and that mitigation measures are being implemented. <br /> D. The BAC report conducts an evaluation of increased noise levels due to the <br /> project. The analysis correctly utilizes the FICON procedure which indicates that <br /> if existing background noise levels exceed 65 dB, a 1.5 dB increase would be <br /> required to trigger a significant increase in noise levels. If existing background <br /> noise levels range between 60 dB and 65 dB, a 3 dB increase would be required to <br /> trigger a significant increase in noise levels. In addition, if existing background <br /> noise levels are less than 60 dB, a 5 dB increase would be required to trigger a <br /> significant increase in noise levels. <br /> That being said, if you review the measured background noise levels contained <br /> within the appendix to the report, the background hourly average (Leq) values <br /> during the 9:00 p.m. hour at Noise Measurement Sites 1, 3, 4 & 5; which <br /> represent distances between 40 feet and 60 feet from the East River Road <br /> centerline,the noise levels range between 62 dB and 68 dB Leq. Based upon the <br /> average measured truck passby noise level of 86 dB SEL, at a distance of 40 feet, <br /> and the predicted anticipated 66 truck trips during the 9:00 p.m. hour associated <br /> with the Munn Perkins plant expansion, the noise level associated with the <br /> additional truck trips would be 68.6 dB Leq. Therefore, the cumulative increase <br /> in truck traffic noise levels is expected to range between 3 dB and 7 dB Leq. So <br /> clearly during the start-up of the truck traffic, there would be a significant <br /> increase truck traffic noise levels. The report does not provide this conclusion. <br /> SPECIFIC COMMENTS ON THE BAC REPORT <br /> Criteria for Acceptable Noise Exposure <br /> 1. The report provides a discussion, on Page 6, that describes the effects of single <br /> event noise. The discussion centers around the potential for sleep disturbance, <br /> and utilizes the Federal Interagency Committee on Aviation Noise (FICAN) <br /> report which estimated a 5— 10%of the population is affected when interior SEL <br /> noise levels are between 65 and 81 dB,and few sleep awakenings (less than 5%) <br /> are predicted if the interior SEL is less than 65 dB. However, most recent <br /> research and procedures for evaluating sleep disturbance are based upon the <br /> American National Standards Institute (ANSI) which has developed procedures <br /> for evaluating the potential for sleep disturbance. The Procedure ANSI/ASA <br /> S12.9-2008 / Part 6 sets for the procedures for evaluating the potential for sleep <br /> disturbance. It establishes a threshold for a single event for which the A-weighted <br /> sound exposure level (ASEL) which occurs within a room at 50 dBA. The ANSI <br /> procedure calculates the probability of awakening based upon the interior mean <br /> 3 <br />
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