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SU0007300
Environmental Health - Public
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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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\MIGRATIONS\R\RIVER\26292\QX-890002\SU0007300\CORRESPOND.PDF
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EHD - Public
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night, noise generated by the maximum project truck generation (26 hourly trucks) would not <br /> significantly exceed existing ambient noise levels. However, Appendix D also illustrates the <br /> generation of 20 project heavy truck trips in an hour would result in exceedance of measured <br /> ambient noise levels during the 1 a.m. hour for typical weekday conditions at three of the five <br /> locations monitored. Therefore, it is likely that during the quietest hours of the night the <br /> changes in hourly average noise levels due to project-generated truck traffic would be clearly <br /> noticeable outdoors. <br /> Although the project will occasionally result in clearly noticeable increases in average noise .. <br /> levels during the quietest hours of the night, those increases would not necessarily translate to <br /> adverse noise impacts. As described previously, the noise generation of the project would <br /> occur primarily during sleeping hours, so residents along East River Road would not likely be .. <br /> outdoors during those hours affected by the project. It is more likely those residents would <br /> affected by noise generated inside their bedrooms by individual passages of heavy trucks than <br /> by changes in outdoor average noise levels associated with several such passages. Impacts . <br /> associated with sleep disturbance were evaluated previously in this report. Although the <br /> project may result in clearly noticeable increases in average exterior noise levels during <br /> the quietest hours of the night (midnight— 2 am), given the reduced noise-sensitivity at �.. <br /> outdoor locations during those hours this impact is considered loss than signific,',mt. <br /> Summary of Potential Project-Related Noise Impacts Not Related to Adopted County <br /> Noise Standards <br /> The following bullet list summarizes the findings of this analysis with respect to the potential <br /> significance of project-related noise impacts: <br /> Jake Brake Usage: Due to the low percentage of observed Jake Brake usage and a . <br /> relatively small increase associated with the trucks which were observed using Jake <br /> Brakes (2 dB SEL increase), noise impacts associated with Jake Brake usage during <br /> nighttime truck passages associated with this project are not expected. Less than <br /> significant. <br /> • Sleep Disturbance During Individual Truck Passages - Bedroom Windows Closed: , <br /> With bedroom windows closed, SEL values within residences located along East River <br /> Road are predicted to be below levels which pose a significant probability of sleep <br /> disturbance. Less than <br /> • Sleep Disturbance During Individual Truck Passages - Bedroom Windows Open: <br /> With bedroom windows open, SEL values within residences located along East River <br /> Road could exceed levels which pose a significant probability of sleep disturbance. <br /> Environmental Noise Analysis <br /> Munn&Perkins Expanded Hours of Operations- San Joaquin County <br /> Page 35 <br />
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