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SU0007300
Environmental Health - Public
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EHD Program Facility Records by Street Name
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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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Noise Criteria Used to Assess Impacts Associated with this Project <br /> Any noise impact analysis should consider where and when the noise-sensitivity of those <br /> potentially affected by a project exists. For this project, noise will be periodically generated by <br /> Munn & Perkins on-site equipment (asphalt plant) and off-site truck traffic during the hours of 9 <br /> p.m. to 5 a.m., as it historically has while servicing night paving projects. As noted previously, <br /> however, such operations would continue to occur only when nighttime paving projects require <br /> materials during these hours. One of the critical questions in terms of the noise impact analysis <br /> is where will the sensitivity of noise exist during those nighttime hours? <br /> It is reasonable to assume that noise-sensitivity at outdoor activity areas of the residences <br /> constructed within the project area will be severely limited, if it exists at all, during the nighttime <br /> hours which would be affected by the project. For example, it is highly unlikely that outdoor <br /> activities would be taking place between 1 a.m. and 3 a.m., the quietest measured hours, on <br /> nights when the facility would be operating due to a project's requirement for nighttime paving <br /> materials. <br /> Because the hours affected by the project are nighttime hours (with the exception of the 9 p.m. <br /> hour, which technically is considered daytime), it is equally reasonable to assume that the vast <br /> majority of the noise-sensitivity during those hours will be within bedrooms while residents are <br /> sleeping. <br /> In light of these reasonable assumptions regarding the realistic locations where and when <br /> project noise impacts would be likely to occur, the focus of this analysis is on noise impacts <br /> associated with sleep disturbance caused by the project. In light of recent findings that the <br /> potential for awakenings is less than 5% for interior SEL values of 65 dB or less, potential noise <br /> impacts are identified in cases where interior SEL values would exceed that level within <br /> bedrooms due to project traffic. <br /> Although there is likely very little (if any), nighttime sensitivity at the exterior areas of residences <br /> located along East River Road, the County's nighttime noise standards for outdoor activity areas <br /> of residential uses are nonetheless addressed in this assessment as well. Specifically, potential <br /> noise impacts are identified if the nighttime operation of on-site sources (i.e. those sources <br /> involved with the nighttime production of asphalt materials) would cause noise levels to exceed <br /> the County's 45 dB Leq and 65 dB Lmax noise standards at the exterior space of the nearest <br /> residential uses. <br /> Finally, because CEQA requires that impacts be considered if a project would result in either <br /> substantial short-term 1 temporary, or permanent, increases in ambient noise levels, this <br /> analysis provides an assessment of project-related noise increases using the FICON <br /> methodology identified in Table 4. <br /> Environmental Noise analysis <br /> Munn&Perkins Expanded Hours of Operations—San Joaquin County <br /> Page 10 <br />
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