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SU0007300
Environmental Health - Public
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EHD Program Facility Records by Street Name
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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
Supplemental fields
FilePath
\MIGRATIONS\R\RIVER\26292\QX-890002\SU0007300\CORRESPOND.PDF
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EHD - Public
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CEQA Noise Level Increase Criteria <br /> The California Environmental Quality Act (CEQA) requires that noise impacts of a project be <br /> evaluated not only relative to local noise standards, but also relative to project-related increases <br /> in ambient noise levels. As noted previously, this facility has historically operated at night when <br /> necessary to service night paving projects with approval from the County on a project-by-project - <br /> basis. Technically, therefore. the project would result in the continuation of those periodic <br /> nighttime operations which have historically occurred at the project site, and would not result in <br /> an increase in noise relative to those historic operations. In cases where a project would result <br /> in changes to ambient conditions, the significance of those project-related noise level increases <br /> can be evaluated using the Table 4 criteria. <br /> Table 4 was developed by the Federal Interagency Committee on Noise (FICON) as a means of <br /> developing thresholds for impact identification for project-related noise level increases. The <br /> rationale for the graduated scales is that test subject's reactions to increases in noise levels <br /> varied depending on the starting level of noise. Specifically, with lower ambient noise <br /> environments, such as those below 60 dB Ldn, a larger increase in noise levels was required to <br /> achieve a negative reaction than was necessary in environments that are already elevated. - <br /> Table 4 <br /> Significance of Changes in Cumulative Noise Exposure <br /> Munn & Perkins Expanded Hours of Operations <br /> San Joaquin County, California <br /> Ambient Noise Level Without Project, Ltl„ Increase Required for Significant Impact <br /> Less than 60 dB +5.0 dB or more <br /> 60 to 65 dB +3.0 dB or more <br /> Greater than 65 dB +1.5 dB or more <br /> Source:Federal Interagency Committee on Noise (FICON) <br /> As indicated by Table 4, an increase in the traffic noise levels becomes more significant as the <br /> ambient noise levels increase. For instance, a significant increase in traffic noise levels is <br /> expected to be 1.5 dB when the no-project traffic noise levels exceed 65 dB Ldl. However, a <br /> significant increase in traffic noise levels is expected to be 5 dB when the no-project traffic noise <br /> levels are less than 60 dB L,;,,. In other words, as ambient noise levels increase, a smaller <br /> increase in noise resulting from the project is sufficient to cause significant annoyance. <br /> -- Environniental Noise Analysis <br /> Munn&Perkins Expanded Hours of Operations—San Joaquin County <br /> Page 9 <br />
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