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SU0007300
Environmental Health - Public
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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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Impact Evaluation Relative to CEQA Guidelines, Sleep Disturbance & <br /> Single Event Criteria <br /> Nighttime Asphalt Plant operations Relative to Potential Sleep Disturbance <br /> As noted previously, the focus of this analysis is on noise levels within sleeping rooms of . <br /> project-area residences. Asphalt plant noise generation at the nearest residences to the project <br /> site is predicted to average approximately 40 dB Leq, with variations of approximately +1- 5 dB <br /> depending on normal variations in atmospheric conditions. Also as noted previously, average <br /> and maximum noise levels associated with the asphalt plant operations are not appreciably <br /> different at the nearest residences located approximately 2,000+ feet from that equipment. <br /> Within the nearest residences, asphalt plant noise levels are predicted to be approximately 10 to <br /> 25 dB lower than noise levels outside the residence with windows in the open and closed <br /> positions, respectively. Given an exterior noise level of approximately 45 dB Leq or less, <br /> resulting interior levels with windows closed and open would be approximately 20 to 35 dB. <br /> As shown in Table 2, a typical background level within residences is approximately 40 dB, with <br /> a level of 30 dB equivalent to a soft whisper two feet away. Even when added to existing <br /> ambient noise levels without the asphalt plant in operation, the range noise levels predicted <br /> within the nearest residences during nighttime asphalt production is not expected to change <br /> significantly within those nearest residences. Since there is no appreciable change in noise <br /> levels predicted within the nearest residences to the Munn & Perkins asphalt plant equipment <br /> during nighttime operation of that equipment. the probability of this aspect of the project <br /> resulting in sleep disturbance is very low. Therefore, noise impacts associated with <br /> nighttime operation of the asphalt plant associated with sleep disturbance at the nearest <br /> neighbors are predicted to be less than si9flificarrf. <br /> Sleep Disturbance Impacts due to Nighttime Project-Related Truck Traffic — Bedroom <br /> Windows Closed <br /> As discussed earlier, incidents of sleep disturbance are predicted to be relatively low at interior <br /> SEL values of less than 65 dB. Given an optimized SEL value of 82 dB at 40 feet, the SEL at <br /> the nearest residential building facades located 60 feet from the centerline would be <br /> approximately 79 dB. To reduce an exterior SEL value of 79 dB outside the residence to a level <br /> of 65 dB SEL inside, a building facade noise reduction of 14 dB would be required. <br /> Typical residential construction can be expected to provide approximately 25 dB of noise <br /> reduction with windows in the closed position. Based on this degree of building facade noise <br /> reduction the interior SEL during individual truck passages at the closest residences to the <br /> roadway would be approximately 54 dB (79 — 25 = 54) when residences have their windows in <br /> the closed position. At more distant residences (i.e. beyond 60 feet from the East River Road <br /> centerline), interior SEL values would be even lower due to normal decreases in noise with <br /> increasing distance. <br /> Environmental!Noise Analysis <br /> Munn &Perkins Expanders Hours of Operations—San Joaquin County _ <br /> Page 31 <br />
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