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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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\MIGRATIONS\R\RIVER\26292\QX-890002\SU0007300\CORRESPOND.PDF
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EHD - Public
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r 3.4 Noise <br /> Non-Transportation Noise Sources <br /> t ' Non-transportation noise sources are commonly considered to be any source of noise on private <br /> s� <br /> property.San Joaquin County utilizes the performance standards of the Development Title to <br /> i assess impacts associated with non-transportation noise sources, including all sources of noise <br /> ' t originating from the project site(e.g., asphalt plant equipment,water trucks, loaders). <br /> �- Leq: the equivalent sound level is used to describe noise over a specified period of time, <br /> j typically one hour, in terms of a single numerical value. The Leq is the constant sound <br /> level which would contain the same acoustic energy as the varying sound level,during <br /> the same time period(i.e.,the average noise exposure level for the given time period). <br /> I <br /> Lmax: the instantaneous maximum noise level for a specified period of time. <br /> rL&/DNL: 24-hour day and night A-weighted noise exposure level which accounts for the greater <br /> -^ sensitivity of most people to nighttime noise by weighting noise levels at night <br /> ("penalizing"nighttime noises).Noise during nighttime hours(10:00 p.m. and 7:00 <br /> F# a.m.)is weighted(penalized)by adding 10 dB to take into account the greater <br /> annoyance of nighttime noises. <br /> ' 5 SEL: The equivalent sound level over a I-second time interval for a discrete sound event <br /> (e.g.,truck passby). <br /> E General Effects of Noise <br /> r The effects of noise on people can be placed into three categories: <br /> • subjective effects of annoyance,nuisance, dissatisfaction; <br /> �.._ • interference with activities such as speech, sleep, learning; and <br /> • physiological effects such as hearing loss or sudden startling. <br /> k <br /> For the average person, environmental noise typically produces effects in the first two categories. <br /> Workers in industrial plants or others exposed to high noise exposure for extended periods may also <br /> f experience physiological effects.There is no completely satisfactory way to measure the subjective <br /> effects of noise, or the corresponding reactions of annoyance and dissatisfaction.A wide variation <br /> in individual thresholds of annoyance exists, and different tolerances to noise tend to develop based <br /> on an individual's past experiences with noise. <br /> r Thus, an important way of predicting human reaction to a new noise environment is the way it <br /> compares to the existing environment to which one has adapted. In general,the more a new noise <br /> ' exceeds the previously existing ambient noise level,the less acceptable the new noise will be judged <br /> 3 � <br /> by those affected by it.With regard to increases in A-weighted noise level,the following relationships <br /> generally occur assuming that the introduced noise is of a similar character to sources composing <br /> the ambient noise environment: <br /> 1 <br /> 3 � <br /> Munn 8 Perkins Quarry Excavation Permit 3.4-5 ESA 1211486 <br /> Draft EIR April 2011 <br />
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