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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
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\MIGRATIONS\R\RIVER\26292\QX-890002\SU0007300\CORRESPOND.PDF
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EHD - Public
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NOISE FUNDAMENTALS AND TERMINOLOGY <br /> Background on Noise <br /> Noise is often described as unwanted sound. Sound is defined as any pressure variation in air <br /> that the human ear can detect. If the pressure variations occur frequently enough (at least 20 <br /> times per second), they can be heard and are called sound. The number of pressure variations <br /> per second is called the frequency of sound, and is expressed as cycles per second, called <br /> Hertz (Hz). <br /> Measuring sound directly in terms of pressure would require a very large and awkward range of <br /> numbers. To avoid this, the decibel scale was devised. The decibel scale uses the hearing <br /> threshold (20 micropascals of pressure), as a point of reference, defined as 0 dB. Other sound <br /> pressures are then compared to the reference pressure, and the logarithm is taken to keep the <br /> numbers in a practical range. The decibel scale allows a million-fold increase in pressure to be <br /> expressed as 120 d8. Another useful aspect of the decibel scale is that changes in levels (dB) <br /> correspond closely to human perception of relative loudness. Table 1 contains definitions of <br /> Acoustical Terminology. Table 2 shows common noise levels associated with various sources. <br /> Effects of Noise on People <br /> The perceived loudness of sounds is dependent upon many factors, including sound pressure <br /> level and frequency content. However, within the usual range of environmental noise levels, <br /> perception of loudness is relatively predictable, and can be approximated by weighing the <br /> frequency response of a sound level meter by means of the standardized A-weighing network. <br /> There is a strong correlation between A-weighted sound levels (expressed as dBA) and <br /> community response to noise. For this reason, the A-weighted sound level has become the <br /> standard tool of environmental noise assessment. All noise levels reported in this section are in <br /> terms of A-weighted levels in decibels. <br /> Community noise is commonly described in terms of the "ambient' noise level, which is defined <br /> as the all-encompassing noise level associated with a given noise environment. A common <br /> statistical tool to measure the ambient noise level is the average, or equivalent, sound level <br /> (Leq) over a given time period (usually one hour). The Leq is the foundation of the Day-Night <br /> Average Level noise descriptor, Ldn, and shows very good correlation with community response <br /> to noise. <br /> The Day-Night Average Level (Ldn) is based upon the average noise level over a 24-hour day, <br /> with a +10 decibel weighing applied to noise occurring during nighttime (10:00 p.m. to 7:00 <br /> a.m.) hours. The nighttime penalty is based upon the assumption that people react to nighttime <br /> noise exposures as though they were twice as loud as daytime exposures. Because Ldn <br /> represents a 24-hour average, it tends to disguise short-term variations in the noise <br /> environment. Ldn-based noise standards are commonly used to assess noise impacts <br /> associated with traffic, railroad and aircraft noise sources. <br /> Environmental Noise Analysis <br /> Munn&Perkins Expanded Hours of Operations—San Joaquin County <br /> Page 4 <br />
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