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SU0014502
Environmental Health - Public
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SU0014502
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Entry Properties
Last modified
8/25/2022 10:29:54 AM
Creation date
11/4/2021 4:18:13 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0014502
PE
2675
FACILITY_NAME
PA-1900240
STREET_NUMBER
11000
Direction
N
STREET_NAME
WEST
STREET_TYPE
LN
City
LODI
Zip
95242-
APN
05908029, -07 -30
ENTERED_DATE
11/4/2021 12:00:00 AM
SITE_LOCATION
11000 N WEST LN
RECEIVED_DATE
5/2/2022 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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Administrative Draft Environmental Impact Report <br /> Gill Medical Center Project <br /> 4.15.1.5 Effects of Noise on People <br /> Hearing Loss <br /> While physical damage to the ear from an intense noise impulse is rare, a degradation of auditory acuity <br /> can occur even within a community noise environment. Hearing loss occurs mainly due to chronic <br /> exposure to excessive noise but may be due to a single event such as an explosion. Natural hearing loss <br /> associated with aging may also be accelerated from chronic exposure to loud noise. <br /> The Occupational Safety and Health Administration (OSHA) has a noise exposure standard that is set at <br /> the noise threshold where hearing loss may occur from long-term exposures. The maximum allowable <br /> level is 90 dBA averaged over eight hours. If the noise is above 90 dBA, the allowable exposure time is <br /> correspondingly shorter. <br /> Annoyance <br /> Attitude surveys are used for measuring the annoyance felt in a community for noises intruding into <br /> homes or affecting outdoor activity areas. In these surveys, it was determined that causes for annoyance <br /> include interference with speech, radio and television, house vibrations, and interference with sleep and <br /> rest.The Ldn as a measure of noise has been found to provide a valid correlation of noise level and the <br /> percentage of people annoyed. People have been asked to judge the annoyance caused by aircraft noise <br /> and ground transportation noise.There continues to be disagreement about the relative annoyance of <br /> these different sources. For ground vehicles, a noise level of about 55 dBA Ldn is the threshold at which a <br /> substantial percentage of people begin to report annoyance. <br /> 4.15.2 Fundamentals of Environmental Groundborne Vibration <br /> 4.15.2.1 Vibration Sources and Characteristics <br /> Sources of earthborne vibrations include natural phenomena (e.g., earthquakes,volcanic eruptions, sea <br /> waves, landslides) or manmade causes (explosions, machinery, traffic, trains, construction equipment, etc.). <br /> Vibration sources may be continuous (e.g., factory machinery) or transient (e.g., explosions). <br /> Ground vibration consists of rapidly fluctuating motions or waves with an average motion of zero. Several <br /> different methods are typically used to quantify vibration amplitude. One is the peak particle velocity <br /> (PPV); another is the root mean square (RMS)velocity. The PPV is defined as the maximum instantaneous <br /> positive or negative peak of the vibration wave.The RMS velocity is defined as the average of the squared <br /> amplitude of the signal.The PPV and RMS vibration velocity amplitudes are used to evaluate human <br /> response to vibration. <br /> PPV is generally accepted as the most appropriate descriptor for evaluating the potential for building <br /> damage. For human response, however, an average vibration amplitude is more appropriate because it <br /> takes time for the human body to respond to the excitation (the human body responds to an average <br /> vibration amplitude, not a peak amplitude). Because the average particle velocity over time is zero, the <br /> RMS amplitude is typically used to assess human response.The RMS value is the average of the amplitude <br /> squared over time, typically a 1- sec. period (FTA 2018). <br /> Noise 4.15-6 October 2021 <br />
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