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2900 - Site Mitigation Program
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PR0537485
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Last modified
7/27/2020 3:42:55 PM
Creation date
7/27/2020 2:46:18 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0537485
PE
2957
FACILITY_ID
FA0021568
FACILITY_NAME
FORMER RAINWATER CAR WASH
STREET_NUMBER
420
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
21931206
CURRENT_STATUS
01
SITE_LOCATION
420 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Community Health and Safery Plan <br /> ' RAINWATER CAR WASH,Manteca,California 95336 Page 15 <br /> May 30,2012 <br /> t specific and limited assignment of performing air monitoring during the specific site operations expressly covered <br /> in this HSP. <br /> ' The air monitoring conducted by the SHSS or designee will be used to identify and quantify airborne levels of <br /> hazardous substances in order to determine the appropriate level of employee protection needed on-site,and if <br /> possible to delineate work zones. Site-specific action level criteria must be established for all the instruments that <br /> may be used in making field health and safety determinations.Other data, such as the visible presence of <br /> ' contamination and/or odors, or employee complaints,may also be used in making field health and safety <br /> decisions.As a result,the SHSS may establish exclusion zones and/or require a person to wear a respirator even <br /> though atmospheric air contaminant concentrations are below established HSP action levels. <br /> For sites containing petroleum hydrocarbons such as gasoline and related compounds,and/or certain chlorinated <br /> hydrocarbons such as tetrachloroethylene and/or trichloroethylene,monitoring can be accomplished using a'PID <br /> ' with a 10.6-electron-volt lamp or equivalent calibrated to isobutylene. Monitoring for the aforementioned gases <br /> and vapors should be done at the source of emission as well as in the breathing zone of site personnel believed to <br /> represent the highest risk of exposure. The PID will be checked with a calibration gas standard(hexane or <br /> ' isobutylene)prior to each day's activities and at any other time when the instrument response is questionable. The <br /> instrument check procedure will be recorded in a logbook and initialed by the person performing the procedure. <br /> Other methods of air sampling using colorimetric detector tubes,and/or sampling pumps with charcoal tubes may <br /> also be used at the direction of the SHSS,or if required by this HSP.If benzene levels could exceed 1 part per <br /> ' million(ppm)for extended periods of time,colorimetric detector tubes specific for benzene will be required. For <br /> certain chlorinated compounds(e.g.,methyl chloroform), an 11.7-electron-volt lamp should be used in the PID. <br /> Consult the NIOSH pocket guide to chemical hazards for information on ionization potentials before selecting the <br /> appropriate electron-volt lamp. <br /> For sites containing flammable or explosive gases and/or vapors(i.e.methane gas),and/or hydrogen sulfide <br /> ' and/or carbon monoxide, and/or oxygen deficiency atmospheres, monitoring will be accomplished using a four- <br /> gas direct reading instrument calibrated for methane,hydrogen sulfide,carbon monoxide and oxygen. Monitoring <br /> for the aforementioned gases and atmospheres should be done at the source as well as in the breathing zone of site <br /> personnel believed to represent the highest risk of exposure. The four-gas meter will be checked with a calibration <br /> gas standard prior to each day's activities and at any other time when the instrument response is questionable. The <br /> aforementioned instrument check procedure will be recorded in a logbook and initialed by the person performing <br /> the procedure. <br /> ' For sites containing elevated concentrations of airborne dust that could exceed the applicable PEL,a real-time <br /> aerosol monitor will be used.Monitoring for the aforementioned dusts and atmospheres should be done in the <br /> ' breathing zone of site personnel believed to represent the highest risk of exposure. The instrument will be checked <br /> prior to each day's activities according to the manufacturer's recommendations and procedures and at any other <br /> time when the instrument response is questionable. The aforementioned instrument check procedure will be <br /> ' recorded in a logbook and initialed by the person performing the procedure. <br /> All monitoring instruments will be operated and maintained pursuant to the manufacturer's written procedures. <br /> Instruments that exhibit an inappropriate field response or provide questionable results will not be used and sent <br /> out for servicing. <br /> 6.2 Exposure Monitoring Plan <br /> ' Before any field activities commence,a wind direction indicator may be used to ensure the direction that <br /> personnel will move when instructed to do so or in an emergency.This wind measurement will be followed by the <br /> sampling of the general background levels of gasoline, VOCs,dust etc. <br />
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