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ARCHIVED REPORTS XR0011078
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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C
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814
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3500 - Local Oversight Program
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PR0544222
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ARCHIVED REPORTS XR0011078
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Entry Properties
Last modified
3/5/2019 5:09:56 PM
Creation date
3/5/2019 1:55:03 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011078
RECORD_ID
PR0544222
PE
3528
FACILITY_ID
FA0005976
FACILITY_NAME
TIRE & WHEEL MASTERS
STREET_NUMBER
814
Direction
E
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
16718101
CURRENT_STATUS
02
SITE_LOCATION
814 E CHARTER WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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WNg
Tags
EHD - Public
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ectruin Laboratories Chen9acal Fact Sheet-Cas#1 71432 littp//-Www speclab coati/cornpound/c92527 <br /> Demand 1986 1,603 million gal, 1987 1,667 mullion gal, 1991 projected/ 1,790 <br /> `J _ million gal (Includes imports, 155 million gal were imported m 1986 <br /> C } <br /> . Apparent olor CLEAR,COLORLESS LIQ,RHOMBIC PRISMS <br /> Odor JAROMATIC ODOR <br /> ' 1__T Boiling Po1nt -___J$0 1 DEG "-- <br /> ! Melti"F Point _'_-'JS 5 DEG? <br /> r Molecular erg t 7$ 11J � � J <br /> Density- ---__IO 7$87 AT 15 DEG 4 DEG <br /> - �(BENZENE HAS DISTINCTIVE SRP AROMATIC ODOR HOWEVER <br /> ' Odor Threshold Concentration i/WARNING PROPERTIES ARE INADEQUATE SINCE I00 PPM HAS <br /> 1IRRITATION RATING OF 0&ODOR INTENSITY BETWEEN 1 &2 4 68 PPM <br /> 1n air 4 9 mg/cu in (character istic odor), in water 2 0 mg/1 <br /> ' Saaltsttivtty Data _ Benzene is irritant <br /> Benzene will enter the atmosphere primarily fiom fugitive emissions and exhaust <br /> connected with its use in gasoline Anothei unportant source is emissions associated <br /> with its production and use as an industrial intermediate In addition, there are <br /> discharges into water fiom industrial effluents and losses during spalls If benzene is <br /> released to soil, it will be subject to Lapid volatilization near the surface and that { <br /> which does not evaporate will be lughly to very highly mobile in the soil and may <br /> leach to groundwater It may be subject to biodegiadation based on ieported <br /> biodegradation of 24%and 47%of the initial 20 ppm benzene in a mase-rich <br /> para-biownish soil in 1 and 10 weeks,respectively It may be subject to <br /> ' biodegradation in shallow,aei obic groundwaters,but probably not under anaei obit <br /> conditions If benzene is released to water,it will be subject to rapid volatilization, <br /> the half-life for evaporation in a wind-wave tank with a moderate wind speed of <br /> 7 09 msec was 5 23 his, the estimated half-life for volatilization of benzene fiom a <br /> model river one meter deep flowing I m/sec with a wind velocity of 3 m/sec is <br /> estimated to be 2 7 hi s at 20 deg C It will not be expected to significantly adsorb to <br /> sediment,bnoconcentiate in aquatic otganisnms or hydrolyze It may be subject to <br /> Environmental I[axlpact biodegradation based on a teported biodegradation half-life of 16 days nm an aerobic <br /> ' raver die-away test In a marine ecosystem biodegradation occurred in 2 days aftei <br /> ? an acclimation period of 2 days and 2 weeks in the summei and spring,respectively, <br /> wheieas no degiadation occurred in winter Accoiding to one experiment,benzene <br /> ' ,has a half-life of 17 days due to photodegiadation which could contribute to <br /> benzene's removal in situations of cold watei,poor nutrients,of other conditions I <br /> less conductive to microbial degradation If benzene is released to the atrnospheie, it <br /> will exist predominantly in the vapor phase Gas-phase benzene will not be subject <br /> 4to du ect photolysis but it will react with photochemically produced hydroxyl <br /> radicals with a half-life of 13 4 days calculated using an experimental sate constant <br /> j ,for the reaction The reaction tinie in polluted atmospheres which contain nitrogen <br /> oxides or sulfur dioxide is accelerated with the half-life being reported as 4-6 hours <br /> jlPioducts of photooxidation include phenol,nmttophenols,rutrobernzene,formic acid, <br /> and peroxyacetyl nitrate Benzene is fanly soluble m water and is iemoved from the ! <br /> ! atmosphere in rain The primary routes of eaposuie ane inhalation of contaminated e <br /> air,especially in areas with high traffic,and in the vicinity of gasolene service <br /> stations and consumption of contaminated dunking water <br /> ,TERRESTRIAL FATE If benzene is released to soil it will be subject to rapid <br />' !volatilization near the surface That which does not evaporate will be highly to very <br /> !highly mobile in soil and may leach to groundwatei The effective half-lives for i <br /> ;volatilization without water evaporation from soil to benzene uniformly dnstitbuted i <br /> I !to 1 and 10 cm in soil were 7 2 and 38 4 days,respectively It may be subject to <br />' I ibiodegradation based on ieported biodegradation of 24%and 47%of the initial 20 <br /> f <br /> !ppm benzene in a based-itch para-brownish soil in land 10 weeks, iespectively It <br /> I may be subject to biodegiadation in shallow, aerobic groundwaters,but probably <br /> not under anaerobic conditions AQUATIC FATE If benzene is released to water, it <br /> !will be subject to iapid volatilization,the half-life for evaporation in a wind-wave <br /> 1 <br /> nf� nuinr-,nm e 1> <br />
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