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ARCHIVED REPORTS_XR0010990
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545039
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ARCHIVED REPORTS_XR0010990
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Last modified
12/10/2019 1:50:39 PM
Creation date
12/10/2019 11:04:20 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010990
RECORD_ID
PR0545039
PE
3528
FACILITY_ID
FA0010186
FACILITY_NAME
DEL MONTE FOODS PLNT #33 - DISCO WH
STREET_NUMBER
110
Direction
N
STREET_NAME
FILBERT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15702009
CURRENT_STATUS
02
SITE_LOCATION
110 N FILBERT ST
P_DISTRICT
001
QC Status
Approved
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;,pectrum Laboratories Chemical Fact Sheet - Cas# 107062 Page 2 of 3 <br /> A arent Color iCLEAR,COLORLESS,OILY LIQUID <br /> Odor IPLEASANT ODOR;CHLOROFORM-LIKE ODOR;Sweet <br /> Density 1.2351 AT 20 DEG C <br /> Although olfactory warning properties are limited by development of tolerance,this liquid has an <br /> odor detectable between 6&40 ppm. Of 20 subjects, 13 could detect ethylene dichloride at 6 ppm <br /> Odor Threshold (23.2-24.9 mg/cu m),6 persons could detect it at 4.5 ppm(17.5 mg/cu m),and 1 person at 3 ppm <br /> CoIICeIItration (12.2 mg/cu m). Odor is not a dependable guide for avoiding dangerous chronic exposures to <br /> EDC.The odor may be considered pleasant until well above 180 ppm,and may be missed below <br /> 100 ppm.Detection in air=2.5X 10-2 mg/l(gas),chemically pure Odor threshold low:24 mg/cu <br /> m;high:440 mg/cu m. <br /> The majority of 1,2-dichloroethame released into the environment will enter the atmosphere mostly! <br /> from its production and use as a chemical intermediate,solvent,and use as a lead scavenger in <br /> gasoline.Once in the atmosphere,it may be transported Iong distances and is primarily removed <br /> Environmental <br /> by photooxidation(half-life approx. 1 month).Releases to water will primarily be removed by <br /> Impact evaporation(half-life several hours to 10 days).Releases on land will dissipate by volatilization to <br /> air and by percolation into groundwater where it is likely to persist for a very long time. 1,2- <br /> Dichloroethane is not expected to bioconcentrate in the food chain;its presence in some food <br /> products is probably due to its use as an extractant.Major human exposure is from urban air, <br /> drinking water from contaminated aquifers and occupational atmospheres. <br /> TERRESTRIAL FATE: Smaller releases on land will evaporate fairly rapidly because of 1,2- <br /> dichlorethane's moderately high vapor pressure.Larger releases may leach rapidly through sandy <br /> soil into groundwater.AQUATIC FATE: When 1,2-dichloroethane is released to surface water,its! <br /> primary loss will be by evaporation.The half-life for evaporation will depend on wind and mixing <br /> conditions and was of the order of hours in the laboratory.However a modeling study using the <br /> EXAMS model for a eutrophic lake gave a half-life of 10 days .The half-life for evaporation <br /> Environmental would be much less in a river or stream.Chemical and biological degradation is expected to be <br /> Fate very slow. Adsorption to sediment is not expected.ATMOSPHERIC FATE: When released to the <br /> atmosphere, 1,2-dichloroethane will degrade by reaction with hydroxyl radicals which are formed <br /> photochemically in the atmosphere with a half-life of a little over a month. One would expect the <br /> chemical to be transported long distances and be washed out in rain.Aquatic and Atmospheric <br /> Fate: Chloroethanes are expected to be present in industrial air and water emissions.They <br /> volatilize rapidly from surface water and persist in urban atmospheres. Hydrolysis and <br /> biodegradation are expected to be slow.Chloroethanes <br /> 1,2-Dichloroethane was found in the waters of 28 cities at level of 0-6 ug/l.The Aerojet-General <br /> Corporation reports that 1,2-dichloroethane has been identified as a groundwater contaminant at a <br /> site outside Sacramento,CA.SURFACE WATER:USA-6 river basins 1-90 ppb,53 of 204 sites <br /> pos,only 1 site above 15 ppb;Ohio R basin(1977-1978)0.1-29 ppb,39 of 243 samples pos; <br /> Ohio R basin(1980-1981,4972 samples)7%pas,44 samples 1-10 ppb; 105 USA cities-raw <br /> drinking water 1-4 ppb,0.55 ppb median,9.5%pos; 80 USA municipal water systems-raw water <br /> 0-0.3 ppb, 14%pos;Lake Erie-2 sites,4 ppb, 1 site pos(6). SEAWATER:Gulf of Mexico 0-210 <br /> pa trillion(anthropogenic influence)and not detected(unpolluted areas).GROUNDWATER: <br /> Drinking Water 13 USA cities-rawoundwater 0.2 b 7.7% <br /> Impact � pp � pos •� State groundwater survey:2 states 400 ppb <br /> max,7%pos,Aerojet General Rocket Plant-well water, Sacramento-up to 52 ppm. <br /> DRINKING WATER: 133 USA Cities-finished surface water 0.8-4.8 ppb, 1.8 ppb median, 4.5% <br /> pos;25 USA cities-finished groundwater-0.2 ppb avg,4.0%pas .National Organic Monitoring <br /> Survey(1976-77)-3 of 218 samples pos,limits of detection<0.2 ppb .Detected in 7 wells in the <br /> Central Sands area of Wisconsin 2 of which exceeded the recommended health advisory of 7 ppb <br /> (detection limit=0.1-3.0 ppb).EFFL:Industries whose wastewater may exceed a mean of 1000 <br /> ppb include:photographic equipment/supplies,pharmaceutical mfg and organic chemicals/plastics <br /> mfg;max conn in wastewater was 14 ppm(pharmaceutical mfg) . <br /> http://www.speciab.com/compound/cIO7062.htm 811/00 <br />
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