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ARCHIVED REPORTS XR0002618
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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H
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HARDING
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3500 - Local Oversight Program
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PR0544424
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ARCHIVED REPORTS XR0002618
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Entry Properties
Last modified
5/6/2019 11:57:32 AM
Creation date
5/6/2019 11:23:30 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002618
RECORD_ID
PR0544424
PE
3529
FACILITY_ID
FA0005099
FACILITY_NAME
HESS DUBOIS CLEANERS
STREET_NUMBER
300
Direction
W
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95203
CURRENT_STATUS
02
SITE_LOCATION
300 W HARDING WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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SJGOV\wng
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EHD - Public
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•`� r f.r - .. h s'^ F:,' fH'. r �y _ L , .gym. � ? <br /> ,I <br /> SII '1 } 1 .,l•_ ' 1 r� ,}e �.Y'. - <br /> 41 <br /> 2 2. ,COLLECTION AND`ANALYSIS'OF'GROUND WATER;SAMPLES, ' <br /> ' • G'round'water samples were collected from the pur'ged,wells using new disposable bailers following . <br /> `recovery of.at.least 80%,05f th pre-purge casing water volume. 'Inrmediateiy upon'retrieval, the f�. <br /> samples were fransferred.into 40-ml EPA-appro�ed?VOA vials containing 0.5 ml'ofhydrochloric <br /> aeid`(18%)as a sample preservative,,and were properly labeled.-The samples were transported in.a <br /> chilled coritainer.under.chain-of-custody to Cal Tech•Environmental Laboratories, Inc•(CTEL),'a <br /> State.of California Department.of Health- Services-(DHS)_certified laboratory ,in Paramount, <br /> :.California. The'samples were arialyzed for`. <br /> •' -Volatile organic compounds (VOCs),,specifically;benzene, toluene, ethylbenzene and <br /> xylenes (BTEX) and the Riel additives methanol, ethanol, ethylene dibromide (EDB), 1,2-' <br /> dichloroethane(1,2-DCA);tertiary butanol(TBA),di-isopropyl ether(DIPE),ethyl tert butyl <br /> ether(ETBE);tert arnyl methyl ether(TAME)`, and MTBE by EPA Method 8260B;,a'nd <br /> 1 . Total petroleum'hydrocarb6ns quantified as stoddard solvents (TPH-ss) by EPA Method <br /> 8015 Modified. <br /> . 3.0. FINDINGS <br /> Ground water flow'direction and gradient were inferred from the field data. The current distribution' <br /> 'of dissolved petroleum hydrocarbons and dissolved.chlorinated hydrocarbons.was assessed from- <br /> laboratory analytical results of the soil and groundwater samples. r <br /> ' 3:1. GROUND WATER GRADIENT AND DIRECTION <br /> During the September.2002-ground water•monitoring event,.the depth to ground water at the site <br /> ranged from 24.97 to'26.57 feet.below the to s ofthe g well casings.The ground water flow direction <br /> ' g p v <br /> was toward the northeast from well MW,-5 toward well MW-10, with a gradient-of approximately <br /> ' 0.00 15 feet/feet. Ground water elevation data are summarized in Table 1. The contoured ground' <br /> .water elevation for.the ground water monitoring event is depicted in Figure.3. <br /> Wells MW-1through MW-5 were screened between 30 or 34 and 50 feet bsg;wells MW-6 through, <br /> MW-10 were screened;between 20 or 25 and 45 or 50 feet bsg. The ground water level.'was more <br /> than 10 feet above the tops.of the screened intervals of wells MW-1 and MW-2;almost 6 feet above <br /> the tops of the screened intervals of wells MW-3R,MW74 and MW-5,and at the tops of the screened <br /> intervals of wells MW-6•through MW40. <br /> ,3.2. ' LABORATORY ANALYTICAL RESULTS OF GROUND WATER SAMPLES J <br /> During the September 2002.m6nitorin9 event,TPH-ss.was detected in'ground water samples from' y - <br /> ' monitoring wells MW-3, MW-6, ,MW-7; MW-9, MW-10 at concentrations ranging between ' <br /> 120 micrograms per liter(µg/1) in MW-7.to'3,600 pg/l,in MW-9. <br />
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