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ARCHIVED REPORTS_XR0003776
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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H
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HAZELTON
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2900 - Site Mitigation Program
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PR0540905
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ARCHIVED REPORTS_XR0003776
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Last modified
2/3/2020 9:23:25 PM
Creation date
2/3/2020 9:14:58 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003776
RECORD_ID
PR0540905
PE
2960
FACILITY_ID
FA0023406
FACILITY_NAME
SIERRA LUMBER MANUFACTURERS
STREET_NUMBER
375
Direction
W
STREET_NAME
HAZELTON
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
APN
147120808
CURRENT_STATUS
01
SITE_LOCATION
375 W HAZELTON AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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H <br /> 20 July 1998 <br /> AGE-NC Protect No 98-0448 <br />' Page 2 of 4 <br /> percent recharge prior to sample collection Ground water! samples were collected utilizing <br /> disposable polyethylene bailers and new nylon rope Sufficient ground water sample was collected <br /> ! <br /> from each well to fill three EPA-approved 40-m1 VOA vials containing 0 5 ml 18% hydrochloric a , <br />' acrd as a preservative for the samples Care was taken to ensure that visible air bubbles were not <br /> present in the VOAs after filling and capping Ground water sample containers were labeled with <br /> the well designation, date, time, and sampler's initials <br /> 23 LABORATORY ANALYSIS OF GROUND WATER SAMPLES <br /> Each ground water sample was logged on a chain-of-custody form,placed in a chilled container and <br /> transported to a California state-certified laboratory for analysis in accordance with EPA Methods <br /> i <br /> • 8015M for total petroleum hydrocarbons quantified as gasoline (TPH-g), <br /> • 8020 for volatile aromatics (benzene, toluene, ethyl benzene and xylene BTE&X) with <br /> methyl-tertiary butyl ether (MTBE), and <br /> • 8260 for tertiary butanol (TBA), di-isopropyl ether(DIPE),ethyl tert butyl ether(ETBE)and <br /> tert amyl methyl ether (TAME), and to confirm and quantify MTBE if detected by EPA <br /> Method 8020 <br /> 3.0. FINDINGS <br /> 31 RELATIVE GROUND WATER ELEVATION AND GRADIENT <br /> The depth to ground water in monitoring wells MW- through MW-3 was measured at 15 66 to <br /> p � g g <br /> 16 52 feet below the tops of the well casings Between April 1997 and June 1998, ground water <br /> elevation increased an average 4 80 feet at the site The ground water elevation data for MW-1 <br /> though MW-3 during June's ground water monitoring event is,depicted in Figure 3 <br /> During the June 1998 monitoring event, the ground water surface was between 3 53 and,4 34 feet <br /> above the screened intervals in monitoring wells MW-I through MW-3 Therefore, the wells are <br /> I "drowned", and may not yield samples fully representative of ground water conditions near the top <br /> of the saturated zone, where fuel hydrocarbons would be expected to have the greatest impact <br /> In June 1998,the gradient was calculated to be 0 006 ft/ft,or approximately 31 feet per mile(Figure <br /> 3) Based upon ground water momtonng data collected in June 1998, ground water was inferred to <br /> be flowing toward the southeast However, due to the low gradient at the site, slight variations in <br /> Advanced GeoEnvironmental,Inc <br /> ' i <br />
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