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ARCHIVED REPORTS XR0001705
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PR0522479
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ARCHIVED REPORTS XR0001705
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Entry Properties
Last modified
5/17/2019 3:18:37 PM
Creation date
5/17/2019 2:31:12 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001705
RECORD_ID
PR0522479
PE
2957
FACILITY_ID
FA0015299
FACILITY_NAME
GEWEKE LAND DEVELOPMENT & MARKETING
STREET_NUMBER
16
Direction
S
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04323013
CURRENT_STATUS
01
SITE_LOCATION
16 S CHEROKEE LN
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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• 10 March 2000 <br /> AGE-NC Project No. 95-0109 <br /> Page 2 of 4 <br /> 2.2. COLLECTION OF GROUND WATER SAMPLES <br /> The depth to water was remeasured after purging to ensure a minimum of 80 per cent recharge prior <br /> to sampling. Water samples were collected from each purged well using disposable plastic bailers. <br /> Immediately upon retrieval, the samples were transferred into 40-m1 EPA-approved VOA vials <br /> containing 0.5ml 18%hydrochloric acid as a sample preservative. The samples were labeled, stored <br /> on ice, and transported in a chilled container, under chain-of-custody, to McCampbell Analytical, <br /> Inc. (MAI), a State of California Department of Health Services (DHS)-certified analytical <br /> laboratory. All samples were analyzed for: <br /> • Total petroleum hydrocarbons quantified as gasoline (TPH-g) in accordance with EPA <br /> Methods 5030/8015m; <br /> • Volatile aromatic compounds: benzene, toluene, ethylbenzene and xylenes (BTEX) and <br /> methyl tertiary-butyl ether (MTBE) in accordance with EPA method 80201602; and <br /> • Volatile organic compounds with fuel oxygenates: di-isopropyl ether(DIPE), ethyl tertiary- <br /> butyl ether(ETBE),MTBE,tertiary-amyl methyl ether(TAME) and tertiary butanol (TBA) <br /> in accordance with EPA Method 8260/8260m. <br /> Samples collected from MW-9 and MW-14 were also transferred into one-liter amber bottles without <br /> added preservative. These samples were transported to A. Keith Kaufman in Culver City and <br /> analyzed for physicochemical properties and microbiological enumeration. <br /> 3.0. FINDINGS <br /> Ground water elevation and flow direction were calculated from field data; hydrocarbon-impact to <br /> ground water was inferred from laboratory analysis of the ground water samples. <br /> 3.1. GROUND WATER GRADIENT AND DIRECTION <br /> The depth to ground water ranged from 50.62 feet bsg north of the site to 53.23 feet bsg south of the <br /> site during the January 2000 monitoring event. The data indicates an average 1.58-foot increase of <br /> ground water elevation between September 1999 and January 2000. Ground water elevation <br /> contours, based upon data collected on 18 January 2000, are depicted in Figure 3. The inferred <br /> ground water flow direction is toward the south. The ground water depression and localized high <br /> previously observed west of the site was not evident during the January 2000 monitoring event. <br /> Ground water elevations are summarized on Table 1. <br /> Advanced GeoEnviron mental,Inc. <br />
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