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ARCHIVED REPORTS XR0001708
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PR0522479
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ARCHIVED REPORTS XR0001708
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Last modified
5/17/2019 3:17:41 PM
Creation date
5/17/2019 2:33:05 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001708
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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12 February 1999 <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 in each purged well was remeasured after purging to ensure a minimum of 80 per <br /> cent recharge prior to sampling. Water samples were collected from each purged well using <br /> disposable plastic bailers. Immediately upon retrieval,the samples were transferred into 40-m1 EPA- <br /> approved VOA vials containing 0.5 ml 18%hydrochloric acid as a sample preservative. The samples <br /> were labeled, stored on ice, and transported in a chilled container, under chain-of-custody, to <br /> McCampbell Analytical, Inc. (MAI) in Pacheco, California, a California Department of Health <br /> Services (DHS)-certified laboratory. All samples were analyzed for: <br /> • Total petroleum hydrocarbons quantified as gasoline (TPH-g) in accordance with EPA <br /> Method 5030/8015m; <br /> • Volatile organic compounds (benzene, toluene, ethylbenzene and xylenes; BTEX) with <br /> methyl tertiary-butyl ether(MTBE) in accordance with EPA Method 602; and <br /> • Volatile organic compounds with oxygenated compounds (di-isopropyl ether [DIPE], ethyl <br /> tertiary-butyl ether [ETBE], MTBE,tertiary-amyl methyl ether [TAME] and tertiary-butanol <br /> [TBA]) in accordance with EPA Method 8260/8260m. <br /> • <br /> 3.0. FINDINGS <br /> 3.1. GROUND WATER GRADIENT AND DIRECTION <br /> The depth to ground water ranged from 50.65 feet below surface grade (bsg) north of the site to <br /> 53.78 feet bsg south of the site. The data indicates an average 1.04 feet increase of ground water <br /> elevation since September 1998. Ground water elevations are summarized on Table 1. <br /> Ground water elevation contours, based upon data collected on 21 December 1998, are depicted in <br /> Figure 3. The inferred ground water flow direction is toward the south. Ground water elevations for <br /> MW-I through MW-3 were higher than the surrounding wells. These wells exhibit poor recharge <br /> and do not appear to be in equilibrium with the surrounding ground water. Therefore data from these <br /> wells was not used to determine the ground water flow direction. The depth to ground water in MW- <br /> 9 was higher than expected, based upon data from surrounding wells. Remeasurement of ground <br /> water depth following purging confirmed the initially measured depth to ground water. <br /> Advanced GeoEnvironmental,Inc. <br />
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