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ARCHIVED REPORTS_XR0005924
EnvironmentalHealth
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1022
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2900 - Site Mitigation Program
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PR0534875
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ARCHIVED REPORTS_XR0005924
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Last modified
4/7/2020 2:07:53 PM
Creation date
4/7/2020 1:45:18 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005924
RECORD_ID
PR0534875
PE
2960
FACILITY_ID
FA0020170
FACILITY_NAME
AAA TRUCK WASH/JIMCO TRUCK PLAZA
STREET_NUMBER
1022
Direction
E
STREET_NAME
FRONTAGE
STREET_TYPE
RD
City
RIPON
Zip
95366
APN
26102004
CURRENT_STATUS
01
SITE_LOCATION
1022 E FRONTAGE RD
P_LOCATION
05
P_DISTRICT
005
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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' 2 <br /> • 1 December 2001 <br />' AGE-NC Project No 98-0433 <br /> Page 2 of <br />' 2 2 GROUND WATER SAMPLE COLLECTION <br />' Prior to the collection of ground water samples, the depth to ground water was re-measured in each <br /> well to ensure that a minimum of 80%ofthe initial water volume had recharged Water samples were <br /> then collected from each well using the pre-dedicated disposable bailer The water was transferred <br />' into one 1-liter amber bottle and three chilled 40-m1 volatile organic analysis(VOA)vials containing <br /> 0 5 ml hydrochloric acid(18%) as a sample preservative After collection, the samples were Iabeled <br /> and placed in a chilled container for transportation under chain-of-custodyto McCampbell Analytical <br />' Laboratories (MAI), a DHS-certified analytical laboratory Each sample was analyzed for <br /> • Total petroleum hydrocarbons quantified as gasoline and diesel (TPH-g and TPH-d) in <br /> Iaccordance with EPA Method 8015 Modified, <br /> • Benzene, toluene, ethyl benzene and total xylene(BTEX) in accordance with EPA Method <br /> I 8020, <br /> • Oxygenated fuel additives - methyl butyl ether (MTBE), tertiary butyl alcohol (TBA), di- <br /> isopropyI ether (DIPE), ethyl tertiary butyl ether (ETBE) and tertiary amyl methyl ether <br /> pe (TAME) in accordance with EPA Method 8260 Modified <br /> 3.0 FINDINGS - <br /> I Ground water elevations were determined by subtracting the measured depths-to-water• from the <br /> surveyed casing elevations Ground water flow directions were determined by contouring the water <br /> elevations on a scaled site plan (Figure 3) The impact of the unauthorized release on ground water <br /> Iwas quantified by laboratory analysis of samples collected during the quarter <br /> 3 1 GROUND WATER GRADIENT AND FLOW DIRECTION <br /> Depth to ground water at the site on 05 October 2001 ranged from 20 26 to 22 04 feet below well <br /> casing tops The ground water elevations at the site ranged from 36 35 feet to 36 90 feet above mean <br /> sea level (mst) The data indicates an average decrease of the ground water elevation at the site of <br /> 1 6 feet since the previous quarterly monitoring event <br /> Ground water flow direction and gradient were calculated from the October 2001 gauging data The <br /> flow direction was determined to be in a westerly direction,from well MW-6 toward the former UST <br /> location and north away from the former UST area with a hydraulic gradient of approximately 0 002 <br /> feet/feet The depth to ground water and calculated elevation date are presented in Table 1 Figure <br /> I3 illustrates the contoured ground water elevations <br /> Advanced GeoEnviroamental,Inc <br /> I <br />
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