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ARCHIVED REPORTS_XR0006067
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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3500 - Local Oversight Program
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PR0545601
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ARCHIVED REPORTS_XR0006067
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Last modified
3/23/2020 4:57:39 PM
Creation date
3/23/2020 4:33:44 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006067
RECORD_ID
PR0545601
PE
3528
FACILITY_ID
FA0003588
FACILITY_NAME
EAGLE ROOFING PRODUCTS
STREET_NUMBER
2191
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95206
APN
16331006
CURRENT_STATUS
02
SITE_LOCATION
2191 NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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I <br />' 15 March 2003 <br /> • AGE-NC Project No 98-0534 <br />' Page 2 of 3 <br />' 2 2 COLLECTION AND ANALYSIS OF GROUND WATER SAMPLES <br /> After the depth to ground water was measured to ensure that a minimum of 80% well-volume <br />' recharge had been achieved, a water sample was collected from each well using a dedicated and <br /> disposable plastic bailer Immediately upon retrieval,samples were transferred Into one-liter amber <br /> bottles and three 40-m1 EPA-approved volatile organic analysis(VOA)vials containing 0 5 nil 18% <br /> hydrochloric acid as a sample preservative The samples were stored in a chilled container and the <br /> samples were logged on a chain-of-custody form The samples were later transported under chain-of- <br /> custody to Cal Tech Environmental Laboratory(CTEL), a State of California Department of Health <br />' Services (DHS)-certified analytical laboratory#2424 for analysis The samples were analyzed for <br />' • Total petroleum hydrocarbons quantified as gasoline (TPH-g) and diesel (TPH-d) In <br /> accordance with EPA Method 8015-modified for gasoline and diesel, <br /> • Benzene, toluene, ethylbenzene and total xylenes (BTEX) and methyl tertiary-butyl ether <br /> (MTBE) in accordance with EPA Method 8 02 1, and <br /> • Oxygenated compounds - di-Isopropyl ether (RIPE), ethyl tertiary-butyl ether(ETBE), <br /> M MTBE,tertiary-amyl methyl ether(TAME),tertiary butanol(TBA),ethanol,methanol, 1,2- <br /> dlbromoethane (EDB) and 1,2-dichloroethane(1,2-DCA) in accordance with EPA Method <br /> 8260B <br /> 3.0. FINDINGS <br /> Ground water elevation, flow direction and gradient were determined from field data collected on <br /> 23 January 2003 The contaminant impact to ground water was assessed from the laboratory data <br />' 3 1 GROUND WATER ELEVATION AND GRADIENT <br /> The relative elevation of ground water in each well was calculated by subtracting the depth to ground <br /> water from the relative casing elevation (Table 1) The average depth to ground water on <br /> 23 January 2003 was 10 feet below the tops of the well casings A ground water ridge is present in <br /> the area of the former UST with ground water flowing towards the northeast away from the former <br /> UST area, with a gradient of approximately 0 0063 feet/feet and towards the southwest away from <br /> the former UST area to 0 0052 feet/feet (see Figure 3) The ground water elevation of monitoring <br /> wells MW-4 and MW-5 appeared anomalously low and further failed to recharge after purging, <br />' therefore the data from these wells was not used to map the ground water elevation <br /> • <br /> Advonced GeoEnvironmental,Inc. <br /> 1 <br />
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