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ARCHIVED REPORTS XR0006988
EnvironmentalHealth
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EIGHT MILE
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2900 - Site Mitigation Program
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PR0518132
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ARCHIVED REPORTS XR0006988
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Last modified
7/10/2019 1:55:29 PM
Creation date
7/10/2019 11:44:25 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006988
RECORD_ID
PR0518132
PE
2960
FACILITY_ID
FA0013716
FACILITY_NAME
H & H MARINA
STREET_NUMBER
15135
STREET_NAME
EIGHT MILE
STREET_TYPE
RD
City
STOCKTON
Zip
95219
APN
06908021
CURRENT_STATUS
01
SITE_LOCATION
15135 EIGHT MILE RD
P_LOCATION
01
QC Status
Approved
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EHD - Public
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Herman do Helen s Marina third Quarter 1998 C,ruundw.ater Moniuinng <br /> Novernhcr 23 1998 <br /> Page. 3- <br /> Groundwater Samples were, collected by filling the sample containers directly from the pump discharge tubing <br /> 3-he groundwater was transferred to three 40-milliliter glass volatile organic analysis (VOA) vials fitted with <br /> Teflon-lined caps (fur petroleum hydrocarbon analysts) and to a one-liter polyethylene bottle (for laboratory <br /> tested intrinsic bioremcdiation parameters - alkalinity nitrate, sulfate, and ferrous iron) rhe vials were checked <br />' to assure that no air bubbles were present l;ach sample container was labeled and placed in a cooler chilled with <br /> ice and delivered under chain-of-custody procedures to CGeoAnalytical Laboratories, inc , in Modesto, California, <br /> within 24 hours of sample collection <br /> l-or quality control, one rinsate sample was colleLtcd and labeled 1432-MW5-9130198 the rinsate sample was <br /> collected by pumping hydrocarbon-free water through the Grundfos Readitlo 11 submersible pump and into the <br /> sampling containers after the pump was decontaminated After the rinsate Sample was collected, the pump was <br /> used to sample monitor wel l MW-1 Results of laboratory analyses are discussed in Section 3 3 <br /> 3 2 LABORATORY ANALYTICAL METHODOLOGY <br /> The methods used for laboratory analyses for the September 30, 1998, groundwater monitoring event arc <br /> summarized in Table 1 <br /> Table I <br /> Laboratory Methods <br /> 1 Analyte(s) BTFX TPH-G Gasoline Oxygenates/Additives Alkalinity Nitrate Sulfate Ferrous Iron <br /> Method 602 5030/1 UFT 8260 310 1 300 300 SM-3500-Fe <br /> MDet I imit 0 3 ug/1 (13TI-) 0 05 rngil 1 0 4g/1 10 mg/] l 0 mg/1. 1 mg/i 0 1 mg/L <br /> 0 6µg/1 (X) 10 0µg/l (tert Butanol) <br />' BTFX beniene toluene, ethyl bensene and total xylenes <br /> TP11-G=total petroleum hydrocarbons,quantified as gasoline <br /> Gasoline Oxygenates/Additives methyl tertiary butyl ether(MTBE),ethanol tertiary-butanol,di-isopropyl ether(DiPP) ethyl <br /> tertiary-butyl ether(ETBE)and tertiary amyl methyl ether(TAME) <br />' 3 3 LABORATORY ANALYTICAL RESULTS <br /> BTEX, TPH-G and the selected gasoline oxygenates/additives were not detected at or above the laboratory <br />' reported detection limits in the sample collected from MW-1 or the rinsate sample (1432-MW5-9/30198) <br /> Ethanol, tertiary-butanol, DIPS, and ETBE were not detected at or above the laboratory reported detection limits <br /> in any of the groundwater samples Toluene was detected at a concentration of 7 0 µg/l in the groundwater <br />' sample collected from MW-2 Benzene, ethyl benTene, and total xylenes were not detected at or above raised <br /> laboratory detection limits in the sample collected from monitor well MW-2 BTEX constituents were not <br /> detected at or above raised laboratory reported detection limits in the groundwater sample collected from MW-3 <br />' TAME was detected in the groundwater samples collected from monitor wells MW-2 and MW-3 in <br /> concentrations of 270 µg/l and 22 gg/l, respectively TPH-G constituents were not detected at or above a raised <br /> and a standard laboratory reported detection limit in the samples collected from MW-2 and MW-3, respectively <br /> The analytical detection limits associated with BTEX constituents for the samples collected from monitor wells <br /> MW-2 and MW-3 were raised, due to relatively high concentrations of MTBE in the samples collected from <br /> those wells MTBE was detected at 59,000 pg/1 and 5,900 4g11 in the samples collected from MW-2 and MW-3, <br />' respectively The analytical detection limits associated with BTEX constituents for the sample collected from <br /> MW-4 were also raised due to the presence of petroleum hydrocarbons in the sample Benzene, ethyl benzene, <br /> . total xylenes, and MTBE were detected in concentrations of 35 gg/l, 15 4g/1, 13 gg/l, and 3 7 pg/l, respectively, <br />' in the sample collected from MW-4 A concentration of 0 2 mg/I of TPH-G was detected in the sample collected <br /> ow NZ6—w <br />' t� CONi)OR <br />
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