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ARCHIVED REPORTS XR0006993
Environmental Health - Public
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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 XR0006993
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Last modified
7/10/2019 2:40:21 PM
Creation date
7/10/2019 11:49:00 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006993
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&Helen s Manna Third Quarter 1999 Groundwater Monitoring <br /> October 26 1999 <br /> Page-7- <br /> 4 THIRD QUARTER, 1999, SURFACE WATER MONITORING <br /> 4 1 FIELD METHODOLOGY <br />' On September 23, 1999, a Condor representative was on site to conduct quarterly surface water monitoring <br /> activities The monitoring activities included the collec.tlon of surface water samples from the drainage ditch and <br />' island drainage channel located east and south of the site, respectively (Figure 5, Appendix A) Four surface <br /> water samples were collected with a Teflon® dipping cup and transferred to two 40-milliliter glass vials fitted <br /> with Tcflon®-lined caps Surface water samples DDS (drainage ditch south) and DDN (drainage ditch north) <br /> I were collected approximately five feet and 100 feet north of EightMile Road, respectively Surface water <br /> samples IDCW (island drainage channel west) and IDCE (island drainage channel east) were collected from the <br /> western terminus of the island drainage channel and approximately 100 feet east of the confluence of the <br /> drainage ditch and the island drainage channel, respectively Each sample container was labeled and placed in a <br />' cooler chilled with ice and delivered under chain-of-custody procedures to GeoAnalytical Laboratories, Inc , in <br /> Modesto, California, within 24 hours of sample collection Results of the laboratory analyses are discussed in <br />' Section 4 3 <br /> 4 2 LABORATORY ANALYTICAL METHODOLOGY <br />' The laboratory analytical methods for the surface water samples collected on September 23, 1999, are <br /> summarized in Table 4 <br />' TABLE 4 <br /> Laboratory Analytical Methods <br /> Analytes <br /> BTEX 1PH-G Gasolme <br /> Oxygenates/Additives <br /> Analytical Methods 602 503OfLUFT 8260 <br />' Detection Limits 0 3 g11L (BTL) 0 05 mg/L 1 0 �Lg <br /> 0 6 L (X) 10 0 ug/L(tert Butanol) <br />' <br /> BTI-X -benzene,toluene ethyl benzene and total xylenes <br /> TPH-G total petroleum hydrocarbons,quantified as gasoline <br /> Gasoline Oxygenates/Additives=methyl tertiary butyl ether(MT13h) ethanol,tertiary-butanol, <br /> di-isopropyl ether(DIPE) Lthyl tertiary-butyl ether(ETRE)and tertiary amyl methyl ether(TAME) <br /> 4 3 LABORATORY ANALYTICAL RESULTS <br /> TPH-G was not detected at or above the laboratory reported detection limits in any of the surface water samples <br /> BTEX constituents were not detected in any of the surface water samples, with the exception of DDN Toluene <br /> and total xylenes were detected in surface water sample DDN at concentrations of 0 6 and 0 9 gg/l, respectively <br /> MTBE was detected in surface water samples DDN and IDCW at concentrations of 1 7 and 1 6 jag/l, <br /> respectively MTBE was not detected at or above the laboratory reported detection limits in surface water <br /> samples DDS or ICDE None of the gasoline oxygenates other than MTBE were detected at or above the <br /> laboratory reported detection limits in any of the surface water samples A summary of the current and historical <br /> laboratory analytical results of the surface water samples is presented in Table 5 on the next page The current <br /> laboratory analytical results of the surface water samples are shown in Figure 5, Appendix A <br /> 1 <br />' � CONDOR <br />
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