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ARCHIVED REPORTS_XR0002477
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0540859
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ARCHIVED REPORTS_XR0002477
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Last modified
1/15/2020 3:44:08 PM
Creation date
1/15/2020 3:01:28 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002477
RECORD_ID
PR0540859
PE
2960
FACILITY_ID
FA0023361
FACILITY_NAME
PLAY N PARK (FORMER BARNES TRUCKING)
STREET_NUMBER
1817
Direction
S
STREET_NAME
FRESNO
STREET_TYPE
AVE
City
STOCKTON
Zip
95206
CURRENT_STATUS
01
SITE_LOCATION
1817 S FRESNO AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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CLEARWATER <br /> G R O U P <br /> Environmental Services <br /> temperature, conductivity, and pH were made and recorded on Monitoring Well Data Sheets for <br /> each well Well stabilization data are included in Appendix A <br /> Following purging, each well was allowed to recharge to at least 80% of its static water level <br /> prior to sampling Groundwater samples were obtained from each well using disposable <br /> polyethylene bailers and decanted into clean laboratory supplied bottles Samples were labeled, <br /> documented on a chain-of-custody form, and placed on ice in a cooler for transport to the project <br /> laboratory Groundwater samples were analyzed by Kiff Analytical Labs, located in Davis <br /> California, a California State-certified laboratory, for concentrations of TPHg, BTEX and MTBE <br /> by EPA Method 8260B Groundwater samples collected for MNA data were delivered to <br /> CytoCulture Environmental Biotechnology Laboratories (CytoCulture) in Richmond, California <br /> All field work was conducted in accordance with Clearwater's Groundwater Monitoring and <br /> Sampling Field Procedures and Natural Attenuation Processes and Recommended Monitoring <br /> Guidelines included in this report as Appendix B <br /> GROUNDWATER MONITORING AND SAMPLING RESULTS <br /> Groundwater sampling results for gasoline range hydrocarbons are summarized as follows <br /> Depth to groundwater range 8 88 (MW-2) to 1104 (MW-8) feet below <br /> • to -of-casin TQC <br /> Flow direction and gradient Southeast at approximately 0 004 feet/foot <br /> Benzene concentration range From not detectable (MW-2, MW-3, MW- <br /> 4) to 2,400 micrograms per liter (Rg/L) in <br /> MW-5B <br /> Toluene concentration range From<0 50 Rg/L (MW-2, -3, -4, -7, & MW- <br /> 8)to 630 tig/L MW-5B <br /> Ethylbenzene concentration range From <0 50 Rg/L (MW-2, -3, -4, -7, &MW- <br /> 8)to 550 -5B <br /> Xylenes concentration range From <0 50 Rg/L (MW-2, -3, -4, & MW-8) <br /> to 1,300 MW-5B <br /> TPH-g concentration range From <50 Rg/L (MW-2, -3, and MW-4) to <br /> 16,000 -5B <br /> MTBE concentration range Not detected in concentrations exceeding <br /> indicated laboratory method reporting limits <br /> (<0 50 R to<10 g/L <br /> The groundwater flow direction and gradient as determined by this sampling event is <br /> substantially the same as was determined by previous monitoring events Groundwater elevation <br /> and analytical data are included in Table 1 A groundwater elevation map based on the <br /> groundwater elevation data from all monitoring wells was prepared and is presented as Figure 3 <br /> A revised dissolved-phase hydrocarbon distnbution map including iso-concentration contours of <br /> benzene in groundwater is presented as Figure 4 Analytical reports for this groundwater <br /> monitoring event are included as Appendix C <br /> ZB178C/2Q03 Monitoring Rpt 4 September 15,2003 <br />
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