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ARCHIVED REPORTS_2014
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ARCHIVED REPORTS_2014
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Last modified
9/14/2020 4:46:46 AM
Creation date
7/3/2020 11:07:50 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2014
RECORD_ID
PR0440006
PE
4434
FACILITY_ID
FA0004515
FACILITY_NAME
FRENCH CAMP LANDFILL
STREET_NUMBER
0
STREET_NAME
MANTHEY
STREET_TYPE
RD
City
STOCKTON
Zip
95231
APN
16307035
CURRENT_STATUS
02
SITE_LOCATION
MANTHEY RD
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4434_PR0440006_0 MANTHEY_2014.tif
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EHD - Public
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Water Quality Monitoring Report <br /> French Camp Landfill <br /> 6.0 ANNUAL SUMMARY <br /> 6.1 General <br /> During the 2014 monitoring year, groundwater elevation measurements were performed <br /> quarterly and water quality sampling and soil-pore gas monitoring were performed <br /> semiannually in accordance with WDR Order No. 115-2007-0046. All of the monitoring points <br /> were sampled for the monitoring parameters summarized in Table 1. A tabular summary of the <br /> historical monitoring data is presented in Appendix C and time-series plots depicting <br /> groundwater and surface water constituent concentrations are presented in Appendix D. Stiff <br /> diagrams of the semiannual data obtained in 2014, hydrographs illustrating the historical <br /> groundwater elevations of the detection monitoring wells, and information relative to well <br /> screen elevations and pump intake elevations are also included in Appendix D. <br /> 6.2 Groundwater <br /> Over the 2014 monitoring year, groundwater elevations varied by about one to two feet with <br /> hydraulic gradients ranging between 0.001 ft/ft to 0.004 ft/ft to the east and southeast. <br /> Groundwater quality conditions beneath the French Camp Landfill during the 2014 monitoring <br /> year are generally similar to those observed in previous years. During one or both semiannual <br /> monitoring periods in 2014, inorganic CLs were exceeded for chloride in the samples from wells <br /> MW-913 and MW-10A; for pH value at wells MW-9A and MW-10A; and for specific conductance <br /> and TDS in the sample from well MW-10A. However, none of the constituents that exceeded a <br /> CL exhibited a statistically significant increasing trend. In January 2005 a No Release <br /> Demonstration (NRD) for groundwater monitoring well MW-10A was performed (Herst, 2005) <br /> in response to CL exceedances of chloride and TDS. The NRD concluded that French Camp <br /> Landfill, located within the central Stockton area, has been impacted by saltwater intrusion and <br /> the elevated chloride and TDS concentrations measured in well MW-10A are believed to be the <br /> result of this condition and not the result of landfill-related impacts. <br /> With the exception of TCFM at well WM-9A and chloroform at well MW-6A, no VOCs were <br /> measured at quantifiable concentrations in groundwater samples during the 2014 monitoring <br /> year. Roth TCFM and chloroform have been previously confirmed in retest samples, however, <br /> neither of these VOCs exhibited an increasing trend. Given the distance of well MW-6A from <br /> the landfill, the chloroform concentrations measured in well MW-6A are not believed to be the <br /> result of a release from the landfill. The TCFM concentrations measured in well MW-9A are <br /> well below risk-based concentrations and have been attributed to LFG. <br /> 6.3 Surface Water <br /> Surface water elevations at stream gauging locations varied by about one to two feet during the <br /> 2014 monitoring year. These changes reflect tidal and seasonal precipitation patterns. Surface <br /> water generally flows west toward the San Francisco Bay. <br /> Project No.2014.0012 FC 2SA14 Report.docx 6 <br /> 1/20/2015, Rev.0 <br />
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