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ARCHIVED REPORTS_2013_1
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ARCHIVED REPORTS_2013_1
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Last modified
9/14/2020 3:50:49 AM
Creation date
7/3/2020 11:07:48 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2013_1
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_2013_1.tif
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EHD - Public
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6.0 ANNUAL SUMMARY <br /> 6.1 GENERAL <br /> During the 2012 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. R5-2007-0046. All of the monitoring <br /> points were sampled for the monitoring parameters summarized in Table 1. Time-series <br /> plots depicting groundwater and surface water constituent concentrations and a tabular <br /> summary of the historical monitoring data are presented in Appendix D and in an <br /> electronic format in Appendix C. Piper diagrams of the semiannual data obtained in <br /> 2012, hydrographs illustrating the historic groundwater elevations of the detection <br /> monitoring wells, and information relative to well screen elevations and pump intake <br /> elevations are included in Appendix D. Discussions of the historical trends in constituent <br /> concentrations are presented in Section 4. <br /> 6.2 GROUNDWATER <br /> Over the 2012 monitoring year, groundwater elevations varied by about one to two feet <br /> with a gradient between 0.001 to 0.004 ft/ft to the south to southeast. <br /> Groundwater quality conditions beneath the French Camp Landfill during the 2012 <br /> monitoring year are generally similar to those observed over the previous years. <br /> Excluding field parameters, CLs were exceeded for chloride at wells MW-9A and <br /> MW-10A; for TDS at well MW-10A; and for TCFM at well MW-9A during both <br /> semiannual monitoring events in 2012. Additionally,the CL for chloroform was <br /> exceeded in well MW-6A during the first semiannual 2012 monitoring period. <br /> Statistically significant increasing trends were consistently noted for potassium and <br /> sulfate at well MW-9B and for chloride at well MW-10A,while decreasing trends were <br /> consistently noted for chloride, specific conductance, and TDS at well MW-7A; for <br /> bicarbonate, chloride, nitrate, and TDS at well MW-8A; for nitrate and TCFM at well <br /> MW-9A; and for nitrate at well MW-10A. <br /> With the exception of the consistent detection of TCFM at well MW-9A and the <br /> detection of chloroform during the first semiannual monitoring period at well MW-6A, <br /> no VOCs were detected in groundwater samples collected during the 2012 monitoring <br /> year. <br /> 6.3 SURFACE WATER <br /> Surface water elevations at the stream gauging stations varied by approximately two feet <br /> during the 2012 monitoring year. These changes reflect seasonal precipitation patterns. <br /> Surface water generally flows west toward the San Francisco Bay. <br /> c:\zoia-027\Fczsntz.aoc 6Geo-Logic Associates <br />
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