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ARCHIVED REPORTS_2017
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ARCHIVED REPORTS_2017
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Last modified
7/18/2020 12:55:52 PM
Creation date
7/3/2020 11:08:04 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2017
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
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4434_PR0440006_0 MANTHEY_2017.tif
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EHD - Public
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Water Quality Monitoring Report <br /> French Camp Landfill <br /> two sloughs. A comparison of upgradient (SW-1 and SW-2) to downgradient (SW-3) surface <br /> water samples indicates generally similar inorganic constituent concentrations. No VOCs were <br /> detected in surface water samples during the monitoring period. <br /> Stream gauging was performed on August 3 and November 25, 2016, at monitoring points SG-1 <br /> and SG-2 and the data are summarized in Table 5. As shown in Figures 1 and 2, monitoring <br /> point SG-1 is located upgradient in the Walker Slough and monitoring point SG-2 is located <br /> upgradient in the French Camp Slough. <br /> 5.0 SOIL-PORE GAS MONITORING <br /> In accordance with WDR Order No. R5-2007-0046; perimeter soil-pore gas probes are <br /> monitored using a field screening protocol, and soil-pore gas samples are only collected if field <br /> screening indicates methane concentrations greater than 2.5 percent. During the monitoring <br /> period, field screening of soil-pore gas probes was conducted on September 30 and December <br /> 28, 2016. As shown on Table 6, methane was only detected in two of the soil-pore gas probes <br /> (SGP-2A and SGP-7A) at concentrations of 0.1 percent by volume during the third quarter 2016. <br /> As a result, no samples were collected. <br /> 6.0 ANNUAL SUMMARY <br /> .1 General <br /> During the 2016 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 2016, 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 2016 monitoring year, groundwater elevations varied by about one to four feet with <br /> hydraulic gradients ranging between 0.001 ft/ft to 0.002 ft/ft to the east-southeast. <br /> Groundwater quality conditions beneath the French Camp Landfill during the 2016 monitoring <br /> year are generally similar to those observed in previous years. During one or both semiannual <br /> monitoring periods in 2016, inorganic CLs were exceeded for chloride in the samples from wells <br /> MW-913 and MW-10A. However, trend analyses for these chloride concentrations do not <br /> exhibited statistically significant increasing trends. 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 /> Project No.2016.0007 5 <br />
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