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ARCHIVED REPORTS_2014_2
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ARCHIVED REPORTS_2014_2
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Last modified
7/18/2020 7:46:17 AM
Creation date
7/3/2020 11:07:52 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2014_2
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_2.tif
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EHD - Public
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Water quality Monitoring Report <br /> French Camp Landfill <br /> In order to evaluate changes in water quality in DMP wells at the French Camp Landfill, <br /> Sen's Slope trend analyses were performed for those constituents exceeding a CL. <br /> During the monitoring period, no statistically significant increasing temporal trends <br /> were calculated for constituents exceeding a CL and current concentrations measured in <br /> these wells are generally within the historical range of values for these wells. Trend <br /> analyses are presented in Appendix D. <br /> 4.5 Leachate Monitoring <br /> The laboratory results for leachate monitoring well MW-2 are summarized in Table 3. <br /> As shown on Table 3, no VOCs were detected in leachate monitoring well MW-2 during <br /> the monitoring period. <br /> 4.6 Surface Water Monitoring <br /> Field and laboratory results for surface water monitoring stations(SW-1,SW-2, and <br /> SW-3) for the current monitoring period are summarized in Table 4 and time-series <br /> concentration plots are presented in Appendix D. Stations SW-1 and SW-2 are located <br /> upstream of the landfill within the Walker and French Camp Sloughs (respectively) and <br /> are used as background sampling points. Station SW-3 is located downstream of the <br /> landfill at the confluence of the two sloughs. A comparison of upgradient (SW-1 and <br /> SW-2) to downgradient (SW-3) surface water samples indicates generally similar <br /> inorganic constituent concentrations. Trace concentrations of chloroform were <br /> measured in upstream samples and low, quantifiable concentrations of <br /> bromodichloromethane and chloroform and a trace concentration of <br /> dibromochloromethane were measured in the downstream sample. These particular <br /> VOCs are drinking water disinfection byproducts (trihalomethanes) that likely originate <br /> from a source other than the landfill. No other VOCs were detected in the surface water <br /> monitoring stations. In a letter dated June 23, 2014, the RWQCB was notified of the <br /> non-statistical exceedance in SW-3 and confirmation samples were collected in June <br /> 2014. <br /> Stream gauging was performed on February 24 and May 5, 2014, at monitoring points <br /> SG-1 and SG-2 and the data is summarized in Table S. As shown in Figures 1 and 2, <br /> monitoring point SG-1 is located upgradient in the Walker Slough and monitoring point <br /> SG-2 is located upgradient,in the French Camp Slough. <br /> 5.0 SOIL-PORE GAS MONITORING <br /> In accordance with WDR Order No. 115-2007-0046, soil-pore gas probes are monitored <br /> semiannually using a field screening protocol, and soil-pore gas samples are only <br /> collected if field screening indicates methane concentrations greater than 2.5 percent. <br /> During the monitoring period, field screening of soil-pore gas probes was conducted on <br /> M:\2014.0012\FC i5A14.doc 5 <br /> 7/10/2014,Rev.0 <br />
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