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ARCHIVED REPORTS_2013_4
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ARCHIVED REPORTS_2013_4
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Last modified
9/14/2020 7:00:40 AM
Creation date
7/3/2020 11:05:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2013_4
RECORD_ID
PR0440003
PE
4434
FACILITY_ID
FA0003698
FACILITY_NAME
CORRAL HOLLOW LANDFILL
STREET_NUMBER
31130
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25303010
CURRENT_STATUS
01
SITE_LOCATION
31130 CORRAL HOLLOW RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4434_PR0440003_31130 CORRAL HOLLOW_2013_4.tif
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EHD - Public
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® A linear extrapolation of the 1 ug/L contour interval lines between a PCE concentration of <br /> 5.3 ug/L at MW-5 and a PCE concentration of 0.44 ug/L at MW-l0A <br /> The overall shape of the PCE plume is relatively symmetrical from an apparent source located <br /> near the northern boundary of the landfill, an area that includes both County and Caltrans refuse. <br /> The source location appears to be centered between well MW-5, LFG probe GW-1, and well MW- <br /> 8. The apparent western edge of VOC impacted groundwater adjacent to the landfill is the <br /> western edge of the Corcoran Clay Formation, (Figures 2 and 5). The apparent eastern edge of <br /> VOC impacted groundwater adjacent to the landfill is well SB-1, which is an apparent <br /> groundwater high elevation point in the shallow aquifer(Figure 2). The plume of impacted <br /> groundwater is elongated in the direction of groundwater flow, which is generally to the north- <br /> northeast from the landfill. <br /> After the first four monitoring events and on climatic cycle there does not appear to be any trends <br /> in the VOC data. <br /> Whether the plume is increasing or decreasing cannot be determined at this time from the limited <br /> data available. However, concentration of VOCs at the two impacted wells on site have been <br /> relatively stable since the installation of the LFG collection system in 2001, allowing the <br /> presumption that the plume has remained constant during that time. Data from the off-site wells <br /> (MW-9A, MW-l0A and MW-11A) will indicate if the extent of the plume is changing with time. <br /> Deep Aquifer <br /> AI'W- own gradient): <br /> Concentrations of all parameters were within established concentration limits where the limits <br /> could be determined with the exception of chloride, nitrate as nitrogen, sulfate, TDS, and <br /> Magnesium(Table 2). However,this is an unusual occurrence for this well, <br /> However, the changes in concentration are very small. Report of a"trend"by Sanitas software is <br /> an artifact of the software. <br /> No VOCs were reported at this well this quarter. Other than false positives,no VOCs have been <br /> reported since Toluene was reported in 2005 when the well was first installed. These Toluene data <br /> indicate that this compound was probably introduced by the drilling company when this well was <br /> installed in 2003, but quickly reduced to "trace" in three quarters. Excluding probable <br /> contamination during well construction and compounds also found the QC blanks, no VOC has <br /> been reported in this well. Therefore, there has been no indication of impact from the landfill at <br /> this well. <br /> MW-7(Upgradie nt): <br /> Concentrations of all parameters were within established concentration limits where the limits <br /> could be determined (Table 2). <br /> Corral Hollow Sanitary Landfill 15 Department of Public Works/Solid Waste <br /> Is'Quarter 2013 Groundwater Monitoring County of San Joaquin—April 15,2013 <br />
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