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ARCHIVED REPORTS_2017_1
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ARCHIVED REPORTS_2017_1
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Last modified
7/18/2020 4:15:11 PM
Creation date
7/3/2020 10:59:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2017_1
RECORD_ID
PR0440005
PE
4433
FACILITY_ID
FA0004516
FACILITY_NAME
FORWARD DISPOSAL SITE
STREET_NUMBER
9999
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
20106001-3, 5
CURRENT_STATUS
01
SITE_LOCATION
9999 AUSTIN RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2017_1.tif
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EHD - Public
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Water Quality Monitoring Report <br /> Forward Landfill <br /> calculated for CWLAM constituents (total nitrogen, arsenic, iron, and manganese). As shown on 3- <br /> 4, WQPS were exceeded for iron in well AMW-10. In a letter dated April 17, 2017, the RWQCB <br /> was notified of the CWLAM CL exceedances and retesting is scheduled for April 2017. <br /> 3.1.7 Domestic Well Monitoring <br /> Two domestic wells (8106-A and 7898-A) were sampled on March 10, 2017. Table 3-5 <br /> summarizes the current analytical results for the domestic well samples collected. <br /> Tetrachloroethene was measured above the PQL in both domestic well samples and DCDFM <br /> and TCE were also measured above their PQLs in the sample collected from well 8106-A. <br /> Estimated trace concentrations of two VOC (each) were also measured in the domestic well <br /> samples. <br /> 3.1.8 Vadose Zone Monitoring <br /> The current vadose-zone monitoring network at the Austin Unit consists of seven lysimeters. <br /> The lysimeter locations are shown on Figure 3-1. As shown on Table 2-6, with the exception of <br /> FU-05, all of the lysimeters were reported dry or had insufficient soil-pore liquid (10 milliliters) <br /> for analysis. As shown in Table 2-613, a quantifiable concentrations of 1,2-dichloroethane, <br /> acetone, methyl ethyl ketone, and tert-butyl alcohol were measured in the soil-pore liquid <br /> collected from lysimeter FU-05. <br /> 3.1.9 Leachate Surface Impoundment Monitoring <br /> For the Austin Unit, leachate sumps and surface impoundments are inspected weekly by <br /> Forward Landfill personnel. If leachate is detected in a sump, it is pumped into the surface <br /> impoundment WMU F (West) for evaporation. During the first quarter 2017, leachate was <br /> observed at holding areas WMU FU-03, WMU FU-04, WMU FU-05, WMU FU-06, WMU FU-13, <br /> and WMU FU-14 and a total of 441,257 gallons of leachate was removed from the lined areas at <br /> an average rate of 4,849 gallons per day. For surface impoundment WMU-F (West) Freeboard <br /> ranged from approximately 6.33 to 7.33 feet during the first quarter 2017 monitoring period. <br /> Appendix A presents copies of the leachate observation logs, freeboard observation logs, and <br /> surface impoundment monitoring log. <br /> Leachate samples were collected on a quarterly basis and analyzed in the field for pH, specific <br /> conductance, temperature, and turbidity. The results of quarterly field monitoring <br /> measurements and analytical results for the first quarter 2017 are presented in Table 3-8. <br /> 3.1.10 Surface Water Monitoring <br /> Site run-on and run-off control facilities are designed to effectively channel surface water to <br /> site stormwater/sedimentation ponds. According to the Operations Manager, stormwater was <br /> ® discharged to surface water (North Little Johns Creek) during heavy rain events in January 2017. <br /> Project No.S017.1030 I Water Quality Monitoring Report 12 <br /> April 2017 <br />
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