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ARCHIVED REPORTS_2017_3
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ARCHIVED REPORTS_2017_3
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Last modified
7/18/2020 10:03:16 AM
Creation date
7/3/2020 10:59:36 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2017_3
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_3.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 manganese in well AMW-10, and iron and manganese in wells <br />AMW-13 during the fourth quarter 2016 monitoring period. In a letter dated January 23, 2017, <br />the RWQCB was notified of the CWLARA CL exceedances and retesting is scheduled for January <br />2017. <br />3.1.7 Domestic Well Monitoring <br />Two domestic wells (8106-A and 7898-A) were sampled on October 26 and 27, 2016, <br />respectively. Table 3-5 summarizes the current analytical results for the domestic well samples <br />collected. Tetrachloroethene was measured above the PQL in both domestic well samples and <br />cis-1,2-DCE, DCDFM and TCE were also measured above their PQLs in the sample collected from <br />well 8106-A. Estimated trace concentrations of one VOC (each) were also measured in the <br />domestic well 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 2-5, with the exception of <br />FU -04W, all of the lysimeters were reported dry. However, there was insufficient soil -pore <br />liquid (4 milliliters) for analysis. <br />0 <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 fourth quarter 2016, 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 358,200 gallons of leachate was removed from the lined areas at <br />an average rate of 3,936 gallons per day. For surface impoundment WMU-F (West) Freeboard <br />ranged from approximately 7.33 to 7.67 feet during the fourth quarter 2016 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. In addition to quarterly monitoring, leachate is <br />sampled annually during the fourth quarter monitoring period for the parameters listed in <br />Table 2-1. The results of quarterly field monitoring measurements and analytical results for the <br />fourth quarter 2016 are presented in Table 3-7. As shown on Table 3-7, six VOCs were detected <br />in the Austin Unit leachate sample. <br />Project No. 2016.0007 1 Water Quality Monitoring Report 13 <br />January 2017 <br />
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