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ARCHIVED REPORTS_2016_1
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ARCHIVED REPORTS_2016_1
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Last modified
7/18/2020 7:46:14 AM
Creation date
7/3/2020 10:59:21 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2016_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
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SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2016_1.tif
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EHD - Public
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Water Quality Monitoring Report <br />Forward Landfill <br />per day per square foot (0.04 cm/sec) and an estimated effective porosity of 35 percent <br />(CH2M Hill, 2000). An estimated groundwater flow velocity was calculated using Darcy's <br />Law: <br />Ki cm 0.002 sec — ft <br />V = — _ [( 0.04 ) * ] * 2835 = 0.65 ft l da_y <br />ne sec 0.35 cm — day <br />where: V = Groundwater flow velocity. <br />K = Hydraulic conductivity of the water -bearing unit (0.04 cm/sec). <br />i = Hydraulic gradient: i = 0.002 at the site during the first quarter 2016. <br />ne= Effective porosity (ne = 0.35); an estimated value. <br />The maximum groundwater flow rate is calculated to be 0.65 feet per day (237 <br />feet/year). <br />2.1.4 Detection Monitoring Program <br />Field and laboratory results for the Forward Unit groundwater monitoring wells for the <br />first quarter 2016 monitoring period are summarized in Table 2-2. <br />0 Non -Statistical Data Analysis <br />The California Non -Statistical Data Analysis Method (CNSDAM) was performed for VOCs <br />detected less than 10 percent of the time in background samples. Under the CNSDAM, <br />a measurably significant indication of release occurs in a given sample when: two or <br />more VOCs exceed their respective Method Detection Limits (MDLs); or one or more <br />VOCs equals or exceeds its respective practical quantitation limit (PQL). During the first <br />quarter 2016 monitoring period, non -statistical indications of a release were identified <br />at wells MW -13 and MW -16 as a result of a quantifiable concentrations of diisopropyl <br />ether (DIPE); at well MW -14 for trace -level concentrations of dichlorodifluoromethane <br />(DCDFM), tetrachloroethene (PCE), and trichlorofluoromethane (TDFM); and at well <br />MW -17 for trace -level concentrations of carbon tetrachloride, chloroform, and TCFM. <br />In a letter dated August 13, 2015, similar concentrations of VOCs in wells MW -16 and <br />MW -17 were reported to the RWQCB for the second quarter 2015 and confirmed in <br />retest samples collected on July 29, 2015. It should be noted that these confirmed VOCs <br />are well below state and/or federal maximum contaminant levels (MCLS), and were <br />place in "tracking mode" and are being evaluated quarterly for temporal trends. For <br />wells MW -13 and MW -14, the RWQCB was notified of these exceedances in a letter <br />dated April 18, 2016 and retesting is scheduled for April 2016. The results of the <br />verification sampling will be reported under separate cover. <br />M:\ 2016.0007\FA 1Q16.docx 6 <br />Historically, low-level concentrations <br />of <br />VOCs <br />have been <br />detected in <br />the sampled <br />iscollected <br />from the Forward Unit. <br />On <br />behalf <br />of Forward <br />Inc., GLA <br />performed an <br />M:\ 2016.0007\FA 1Q16.docx 6 <br />
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