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ARCHIVED REPORTS_2015_3
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ARCHIVED REPORTS_2015_3
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Entry Properties
Last modified
7/18/2020 2:34:19 PM
Creation date
7/3/2020 10:59:17 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2015_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_2015_3.tif
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EHD - Public
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Water Quality Monitoring Report <br /> Forward Landfill <br /> the Forward Unit flows to the southeast at a hydraulic gradient of 0.003 to 0.005 ft/ft; <br /> is while groundwater beneath the northwestern portion of the Forward Unit flows to the <br /> northeast at a hydraulic gradient of 0.001 ft/ft. <br /> To calculate the approximate linear groundwater flow velocity for the Forward Unit, <br /> conservative assumptions were used, including a hydraulic conductivity of 875 gallons <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 0.005 sec— ft <br /> V = —_ [(0.04—)* ]*2835 1.62 ft/day <br /> ne see 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;--0.005 at the site during the first quarter 2015. <br /> ne= Effective porosity (ne= 0.35); an estimated value. <br /> The maximum groundwater flow rate is calculated to be 1.62 feet per day (591 <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 2015 monitoring period are summarized in Table 2-2. <br /> 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, a <br /> measurably significant indication of release occurs in a given sample when: two or more <br /> VOCs exceed their respective Method Detection Limits (MDLs); or one or more VOCs <br /> equals or exceeds its respective practical quantitation limit (PQL). During the first <br /> quarter 2015 monitoring period, non-statistical indications of a release were identified <br /> at well MW-13 as a result of a quantifiable concentration of diisopropyl ether (DIPS) <br /> (0.58 Vg/L), and at well MW-14 as a result of trace-level concentrations of <br /> dichlorodifluoromethane (DCDFM) (0.17j µg/L), tetrachloroethene (PCE) (0.16j Itg/L), <br /> and trichlorofluoromethane (TCFM) (0.17j pg/L). In a letter dated April 1, 2015, the <br /> RWQCB was notified of these exceedances and retesting is scheduled for April 2015. <br /> The results of the verification sampling will be reported under separate cover. On <br /> behalf of Forward Inc., GLA performed an assessment of the source and potential <br /> impacts of low-level VOCs in groundwater adjacent to the Forward Landfill. It was <br /> concluded that the sporadic detection of low-level VOCs in groundwater (and lysimeter <br /> M:\2015.0014\FA 1Q15.docx 6 <br /> 4/27/2015,Rev.0 <br />
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