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ARCHIVED REPORTS_2011_17
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ARCHIVED REPORTS_2011_17
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Last modified
7/17/2020 3:53:37 PM
Creation date
7/3/2020 10:56:05 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2011_17
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
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2011_17.tif
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EHD - Public
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The groundwater elevation data obtained during the second quarter 2011 monitoring <br /> period were used to generate the groundwater elevation contour map shown on Figure <br /> 2-1, which indicates that groundwater generally flows to the north-northeast towards the <br /> Austin Unit, at an average hydraulic gradient of approximately 0.002 ft/ft. However, a <br /> south-southwest gradient of 0.009 ft/ft was calculated in the northwest comer of the <br /> Forward Unit. <br /> To calculate the approximate linear groundwater flow velocity for the site, conservative <br /> assumptions were used, including a hydraulic conductivity of 875 gallons per day per <br /> square foot(0.04 cm/sec) and an estimated effective porosity of 35 percent (CH2M Hill <br /> 2000). An estimated groundwater flow velocity was calculated using Darcy's Law: <br /> Ki cell 0.002 Sec - li <br /> - = 1(0,04 ----)* - 2835 0.648 ft , daY <br /> lie sec 0.35 cin - 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 for the site during the second quarter 2011. <br /> n,=Effective porosity(n,=0.35);an estimated value. <br /> The groundwater flow rate is calculated to be 0.648 feet/day (237 feet/year). <br /> 2.1.4 Detection Monitoring Program <br /> Field and laboratory results for the groundwater monitoring wells for the second quarter <br /> 2011 are summarized in Table 2-2. The organic results for the Forward Unit indicate that <br /> the following VOCs were measured at estimated trace concentrations (between the <br /> method detection limit [MDL] and the PQL), dichlorodifluoromethane (DDFM) and <br /> Trichlorofluoromethane (TCFM) in the sample collected from well MW-10; and 1,1- <br /> dichloroethane (1,1-DCA), cis-1,2-dichloroethene (cis-1,2-DCE),tetrachloroethene <br /> (PCE),trichloroethene (TCE), and TCFM in the sample collected from well MW-14. In <br /> addition, diisopropyl ether(DIPE) was measured above the PQL in the sample collected <br /> from well MW-2A. <br /> On behalf of Forward Inc., GLA prepared a letter report dated February 14, 2001 <br /> (RWQCB Case No. 2209), to assess the source and potential impacts of low-level VOCs <br /> in groundwater adjacent to the Forward Landfill. The letter report concluded that the <br /> sporadic detection of low-level VOCs in groundwater(and lysimeter samples) at the <br /> Forward Unit are most likely due to landfill gas from unlined unit WMU-B. The <br /> particular VOCs detected in samples during the current monitoring period appear to <br /> support this conclusion. Forward has continued to minimize gas related impacts to <br /> groundwater by limiting interim fill areas that promote ponding of water. Furthermore, <br /> in accordance with CCR Title 27, Section 20937, Forward continues to install additional <br /> landfill gas extraction wells, as needed, and make adjustments to the LFG wells. <br /> W201 1_0050\FA_2Q I Ldocx <br /> 5 Geologic Associates <br />
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