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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
Supplemental fields
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 /> fe (CDM, 1997) and an estimated effective porosity of 35 percent. An estimated groundwater <br /> flow velocity was calculated using Darcy's Law: <br /> V = Ki = (255 ft )* 0.003 ;,, 2.19 ft/day <br /> ne day 0.35 <br /> where: V=Groundwater flow velocity. <br /> K=Hydraulic conductivity of the water-bearing unit(255 ft/day). <br /> i=Average hydraulic gradient:i;:t�0.003 during the first quarter 2017. <br /> ne=Effective porosity(ne=0.35);an estimated value. <br /> The maximum groundwater flow rate is calculated to be 2.19 feet per day(798 feet/year). <br /> 2.1.4 Detection Monitoring Program <br /> Field and laboratory results for the Forward Unit groundwater monitoring wells for the first <br /> quarter 2017 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 VOCs <br /> exceed their respective Method Detection Limits (MDLs); or one or more VOCs equals or <br /> exceeds its respective practical quantitation limit (PQL). During the first quarter 2017 <br /> monitoring period, non-statistical indications of a release was identified at well MW-2A as a <br /> result of trace concentration of 1,1-dichloroethene (1,1-DCA) and a quantifiable concentration <br /> of cis-1,2-dichloroethene (cis-1,2-DCE); MW-13 as a result of a quantifiable concentration of <br /> diisopropyl ether (DIPS); MW-14 as a result of a quantifiable concentration of <br /> dichlorodifluoromethane (DCDFM); MW-16 as a result of a quantifiable concentration of DIPS; <br /> and at well MW-17 as a result of quantifiable concentrations of chloroform and carbon <br /> tetrachloride. Constituents exceeding a CNSDAM were place in "tracking mode" and are being <br /> evaluated quarterly for temporal trends (discussed below). <br /> Historically, low-level concentrations of VOCs have been detected in the samples collected from the <br /> Forward Unit. 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 in <br /> groundwater adjacent to the Forward Landfill. The letter report concluded that the sporadic <br /> detection of low-level VOCs in groundwater (and lysimeter samples) at the Forward Unit are most <br /> likely due to landfill gas from unlined unit WMU-B. Forward has continued to minimize gas related <br /> impacts to groundwater by preventing ponding of water through regular site maintenance. <br /> Project No.5017.1030 I Water Quality Monitoring Report 6 <br /> April 2017 <br />
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