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ARCHIVED REPORTS_2010_12
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ARCHIVED REPORTS_2010_12
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Last modified
7/17/2020 3:53:35 PM
Creation date
7/3/2020 10:55:17 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2010_12
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_2010_12.tif
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EHD - Public
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it is concluded that the laboratory data generated for the second quarter 2010 monitoring <br /> period are generally acceptable and the water quality samples collected from the Austin <br /> Unit appear to be representative of water quality at the site. <br /> 3.1.3 Groundwater Elevations and Contours <br /> Prior to purging and sampling, each well was sounded for water depth using a weighted <br /> electronic sounder, and the static water level was recorded on a well data sheet <br /> (Appendix C). The groundwater elevations were calculated for each well by subtracting <br /> the depth-to-water measurement from the top-of-casing reference elevation. The current <br /> groundwater elevation data for the Austin Unit are summarized in Table 3-4. <br /> The groundwater elevation data obtained during this quarterly monitoring period were <br /> used to generate the groundwater elevation contour map shown on Figure 3-1,which <br /> indicates that groundwater beneath the Austin Unit generally flows to the north at an <br /> average hydraulic gradient of approximately 0.002 ft/ft. <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 cm 0.002 sec– ft <br /> V = — _ [(0.04 —)* ]*2835 0.65 ft l day <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 for the site during the current the second quarter 2010. <br /> ne=Effective porosity(ne=0.35);an estimated value. <br /> The groundwater flow rate is calculated to be 0.65 feet/day (237 feet/year). <br /> 3.1.4 Detection Monitoring Program <br /> Field and laboratory results for the DMP wells for the second quarter 2010 are <br /> summarized in Table 3-1 and time-series plots are presented in Appendix D. As shown <br /> in Table 3-1, a trace concentration of DCDFM was measured in the sample collected <br /> from well AMW-6; PCE was measure at a trace concentration in the sample collected <br /> from well AMW-12;trace concentrations of 1,1-DCA, DCDFM, and TCFM were <br /> measured in the sample collected from well AMW-13; and trace concentrations of 1,2- <br /> dichloropropane (1,2-DCP), DCDFM, and TCE were measured in the sample collected <br /> from well AMW-14. In addition,PCE was measured above the PQL, in the samples <br /> collected from wells AMW-6 and AMW-14; and PCE and TCE were measured above the <br /> PQL in the sample collected from well AMW-13. <br /> DA2010_0013\1FA 2Q10.doc <br /> 9 GeoLogic Associates <br />
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