My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_2014_8
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
A
>
AUSTIN
>
9999
>
4400 - Solid Waste Program
>
PR0440005
>
Archived Reports
>
ARCHIVED REPORTS_2014_8
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
7/18/2020 12:38:44 PM
Creation date
7/3/2020 10:58:20 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2014_8
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_2014_8.tif
Tags
EHD - Public
Jump to thumbnail
< previous set
next set >
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
595
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
0 3.2.1 MULTIMED Simulations <br />The U.S. Environmental Protection Agency's Multimedia Exposure Assessment Model <br />(MULTIMED) was employed to evaluate potential impacts to groundwater associated <br />with leachate migration through the 17 -foot -thick vadose zone beneath the site. As <br />described by Sharp -Hansen et al. (1990) and Salhotra et al. (1990), MULTIMED <br />simulates the movement of liquids in both the unsaturated (vadose) and saturated <br />(groundwater) zones. A steady-state, one-dimensional, semi -analytical module simulates <br />flow in the unsaturated zone. The output from this module (water saturation as a function <br />of depth) is used as input to the unsaturated zone transport module. The latter simulates <br />transient, one-dimensional (vertical) transport in the unsaturated zone and includes the <br />effects of longitudinal dispersion, linear adsorption, and first -order decay. For the <br />Forward Landfill analyses, the decay coefficients were conservatively ignored (i.e., set to <br />0.0). The unsaturated zone transport module calculates contaminant concentrations at the <br />base of the vadose zone as a function of time. <br />Output from both unsaturated zone modules is coupled with the saturated zone transport <br />module to estimate contaminant concentrations in groundwater as a function of time at a <br />specified distance downgradient from the edge of the landfill. The saturated zone <br />transport module includes one-dimensional uniform flow, three-dimensional dispersion, <br />linear adsorption, and first -order decay. Again, for the saturated zone simulations, the <br />decay coefficients were conservatively set to 0.0. <br />0 Model Input <br />v <br />As indicated on Table 1 in Attachment A, the MULTIMED analyses assumed that <br />leachate leakage would occur at a rate of approximately 0.0 17 cubic feet per day per acre <br />for the approximately 127 acres where the new single composite liner would be installed. <br />This leakage rate is based on the geomembrane defects anticipated in the HELP3 model <br />and conservatively assumes that 1 -foot of leachate will be applied on a prescriptive liner <br />whose minimum hydraulic conductivity is 1 x 10"7 cm/sec. The MULTIMED <br />simulations also conservatively assumed that the 1 -foot of leachate head would be <br />applied for 200 years. <br />The MULTIMED simulations assumed that the hydraulic conductivity of the 17 -foot <br />thick clayey vadose zone soils would be about 1 x 10"5 cm/sec. Conservative <br />assumptions were also integrated with respect to soil properties such as suction, porosity, <br />and density. The potential for biological degradation within the vadose zone was <br />conservatively ignored, and conservative estimates of potential dispersivity were <br />integrated. <br />The groundwater properties integrated in the model are consistent with those identified by <br />HA/AEE (2001) which indicate that the hydraulic conductivity of aquifer materials in the <br />area is relatively high (250 ft/d). Using the hydraulic conductivity value selected by <br />HA/AEE (250 R/d), an average groundwater gradient of 0.003 percent, and an estimated <br />effective porosity of 0.25, the calculated average linear groundwater velocity at the site is: <br />CA2002-002\Revised Appx A - Leakageldoc\09/19/02 <br />Geologic Associates <br />
The URL can be used to link to this page
Your browser does not support the video tag.