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ARCHIVED REPORTS_XR0004337
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2900 - Site Mitigation Program
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PR0506313
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ARCHIVED REPORTS_XR0004337
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Last modified
3/9/2020 8:21:28 PM
Creation date
3/9/2020 9:01:14 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004337
RECORD_ID
PR0506313
PE
2950
FACILITY_ID
FA0000514
FACILITY_NAME
MAIN STREET SHELL*
STREET_NUMBER
1071
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95336
APN
21707011
CURRENT_STATUS
02
SITE_LOCATION
1071 N MAIN ST
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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O <br /> Hydrogeology. Currently groundwater occurs at approximately 25 5 fbg beneath the site <br /> Measured depths to groundwater in the site wells have ranged historically from 15.1 to 29 5 fbg, <br /> and groundwater elevations have ranged historically from 7 2 to 20 3 feet above nisl Shallow <br /> groundwater flow beneath the subject site is variable but generally is toward the southwest at a <br /> gradient ranging from 0 001 to 0 003 <br /> A general description of the VLEACH model, model setup, and the fate and transport modeling <br /> results are presented below <br /> VLEACH Model Description <br /> VLEACH is a one dunensionat finite difference model used to assess potential groundwater <br /> impacts and volatilization of volatile organic constituents (VOCs) from unsaturated soils The <br /> model assumes a one-layer homogeneous profile and a constant recharge rate at the surface In <br /> the subsurface, the model assumes constant flow and transport of VOCs through soil by the n <br /> following transport mechanisms -sorption, volatilization,-diffusion to the atmosphere, and VOC <br /> leaching to groundwater The model does not take into account VOC degradation and <br /> dispersion, which are fundamental fate and transport mechanisms for gasoline constituents <br /> Because of these assumptions, the model output results can be quite conservative <br /> VLEACH Model Setup <br /> The modelmg results are presented in Attachment A As shown, Profile 1 presents the Model <br /> Settings, Profile Structure, Chemical, and graphical representation of the model output for <br /> MTBE(Figure 1) The model settings and results are presented below <br /> Model Settings- The Model Settings are shown in Table 1- Case Settings and Table 2 - Initial <br /> Conditions For the Case Settings table the simulation timestep or model recalculation interval <br /> was set at 01 years, and the simulation length was set at 100 years The cell number was set at <br /> 15, which equals the depth to groundwater We used 15 fbg as the depth to groundwater because <br /> this is the most representative value to use based on the soil sample collection date of August <br /> 1996 The representative area is not shown in the model settings (but is part of setup) is shown <br /> on Figure 2 and is approximately 0 004 acre or 176 ft2 The surface water recharge rate is 0 17 <br /> feet per year This value is approximately 10% of the annual rainfall for the area and assumes <br /> that this is the rate of water entering a paved surface and moving through the unsaturated zone <br /> 0323 2 <br />
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