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CO0003088
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CORRAL HOLLOW
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2500 – Emergency Response Program
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CO0003088
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Last modified
8/5/2019 1:18:19 PM
Creation date
12/5/2018 11:25:34 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2500 – Emergency Response Program
RECORD_ID
CO0003088
PE
2546
FACILITY_NAME
CORRAL HOLLOW LANDFILL
STREET_NUMBER
31130
Direction
S
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
ENTERED_DATE
12/22/1994 12:00:00 AM
SITE_LOCATION
31130 S CORRAL HOLLOW ROAD
RECEIVED_DATE
12/21/1994 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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SCS ENGINEERS- <br /> These three sections are as follows: <br /> • The Upper Section consisting of coarse grained alluvial deposits. We presume <br /> the original landfill excavation and vertical extent of refuse are generally <br /> within the limits of the Upper Section <br /> • The Corcoran Clay Member consisting of sandy silts and clays. <br /> • The Lower Section consisting of coarse grained alluvial deposits. _ <br /> Shallow soils around the landfill perimeter are predominantly within the Upper Section <br /> and are considered relatively permeable with respect to LFG migration. _ <br /> The Corcoran Clay Member is approximately 50 feet thick beneath the eastern margin <br /> of the landfill, and is first encountered at a depth of approximately 10 to 15 ft below _ <br /> ground surface (bgs) in this area. The Corcoran Clay layer thins to the west pinching <br /> out into the coarse grained alluvial deposits of the Upper and Lower Sections of the <br /> Tulare Formation near the eastern margin of the landfill. The Corcoran Clay units are <br /> considered relatively impermeable with respect to subsurface LFG migration. <br /> Groundwater below the site occurs in two water bearing zones: (1) the upper zone <br /> which consists of perched unconfined water above the Corcoran Clay Member; and (2) — <br /> a lower water bearing zone below the Corcoran Clay Member. Ground water in the <br /> upper zone is present at a depth of approximately 15 ft bgs in the vicinity of GW-7 (at <br /> approximate elevation 225 ft MSL), and is expected to act as a barrier to LFG migration — <br /> in this area. Ground water has been encountered in the lower zone at depths of <br /> approximately 300 ft below grade in other parts of the site and is not expected to <br /> affect LFG migration patterns. — <br /> The proposed well depths take the above factors into account. For example, well <br /> GW-7 will extend to a depth of approximately 15 ft bgs, or just above the shallow <br /> water table. It is anticipated that the depth of wells GW-1 and GW-6 will be similarly <br /> limited; the borings will be advanced to just above the water table (or Corcoran Clay <br /> layer). All other monitoring wells will extend to the depths of adjacent refuse. Ground — <br /> water is not anticipated at those locations. <br /> We anticipate that all monitoring well borings will be advanced through the alluvial _ <br /> deposits of the Upper Section. Therefore, proposed probe depths are primarily a <br /> function of the total boring depth. Probe depths will be adjusted in the field, based on <br /> subsurface conditions. All probes will be set above the Corcoran Clay units. <br /> Locations of On-Site Structures Relative to the Waste Disposal Area-- <br /> Existing on-site structures include an equipment shed and gate house. Both are <br /> considered temporary and will be removed at the end of closure activities in late 1995. <br /> For this reason, permanent LFG monitoring wells are not proposed for installation <br /> immediately adjacent to these structures. Proposed well GW-2 will provide information <br /> on subsurface LFG conditions near the temporary structures, however. The interior of <br /> 9 — <br />
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