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2900 - Site Mitigation Program
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PR0522383
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Last modified
6/1/2020 12:41:17 PM
Creation date
6/1/2020 12:36:27 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0522383
PE
2950
FACILITY_ID
FA0015246
FACILITY_NAME
MUSCO OLIVE - OFFSITE
STREET_NUMBER
17950
Direction
W
STREET_NAME
VIA NICOLO
STREET_TYPE
RD
City
TRACY
Zip
95377
APN
20911032
CURRENT_STATUS
02
SITE_LOCATION
17950 W VIA NICOLO RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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' • Kennedy/Jenks Consultants <br /> ' Section 3: Groundwater Quality <br /> This section describes hydrogeology and groundwater quality in the reclamation area near <br /> Jepsen Webb Ranch and Valley View Thoroughbred Farm. Groundwater quality data from the <br /> surrounding area and sample data from wells near the two reclamation properties was used to <br /> ' construct isoconcentration contours, which allowed analysis of regional total dissolved solids <br /> (TDS) concentrations. <br /> ' 3.1 Regional Hydrogeology <br /> The Jepsen Webb Ranch and Valley View Thoroughbred Farm properties are approximately 2.5 <br /> miles to the north-northeast of the Lawrence Livermore National Laboratory Site 300 (LLNL Site <br /> 300) and approximately 4 miles southwest of the City of Tracy. <br /> ' 3.1.1 Site 300 <br /> Site 300 is generally underlain by gently dipping sedimentary bedrock dissected by steep <br /> ' ravines. The bedrock is made up primarily of interbedded sandstone, siltstone, and claystone. <br /> Most groundwater occurs in the Neroly Formation upper and lower blue sandstone aquifers. <br /> Significant groundwater is also locally present in permeable Quaternary alluvium valley fill. <br /> ' Much less groundwater is present within perched aquifers in the unnamed Pliocene nonmarine <br /> unit. Perched aquifers contain unconfined water separated from an underlying main body of <br /> water by impermeable layers; normally they are discontinuous and highly localized. According to <br /> ' information from LLNL, these perched water-bearing zones do not meet the RWQCB criteria for <br /> aquifers that are potential water supplies because water quality generally is poor and yields are <br /> low. <br /> t Fine-grained siltstone and claystone interbeds may confine the groundwater and act as <br /> aquitards, confining layers, or perching horizons. Groundwater is present under confined <br /> conditions in parts of the deeper bedrock aquifers but is generally unconfined elsewhere. <br /> Groundwater flow in most aquifers follows the attitude of the bedrock. In the northwest part of <br /> Site 300, groundwater in bedrock generally flows northeast except where it is locally influenced <br /> by the geometry of alluvium-filled ravines. In the southern half of Site 300, groundwater in <br /> bedrock flows roughly south-southeast, approximately coincident with the attitude of bedrock <br /> strata. The groundwater gradient data is based primarily on water levels measured in the Neroly <br /> lower blue sandstone aquifer. (LLNL, 2001) <br /> ' The thick Neroly lower blue sandstone, which is stratigraphically near the base of the formation, <br /> generally contains confined water. Wells located in the southeast edge of Site 300 are <br /> completed in this aquifer and are used to supply drinking and process water. (LLNL, 2001) <br /> In the area of Site 300, recharge occurs predominantly in locations where saturated alluvial fill is <br /> in contact with underlying permeable bedrock in the uplands, or where permeable bedrock <br /> strata crop out because of structure or topography. Local recharge mostly occurs on hilltops, <br /> creating some perched water-bearing zones. Low rainfall, high evapotranspiration, steep <br /> topography, and intervening aquitards generally preclude direct vertical recharge of the bedrock <br /> aquifers (LLNL, 2001). <br /> Reclamation Report, Page 5 <br /> Musco Family Olive Company <br /> g 4s,roupMnlb!DUTlm ldmaWw lq� AIB.12.M.dM <br />
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