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PR0517323
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
2/14/2019 3:46:08 PM
Creation date
2/14/2019 9:40:06 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0517323
PE
2960
FACILITY_ID
FA0013339
FACILITY_NAME
MT HOUSE SITES 1-6
STREET_NUMBER
0
STREET_NAME
BYRON
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
BYRON RD
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Soil and Groundwater Investigation Report <br /> Mountain House Development Site#6 July 2008 <br /> Depth-discrete vertical profile samples were not collected in Area 2 and Area 3. <br /> 5.2.2 Suitability of the Groundwater for Drinking <br /> TDS concentrations ranged from 2,260 to 2,560 milligrams per liter(mg/L)in samples collected from <br /> SB-20 and SB-25,respectively(Table 6),which exceed the following current California Department of <br /> Health Services (Ca1DHS)Maximum Contaminant Levels(MCLs)for drinking water(Ca1DHS,March <br /> 2008): <br /> • 500 mg/L,recommended. <br /> • 1,000 mg/L,upper. <br /> • 1,500 mg/L, short term, as well as: <br /> • RWQCB Water Quality Goals(WQG), Ca1DHS and US EPA drinking water standards: 500 <br /> mg/L(RWQCB,August 2007). <br /> • RWQCB WQG,Agricultural Water Quality Goal: 450 mg/L(RWQCB,August 2007). <br /> • RWQCB WQG,US EPA Ambient Water Quality Criteria for Taste and Odor or Welfare: 250 <br /> mg/L(RWQCB,August 2007). <br /> The groundwater at this site exceeds numerous State of California and federal TDS standards for drinking <br /> water as well as agricultural-use criteria. Therefore, groundwater at this site will not be used as a drinking <br /> water source. <br /> 6. CONCLUSIONS AND RECOMMENDATIONS <br /> SAIC reviewed the findings of this investigation and the previous soil and groundwater investigation and <br /> concludes the following: <br /> • Field observations and laboratory analytical results indicate that there are at least three areas of <br /> affected soil and groundwater: <br /> o Area 1 <br /> ■ The vertical extent of affected soil has been defined by borings SB-9, SB-10, SB-11, and <br /> SB-15, at depths ranging from 35 to 39.5 feet bgs. Soil samples were not collected from <br /> borings SB-26 and SB-8 at deeper depths corresponding to where affected soil was <br /> detected in adjacent borings (SB-9, SB-10, SB-11, and SB-15). Therefore,the lateral <br /> extent of affected soil in this area is undefined. A source area has not been identified <br /> during field activities as evidenced by the absence of shallow affected soil. <br /> The down-gradient and up-gradient extents of affected groundwater in this area have <br /> been defined at borings SB-26 and SB-8,respectively. The vertical extent of affected <br /> groundwater has been defined by borings SB-10 and SB-15 at 35 and 30 feet bgs, <br /> respectively. <br /> o Area 2 <br /> ■ The affected soil and groundwater in this area has not been entirely delineated. Affected <br /> soil and groundwater was not encountered in borings SB-17, SB-19, SB-20, and SB-24, <br /> which delineates the southeastern extent of Area 2. Soil samples were not collected from <br /> borings SB-4, SB-6, and SB-7 at deeper depths corresponding to where affected soil was <br /> detected in adjacent borings (SB-13, SB-14, SB-16, and SB-18). Therefore,the lateral <br /> extent of affected soil in the northeastern portion of the area is undefined. The vertical <br /> extent of affected soil has been defined by borings SB-5, SB-13, SB-14, SB-16, and <br /> 8 <br /> AAe <br /> From Science to Solutions <br />
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