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2900 - Site Mitigation Program
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PR0506509
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
6/1/2020 12:26:14 PM
Creation date
6/1/2020 12:12:07 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0506509
PE
2960
FACILITY_ID
FA0007466
FACILITY_NAME
GEORGIA PACIFIC CORP (FORMER)
STREET_NUMBER
75
Direction
W
STREET_NAME
VALPICO
STREET_TYPE
RD
City
TRACY
Zip
95336
APN
24613007
CURRENT_STATUS
01
SITE_LOCATION
75 W VALPICO RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Memorandum ST AT; r- C 'J „ ; < <br /> REGIONAL WATER QUALITY CONTROL 130ARD o CENTRAL VALLEY REGION <br /> 3201 `"Street 53 rc^:rnto, C;lilorm3 °5316-7090 Pnone 916✓445-0:70 <br /> To: 1 om Plnkos, Chief FROM: Jon Marshack <br /> Ground Water, Protection Environmental SUDDOrt Unit <br /> & Investigations Section <br /> DATE: 24 July 1986 SIGNATURE: <br /> SUBJECT: CLEANUP CRITERIA FOR CHLOROFORM (CHC13) <br /> Problem: <br /> There is an inconsistency in the application of water quality standards and <br /> criteria for cleanup of sites contaminated with chlorinated volatile organic <br /> contaminants. For most potentially carcinogenic VOCs, the 10-6 cancer risk <br /> level is used as the upper limit, above which contaminants in ground water are <br /> assumed to impair its use for domestic supply. A common example is the 5 <br /> ug/l value for TCE. For chloroform, another potentially carcinogenic VOC, <br /> some staff and dischargers are applying the MCL for total trihalomethanes <br /> (TTHMs) of 100 µg/l, a value that is over 500-times greater than the )0-6 <br /> cancer risk level for chloroform. Chloroform is one of the four chemicals <br /> covered by the term "trihalomethanes". DHS is also advocating the use of the <br /> TTHM standard as a cleanup criterion for chloroform in ground water. <br /> PrODOsed Solution: <br /> EPA has stated that the MCL for TTHMs was based mainly on technology and <br /> economics. I Therefore, this standard does not clearly protect the beneficial <br /> use for domestic supply of waters of the state. The MCL for TTHMs was <br /> derived for application to water as it is delivered to consumers after <br /> disinfection by chlorination, and not to the protection of the ambient quality <br /> of domestic water supply sources. In site cleanup situations the 10-6 cancer <br /> risk level of 0.19 ug/1 should be used as the measure of potential impairment <br /> by chloroform of the beneficial use of ground water for domestic supply. <br /> �o <br /> n In fact, virtually all primary MCLs are derived by balancing technologic and <br /> economic concerns directly related .to the use of water for domestic supply <br />
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