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4400 - Solid Waste Program
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PR0504215
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Last modified
7/31/2020 9:46:20 AM
Creation date
7/3/2020 10:35:00 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0504215
PE
4430
FACILITY_ID
FA0003934
FACILITY_NAME
Lawrence Livermore National Lab - Site 300
STREET_NUMBER
15999
Direction
W
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
15999 W CORRAL HOLLOW RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
CField
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4430_PR0504215_15999 W CORRAL HOLLOW_.tif
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EHD - Public
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• <br /> CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD • CENTRAL VALLEY REGION <br /> 3443 Routier Road Phone: (91 6) 361-5600 <br /> Sacramento, CA 95827-3098 ATSS: 8-495-5600 <br /> TO: Kenneth D. Landau FROM: Wendy L. Cohen <br /> Senior Engineer Project Engineer <br /> DATE: 16 June 1987SIGNATURE: <br /> SUBJECT: DRYELL STATUS REPORT, LAWRENCE LIVERMORE NATIONAL LABORATORY SITE <br /> 300, SAN JOAQUIN COUNTY <br /> I have reviewed Lawrence Livermore National Laboratory's (LLNL) drywell status <br /> report dated 14 April 1987 and information submitted previously on drywells at <br /> LLNL' s Site 300. The combined submittals list 16 drywells plus two discharges <br /> to land for a total of 18 sites. The following comments cover all 18 sites with <br /> recommendations for any further actions. <br /> 1. Six drywells in the General Services Area (GSA) (at Buildings 872, 873-E, <br /> 873-S, 874, 875-S1 and 875-S2) were permanently closed in 1983 and a report <br /> submitted in February 1984; no further action was taken. The closure plan <br /> submitted in February 1983 shows the wastewater discharged to drywells <br /> 873-E and 875-S2 resulted from acid dip tank operations (nitric and chromic <br /> acid used with copper parts) , and was hazardous with 8.7 mg/l of chromium. <br /> The wastewater discharged to drywell 872-S contained very high BOD, COD, <br /> and filtered organic carbon. _ Drywells 875-S1 and 873-S received wastewater <br /> which likely would not cause water quality problems , and wastewater <br /> directed to drywell 874 was® not characterized. A seventh "drywell " <br /> tactually an unlined ditch at Building 879.) also was mentioned in the 1983 <br /> closure plan but was not characterized (see item 5 below for a full <br /> discussion of this location). <br /> The six drywells were closed by removing the gravels, casings, and about <br /> three feet of surrounding soil , filling the holes with native soil and <br /> compacting, and capping with asphalt for wells that originally were under <br /> asphalt. We have no construction details on the wells, and apparently no <br /> samples were taken at the bottom of the holes before backfilling. Soil <br /> samples were taken from augered holes about one foot and five feet down- <br /> gradient of the drywells at depths of six and nine feet (the drywells were <br /> reported to be six feet deep) . Samples were analyzed by the EP Toxicity <br /> test for chromium, copper, and lead, but the detection limit for lead was <br /> 0.16 mg/i , more than three times the drinking water standard. Samples also <br /> were analyzed by EPA Method 624 with results showing most of the samples <br /> contained toluene (11 out of 15 samples) with values ranging from 30 to <br /> 1,000 ppb, and one-half the samples contained methylethyl ketone (MEK) with <br /> values ranging from 1 to 6 ppm. One sample from nine feet deep in a <br /> borehole near drywell 875-S (the lab sheet does not differentiate between <br /> 875-S1 and 875-S2) contained 10 ppb of TCF_. <br />
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