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SR0079530
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Entry Properties
Last modified
11/24/2020 3:15:50 PM
Creation date
11/24/2020 3:11:46 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
RECORD_ID
SR0079530
PE
2903
FACILITY_ID
FA0024812
FACILITY_NAME
LAWRENCE LIVERMORE NATIONAL LABORATORY SITE 300
STREET_NUMBER
0
Direction
S
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
95376
ENTERED_DATE
8/20/2018 12:00:00 AM
SITE_LOCATION
S CORRAL HOLLOW RD
QC Status
Approved
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EHD - Public
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WASTE DISCHARGE REQUIREMENTS ORDER NO. R5-2008-0148 -11- <br /> LAWRENCE LIVERMORE NATIONAL SECURITY, LLC AND <br /> THE U.S. DEPARTMENT OF ENERGY FOR <br /> LAWRENCE LIVERMORE NATIONAL LABORATORY SITE 300 <br /> SAN JOAQUIN AND ALAMEDA COUNTIES <br /> 30 feet bgs, the Discharger determined that all constituents detected in the <br /> mechanical equipment discharges were lower than the DLM value, indicating <br /> the discharges are not predicted to negatively affect groundwater. However, <br /> the Regional Water Board has since concluded that salts do not attenuate; <br /> therefore, an attenuation factor of one (1) should be applied for salts. In <br /> response to this conclusion, the results of the Discharger's analyses reported <br /> in the 28 January 2005 report were revised to reflect an attenuation factor of 1 <br /> for salts as shown on Attachment 16, a part of this Order. Concentrations of <br /> conductivity (measured as SC), sulfate, sodium, and TDS in the mechanical <br /> equipment effluent exceed water quality goals. Concentrations of chloride <br /> were elevated as well and have the potential to exceed the water quality goal. <br /> Concentrations of these five constituents in groundwater vary throughout the <br /> site and vary in the different hydrostratigrahic units. Concentrations observed <br /> in existing monitor wells upgradient of the percolation pits range from just <br /> below to significantly above the water quality goals (see Attachment 17, a part <br /> of this Order). <br /> 46.For discharges of mechanical equipment effluent, this Order requires the <br /> Discharger to conduct a salinity evaluation and minimization plan; requires <br /> the Discharger to obtain additional effluent information; requires the <br /> Discharger to evaluate fate and transport of salt and metals to ground water; <br /> and requires the Discharger to develop additional information on salinity in the <br /> source water and receiving water. If any mechanical equipment discharges to <br /> percolation pits have degraded groundwater, the Discharger will be required <br /> to monitor groundwater up and downgradient of those discharges and submit <br /> a feasibility study proposing remedial alternatives to restore beneficial uses of <br /> groundwater if it is determined by the Regional Water Board that the <br /> groundwater has been unreasonably degraded. The Discharger must include <br /> a proposal for implementing a source control program and best practicable <br /> technology (BPT) to reduce pollutants in the discharge. <br /> 47. This Order also requires the Discharger to monitor semi-annually wastewater <br /> discharged to each mechanical equipment percolation pit as described in <br /> MRP No. R5-2008-0148. <br /> Cooling Tower Percolation Pits <br /> 48.Nine non-contact cooling towers, one each at Buildings 801, 809, 812, 817A, <br /> 826, two at 827A, and two at 851, discharge blowdown to seven percolation <br /> pits, one at each building. Maximum design discharge to these percolation <br /> pits ranges from 300 to 1,200 gpd. Attachment 15 provides a summary of the <br /> location and design of the percolation pits, nearby wells, depth to <br /> groundwater and groundwater flow direction. Additional wells may be <br />
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