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2900 - Site Mitigation Program
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/29/2019 11:58:23 AM
Creation date
5/29/2019 11:10:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0508450
PE
2960
FACILITY_ID
FA0008087
FACILITY_NAME
DDJC-TRACY
STREET_NUMBER
25700
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25207002
CURRENT_STATUS
01
SITE_LOCATION
25700 CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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3 <br /> Summary of Health Risks <br /> As part of the Remedial Investiga- to an amount of the material known drinking,bathing in,or breathing <br /> tion,LLNL conducted a Baseline or suspected to cause harm. The vapors while showering in contam- <br /> Public Health Assessment to estimate risk is expressed as the chance of a inated ground water. <br /> the current and future risks to disease or an effect occurring. For Using EPA methods,LLNL esti- <br /> human health and the environment example,a risk level of one in one mated the potential cancer risks for <br /> if no cleanup actions were taken at million means that a person coming two different exposure scenarios,one <br /> LLNL. Copies of this assessment into contact with a certain chemical more conservative than the other: <br /> are available for review in the infor- would increase his or her normal <br /> mation repositories listed on the risk of developing cancer(which for ■ A "best-estimate" case,which <br /> back page. Americans is about a one in four took into account the locations of <br /> What is a Risk Assessment? chance)by one in one million. existing private and municipal sup- <br /> A risk assessment is a scientific Risk assessments make conserva- ply wells and the most realistichydrogeologic and chemical- <br /> procedure that uses facts and five assumptions that weigh in favor concentration estimates. The best- <br /> assumptions to estimate the poten- of protecting public health. For estimate scenario represents the <br /> tial for adverse effects on human example,the risk assessment for most probable set of conditions, <br /> health from exposure to chemicals. LLNL assumed exposure to the using EPA's assumptions regarding <br /> Potential risk is determined by maximum possible chemical concen- exposure and toxicity. <br /> assessing the amount of a material a trations,every day,for a 70-year <br /> person may ingest or come into con- period,even though actual exposure ■ A"health-conservative"case, <br /> tact with in water,soil,and air,and is likely to be far less. which assumes the highest conceiv- <br /> comparing the estimated exposure Results for LLNL able exposures,such as drinking two <br /> liters of water a day from the most <br /> Background ContinuedJrompugel The main ways that a person contaminated zone located immedi- <br /> could potentially be exposed to atel west of LLNL. <br /> cleanup alternatives for LLNL.This Livermore site contaminants is by y <br /> Feasibility Study(FS)evaluated the continued on page 4 <br /> health impacts after cleanup and esti- TRITIUM <br /> mated the costs of the cleanup alter- <br /> natives.(See the back page of this To date,tritium is the only radioactive material that has been found at or <br /> fact sheet for information on how near regulatory cleanup limits in ground water or soil at the LLNL site. <br /> you can review a copy of the FS.) With the exception of two monitor wells in the area of an old hazardous <br /> waste disposal pit in eastern LLNL,tritium has historically been found in <br /> LLNL has been conducting two ground water in concentrations well below the drinking water standard of <br /> pilot studies to test the effectiveness 20,000 picocuries per liter. <br /> of promising technologies for LLNL conducted a special risk analysis to assess the risks from tritium in <br /> extracting and,treating VOCs and ground water and soil at the LLNL main site. There are two primary ways <br /> FHCs from ground water and unsat- that someone could potentially be exposed to subsurface tritium at LLNL: <br /> urated soil.LLNL has extracted over 0 From air emissions associated with ground water cleanup activities <br /> 30 million gallons of ground water that,in the future,might be treating ground water that <br /> from the southwest part of the site contains both VOCs and tritium(e.g.,using an air stripping process). <br /> and employed an ultraviolet ■ From vegetation that has absorbed soil moisture and then given off into <br /> light/hydrogen peroxide system to the air the water that contains tritium. This process is called transpiration. <br /> destroy the contaminants.(See page The results of this screening-level risk analysis show that the maximum <br /> 7 for a description of this technolo- annual dose that a person could receive from either of these ways is substan- <br /> gy.)To conserve local ground water, tially lower than the 10 millirems per year dose considered to be safe under <br /> most of this treated water has been EPA's Clean Air Act. <br /> returned to ground water via a Studies show that the tritium in the subsurface at LLNL is moving so slow- <br /> recharge basin just south of LLNL, ly that,even if no cleanup were done,it will naturally decay to background <br /> or used at LLNL for landscape irri- levels before anyone offsite could be exposed to it in the future. At the pre- <br /> gation and in cooling towers.In sent,there are no known significant ongoing sources of tritium to ground <br /> another pilot study,the equivalent of water or the unsaturated soils. Consequently,tritium does not pose a health <br /> about 2,200 gallons of FHCs have threat. LLNL believes that it knows the major sources of tritium in the soils <br /> been removed as of June 1991 by and ground water,but will continue to monitor and investigate for tritium in <br /> withdrawing vapors from the unsat- the future. <br /> urated sediments in the Gasoline <br /> Spill Area.The FHC vapors were <br /> destroyed by a thermal oxidizer. <br />
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