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(I TLC) value of 1,000 mg/kg. The TTLC value, 'per Title 22 of the California Code of <br /> Regulations (CCR), is the concentration of a solubilized, extractable and .nonextractable <br /> bioaccumulative or persistent toxic substance which, if equaled or exceeded in a waste, renders <br /> the waste hazardous.' . <br /> 4.3 PRELEW NARY RISK ASSESSMENT <br /> The concentration of MTBE detected in groundwater in boring B1-2 (120 µglf) exceeds the <br /> US EPA Region IX Preliminary Remediation Goal (May 1998) of 201cg/I (for tap water) and <br /> the recommended US EPA drinking water health advisory for MTBE of 20 to 40 µgl f. These 1 <br /> levels are recommended concentrations that would likely avoid objectionable/unpleasant taste R <br /> and odor effects in drinking water. Health risks have been evaluated by Cal/EPA's Office of <br /> Environmental Health Hazard Assessment (OEHHA), who have proposed a public health goal <br /> of 14. parts per billion in drinking water based on their findings of potential cancer risk <br /> associated with MTBE exposure (OEHHA, 1998). <br /> The primary risks caused by the presence of-MTBE in groundwater at this site appear to be: <br /> 1) impairment of beneficial uses of groundwater in the immediate area; and 2) risks to the <br /> health and safety of sensitive receptors through exposure to MTBE. Beneficial uses of <br /> groundwater.in the area are identified in the Regional Water Quality Control Board Basin Pian <br /> as municipal, agricultural or industrial supply.- Sensitive receptors in the area are people who <br /> work in the vicinity'of the site, and possibly aquatic biota in the deep water channel located <br /> about 350 feet north of the site. Reasonable potential exposure pathways/scenarios for human <br /> contact with-the MTBE include inhalation of vapors, ingestion, or dermal contact. Scenarios <br /> for aquatic biota include ingestion.or external contact with potentially sensitive tissue. The <br /> following factors have been identified regarding the likelihood.of MTBE contact associated <br /> with these exposure scenarios: <br /> o Assuming that the MTBE found in the B1-2water sample was introduced by a ,_1 <br /> leak from the former tank at Site 1, the removal of the tank and the absence of <br /> MTBE (or any other petroleum constituents) in soils in the vicinity of the tank <br /> constitutes source removal. As such, remaining MTBE in groundwater will <br /> eventually be reduced to concentrations below action levels through natural <br /> attenuation and dilution through mixing with groundwater, thus reducing <br /> potential exposure. <br /> o Ingestion of MTBE is only likely to occur if the MTBE is transported by <br /> groundwater flow to an active municipal supply well used for drinking water. <br /> B&R contacted California Water Service, the municipal water supplier in the <br /> 6 98111AINVRPTs1S1USTINV.RPT <br />