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Marley Cooling Tower • • <br /> Page 3 <br /> The only exposure which exceeds an Al is the chromium ex <br /> AIC (acceptable intake -- chronic) for Cr VI . There <br /> chronic toxicity from chromium if all of the Cr is Cr VI <br /> Cr is Cr VI, there would be no exceedance. <br /> Even this possibility is based on lifetime soil exposure <br /> absorption, which assumes that all of the soil that- <br /> contaminated <br /> hatcontaminated as the maximally contaminated sample taken a <br /> These are extremely conservative assumptions. Realistica <br /> to be a chronic toxicity problem from chromium, unless t; <br /> more widespread than is apparent from the present evidence <br /> in the sample is Cr VI . <br /> Arsenic -- Carcinogenicity <br /> The analysis identified arsenic, but did not discriminai <br /> form or an inorganic salt or organic compound is present. Elemental arsenic is <br /> relatively non-toxic (oral TDLo for man is. 7857 mg/kg) because it is poorly <br /> absorbed. Arsenic trioxide is very toxic (oral LD50 for man is 1.4 mg/kg) <br /> because it is well absorbed. The health-conservative assumption would be that <br /> all the arsenic is present as arsenic trioxide. However, according to Bob <br /> Schlag, it is much more likely to be arsenic pentoxide, because this is the form <br /> of arsenic which has been used on site. <br /> The maximum concentration of arsenic found in a soil sample at Marley is 253 ppm. <br /> Based on a lifetime exposure to soil with this concentration, and based on a CAG <br /> unit risk of 15 (mg/kg.d)-1, the lifetime excess cancer risk would be 4 X 10(-2) , <br /> or 4 per 100. <br /> Exposure Unit Risk Risk <br /> Arsenic .18 mg/d 15 (mg/kg.d)-1 4 x 10(-2) <br /> This is a very high risk, but the assumptions are extremely conservative. The <br /> basic assumption is that all the soil ingested or adhering to the skin during the <br /> lifetime of the individual would be contaminated with the amount of arsenic found <br /> in the soil sample at Marley with the highest arsenic concentration. In reality, <br /> this soil contamination is probably very localized, and no one would be exposed <br /> exclusively to soil with the maximum concentration of arsenic. If the estimate <br /> of exposure were reduced by a factor of 1 ,000, then the risk would be 4 X 10-5 <br /> which is low but still significant. The exposure would have to be reduced by a <br /> factor of 40,000 to get down to the 1 X 10-6 risk level. At present we simply do <br /> not have adequate information on which to base any reasonable estimate of the <br /> exposure. <br /> Chromium -- Carcinogenicity <br /> If one were to assume that all of the chromium onsite is in the form of Cr VI, <br /> and that contamination is widespread at levels equal to the maximum detected, and <br /> further assuming that carcinogenic risk determined from inhalation exposure data <br /> is valid for estimating risk due to oral and dermal exposure, one might estimate <br /> a high level of exposure and calculate a high cancer risk from chromium. <br />