Sp. Felter et Ml. Dourson, HEXAVALENT CHROMIUM-CONTAMINATED SOILS - OPTIONS FOR RISK ASSESSMENT AND RISK MANAGEMENT, Regulatory toxicology and pharmacology, 25(1), 1997, pp. 43-59
Risk assessment involves establishing scientifically defensible dose-r
esponse relationships for end points of concern. For Cr(VI)-contaminat
ed soils, this includes conducting dose-response assessments for blood
, Liver, and kidney toxicity following oral exposure; lung cancer foll
owing inhalation exposure; and allergic contact dermatitis following d
ermal exposure. This dose-response information is then integrated with
a site-specific exposure assessment (or default assumptions) in order
to develop a site-specific (or generic) soil criterion within the fra
mework of a comprehensive risk characterization. Risk managers develop
cleanup standards designed to protect against all possible adverse ef
fects, taking into account these site-specific (or generic) criteria a
nd other factors such as technical feasibility, cost-benefit analyses,
and sociopolitical concerns. Recently a push for cost-benefit analyse
s of environmental decisions has occurred, further supporting the need
for risk assessors to prepare a comprehensive risk characterization,
with its attendant uncertainties. These risk assessment and management
issues are brought to the forefront by risk assessors and risk manage
rs dealing with Cr(VI)-contaminated soils. This article offers a revie
w and analysis of the risk characterization of Cr(VI)-contaminated soi
ls, showing that the differing toxicities with route of exposures do n
ot necessarily lead to different characterizations of risk. Soil conce
ntrations in the range of 130 to 450 ppm appear to protect against non
cancer toxicity hom oral exposure, cancer toxicity from inhalation exp
osure, and allergic contact dermatitis from dermal exposure. (C) 1997
Academic Press.