EVALUATING HUMAN VARIABILITY IN CHEMICAL RISK ASSESSMENT - HAZARD IDENTIFICATION AND DOSE-RESPONSE ASSESSMENT FOR NONCANCER ORAL TOXICITY OF TRICHLOROETHYLENE
Ha. Barton et al., EVALUATING HUMAN VARIABILITY IN CHEMICAL RISK ASSESSMENT - HAZARD IDENTIFICATION AND DOSE-RESPONSE ASSESSMENT FOR NONCANCER ORAL TOXICITY OF TRICHLOROETHYLENE, Toxicology, 111(1-3), 1996, pp. 271-287
Human variability can be addressed during each stage in the risk asses
sment of chemicals causing noncancer toxicities, Noncancer toxicities
arising from oral exposure to trichloroethylene (TCE) are used in this
paper as a case study for exploring strategies for identifying and in
corporating information about human variability in the chemical specif
ic hazard identification and dose-response assessment steps. Toxicity
testing in laboratory rodents is the most commonly used method for haz
ard identification. By using animal models for sensitive populations,
such as developing fetuses, testing can identify some potentially sens
itive populations, A large variety of reproductive and developmental s
tudies with TCE were reviewed. The results were mostly negative and th
e limited positive findings generally occurred at doses similar to tho
se causing liver and kidney toxicity. Physiologically based pharmacoki
netic modeling using Monte Carlo simulation is one method for evaluati
ng human variability in the dose-response assessment, Three strategies
for obtaining data describing this variability for TCE are discussed:
(1) using in vivo human pharmacokinetic data for TCE and its metaboli
tes, (2) studying metabolism in vitro, and (3) identifying the respons
ible enzymes and their variability. A review of important steps in the
metabolic pathways for TCE describes known metabolic variabilities in
cluding genetic polymorphisms, enzyme induction, and disease states. A
significant problem for incorporating data on pharmacokinetic variabi
lity is a lack of information on how it relates to alterations in toxi
city. Response modeling is still largely limited to empirical methods
due to the lack of knowledge about toxicodynamic processes. Empirical
methods, such as reduction of the No-Observed-Adverse-Effect-Level or
a Benchmark Dose by uncertainty factors, incorporate human variability
only qualitatively by use of an uncertainty factor. As improved data
and methods for biologically based dose-response assessment become ava
ilable, use of quantitative information about variability will increas
e in the risk assessment of chemicals.