Evaluating the similarity of complex drinking-water disinfection by-product mixtures: overview of the issues.
Humans are exposed daily to complex mixtures of environmental chemical contaminants, which arise as releases from sources such as engineering procedures, degradation processes, and emissions from mobile or stationary sources. When dose-response data are available for the actual environmental mixture to which individuals are exposed (i.e., the mixture of concern), these data provide the best information for dose-response assessment of the mixture. When suitable data on the mixture itself are not available, surrogate data might be used from a sufficiently similar mixture or a group of similar mixtures. Consequently, the determination of whether the mixture of concern is "sufficiently similar" to a tested mixture or a group of tested mixtures is central to the use of whole mixture methods. This article provides an overview for a series of companion articles whose purpose is to develop a set of biostatistical, chemical, and toxicological criteria and approaches for evaluating the similarity of drinking-water disinfection by-product (DBPs) complex mixtures. Together, the five articles in this series serve as a case study whose techniques will be relevant to assessing similarity for other classes of complex mixtures of environmental chemicals. Schenck et al. (2009) describe the chemistry and mutagenicity of a set of DBP mixtures concentrated from five different drinking-water treatment plants. Bull et al. (2009a, 2009b) describe how the variables that impact the formation of DBP affect the chemical composition and, subsequently, the expected toxicity of the mixture. Feder et al. (2009a, 2009b) evaluate the similarity of DBP mixture concentrates by applying two biostatistical approaches, principal components analysis, and a nonparametric "bootstrap" analysis. Important factors for determining sufficient similarity of DBP mixtures found in this research include disinfectant used; source water characteristics, including the concentrations of bromide and total organic carbon; concentrations and proportions of individual DBPs with known toxicity data on the same endpoint; magnitude of the unidentified fraction of total organic halides; similar toxicity outcomes for whole mixture testing (e.g., mutagenicity); and summary chemical measures such as total trihalomethanes, total haloacetic acids, total haloacetonitriles, and the levels of bromide incorporation in the DBP classes.
Rice
Glenn E
GE
U.S. Environmental Protection Agency, Cincinnati, Ohio 45268, USA. rice.glenn@epa.gov
Teuschler
Linda K
LK
Bull
Richard J
RJ
Simmons
Jane E
JE
Feder
Paul I
PI
D000818:Animals; D045424:Complex Mixtures / Q000032:analysis* / Q000633:toxicity*; D004202:Disinfectants / Q000032:analysis / Q000494:pharmacology / Q000633:toxicity*; D004203:Disinfection; D004305:Dose-Response Relationship, Drug; D006801:Humans; D018570:Risk Assessment; D014873:Water Pollutants / Q000032:analysis* / Q000302:isolation & purification / Q000633:toxicity*; D014881:Water Supply / Q000032:analysis*
D045424:Complex Mixtures; D004202:Disinfectants; D014873:Water Pollutants