Environmental Health Criteria 214
Environmental Health Criteria 214
Environmental Health Criteria 214
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
HUMAN EXPOSURE ASSESSMENT<br />
Air dermal contact inhalation<br />
Tap water dermal contact ingestion<br />
Food and beverages ingestion<br />
Surface soil dermal contact ingestion<br />
Surface water dermal contact ingestion<br />
6.5.1 Inter-media transfer factors<br />
Transfer of contaminants between media is commonly modelled as<br />
partitioning of a chemical between two or more media. Thus,<br />
multiple-pathway models require the measurement or estimation of<br />
partition coefficients of contaminants between several pairs of<br />
environmental media. There are two general classes of partitioning<br />
coefficients. The first class relies on basic physicochemical<br />
properties of the compounds of interest such as aqueous solubility,<br />
vapour pressure and dipole moment; they describe partitioning due to<br />
diffusive processes. Coefficients in the second class describe<br />
partitioning resulting from what may be considered advective<br />
processes, but also implicitly include diffusive partitioning.<br />
6.5.1.1 Diffusive partition coefficients<br />
The class of diffusive partition coefficients includes those<br />
between soil and water in soil (e.g., groundwater), air and plants,<br />
soil and plants, animal intake and food, surface water and fish,<br />
mother's uptake and breast milk, residential water and indoor air,<br />
soil-gas and indoor air, human skin and soil, and human skin and<br />
water. In many cases, partition coefficients developed from<br />
laboratory-scale experiments are the basis for modelling partitioning<br />
of a compound between environmental media (Lyman et al., 1990). For<br />
example, the octanol-water partition coefficient is often used as a<br />
proxy for partitioning non-polar organic compounds (e.g.,<br />
organochlorine substances) between water and fish lipids. In this<br />
case, n-octanol is considered a good model for fish lipids.<br />
Similarly, the organic carbon-water partition coefficient is used to<br />
characterize partitioning of non-polar substances between organic<br />
matter in soil and water. Finally, Henry's constant describes<br />
partitioning of volatile and non-volatile compounds between air and<br />
water. Connell et al. (1997) provide a comprehensive introduction to<br />
the use of this type of partition coefficient in environmental science<br />
and exposure assessment.<br />
6.5.1.2 Advective partition coefficients<br />
The second class of partitioning coefficients jointly describe<br />
bulk transfer of compounds from one medium to another and diffusive<br />
partitioning. They are often used to model active uptake of<br />
contaminants by animals, principally livestock and game such as fish<br />
or fowl. Factors of this type are used to model transfer of<br />
semi-volatile compounds (SVOCs) such as dioxins from air to soil, soil<br />
to beef and soil to cow's milk (e.g., Nessel et al., 1991; Fries,<br />
1995). Bioaccumulation of lipophilic compounds and some forms of heavy<br />
metals (e.g., methylmercury) in fish from ingestion of contaminated<br />
prey and diffusive uptake through respiration is also modelled using<br />
http://www.inchem.org/documents/ehc/ehc/ehc<strong>214</strong>.htm<br />
Page 102 of 284<br />
6/1/2007