Environmental Health Criteria 214
Environmental Health Criteria 214
Environmental Health Criteria 214
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HUMAN EXPOSURE ASSESSMENT<br />
There are a number of methods for measuring estimating food<br />
consumption and contamination. The method chosen will depend on the<br />
information available, the population group of concern, whether acute<br />
or chronic effects of the chemical are being expressed, the intended<br />
use of the results and available resources. The reader is strongly<br />
advised to refer to more comprehensive documents on dietary survey<br />
methodology and dietary exposure assessment approaches.<br />
8. MEASURING HUMAN EXPOSURE TO CHEMICAL CONTAMINANTS IN SOIL AND<br />
SETTLED DUST<br />
8.1 Introduction<br />
This chapter is intended to provide the reader with important<br />
concepts and a basic understanding of soil and settled dust sampling<br />
so that effective sampling strategies can be designed to meet specific<br />
research needs. Choices in sampling methods, sampling locations,<br />
sampling areas and the sampling time of the sample collection may be<br />
particularly important when the results are used for exposure<br />
assessment purposes. For these methods to be used successfully, it is<br />
important that the investigators understand the basic concepts behind<br />
collecting soil and settled dust and the limitations of different<br />
methods and strategies. Because this field of research is currently<br />
evolving rapidly, it is recommended that researchers consult the<br />
literature for new and complete information before designing a study<br />
to measure toxic metals, pesticides, PAHs, other products of<br />
incomplete combustion, fibres and biological matter. The most<br />
appropriate method for sampling soil and settled dust depends on the<br />
living conditions of the study population and the target contaminants.<br />
The information in this chapter is therefore intended to provide<br />
general guidance on approaches that might be taken.<br />
Soil is a mixture of air, water, mineral and organic components<br />
(Horne, 1978). The relative mix of these components determines to a<br />
large extent the capacity of a soil for containing chemical<br />
contaminants and the potential for it to be an important source of<br />
exposure. Settled dust, which may be found outdoors or indoors, is<br />
often a complex mixture of material from several sources. Outdoor<br />
settled dust is material deposited on roadways, streets and other<br />
paved surfaces. Indoor settled dust (house dust) is material deposited<br />
on indoor surfaces such as floors, carpets and furniture. Chemical<br />
contaminants present in indoor dust can originate from activities in<br />
the home or can be tracked into the home from road dust, soil or work<br />
sites (US EPA, 1991). Material present in soil, outdoor dust and<br />
indoor dust may include clay, sand, bacteria, viruses, allergens,<br />
products of incomplete combustion, environmental tobacco smoke, heavy<br />
metals, pesticides, asbestos fibres, paint fragments, solvents, flame<br />
retardants, cleaners, and residues from synthetic fibres, building<br />
products and many other materials and pollutants (Robert & Dickey,<br />
1995).<br />
Unintentional ingestion of house dust, particularly for children,<br />
may be a significant contributor to the total human exposure to many<br />
potentially toxic substances, depending on personal living conditions<br />
and frequency of contact with this media. Because children spend more<br />
time in contact with soil and indoor surfaces than adults and have a<br />
greater dose given the same exposure, these exposure pathways are<br />
particularly relevant to children. For example, it is likely that<br />
children's lead exposure from settled dust is an important<br />
contribution to total lead exposure because of the past and present<br />
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