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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 />

http://www.inchem.org/documents/ehc/ehc/ehc<strong>214</strong>.htm<br />

Page 137 of 284<br />

6/1/2007

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