Environmental Health Criteria 214
Environmental Health Criteria 214
Environmental Health Criteria 214
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HUMAN EXPOSURE ASSESSMENT<br />
processing<br />
5667-6: 1985 Sampling - Part 6: Guidance on sampling of rivers and<br />
streams<br />
The design of a water monitoring programme would be incomplete<br />
without consideration of the demographic and socioeconomic<br />
characteristics, and also an understanding of the historical<br />
development, of the potentially exposed community. The evolution of<br />
materials used in distribution systems changes the profiles of<br />
pollutants requiring measurement. Cultural and socio-economic factors<br />
affect usage patterns, which in turn influence the extent of exposure<br />
to contaminants in drinking-water.<br />
In order to ensure the representativeness and validity of water<br />
samples, sampling techniques must be carefully selected (WHO, 1992,<br />
1993). The first step in the design of a sampling programme is to<br />
develop concise objectives, accounting for<br />
* the nature of the substance to be measured<br />
* point of exposure<br />
* the duration of time over which measurements will be taken.<br />
The type and magnitude of spatial and temporal variations in the<br />
concentration of water constituents will depend upon both their<br />
sources and their behaviour in the distribution and service systems.<br />
Substances can be classified into two main types:<br />
* Type 1. Substances whose concentration is unlikely to vary during<br />
distribution. The concentration of these substances in the<br />
distribution system is largely governed by the concentration in the<br />
water going into the supply, and the substances do not undergo any<br />
reaction in the distribution system. Examples of such substances<br />
are arsenic, chloride, fluoride, hardness, pesticides, sodium and<br />
total dissolved solids.<br />
* Type 2. Substances whose concentrations may vary during<br />
distribution. These include<br />
- substances whose concentration during distribution is dependent<br />
mainly on the concentration in the water going into the supply,<br />
but which may participate in reactions (which change the<br />
concentration) within the distribution system. Examples are<br />
aluminium, chloroform, iron, manganese and hydrogen ion (pH).<br />
- substances for which the distribution system provides the main<br />
source, such as benzo [a]pyrene, copper, lead and zinc.<br />
This classification applies only to piped water supplies. In all<br />
other types of supply, water constituents should be regarded as type 1<br />
substances. The same substance may belong to different classes in<br />
different distribution systems.<br />
7.3.3 Sample collection<br />
The location, frequency and time of sampling is strongly<br />
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