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Environmental Health Criteria 214

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HUMAN EXPOSURE ASSESSMENT<br />

Fluosilicic acid Sulfur dioxide<br />

Potassium permanganate Sulfuric acid<br />

Sodium aluminate Tetrasodium pyrophosphate<br />

Distribution networks constitute another potential source of<br />

chemical contaminants in drinking-water. The materials used in<br />

distribution networks may serve as a pollutant source by leaching into<br />

the water over time. Some examples include lead from lead-containing<br />

solders and pipes, asbestos fibres from the surface of asbestos-cement<br />

pipes and cadmium from metallic fittings. Other contaminants include<br />

PAHs from coal-tar-based sealants, plasticizers, stabilizers and<br />

solvents used in the manufacture of plastic pipes.<br />

Water sources experience considerable variations in quality over<br />

time and geographic location. The quality of river water may change<br />

rapidly during heavy storms, melting snows and droughts. The quality<br />

of water in lakes may be affected by climate, season, location or some<br />

combination thereof. Groundwater historically has enjoyed the most<br />

consistent quality, with relatively constant composition. However, the<br />

vulnerability of groundwater to contamination is gaining widespread<br />

attention, with particular emphasis on synthetic organic substances,<br />

surface impoundments, landfills, agriculture, leaks and spills, land<br />

disposal of wastewater, septic tanks and the petroleum/mining<br />

production industries.<br />

7.3.2 Water quality monitoring strategies<br />

There are numerous considerations in the design of a monitoring<br />

and measurement strategy for water quality assessment. The<br />

International Organization for Standardization (ISO) has provided<br />

guidance on a number of issues related to sampling strategies for<br />

water quality assessment (Table 27). A sound monitoring methodology<br />

must be followed by the appropriate sample storage and transportation,<br />

to minimize changes in sample composition. Losses can occur due to<br />

several physical, chemical and biological changes, such as ion<br />

exchange, adsorption with the container material, oxidation to<br />

precipitated forms, loss of volatiles to the vapour space and<br />

biochemical conversions. For contaminants at low source<br />

concentrations, these changes can introduce significant errors in the<br />

analytical results.<br />

Table 27. ISO standards of water quality giving guidance on sampling<br />

ISO standard Title (water quality)<br />

number<br />

5667-1: 1980 Sampling - Part 1: Guidance on the design of sampling<br />

programmes<br />

5667-2: 1982 Sampling - Part 2: Guidance on sampling techniques<br />

5667-3: 1985 Sampling - Part 3: Guidance on the preservation and<br />

handling of samples<br />

5667-4: 1987 Sampling - Part 4: Guidance on sampling from lakes,<br />

natural and man-made<br />

5667-5: 1985 Sampling - Part 5: Guidance on sampling of<br />

drinking-water and water used for food and beverage<br />

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

Page 129 of 284<br />

6/1/2007

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