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rapid assessment of drinking-water quality in the republic of tajikistan

rapid assessment of drinking-water quality in the republic of tajikistan

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Table 3.11 Compliance with WHO suggested value for conductivity<br />

a<br />

Broad area a Utility piped supplies Protected spr<strong>in</strong>gs Total<br />

No. <strong>of</strong><br />

samples<br />

Compliance<br />

(%)<br />

No. <strong>of</strong><br />

samples<br />

Compliance<br />

(%)<br />

No. <strong>of</strong><br />

samples<br />

Compliance<br />

(%)<br />

RRS & Dushanbe 506 99.6 108 99.1 614 99.5<br />

Khatlon 346 100.0 103 100.0 449 100.0<br />

Sughd 410 81.5 60 95.0 470 83.2<br />

GBAO 24 100.0 63 100.0 87 100.0<br />

National 1 286 93.9 334 98.8 1 620 94.9<br />

GBAO = Gorno-Badakhshan Autonomous Oblast. RRS = rayons under direct <strong>republic</strong>an subord<strong>in</strong>ation.<br />

Nationally, only 5.1% <strong>of</strong> all <strong>water</strong> samples tested were not <strong>in</strong> compliance with <strong>the</strong> WHO suggested<br />

value for electrical conductivity (1.4 µS/cm) (Table 3.11). Total noncompliance was greatest <strong>in</strong> <strong>the</strong><br />

Sughd region (16.8%), which may be expla<strong>in</strong>ed by <strong>the</strong> “hard” <strong>water</strong> <strong>in</strong> <strong>the</strong> area (i.e. <strong>water</strong> with high<br />

concentrations <strong>of</strong> salts, such as calcium and magnesium).<br />

3.4 Overall compliance<br />

The RADWQ project def<strong>in</strong>ed overall compliance as <strong>the</strong> proportion <strong>of</strong> <strong>water</strong> samples that met <strong>the</strong><br />

WHO guidel<strong>in</strong>e values and national standards for <strong>the</strong>rmotolerant coliform count, and for chemicals<br />

such as arsenic, fluoride and nitrate, which are <strong>of</strong> public health imporftance. In <strong>the</strong> case <strong>of</strong> Tajikistan,<br />

however, overall compliance was synonymous with compliance for <strong>the</strong>rmotolerant coliforms and<br />

fluoride, as all <strong>water</strong> supplies <strong>in</strong> <strong>the</strong> RADWQ survey were <strong>in</strong> compliance with <strong>the</strong> national standards<br />

or WHO guidel<strong>in</strong>e values for nitrate and arsenic (Table 3.6, Table 3.8).<br />

Of <strong>the</strong> 1620 <strong>water</strong> supplies tested, 86.9% and 65.9% were <strong>in</strong> overall compliance with WHO guidel<strong>in</strong>e<br />

values and national standards, respectively (Table 3.12). The difference <strong>in</strong> overall compliance levels<br />

is expla<strong>in</strong>ed by <strong>the</strong> fact that <strong>the</strong> national standard for fluoride is less than half <strong>of</strong> <strong>the</strong> WHO guidel<strong>in</strong>e<br />

value. In <strong>the</strong> broad areas or oblasts, compliance with <strong>the</strong> WHO guidel<strong>in</strong>e values was greatest for<br />

<strong>water</strong> supplies <strong>in</strong> RRS and Dushanbe (92.0%) and least for those <strong>in</strong> GBAO (74.7%).<br />

3.5 Sanitary risk factors<br />

In addition to <strong>the</strong> analysis <strong>of</strong> microbial, chemical and aes<strong>the</strong>tic parameters, sanitary <strong>in</strong>spections were<br />

carried out at all supply po<strong>in</strong>ts visited dur<strong>in</strong>g <strong>the</strong> RADWQ study. Sanitary <strong>in</strong>spections are visual<br />

<strong>assessment</strong>s <strong>of</strong> <strong>the</strong> <strong>in</strong>frastructure and environment surround<strong>in</strong>g a <strong>water</strong> supply, tak<strong>in</strong>g <strong>in</strong>to account <strong>the</strong><br />

condition, devices and practices <strong>in</strong> <strong>the</strong> <strong>water</strong>-supply system that pose an actual or potential danger to<br />

<strong>dr<strong>in</strong>k<strong>in</strong>g</strong>-<strong>water</strong> <strong>quality</strong> and thus to <strong>the</strong> health and well-be<strong>in</strong>g <strong>of</strong> <strong>the</strong> consumers. The most effective<br />

way to undertake sanitary <strong>in</strong>spections is a semiquantitative standardized approach us<strong>in</strong>g logical<br />

questions and a simple scor<strong>in</strong>g system. Sanitary <strong>in</strong>spections are complementary to a <strong>water</strong> <strong>quality</strong><br />

analysis and <strong>the</strong>re is an <strong>in</strong>crease <strong>in</strong> <strong>the</strong> power <strong>of</strong> analysis when both types <strong>of</strong> data are available.<br />

Sanitary <strong>in</strong>spections also provide a longer-term perspective on <strong>the</strong> risks <strong>of</strong> microbiological<br />

contam<strong>in</strong>ation, and thus complements <strong>the</strong> “snapshot” <strong>water</strong> <strong>quality</strong> analysis.<br />

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