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Rapid assessment of drinking-water quality in the - WHO/UNICEF ...

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3.4 Overall compliance<br />

The RADWQ survey results were consistent with those <strong>of</strong> <strong>the</strong> Jordanian national surveillance system,<br />

and confirmed that <strong>dr<strong>in</strong>k<strong>in</strong>g</strong>-<strong>water</strong> <strong>quality</strong> was generally high <strong>in</strong> <strong>the</strong> distribution network. Overall<br />

compliance with <strong>WHO</strong> guidel<strong>in</strong>e values and national standards was 97.8% (<strong>in</strong>clud<strong>in</strong>g chemicals<br />

relevant to health), but this <strong>in</strong>creased to 99.9% if <strong>the</strong> Jordanian maximum permitted limits were used<br />

as references (Table 3.9).<br />

Table 3.9<br />

Broad area<br />

Overall compliance <strong>of</strong> Jordanian utility piped <strong>water</strong> supplies<br />

with <strong>WHO</strong> guidel<strong>in</strong>e values and national standards a<br />

Overall compliance<br />

n<br />

Compliance with<br />

<strong>WHO</strong> GVs (%)<br />

Compliance with<br />

allowed national<br />

standards (%)<br />

Compliance with<br />

maximum national<br />

standards (%)<br />

Amman 611 94.4 94.4 100.0<br />

Albalqa 146 100.0 100.0 100.0<br />

Alzarqa 244 99.6 99.6 100.0<br />

Madaba 25 100.0 100.0 100.0<br />

Irbed 270 100.0 100.0 100.0<br />

Almafraq 73 98.6 98.6 98.6<br />

Jarash 73 100.0 100.0 100.0<br />

Ajloun 49 93.9 93.9 100.0<br />

Alkarak 73 100.0 100.0 100.0<br />

Altafiela 25 100.0 100.0 100.0<br />

Ma’an 25 100.0 100.0 100.0<br />

Aqaba 25 100.0 100.0 100.0<br />

National 1 639 97.8 97.8 99.9<br />

a<br />

Compliance was calculated for <strong>the</strong>rmotolerant coliforms, arsenic, fluoride and nitrate. n = total number <strong>of</strong> samples assessed. <strong>WHO</strong><br />

GVs = <strong>WHO</strong> guidel<strong>in</strong>e values.<br />

3.5 Sanitary risk factors<br />

The sanitary risk <strong>in</strong>spections (Tables 3.10–3.12) showed that <strong>the</strong> most common risk factors for <strong>the</strong><br />

<strong>water</strong> supplies <strong>in</strong>cluded:<br />

<br />

<br />

<br />

Sewer l<strong>in</strong>es close to <strong>the</strong> <strong>water</strong> distribution network. This is frequently unavoidable, especially <strong>in</strong><br />

urban sett<strong>in</strong>gs.<br />

A failure to ma<strong>in</strong>ta<strong>in</strong> household storage tanks. Water storage tanks are common <strong>in</strong> all <strong>water</strong>scarce<br />

countries, <strong>in</strong>clud<strong>in</strong>g Jordan, where <strong>in</strong>termittent <strong>water</strong> supplies have <strong>in</strong>creased <strong>the</strong> need for<br />

storage. Poor ma<strong>in</strong>tenance <strong>of</strong> <strong>the</strong> tanks <strong>in</strong>creases <strong>the</strong> risk that <strong>water</strong> will become contam<strong>in</strong>ated,<br />

which <strong>in</strong> turn would jeopardize <strong>the</strong> health <strong>of</strong> <strong>in</strong>dividuals us<strong>in</strong>g <strong>the</strong> household <strong>water</strong> supply.<br />

Old pipes <strong>in</strong> <strong>the</strong> <strong>water</strong> distribution network. Many pipes <strong>in</strong> <strong>the</strong> network are rusted and leak, and<br />

need to be replaced to reduce losses and breakdowns <strong>in</strong> <strong>the</strong> supply system, as well as to prevent<br />

iron contam<strong>in</strong>ation <strong>of</strong> <strong>the</strong> piped <strong>water</strong> (Table 3.7).<br />

21

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