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MAP Technical Reports Series No. 106 UNEP

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- 153 -<br />

presents also a risk, particularly in warmer climates, because of its invasive potential; indeed,<br />

water lilies have become a pest in water courses, lagoons and reservoirs throughout the world.<br />

In fertirrigation, by contrast, partly purified water is returned to agricultural lands and<br />

reused (Rismal, personal communication). Besides watering the soil, fertirrigation serves to<br />

recycle nitrogen, phosphorus and organic matter in a cultivation environment (accordingly,<br />

elimination of nutrients from sewage in this instance would be illogical and counterproductive).<br />

Naturally, the risk of contamination from bacteria or other pathogens (viruses, fungi) must dictate<br />

caution in the use of any such procedure for crops like salad and fruit; on the other hand there<br />

is practically no health hazard in applying fertirrigation for others crops destined to be stored and<br />

processed (cereals in general, sugar beet, etc.).<br />

10.3 Other courses of action<br />

Alternatively to full sewage treatment, lagooning and otherwise, there is the option of<br />

discharging urban and/or industrial sewage effluents by way of pipelines laid on the sea bed out<br />

to deeper offshore waters. This arrangement is not recommended for shallow inshore waters<br />

and sheltered bays, where the discharged waste can resurface, or accumulate progressively<br />

by reason of insufficient dispersion. A further often used but questionable procedure is to<br />

transport solid and/or liquid waste by tanker out into the oceans, far from land, where the risk to<br />

contaminate the coastline appears attenuated.<br />

10.4 Monitoring programmes<br />

As an essential complement to interventions, monitoring programmes should be<br />

established.<br />

Monitoring programmes are in fact an essential prerequisite for the assessment and<br />

the control of the evolution of phenomena as well as of assessment of the effectiveness of the<br />

interventions.<br />

For their establishment the following point should be considered:<br />

- Monitoring objectives must be reformulated in a more coherent way in order to<br />

make planning more comprehensible and effective (Reuss, 1990);<br />

- It is necessary to reaffirm the crucial role of the monitoring of pollution sources<br />

(UNESCO, 1988);<br />

- The first essential phase is to establish beyond the shadow of doubt the baseline<br />

contamination levels, before establishing permanent programmes for certain areas<br />

of special concern;<br />

- A biological effects monitoring programme must be devised and implemented<br />

within the MED POL framework (<strong>UNEP</strong>, 1992);<br />

- The quality assurance programme for results must not only be continued but<br />

reinforced as well;<br />

- At the same time, all research efforts which might add to the general knowledge<br />

of the marine environment must be encouraged in order to promote the<br />

optimisation of monitoring programmes.

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