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MAP Technical Reports Series No. 106 UNEP

MAP Technical Reports Series No. 106 UNEP

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- 145 -<br />

- Protection of human health;<br />

- Protection of marine life and its environment;<br />

- Assessment of levels and trends.<br />

9.1 Monitoring of eutrophication<br />

In the pelagic domain, monitoring of eutrophication should be relatively straightforward.<br />

The only difficulty may be in finding the most cost-effective strategy. Two major strategies are<br />

available, namely remote sensing and direct measurements in the field.<br />

a) Remote sensing<br />

Remote sensing may be successfully employed when eutrophication extends over<br />

large areas such as the northern Adriatic Sea or the Aegean Sea. Although the satellite operated<br />

Coastal Zone Colour Scanner (CZCS) has been terminated, the possibility of using LANDSAT's<br />

thematic mapper or SPOT's sensors still exists: their low sensitivity is overcome by the high<br />

chlorophyll content of the upper layers of the eutrophic areas. Another possibility is the use of<br />

airborne spectral scanners or even aerial photographs to monitor the extent of eutrophication<br />

(Zevenboom, 1989; Zevenboom et al., 1989; Zevenboom et al., 1990).<br />

b) Direct measurements made in the field<br />

<strong>No</strong> single analytical tool is adequate to measure the degree of eutrophication of a given<br />

body of water. Instead, most experts believe the best approach is to measure many different<br />

parameters and to synthesize the results into a general model providing an overall, somewhat<br />

integrated degree of eutrophication for the water. Unless proper selection of the parameters to<br />

be measured is made, the amount of work required to assess the extent and intensity of<br />

eutrophication may be rather costly.<br />

Much in the same way that the information provided by remote sensors on the surface<br />

layer is used to evaluate the entire water column, direct measurement of surface variables may<br />

be used to infer what is happening at deeper layers. However, subsurface and near bottom<br />

waters should also be monitored, particularly in relation to monitoring of the benthic domain.<br />

Direct observations by SCUBA or underwater TV can also be very useful in detecting<br />

changes in benthic populations, especially in the early stages of deterioration.<br />

9.2 Major variables to be sampled<br />

Various parameters such as suspended solids, light penetration, chlorophyll, dissolved<br />

oxygen, nutrients, organic matter, etc. may be determined either at the surface or at various<br />

depths.<br />

If only limited means are available, determination of those parameters that synthesize<br />

the most information should be retained. Chlorophyll determinations for example, although not<br />

very precise representations of the system, are data which provide a great deal of information.<br />

Reliable data on nutrients are extremely useful indicators of potential eutrophication. Turbidity<br />

and water colour may also be a good measure of eutrophication, except near the mouths of<br />

rivers where inert suspended solids may be extremely abundant. Dissolved oxygen is one<br />

parameter that integrates much information on the processes involved in eutrophication,<br />

provided it is measured near the bottom or, at least, below the euphotic zone where an oxycline<br />

usually appears.

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