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Hydro-ecological relations in the Delta Waters

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prevention measures are desirable here to prevent <strong>the</strong> diffusion of<br />

pollution to adjacent waters.<br />

5 EFFECTS ON THE ENVIRONMENT<br />

Relatively little is knm about rhe impact polluted beds have on<br />

aquatic ecosystems, partly because <strong>the</strong>se areas are not directly<br />

obsesvable. Future research strateges will <strong>the</strong>refore be ma<strong>in</strong>ly<br />

concerned vith address<strong>in</strong>g <strong>the</strong>se shorreom<strong>in</strong>gs. There are, however,<br />

various <strong>in</strong>dications that pollution m y be a hazard to public health md<br />

may <strong>in</strong>fluence <strong>the</strong> function<strong>in</strong>g of aquatic ecosystems. The presence of<br />

heavy metals ad organic micropollutants <strong>in</strong> benthic organisms is<br />

clearlybigher <strong>in</strong> polluted areas rhan is less wntam<strong>in</strong>ated areas. This<br />

has been verified for various organisms such as Dreissena palymol-pha.<br />

Tubifex spec., miromid larvae and also zooplankton (Urk, 1987). There<br />

are, of course, specific differences between <strong>in</strong>dividual species with<br />

regard to <strong>the</strong> type and mwunt of heavy metals found. In molluscs, for<br />

example, contam<strong>in</strong>ation levels are Ngher <strong>in</strong> species that live ia <strong>the</strong><br />

top layer of sediment than surface dwellers.<br />

Kelatively low levels of p@llution are found <strong>in</strong> <strong>the</strong> eastern part of <strong>the</strong><br />

Xar<strong>in</strong>$vliet bas<strong>in</strong> (Hollands Diep), whereas higher levels can be<br />

detected <strong>in</strong> <strong>the</strong> western part of <strong>the</strong> Bar<strong>in</strong>gvliet. This is a coneequence<br />

of <strong>the</strong> sedimentation process, which has <strong>in</strong>fluenced <strong>the</strong> quality ef river<br />

sediments <strong>in</strong> <strong>the</strong> areas, as outl<strong>in</strong>ed <strong>in</strong> <strong>the</strong> previous section. These<br />

gradients are also reflected <strong>in</strong> <strong>the</strong> concentration of contam<strong>in</strong>ants found<br />

<strong>in</strong> specific organisms. Xigure 8 shows how <strong>the</strong> cadmium content 3s <strong>the</strong><br />

gills of Anadonta anat<strong>in</strong>a varies at different locations. The levels <strong>in</strong><br />

<strong>the</strong> western part of <strong>the</strong> bas<strong>in</strong> (Har<strong>in</strong>gvliet) are two to three t h e<br />

higher than those found <strong>in</strong> <strong>the</strong> eastern part (ILollands Diep) . Simular<br />

problems have been encountered with orgsnie micropollutante. For<br />

<strong>in</strong>stance, from 1977 to 1985, PCB levels <strong>in</strong> eels from <strong>the</strong> different<br />

surface waters <strong>in</strong> <strong>the</strong> We<strong>the</strong>rlands were monitored bg <strong>the</strong> State Institute<br />

for Fishery Research CRIVO). At <strong>the</strong> end of <strong>the</strong> seventies PCB levels <strong>in</strong><br />

eels from <strong>the</strong> Bar<strong>in</strong>gvlieL bas<strong>in</strong> were extremely bigh, prohahle as a<br />

result of local discharges, some of <strong>the</strong>m illegal. S<strong>in</strong>ce tbis time, <strong>the</strong>

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