Hydro-ecological relations in the Delta Waters
Hydro-ecological relations in the Delta Waters
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>