Hydro-ecological relations in the Delta Waters
Hydro-ecological relations in the Delta Waters Hydro-ecological relations in the Delta Waters
and only l-2% cows frm the aive Scheldt (Pig. 4). The Scheldt has an averege discharge of only 112 m's-' CVe Ruyter,, et al, 1987) which is only 4% of rho Rhiae-Meuse discharge. Total nitrogen Totai phosphorus ennel 37 % Rhine / Meme 57 % Rhine Meuse 16 % Figure 4 The ahares of Rhine-Ueuse load, Chamel load aqd Scheldt load in the rota1 eanceqtratiop aP N and F Dutch cpastal waters (Van Buuren, 1988). Only a veky small pereentzse of the original We-Mewe water reaches directly (or indirectly via the North Sea) the estuariee and brackish Lagoons in the South-West Netherlands. Especially the construction of the Volkerekdam in 1969 (Fig. 1) deprived the saline waters of the direct influx af fresh river-w-ater. me Oosterse.helde, Grevtrlingenmeer and Veezse Meet are mainly loaded with nutrients from dSSfuse Bourees such W apicrienral run-off, treated vasce water and drainwe canals. The saline water bodks in the South-KeSt Netherlands have been separated spatiallq fcompartmentalization) ovlng to the Delta Works. Cmseguentlg each of these waters has its oun eutrophicatim history and its orm sperffic ehareteristics, excluding, an integrated epproach to manage eh= nutrisnt 10.oading~ B$ these syatema. Table 1 sumeariaes a hlmmer of ~paLem peameters. The residence tines of the uater masses Zu tke stagnant, nen tidal OreVdingewer and "ieerse Beer are long, cwmpared to ch8 saate cha+ac+etistic in the tihl
estuaries. The net freshwater load directly from the rivers Rhine and Mwse is extremelp small (1% of the discharge). Tba Veerse Meer lagoon eaperiences almost permanent stratiEicaeion, whereas the Oreveliugenmeer has only a few deep channels, stratified during summer. The Westerschelde and Oostersehelde estuaries are completely &ed tidal systems. Table 1 System parameters of the saline waters in the Swth-West Netherlands, derived from Wollast, 1988, and Bokhorst, 1988, for the Westerschelde; Projectgroep Balans, 191d8, and Wetsteyn and Peperzak, 1988, for the Oosferschelde; Nienhuis, 1985, and De Vries, et al, 1988, for the Grevelingen: Daemen, 1985. and Stronkhorst. et al, 1985. for the Veerse Meer. Load = direet water load from Rhine-Meuse. reddenGB time (4) bad h%-1, tides stFati£icatlan extinct-. (m-') The Westerschelde is extremely turbid (extinction coefficient 0.5-7) and the Grevelfngenmeor contains very clear water (extinction coefficient 0.2- 0.5). with the Oosterschelde and Veerse Meer in between. The range in nutrient concentrations in the saline Delta waters differs greatly (lfig. 5). The Oostersehelde and Crevelfngen reach only seldom for N. P and Si; nutrient values frequently values above 1 mg I-' approach zero concantratione during heavy blooms of phytoplankton. The Veersa Meet has higher maximum values for N and Si, but depletion occurs during the growing season. The Westerschelde has far out the
- Page 11 and 12: This approach will put to use what
- Page 13 and 14: Estuaries that have not been influe
- Page 15 and 16: 2 CHIWGES XN TEE DELTA The Delta ar
- Page 17 and 18: area decltned cnnside~ably, leadins
- Page 19 and 20: Plan, then it is apparent tbt the s
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- Page 25 and 26: Figsrlre 7 Changes in the cadrnrum
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- Page 29 and 30: elationships between different spec
- Page 31 and 32: Bio-essay Weriments with polluted s
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- Page 35 and 36: ShLOUONS, W. and BYSINK, W.D., 1981
- Page 37 and 38: are taken. The first year after the
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- Page 43 and 44: , 0.66 m 0,s - 0.02 1989 I 0.86 - 0
- Page 45 and 46: Table 3 Eutrophication of the Volke
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- Page 68 and 69: model calculations reveal that a ni
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- Page 84 and 85: osi* rn@8IOIP m .SL 4 Has F~~ULB 3
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- Page 90 and 91: aq811~33a.e~ pue 3pTatlJS uxaJsafi
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- Page 106 and 107: wind erasson, desaliuation, aeratio
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estuaries. The net freshwater load directly from <strong>the</strong> rivers Rh<strong>in</strong>e and<br />
Mwse is extremelp small (1% of <strong>the</strong> discharge). Tba Veerse Meer lagoon<br />
eaperiences almost permanent stratiEicaeion, whereas <strong>the</strong><br />
Oreveliugenmeer has only a few deep channels, stratified dur<strong>in</strong>g summer.<br />
The Westerschelde and Oostersehelde estuaries are completely &ed<br />
tidal systems.<br />
Table 1<br />
System parameters of <strong>the</strong> sal<strong>in</strong>e waters <strong>in</strong> <strong>the</strong> Swth-West<br />
Ne<strong>the</strong>rlands, derived from Wollast, 1988, and Bokhorst, 1988,<br />
for <strong>the</strong> Westerschelde; Projectgroep Balans, 191d8, and<br />
Wetsteyn and Peperzak, 1988, for <strong>the</strong> Oosferschelde; Nienhuis,<br />
1985, and De Vries, et al, 1988, for <strong>the</strong> Grevel<strong>in</strong>gen: Daemen,<br />
1985. and Stronkhorst. et al, 1985. for <strong>the</strong> Veerse Meer. Load<br />
= direet water load from Rh<strong>in</strong>e-Meuse.<br />
reddenGB time (4)<br />
bad h%-1,<br />
tides<br />
stFati£icatlan<br />
ext<strong>in</strong>ct-.<br />
(m-')<br />
The Westerschelde is extremely turbid (ext<strong>in</strong>ction coefficient 0.5-7)<br />
and <strong>the</strong> Grevelfngenmeor conta<strong>in</strong>s very clear water (ext<strong>in</strong>ction<br />
coefficient 0.2- 0.5). with <strong>the</strong> Oosterschelde and Veerse Meer <strong>in</strong><br />
between.<br />
The range <strong>in</strong> nutrient concentrations <strong>in</strong> <strong>the</strong> sal<strong>in</strong>e <strong>Delta</strong> waters differs<br />
greatly (lfig. 5). The Oostersehelde and Crevelfngen reach only seldom<br />
for N. P and Si; nutrient values frequently<br />
values above 1 mg I-'<br />
approach zero concantratione dur<strong>in</strong>g heavy blooms of phytoplankton.<br />
The Veersa Meet has higher maximum values for N and Si, but depletion<br />
occurs dur<strong>in</strong>g <strong>the</strong> grow<strong>in</strong>g season. The Westerschelde has far out <strong>the</strong>