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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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

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>

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