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Hydro-ecological relations in the Delta Waters

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In Tahle 3 a tentative carbon budget of <strong>the</strong> 4 sal<strong>in</strong>e <strong>Delta</strong> <strong>Waters</strong> Is<br />

given. as an expression of <strong>the</strong> transfotmation of <strong>in</strong>organk nutrients<br />

<strong>in</strong>to organic carbon of primary pxohcers. Table 3 does not girre<br />

<strong>in</strong>fetmatioa about <strong>the</strong> turnover of nutrients between <strong>the</strong> successive<br />

generations of plants. Notwithstazdlng <strong>the</strong> large dlfkrences <strong>in</strong><br />

nutrient loadjags of <strong>the</strong> separate waters, primasy production of<br />

phytoplankton only shows a difference of a factor 2 between <strong>the</strong> light<br />

-2 -1<br />

limited, tUrbid Westerschelde (l25 g C m y ) and <strong>the</strong> clear,<br />

-2 -1<br />

presumably not nutrient limited Veerse Meer (249 g C m y ). The<br />

Oosterseblde and Orevel<strong>in</strong>gemseer hold <strong>in</strong>t-diate positions.<br />

Production of microphytobent!hos (benthic diatoms, gzeen algae etc.) is<br />

roughly one third of <strong>the</strong> production of phytoplankton. In <strong>the</strong><br />

Westerschelde estuary, however, <strong>the</strong> relative skre of benthic<br />

microphytes is considerahLy higher, based on P/B ratio's derived from<br />

high biomass data, taken on <strong>in</strong>tertidal flats (personal eonrmnaicatFoa<br />

D.J.<br />

de Jong, DW).<br />

OwFng to <strong>the</strong> relatrvely large surface area of supratidal wetlands, <strong>the</strong><br />

contributivn of ahoae-ground peimarp production to <strong>the</strong> carbon budget <strong>in</strong><br />

-9 -1<br />

Westersehelde estusry (60 g C m y is about 20%. The larger part of<br />

<strong>the</strong> saltmarsh plants is produced <strong>in</strong> <strong>the</strong> eastern secrion of <strong>the</strong><br />

Westerschelde estuary (Verdrmken Land van Saeft<strong>in</strong>ghe) and is not<br />

transpwrted over <strong>the</strong> entire estuary, In contrast with <strong>the</strong><br />

Westerschelde, <strong>the</strong> Oosterachelde salt marshes pay only an <strong>in</strong>significant<br />

contrLhution (lees thau 5Z) to <strong>the</strong> system metabolism of <strong>the</strong> entire<br />

estuary.<br />

Maarophytes grow<strong>in</strong>g on bard substretes (i.e. seaweeds attached to<br />

sewalls and stone-clad dilres) have only a m<strong>in</strong>or contriburian to <strong>the</strong><br />

carbon budgets of <strong>the</strong> entire water hobtes, notwithstandiag <strong>the</strong>ir high<br />

production per square metre habitat.<br />

Eigh turbidity and exposure to waves and tides prevents <strong>the</strong> potential<br />

sediment habitats <strong>in</strong> tke Weatersehelde egtuary from be<strong>in</strong>g <strong>in</strong>vaded by<br />

macrephytes, The Oosterschelde estuary has only local growth of<br />

laactophytes an sediment substrams <strong>in</strong> sbeltered regions (Zandkteek,<br />

Ktabbenkreek, eastern part). In <strong>the</strong> sheltered, stagnant lagoons

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