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Salinity Intrusion and Seasonal Water Quality Variations in the Tidal ...

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Nutrients are generally more abundant <strong>in</strong> river water than <strong>in</strong> sea water due partly to<br />

<strong>the</strong>ir removal by organisms from oceanic water <strong>and</strong> partly to <strong>the</strong> <strong>in</strong>put to rivers from<br />

pollutants <strong>and</strong> l<strong>and</strong> wea<strong>the</strong>r<strong>in</strong>g. Rivers serve as nutrient sources for estuaries <strong>and</strong> here<br />

biogenic removal is often found. For phytoplankton blooms to occur <strong>in</strong> estuaries <strong>the</strong><br />

surface water must be fairly clear so that <strong>the</strong> light necessary for photosyn<strong>the</strong>sis can pass<br />

though, large amounts of suspended sediments tend to <strong>in</strong>hibit organic growth. In<br />

temperate estuaries blooms are seasonal occurr<strong>in</strong>g <strong>in</strong> <strong>the</strong> spr<strong>in</strong>g <strong>and</strong> summer when <strong>the</strong>re is<br />

more light <strong>and</strong> wanner water temperatures. Ano<strong>the</strong>r factor that <strong>in</strong>fluences bloom <strong>in</strong> an<br />

estuary is flush<strong>in</strong>g time for fresh water. Longer flush<strong>in</strong>g time favors greater growth <strong>and</strong><br />

more biogenic nutrient removal. The flush<strong>in</strong>g time for fresh, nutrient rich water is longer<br />

<strong>in</strong> a wellmixed estuary than <strong>in</strong> a stratified estuary where <strong>the</strong> river water rapidly flows out<br />

<strong>in</strong> <strong>the</strong> surface layer. Krone <strong>and</strong> Bemer (1981) found that <strong>the</strong>re was a considerable flux<br />

from sediments to <strong>the</strong> water column ofdissolved P04 which had been adsorbed on ferric<br />

oxyhydroxides. This P release accompanied <strong>the</strong> reduction of<strong>the</strong> iron m<strong>in</strong>erals by H2S <strong>in</strong><br />

anoxic portionsof<strong>the</strong> sediment. Thus <strong>the</strong> flux ofP04 from <strong>the</strong> bottom sediment was due<br />

to both <strong>the</strong> microbial breakdown of organic P <strong>and</strong> <strong>the</strong> release of adsorbed <strong>in</strong>organic P.<br />

Some planktonic organisms remove silica from solution as well as P <strong>and</strong> N. Diatoms use<br />

Si <strong>in</strong> form<strong>in</strong>g <strong>the</strong>ir opal<strong>in</strong>e-silica shells. Silica removal associated with diatom blooms<br />

has been observed <strong>in</strong> <strong>the</strong> Amazon River estuary (Milliman & Boyle 1975). However<br />

because of <strong>the</strong> redissolution of diatom shells on <strong>the</strong> bottom <strong>the</strong> net removal of dissolved<br />

river silica by deposition ofbiogenic silica <strong>in</strong> natural estuar<strong>in</strong>e sediments is probably far<br />

less than 20% <strong>and</strong> <strong>in</strong> some well mixed estuaries at least silica is conservative. In addition<br />

.to dissolved nutrientscarried <strong>in</strong> fresh water river run off<strong>in</strong>to estuaries, <strong>the</strong>re are a number<br />

ofo<strong>the</strong>r nutrient sources for phytoplankton <strong>in</strong> <strong>the</strong> surface water (Bemer <strong>and</strong> Bemer, 1987)<br />

20

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