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

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eaches 15 g/kg. Work by Boyle, Edmond & Sholkovitz (1977) suggests that for iron<br />

removal <strong>the</strong> pH change is less important than <strong>the</strong> mix<strong>in</strong>g of sea water electrolytes with<br />

fresh water. The mar<strong>in</strong>e cations Ca++, Mg++ <strong>and</strong> Na+ neutralize <strong>the</strong> negative charge of<br />

river borne substances <strong>and</strong> cause flocculation <strong>and</strong> coagulation. Sholkovitz (1976) <strong>in</strong><br />

laboratory experiments found that <strong>the</strong> solubility of <strong>the</strong> <strong>in</strong>organic constituents <strong>in</strong> river<br />

water <strong>and</strong> <strong>the</strong>ir flocculation <strong>in</strong> sea water are due to <strong>the</strong>ir association with organic matter.<br />

The mechanism suggested is <strong>the</strong> flocculation ofmixed iron oxide -organic matter colloids<br />

due to <strong>the</strong> neutralization by sea water cations of<strong>the</strong> negative colloid charges.<br />

Several recent review papers (Down<strong>in</strong>g 1997, Smith 1998, Smith et al. 1999, Conley<br />

2000 & <strong>the</strong> NRC, 2000) concluded that <strong>the</strong> major nutrients caus<strong>in</strong>g over-enrichment<br />

problems <strong>in</strong> estuaries are N <strong>and</strong> P. A schematic ofphytoplankton <strong>and</strong> nutrient circulation<br />

isshown <strong>in</strong> figure 1.7. P limits primary production <strong>in</strong> some tropical near shore habitats,<br />

although <strong>the</strong> study of<strong>the</strong>se systems is limited (Howarth et al., 1995). Often <strong>the</strong> addition<br />

of both N <strong>and</strong> P will elicit greater phytoplankton biomass stimulation than <strong>the</strong> sum of<br />

both nutrients added separately (Fisher et al., 1992). There are reported cases where both<br />

N<strong>and</strong> P are required to elicit a phytoplankton bio mass production response <strong>in</strong> estuaries<br />

(Flemer et al., 1998), suggest<strong>in</strong>g that N <strong>and</strong> P supply rates are equally limit<strong>in</strong>g (Figure<br />

1.8). <strong>Tidal</strong> fresh <strong>and</strong> brackish waters <strong>in</strong> many estuaries are more light limited than higher<br />

sal<strong>in</strong>e waters (Flemer, 1970, S<strong>in</strong> et al. 1999). As fresh water flows seaward, processes<br />

operate to modify nutrient stoichiometry (e.g., sedimentation of P-absorbed particles,<br />

denitrification, <strong>and</strong> differential microbial decomposition). Experiments showed that P<br />

addition was not stimulatory, but N or N+P caused large <strong>in</strong>creases <strong>in</strong> <strong>the</strong> net primary<br />

production (Oviatt et al. 1995). In a 17-year field experiment carried out <strong>in</strong><br />

Himmerfjarden Estuary south of Stockholm, Sweden (Elmgren & Larsson, 1997). The<br />

16

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