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<br /> <br />some extent. <br />!rs also is <br />~ment. Changes <br />!s in suspended <br />:ion, bed-load <br /> <br />I. <br /> <br />by modifying <br />.reas with high <br />high rates of <br />c organisms by <br />ion of the <br />levels often <br />out of the <br />es, especially <br />sely affected <br />tended periods <br />diment-induced <br />Recovery by <br />resumption of <br />ow the habitat <br />Lfe history of <br />, and the mode <br />downstream <br />;;ubstrate, and <br /> <br />, increasing <br />and modifying <br />lppear to be <br />, reduce their <br />.ssues. Fish <br />lsed sediment <br />to sand-size <br />some groups, <br />rom reducing <br />of oxygen to <br />icularly the <br />1 of suitable <br />ations. The <br />have special, <br />turbidity of <br /> <br />White River <br />o predict the <br />istics. The <br />'f explain the <br />i, silt load, <br />evident that <br />lW available <br /> <br />light at the substrate (Figure 5). <br />easily quantified. <br /> <br />Such results are <br /> <br />Because most aquatic organisms are poikilothermic, <br />temperature is an essential parameter to be measured. <br />Wlosinski (1979) indicated in the validation of his Desert <br />Stream Ecosystem model (DSEM) that temperature was the <br />most important physical parameter affecting the community <br />metabolism. Experiments conducted in the White River <br />indicate that temperature is highly significant in <br />regulating decomposition (Figure 8). <br /> <br />40 <br />z <br />o <br />i=3 <br />UJ <br />o <br />c. 20 <br />:E <br />o <br />~ 10 <br />o <br />* <br /> <br /> <br />Y: 4.74 + 0.0748x <br />R2: .91 <br />N:52 <br /> <br />o <br /> <br /> <br />100 200 300 400 500 <br />DEGREE DAYS <br /> <br />Figure 8. Leaf decomposition rates as <br />percent weight loss. Studies conducted <br />in the White River (October, 1981- <br />April, 198Z). <br /> <br />Fluvial Characteristics <br /> <br />The second major set of characteristics needed to <br />define the abiotic structure of the White River is the <br />fluvial characteristics (Table II). The chemical load of <br />the river is derived from atmospheric precipitation, from <br />mineral matter dissolved by the surface and ground waters, <br />and from atmospheric gases (previously described in Table <br />I, as external inputs). <br /> <br />Gibbs (1970) has distinguished three basic origins <br />for dissolved substances in surface waters. These are <br />atmospheric precipitation, rock weathering, and <br />evaporation-crystallization processes. The processes <br />affect the relative concentration of thez maj~r <br />macro-elements found in freshwater (Na+, K+, Ca+. Mg+ , <br /> <br />Z~5 <br />