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The chemistry, mineralogy, and rates of transport of sediments in the ...

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10<br />

log Pra -<br />

1 .0892 + 0 .9073 log Ad + 1 .1828 log AE<br />

-2 .8210 log F, R2 - 0 .98 ; ( 2 )<br />

log PWg - 1 .0243 + 1 .1333 log Ad + 0 .6353 log AE - 3 .3231 log F,<br />

R2 - 0 .97 ; (3)<br />

log PE - 4 .5434 + 1 .0059 log Ad + 1 .8438 log AE - 2 .0173 log P<br />

<strong>and</strong><br />

- 3 .7420 log F, R 2 - 0 .98 ; ( 4 )<br />

log •STQ - 8 .8995 + 1 .2741 log<br />

Ad + 1 .1417 log AE - 2 .6367-log P<br />

- 6 .1278 log F, R2 - 0 .98 ( 5 )<br />

<strong>The</strong>se predictive relationships would likely be improved by <strong>in</strong>clusion <strong>of</strong><br />

meterorological <strong>and</strong> soil-permafrost-vegetation parameters, by <strong>in</strong>creased<br />

frequency <strong>of</strong> sampl<strong>in</strong>g, <strong>and</strong> a more widespread geographic distribution <strong>of</strong> river<br />

discharge, suspended sediment, <strong>and</strong> chemical measurement stations . In particular,<br />

small mounta<strong>in</strong> streams <strong>and</strong> <strong>in</strong>termediate sized rivers (i .e . Hare Indian,<br />

Horn, Blackwater, North Nahanni, Root Rivers) are not represented <strong>in</strong> our data<br />

set .<br />

DISCUSSION<br />

<strong>The</strong> Usefulness<strong>of</strong>RelationshipsBetweenConcentrations<strong>of</strong>Particulate_<br />

Material <strong>and</strong>Discharge<br />

As shown <strong>in</strong> Figs . 1, 3, 4 <strong>and</strong> Table 2, <strong>the</strong> concentrations <strong>of</strong> suspended<br />

<strong>sediments</strong> (SS4), <strong>and</strong> to a lesser extent particulate phosphorus (PP,), particulate<br />

nitrogen (PNi), <strong>and</strong> particulate carbon (PCB), vary <strong>in</strong> logarithmic<br />

proportion with discharge (Qi) . Such relationships (usually only for SS,)<br />

have been <strong>in</strong>vestigated <strong>in</strong> Temperate Zone rivers by Leopold et al . (1964,<br />

p : 220) <strong>and</strong> Abrahams <strong>and</strong> Kellerhalls (1973) . Sediment rat<strong>in</strong>g curves, such<br />

as Fig . 1, have been used to estimate, suspended sediment concentrations<br />

between sampl<strong>in</strong>g dates (such as <strong>in</strong> Davies, 1974) . Abrahams <strong>and</strong> Kellerhalls<br />

(1973) suggest that, with careful evaluation <strong>of</strong> 5-9 years <strong>of</strong> data, <strong>the</strong>se<br />

relationships may be useful <strong>in</strong> predictive estimation <strong>of</strong> sediment concentrations<br />

<strong>and</strong> <strong>rates</strong> <strong>of</strong> <strong>transport</strong> <strong>of</strong> <strong>sediments</strong> . When a longer period <strong>of</strong><br />

measurement <strong>of</strong> Qi <strong>and</strong> SSi is available,, <strong>the</strong>se relationships (Fig . 1) could<br />

contribute to a method to observe <strong>the</strong> effects <strong>of</strong> terra<strong>in</strong> disturbance on<br />

suspended . sediment loads <strong>of</strong> smaller rivers <strong>and</strong> streams (i .e . similar <strong>in</strong><br />

size <strong>and</strong> character to <strong>the</strong> rivers <strong>of</strong> Group 2 <strong>in</strong> Table 1) . If <strong>the</strong>re have been<br />

no recent natural erosion events (fires or l<strong>and</strong>slides) <strong>in</strong> a watershed under<br />

technological development (e .g ., rights-<strong>of</strong>-way clear<strong>in</strong>g for pipel<strong>in</strong>es or<br />

roads), <strong>the</strong>n Qi <strong>and</strong> SSi data po<strong>in</strong>ts that fall greatly above <strong>the</strong> regression<br />

l<strong>in</strong>es (or <strong>the</strong>ir confidence limits, not shown) <strong>in</strong> Fig . 1 might <strong>in</strong>dicate

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