Brown, Timothy. 2002. Short-term total suspended-solid concentrations resulting from stream crossing obliteration in the Clearwater National Forest, Idaho. M.S.
This was a pilot study to investigate the short-term effects of stream
crossing obliteration (removal) on downstream water quality in small,
headwater streams. Study sites were located on the Idaho Batholith in
the Clearwater National Forest in north central Idaho. Paired grab-samples
were taken above and below stream crossings just before, during, and after
stream crossing obliteration. Samples were analyzed in a laboratory for
total suspended-solid (TSS) concentrations and nephelometric turbidity
according to standard, widely accepted methods. Paired- and one-sample
t-tests were used to compare upstream and downstream sediment yields resulting
from various levels of mitigation. The relationship between TSS concentrations
and nephelometric turbidity was examined using simple linear regression
analysis.
The objectives of this study were to: (1) determine the significance of
short-term increases in TSS concentrations and turbidity; (2) quantitatively
describe changes in suspended-sediment yield; (3) compare the effectiveness
of different sediment trap configurations; (4) document currently accepted
stream crossing obliteration methods; and (5) evaluate the compliance
of current practices with adopted water quality standards from which projects
of this type are exempted.
Total suspended-solid concentrations upstream of sites ranged from 1.0
to 5.7 milligrams per liter (mg/L). Downstream concentrations were highly
variable ranging from 2.9 to approximately 68,500 mg/L. Upstream suspended-sediment
yields ranged from 0.1 to 0.8 kilograms (0.3 to 1.7 lbs), while downstream
yields ranged from 0.8 to 95.4 kilograms (1.9 to 210.3 lbs). Yields were
normalized by the duration each site was monitored for statistical comparison.
The linear relationship between TSS concentrations and nephelometric turbidity
was strong, with a Pearson correlation coefficient of 0.918. Nephelometric
turbidity was estimated for samples based on the resulting regression
equation (MSE = 0.132; r2 = 0.842). Adopted water quality standards were
exceeded a majority of the time when one or no sediment trap was used,
but only occasionally when two were used.
Downstream, normalized yields were statistically greater when all sites
were considered (p = 0.082), but statistically indistinguishable when
the yields of just mitigated or highly mitigated sites were compared (0.119
< p < 0.148) at a 0.10 level of significance.
As expected, the highest concentrations and sediment yields were observed
downstream of sites with little or no mitigation. The highest concentrations
observed were frequently associated with the sediment trap removal process.
The use of two sediment traps reduced peak concentrations an order of
magnitude from approximately 68,500 mg/L to 3,000 mg/L, and suspended-sediment
yields 10 to 30 times. Thus, the use of at least two sediment traps is
recommended during this type of work.
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