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Published byShannon Harrington Modified over 9 years ago
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Stream Sediment Sediment - particles transported or deposited in stream channels Sediment levels - good indicator of effectiveness of watershed mangement
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Erosion is a natural process
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Clearwater River, Idaho
The name says what the watershed management goal is.
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Clearwater River, Idaho
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Clean gravel beds for spawning
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Erosion Process Detachment Transport Deposition Eroded skid trail
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Watershed Gross Erosion
Components of gross erosion Interrills Rills Ephemeral gullies Channels Landslides or slumping
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Interril Erosion Raindrops striking exposed soil detach the soil particles and splash them into the air and into shallow overland flows. Raindrops striking these shallow flows enhance the flows's turbulence and help to transport more of the detached sediment to a nearby rill or flow concentration
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Rill Erosion
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Gully Erosion
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Channel Erosion
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Grand Ditch, Rocky Mountain National Park
Landslides Grand Ditch, Rocky Mountain National Park
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Estimates of rill erosion
Universal soil loss equation Developed by US Dept. Agriculture Oldest and most accepted estimator Over-estimates for forest land Use as a starting point only
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Universal Soil Loss Equation
A = R K LS C P A = tons/acre/year R = rainfall energy factor K = soil erodibility factors LS = effect of topography C = ratio of soil loss with specified cover and with continuous tillage P = conservation practice factor
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R factor R = [∑ ∑ (E I30)] / 100 n)
E = storm kinetic energy, ft-t/acre/inch of rainfall I = maximum 30 minute storm intensity, in./hr. n = total number of years m = number of storms in each year R = 150 to 200 for Indiana n m
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K factor Describes soil detachability and transport-ability due to soil texture, structure, organic matter, density, compaction, and biological characteristics K = A / (RLSCP) K is given in NRCS soil survey reports
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K factor 100 K = 2.1M1.14(10-4)(12-a) + 3.25(b-2) + 2.5 (c-3)
M = (%silt + %very fine sand) (100 - % clay) a = % organic matter b = soil structure code used in soil classification c = profile permeability class
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LS factor LS = (λ/22.13)a (0.065 + 0.0454 S + 0.0065 S2
λ = slope length a = 0.5 for slope ≥ 5%, and 0.3 for 1 to 3% slope S = slope steepness in %
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C factor C = A (with treatment) / A (with clean tillage)
C values reported in 3 studies of forested site conditions Undisturbed mature forest Thinned to 50% density Clearcut, no site preparation Clearcut, roller chopped Clearcut, complete site prep. Clearcut, site prep., fallowed 0.03 NA 0.001 – – 0.01 0.001 – 0.022 0.004 – 0.028 0.023 – 0.068 0.0242 0.097
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P factor P = A (with conservation practice) / A (up-and-down hill cultivation) P = 1 if no conservation practices P < with conservation practices
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Recommended Values for P Factor
Land slope % Contouring Contour stripcropping Terrace and stripcropping 1 to 2 0.60 0.45 0.30 3 to 5 0.50 0.38 0.25 6 to 8 9 to 12 13 to 16 0.70 0.52 0.35 17 to 20 0.80 0.40 21 to 25 0.90 0.68
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Example
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Drum chopper for site preparation
Windrow of logging slash Burning piles of logging slash
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Erosion rates for clear cuttings in SE US
Treatment Recovery time Annual erosion (t/ha) Natural NA 0.00 – 0.05 Logged and roaded 3 0.10 – 0.50 Burned 2 0.05 – 0.7 Chopped 0.05 – 0.25 Chopped and burned 4 0.15 – 0.40 Windrowed 0.20 – 0.24 Disked 2.50 – 10.0
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