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WSP08749
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Last modified
1/26/2010 2:49:30 PM
Creation date
10/12/2006 3:14:47 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8272.500
Description
Colorado River Basin Salinity Control - Colo Dept of Public Health - WQCC and WQCD
Basin
Colorado Mainstem
Water Division
5
Date
11/14/1983
Title
Erosion and Sediment Yield - Channel Evaluation Workshop
Water Supply Pro - Doc Type
Report/Study
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<br />, <br /> <br />~ <br />toO <br />.... <br />-.oJ <br /> <br />As mentioned previously, field measurement is the most reliable and accurate <br />source of channel erosion data. However, the time involved in monitoring your <br />sites, in wet years and in dry years, often precludes this method of data <br />collection for project sedimentation studies. The remainder of this <br />discussion will be on field procedures for estimating channel erosion. <br /> <br />FIELD ESTIMATE PROCEDURE (DIRECT VOLUME METHOD) <br /> <br />The direct volume method is summarized in Equation 6. <br /> <br />'. <br /> <br /> <br />lateral recession <br />2 s/ton <br /> <br /> <br />(6) <br /> <br />= E <br /> <br />E = erosion in tons/year <br /> <br />The eroding area is in square feet, the lateral recession rate is in <br />feet/year, and density is in pounds/cubic feet (pcf). <br /> <br />Determining Eroding Area <br /> <br />Eroding arE 1S are channel banks or bottoms that are bare, rilled or gullied. <br />They genera lly have sloughed soi 1 at thei r bases. A grassed bank or rock bank <br />is considered to be noneroding. The actual eroding area is defined by the <br />height or width and the length to obtain squ'are feet of eroding area. The <br />height is not vertical; it is measured on the bank surface as a slope height. <br /> <br />'....'IICfl ~:,.:.;jnal erosicr. is irwc~t::i~~~ in a pr',:,j~~: ~P"'?3 t~e pt?rce.,tage of <br />eroding versus noneroding areas must be establ ished so that sample data can be <br />expanded over the entire watershed. As an example, for streambanks, you may <br />divide the streams in a watershed into geomorphic provinces (mountain streams, <br />foothhill streams, flood plain streams), flow regimes (ephemeral, <br />intermittent, or perennial), or use Horton's stream ordering (Figure 5). The <br />total miles of streambanks must then be measured. Based on time and study <br />intensity, a sample size must be selected. Five to ten percent is generally <br />an adequate sample but to be statistically accurate a sample size of up to 25 <br />percent may be required. This dependS on the variability of the streams. <br /> <br />Areas to be sampled are then ,marked on a map and the direct volume method is <br />used to qu~ntify erosion from the eroding areas in the samples. If only 30 <br />percent of the banks in the sample are eroding, this is interpreted to mean <br />only 30 rorcent of the banks in the watershed are eroding. By knowing the <br />erosion rate in tons per bank mile and knowing the total bank miles of stream <br />you can calculate the total tons of erosion from streambanks in that <br />watershed. For example: <br /> <br />--10 miles of 1st order streams in the Doodad Watershed <br />--2 miles are sampled (4 bank miles) . <br />--5,280 feet are eroding <br />--52BO T 4 bank miles = 25% eroding <br />--100 tons erosion from sample <br />--tons erosion from sample divided by bank miles eroding is erosion rate <br />--100 tonsIl bank mile eroding. 100 tons/yr/bank mile <br />--total bank erosion is 25% x 10 miles of streams x 2 (banks/mile) . <br />5 bank miles eroding and 5 bank miles eroding x 100 tons/yr/bank mile. <br />500 tons benk erosion <br /> <br />17 <br />
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