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Last modified
1/29/2010 10:12:12 AM
Creation date
12/26/2007 3:42:07 PM
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Floodplain Documents
County
Jefferson
Arapahoe
Basin
South Platte
Title
Chatfield Reallocation Study: Meeting Minutes 06/22/2005
Date
6/22/2005
Prepared For
Meeting Participants
Prepared By
CWCB
Floodplain - Doc Type
Meeting Summary
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<br />. . . .. .. <br />. . <br />. Federally listed and proposed listed endangered andthreatened species. and their designated <br />critical habitat; will consider comments furnished by local public officials and the general public <br />and use the information. as appropriate, to supplement information and recommendations <br />provided by the above Federal and State fish and wildlife resources agencies; and will detetminl:!' <br />the need. for any mitigation by assessing ecological resources gains and losses attributed to <br />alternative plans~ A summariiedstatementof compliance with enviromnentallaws and executive <br />orderS will be prepared. . . . . '. . . . '. . . . <br />(Note - the. water supplyplarining analysis, will analyze any far downstr~meffect.on threatened <br />. and endangered species Platte River habitat in Nebraska) . <br /> <br />Habitat-based evaluation methodologies will be used to the extent poSsible to describe and <br />evaluate ecological resources and benefits!imp~cts associated with alternative plans. The Corps <br />will use the ecosystem assessment method~IQgy developed in Step 2. The method win. involve . <br />outputs in acres of stream habitat andri parian habitat . improved and/or gained~The metho<r\vill <br />also involve outputs in quality as discussed in Step 2. <br /> <br />. .. <br />Regarding the simplest. least costly approach that would give an approximation of ecosystem. <br />units. the analvsis milZht work as follows for wintertime target flows - it would be essentiallv a <br />top width analysis. We know thatthe added flows within the.targetedrange will make pools and. <br />runs deeper and slower,' which is' the most important winter habitat of most fish species found in . <br />the South Platte, And we know that the added flows will provide soine added top width, which <br />will provide open water that is shallow that is preferred by wintering bird populations. Thus, for <br />each alternative with winter time flow increase, we can. claim the entireb3seline top width <br />acreage for winter fish habitat benefit because the alternative will have made all the pools and <br />runs deeper; and we can claim the added top width acrea~e as added wlnterin~ bird habitat. <br />because the alternative will have add~d that habitat, and the existing shallow open water habitat <br />will not have been made so much deeper as to be unusable. And we would figure out something. <br />similar for other timesofthe year once the workgroup of fish andwildlife stakeholders develops <br />those in-stream flow targets. <br /> <br />. . .. <br />. . <br />Regarding the more detailed and accurate approach. depth and velocity IZrids would be developed <br />and mapped for each alternative. and then related to not on Iy the tar~et flows. but also ecosystem <br />indicator species based upon preferred depth and velocity requirements forthose species for the <br />time of year involved~ This approach would enable a more detailed a.creage calculation for a mix <br />ofrepresentativelindicator speCie~ and their specificneeds,and would enable a visualization of <br />wherethe outputs would occur. . . <br /> <br />For either method. the stream bank and vegetation conditions would be considered in making <br />determinations of where andhow much.riparian habitat would be improved by the added flows <br />and their timing. The 1996-1998 Denver Audubon Society vegetation mapping would be <br />utilized:.Polygons of riparian habitat that would be considered benefited (ie. vegetated shoreline <br />habitat made wetted longer) by the added flows would be detennined. It may be that some eco- <br />hyrdo relationships can be developed for.some shoreline habitats because we know that added <br />flows wHlimprove biotic conditions and food chains in and adjacent to the river. And it may be <br />that the detailed. approach would enable a beth~rdevelopment oft1te rehitiOllships. <br /> <br />As discussed in' Step 2, either approach will also involve outputs in qmllity. Quality indexes ~i11 <br />relate to the need of indicator soecies.. stream bank conditions. and stream flow conditions. For <br />example, the closer the upper numbers of the range of target flows is achieved by an alternative <br />the better the biotic conditions will be, and the index will recognize that. Banklines that are steep, <br />armored, and with weedy vegetation will be indexed differentthanbanklines that are not steep <br /> <br />10 <br />
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