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8/16/2009 3:09:58 PM
Creation date
10/4/2006 7:06:50 AM
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Board Meetings
Board Meeting Date
9/24/2001
Description
Snowmass Water and Sanitation District 404 Permit
Board Meetings - Doc Type
Memo
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<br />. <br /> <br />recommended for the Surmnit County Ski Areas through the Green Mountain EIS were absolute <br />minimum or survival flows, He stated the CDOW "does not like to use the term survival flow in <br />recommending in-stream flows for the CWCB except in extreme circumstances where the <br />balance between preserving the natural environment to a reasonable degree and existing water <br />uses is stressed to the point of survival." Since the Green Mountain EIS recommended flows <br />were survival flows, then the 25% threshold was an absolute maximum impact beyond which the <br />survival ofthe fishery was in question. <br /> <br />Analysis ofthe Miller (1993) report (tables 6 to 10) reveals that reductions in flows from <br />10 cfs to 4 cfs create a loss of 50% of winter habitat types for all species (brown, brook and <br />rainbow trout). For brown trout winter habitat, fry would lose 47%, juvenile would lose 42%, <br />and adult losses would reach 36%. For rainbow trout, the loss of fry, juvenile and adult winter <br />habitat would be 16%, 32%, and 43%, respectively. For brook trout, juvenile and fry habitat <br />curves were not available so only adult winter habitat losses were calculable, and they were 15%. <br />For riffle habitat the losses ranged from highs of 34% for rainbow adult habitat and 32% for <br />brown juvenile habitat to a low of only 6% for rainbows juveniles, For brook trout there was an <br />increase of23% of riffle habitat for adults. This analysis reveals that the 4 cfs flow creates <br />adverse impacts to the fishery in excess oHhe maximum allowed significant threshold of25%. <br />Even under the CDOW conditions for a survival flow, which they use only in "extreme <br />circumstances", the 4 cfs flow would not be recommended as the impacts exceed the 25% <br />threshold. <br /> <br />. <br /> <br />iii) Chadwick Ecological Consultmlts produced several reports using IFIMiPHABSIM on <br />Snowmass Creek while working for the Aspen Skiing Company during the CWCB hearings and <br />the 404 pennit process in the mid 1990's and now for the SWSD. Chadwick reports from 1992 <br />and 1996 provide some IFIM analysis but he does not provide the data as in the Miller report. <br />These Chadwick reports justify 7 cfs as a valid minimum flow and the basis for the justification <br />is the "habitat bottlenecks" that occur in every Rocky Mountain stream. According to Chadwick, <br />the trout populations in Snowmass Creek are limited by a "bottleneck" that occurs during spring <br />high flows, Using the IFIM data, he shows that there is more Weighted Useab1e Area (WUA) at <br />a 7cfs flow than at the 243 cfs average peak flows. Chadwick cites the work ofMr, Barry <br />Nehring of the Colorado Division ofWildJife to support his theory, This comparison may not be <br />valid within the confines ofthe IFIM model, as the data was not collected within the range of <br />flows near high water. More importantly, the logic appears to be flawed, Chadwick ignores the <br />presence of abundant wetlands that are fed by side channels and support beaver ponds in the <br />upper segment of Snowmass Creek. The lower segment contains the same habitat features <br />although not as abundant. High water does reduce trout habitat, temporarily, but the fish seek <br />refuge in flooded wetlands and side channels, These features are termed refuge habitat. A Corps <br />biologist walked through these wetlands and observed many juvenile trout in the flooded willows <br />along beaver ponds, and also observed adults in the side channels. Refuge habitat is a very <br />common feature in Rocky Mountain streams that experience extreme snowmelt runoff events <br />that reduce habitat. Others document the presence of off-channel or refuge habitat in the <br />Snowmass Creek (Chapman 1996, Walsh and Walsh 1995). Walsh and Walsh (1995) reported <br />the presence of trout fry in the side-channels in August and September of 1995, and 1995 high <br />flow was an extremely high flow event. The presence ofthe fry in 1995 in the side channels not <br /> <br />. <br /> <br />7 <br />
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