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Impact of Forest Service Activities on Stream Flow
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Impact of Forest Service Activities on Stream Flow
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Last modified
1/26/2010 4:41:00 PM
Creation date
7/20/2009 11:44:54 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8461.250
Description
Water Issues
State
CO
Basin
South Platte
Water Division
1
Date
5/22/2003
Author
Charles A. Troendle, James M. Nankervis, Laurie S. Porth
Title
Impact of Forest Service Activities on Stream Flow
Water Supply Pro - Doc Type
Report/Study
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TroendlelNankervis/Porth Page 19 5/22/2003 <br />evaluation, 36 years of record were deleted. This represents 1.2 percent of the potential data set. <br />The logic for doing this, and the impact on the double-mass analysis, has been developed in <br />Troendle and Porth (2000). <br />Seasonal stream flows for the 47 Colorado and Wyoming gauging sites were plotted in a double- <br />mass comparison with the stream flow for the Encampment River above Hog Park. The Hog <br />Park gauge had been demonstrated to be a stable record useful for such a screening process <br />(Troendle and Porth 2000). Based on this comparison, many of the stream flow records did not <br />appear suitable for future comparisons (Figure 15) while others appeared quite good (Figure 16). <br />The list was reduced to 11 stream gauges in Colorado and 8 in Wyoming as a result of this <br />analysis. <br />CHERRY CRFEK BELAW CHERRY CREEK LAKE C0.:06713000 8c <br />ENCAMPMENT RN AB HOG PARK CR NR ENCAMPMENT WY0:06623800 <br />w <br />[s. <br />? <br />? <br />? <br />> <br />L <br />75 <br />? <br />g <br />O <br />? <br />06623800: Cumulative WYRDMF(cfs) <br />Figure 15. Example of an unstable double-mass comparison. If you assume that the stream flow measured <br />at Hog Park is stable, the stream flow from Cherry Creek is quite erratic. No attempt is made <br />to determine the cause of instability. <br />As noted by Troendle and Porth (2000), the double-mass plots do not indicate that change is not <br />occurring at the sites being compazed. What it does indicate is that stream flow at both sites <br />varies similarly, in the case of the comparison in Figure 16, or that one or both sites is erratic as <br />in Figure 15. The next step in the analysis is to assess the stability, and appropriateness, of each <br />site as a reference site. The 19 stream gauges retained for further analysis are listed in Appendix <br />C, Table 1, along with watershed area and length of record. <br />The neact step in the process was to identify some number of reference NRCS snow courses in <br />order to compare snow pack accumulation with stream flow. Ten snow courses in Colorado and <br />9 courses in Wyoming appeared to be located in the watersheds of concern. We also added the <br />Glade Creek snow course in Wyoming to the list as we knew it was stable and compared well <br />with measured stream flow even though it is in the Little Snake Watershed. The snow course <br />data was downloaded from the NRCS website at http://www.wcc.nres.usda.2ov/water/wmdata.html. <br />Four of the 10 Wyoming snow courses are now snotel (pillow) sites. We found in plotting the <br />data for the 4 manual sites that had been upgraded to snotel sites over time that the data was not <br />consistent through the transition. We dropped those sites from further consideration. We then <br />0 200000 400000 600000 800000 1000000 1200000 1400000
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