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each sampling occasion. Biomass values were obtained by drying the benthic <br />macroinvertebrates from each sample in an oven at 100°C for 24-hours or until all water <br />content had evaporated. Biomass is reported as the mean dry weight of <br />macroinvertebrates/mz at each site location. <br />Spawning <br />Artificial redds were constructed at two sites on the Fryingpan River (Figures 3 and 4) in <br />order to describe intragravel conditions during the brown trout and rainbow trout <br />spawning and egg incubation period. The most upstream site was established on the <br />Pruessing Property just below the CDOW Catch and Release section (Figure 13). <br />Another site was established upstream of Taylor Creek confluence on Roy Palm's <br />property (Figure 11). This location corresponded to FPR-LG-an IFIM site. A third site <br />in the town of Basalt was initially chosen but abandoned due to sub-marginal spawning <br />habitat and difficulty with equipment maintenance. <br />On 10 October 2001, two artificial redds were constructed at each site. Areas chosen <br />were based upon professional judgment regarding typical salmonid spawning locations. <br />Specific redd locations are shown in Figures 14 and 15. Redds were excavated by <br />mimicking a salmonids' natural substrate "cleaning" behavior using a shovel. This action <br />disrupts the hydraulic conditions on the stream bottom and removes fine sediments and <br />creates a "bowl" in the gravel-cobble matrix. Once the initial redd bowl was created, an <br />aluminum standpipe was pounded into the redd substrate. Holes had been pre-drilled into <br />the standpipe to allow water circulation from the substrate into the standpipe. A <br />Stowaway® Tidbit® temperature logger (accuracy ±0.2°C) encased in a small (10 cm) <br />section of pvc pipe was placed in the redd as well. Each thermograph was set to record <br />temperature every hour. After the standpipe and thermograph were installed, substrate <br />was dislodged upstream of the redd and allowed to cover the thermograph and holes of <br />the standpipe. Once construction of the artificial redds was completed, the area was not <br />disturbed until March. Active brown trout spawning was observed within 1 m of the <br />artificial redds at both sites. <br />Draft Final Report, Fryingpan and Roaring Fork Rivers February 12, 2003 <br />Miller Ecological Consultants, Inc. Page 19