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WSP11999
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Last modified
1/26/2010 3:19:33 PM
Creation date
10/12/2006 5:20:34 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8220.102.01.I
Description
Aspinall (AKA Curecanti)
State
CO
Basin
Gunnison
Water Division
4
Date
1/1/1992
Title
Scopes of Work - Endangered Fish Program as Related to Aspinall
Water Supply Pro - Doc Type
Report/Study
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<br />.1 <br /> <br />~ <br /> <br />- 3 - <br /> <br />Habitat mapping will also be done in the areas used by radiotagged fish during <br />tracking, prior to spawning. The purpose of this mapping is to establish habitat <br />use prior to spawning, and to determine if staging is a critical element to the <br />spawning event. <br /> <br />The habitats delineated on <br />AutOCad digitizing program. <br />and percent of each habitat <br /> <br />the acetate overlays will be quantified using an <br />This system will be used to assess the surface area <br />type, as well as changes in area by flow. <br /> <br />The primary purpose of this investigation is to identify and describe spawning <br />sites and nursery areas of humpback chub in Westwater Canyon, and to determine <br />spawning flow requirements. Once a spawning site is identified, complete <br />documentation will be developed for the area inCluding measurements of depth, <br />velocity, substrate size, cover, and water temperature. These parameters will <br />be recorded to quantitatively describe the spawning site and nursery area. <br /> <br />Also, the site will be mapped for habitat types at the spawning flow, at the <br />peak of runoff, at base flow, midway between base flow and runoff, and at the <br />flows observed during radiotracking. This approach will be used to establish a <br />relationship between flow and surface area of spawning and associated habitats, <br />in a similar analysis to that performed by Carter et al. (1985) for fish habitat <br />of the Colorado River near Parachute, CO. The analysis involves developing <br />mathematical relationships between flow and each habitat type, based on the <br />surface area of each. Those mathematical relationships will be 1eveloped over <br />the 3 years of the study, and have associated with each, Ir' values, or <br />coefficients of determination. These mathematical relationships are proposed as <br />the principal tool for determining spawning flow recommendations for humpback <br />chub in Westwater Canyon. <br /> <br />In addition to determining the spawning-flow requirements as outlined above, an <br />effort will be made to determine the environmental and water quality parameters <br />that prompt the humpback chub to spawn at a given time. We hypothesize that the <br />timing of spawning is determined by a combination of environmental factors, <br />including water temperature and cumulative temperature degree days. <br /> <br />Ongoing river flows and temperatures will be secured from the USGS Stateline <br />Gaging Station located on the Colorado River about 15 miles upstream of the <br />proposed study area. No major influences occur between the gage and the study <br />area, and it is expected that this station will accurately represent conditions <br />in Westwater Canyon. <br /> <br />TASK 2: DETERMINE EXTENT OF LARVAL DRIFT <br /> <br />Subtask 2A: Deploy Drift Nets. The mechanism by which larval humpback chub <br />emerge from their egg and find their way to suitable nursery habitat is unknown. <br />In contrast to larval Colorado squawfish, which may become transported for many <br />miles by river currents, the fidelity of the humpback chub to specific regions <br />of river probably precludes long distance drift for this species. If long <br />distance drift did occur, large numbers of young chubs would be expected in <br />regions far downstream of population concentrations such as Black Rocks and <br />Westwater Canyon. This does not seem to be the case. Hatchery personnel also <br />report distinct behavior for swim-up chubs that will be further investigated. <br /> <br />Drift of larval humpback chub will be monitored immediately below identified <br />spawning sites to confirm the site and to ascertain the age at which the fish <br />drift, as well as the distance. A minimum of four shoreline and four midchannel <br />drift samples will be taken using the drift nets and techniques described by <br />Haynes et a1. (1984) and Yaldez et a1. (1985). The shoreline sets will be <br />positioned with rebar driven into the shore below the spawning site. The <br />midchannel samples will be taken from the motorized rafts towing a bongo type net <br />
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