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Last modified
7/14/2009 5:02:35 PM
Creation date
6/1/2009 12:40:46 PM
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UCREFRP
UCREFRP Catalog Number
9397
Author
Hydrosphere Resource Consultants.
Title
Gunnison River / Aspinall Unit Temperature Study - Phase I.
USFW Year
2002.
USFW - Doc Type
107,
Copyright Material
NO
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Gunnison River /Aspinall-Unit Temperature Analysis -Phase I <br />Page 1 <br />1. INTRODUCTION <br />Hydrology of the Gunnison basin has been significantly altered by the construction and <br />operation of the Aspinall Unit (Blue Mesa, Morrow Point and Crystal Reservoirs), and by <br />diversion and return flow features primarily related to irrigation in the areas surrounding <br />Montrose and Delta (Figure 1). Cool stream temperatures resulting from changes to the <br />basin hydrology (Stanford, 1994) have been identified as a significant impediment to re- <br />establishment of pikeminnow habitat in the Gunnison River near Delta (Osmundson, <br />1999). <br />Records indicate that Colorado pikeminnow historically were found in the Gunnison <br />River as far upstream as the Town of Delta (Quarterone, 1993), though recent studies <br />indicate that pikemiruiow are largely confined to downstream reaches of the river (Valdez <br />et al., 1982, Burdick 1995). Osmundson (1999) notes that areas upstream of Whitewater <br />through the Town of Delta show no reduction in forage-size fish and that the floodplain <br />area near Delta provides the "most diverse physical habitat conditions in the Gunnison <br />River" between Hartland Diversion and the mouth. The Hartland Diversion dam is <br />located above the city of Delta, just below the mouth of Tongue Creek. <br />Results of Osmundson's work indicate that increasing mean water temperatures at Delta <br />by 1 °C in June, September and October, and by 2 °C in July and August, would increase <br />the mean annual thermal units (ATU) from 32 to 46 units. Such an increase would put <br />stream temperatures at Delta at a level similar to sites on the Yampa and Colorado Rivers <br />which have abundant populations of pikeminnow. <br />Stream temperature in reservoir-regulated rivers is a function of several related variables. <br />The "natural" mean water temperature is closely related to mean air temperature <br />(Sinokrot and Stefan, 1993). Water released from a reservoir will tend to approach this <br />natural or ambient water temperature as it travels downstream. The rate at which the <br />waters warm, and the ability to achieve a specific temperature at a specific location, <br />depends on release temperature, flow, and atmospheric conditions. In general, increasing <br />reservoir release temperatures will result in warmer downstream temperatures. The <br />relationship between release temperature and downstream temperature is nonlinear (e.g., <br />a 1 °C increase in release temperature does not necessarily result in a 1 °C increase <br />downstream) and is limited by the ambient atmospheric conditions. Reducing reservoir <br />releases will also increase downstream temperatures. This is the result of a reduced <br />volumetric heat capacity per unit surface area of stream, and of the slower rate at which <br />the water travels downstream, thus increasing the time it is exposed to atmospheric <br />heating. <br />There are potentially two ways that downstream temperature control can be achieved in <br />the Gunnison River. These are to 1~) increase the temperature of the water being released <br />from the Aspinall Reservoirs, and/or 2) decrease the amount of water being released. <br />Analysis of the potential for releasing warmer water is complicated by the physical <br />characteristics of the Aspinall Unit reservoirs. If a temperature control device (TCD) <br />Hydrosphere Resource Consultants <br />
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