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Last modified
1/26/2010 2:27:40 PM
Creation date
10/12/2006 2:26:01 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8200.760
Description
Yampa River General
State
CO
Basin
Yampa/White
Water Division
6
Date
1/1/1981
Author
USGS
Title
Assessments of Impacts of Proposed Coal-Resource and Related Economic Development on Water Resources - Yampa River Basin - Colorado and Wyoming - A Summary - 1981
Water Supply Pro - Doc Type
Report/Study
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<br />For a wet-cooling tower system. the dissolved- <br />solids load in the river would decrease by an es- <br />timated 8.400 tons (7,620 t) per year. while the <br />dissolved-solids concentration would remain un- <br />changed at 140 mgfL (table 6). The land area oc- <br />cupied by the towers is conaiderably less than that <br />required for cooling ponds (N ational Academy of <br />Engineering, 1972, p. 131). The wet-cooling towers <br />may increase fog, ice, and precipitation over the <br />immediately surrounding area. <br />In dry-cooling towers, the cooling water moves <br />through 'I collection of finned tubes and the system <br />operates on the same principle as an automobile <br />radiator. Like an automobile radiator, the rate of <br />consumption of water is virtually zero, because <br />cooling occurs by conduction only (fig. 3D). Several <br />characteristics of dry cooling relative to wet cooling <br />are discussed by Hirsch, James, and Schefter <br />(1978). <br />Each cooling-system technology has its own ad- <br />vantages and disadvantages. For example, to avoid <br />withdrawing the vast amounts of water necessary <br />for once-through cooling, ponds that evaporate <br />substantially more water can be used. To prevent <br />the di8801ved-solids concentration of the river from <br />increasing when an evaporative system is used, the <br />long-term hazard of permanent impoundment of <br />the salts must be accepted. To achieve the advan- <br />tages of no water consumption at all, the increased <br />air pollution and waste of coal due to the decreased <br />efficiency of a powerplant with dry cooling must be <br />accepted. <br />Perhaps a useful comparison of water-use <br />implications for coal-use alternatives is to consider <br />inbasin conversion of an additional 12.5 million <br />tons (11.3 million t) of coal to electricity or syn- <br />thetic gas products or export of the same amount of <br />coal via a slurry pipeline. Comparisons of <br />withdrawals and consumption of water are made in <br />figure 4. The magnitude of water-use requirements <br />in electric-power-generation facilities can be noted. <br />All water exported in a slurry pipepine is a con- <br />sumptive loss from the standpoint of the basin; <br />however, some of this water can be recovered and <br />used at the delivery end of the pipeline. <br />Nonetheless, basin water 1088es using a slurry- <br />pipeline transport alternative are about one-fifth to <br />one-third as great as the losses for cooling purposes <br />in electric-power generation in the basin (fig. 4B). <br />The choice of coal use has a profound effect on <br />the amounts !lnd forms of diacharged waste <br /> <br />'.T f' .,. <br />.... .'!.. t <br /> <br />residuals that must be assimilated into the en- <br />vironment (Steele, 1978a). Using the set of seven <br />mixed coal-resources development alternatives, the <br />projected residuals given previously in table 5 are <br />aggregated and compared in figure 5, Total <br />residuals discharged increase both as a function of <br />the coal mined and the amount of the coal con- <br />verted to other energy forms in the basIn. These <br />projected discharges include both direct and in- <br />direct impacts. As noted in table 4, the indirect ef- <br />fects of population, urban development, and ser- <br />vices constitute the dominant part of several <br />residual forms (Bower and Basta, 1973). With in- <br />creasing in-basin coal use. greater amounts of solid <br />residuals have to be contended with; these <br />residuals dominate the total discharge loadings <br />(table 5; fig. 5). As will be discu88ed later, chemical <br />constituents from these residuals through decom- <br />position processes may still adversely affect <br />hydrologic conditions adjacent to disposal areas. <br />In summary, each cooling technology has both <br />advantages and disadvantages (Reynolds. 1980). <br />Some disadvantages must be accepted in order to <br />obtain the advantages of a given technology. For <br />example, evaporation ponds or wet-cooling towers <br />can be used to avoid withdrawing the large <br />amounts of water needed for once-through cooling. <br />However, this lower rate of withdrawals is accom- <br />panied by a higher rate of consumptive use and a <br />greater amount of dissolved solids requiring dis- <br />posal. For any given combination of coal uses there <br />are different water-use and residuals-generation <br />impacts. Among all of the options considered in <br />this study, those involving transport of the coal in <br />raw form have the smallest impacts. <br /> <br />SURFACE-WATER INVESTIGATIONS <br /> <br />By DANIEL P. BAUER <br /> <br />Three study components composed the surface- <br />water investigations for the Yampa River basin as- <br />sessment: (1) an anaiysis of the waste-load as- <br />similative capacity for a reach of the Yampa River <br />between Steamboat Springs and Hayden, Colo.; <br />(2) an evaluation of several hydraulic character- <br />istics of selected subreaches of the Yampa and the <br />Little Snake Rivers; and (3) a modeling analysis of <br />several proposed reservoirs. Selected results of each <br />of these studies are highlighted. Detailed inform a- <br /> <br />24 <br />
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