My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
WSP07510
CWCB
>
Water Supply Protection
>
Backfile
>
7001-8000
>
WSP07510
Metadata
Thumbnails
Annotations
Entry Properties
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
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
63
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
Show annotations
View images
View plain text
<br />IlD!11S <br /> <br />the residuals coefficients were derived using a <br />variety of sources. <br />Not all of the estimates of residuals discharge <br />were linked solely to the value of the output of the <br />various sectors. Some also were based on estimates <br />of residuals discharged per person and, thus, were <br />linked to the regional population. For example. the <br />quantity of biochemical oxygen demand was linked <br />both to the dollar value of the output of the <br />livestock sector and the population of the region. <br />Population estimates for the Yampa River basin <br />were based on estimated employment in each sec- <br />tor. The employment estimates were, in turn, <br />based on sector-employment coefficients. which <br />are estimates of the num ber of persons employed <br />per dollar of output by each sector. Due to space <br />limitations, the estimated employment coef- <br />ficients, residuals coefficients. and the corres- <br />ponding multipliers for each sector are not <br />presented herein. <br />The input-output model was used to predict the <br />impacts of alternative methods and rates of coal <br />use on several aspects of the basin's environment. <br />In making these predictions, the output of the ex- <br />isting coal-mining and electric-energy sectors (sec- <br />tors 6, 7. and 27. table 2) was constrained to 1975 <br />levels. All additional coal mining and utilization is <br />assumed to occur in the new and expansion sectors <br />(33 through 38. table 2). <br />Predictions were made using two sets of <br />scenarios. In the first set of four scenarios, it was <br />assumed that an additional 12.5 million tons (11.3 <br />million t) of coal, above the estimated 4.6 million <br />tons (4.2 million t) extracted in 1975, is to be sur- <br />face mined. Tbe second set of aeven scenarios (the <br />coal-resource development alternatives presented <br />in table 1) is intended to encompass the range of <br />anticipated coal-resource development in the <br />basin. <br />The four scenarios were employed to obtain <br />across-use comparisons of the impacts of using the <br />additional coal in each of four ways. <br />1. All of the additional coal is used within the <br />basin by thermal-electric powerplants to generate <br />electricity, solely for export from the basin. <br />2. All of the additional coal is used within the <br />basin by coal-gasification plants to manufacture <br />gas for export from the basin. <br />3. All of the additional coal is exported from the <br />basin via a coal-slurry pipeline. <br />4. All of the additional coal is exported from the <br />basin via unit trains. <br /> <br />In this first set of scenarios, any required con. <br />struction under each of the alternatives has been <br />assumed to be completed and the economy is as- <br />sumed to be in a relatively steady state. This, of <br />course, ignores part of the problem, as many <br />severe, though relatively short-lived. impacts of <br />energy development. may occur during. the con- <br />struction phase (Luken, 1974). <br />Estimates of population, water withdrawal and <br />consumption. and residuals discharge under each <br />of the scenarios are presented in table 3. Estimates <br />also are presented for the existing (1975) level of <br />development. <br />The two scenarios under which coal is used <br />within the basin give rise to the most economic <br />development, which results in the greatest increase <br />in population, residuals output. and water use. The <br />export of coal from the basin for use elsewhere, as <br />in the other two scenarios, does not, of course, <br />eliminate either residuals output or water use-it <br />only "exports" these problems along with the coal. <br />If a goal is to increase the level of economic ac- <br />tivity in the Yampa River basin. then coal- <br />gasification plants could be considered, for they <br />prod uce the greatest increase of the four scenarios <br />(table 3). On the other hand. if a goal is to remove <br />coal resources with the least disruption to the ex- <br />isting conditions in the region (at least to those <br />aspects considered), then either unit trains or a <br />coal-slurry pipeline appear to be better alternatives <br />(table 3). <br />The coal-slurry pipeline would consume, directly <br />and indirectly, more water than would unit trains. <br />The estimates of residuals discharge associated <br />with the coal-slurry pipeline, however, are less than <br />or equal to those in the unit-train scenario, for most <br />types of residuals considered. Moreover, estimates <br />were not made of noise pollution and of "damages" <br />imposed on motorists who must wait. at railroad <br />crossings for unit trains to pass. These problems as- <br />sociated with unit trains may be of significant <br />magnitude if trains are frequently used. <br />Though all water used directly by a coal-slurry <br />pipeline would be consumed through export from <br />the basin, the total rate of consumption under the <br />pipeline alternative would be considerably less <br />than that for either the thermal-electric power. <br />plant or coal-gasification-plant scenarios. <br />The total impacts of energy development under <br />each scenario are divided into percentage direct <br />and percentage indirect in table 4. It can be seen <br />that plant-process models, which estimate only <br />direct impacts. provide nearly the same, but lower <br /> <br />17 <br />
The URL can be used to link to this page
Your browser does not support the video tag.