My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
7629
CWCB
>
UCREFRP
>
Public
>
7629
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
7/14/2009 5:02:30 PM
Creation date
5/20/2009 3:44:46 PM
Metadata
Fields
Template:
UCREFRP
UCREFRP Catalog Number
7629
Author
Pucherelli, M. J.
Title
Summary of Methods and Results for the Green River Backwater Pilot Study Using Remote Sensing and GIS (Geographic Information Systems).
USFW Year
1987.
USFW - Doc Type
\
Copyright Material
NO
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
10
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 />3 <br /> <br />Results and Discussion <br /> <br />Final map plots and acreage tabulations were hand delivered to Mr. Bob <br />Williams. GenerallYt the number and total acreage of backwaters are maxi- <br />mized at lower flows (see Appendix A and B). Howevert because only three <br />flows were studied, it is not certain what flow will produce the optimum <br />number of backwaters. This number may occur at a higher or lower flow than <br />the 1,889 ft3/s reported in this study. Additionally, the highest flow <br />studied (4,359 ft3/s) maintained larger backwaters than the lowest <br />(1,889 ft3/s) and middle (3,119 ft3/s) flows; therefore, it is possible <br />that a different high flow scenario may maximize backwaters. More flows <br />need to be studied to determine the optimum strategy. Furthermoret a <br />greater number of study sites encompassing larger river reaches should be <br />examined to reduce the variability in the data. <br /> <br />The Ouray study site maintained the greatest number and acreages of back- <br />waters at the highest flow. This may have occurred because the sandbars <br />in this study s'ite are higher in elevation, steeper, and more permanent <br />(vegetated) than the sandbars in the other areas. Thus, backwaters on <br />higher sandbars only occur at higher flows. <br /> <br />Comparing 1:4,000 and 1:2,000 scale photography indicates the former is <br />adequate for mapping backwaters. Cost savings dictate the use of 1:4,000 <br />scale photography. Color infrared photography appears superior to color <br />photography since color infrared increases the contrast between water, <br />sand, and sediment laden water. Moreover, backwater delineation is <br />simpler and more accurate using color infrared photography. <br /> <br />In our efforts to obtain a fourth set of photography, an interesting <br />observation occurred. We requested flows of 1,500 ft3/s in order to help <br />define the lower end of the graphs. More specifically we felt that with a <br />1500 cfs data set it would be possible to focus in on the range of flows <br />needed to maximize backwater habitat. A fourth set of aerial photography <br />was acquired on December 4, 1986, almost 3 months after the first low <br />flow. The Jensen Gage reading was nearly identical to the September 12, <br />1,986, It889 ft3/s flow record. It was then determined that it would be <br />unneccessary to interpret this data as results would probably be iden- <br />tical to the September 12, 1986 data set. After a brief examination of the <br />photographs, it was noted that sandbar configuration and backwaters were <br />drastically changed. Moreover, there was an average of approximately <br />30 percent loss in the area of sandbars calculated at the same flows in <br />the same study sitest 3 months apart. (see map plots and Appendix A for <br />acreage tabulation and a visual account of cover type changes). On the <br />Ouray site, an important backwater near mile 135.2 was reduced to a <br />
The URL can be used to link to this page
Your browser does not support the video tag.