Adam L. Majeski
GIS in Water
Resources
Term Project – Final
Report
December 8, 2006
A Brief Introduction to My Masters Thesis
By surveying channel slopes, and cross sections based on those established by the Bureau of Reclamation in 1986, the present state of these systems can be compared to similar historical records and to pre-dam topography. This will also allow volumetric analysis of deposited delta sediment to be conducted in order to determine the amount mobilized and/or deposited. By observing photographs taken by several researchers, including John Dornwend, James Evans, William Vernieu, and myself, changes in delta morphology, and sediment deformation over time can be viewed in a qualitative manner. Finally, by observing delta stratigraphy and associated grain size distributions and bed material size distributions, inferences can be made on differences in incision rates, and the presence or absence of lateral slumping, mud cracking, and slope failure. Each piece of data will help to characterize each system and through comparison and contrast with the others, it will become more clear which responses are dependent and independent of the size and physical characteristics of the river system.
Where GIS Fits In
The driving theme behind my research is physical system characterization so comparisons can be made between these 3 systems. While much of my comparative data will come from field based methods, there is some that is more logically gathered in the office; drainage area delineation, drainage density, and interpolation of existing USGS gage records to streams where no recent ones exist. These three things will identify fundamental basin characteristics and the very different spatial scales of each system, which will help to frame and put into context the magnitudes of their responses to base level drop, to be investigated in my masters thesis.
Methods
Overview
To begin the
investigation the necessary data sets were gathered; NHD and NHDplus for the
United States Region 14 (The Upper Colorado Basin, from its headwaters to Lees
Ferry, AZ), USGS gaging information point file, state boundaries, and major
roads. From the NHD datasets, GIS was
used to create feature datasets containing the HUC-6 basins of the
Drainage Basin Delineation
For the
For the Dirty Devil /
Drainage Density
To compute drainage density, the
NHD flowlines were added for the
North Wash Creek only contains
gaging records from 1950 to 1970 so interpolation from nearby gages with longer
records on the Dirty Devil / Fremont River (DDF) was used to approximate
current mean annual flow (MAF). The USGS
gage feature class was added to the map and those lying along the Dirty Devil /
As another
method to calculate MAF on
Results
Drainage Basin Delineation
The Upper Colorado Drainage
Basin above Lees Ferry, AZ spans 5 states (
|
Table 1 |
|
|
HU_6_Name |
Area (km^2) |
Area (mi^2) |
|
140100 |
|
25496.89 |
9844.40 |
140200 |
|
20822.10 |
8039.46 |
140300 |
Upper Colorado-Dolores |
21664.64 |
8364.76 |
140401 |
Upper Green |
43799.45 |
16911.06 |
140402 |
Great Divide Closed Basin |
9947.52 |
3840.76 |
140500 |
White-Yampa |
34332.46 |
13255.84 |
140600 |
Lower Green |
37701.43 |
14556.60 |
140700 |
Upper Colorado-Dirty Devil |
35395.27 |
13666.19 |
140801 |
|
37583.40 |
14511.03 |
140802 |
|
26937.01 |
10400.44 |
|
|
|
|
|
Total Area |
293680.17 |
113390.55 |
To compute the drainage area above
Glen Canyon Dam, it was necessary to remove any downstream drainage area. A majority of this excess area belongs to the
Figure 5 – Removing the
Table 2 |
|
|
|
|
|
|
|
Total Drainage Area Below GCD = |
4309760147.3100 |
m^2 |
4309.760147 |
km^2 |
|
1664.007698 |
mi^2 |
|
|
|
|
|
|
|
|
|
|
|
293680.1706 |
km^2 |
|
113390.5479 |
mi^2 |
|
|
|
|
|
|
|
|
Drainage Basin Area Above GCD = |
|
|
289370.4105 |
km^2 |
|
111726.5402 |
mi^2 |
The Dirty Devil / Fremont drainage
area is comprised of 22 HUC-10 watersheds and it covers an area of 4374.05 sq.
mi. (Figure 7 and Table 3).
Table 3 |
|
|
|
|
|
|
Dirty
Devil Drainage Area |
|
|
|
|
|
|
HUC_10 |
HU_10_Name |
Shape_Area (m^2) |
Shape_Area (km^2) |
|
Shape Area (mi^2) |
|
1407000408 |
Lower Dirty |
326137972.7 |
326.1379727 |
|
125.9225754 |
|
1407000202 |
Headwaters Muddy Creek |
419029537.7 |
419.0295377 |
|
161.7882092 |
|
1407000204 |
Salt Wash-Muddy Creek |
451449431.8 |
451.4494318 |
|
174.3056003 |
|
1407000201 |
Ivie Creek |
663385884.6 |
663.3858846 |
|
256.1347223 |
|
1407000203 |
|
338727335.8 |
338.7273358 |
|
130.7833557 |
|
1407000207 |
Wild Horse Creek |
304816189.9 |
304.8161899 |
|
117.690189 |
|
1407000206 |
Red Canyon-Muddy Creek |
352701457.3 |
352.7014573 |
|
136.1787942 |
|
1407000403 |
Upper Dirty |
417976216.1 |
417.9762161 |
|
161.3815194 |
|
1407000205 |
Salt |
902300916.1 |
902.3009161 |
|
348.3803318 |
|
1407000301 |
|
1004475775 |
1004.475775 |
|
387.8302654 |
|
1407000208 |
Outlet Muddy Creek |
584417662.3 |
584.4176623 |
|
225.6449212 |
|
1407000303 |
|
896583306 |
896.583306 |
|
346.1727502 |
|
1407000402 |
|
215183048.1 |
215.1830481 |
|
83.08263944 |
|
1407000306 |
|
400267456.6 |
400.2674566 |
|
154.5441292 |
|
1407000401 |
|
229381149.3 |
229.3811493 |
|
88.56455698 |
|
1407000406 |
Middle Dirty |
370808952.3 |
370.8089523 |
|
143.1701371 |
|
1407000305 |
|
858902217.3 |
858.9022173 |
|
331.6240005 |
|
1407000405 |
|
234091961.8 |
234.0919618 |
|
90.38341185 |
|
1407000304 |
|
992904500.3 |
992.9045003 |
|
383.3625712 |
|
1407000407 |
|
247287953.8 |
247.2879538 |
|
95.47841286 |
|
1407000404 |
Beaver Canyon-Granite Creek |
208031956.1 |
208.0319561 |
|
80.32158738 |
|
1407000302 |
|
909872998.3 |
909.8729983 |
|
351.3039291 |
|
|
|
|
|
|
|
|
|
|
Total Drainage Area = |
11328.73 |
km^2 |
4374.048609 |
mi^2 |
|
|
|
|
|
|
|
|
HU_10_Name |
Shape_Area (m^2) |
Shape Area (km^2) |
|
Shape Area (mi^2) |
|
|
|
369981699 |
369.981699 |
|
142.8507328 |
|
|
|
|
|
|
|
|
|
|
Total Drainage Area = |
369.981699 |
km^2 |
142.8507328 |
mi^2 |
As can be seen from the drainage basin
delineation for each system, they represent 3 quite different spatial scales,
all of which are responding to the base level drop of
Drainage
Density
Drainage Density = Total Stream
Length /
Table 4
|
|
293680.1706 |
km^2 |
113390.5479 |
mi^2 |
|
|
|
|
|
|
From
summary statistics of the NDH Flowlines ==> |
Total
Stream Length in Drainage Basin Area = |
463652.849 |
km |
288100.5234 |
mi |
|
|
|
|
|
|
|
Drainage
Density = |
1.578767977 |
|
2.540780768 |
|
|
|
|
|
|
|
|
Dirty
Devil / |
11328.73388 |
km^2 |
4374.048609 |
mi^2 |
|
|
|
|
|
|
From
summary statistics of the NDH Flowlines ==> |
Total
Stream Length in Drainage Basin Area = |
17549.426 |
km |
10904.70775 |
mi |
|
|
|
|
|
|
|
Drainage
Density = |
1.549107445 |
|
2.493046769 |
|
Table 3 - continued |
|
|
|
|
|
|
North
Wash Creek Drainage Basin Area = |
369.981699 |
km^2 |
142.8507328 |
mi^2 |
|
|
|
|
|
|
From
summary statistics of the NDH Flowlines ==> |
Total
Stream Length in Drainage Basin Area = |
481.66807 |
km |
299.2946628 |
mi |
|
|
|
|
|
|
|
Drainage
Density = |
1.301869988 |
|
2.09515665 |
|
The topology of a basin depends in large part on the
interaction between hillslope and fluvial processes. Where a hillslope transitions from a straight
or convex form to a concave one is generally recognized as representing a
transition in dominant process. One of
the most fundamental ways to express this transition/interaction, and also one
of the most fundamental basin characteristics, is drainage density (Tucker and
Bras, 1998). By comparing the values for
the Upper Colorado, Dirty Devil /
When the 4 selected gage records
of mean annual flow on the Dirty Devil / Fremont were broken into 10 or 20 year
intervals, the t-test showed that MAF did not significantly vary through
time. Since North Wash is a directly
adjacent basin, it is assumed that its MAF has not varied through time either,
and that the 1950-1970 record of 1.20 cfs still holds true today (Table 4). çFollow the hyperlink to the excel file containing the gage records,
broken down, and the results of the t-test as run using XLStat.
North Wash MAF was also estimated
by dividing each gage’s MAF by the USGS drainage area above the gage. This flow per unit area for each gage was
then applied to
Table 5 |
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|||
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|||
|
Most
Upstream |
|
|
|
3rd |
|
|
SEVEN
MILE CREEK NEAR |
|
|
|
||||
|
|
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|
|
|
|
|
|
Mean Annual Flow |
Drainage Area (mi^2) Above the Gage |
cfs / mi^2 |
|
Mean Annual Flow |
Drainage Area (mi^2) Above the Gage |
cfs / mi^2 |
|
15.157 |
24 |
0.631542 |
|
74.281 |
1208 |
0.061491 |
|
|
|
|
|
|
|
|
|
Applied
to |
90.20309625 |
cfs |
|
Applied
to |
8.782744396 |
cfs |
|
|
|
|
|
|
|
|
|
2nd |
|
|
|
Most
Downstream |
|
|
PINE
CREEK NEAR |
|
DIRTY DEVIL
R AB POISON SP WSH NR HANKSVILLE UT |
|||||
|
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|
|
|
|
|
Mean Annual Flow |
Drainage Area (mi^2) Above the Gage |
cfs / mi^2 |
|
Mean Annual Flow |
Drainage Area (mi^2) Above the Gage |
cfs / mi^2 |
|
3.986 |
104 |
0.038327 |
|
97.174 |
4159 |
0.023365 |
|
|
|
|
|
|
|
|
|
Applied
to |
5.474234423 |
cfs |
|
Applied
to |
3.337187406 |
cfs |
It can be seen that the most upstream (and farthest from NW)
gage provided the worst approximation of the North Wash MAF and the most
downstream (and closest to NW) provided the best. As shown in table 4, the gage at Poison
Spider Wash also has the longest flow record (from 1949-1993 and 2002-2005),
adding robustness to the MAF calculated for NW from the contribution per unit
area value. The difference between 1.191
cfs and 3.337 seems small at only 2.15 cfs, but it represents an increase of
35% which is not trivial. However, MAF
is not generally regarded as the flow responsible for geomorphic work so it is
not necessary at this point to reach an accurate present day value of MAF on
Conclusion
GIS is an extremely powerful tool for organizing and analyzing data sets pertaining to water resource issues. This utility is further enhanced by the initiative of many different groups collaborating to produce comprehensive datasets like NHD and NHDplus, among others. However, this term project stressed the fact that some data errors exist and that adaptations and processing are still necessary (although greatly reduced) to analyze the data. It also stressed that computing power is still a limiting factor on working with a highly detailed representation of a large physical area. At the end of the day though, fundamental and important basin characteristics were calculated in an accurate and easily displayed format which can be packaged and distributed; the very essence of geographic information systems.
References:
Data
NHD
NHDplus
http://www.horizon-systems.com/nhdplus/
USGS Gage Records
http://waterdata.usgs.gov/ut/nwis/rt
Publications
Ferrari, Ronald
L. 1986.
1986
Webb et al. 2004.
Climatic Fluctuations, Drought, and Flow in the
Tucker, Gregory E. and Bras, Rafael L., 1998. Hillslope Processes, Drainage Density, and Landscape Morphology. Water Resources Research, Vol. 34, NO 10, pp. 2751-2764