Adam L. Majeski

GIS in Water Resources

Term Project – Final Report

December 8, 2006

 

A Brief Introduction to My Masters Thesis

 

Lake Powell is created by Glen Canyon Dam, on the Colorado River.  The drainage area above the lake encompasses ~108,335 mi2, collecting enough water to make Lake Powell the 2nd largest reservoir in the U.S and the current depocenter for 868,231 acre-feet (as measured in 1986) of sediment (Ferrari, 1988).  Since dam closure in 1963, the reservoir has experienced one transgression, filling to the top of its active storage (3700 ft) in 1980, and a minor regression from 1988 to 1993.  The lake recovered by 1999, but this year also marked the beginning of the most significant flow deficit in the Colorado River basin in over 100 years (Webb et al, 2004).  As a result, the lake dropped 150 ft over a 6 year period, and the delta sediments ~95 miles upstream of the dam, near the marina of Hite, were exposed for the first time.  Since then, the Colorado River has been down cutting and reworking these sediments.  Furthermore, delta sediments accumulating in side canyons and tributaries of the Colorado have been subject to exposure and reworking as well.  Of particular interest are two tributaries, North Wash Creek and the Dirty Devil River, which join the Colorado at its delta near Hite.  The Dirty Devil River is the only minor tributary of the lake to show significant sediment accumulation and it is one of the few to have its delta extend to the main channel storage area of the Colorado River.  North Wash Creek enters ~3 km downstream of the Dirty Devil River and contrasts it greatly; its delta does not extend to the Colorado River and its sediment accumulation has been minor by comparison. Therefore, the current lowered reservoir state sets up a perfect natural laboratory to allow the response of these three different fluvial systems to the same drop in base-level to be compared and contrasted.  

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 Colorado River and their associated stream networks.  From this large data set the HUC-10 watersheds of the Dirty Devil/Fremont River and North Wash creek and their associated stream networks was also isolated.  The data was organized into personal geodatabases for the Colorado River and for the Dirty Devil/Fremont, North Wash features and everything was reprojected into the USA Contiguous Albers Equal Area Conic coordinate system using the NAD 83.

 

            Drainage Basin Delineation

            For the Colorado River above Lees Ferry, the HUC-6 basins were contained in 8 separate geodatabases for region 14.  Each of these feature class layers were put into ArcGIS and the Colorado Drainage basin was identified by overlaying the NHDflowline layer and selecting the HUC-6’s it covered (the shape was also compared to a figure in the 1986 Bureau of Reclamation study).  These were exported into a new feature class, duplicates from overlap were removed, and the data set was finalized.  Drainage basin area was computed from the feature class’s attribute table category shape area with the summarize command.

           

For the Dirty Devil / Fremont Rivers, the HUC-8 subbasins were used as a template to select the necessary HUC-10 watersheds and the associated NHD flowlines.  The HUC-8 for the Dirty Devil and Fremont Rivers were identified via the HUC-8 name column of the attribute table, and careful observation of the NHD flowlines in conjunction with previous research also dictated the inclusion of the Muddy Creek subbasin.  For North Wash Creek a major highway feature class was added because the stream is known to trace Utah Highway 95 south from Hanksville.  Using this spatial relationship and the identify tool, the HUC-10 for North Wash easily identified and a quick visual inspection of the small area showed that the entire drainage area had been captured.  Again, drainage area was calculated using the summarize command on each feature class’ shape area attribute.  See Figure 1.

 

           

            Drainage Density

To compute drainage density, the NHD flowlines were added for the Upper Colorado Basin.  In the case of the Dirty Devil / Fremont and North Wash, the flowline file was clipped by using the select by location tool and the drainage area polygons as the template.  It is important to note that the NHD flowlines were used and NOT the NHDplus flowlines, because the NHD are of higher resolution (Figure 2).  The summary command was used to sum the length of the drainage lines and this value was entered into an excel spread sheet, along with the drainage area.  Drainage Density = Total Stream Length / Drainage Area.

 

            North Wash Gage Interpolation

            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 / Fremont and North Wash were selected by location and exported into their own feature class.  Then, the gages on the DDF were further thinned to those containing at least 15 years of record.  Each of these gages was ten selected with the identify tool and the active hyperlink displayed in the information box was followed to download the gage records (Figure 3).  These were then placed into excel for analysis.  Records were broken into intervals of the first and last 10 or 20 years and averaged.  These averages were compared with the t-test to determine if they were significantly different, or if MAF was consistant for any given 10 to 20 year period.  If MAF on the DDF showed to be invariant with time, then it could be assumed that the MAF on NW is as well.  Therefore, the 1950-1970 MAF value would still hold true today. 

            As another method to calculate MAF on North Wash, the drainage area above each gage selected above was gathered from the info file.  The MAF value was divided by this drainage area to compute a cfs per mi^2 vale, which was then multiplied by the drainage area of North Wash.

 

Results

 

            Drainage Basin Delineation

            The Upper Colorado Drainage Basin above Lees Ferry, AZ spans 5 states (Wyoming, Utah, Colorado New Mexico and Arizona) and covers a total area of 113,390.55 sq. mi. (Figure 4).  It is comprised of the10 HUC-6 basins listed in the table 1 and also displayed on figure 4.

 

Table 1

 

 

HUC_6

HU_6_Name

Area (km^2)

Area (mi^2)

140100

Colorado Headwaters

25496.89

9844.40

140200

Gunnison

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

Upper San Juan

37583.40

14511.03

140802

Lower San Juan

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 Paria River and this area was removed by selecting its HUC-8 subbasin (Figure 5).  Several other minor tributaries also enter below the dam and their NHDplus catchments were overlaid and selected, roughly removing all of their excess drainage area as well.  The end result was a drainage area of 111,726.54 sq. mi., which is larger than the108,335 sq. mi. drainage area reported by the Bureau of Reclamation website on Glen Canyon Dam (Table 2).  To reconcile this discrepancy flowline network tracing was implemented, with considerable difficulty, to isolate the NHDplus flowlines above Glen Canyon Dam (and therefore isolate the drainage area above the dam because each flowline is attributed with its contributing area via linking the flowlineattributeflow table to the flowline feature class).  Upon tracing it became apparent that the network was not entirely connected, and that the effort to connect each segment by hand would be far too time consuming and also require referencing DEM’s to properly connect many of the segments (Figure 6).  So the effort would not be in vain however, the connected and traced network was saved as a feature class and used to select by location the associated catchments.  Then, those catchments not selected because of unconnected flowlines were roughly selected by hand.  The total sum of the these two areas was very near 111,700 sq. mi., confirming that calculating the area above GCD with GIS will yield a higher value than that reported by the Bureau of Reclamation.

Figure 5 – Removing the Paria River drainage area to calculate the drainage area above Glen Canyon Dam.

 
 

 

 


Table 2

 

 

 

 

 

 

 

Total Drainage Area Below GCD =

4309760147.3100

m^2

4309.760147

km^2

 

1664.007698

mi^2

 

 

 

 

 

 

 

 

Upper Colorado River Drainage Basin Area =

 

 

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).  North Wash creek drains an area of 142.85 sq. mi. and is represented by 1 HUC-10 watershed (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 Devil River

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

Willow Spring Wash

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 Devil River

417976216.1

417.9762161

 

161.3815194

 

1407000205

Salt Wash

902300916.1

902.3009161

 

348.3803318

 

1407000301

Headwaters Fremont River

1004475775

1004.475775

 

387.8302654

 

1407000208

Outlet Muddy Creek

584417662.3

584.4176623

 

225.6449212

 

1407000303

Deep Creek-Fremont River

896583306

896.583306

 

346.1727502

 

1407000402

Robbers Roost Canyon

215183048.1

215.1830481

 

83.08263944

 

1407000306

Town Wash-Fremont River

400267456.6

400.2674566

 

154.5441292

 

1407000401

Dry Valley Wash

229381149.3

229.3811493

 

88.56455698

 

1407000406

Middle Dirty Devil River

370808952.3

370.8089523

 

143.1701371

 

1407000305

Sweetwater Creek-Fremont River

858902217.3

858.9022173

 

331.6240005

 

1407000405

French Spring Fork-Happy Canyon

234091961.8

234.0919618

 

90.38341185

 

1407000304

Sandy Creek-Fremont River

992904500.3

992.9045003

 

383.3625712

 

1407000407

Poison Spring Canyon

247287953.8

247.2879538

 

95.47841286

 

1407000404

Beaver Canyon-Granite Creek

208031956.1

208.0319561

 

80.32158738

 

1407000302

Pine Creek-Fremont River

909872998.3

909.8729983

 

351.3039291

 

 

 

 

 

 

 

 

 

 

Total Drainage Area =

11328.73

km^2

4374.048609

mi^2

North Wash Drainage Area

 

 

 

 

 

 

HU_10_Name

Shape_Area (m^2)

Shape Area (km^2)

 

Shape Area (mi^2)

 

 

North Wash

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 Lake Powell.  By understanding the magnitude of this difference, each system’s response can be more fully understood and responses dependent or independent of basin size will be easier to identify. 

 

Drainage Density

            Drainage Density = Total Stream Length / Total Basin Area.  Table 4 reports the results of drainage density analysis for the Upper Colorado, Dirty Devil / Fremont, and North Wash drainage areas.

 

Table 4

 

Colorado River Drainage Basin Area =

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 / Fremont River Drainage Basin Area =

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 / Fremont, and North Wash it is apparent that even though the spatial scales of the basins are quite different, the interaction between hillslope and fluvial processes is comparable.  Therefore it is reasonable to assume that any difference in the response of the systems to the base level drop of Lake Powell is not on account of differences in the variables that influence drainage density, such as vegetation, precipitation, soil/rock types, relief, and etcetera. 

           

North Wash Gage Interpolation

            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 North Wash’s drainage area to generate MAF.  Table 5 shows the results.

 

Table 5

 

 

 

 

North Wash's MAF = 1.191 cfs from the 1950-1970 gage record

 

 

 

 

 

Most Upstream

 

 

 

3rd

 

 

SEVEN MILE CREEK NEAR FISH LAKE, UT

 

FREMONT RIVER NEAR CAINEVILLE, UT

 

 

 

 

 

 

 

 

 

 

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 North Wash's Drainage Area yields a MAF =

90.20309625

cfs

 

Applied to North Wash's Drainage Area yields a MAF =

8.782744396

cfs

 

 

 

 

 

 

 

 

 

2nd

 

 

 

Most Downstream

 

 

PINE CREEK NEAR BICKNELL, UTAH

 

DIRTY DEVIL R AB POISON SP WSH NR HANKSVILLE UT

 

 

 

 

 

 

 

 

 

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 North Wash's Drainage Area yields a MAF =

5.474234423

cfs

 

Applied to North Wash's Drainage Area yields a MAF =

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 North Wash.  However, by showing that it is more than an order of magnitude smaller than that of the Dirty Devil and over 3 orders of magnitude smaller than that of the Colorado it again provides a frame of reference in which system responses to base level drop can be compared.

 

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

http://nhd.usgs.gov/

 

NHDplus

http://www.horizon-systems.com/nhdplus/

 

USGS Gage Records

http://waterdata.usgs.gov/ut/nwis/rt

 

Publications

Ferrari, Ronald L.  1986.  1986 Lake Powell Survey.  Bureau of Reclamation, Denver Office, December 1988.

 

Webb et al.  2004.  Climatic Fluctuations, Drought, and Flow in the Colorado River Basin.  USGS Fact Sheet 2004-3062 Version 2, August 2004.

 

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