Comparison of Methods for Estimating Stream Channel Gradient Using GIS
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Geomorphic Classification of Rivers
9.36 Geomorphic Classification of Rivers JM Buffington, U.S. Forest Service, Boise, ID, USA DR Montgomery, University of Washington, Seattle, WA, USA Published by Elsevier Inc. 9.36.1 Introduction 730 9.36.2 Purpose of Classification 730 9.36.3 Types of Channel Classification 731 9.36.3.1 Stream Order 731 9.36.3.2 Process Domains 732 9.36.3.3 Channel Pattern 732 9.36.3.4 Channel–Floodplain Interactions 735 9.36.3.5 Bed Material and Mobility 737 9.36.3.6 Channel Units 739 9.36.3.7 Hierarchical Classifications 739 9.36.3.8 Statistical Classifications 745 9.36.4 Use and Compatibility of Channel Classifications 745 9.36.5 The Rise and Fall of Classifications: Why Are Some Channel Classifications More Used Than Others? 747 9.36.6 Future Needs and Directions 753 9.36.6.1 Standardization and Sample Size 753 9.36.6.2 Remote Sensing 754 9.36.7 Conclusion 755 Acknowledgements 756 References 756 Appendix 762 9.36.1 Introduction 9.36.2 Purpose of Classification Over the last several decades, environmental legislation and a A basic tenet in geomorphology is that ‘form implies process.’As growing awareness of historical human disturbance to rivers such, numerous geomorphic classifications have been de- worldwide (Schumm, 1977; Collins et al., 2003; Surian and veloped for landscapes (Davis, 1899), hillslopes (Varnes, 1958), Rinaldi, 2003; Nilsson et al., 2005; Chin, 2006; Walter and and rivers (Section 9.36.3). The form–process paradigm is a Merritts, 2008) have fostered unprecedented collaboration potentially powerful tool for conducting quantitative geo- among scientists, land managers, and stakeholders to better morphic investigations. -
Stream Restoration, a Natural Channel Design
Stream Restoration Prep8AICI by the North Carolina Stream Restonltlon Institute and North Carolina Sea Grant INC STATE UNIVERSITY I North Carolina State University and North Carolina A&T State University commit themselves to positive action to secure equal opportunity regardless of race, color, creed, national origin, religion, sex, age or disability. In addition, the two Universities welcome all persons without regard to sexual orientation. Contents Introduction to Fluvial Processes 1 Stream Assessment and Survey Procedures 2 Rosgen Stream-Classification Systems/ Channel Assessment and Validation Procedures 3 Bankfull Verification and Gage Station Analyses 4 Priority Options for Restoring Incised Streams 5 Reference Reach Survey 6 Design Procedures 7 Structures 8 Vegetation Stabilization and Riparian-Buffer Re-establishment 9 Erosion and Sediment-Control Plan 10 Flood Studies 11 Restoration Evaluation and Monitoring 12 References and Resources 13 Appendices Preface Streams and rivers serve many purposes, including water supply, The authors would like to thank the following people for reviewing wildlife habitat, energy generation, transportation and recreation. the document: A stream is a dynamic, complex system that includes not only Micky Clemmons the active channel but also the floodplain and the vegetation Rockie English, Ph.D. along its edges. A natural stream system remains stable while Chris Estes transporting a wide range of flows and sediment produced in its Angela Jessup, P.E. watershed, maintaining a state of "dynamic equilibrium." When Joseph Mickey changes to the channel, floodplain, vegetation, flow or sediment David Penrose supply significantly affect this equilibrium, the stream may Todd St. John become unstable and start adjusting toward a new equilibrium state. -
Lower Wisconsin River Main Stem
LOWER WISCONSIN RIVER MAIN STEM The Wisconsin River begins at Lac Vieux Desert, a lake in Vilas County that lies on the border of Wisconsin and the Lower Wisconsin River Upper Pennisula in Michigan. The river is approximately At A Glance 430 miles long and collects water from 12,280 square miles. As a result of glaciation across the state, the river Drainage Area: 4,940 sq. miles traverses a variety of different geologic and topographic Total Stream Miles: 165 miles settings. The section of the river known as the Lower Wisconsin River crosses over several of these different Major Public Land: geologic settings. From the Castle Rock Flowage, the river ♦ Units of the Lower Wisconsin flows through the flat Central Sand Plain that is thought to State Riverway be a legacy of Glacial Lake Wisconsin. Downstream from ♦ Tower Hill, Rocky Arbor, and Wisconsin Dells, the river flows through glacial drift until Wyalusing State Parks it enters the Driftless Area and eventually flows into the ♦ Wildlife areas and other Mississippi River (Map 1, Chapter Three ). recreation areas adjacent to river Overall, the Lower Wisconsin River portion of the Concerns and Issues: Wisconsin River extends approximately 165 miles from the ♦ Nonpoint source pollution Castle Rock Flowage dam downstream to its confluence ♦ Impoundments with the Mississippi River near Prairie du Chien. There are ♦ Atrazine two major hydropower dams operate on the Lower ♦ Fish consumption advisories Wisconsin, one at Wisconsin Dells and one at Prairie Du for PCB’s and mercury Sac. The Wisconsin Dells dam creates Kilbourn Flowage. ♦ Badger Army Ammunition The dam at Prairie Du Sac creates Lake Wisconsin. -
Tualatin River Basin Rapid Stream Assessment Technique (RSAT)
Tualatin River Basin Rapid Stream Assessment Technique (RSAT) Watersheds 2000 Field Methods Clean Water Services Watershed Management Division 155 North First Ave Hillsboro, OR 97124 July 2000 Acknowledgements Rapid Stream Assessment Technique Adapted from Rapid Stream Assessment Technique (RSAT) Field Methods 1996 Montgomery County Department of Environmental Protection Division of Water Resources Management Montgomery County, Maryland and Department of Environmental Programs Metropolitan Washington Council of Governments 777 North Capitol St., NE Washington, DC 20002 Rapid Stream Assessment Technique Table of Contents Page I. Introduction.............................................................................. 1 I. Tualatin Basin RSAT Field Protocols..................................... 2 A. Field Survey Preparation, Planning, and Data Organization......................2 A. Stream Flow Characterization Valley Profile, Reach Gradient..................3 Velocity Volume/discharge A. Stream Cross Section Characterization ........................................................4 Bankfull Width Bed Width Wetted Width Average Wetted Depth Maximum Bankfull Depth Over Bank Height Bankfull Height Bank Angle Ratio A. Stream Channel Characterization..................................................................7 Bank Material Bank Stability and Undercut Banks Recent Bed Downcutting Dominant Bed Material Deposition Material Embeddedness A. Water Quality.................................................................................................11 -
Watershed Technical Analysis
Trout Creek Watershed Stormwater Management Plan SECTION III: WATERSHED TECHNICAL ANALYSIS A. Watershed Modeling An initial step this study of the Trout Creek watershed was the selection of a stormwater simulation model to be used in the analysis. To provide a reasonable estimate of existing flows within the watershed to serve as a baseline for the study of stormwater management and to effectively evaluate the hydrologic response of the watershed to various changes in stormwater management it was necessary to select a model which: • Modeled design storms of various durations and frequencies to produce routed hydrographs which could be combined • Was adaptable to the size of subwatersheds in this study • Could evaluate specific physical characteristics of the rainfall-runoff process • Did not require an excessive amount of input data yet yielded reliable results The model selected for use in this study was the U. S. Army Corps of Engineers, Hydrologic Engineering Center, Hydrologic Modeling System (HEC-HMS) for the following reasons: • It had been developed at the Hydrologic Engineering Center specifically for the analysis of the timing of surface flow contributions to peak rates at various locations in a watershed • Although originally developed as an urban runoff simulation model, data requirements make it easily adaptable to a rural situation • Input parameters provide a flexible calibration process • It has the ability to analyze reservoir or detention basin routing effects • It is accepted by the Pennsylvania Department of Environmental Protection Although other models, such as TR-20, may provide essentially the same results as the HEC-HMS, HMS’s ability to compare subwatershed contributions in a peak flow presentation table make it specifically attractive for this study. -
Waterbody Classifications, Streams Based on Waterbody Classifications
Waterbody Classifications, Streams Based on Waterbody Classifications Waterbody Type Segment ID Waterbody Index Number (WIN) Streams 0202-0047 Pa-63-30 Streams 0202-0048 Pa-63-33 Streams 0801-0419 Ont 19- 94- 1-P922- Streams 0201-0034 Pa-53-21 Streams 0801-0422 Ont 19- 98 Streams 0801-0423 Ont 19- 99 Streams 0801-0424 Ont 19-103 Streams 0801-0429 Ont 19-104- 3 Streams 0801-0442 Ont 19-105 thru 112 Streams 0801-0445 Ont 19-114 Streams 0801-0447 Ont 19-119 Streams 0801-0452 Ont 19-P1007- Streams 1001-0017 C- 86 Streams 1001-0018 C- 5 thru 13 Streams 1001-0019 C- 14 Streams 1001-0022 C- 57 thru 95 (selected) Streams 1001-0023 C- 73 Streams 1001-0024 C- 80 Streams 1001-0025 C- 86-3 Streams 1001-0026 C- 86-5 Page 1 of 464 09/28/2021 Waterbody Classifications, Streams Based on Waterbody Classifications Name Description Clear Creek and tribs entire stream and tribs Mud Creek and tribs entire stream and tribs Tribs to Long Lake total length of all tribs to lake Little Valley Creek, Upper, and tribs stream and tribs, above Elkdale Kents Creek and tribs entire stream and tribs Crystal Creek, Upper, and tribs stream and tribs, above Forestport Alder Creek and tribs entire stream and tribs Bear Creek and tribs entire stream and tribs Minor Tribs to Kayuta Lake total length of select tribs to the lake Little Black Creek, Upper, and tribs stream and tribs, above Wheelertown Twin Lakes Stream and tribs entire stream and tribs Tribs to North Lake total length of all tribs to lake Mill Brook and minor tribs entire stream and selected tribs Riley Brook -
Stream Gradient Settings Variable
Designing Sustainable Landscapes: Stream gradient settings variable A project of the University of Massachusetts Landscape Ecology Lab Principals: • Kevin McGarigal, Professor • Brad Compton, Research Associate • Ethan Plunkett, Research Associate • Bill DeLuca, Research Associate • Joanna Grand, Research Associate With support from: • US Fish and Wildlife Service, North Atlantic-Appalachian Region • Northeast Climate Adaptation Science Center (USGS) • University of Massachusetts, Amherst Reference: McGarigal K, Compton BW, Plunkett EB, DeLuca WV, and Grand J. 2020. Designing sustainable landscapes: stream gradient settings variable. Report to the North Atlantic Conservation Cooperative, US Fish and Wildlife Service, Northeast Region. DSL Data Products: Stream gradient General description Stream gradient is one of several ecological settings variables that collectively characterize the biophysical setting of each 30 m cell at a given point in time (McGarigal et al 2020). Stream gradient (Fig. 1) is a measure of the percent slope of a stream, which is a primary determinate of water velocity and thus sediment and nutrient transport, and habitat for aquatic plants, invertebrate, fish, and other organisms. Stream gradient is often approximated by categories such as pool, riffle, run, and cascade. Stream gradient is 0% for lentic waterbodies, palustrine, and uplands. It ranges from 0% to infinity (theoretically) for streams. We set a ceiling of gradient at 100%, and then log-scale the trimmed gradient. Use and interpretation of this layer This ecological settings variable is used for the similarity and connectedness ecological integrity metrics. This layer carries the following assumptions: • The digital elevation model is accurate. Although this seems to be true at broader scales, the NED does include many fine-scale ∞ errors. -
Section 5 Low-Gradient Streams
Chapter 4 Surface Processes Section 5 Low-Gradient Streams What Do You See? Learning Outcomes Think About It In this section, you will During the Mississippi River flood of 1993, stream gauges at • Use models and real-time 42 stations along the river recorded their highest water levels on streamflow data to understand record. The effects of the flood were catastrophic. Seventy-five the characteristics of low- towns were completely covered by water, 54,000 people had to gradient streams. be evacuated, and 47 people lost their lives. • Explore how models can help scientists interpret the natural • What happens during a flood? world. Record your ideas about this question in your Geo log. Include a • Identify areas likely to have sketch of the water line (the line where the water surface meets the low-gradient streams. riverbank) during normal flow in the river and during a flood. Be • Describe hazards of low- prepared to discuss your responses with your small group and gradient streams. the class. Investigate In this Investigate, you will use a stream table to model how a low-gradient stream flows and what effects this can have on the areas surrounding the stream. Part A: Investigating Low-Gradient Streams Using a Stream Table 1. To model a low-gradient stream, set up a stream table as follows. Use the photograph on the next page to help you with your setup. 418 EarthComm EC_Natl_SE_C4.indd 418 7/12/11 9:55:03 AM Section 5 Low-Gradient Streams • Make a batch of river sediment by 3. Turn on a water source or use a beaker mixing a small portion of silt with filled with water to create a gently a large portion of fine sand. -
Channel Changes and Flood Frequency on the Upper Main Stem of the Nooksack River, Whatcom County, Washington
Western Washington University Western CEDAR WWU Graduate School Collection WWU Graduate and Undergraduate Scholarship Winter 1993 Channel Changes and Flood Frequency on the Upper Main Stem of the Nooksack River, Whatcom County, Washington Roger G. Bertschi Western Washington University, [email protected] Follow this and additional works at: https://cedar.wwu.edu/wwuet Part of the Geology Commons Recommended Citation Bertschi, Roger G., "Channel Changes and Flood Frequency on the Upper Main Stem of the Nooksack River, Whatcom County, Washington" (1993). WWU Graduate School Collection. 717. https://cedar.wwu.edu/wwuet/717 This Masters Thesis is brought to you for free and open access by the WWU Graduate and Undergraduate Scholarship at Western CEDAR. It has been accepted for inclusion in WWU Graduate School Collection by an authorized administrator of Western CEDAR. For more information, please contact [email protected]. CHANNEL CHANGES AND FLOOD FREQUENCY ON THE UPPER MAIN STEM OF THE NOOKSACK RIVER, WHATCOM COUNTY, WASHINGTON by Roger G. Bertschi Accepted in Partial Completion of the Requirements for the Degree Master of Science Advisory Committee MASTER'S THESIS In presenting this thesis in partial fulfillment of the requirements for a master's degree at Western Washington University, I agree that the Library shall make its copies freely available for inspection. I further agree that extensive copying of this thesis is allowable only for scholarly purposes. It is understood, however, that any copying or publication of this thesis for commercial purposes, or for financial gain, shall not be allowed without mv permission. Signature Date MASTER’S THESIS In presenting this thesis in partial fulfillment of the requirements for a master’s degree at Western Washington University, I grant to Western Washington University the non-exclusive royalty-free right to archive, reproduce, distribute, and display the thesis in any and all forms, including electronic format, via any digital library mechanisms maintained by WWU. -
TS3E Rosgen Stream Classification Technique
Technical Rosgen Stream Classification Supplement 3E Technique—Supplemental Materials (210–VI–NEH, August 2007) Technical Supplement 3E Rosgen Stream Classification Part 654 Technique—Supplemental Materials National Engineering Handbook Issued August 2007 Cover photo: The Rosgen stream classification system uses morphometric data to characterize streams. Advisory Note Techniques and approaches contained in this handbook are not all-inclusive, nor universally applicable. Designing stream restorations requires appropriate training and experience, especially to identify conditions where various approaches, tools, and techniques are most applicable, as well as their limitations for design. Note also that prod- uct names are included only to show type and availability and do not constitute endorsement for their specific use. (210–VI–NEH, August 2007) Technical Rosgen Stream Classification Supplement 3E Technique—Supplemental Materials Contents Purpose TS3E–1 Data requirements TS3E–1 Stream reach TS3E–1 Plan view (planform) type and level I classification TS3E–1 Valley types .......................................................................................................TS3E–2 Channel slope—level I ....................................................................................TS3E–2 Morphological description (level II classification) TS3E–2 Channel slope—level II ...................................................................................TS3E–9 Bankfull discharge validations .......................................................................TS3E–9 -
Memorandum 6E. Review of Main Stem Restoration Project; Golden
Memorandum To: Bassett Creek Watershed Management Commission From: Barr Engineering Co. Subject: Item 6E – Review of Main Stem Restoration Project; Golden Valley Rd. to Irving Ave. N. – 50% Development Plans (CIP 2012 CR) BCWMC September 19, 2013 Meeting Agenda Date: September 12, 2013 Project: 23270051 2013 626 6E. Review of Main Stem Restoration Project; Golden Valley Rd. to Irving Ave. N. – 50% Development Plans (CIP 2012 CR) Summary Proposed Work: Main Stem of Bassett Creek Restoration Project (CIP 2012 CR) Basis for Commission Review: 50% plan review Change in Impervious Surface: N.A. Recommendation: Conditional Approval The Minneapolis Park and Recreation Board (MPRB) Main Stem of Bassett Creek restoration project (CIP 2012 CR) is being funded by the BCWMC’s ad valorem levy (via Hennepin County) and by a Minnesota Board of Water and Soil Resources Clean Water Fund Grant. The MPRB provided the 50% design plans to the BCWMC for review and comment, as set forth in the BCWMC CIP project flow chart developed by the TAC. Feasibility Study Summary The Feasibility Report for the 2012 Bassett Creek Main Stem Restoration Project – Golden Valley Road to Irving Avenue North (Barr, June 2011) was completed by the BCWMC to develop approaches to stabilize eroding stream banks along the Main Stem of Bassett Creek. Between Golden Valley Road and Irving Avenue North, Bassett Creek flows through Golden Valley and Minneapolis, and is nearly entirely contained within MPRB-owned land in Theodore Wirth Regional Park, Theodore Wirth Golf Course, and city parks. The goal of the project is to reduce the phosphorus loading to the Main Stem of Bassett Creek by 60 pounds per year and to consolidate sediments in an in-stream pond upstream of Highway 55. -
Surface Water Types and Sediment Distribution Patterns at the Confluence of Mega Rivers: the Solimões-Amazon and Negro Rivers Junction
Surface water types and sediment distribution patterns at the confluence of mega rivers: the Solimões-Amazon and Negro rivers junction Edward Park1, Edgardo M. Latrubesse1 1University of Texas at Austin, Department of Geography and the Environment, Austin, TX, USA Correspondence to: Edward Park, Tel +1-512-230-4603 Fax +1-512-471-5049 University of Texas at Austin, SAC 4.178, 2201 Speedway, Austin, TX 78712, USA Email address: [email protected] This article has been accepted for publication and undergone full peer review but has not been through the copyediting, typesetting, pagination and proofreading process which may lead to differences between this version and the Version of Record. Please cite this article as an ‘Accepted Article’, doi: 10.1002/2014WR016757 This article is protected by copyright. All rights reserved. Abstract Large river channel confluences are recognized as critical fluvial features because both intensive and extensive hydrophysical and geoecological processes take place at this interface. However, identifications of suspended sediment routing patterns through channel junctions and the roles of tributaries on downstream sediment transport in large rivers are still poorly explored. In this paper, we propose a remote sensing-based approach to characterize the spatiotemporal patterns of the post-confluence suspended sediment transport by mapping the surface water distribution in the ultimate example of large river confluence on Earth where distinct water types meet: The Solimões-Amazon (white water) and Negro (black water) rivers. The surface water types distribution was modeled for three different years: average hydrological condition (2007) and two years when extreme events occurred (drought-2005 and flood-2009).