Scaling Relationships Between Bed Load Volumes, Transport Distances
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Measurement of Bedload Transport in Sand-Bed Rivers: a Look at Two Indirect Sampling Methods
Published online in 2010 as part of U.S. Geological Survey Scientific Investigations Report 2010-5091. Measurement of Bedload Transport in Sand-Bed Rivers: A Look at Two Indirect Sampling Methods Robert R. Holmes, Jr. U.S. Geological Survey, Rolla, Missouri, United States. Abstract Sand-bed rivers present unique challenges to accurate measurement of the bedload transport rate using the traditional direct sampling methods of direct traps (for example the Helley-Smith bedload sampler). The two major issues are: 1) over sampling of sand transport caused by “mining” of sand due to the flow disturbance induced by the presence of the sampler and 2) clogging of the mesh bag with sand particles reducing the hydraulic efficiency of the sampler. Indirect measurement methods hold promise in that unlike direct methods, no transport-altering flow disturbance near the bed occurs. The bedform velocimetry method utilizes a measure of the bedform geometry and the speed of bedform translation to estimate the bedload transport through mass balance. The bedform velocimetry method is readily applied for the estimation of bedload transport in large sand-bed rivers so long as prominent bedforms are present and the streamflow discharge is steady for long enough to provide sufficient bedform translation between the successive bathymetric data sets. Bedform velocimetry in small sand- bed rivers is often problematic due to rapid variation within the hydrograph. The bottom-track bias feature of the acoustic Doppler current profiler (ADCP) has been utilized to accurately estimate the virtual velocities of sand-bed rivers. Coupling measurement of the virtual velocity with an accurate determination of the active depth of the streambed sediment movement is another method to measure bedload transport, which will be termed the “virtual velocity” method. -
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. -
Secondary Flow Effects on Deposition of Cohesive Sediment in A
water Article Secondary Flow Effects on Deposition of Cohesive Sediment in a Meandering Reach of Yangtze River Cuicui Qin 1,* , Xuejun Shao 1 and Yi Xiao 2 1 State Key Laboratory of Hydroscience and Engineering, Tsinghua University, Beijing 100084, China 2 National Inland Waterway Regulation Engineering Research Center, Chongqing Jiaotong University, Chongqing 400074, China * Correspondence: [email protected]; Tel.: +86-188-1137-0675 Received: 27 May 2019; Accepted: 9 July 2019; Published: 12 July 2019 Abstract: Few researches focus on secondary flow effects on bed deformation caused by cohesive sediment deposition in meandering channels of field mega scale. A 2D depth-averaged model is improved by incorporating three submodels to consider different effects of secondary flow and a module for cohesive sediment transport. These models are applied to a meandering reach of Yangtze River to investigate secondary flow effects on cohesive sediment deposition, and a preferable submodel is selected based on the flow simulation results. Sediment simulation results indicate that the improved model predictions are in better agreement with the measurements in planar distribution of deposition, as the increased sediment deposits caused by secondary current on the convex bank have been well predicted. Secondary flow effects on the predicted amount of deposition become more obvious during the period when the sediment load is low and velocity redistribution induced by the bed topography is evident. Such effects vary with the settling velocity and critical shear stress for deposition of cohesive sediment. The bed topography effects can be reflected by the secondary flow submodels and play an important role in velocity and sediment deposition predictions. -
River Dynamics 101 - Fact Sheet River Management Program Vermont Agency of Natural Resources
River Dynamics 101 - Fact Sheet River Management Program Vermont Agency of Natural Resources Overview In the discussion of river, or fluvial systems, and the strategies that may be used in the management of fluvial systems, it is important to have a basic understanding of the fundamental principals of how river systems work. This fact sheet will illustrate how sediment moves in the river, and the general response of the fluvial system when changes are imposed on or occur in the watershed, river channel, and the sediment supply. The Working River The complex river network that is an integral component of Vermont’s landscape is created as water flows from higher to lower elevations. There is an inherent supply of potential energy in the river systems created by the change in elevation between the beginning and ending points of the river or within any discrete stream reach. This potential energy is expressed in a variety of ways as the river moves through and shapes the landscape, developing a complex fluvial network, with a variety of channel and valley forms and associated aquatic and riparian habitats. Excess energy is dissipated in many ways: contact with vegetation along the banks, in turbulence at steps and riffles in the river profiles, in erosion at meander bends, in irregularities, or roughness of the channel bed and banks, and in sediment, ice and debris transport (Kondolf, 2002). Sediment Production, Transport, and Storage in the Working River Sediment production is influenced by many factors, including soil type, vegetation type and coverage, land use, climate, and weathering/erosion rates. -
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. -
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 -
Morphological Bedload Transport in Gravel-Bed Braided Rivers
Western University Scholarship@Western Electronic Thesis and Dissertation Repository 6-16-2017 12:00 AM Morphological Bedload Transport in Gravel-Bed Braided Rivers Sarah E. K. Peirce The University of Western Ontario Supervisor Dr. Peter Ashmore The University of Western Ontario Graduate Program in Geography A thesis submitted in partial fulfillment of the equirr ements for the degree in Doctor of Philosophy © Sarah E. K. Peirce 2017 Follow this and additional works at: https://ir.lib.uwo.ca/etd Part of the Physical and Environmental Geography Commons Recommended Citation Peirce, Sarah E. K., "Morphological Bedload Transport in Gravel-Bed Braided Rivers" (2017). Electronic Thesis and Dissertation Repository. 4595. https://ir.lib.uwo.ca/etd/4595 This Dissertation/Thesis is brought to you for free and open access by Scholarship@Western. It has been accepted for inclusion in Electronic Thesis and Dissertation Repository by an authorized administrator of Scholarship@Western. For more information, please contact [email protected]. Abstract Gravel-bed braided rivers, defined by their multi-thread planform and dynamic morphology, are commonly found in proglacial mountainous areas. With little cohesive sediment and a lack of stabilizing vegetation, the dynamic morphology of these rivers is the result of bedload transport processes. Yet, our understanding of the fundamental relationships between channel form and bedload processes in these rivers remains incomplete. For example, the area of the bed actively transporting bedload, known as the active width, is strongly linked to bedload transport rates but these relationships have not been investigated systematically in braided rivers. This research builds on previous research to investigate the relationships between morphology, bedload transport rates, and bed-material mobility using physical models of braided rivers over a range of constant channel-forming discharges and event hydrographs. -
Sediment Bed-Load Transport: a Standardized Notation
geosciences Article Sediment Bed-Load Transport: A Standardized Notation Ulrich Zanke 1,2,* and Aron Roland 3 1 TU, Darmstadt, Inst. für Wasserbau und Hydraulik, 64287 Darmstadt, Germany 2 Z & P—Prof. Zanke & Partner, Ackerstr. 21, D-30826 Garbsen-Hannover, Germany 3 CEO BGS-ITE, Pfungstaedter Straße 20, D-64297 Darmstadt, Germany; [email protected] * Correspondence: [email protected] Received: 7 August 2020; Accepted: 1 September 2020; Published: 16 September 2020 Abstract: Morphodynamic processes on Earth are a result of sediment displacements by the flow of water or the action of wind. An essential part of sediment transport takes place with permanent or intermittent contact with the bed. In the past, numerous approaches for bed-load transport rates have been developed, based on various fundamental ideas. For the user, the question arises which transport function to choose and why just that one. Different transport approaches can be compared based on measured transport rates. However, this method has the disadvantage that any measured data contains inaccuracies that correlate in different ways with the transport functions under comparison. Unequal conditions also exist if the factors of transport functions under test are fitted to parts of the test data set during the development of the function, but others are not. Therefore, a structural formula comparison is made by transferring altogether 13 transport functions into a standardized notation. Although these formulas were developed from different perspectives and with different approaches, it is shown that these approaches lead to essentially the same basic formula for the main variables. These are shear stress and critical shear stress. -
Salmon-Driven Bed Load Transport and Bed Morphology in Mountain Streams
GEOPHYSICAL RESEARCH LETTERS, VOL. 35, LXXXXX, doi:10.1029/2007GL032997, 2008 Click Here for Full Article 2 Salmon-driven bed load transport and bed morphology in mountain 3 streams 1 2 3 4 4 Marwan A. Hassan, Allen S. Gottesfeld, David R. Montgomery, Jon F. Tunnicliffe, 5 1 1 1 6 5 Garry K. C. Clarke, Graeme Wynn, Hale Jones-Cox, Ronald Poirier, Erland MacIsaac, 6 7 6 Herb Herunter, and Steve J. Macdonald Received 13 December 2007; revised 10 January 2008; accepted 18 January 2008; published XX Month 2008. 7 9 [1] Analyses of bed load transport data from four streams of nests (redds) have been widely recognized [Kondolf and 41 10 in British Columbia show that the activity of mass spawning Wolman, 1993; Kondolf et al., 1993; Montgomery et al., 42 11 salmon moved an average of almost half of the annual bed 1996], the role of fish on sediment transport remains little 43 12 load yield. Spawning-generated changes in bed surface explored due to the difficulty in both collecting bed load 44 13 topography persisted from August through May due to lack transport data and in discriminating between hydrologic and 45 14 of floods during the winter season, defining the bed surface biologic transport. 46 15 morphology for most of the year. Hence, salmon-driven bed [3] The localized geomorphic role of spawning salmon 47 16 load transport can substantially influence total sediment involves both direct transport during redd excavation that 48 17 transport rates, and alters typical alluvial reach morphology. modifies streambeds and indirect effects through changes 49 18 The finding that mass-spawning fish can dominate sediment in bed-surface grain size and packing [Butler, 1995; 50 19 transport in mountain drainage basins has fundamental Montgomery et al., 1996]. -
5.1 Coarse Bed Load Sampling
University of Montana ScholarWorks at University of Montana Graduate Student Theses, Dissertations, & Professional Papers Graduate School 1997 The initiation of coarse bed load transport in gravel bed streams Andrew C. Whitaker The University of Montana Follow this and additional works at: https://scholarworks.umt.edu/etd Let us know how access to this document benefits ou.y Recommended Citation Whitaker, Andrew C., "The initiation of coarse bed load transport in gravel bed streams" (1997). Graduate Student Theses, Dissertations, & Professional Papers. 10498. https://scholarworks.umt.edu/etd/10498 This Dissertation is brought to you for free and open access by the Graduate School at ScholarWorks at University of Montana. It has been accepted for inclusion in Graduate Student Theses, Dissertations, & Professional Papers by an authorized administrator of ScholarWorks at University of Montana. For more information, please contact [email protected]. INFORMATION TO USERS This manuscript has been reproduced from the microfilm master. UMI films the text directly from the original or copy submitted. Thus, some thesis and dissertation copies are in typewriter free, while others may be from any type of computer printer. The quality of this reproduction is dependent upon the quality of the copy submitted. Broken or indistinct print, colored or poor quality illustrations and photographs, print bleedthrough, substandard margins, and improper alignment can adversely affect reproduction. In the unlikely event that the author did not send UMI a complete manuscript and there are missing pages, these will be noted. Also, if unauthorized copyright material had to be removed, a note will indicate the deletion. Oversize materials (e.g., maps, drawings, charts) are reproduced by sectioning the original, beginning at the upper left-hand comer and continuing from left to right in equal sections with small overlaps. -
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.