Watersheds & River Continuum
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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. -
Influence of a Waterfall Over Richness and Similarity in Adjoining Pools Of
Acta Limnologica Brasiliensia, 2010, vol. 22, no. 4, p. 378-383 doi: 10.4322/actalb.2011.003 Influence of a waterfall over richness and similarity in adjoining pools of an Atlantic Rainforest stream Influência de uma queda d’água sobre a riqueza e a similaridade de dois remansos em um rio da Mata Atlântica Biological LimnologyBiological Célio Roberto Jönck¹ and José Marcelo Rocha Aranha² ¹Avaliação e Monitoramento Ambiental, Centro de Pesquisas Leopoldo Américo Miguez de Melo, CEP 21941-915, Rio de Janeiro, RJ, Brazil e-mail: [email protected] ²Laboratório de Ecologia de Rios, Universidade Federal do Paraná – UFPR, Campus Palotina, Rua 24 de Junho, 698, CEP 85950-000, Palotina, PR, Brazil e-mail: [email protected] Abstract: Aim: The main goal of the study was to determine the effect of the Morato Fall in the richness and composition of the aquatic animal community; Methods: We compared faunal richness and similarity in four substrate samples from two pools separated by a waterfall in the Morato River, southern Brazil; Results: The richness was not significantly different, although the upstream pool had 72 taxa and the downstream one just 65. On the other hand, composition was poorly similar, just a 36.5% similarity between the two sites; Conclusions: That indicates a strong influence of the waterfall, mainly on organisms which spent its entire life cycle on the water, such as fish and small crustaceans. That allow aquatic insects, a group with airborne adult phase and, therefore, able to disperse up to the upstream pool, to evolve with less predatory pressure, becoming the top group in the food web of this environment. -
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. -
Mitchell Creek Watershed Hydrologic Study 12/18/2007 Page 1
Mitchell Creek Watershed Hydrologic Study Dave Fongers Hydrologic Studies Unit Land and Water Management Division Michigan Department of Environmental Quality September 19, 2007 Table of Contents Summary......................................................................................................................... 1 Watershed Description .................................................................................................... 2 Hydrologic Analysis......................................................................................................... 8 General ........................................................................................................................ 8 Mitchell Creek Results.................................................................................................. 9 Tributary 1 Results ..................................................................................................... 11 Tributary 2 Results ..................................................................................................... 15 Recommendations ..................................................................................................... 18 Stormwater Management .............................................................................................. 19 Water Quality ............................................................................................................. 20 Stream Channel Protection ....................................................................................... -
Stream Visual Assessment Manual
U.S. Fish & Wildlife Service Stream Visual Assessment Manual Cane River, credit USFWS/Gary Peeples U.S. Fish & Wildlife Service Conasauga River, credit USFWS Table of Contents Introduction ..............................................................................................................................1 What is a Stream? .............................................................................................................1 What Makes a Stream “Healthy”? .................................................................................1 Pollution Types and How Pollutants are Harmful ........................................................1 What is a “Reach”? ...........................................................................................................1 Using This Protocol..................................................................................................................2 Reach Identification ..........................................................................................................2 Context for Use of this Guide .................................................................................................2 Assessment ........................................................................................................................3 Scoring Details ..................................................................................................................4 Channel Conditions ...........................................................................................................4 -
C. Natural Stream Processes
Natural Stream Processes Guide No. 03 Streams in their natural state are dy- agency officials, and others to start a recycle nutrients from natural pollution namic ecosystems that perform many thoughtful inquiry into the true source sources, such as leaf fall, to purifying beneficial functions. Natural streams of local stream management problems. the water. The natural stream tends and their flood plains convey water The material contained in this guide to maintain itself through the flushing and sediment, temporarily store excess makes evident that the source of many flows of annual floods that clear the flood water, filter and entrap sediment stream problems is in the watershed, channel of accumulated sediments, and pollutants in overbank areas, far from the main stream channel. debris, and encroaching vegetation. recharge and discharge groundwater, Landowners, local officials, and oth- Extreme floods may severely disrupt naturally purify instream flows, and ers concerned with streams need to the stream on occasion, but the natural provide supportive habitat for diverse work together across property lines balance of the stream ecosystem is plant and animal species. The stream and jurisdictional boundaries to find restored rapidly when it is in a state of corridors wherein these beneficial func- suitable solutions to stream problems dynamic equilibrium. tions occur give definition to the land and to implement practices to protect, and offer “riverscapes” with aesthetic restore and maintain healthy stream qualities that are attractive to people. ecosystems. CHANNEL FORMING Human activities that impact stream AND RECONDITIONING ecosystems can and often do cause STREAMS ARE problems by impairing stream functions PROCESSES and beneficial uses of the resource. -
Chapter 11 – Glossary of Terms
CHAPTER 11 GLOSSARY OF TERMS WORD DEFINITION SOURCE Active Channel The channel that contains the discharge Leopold where channel maintenance is most effective, sediment are actively transported and deposited, and that are capable of containing most flows. Active channels are located within the area bounded by bankfull stages. Active Flood plain Low lying areas built by watercourse Collaborative, sediment depositions between top of bank Leopold that are adjacent to a watercourse and that have been constructed by the present river in the present climate. These areas are susceptible to frequent inundation during moderate and higher flows when the active channel’s capacity is exceeded. Active floodplains are most prominent along low- gradient, meandering reaches and are often absent or undistinguishable along steeper sloped stream channels. Active Recreation Includes sports fields, recreation centers, tot San Jose lots, play equipment, multi-use courts, etc. Riparian Should not be located within riparian area. Corridor Policy USER MANUAL: GUIDELINES + STANDARDS FOR LAND USE NEAR STREAMS 11.1 GLOSSARY OF TERMS GLOSSARY OF TERMS WORD DEFINITION SOURCE Bankfull stage Bankfull stage is the point at which the flow Water just begins to enter the active floodplain. Resources Accurate measurements have been Protection conducted on gaged streams, however, in Collaborative, absence of historical hydrological records Leopold there are a number of field indicators that can be used to identify bankfull stages with a great deal of accuracy: • An abrupt change in the slope of the stream channel, usually from a vertical plane to a horizontal plane on top of the floodplain. • The bankfull stage is usually marked by a change in vegetation such as the change from gravel bars to forbs, herbs, or grasses. -
Streams and Running Water Streams Are Part of the Hydrologic Cycle (Figure 10.1)
Streams and Running Water Streams are part of the hydrologic cycle (Figure 10.1) Stream: body of running water that is confined in a channel and moves downhill under the influence of gravity. Cross-section of a typical stream (Figure 10.2) 1) Channel Flow 2) Sheet Flow Drainage Basin: area of a stream and its’ tributaries. Tributary: small stream flowing into a large one. Divide: ridge seperating drainage basins. Drainage Patterns 1) Dendritic: resembles tree branches > occurs on uniformly resistant rock 2) Radial: streams diverge outward from a central point > occurs on conic shapes, like volcanoes 3) Rectangular: steams have sharp bends ¾ due to presence of faulting, river follows the fault 4) Trellis: Parallel main streams with right angle tributaries > occurs on valley and ridge geomorphologies Factors Affecting Stream Erosion and Deposition 1) Velocity = distance/time Fast = 5km/hr or 3mi/hr Flood = 25 km/hr or 15 mi/hr Figure 10.6: Fastest in the middle of the channel a) Gradient: downhill slope of the bed of the stream ¾ very high near the mountains ¾ 50-200 feet/ mile in highlands, 0.5 ft/mile in floodplain b) Channel Shape and Roughness (Friction) > Figure 10.9 ¾ Lots of fine particles – low roughness, faster river ¾ Lots of big particles – high roughness, slower river (more friction) High Velocity = erosion (upstream) Low Velocity = deposition (downstream) Figure 10.7 > Hjulstrom Diagram What do these lines represent? Salt and clay are hard to erode, and typically stay suspended 2) Discharge: amount of flow Q = width x depth -
Terminology and Definitions Associated with Revegetation
TECHNICAL NOTES U.S. DEPARTMENT OF AGRICULTURE NATURAL RESOURCES CONSERVATION SERVICE PLANT MATERIALS - 9 SPOKANE, WASHINGTON FEBRUARY, 2005 TERMINOLOGY AND DEFINITIONS ASSOCIATED WITH REVEGETATION This Technical Note is a compilation of several old Technical Notes. Technical Note #9 is subdivided into the following Sections: Section 9.1 Ecological Definitions Section 9.2 A Technical Glossary of Stream & River Stabilization, Restoration, and Bioengineering Terms Section 9.3 Glossary of Terminology commonly used in Mining & Reclamation Technology SECTION 9.1 Ecological Definitions (S.M. Lambert, 1994; revised/updated M.E. Stannard, 2005) ECOSYSTEM A biological community together with the physical, social and chemical environment with which it interacts. ECOREGIONS Regions that have broad ecological similarities with respect to soil, relief, and dominant vegetation. Ecoregions are less commonly used by NRCS in its day-to-day terminology. NRCS uses Major Land Resource Areas and Conservation Resource Areas. MAJOR LAND RESOURCE AREAS (MLRA) Geographically associated land resource units, usually encompassing several thousand acres. They are characterized by particular patterns of soils, geology, climate, water resources, and land use. A unit may be one continuous area or several separate nearby areas. CONSERVATION RESOURCE AREAS (CRA) A geographical area where resource concerns, problems, or treatment needs are similar. It is considered a subdivision of an existing Major Land Resource Area (MLRA) map delineation or polygon. Landscape conditions, soil, climate, human considerations, and other natural resource information are used to determine the geographic boundaries of a Common Resource Area. USDA NRCS OCTOBER 2005 ECOTYPE The individuals of a species that are adapted to a particular environment BIOTYPE Synonymous with Ecotype INTRODUCED SPECIES Does not naturally occur in an area defined by soil, relief, and climate. -
Water Life: Riffles and Pools Stream Ecosystems Provide a Habitat Or
Water Life: Riffles and Pools Stream ecosystems provide a habitat or natural environment for many diverse aquatic organisms and plants. A deeper look indicates each stream has a distinctive anatomy as each is composed of a series of pools, riffles and runs. Pools: An area of the stream characterized by deep depths and slow current. Pools are typically created by the vertical force of water falling down over logs or boulders. The movement of the water carves a deeper indentation in the stream bed. Pools are important because they can provide depth and still water. Riffles: An area of stream characterized by shallow depths with fast, turbulent water. The riffles are short segments of the stream where water flow is agitated by rocks. The rocky Adapted from: bottom provides protection from predators, food http://share3.esd105.wednet.edu/rsandelin/ees/Resources/Flowing%20water%20concepts.htm deposition and shelter. Riffle depths vary depending upon stream size, but can be as shallow as 1 inch or deep as 1 meter. The turbulence and stream flow results in high dissolved oxygen concentration. Run: An area of stream characterized by moderate current, continuous surface and depths greater than riffles. Runs are stretches of the stream downstream of pools and riffles where stream flow and current are moderate. The smooth surface allows for light to penetrate. Microhabitats: Habitats are the natural environment in which an organism lives. The distinguishing abiotic conditions of riffles, pools and runs result in specialized environments that are known as microhabitats. The abiotic conditions (dissolved oxygen, turbidity, light and temperature) of these microhabitats can influence which aquatic species can survive and reproduce at that given location and time. -
The Applicability of the River Continuum Concept to the Upper Reaches of a Neotropical Lower Montane Stream
AMERICAN JOURNAL OF UNDERGRADUATE RESEARCH VOL. 9, NO. 1 (2010) The Applicability of the River Continuum Concept to the Upper Reaches of a Neotropical Lower Montane Stream Nicholas Skaff Department of Biology Tufts University Medford, Massachusetts 02155 USA ABSTRACT The applicability of the River Continuum Concept (RCC) to the upper reaches of Quebrada Máquina, a lower montane stream in Monteverde, Costa Rica, was examined. Macroinvertebrate samples were taken from ten points along the stream from first through fourth order segments. The families of the collected individuals were then categorized based on functional feeding group. The similarity between the families found at each collection point was calculated, along with correlations between the functional groups and various stream characteristics. In most cases, RCC predictions did not apply to Quebrada Máquina. The first (first order) and last (fourth order) sample points were 92% similar despite RCC predictions of substantial divergence in relative functional group abundance. This digression from the RCC predictions may be caused by the relatively few differences in stream characteristics between first and fourth order sections. Specifically, the observed similarities and correlations may have been determined by local scale heterogeneity of the stream characteristics. I. INTRODUCTION first order. Its mergence with another first order stream forms a second order and the Dynamic abiotic and biotic coalescence of two second order streams interactions in pristine river ecosystems are produces a third order and so on [2]. The extremely consistent due to the predictable RCC generally accounts for river orders biological responses to the physical ranging from one to twelve [3]. components [1].