Hydraulics of bendway weirs

Similar documents
How to Design Bendway Weirs

DATA REPORT FOR COMPLETED SPUR-DIKE CONFIGURATIONS WITHIN THE NATIVE TOPOGRAPHY MODEL

Countermeasure Calculations and Design

Upper Mississippi River Basin Environmental Management Program Workshop

River Restoration and Rehabilitation. Pierre Y. Julien

Stream Geomorphology. Leslie A. Morrissey UVM July 25, 2012

HAW CREEK, PIKE COUNTY, MISSOURI-TRIB TO SALT RIVER ERODING STREAM THREATHENING COUNTY ROAD #107, FOURTEEN FT TALL ERODING BANK WITHIN 4 FT OF THE

Probabilistic Evaluation of a Meandering Low-Flow Channel. February 24 th, UMSRS

Bank stabilization by redirective structures on the Santa Clara River, Ventura County, CA

Technical Memorandum. To: From: Copies: Date: 10/19/2017. Subject: Project No.: Greg Laird, Courtney Moore. Kevin Pilgrim and Travis Stroth

THE HYDRAULIC PERFORMANCE OF ORIENTED SPUR DIKE IMPLEMENTATION IN OPEN CHANNEL

NEWS RELEASE UNDER SECTION 404 OF THE CLEAN WATER ACT (33 USC 1344) ACTION NUMBER SPA ABQ

Stream Restoration and Environmental River Mechanics. Objectives. Pierre Y. Julien. 1. Peligre Dam in Haiti (deforestation)

Carmel River Bank Stabilization at Rancho San Carlos Road Project Description and Work Plan March 2018

Quasi-three dimensional computations for flows and bed variations in curved channel with gently sloped outer bank

JEMEZ RIVER CASE STUDY: UTILIZING A FROUDE NUMBER SIMILITUDE PHYSICAL

NATURE OF RIVERS B-1. Channel Function... ALLUVIAL FEATURES. ... to successfully carry sediment and water from the watershed. ...dissipate energy.

NATURAL RIVER. Karima Attia Nile Research Institute

A STUDY OF LOCAL SCOUR AT BRIDGE PIERS OF EL-MINIA

CASE STUDIES. Introduction

Restoration Goals TFG Meeting. Agenda

Analysis of Cost-Effective Rehabilitation: Principles and Tools for Reducing Uncertainty in Design

Dolores River Watershed Study

Project (Project No. US-CA-62-2) Maintenance Inspection and Reports (Subtask 14.1) Inspection Report No.2

Modeling of long-term sedimentation in the Osijek port basin

~ W 89 CONTENTS J-1 J-1 J-6 J-7 J-9 J-10 J-10 J-10

Garner State Park Pavilion Preservation Study

SEDIMENTATION STUDY OF THE MIDDLE MISSISSIPPI RIVER AT BUFFALO ISLAND RIVER MILES 28.0 TO 22.0 HYDRAULIC MICRO MODEL INVESTIGATION

MEANDER MIGRATION MODEL ASSESSMENT FOR THE JANUARY 2005 STORM, WHITMAN PROPERTY, SAN ANTONIO CREEK, VENTURA COUNTY, CALIFORNIA

Dam Removal Analysis Guidelines for Sediment

Field Methods to Determine/ Verify Bankfull Elevation, XS Area & Discharge

Assessment. Assessment

SCOPE OF PRESENTATION STREAM DYNAMICS, CHANNEL RESTORATION PLANS, & SEDIMENT TRANSPORT ANALYSES IN RELATION TO RESTORATION PLANS

APPENDIX E: Crystal River Hydraulic Modeling Report

EAGLES NEST AND PIASA ISLANDS

Experimental study of scour depth in attracting Groins series

FUTURE MEANDER BEND MIGRATION AND FLOODPLAIN DEVELOPMENT PATTERNS NEAR RIVER MILES 200 TO 191 OF THE SACRAMENTO RIVER PHASE III REPORT

Tom Ballestero University of New Hampshire. 1 May 2013

River Meandering and Braiding. Pierre Y. Julien. Department of Civil and Environmental Engineering Colorado State University Fort Collins, Colorado

LATERAL MIGRATION of ALLUVIAL CHANNELS

Open Channel Flow Part 2. Ch 10 Young, notes, handouts

Field Observations and One-Dimensional Flow Modeling of Summit Creek in Mack Park, Smithfield, Utah

Laboratory Investigation of Submerged Vane Shapes Effect on River Banks Protection

FHWA/IN/JTRP-2010/24. Dennis A. Lyn R. Cunningham

GEOMORPHIC CHANGES IN LOWER CACHE CREEK 2012

STREAM RESTORATION AWRA Summer Specialty Conference, GIS and Water Resources IX

Ways To Identify Background Verses Accelerated Erosion

STABILIZATION OF THE H&CT RAILWAY STONE DAM WALTER E. SKIPWITH, PE, JOYCE CRUM, AIA AND JOHN BAUMGARTNER, PE. Introduction.

Chapter 3.8: Energy Dissipators. By Dr. Nuray Denli Tokyay

5. ROADSIDE AND MEDIAN CHANNELS

LAR BPWG. DWR Erosion Screening Process Application to LAR. May 17, water resource specialists

Perspectives on river restoration science, geomorphic processes, and channel stability

Spreadsheet Tools for Quantifying the Costs and Benefits of Two-Stage Channels

Estimating Scour. CIVE 510 October 21 st, 2008

Laboratory Study of Turbulence Intensity in Longitudinal, Transverse and Deep Directions and Turbulent Burst Event around Various L-Shaped Groynes

Degradation Concerns related to Bridge Structures in Alberta

Rock Sizing for Waterway & Gully Chutes

Fish Passage at Road Crossings

Vegetation effects on river hydraulics. Johannes J. (Joe) DeVries David Ford Consulting Engineers, Inc. Sacramento, CA

RAILWAYS AND FISH: HOW TO PROTECT AND ENHANCE FISH HABITAT VALUES AT STREAM CROSSINGS THROUGH PROJECT DESIGN AND CONSTRUCTION

Sessom Creek Sand Bar Removal HCP Task 5.4.6

Step 5: Channel Bed and Planform Changes

U.S. Army Corps of Engineers Riprap Design for Flood Channels

Evaluation of Scour Depth around Bridge Piers with Various Geometrical Shapes

Appendix F Channel Grade Control Structures

Rapid Geomorphic Assessments: RGA s

CFD Modeling for Structure Designs in Environmental Impacts Mitigation

Canal Velocity Indexing at Colorado River Indian Tribes (CRIT) Irrigation Project in Parker, Arizona using the SonTek Argonaut SL

Aquifer an underground zone or layer of sand, gravel, or porous rock that is saturated with water.

Avoiding Geohazards in the Mid-Atlantic Highlands by Using Natural Stream Principles

GENERAL SUMMARY BIG WOOD RIVER GEOMORPHIC ASSESSMENT BLAINE COUNTY, IDAHO

LOCATIONS OF SELECTED MITIGATION SITES IN JAPAN

Summary of Hydraulic and Sediment-transport. Analysis of Residual Sediment: Alternatives for the San Clemente Dam Removal/Retrofit Project,

Analysis of the Effects of Bendway Weir Construction on Channel Cross Sectional Geometry

APPENDIX B DESIGN CRITERIA FOR TEMPORARY WATER QUALITY BMPS USED DURING CONSTRUCTION

Morphological Changes of Reach Two of the Nile River

Laboratorial investigating of the scouring extension in the range of trapezoidal and rectangular Multiple vanes to direct the flow in the rivers bends

MODELING OF LOCAL SCOUR AROUND AL-KUFA BRIDGE PIERS Saleh I. Khassaf, Saja Sadeq Shakir

A-JACKS CONCRETE ARMOR UNITS Channel Lining and Pier Scour Design Manual

Kaskaskia Morphology Study Headwaters to Lake Shelbyville

MEMORANDUM 1. INTRODUCTION

Hydraulics of stream deflectors used in fish-habitat restoration schemes

Lecture Note for Open Channel Hydraulics

MATHEMATICAL MODELING OF FLUVIAL SEDIMENT DELIVERY, NEKA RIVER, IRAN. S.E. Kermani H. Golmaee M.Z. Ahmadi

APPENDIX D HYDROLOGY AND HYDRAULICS. Micromodel Study Hydrology and Hydraulics Analysis

Session 1 Healthy Streams Stream Hydraulics Natural Channel Design

COMPARISON OF LABORATORY AND FIELD MEASUREMENTS OF BRIDGE PIER SCOUR

Domino Effect of River Training in Large Sand-Bed Braiding Rivers

MEASUREMENT OF 3D FLOW FIELD IN A 90 BEND WITH ULTRASONIC DOPPLER VELOCITY PROFILER

Rock Sizing for Small Dam Spillways

Instream Erosion Control General

Do you think sediment transport is a concern?

Long Valley Meadow Restoration Project

How Do Human Impacts and Geomorphological Responses Vary with Spatial Scale in the Streams and Rivers of the Illinois Basin?

Beaver Creek Corridor Design and Analysis. By: Alex Previte

Two-Dimensional Simulation of Truckee River Hydrodynamics

Fluvial Driven Alluvial Fans

TSEGI WASH 50% DESIGN REPORT

APPENDIX A M&T/Llano Seco Long-Term Water Reliability Study These photos are examples of rock spurs in use throughout the United States

ERDC/LAB TR-0X-X 100. Figure 7-3 Maximum velocity magnitudes for existing conditions for 100-year flood event

Transcription:

River Basin Management IV 389 Hydraulics of bendway weirs C. Thornton 1, S. Abt 1, D. Baird 2 & R. Padilla 3 1 Colorado State University, Fort Collins, CO, USA 2 U.S. Bureau of Reclamation, Denver, CO, USA 3 U.S. Bureau of Reclamation, Albuquerque, NM, USA Abstract Natural processes associated with meandering river systems have been shown to lead to degradation of channel beds, erosion on channel banks, and bend migration. Attempts at mitigating the local instability associated with meandering systems, such as transverse and longitudinal structures, armor protection, and bio-engineering techniques have been utilized worldwide. One type of structure, bendway weirs, are rock structures placed in series along the outer bank of a bend in an effort to alleviate stresses, as well as create habitat. Many aspects associated with the bendway weir indicate the structure to be a viable alternative to longitudinal stone toe for controlling migration and bank erosion. While bendway weirs have been successfully used in many applications, quantifiable design guidance has not been available. Past projects utilizing bendway weirs have relied heavily on field experiences, site-specific flume studies, and engineering judgment, but have lacked general design guidelines. To accurately model flow conditions resulting from the placement of bendway weirs, an undistorted 1:12 Froude scale, hard boundary model was constructed at the Hydraulics Laboratory of the Engineering Research Center at Colorado State University. The model contained two bends, which exhibited unique geometric characteristics representative of those found in the Middle Rio Grande reach. Three-dimensional velocities and water surface profiles were recorded for a series of tests including variations of weir length, spacing, and angle. Using the data obtained from the test series, a relationship of the reduction of velocities relative to pre-weir conditions, due to the variation of bendway weir characteristics, was developed. The location of the strongest eddies found in a bend as a function of weir length was also examined. Bendway-weir testing resulted in the creation of design criteria. Utilization of a known set of base-line conditions for a given bend and design parameters for bendway weirs, a designer is enabled to predict maximum velocities found in the bend after the installation of bendway weirs. Keywords: bendway weirs, river restoration, bank erosion, in-stream structures. doi:10.2495/rm070371

390 River Basin Management IV 1 Introduction Bank erosion and channel migration are natural responses to a shift in the equilibrium of a river system. Natural changes in river systems have impacted navigation and the use of adjacent land for hundreds of years. There have been several methods developed for alleviating bank instability and managing channel migration. The use of rock, riprap, and concrete structure techniques have been popular methods implemented in bank stabilization. More specifically, the use of a riprap blanket placed over an eroding bank, although extremely effective in preventing bank erosion, is not conducive to the enhancement of habitat. Blanketing a portion of a stream bank with riprap hinders the growth of riparian vegetation and favorable aquatic habitat features. Historically bendway weirs, also known as spur dikes, groins, or jetties, have been used extensively in the deepening of navigational channels. It has been documented that in their application to navigation channels, the rock weir structures were also an effective method of bank stabilization. The use of bendway weirs was then extended to river restoration and rehabilitation projects. They have been a useful tool in stabilizing bend migration and outer bank erosion, as well as promoting aquatic habitat and riparian vegetation (Shields et al. [1]). Figure 1 presents a photograph of a series of bendway weirs placed on a river bend. Figure 1: Example of bendway weirs in the field. While the bendway weir has been used and studied for several decades, design guidelines for the use of bendway weirs have, to date, not been successfully developed. Major design parameters of the bendway weir include height, length, orientation angle, and spacing. Current guidance on the design of these rock structures is based on field experience and rule-of-thumb. To date, the behavior of flow conditions following the installation of bendway weirs has

River Basin Management IV 391 not been empirically defined. As an initial step in quantifying the flow conditions resulting from bendway weir placement, a physical hydraulic model was constructed and tested to determine the effects of weir spacing on the resulting flow conditions. 2 Physical model A 29-mile stretch of the Rio Grande, located in central New Mexico extending from Cochiti Dam to the town of Bernalillo, has been the focus of a channel maintenance project conducted by the U.S. Bureau of Reclamation. As part of that maintenance project, the Bureau desired to employ native material and rock weir structures in an effort to mitigate bank erosion, channel migration, and habitat degradation. Upon realizing that design criteria for native material and rock weir structures was scarce and limited, a physical hydraulic model study was contracted for and conducted at Colorado State University. The model was intended to determine the most effective design of bank-stabilization structures, i.e., bendway weirs, vortex weirs, veins, and turning rocks for use on the Middle Rio Grande. An undistorted 1:12 Froude scale, hard boundary physical hydraulic model exhibiting characteristics represented in a 29-mile study reach of the Middle Rio Grande, extending from Cochiti Dam to the town of Bernalillo, was constructed for the testing of bendway weirs. The model consisted of two geometrically unique bends placed in an S-shaped configuration and separated by a straight transition section. Bendway weirs were then constructed from riprap and placed throughout each bend for testing. The model was equipped with an instrumentation and data-collection cart permitting measurements of flow depth, three-dimensional velocity, and boundary shear stress at any location within the model. Cross-sectional geometry in both bends was chosen to be trapezoidal with a 1:3 side slope, which corresponds to conditions found within the study reach. To accommodate the required flow rates needed for testing, a total channel depth of 1.5 ft (0.46 m) and bed slope of 0.000863 were incorporated into the model. To achieve the goals of the study, a fixed bed was incorporated into the model. Throughout the prototype study reach, Manning s n values ranged from 0.026 to 0.035 for the channel bed and banks. The model was, therefore, constructed with a roughened concrete surface that was determined to have a Manning s value of 0.018, which related to prototype roughness of approximately 0.027. Flow depth and water surface elevation measurements were obtained using two methods. A standard point gage, capable of measuring 60.001 ft (60.03 cm), was mounted to the instrumentation cart allowing for bed and water surface measurements to be collected anywhere in the channel. In addition to the point gage, 122 piezometer taps were placed throughout the model. At each cross section, three taps were placed on the side slopes at varying elevations and one tap located in the center of the channel. A SonTek Acoustic Doppler Velocity (ADV) meter was used to collect and record three-dimensional velocity profiles. The velocity measurement system included a data-acquisition card and software

392 River Basin Management IV used on a personal computer to record velocity measurements at a selected sampling rate of 10 Hz. A full description of data-collection techniques and locations can be found in Heintz [2]. Based on the literature review, an initial bendway weir design was determined. The influence of spacing on the flow characteristics and performance of bendway weirs was investigated by maintaining the height, length, width, and shape of the weirs while altering the weir spacing. The crest profile of the weir was chosen to be flat. Weir length was determined to be 28 % of the channel top width at 12 cfs (0.34 cms), also blocking 26.7 % of the flow area in both bends. The weirs were installed perpendicular to the bank at an orientation angle of 90 degrees relative to the flow direction. Figure 2 illustrates the weir geometry in plan view and cross-sectional views. Table 1 presents the weir dimensions tested. The values in Table 1 remained constant for the testing sequences. Lcw Plan View Side Wcw Front Lw Wbw Figure 2: Table 1: Bendway weir schematic. Weir dimensions. Upstream Bend Downstream Bend L cw 4.07 ft (1.24 m) 2.98 ft (0.91 m) L w 4.90 ft (1.49 m) 3.82 ft (1.16 m) W cw 1 ft (0.30 m) 1 ft (0.30 m) W bw 4 ft (1.22 m) 4 ft (1.22 m) L r = L w /TW 0.267 0.267 Spacing ratio between weirs was defined in the literature review as the ratio between the distance separating the weirs and their length. Therefore, the spacing ratio, S, was defined by measuring the arc length between the weirs at the design water line along the bank, L arc, and dividing it by the total length of the weir, L w, as defined in Figure 3 and eqn (1): L S = arc. (1) L w

River Basin Management IV 393 Arc Length Between Weirs, Larc Water Surface at Design Depth Weir Weir Length, Lw Channel Toe Angle, θw Radius, r Plan View Figure 3: Definitions used in spacing ratio measurement. Table 2: Tested spacing ratios. Upstream Bend Downstream Bend S / # of Weirs 3.4 / 6 4.7 / 5 S / # of Weirs 4.1 / 5 5.9 / 4 S / # of Weirs 5.1 / 4 8.4 / 3 Six different spacing ratios, three in each bend, were tested during the program. Table 2 presents the spacing ratios tested, as well as the corresponding number of weirs per bend. 3 Test matrix A test matrix consisting of sixteen individual flume runs was developed to quantify the effect of spacing on the flow patterns and document performance of bendway weirs installed within a channel. A total of four tests were conducted without bendway weirs installed, and termed base-line tests, leaving twelve tests for examining the effect of bendway weirs on resulting flow conditions by varying the parameters described above. An examination of data collected throughout each bend during each test was conducted to determine the influence of weir spacing on flow conditions. The maximum velocity measured on the outer bank of each bend during testing was examined in detail and a thorough description of that analysis is presented by Heintz [2]. Tests were conducted at four different discharges to simulate flow conditions present in the Middle Rio Grande study reach. Prototype flows simulated in the

394 River Basin Management IV physical model include 4,000, 6,000, 8,000, and 10,000 cfs (113, 170, 227, and 283 cms, respectively) corresponding to model flow rates of 8, 12, 16, and 20 cfs (0.23, 0.34, 0.45, and 0.57 cms, respectively). 4 Dimensional analysis Several dimensionless terms were formulated for the analysis of bendway weir data. Dimensionless parameters that would describe the effects of weir spacing on performance were determined by considering the numerous variables describing the physically modeled system and are presented in detail by Heintz [2]. Data analysis was then carried out using a worst-case condition approach to developing design criteria by selecting maximum measured velocities. The initial conditions measured in the base-line tests were incorporated into the dimensional analysis to indicate changes in the flow created by weirs with varying spacing ratios. Identification of the maximum velocity, MaxV, at a specific location in a bend (i.e., center, outer or inner bank) accounts for the most extreme velocity condition occurring during weir testing. The maximum velocity ratio, MVR, presented in eqns (2) through (4), at a specified location incorporates maximum velocity conditions with weirs relative to maximum centerline velocity measured during the base-line testing. Centerline velocity measured at 60 % of the depth is representative of the cross-section average velocity, which would also be attainable from a field site visit or predictive computer model. The maximum base-line center velocity, MaxV CenterBase, was incorporated into the MVR to develop a velocity-based design parameter conveniently adapted to field situations: MaxV MVR = Out, (2) Out MaxV CenterBase MaxV MVR = Center, and (3) Center MaxV CenterBase MaxV MVR = In, (4) In MaxV CenterBase where, MaxV Out = maximum velocity measured between weirs on the outer bank (L/T); MaxV Center = maximum centerline velocity measured during weir testing (L/T); MaxV In = maximum inner bank velocity measured during weir testing (L/T); MaxV CenterBase = maximum base-line center velocity at 60 % depth (L/T); MVR Out = outer bank maximum velocity ratio (dimensionless); MVR Center =

River Basin Management IV 395 centerline maximum velocity ratio (dimensionless); and MVR In = inner bank maximum velocity ratio (dimensionless). 5 Analysis The concept of a velocity ratio, MVR, presented in eqns (2) through (4), was used to develop relationships between maximum measured centerline velocity values during the base-line runs with the maximum recorded velocity at three lateral cross-section locations when bendway weirs were installed in the model. Maximum measured velocity values along the outer bend, inner bend, and thalweg during tests 5 through 16 were determined and utilized in the analysis. A detailed description of the location of each velocity value incorporated into the analysis has been reported by Heintz [2]. The outer bank maximum velocity ratio, MVR Out, was calculated using the MaxV Out and MaxV CenterBase values recorded during each test. A plot of determined MVR Out values versus spacing ratio is presented in Figure 4. MVRout 1.0 0.9 0.8 0.7 0.6 0.5 0.4 0.3 0.2 0.1 0.0 16cfs 12cfs 8cfs Upstream 8cfs Downstream 0 2 4 6 8 10 Spacing Ratio Figure 4: MVR Out plotted versus spacing ratio. Figure 4 shows that weirs at varying spacing ratios effectively reduce the outer bank velocity to at least 40 % of the maximum centerline velocity. Therefore, any bend with a bendway weir field designed with the same length ratio, orientation angle, and having a spacing ratio of 8.4 or less will have its outer bank velocity reduced to at least 40 % of the maximum centerline velocity. Using velocity output from a predictive HEC-RAS model, or center channel velocity measured in the field, it is possible for a designer to determine the maximum expected velocity for the outer bank of a bend with a specific geometry. Differences between the overtopping and non-overtopping flows remain apparent in Figure 4. The overtopping flow data plotted in Figure 4 indicate that there is no dependence on spacing ratio up to a value of S = 6. In both bends, the MVR Out values during overtopping tests were 0.25 for the 16 cfs (0.45 cms) test and 0.19 for the 12 cfs (0.36 cms) test. These values are even less than the

396 River Basin Management IV overall value of 40 %. However, the MVR Out data for overtopping flow conditions present two separate relationships corresponding to the 12 and 16 cfs (0.36 and 0.45 cms, respectively) flow rates. The non-overtopping flow exhibits a much different condition between the upstream and downstream bends, which is attributed to unusually high maximum velocities measured on the outer bank in the upstream bend as previously discussed. An examination of the center and inner bank flow characteristics was conducted to determine the changes induced by weirs with varying spacing ratios. The same analysis as conducted on the outer bank was performed for the centerline and inner bank locations. A direct comparison between base-line and weir data collected at the center and inner bank of the channel was also investigated. Figure 5 presents the MVR Center plotted versus spacing ratio, S, and indicates that the MVR Center has no dependence on the spacing ratio. The plot indicates that the centerline velocity with the placement of weirs is on average 1.422 times greater than the initial maximum centerline velocity, with a standard deviation of 0.139. Therefore, a designer may expect the centerline velocity to increase to a maximum of 1.69 times greater than the maximum centerline velocity without weirs, determined by a predictive computer model or field measurements, with 95 % confidence. MVRCenter 3.00 2.50 2.00 1.50 1.00 0.50 0.00 16cfs 12cfs 8cfs 0 2 4 6 8 10 Spacing Ratio, S Figure 5: MVR Center plotted versus spacing ratio. Effects of weir spacing on the inner bank velocities was also investigated. Techniques applied during the outer bank analysis employed on the data collected along the inner bank of each bend. A direct comparison between weir and base-line data on the inner bank was conducted similar to the centerline comparison analysis. Results of the MVR In analysis are presented in Figure 6. As indicated on the plot, there is an increase in inner bank velocity with respect to the center velocity, which is fully independent of weir spacing and bend. The inner bank velocity for all tests was determined to be an average of 1.478 times greater than the base-line center velocity, with a standard deviation of 0.044. The resulting MVR In value is 1.56, indicating that with 95 % confidence that the inner bank

River Basin Management IV 397 velocity will increase to a maximum of 1.56 times the maximum centerline velocity without weirs. The MVR value enables a designer to determine the maximum inner bank velocity expected after weir construction by providing a maximum center velocity in the channel prior to weir placement. MVRIn 2.50 2.00 1.50 1.00 16cfs 12cfs 8cfs 0.50 0 2 4 6 8 10 Spacing Ratio, S Figure 6: MVR In plotted versus spacing ratio. 6 Conclusions The bendway weir has been used for several decades as an effective method for mitigating bank and bend stabilization problems. Design of the bendway weir in the field has been primarily based on field experience and engineering judgment, not hard design criteria. Weir features that are of interest in the design process include weir height, length, orientation angle, and spacing. The study presented has examined two separate bends with varying geometries to determine their flow characteristics and the changes to those characteristics as a result of bendway weir placement. Furthermore, this study has investigated the role of weir spacing on flow conditions while holding weir geometry constant. An analysis of bendway weir spacing tests revealed that the spacing ratio of S less than 6 has little influence on maximum flow conditions in the two bends as a result of bendway weir placement. The maximum velocity measured on the outer bank between weirs for all tests was approximately 40 % or less of the maximum centerline velocity measured without weir placement. Placement of the bendway weir fields did significantly reduce the outer bank velocity. Outer bank maximum velocity conditions for non-overtopping flow conditions were a result of eddy formation between weirs. Maximum velocities between weirs for non-overtopping flow conditions were as high or higher than maximum velocities measured during overtopping conditions. The maximum centerline velocity was increased by a factor of 1.69 with the placement of weirs. Maximum inner bank velocity measured during all weir tests was determined to be 1.56 times greater than the maximum center velocity measured during baseline testing. Trends in the inner bank velocity ratio relationship in both bends were maintained for all weir testing, even though center and inner bank

398 River Basin Management IV velocities increased with weir placement. Based on the results presented by Heintz [2], weir length and not weir spacing was found to be the dominant factor in the resulting hydraulic conditions within the bendway weir field. References [1] Shields Jr., F.D., Knight, S.S. & Cooper, C.M., Addition of spurs to stone toe protection for warmwater fish habitat rehabilitation. Journal of the American Water Resources Association, 34(6), pp. 1427 1436, 1998. [2] Heintz, M.L., Investigation of Bendway Weir Spacing. MS Thesis, Department of Civil Engineering, Colorado State University, Fort Collins, CO, 2002.