BC Ministry of Forests. March Fish Stream Crossing Guidebook. Forest Practices Code of British Columbia.

Similar documents
HY-8 Version 7.2 Build Date January 17, Federal Highway Administration.

CHAPTER 5 CULVERT DESIGN

APPENDIX B HYDRAULIC DESIGN DATA FOR CULVERTS

Fish Passage Culvert Assessment for Cahilty Creek Watershed FIA Project #

Exercise (3): Open Channel Flow Rapidly Varied Flow

Experiment (13): Flow channel

Indiana LTAP Road Scholar Core Course #10 Culvert Drainage. Presented by Thomas T. Burke, Jr., PhD, PE Christopher B. Burke Engineering, Ltd.

(Revised February,2005) CULVERTS, BRIDGES, AND FORDS

Exercise (4): Open Channel Flow - Gradually Varied Flow

Rock Ramp Design Guidelines. David Mooney MS Chris Holmquist-Johnson MS Drew Baird Ph.D. P.E. Kent Collins P.E.

CHAPTER 4 SPALDING COUNTY, GEORGIA 4.0 CULVERT DESIGN

General Information for Culvert Design

Culvert Design for Low and High Gradient Streams in the Midwest. Dale Higgins, Hydrologist Chequamegon-Nicolet National Forest

ANSWERS TO QUESTIONS IN THE NOTES AUTUMN 2018

HEC 26 Aquatic Organism Passage Design Manual Evolution & Application

Fish Passage Culvert Inspection (FPCI) Nicklen Creek Watershed

The Basics of Culvert and Inlet Design

Section 5: Pond Outlets

EXAMPLES (OPEN-CHANNEL FLOW) AUTUMN 2018

Broadly speaking, there are four different types of structures, each with its own particular function:

Culvert Design An Overview of the NYS Highway Design Manual Chapter 8

2O-2 Open Channel Flow

APPENDIX J HYDROLOGY AND WATER QUALITY

19.1 Problem: Maximum Discharge

Components of a Barrage

Packwood Hydroelectric Project Barrier Analysis December 12, 2006

Culvert Design Basics

Presented by Fred Halterman, URS Jennie Agerton, URS

Sediment Basin 7E-12. Design Manual Chapter 7 - Erosion and Sediment Control 7E - Design Information for ESC Measures BENEFITS.

Chapter 11. Culverts and Bridges Design Checklist for Culvert Design

Discussion on the Selection of the Recommended Fish Passage Design Discharge

Massachusetts Stream Crossing Case Studies

MEMO. Schedule 'B' Class Environmental Assessment and Preliminary Design Lakeview Boulevard Improvements Culvert Assessment.

Hours / 100 Marks Seat No.

WMS 8.4 Tutorial Hydraulics and Floodplain Modeling HY-8 Modeling Wizard Learn how to model a culvert using HY-8 and WMS

Gerald D. Anderson. Education Technical Specialist

PHYS 101 Previous Exam Problems

FLOW MEASUREMENT (SEMI-SUBMERGIBLE OBJECT METHOD)

Greenup Lock Filling and Emptying System Study

NOVEMBER 2006 FLOOD DOWNSTREAM OF THE KATSE DAM STRUCTURE

Chutes Part 2: Synthetic linings

Aquatic Organism Passage at Road-Stream Crossings CHUCK KEEPORTS FOREST HYDROLOGIST ALLEGHENY NATIONAL FOREST WARREN, PENNSYLVANIA

Fish Passage Culvert Inspection (FPCI) 12 Sites on TFL 18 (FIA ) 1 Site on FL #A18688 (Thuya Creek) (FIA )

Washington State Fish Passage Barrier Removal Projects. Casey Kramer, PE WSDOT State Hydraulics Engineer

Lecture 10 : Sewer Appurtenances

Dam Breach Inundation Analysis

WASHINGTON CONSERVATION DISTRICT STANDARD OPERATING PROCEDURE (S.O.P.)

Low Gradient Velocity Control Short Term Steep Gradient Channel Lining Medium-Long Term Outlet Control Soil Treatment Permanent [1]

SELBY CREEK SILVERADO TRAIL CULVERT FISH PASSAGE ASSESSMENT

APPENDIX C VEGETATED EMERGENCY SPILLWAY. VERSION 1.0 March 1, 2011

Illinois State Water Survey

Project Report for Marsh Creek and Albion River Instream Fish Barrier Removal Flynn Creek Road, CR 135, M.P. 8.1 and 8.3

Access requests to County streets and roadways are processed through one of the following methods:

Advanced Hydraulics Prof. Dr. Suresh A. Kartha Department of Civil Engineering Indian Institute of Technology, Guwahati

1. In most economical rectangular section of a channel, depth is kept equal to

Evaluating Surge Potential in CSO Tunnels

TOP:001.3 U.S. Fish and Wildlife Service TECHNICAL OPERATING PROCEDURE

2D Modelling Series. Modelling Structures in Floodplains

APPENDIX A STRUCTURE DESCRIPTIONS AND RATING CURVES

STREAM SURVEY File form No..

Advanced Hydraulics Prof. Dr. Suresh A. Kartha Department of Civil Engineering Indian Institute of Technology, Guwahati

CALIFORNIA SALMONID STREAM HABITAT RESTORATION MANUAL APPENDIX IX-A CULVERT CRITERIA FOR FISH PASSAGE INTRODUCTION

Firth Creek Habitat Enhancement Project 1993

OFFICE OF STRUCTURES MANUAL FOR HYDROLOGIC AND HYDRAULIC DESIGN CHAPTER 11 APPENDIX B TIDEROUT 2 USERS MANUAL

Transactions on Ecology and the Environment vol 12, 1996 WIT Press, ISSN

Interim Guidance Fish Presence Absence

Experiment 8: Minor Losses

Modelling of Pressurised Pipes within InfoWorks ICM and CS

CEE 345, Part 2, Winter 2012, Final Exam Solutions (Open Channel Flow)

Fish Passage Assessment Report Mare Brook Culverts

Creek Trash Assessment (CTA) Methodology (Demonstration: Mill Run Creek, Cheltenham, Pa.)

Plan B Dam Breach Assessment

Simulating Streams Through Culverts in Mat-Su, Alaska

Old-Exam.Questions-Ch-14 T072 T071

TM /AFM 88-5, Chap Underground hydraulic design Inlets UFC - Drainage In Areas Other Than Airfields

The Discussion of this exercise covers the following points:

3. A fluid is forced through a pipe of changing cross section as shown. In which section would the pressure of the fluid be a minimum?

UNDERWATER INSPECTION REPORT DOUBLE CORRUGATED METAL PIPE CULVERT HAWTHORN ROAD OVER RICE CREEK (PELKEY LAKE) MORRISON COUNTY

Ontario Ministry of Transportation (MTO) Restoring Fish Passage to a Tributary of the Saugeen River

Beavers are particularly adept at manipulating their

Slide 5 / What is the difference between the pressure on the bottom of a pool and the pressure on the water surface? A ρgh B ρg/h C ρ/gh D gh/ρ

APPLYING VARIABLE SPEED PRESSURE LIMITING CONTROL DRIVER FIRE PUMPS. SEC Project No

Stormwater Management Pond Design Brief. Greely Village Centre - Commercial Phase - Ultimate Conditions - - City of Ottawa -

OIL SUPPLY SYSTEMS ABOVE 45kW OUTPUT 4.1 Oil Supply

2. RAPIDLY-VARIED FLOW (RVF) AUTUMN 2018

Review of Guidelines for Cycleway Safety Fencing

Fish Passage Planning and Design

13. TIDES Tidal waters

This experiment will develop skills in graphing and graphical analysis.

AP Physics B Ch 10 Fluids. MULTIPLE CHOICE. Choose the one alternative that best completes the statement or answers the question.

Design Data 22M. Flotation of Circular Concrete Pipe. w w I = w - x 1000 (3) (SG x 1000)

Designing Labyrinth Spillways for Less than Ideal Conditions Real World Application of Laboratory Design Methods

Memorandum. Dr. Wilbert Odem, Dr. Paul Trotta, and Mr. Justin Ramsey. From: Timothy Mahon, Patrick Belsheim, and Ali Alrayyes.

1 PIPESYS Application

Great Lakes Stream Crossing Inventory Instructions

Numerical investigation of transition between free surface flow and pressurized flow for a circular pipe flowing full upstream

Water surface slope extending up to 20 channel widths up and downstream of crossing.

Assessment of Baseline Geomorphic Features at. Proposed Stream Crossings On The Proposed County Road 595. Marquette County, Michigan

Exercise 2-3. Flow Rate and Velocity EXERCISE OBJECTIVE C C C

Project Completion Abstract Fish Passage Activity ( Engineering Activities)

Transcription:

FRST 557 Lecture 7c Bridges and Culverts: Water Velocity and Discharge Lesson Background and Overview: The previous two lessons presented methods for estimating water volume flow at a particular site and introduced different types of structures that allow water to pass under a road. This final lesson on water management looks at designing the structure for the volume and velocity of the anticipated water flow. This cedar log culvert was constructed for a railroad logging operation in the late 190s and is still functioning over 75 years later. Lesson Objective: On completion of this lesson and the associated assignment, you will have a general idea of how bridge openings are determined and you will be able to calculate velocity and volume for water in culverts. Lesson References: BC Ministry of Forests. September 1995. Forest Road Engineering Guidebook. Forest Practices Code of British Columbia. Stream Culvert Discharge Design (This is no longer in print, but a copy is available with the course notes under FOPR 6 / Supplemental / FRE Guide Stream Discharge) BC Ministry of Forests. June 00. Forest Road Engineering Guidebook. Forest Practices Code of British Columbia. Chapter 4. Road Drainage Construction BC Ministry of Forests. 1998. Stream Crossing Guidebook for Fish Streams. Forest Practices Code of British Columbia. pp. 10-15 (Sections 3.1 and 3.), pp. 9-33 (Section 5), pp. 66-79 (Appendix 4.1-4.5 and Appendix 6) (This is no longer in print, but this information is available with the course notes under FOPR 6 / Supplemental / SC Guide Fish) BC Ministry of Forests. March 00. Fish Stream Crossing Guidebook. Forest Practices Code of British Columbia. American Iron and Steel Institute. 1984. Handbook of Steel Drainage & Highway Construction Products - Canadian Edition Nagy, M.M. et al. 1980. Log Bridge Construction Handbook. Forest Engineering Research Institute of Canada, Vancouver

Designing Bridges and Culverts Bridges The site assessment for bridge crossings considers the cross sectional area of flowing water at the design event at the site of the bridge. Allowance is also considered in the bridge design for debris floating (or tumbling) downstream during storm events, Ideally, allowance is made for the flow to pass below the bridge unrestricted. That is, the channel is undisturbed by the bridge. If it is not possible for the channel to be bridged without some restriction (e.g. an intermediate piling support) then allowance must be made for additional area to compensate for the area lost to the obstruction. At any point in time, flow volume will be constant whether or not a restriction is present (Q = VA). A restriction may alter the values of velocity (V) and area (A) but the product (Q) will be the same. An exception to this is where the restriction becomes sufficient to actually partially dam the flow and cause water levels to rise. The economic and environmental risks of under designing a bridge make it prudent to seek appropriate professional assistance early in the planning process Culverts Culverts, because of the relatively small water flow, require shorter spans and are most often constructed with either pre-designed and purchased structures (e.g. metal or plastic pipes) or logs meeting appropriate loading specifications. Culverts do not normally require professional design unless extraordinary risks exist. However, diligence at making adequate provision for water passage is required. It is usually expected that provision will be quite conservative. Culvert design for opening area The fastest and most simple method of designing culverts for capacity is to estimate the cross section area of the planned storm event. As stated in the last lesson, the design standard in British Columbia for a major culvert is the peak flow of the 100 year event (Q 100 ). The basis for this calculation is the measurement of the bank-full event which occurs approximately every.3 years on the average. The volume and cross-sectional area of this event are represented as Q and A. Based on empirical data, the 100 year event (Q 100 ) is considered to be 3 times Q. While this ratio is not expected to be representative of all situations, it is considered to be adequate for situations requiring culverts under 000 mm diameter and streams with volume flows of under 6 m 3 /sec. Since Q 100 = 3Q and since area is directly proportional to the volume, A 100 = 3A Although A can be determined by more detailed and precise means, the following method is quite adequate for many situations.

Determining Culvert Size: Q 100 Area Method W 1 D W 1. The stream is measured for width at the bank tops (W 1 ) and the stream bed (W ).. The average depth (D) of the bank full event may be based on the average of several readings. 3. The cross sectional area is calculated using: A = [(W 1 + W )/]D 4. The culvert opening is calculated using A 100 = 3A The culvert may be any shape, provided that this opening size is maintained. Example: W 1 =.5 m W = 1.75 m D = 0.5 m A = [(.5 +1.75)/]0.05 = 1.0 m A 100 = 3(1.0) = 3.0 m This area could be met with a rectangular culvert of 3m width and 1 m depth or a round pipe of 4A 4 3.0 D 1.954m 1954mm Since culvert pipes come in standard sizes of 00 mm increments, a 000mm pipe would be chosen. 3

Simple Log Culvert (Source: BC Ministry of Forests. September 1995. Forest Road Engineering Guidebook. Forest Practices Code of British Columbia. Figure 3) Log Culvert Stringer Table (diameter at mid-span in meters) (Source: BC Ministry of Forests. September 1995. Forest Road Engineering Guidebook. Forest Practices Code of British Columbia. Table 1.) 4

Culvert design using a Nomograph A nomograph is a graphic solution of an equation. In this case, we will use a nomograph for a corrugated metal culvert were the variables are: Type of culvert entrance (inlet control) Depth of water at entrance Culvert diameter Water volume discharge Knowledge of three of the variables provides the unknown. The nomograph assumes a very shallow gradient and that there are no restrictions at the outflow end (including a submerged outflow). Example of Nomograph Use Culvert has a diameter of 900 mm. It is installed with a type 3 entrance and the water at the entrance (headwater depth) is 1980 mm (=. times the pipe diameter). 1. Locate the Headwater depth ratio on the scale for the type 3 entrance.. Project a horizomtal line across to the inner ( type 1) scale. 3. Project a line to the culvert diameter (900 mm). 4. Read off the volume discharge (Q = 1.8 m 3 / second) The nomograph illustrated here is one of many available for many different shapes and sizes of culverts. Because nomographs are based on thorough empirical data, they do provide an excellent means of selecting suitable structures for known flow volumes. 5

Example: Returning to the previous example:.5 m 0.5m 0.56 m 0.56 m 1.75 m W 1 =.5 m W = 1.75 m D = 0.5 m A = [(.5 +1.75)/]0.05 = 1.0 m In this case, we want to work with volumes rather than just areas, so we need two other variables to calculate the stream flow with Manning s equation. Let s assume: Stream gradient or slope (S) is % = 0.0 Manning s coefficient is 0.076 The wetted perimeter is the sum of the stream bed (W ) plus the two banks: P w = 1.75 + 0.56 + 0.56 =.87 The hydraulic radius R = A/P w = 1.0/.87 = 0.35 0.35 / 30.0 1/ / 3 1/ R S V 0.93 m / second n 0.076 Q = V A = (0.93)(1.0) = 0.93 m 3 / second Q 100 = 3Q = 3(0.93) =.79 m 3 / second Going to the nomograph and assuming a type 3 entrance and a 90% water depth at the culvert entrance, a 1500 mm culvert is indicated which is sized up to the nearest 00 mm or 1600 mm diameter. 6

Culvert design using Manning s CAUTION: The previous examples of culvert size selection should direct you to a reasonably safe conclusion. This example will produce figures that may not adequately consider all of the restrictive dynamics of a culvert flowing at the higher range of its capacity. Because of this, caution should be exercised in using this as a method of determining a culvert size for the purpose of handling a particular water volume. We will use this method to design culverts that will provide suitable velocities for fish passage. As with any watercourse, a pipe of any type will have physical attributes that affect the rate of water flow over its surface. Pipe diameter affects the ratio of the cross sectional area to the wetted perimeter (R = A / P w ). Surface roughness and irregularities affect the friction and turbulence of the flow, which is expressed as a Manning s coefficient (n). The corrugation of metal culvert pipes is a major part of the coefficient. It is measured in terms of pitch x depth and by the direction of the corrugation. Pitch (P) Depth (D) Shape of corrugated metal for a culvert pipe. Specifications will include the metal thickness ( gauge ) and P x D (e.g. 76 mm x 5 mm) Helical Corrugation Annular Corrugation Some corrugated metal pipes (CMP) are filled, or partly filled with asphalt ( paved ) to reduce the coefficient. The following table provides Manning coefficients for several different types and sizes of CMP. 7

V a lu e s o f C o e ffic ie n t o f Ro u g h n e s s (n ) fo r S ta n d a rd C o rru g a te d S te e l P ip e (M a n n in g 's F o rm u la ) C orrugations A nnula r 68x13m m 1400 A ll D iam eters & Larger U np a ve d 0.0 4 0.0 1 0.0 1 1 0.0 1 3 0.0 1 4 0.0 1 5 0.0 1 8 0.0 1 8 0.0 0 0.0 1 5% P aved 0.01 0.014 0.017 0.00 0.019 F ully P aved 0.01 0.01 0.01 0.01 0.01 A nnular 76x5m m 00 & Larger U np a ve d 0.0 7 0.0 3 0.0 3 0.0 4 0.0 5 0.0 6 0.0 7 5% P aved 0.03 0.00 0.00 0.01 0.0 0.0 0.03 F ully P aved 0.01 0.01 0.01 0.01 0.01 0.01 0.01 A nnular 15x6m m 38x65m m 00 50 000 & Larger U np a ve d 0.0 5 0.0 0.0 3 0.0 4 0.0 5 5% P aved 0.0 0.019 0.00 0.01 0.0 F ully P aved 0.01 0.01 0.01 0.01 0.01 H e lica l 68x13m m 300 400 500 600 H e lica l - 7 6 x 5 m m 100 1400 1600 1800 000 1400 1600 1800 Helical - 15x6m m 900 100 Taking the results of the previous example, let s assume that the 1600 mm culvert is a Helical 76 mm x 5 mm unpaved pipe with n = 0.04 (from the table). Installed at the creek gradient, the slope S = % or 0.0 Now using the Manning equation, we will determine the rate of flow where, like the last example, the water level is to 90% of the culvert diameter. W d-r r W/ / d-r / 360 - D d r Where pipe is more than ½ full d > r D = 1600mm = 1.6 m r = D/ = 0.8 m d = 90% of D = 0.9(1.6) = 1.44 m d-r = 0.64 m 8

Manning s equation for velocity is: V R 3 S n 1 where: V = the calculated velocity of flow in m / second R = the hydraulic radius ( = A / Pw ) A = the cross sectional area of the stream (m ) (water in culvert) Pw = wetted perimeter (m) S = the slope of the channel segment (m / m) n = coefficient of roughness (see tables) The most challenging part of this assignment is to determine the cross sectional area and wetted perimeter to calculate the hydraulic radius. This requires us to identify some basic shapes in the diagram for which we can calculate area (and perimeters), and then add or subtract the identified areas to get the numerical value for our subject shape. One option in this case is to get the area and the P w of: And then add the area of the missing triangle Going back to the diagram of the whole culvert cross section: Find : cos d r r 73.7 0.64 0.800 0.8 The upper surface of the water: W rsin 0. 96m This additional information is all that is needed to calculate the wetted perimeter and area: 360 P w D 4. 00m 360 360 A r 1 W d r 1.60 0.31 1.91m 360 Next the hydraulic radius is: R A P w 1.91 4.00 0.48m 9

The velocity using Manning s is: R V 3 S n 1.67 0.48 0.0 0.04.5 3.60m / sec Finally, the volume: Q AV 3 1.91 3.60 6.88m / sec If we compare the Q of this calculation with the Q 100 (.79 m 3 / second) used when the 1600 mm culvert was selected from the nomograph, we see a significantly higher figure. This may be confusing at first, but recall that this latest calculation is for just one point in the culvert, and it does not consider all of the dynamics taking place in the entire culvert and its two ends. Also, this calculation used a % slope for the culvert, where the nomograph did not consider slope differences. If a lesser slope is used, the velocity and volume is significantly reduced. Retaining the 90% headwater depth but changing the culvert slope, the Manning equation will produce the following: Slope V (m/sec) Q (m 3 /sec) % 3.60 6.88 1%.55 4.31 0.1% 0.81 1.54 Culvert half full or less It is important to note that the calculations change if the water level is at ½ or less than ½. For a pipe running half full: A 0.5r and P w 0.5D 10

For a pipe less than ½ full, examine the differences in the geometry: 360 - r-d / / r r-d W/ D d r W Where pipe is less than ½ full d < r In this case to get the area and the P w first use: And then subtract the area of the surplus triangle (Note that the height of the triangle changes from: d - r (if d > r) to r - d (in this case where d < r) Culvert variables and their effect Looking at Manning s equation again, the following relationships between each variable and the resultant velocity (and therefore volume) can be seen for a given culvert diameter. 3 R S V n As the water depth decreases, velocity decreases (because the value of R goes down) As slope (S) decreases, velocity decreases Anything that increases the coefficient of roughness (n) will decrease the velocity. 1 11

Fish Passage When crossing fish bearing watercourses, the ideal is to leave the streambed entirely intact by constructing a bridge or an open bottom culvert that spans the entire channel and leaves the bed in a natural condition. Assuming sufficient depth of water, pipe culverts can affect fish passage by either creating a physical barrier (e.g. an elevated outfall too high for the fish to reach) or by accelerating the velocity of water flow to beyond the swimming capabilities of the fish. Refer to the Stream Crossing Guidebook for Fish Streams (1998) and Fish Stream Crossing Guidebook (00) for a discussion on fish passage parameters. Specifically, look at the tables that provide information on the maximum capabilities of various fish to travel upstream. Critical water levels for the fish passage are calculated using a channel flow maintenance level which is illustrated below. The velocity and volume of water flow at this point are called high passage and are labeled V hp and Q hp. Source: FPC: Stream Crossing for Fish Streams Guidebook Calculations of V hp and Q hp are performed as previously described, except for the reduced area and wetted perimeter. The culvert must still be designed for Q 100, but that design is then checked for water flow Q hp. If V hp exceeds the ability of the fish, the culvert variables must be adjusted to slow down the velocity. 1

Velocity can be slowed by: Increasing the culvert size, which will reduce the depth of flow and the hydraulic radius Reducing the slope Increasing n by sinking the culvert into the streambed and filling the culvert bottom with materials (e.g. rock, boulders) similar to the natural streambed. This is called embedment. Baffles may also be installed in the pipe. Whenever the culvert velocity is reduced from the Q 100 design, the culvert must be rechecked to ensure that it will still carry the volume at the 100-year event. Baffles or embedment effectively reduce the area available for water flow and must be considered in the new calculations. It may take several attempts to match an appropriate culvert size and installation for both fish passage and the 100-year event. A final remark Stream flow calculations and culvert design are obviously not an exact science. The ability to assess a site for appropriate evidence and to anticipate factors that will affect culvert performance require skilled application of the knowledge of the planner. 13

14