Discharge Measurement
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Transcript of Discharge Measurement
How do we measure how much water is in a stream?
• Volumetric measurements-– Work on very low flows, collect a known
volume of water for a known period of time Volume/time is discharge or Q
• Cross-section/velocity measurements• Dilution gaging with salt or dye• Artificial controls like weirs• Empirical equations, e.g. Manning’s eqn.
Site factors for gaging
1. stable control - bedrock, non-erosive channel, man-made structure
2. locate gage a short distance above control3. want minimal backwater or tidal influence4. straight reach above gage for 4-5 channel widths5. No local inflows or outflows- groundwater or flood bypasses6. must be accessible at all times7. securely mounted structure8. stable confining banks9. good to have a benchmark nearby for datum10. good to have an auxillary stage nearby- staff gage
Other considerations
• Few eddies or areas of zero velocity
• Few instream obstacles
• Relatively consistent cross-section profile
• Velocity and depth do not exceed instrument capabilities or personnel height
Velocity – Area Method of discharge measurement
By measuring the cross-sectional area of the stream and the Average stream velocity, you can compute discharge
Q = VA units are L3/t (volume / time)
Where Q is discharge V is velocity A is cross-sectional area
Pygmy MeterRotations make clicking
sound in headphones
If current strong may need weight
U Mass, Boston
Velocity Profile
0.6 depth
U Mass, Boston
0.8
0.2
If stream is deep, take average of measurements at 0.2 and 0.8
Velocity Distribution In A Channel
Depth-averaged velocity is above the bed at about 0.4 times the depth
Photo from Black Hills State University
How many subsections?
• Subsections should be at least 0.3 feet or ~0.1 m wide
• Each subsection should have 10% or less of total discharge
• Number of subsections should be doable
in a reasonable amount of time
Water surface
Tape measure- horizontal location of measures taken from tape
Velocity measured 0.6d from water surface (0.4d from bottom)
Record x value (tape distance), y value (total depth at measurementsite, and velocity at 0.6d
Measurement represents mid-section of a polygon
Velocity – Area method of discharge measurement
Area included
Area not included
Key Assumption: Over estimation (area included) = Under estimation (area not included), therefore cross-section area is simply the sum of all the sections (rectangles), which is much easier than taking the integral! However, the hypotenuse of each over-under estimation triangle can be used to calculate the wetted perimeter.
Mid-point method of calculating discharge (Q)Location of depth and velocity measurements
Equation for computing subsection discharge - qi
Equation for computing q in each subsection
X = distance of each velocity point along tape
Y = depth of flow where velocity is measured
V = velocity
Q = total discharge = sum of qis
Float method of discharge measurement
• Gives good estimates when no equipment is available
• Use something that floats that you can retrieve or is biodegradable if you can’t retrieve it– E.g. oranges, dried orange peels, tennis balls
Float method of velocity measurement
Three people are needed to run the float test. One should be positioned upstream and the other downstream a known distance apart, one in the middle to record data.
The upstream person releases the f loat and starts the clock and the downstream person catches the float and signals to stop the clock. The recorder writes down the time of travel of the float.
Velocity is the distance traveled divided by the time it takes to travel that distance.
You should conduct at least 3 float tests and take an average velocity.
With an estimate of cross-sectional area, discharge can be computed as Q = VA where V is average velocity
U Mass, Boston
Float Method
surface velocity = distance / time
average velocity = (0.8*surface velocity) U Mass, Boston
Float method in action
U Mass, Boston
Dilution gaging method
• Use a chemical tracer, dye or salt– Exotic to stream– Stable– Non-toxic– Cheap– Detectable
• Do mass balance on concentrations upstream and downstream
Constant injection method
• Inject at known rate for some time period• Do mass balance
• CTQT = CTd (Q + QT)– CT is concentration of tracer upstream– QT rate of input of tracer upstream– CTd is equilibrium concentration of tracer downstream
• Q = QT (CT - CTd ) CTd
Stream Stage- elevation
The stage of a stream is the elevation of the water surface above a datum.
The most commonly used datum is mean sea level.
Gages are used to measure the stage of streams. Types of gages:
- recording- non-recording
How else might we estimate streamflow?
U Mass, Boston
Fixed Gauging Stations - Weirs
Stable cross section with simple geometryrating curve – just measure stage
U Mass Boston
Nonrecording gauges
Staff Gauge
Estimating Peak Flow
Debris Line
Crest Gauges - Cork
How do we measure the stage?
U Mass, Boston
Continuous Measurement - Water Level Recorders
U Mass, Boston
The Stage of a Stream
Float moves up / down with water surfaceU Mass, Boston
Measure discharge at different flows
How can we relate stage to discharge?
Rating Curve – relates stage to discharge Empirical relationship from observations
USGS
Rating curves usually have a break point, which is around the stage at which the river spreads out of it's banks, or it could be at a lower stage if the river bed cross section changes dramatically. Above that stage, the river does not rise as fast, given that other conditions remain constant. This is illustrated by a change in slope in the rating curve. On this figure the break point appears to be around 6-7 feet.
Rating curve
Fit a mathematical equation
We can do this is Excel
Very often it is a power equation (log-log)
U Mass, Boston
Resistance Equations
Manning’s Equation Equation 7.2
2132 SRn
49.1v
Manning’s Equation• In 1889 Irish Engineer, Robert Manning
presented the formula:
2132 SRn
49.1v
• v is the flow velocity (ft/s)
• n is known as Manning’s n and is a coefficient of roughness
• R is the hydraulic radius (a/P) where P is the wetted perimeter (ft)
• S is the channel bed slope as a fraction
• 1.49 is a unit conversion factor. Approximated as 1.5 in the book. Use 1.0 if SI (metric) units are used.
Equation 7.2
Discharge from Manning’s equation• Q = vA equation 7.1• v =(1.5/n) R2/3 S1/2 (equation 7.2)• R= A/P, hydraulic radius (equation 7.3) • A = width x depth • P= wetted perimeter• S = water slope (ft/ft) • N = Manning’s roughness coefficient
Parameters for Manning’s equation
Wetted perimeter = p area of stream in contact with bottom and sides
Water surface
Cross sectional area = A
R = hydraulic radius = A/p
Area included
Area not included
Key Assumption: Over estimation (area included) = Under estimation (area not included), therefore cross-section area is simply the sum of all the sections (rectangles), which is much easier than taking the integral! However, the hypotenuse of each over-under estimation triangle can be used to calculate the wetted perimeter.
Mid-point method of calculating discharge (Q)Location of depth and velocity measurements
Type of Channel and Description
Minimum Normal Maximum
Streams on a plain
Clean, straight, full stage, no rifts or deep pools 0.025 0.03 0.033
Clean, winding, some pools, shoals, weeds & stones
0.033 0.045 0.05
Same as above, lower stages and more stones 0.045 0.05 0.06
Sluggish reaches, weedy, deep pools 0.05 0.07 0.07
Very weedy reaches, deep pools, or floodways 0.075 0.1 0.15
with heavy stand of timber and underbrush
Mountain streams, no vegetation in channel, banks steep, trees & brush along banks submerged at high stages
Bottom: gravels, cobbles, and few boulders 0.03 0.04 0.05
Bottom: cobbles with large boulders 0.04 0.05 0.07
Table 7.1 Manning’s n Roughness Coefficient
http://manningsn.sdsu.edu/barnes013_24.html
http://manningsn.sdsu.edu/barnes101_41.html
MountainStream-Bottom with cobbles and large boulders
Plains stream- full stage, no rifts or deep pools
http://manningsn.sdsu.edu/barnes020_27.html
Channel Conditions Values Material Involved Earth n0 0.025
Rock Cut 0.025 Fine Gravel 0.024 Coarse Gravel 0.027 Degree of irregularity Smooth n1 0.000 Minor 0.005 Moderate 0.010 Severe 0.020 Variations of Channel Cross
Section Gradual n2 0.000
Alternating Occasionally 0.005 Alternating Frequently 0.010-0.015 Relative Effect of Obstructions Negligible n3 0.000 Minor 0.010-0.015 Appreciable 0.020-0.030 Severe 0.040-0.060 Vegetation Low n4 0.005-0.010 Medium 0.010-0.025 High 0.025-0.050 Very High 0.050-0.100 Degree of Meandering Minor m5 1.000 Appreciable 1.150 Severe 1.300
Table 7.2. Values for the computation of the roughness coefficient (Chow, 1959)
n = (n0 + n1 + n2 + n3 + n4 ) m5 Equation 7.12