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Using Plants to Improve Flood Management - Floodplain Management

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Roughness of <strong>Flood</strong>plain <strong>Plants</strong><br />

<strong>Using</strong> <strong>Plants</strong> <strong>to</strong> <strong>Improve</strong> <strong>Flood</strong> <strong>Management</strong>


What is Roughness<br />

Texture<br />

Friction<br />

Blockage<br />

Resistance <strong>to</strong><br />

flow


<strong>Plants</strong> have roughness


So do the<br />

Things we<br />

Put in channels


We measure roughness using Mannings n –<br />

a number used in a whole bunch of hydraulic<br />

analyses<br />

R= hydraulic radius<br />

S f = friction slope<br />

V = water velocity<br />

n=(1/v)R 2/3 S 1/2<br />

f


Manning's n Coefficients for Open Channel Flow<br />

The fluid mechanics calculations website<br />

Manning n has no units.<br />

Material Manning n Material Manning n<br />

Natural Streams<br />

Excavated Earth Channels<br />

Clean and Straight 0.030 Clean 0.022<br />

Major Rivers 0.035 Gravelly 0.025<br />

Sluggish with Deep Pools 0.040 Weedy 0.030<br />

S<strong>to</strong>ny, Cobbles 0.035<br />

Metals<br />

<strong>Flood</strong>plains<br />

Brass 0.011 Pasture, Farmland 0.035<br />

Cast Iron 0.013 Light Brush 0.050<br />

Smooth Steel 0.012 Heavy Brush 0.075<br />

Corrugated Metal 0.022 Trees 0.15<br />

Non-Metals<br />

Glass 0.010 Finished Concrete 0.012<br />

Clay Tile 0.014 Unfinished Concrete 0.014<br />

Brickwork 0.015 Gravel 0.029<br />

Asphalt 0.016 Earth 0.025<br />

Masonry 0.025 Planed Wood 0.012<br />

Unplaned Wood 0.013


Type of Channel and Description<br />

Minimum Normal Maximum<br />

Natural streams - minor streams (<strong>to</strong>p width at floodstage < 100 ft)<br />

1. Main Channels<br />

a. clean, straight, full stage, no rifts or deep pools<br />

b. same as above, but more s<strong>to</strong>nes and weeds<br />

c. clean, winding, some pools and shoals<br />

d. same as above, but some weeds and s<strong>to</strong>nes<br />

0.025 0.030 0.033<br />

0.030 0.035 0.040<br />

0.033 0.040 0.045<br />

0.035 0.045 0.050<br />

e. same as above, lower stages, more ineffective<br />

slopes and sections<br />

0.040 0.048 0.055<br />

f. same as "d" with more s<strong>to</strong>nes 0.045 0.050 0.060<br />

g. sluggish reaches, weedy, deep pools 0.050 0.070 0.080<br />

h. very weedy reaches, deep pools, or floodways<br />

with heavy stand of timber and underbrush<br />

0.075 0.100 0.150<br />

2. Mountain streams, no vegetation in channel, banks usually steep, trees and brush<br />

along banks submerged at high stages<br />

a. bot<strong>to</strong>m: gravels, cobbles, and few boulders 0.030 0.040 0.050<br />

b bot<strong>to</strong>m: cobbles with large boulders<br />

0.040 0.050 0.070


Mannings n – average of all textures,<br />

but used as a model fitting parameter.<br />

Inaccuracy in other model parameters:<br />

Shape, channel form, grade, slope,<br />

sinuosity, velocity, water density, …<br />

get assigned <strong>to</strong> roughness


O’Connor Lakes, Star Bend<br />

Lots of variation:<br />

∆ velocity = ∆ roughness<br />

Pre‐project velocities


The need for improving safety and<br />

ecosystem management prompted us<br />

<strong>to</strong> look at the role some common<br />

plants play in creating roughness.<br />

<strong>Plants</strong> selected because they are adapted <strong>to</strong><br />

flooding, are common in our floodways, and<br />

provide good habitat value


Mulefat<br />

Wild Rose<br />

Sandbar willow<br />

California Blackberry


x= 47'<br />

x=33'<br />

x=19'<br />

Flume<br />

tail tank<br />

H<br />

V<br />

6’<br />

Depth<br />

Control<br />

Weir<br />

x =60'<br />

C<br />

B<br />

A<br />

2’<br />

x =0'<br />

Pumps<br />

Point gage locations<br />

and<br />

velocity measurement sections


Velocity measurement locations in a cross-section<br />

Flume width 5 ft<br />

Flume width 5 ft<br />

8 ft<br />

6 ft<br />

8 ft<br />

6 ft<br />

2 ft<br />

2 ft<br />

4 ft bin Width<br />

4 ft bin Width<br />

Water depth<br />

higher than 2 ft<br />

Water depth<br />

lower than 2 ft


Velocity and Water Surface Profiles<br />

V Scale X 19.5 33.5 47<br />

2 Z 2.65 2.54 2.56<br />

2.17 4.39 4.69 4.86<br />

1.67 4.18 4.56 4.64<br />

V (ft/s) 1.17 4.11 4.42 4.44<br />

0.67 4.00 4.20 4.03<br />

0.25 3.62 3.47 3.36<br />

8.00<br />

7.00<br />

6.00<br />

Flow Regime S15<br />

Elevation [ft]<br />

5.00<br />

4.00<br />

3.00<br />

2.00<br />

1.00<br />

V= 2 ft/s<br />

0.00<br />

0 10 20 30 40 50 60 70<br />

X [ft]<br />

Water Surface Flume Top Elevation Bot<strong>to</strong>m Elevation<br />

Velocity at P#2 Velocity at P#3 Velocity at P#4


STREAMBED BARE<br />

SOIL SAMPLE<br />

PREPARATION


Sandbar Willow<br />

1 st replicate


Sandbar Willow<br />

3 rd replicate


Velocity Profile Sandbar Willow<br />

5<br />

4<br />

V=1.5 ft/s H=1.5 ft<br />

5<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft 4<br />

V=3.0 ft/s H=1.5 ft<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft<br />

3<br />

3<br />

Z(ft)<br />

Z(ft)<br />

2<br />

2<br />

1<br />

1<br />

0<br />

0 2 4 6<br />

Velocity (ft/s)<br />

0<br />

0 2 4 6<br />

Velocity (ft/s)


Velocity Profile Sandbar Willow<br />

5<br />

4<br />

V=1.5 ft/s H=5 ft<br />

5<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft 4<br />

V=3.0 ft/s H=5 ft<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft<br />

3<br />

3<br />

Z(ft)<br />

Z(ft)<br />

2<br />

2<br />

1<br />

1<br />

0<br />

0 2 4 6<br />

Velocity (ft/s)<br />

0<br />

0 2 4 6<br />

Velocity (ft/s)


Velocity Profile Sandbar Willow<br />

5<br />

4<br />

V=4.5 ft/s H=3 ft<br />

5<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft 4<br />

V=6.0 ft/s H=3 ft<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft<br />

3<br />

3<br />

Z(ft)<br />

Z(ft)<br />

2<br />

2<br />

1<br />

1<br />

0<br />

0 2 4 6<br />

Velocity (ft/s)<br />

0<br />

0 2 4 6<br />

Velocity (ft/s)


Roughness Coefficient vs Reynolds Number<br />

Sandbar Willow<br />

ng's n<br />

Manni<br />

0.09<br />

0.08<br />

0.07<br />

0.06<br />

0.05<br />

0.04<br />

0.03<br />

0.02<br />

0.01<br />

0.00<br />

0 200,000 400,000 600,000<br />

Bare Soil<br />

Willow1<br />

Willow2<br />

Willow3<br />

Linear (Bare Soil)<br />

Linear (Willow1)<br />

Linear (Willow2)<br />

Linear (Willow3)<br />

Re


Velocity Profile Mulefat<br />

V=4.5 ft/s H=3ft<br />

V=6 ft/s H=3 ft<br />

5<br />

4<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft<br />

5<br />

4<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft<br />

Depth<br />

(ft)<br />

3<br />

2<br />

Depth<br />

(ft)<br />

3<br />

2<br />

1<br />

1<br />

0<br />

0 2 4 6<br />

Velocity (ft/s)<br />

0<br />

0 5 10<br />

Velocity (ft/s)


Comparative Roughness: Mulefat & Sandbar Willow<br />

Man ning's n<br />

0.12<br />

0.10<br />

0.08<br />

0.06<br />

Bare Soil<br />

Willow (March)<br />

Willow (April)<br />

Willow (May)<br />

Mule Fat (Nov-Dec)<br />

Mule Fat (Oct-Nov)<br />

Linear (Bare Soil)<br />

Linear (Willow (March))<br />

Linear (Willow (April))<br />

Linear (Willow (May))<br />

Linear (Mule Fat (Nov-Dec))<br />

Linear (Mule Fat (Oct-Nov) )<br />

0.04<br />

0.02<br />

0.00<br />

0 100,000 200,000 300,000 400,000 500,000 600,000 700,000<br />

Re


Velocity Profile California Blackberry<br />

V=3 ft/s Ht=5ft<br />

V=6 ft/s Ht=3.4ft<br />

6<br />

5<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft<br />

6<br />

5<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft<br />

4<br />

4<br />

Height<br />

(ft)<br />

3<br />

Heigh ht (ft)<br />

3<br />

2<br />

2<br />

1<br />

1<br />

0<br />

0.0 2.0 4.0 6.0<br />

Velocity (ft/s)<br />

0<br />

0.0 2.0 4.0 6.0<br />

Velocity (ft/s)


Roughness coefficients vs Reynolds Number<br />

California Blackberry<br />

Mannin ng's n<br />

0.16<br />

0.14<br />

0.12<br />

0.10<br />

008 0.08<br />

0.06<br />

Blackberry(Mar)<br />

Blackberry(Apr)<br />

Blackberry(May)<br />

Willow (March)<br />

Willow (April)<br />

Willow (May)<br />

Mule Fat (Oct-Nov)<br />

Mule Fat (Nov-Dec)<br />

Mule Fat (January)<br />

Mule Fat (February)<br />

Bare Soil<br />

Linear (Blackberry(Mar))<br />

Linear (Blackberry(Apr))<br />

Linear (Blackberry(May))<br />

0.04<br />

0.02<br />

0.00<br />

0 100,000 200,000 300,000 400,000 500,000 600,000 700,000<br />

Re


Velocity profile Wildrose<br />

V=4.5ft/s H=3ft<br />

V=6ft/s H=3.4ft<br />

6<br />

5<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft<br />

6<br />

5<br />

V|x=16ft<br />

V|x=34ft<br />

V|x=47ft<br />

depth (ft)<br />

Water<br />

4<br />

3<br />

2<br />

Water<br />

depth (ft)<br />

4<br />

3<br />

2<br />

1<br />

1<br />

0<br />

0 2 4 6 8<br />

Velocity (ft/s)<br />

0<br />

0 2 4 6 8<br />

Velocity (ft/s)


Mannings Coefficient vs Reynolds Number<br />

Rose and Blackberry<br />

Manning's<br />

n<br />

0.16<br />

0.14<br />

0.12<br />

0.10<br />

0.08<br />

Blackberry(Mar)<br />

Blackberry(Apr)<br />

Blackberry(May)<br />

Willow (March)<br />

Willow (April)<br />

Willow (May)<br />

Mule Fat (Oct-Nov)<br />

Mule Fat (Nov-Dec)<br />

Mule Fat (January)<br />

Mule Fat (February)<br />

Bare Soil<br />

Wildrose#1(Jun)<br />

Wildrose#2(Jun)<br />

Wildrose#3(Jul)<br />

Linear (Blackberry(Mar))<br />

Linear (Blackberry(Apr))<br />

Linear (Blackberry(May))<br />

Linear (Wildrose#1(Jun))<br />

Linear (Wildrose#2(Jun))<br />

Linear (Wildrose#3(Jul))<br />

0.06<br />

0.04<br />

0.02<br />

0.00<br />

0 100,000 200,000 300,000 400,000 500,000 600,000 700,000<br />

Re


Erosion Summary<br />

Erosion (in)<br />

3<br />

Bare soil<br />

2<br />

mulefat<br />

1<br />

rose<br />

willow<br />

1<br />

3 5<br />

Velocity (ft/sec)


Swim Response <strong>to</strong> Sandbar Willow<br />

○ = TBF Swim Chamber<br />

● = MO 2<br />

■ =TBF Flume<br />

(1.5 ft/s)<br />

(3.0 ft/s)<br />

(0.5 ft/s)


A Mosaic of <strong>Plants</strong><br />

As built – velocity

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