Transcript Slide 1

National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
1D MORPHODYNAMICS OF MOUNTAIN RIVERS: UNIFORM SEDIMENT
Morphodynamics is the study of the variation of morphology in response to net
erosion or deposition of sediment. The images below illustrate a reach of the Mad
River, California which has undergone bed lowering (degradation) in response to
gravel mining.
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
AGGRADATION AND DEGRADATION
A river reach aggrades (bed elevation increases) when it is supplied more sediment
than it exports.
A river reach degrades (bed elevation decreases) when it exports more sediment
than it is supplied.
Degraded reach of the Uria
River, Venezuela after the Vargas
disaster, 1999. Cour. J. Lopez.
The Ok Tedi in Papua New Guinea
had aggraded some 5 m near this 2
bridge in response to mine disposal.
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
RESPONSE OF A RIVER TO SUDDEN VERTICAL FAULTING CAUSED
BY AN EARTHQUAKE
View in November, 1999, shortly
after the earthquake caused a sharp
3 m elevation drop at a fault.
View in May, 2000 after aggradation
and degradation have smoothed out
the elevation drop.
The above images of the Deresuyu River, Turkey, are courtesy
of Patrick Lawrence and François Métivier (Lawrence, 2003)
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
RESPONSE OF A RIVER TO SUDDEN VERTICAL FAULTING CAUSED
BY AN EARTHQUAKE contd.
Inferred initial profile
immediately after faulting in
November, 1999
Profile in May, 2001
Upstream degradation (bed level lowering) and downstream aggradation
(bed level increase) are realized as the river responds to the knickpoint
created by the earthquake (Lawrence, 2003).
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
BEDLOAD TRANSPORT
The morphodynamics of mountain rivers is controlled by the differential transport of
gravel moving as bedload. Bedload particles slide, roll, or saltate just above the
bed, as opposed to suspended particles, which can be wafted high in the water
column by turbulence. Bedload transport of uniform 7-mm gravel in a flume is
illustrated below. The video clip is from the experiments of Miguel Wong.
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
BELOW-CAPACITY BEDLOAD TRANSPORT
The video clip is from the experiments of Phairot Chatanantavet.
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
EXNER EQUATION FOR THE CONSERVATION OF BED SEDIMENT
In 1D morphodynamics bed elevation variation is considered in the absence of
width variation, and local bed features such as bars are not specifically modeled.
1D morphodynamics describes the time variation of the longitudinal profile of river
bed elevation in response to net sediment deposition or erosion.
The first step in characterizing 1D morphodynamics is the derivation of the Exner
(19??) equation of bed sediment conservation. The parameters defined below are
used in the derivation.
qb = volume bedload transport rate per unit width [L2T-1]
s = sediment density [ML3/T]
gb = sqb = mass bedload transport rate per unit width [ML-1T-1]
 = bed elevation [L]
p = porosity of sediment in bed deposit [1]
(volume fraction of bed sample that is holes rather than sediment:
0.25 ~ 0.55 for noncohesive material)
x = streamwise coordinate [L]
t = time [T]
B = channel width [L]
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
CONSERVATION OF BED SEDIMENT
/t(gravel mass in control volume of bed) = mass gravel inflow rate – mass
gravel outflow rate



s (1   p )x  1  gb x  gb
t
x  x
 1   q
s
b x
 qb
x  x
 1
or thus
qb

(1   p )
t
x
water
qb
qb
This corresponds to the original
form derived by Exner.
The control volume has a
unit width normal to x

bed sediment + pores
1
8
x
x
x +x
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
BACKGROUND AND ASSUMPTIONS FOR 1D MORPHODYNAMICS
Change in channel bed level (aggradation or degradation) can occur in response to:
• increase or decrease in upstream sediment supply;
• change in hydrologic regime (water diversion or climate change);
• change in river slope (e.g. channel straightening);
• increased or decreased sediment supply from tributaries;
• sudden inputs of sediment from debris flows or landslides;
• faulting due to earthquakes or other tectonic effects such as tilting along the reach,
and;
• changing base level at the downstream end of the reach of interest.
Here “base level” loosely means a
controlling elevation at the downstream
end of the reach of interest. It means
water surface elevation if the river flows
into a lake or the ocean, or a
downstream bed elevation controlled
by e.g. tectonic uplift or subsidence at
a point where the river is not flowing
into standing water.
Base level of this reach
of the Eau Claire river,
Wisconsin, USA is
controlled by a reservoir,
Lake Altoona
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
THE EQUILIBRIUM STATE contd.
Rivers are different in many ways from laboratory flumes. It nevertheless helps to
conceptualize rivers in terms of a long, straight, wide, rectangular flume with high
sidewalls (no floodplain), constant width and a bed covered with alluvium. Such a
“river” has a simple mobile-bed equilibrium (graded) state at which flow depth H, bed
slope S, water discharge per unit width qw and bed material load per unit width qt
remain constant in time t and in the streamwise direction x. A recirculating flume
(with both water and sediment recirculated) at equilibrium is illustrated below.
water
sediment
pump
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
THE EQUILIBRIUM STATE contd.
The hydraulics of the equilibrium state are those of normal flow. Here the case of a
plane bed (no bedforms) is considered as an example. The bed consists of uniform
material with size D. The governing equations are (see lecture on hydraulics):
Water conservation:
qw  UH
Momentum conservation:
Friction relations:
b  Cf U2
b  gHS
1/ 6
Cf  const (Chezy)
or
Cf 1/ 2
H
 r  
 kc 
(Manning  Strickler )
where kc is a composite bed roughness which may include the effect of bedforms
(if present).
Generic transport relation of the form of Meyer-Peter and Müller for total bed
material load: where t and nt are dimensionless constants:
nt
q  t (  c )nt
or
 

qb
 t  b  c 
RgD D
  RgD

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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
THE EQUILIBRIUM STATE contd.
In the case of the Chezy resistance relation, the equations governing the
normal state reduce to (Slide 26 of the lecture on hydraulics):
 C f q2w
H  
 gS
1/ 3




nt
  C q2 1/ 3 S2 / 3 


  c 
qb  RgD D  t   f w 
  g  RD 

In the case of the Manning-Stickler resistance relation with an exponent of 1/6, the
equations governing the normal state reduce to (Slide 30 of the lecture on hydraulics,

with kc  ks and g  r):
 k1s/ 3q2w 

H   2

gS
 r

3 / 10

  k q
qb  RgD D t  
g

 
1/ 3 2
s
w
2
r



3 / 10
nt
S  

  c 
RD 



7 / 10
Let D, ks and R be given. In either case above, there are two equations for four
parameters at equilibrium; water discharge per unit width qw, volume sediment
discharge per unit width qt, bed slope S and flow depth H. If any two of the set (qw,
qb, S and H) are specified, the other two can be computed. In a sediment-feed
flume, qw and qb are set, and equilibrium S and H can be computed from either of the
above pair. In a recirculating flume, qw and H are set (total water mass in flume is12
conserved), and qb and S can be computed.
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
SIMPLIFICATIONS
The concepts of aggradation and degradation are best illustrated by using simplified
relations for hydraulic resistance and sediment transport. Here the following
simplifications are made in addition to the assumptions of constant width and
the absence of a floodplain:
1.
2.
3.
4.
The case of a Manning-Strickler formulation with constant roughness ks is
considered;
Bed material is taken to be uniform with size D;
Only the portion of boundary shear stress due to skin friction is available to
transport sediment;
The Exner equation of sediment conservation is based on a computation of
bedload, which is computed via the generic equation
 

qb
  t  s b  c 
RgD D
  RgD

nt
where s  1 is a constant to convert total boundary shear stress to that due to
skin friction (if necessary). For example, to recover the corrected version of
Meyer-Peter and Müller (1948) relation of Wong (2003) gravel transport, set t =
3.97 , nt = 1.5, c* = 0.0495 and s = 1. A setting s = 0.75 implies that 75%13
of the total resistance is skin friction and 25% is form drag.
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
5.
SIMPLIFICATIONS contd.
The full flood hydrograph or flow duration curve of discharge variation is
replaced by a flood intermittency factor If, so that the river is assumed to be at
low flow (and not transporting significant amounts of sediment) for time fraction
1 – If, and is in flood at constant discharge Q, and thus constant discharge per
unit width qw = Q/B for time fraction If (Paola et al., 1992). The implied
hydrograph takes the conceptual form below:
flood
Q
low flow
t
In the long term, then, the relation between actual time t and time that the river has
been in flood tf is given as
t f  If t
Let the value of the bed material load at flood flow qb be computed in m2/s. Then
the total mean annual sediment load Gt in million tons per year is given as
Gt  sqbBIf ta /(1x106 )
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
AN ISSUE OF NOTATION
A numerical method and program for computing the 1D morphodynamics of rivers
using the normal flow approximation is introduced in the succeeding slides. The
code was originally written for a generic river (gravel-bed or sand-bed), for which
the total volume bed material load per unit width is denoted as qt. Here this code is
applied to mountain rivers, so wherever qt appears, the user of this lecture material
should make the transformation
qt  qb
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
AGGRADATION AND DEGRADATION AS TRANSIENT RESPONSES TO
IMPOSED DISEQIUILBRIUM CONDITIONS
Aggradation or degradation of a river reach can be considered to be a response to
disequilibrium conditions, by which the river tries to reach a new equilibrium. For
example, if a river reach has attained an equilibrium with a given sediment supply
from upstream, and that sediment supply is suddenly increased at t = 0, the river
can be expected to aggrade toward a new equilibrium.
final equilibrium bed profile in
balance with load qt > qta
transient aggradational profile
sediment supply
increases from qta
to qt at t = 0

antecedent equilibrium bed profile
established with load qta
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
NORMAL FLOW FORMULATION OF MORPHODYNAMICS: GOVERNING
EQUATIONS
In this chapter the flow is calculated by approximating it with the normal flow
formulation, even if the profile itself is in disequilibrium. The approximation is of loose
validity in most cases of interest. It is particularly justifiable in the case of mountain
rivers, as shown in the lecture on hydraulics Using the Exner formulation for
sediment conservation and the Manning-Strickler formulation for flow resistance, the
morphodynamic problem has the following character:
(1   p )
q

 -If t
t
x

  k1s/ 3q2w 
qt  RgD D t s  2 
g

  r 
3 / 10
nt
S7 / 10   

  c 
RD 



, S

x
In the above relations t denotes real time (as opposed to flood time) and the
intermittency factor If accounts for the fact that the river is only occasionally in flood
(and thus morphologically active).
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
THE NORMAL FLOW MORPHODYNAMIC FORMULATION AS A
NONLINEAR DIFFUSION PROBLEM
The previous formulation can be rewritten as:
  
 

 d (S ) 

t x 
x 
where d is a kinematic “diffusivity” of sediment (dimensions of L2/T) given by the
relation
nt
3 / 10
If RgD D 
S7 / 10   
  k1s/ 3q2w 

  c 
d 
t s  2 
(1  p ) S   r g 
RD 


 

The top equation is a (nonlinear) diffusion equation. In the bottom equation, it is seen
that d is dependent on S = - /x, so that the diffusion formulation is nonlinear.
The problem is second-order in x and first order in t, so that one initial
condition and two boundary conditions are required for solution.
18
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
INITIAL AND BOUNDARY CONDITIONS
The reach over which morphodynamic evolution is to be described must have a
finite length L. Here it extends from x = 0 to x = L.
The initial condition is that of a specified bed profile;
( x, t ) t 0  I ( x)
The simplest example of this is a profile with specified initial downstream elevation
Id at x = L and constant initial slope SI;
( x, t ) t 0  Id  SI (L  x)
The upstream boundary condition can be specified in terms of given sediment
supply, or feed rate qtf, which may vary in time;
qt ( x, t ) x0  qtf (t )
The simplest case is that of a constant value of sediment feed.
The downstream boundary condition can be one of prescribed base level in terms of
bed elevation;
( x, t) xL  d (t)
Again the simplest case is a constant value, e.g. d = 0.
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National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
NOTES ON THE DOWNSTREAM BOUNDARY CONDITION
In principle the best place to locate the downstream boundary condition is at a
bedrock exposure, as illustrated below. In most alluvial streams, however, such
points may not be available. Three alternatives are possible:
a) Set the boundary condition at a point so far downstream that no effect of e.g.
changed sediment feed rate is felt during the time span of interest;
b) Set the boundary condition where the river joins a much larger river; or
c) Set the boundary condition at a point of known water surface elevation, such as
a lake.
Alluvial Kaiya River, Papua New Guinea, and downstream bedrock exposure
Bedrock
makes a
good
downstream
b.c.
20
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
DISCRETIZATION FOR NUMERICAL SOLUTION
The morphodynamic problem is nonlinear and requires a numerical solution. This
may be done by dividing the domain from x = 0 to x = L into M subreaches bounded
by M + 1 nodes. The step length x is then given as L/M. Sediment is fed in at an
extra “ghost” node one step upstream of the first node.
x 
Feed sediment here!
ghost
i=1
2
L
M
xi  (i  1)x , i  1..M  1
x
3
M -1
L
Bed slope can be computed by the
relations to the right. Once the
slope Si is computed the sediment
transport rate qt,i can be computed
at every node. At the ghost node,
qt,g = qtf.
M
i = M+1
 1  2
,i 1

x
   
i1
Si   i1
, i  2..M
 2 x
 M  M1 , i  M  1
 x
21
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
DISCRETIZATION OF THE EXNER EQUATION
Let t denote the time step. Then the Exner equation discretizes to
i tt
1 qt,i
 i t 
If t , i  1..M
1  p x
where
qt,i
qt,i  qt,i1
qt,i1  qt,i
 au
 (1  au )
x
x
x
and au is an upwinding coefficient. In a pure upwinding scheme, au = 1. In a
central difference scheme, au = 0.5. A central difference scheme generally works
well when the normal flow formulation is used.
At the ghost node, qt,g = qtf. In computing qt,i/x at i = 1, the node at i – 1 (= 0) is
the ghost node. At node M+1, the Exner equation is not implemented because
bed elevation is specified as M+1 = d.
22
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
INTRODUCTION TO RTe-bookAgDegNormal.xls
The basic program in Visual Basic for Applications is contained in Module 1, and is
run from worksheet “Calculator”.
The program is designed to compute a) an ambient mobile-bed equilibrium, and b)
the response of a reach to changed sediment input rate at the upstream end of the
reach starting from t = 0.
The first set of required input includes: flood discharge Q, intermittency If, channel
(bankfull) width B, grain size D, bed porosity p, composite roughness height kc
and ambient bed slope S (before increase in sediment supply). Here composite
roughness height is meant to include the effect of bedforms. For mountain
streams in the absence of form drag, it is appropriate to set kc equal to ks = nkD,
where nk is in the range 3 – 4. When form drag is present it is appropriate to
increase nk to somewhat larger values (~ 5 or 6).
Various parameters of the ambient flow, including the ambient annual bed material
transport rate Gt in tons per year, are then computed directly on worksheet
“Calculator”.
23
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
INTRODUCTION TO RTe-bookAgDegNormal.xls contd.
The next required input is the annual average bed material feed rate Gtf imposed
after t > 0. If this is the same as the ambient rate Gt then nothing should happen;
if Gtf > Gt then the bed should aggrade, and if Gtf < Gt then it should degrade.
The final set of input includes the reach length L, the number of intervals M into
which the reach is divided (so that x = L/M), the time step t, the upwinding
coefficient au (use 0.5 for a central difference scheme), and two parameters
controlling output, the number of time steps to printout Ntoprint and the number of
printouts (in addition to the initial ambient state) Nprint.
The downstream bed elevation d is automatically set equal to zero in the
program.
Auxiliary parameters, including r (coefficient in Manning-Strickler), t and nt
(coefficient and exponent in load relation), c* (critical Shields stress), s (fraction
of boundary shear stress that is skin friction) and R (sediment submerged specific
gravity) are specified in the worksheet “Auxiliary Parameters”.
24
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
INTRODUCTION TO RTe-bookAgDegNormal.xls contd.
The parameter s estimating the fraction of boundary shear stress that is skin
friction, should either be set equal to 1 or estimated using the techniques of
Chapter 9.
In any given case it will be necessary to play with the parameters M (which sets
x) and t in order to obtain good results. For any given x, it is appropriate to
find the largest value of t that does not lead to numerical instability.
The program is executed by clicking the button “Do a Calculation” from the
worksheet “Calculator”. Output for bed elevation is given in terms of numbers in
worksheet “ResultsofCalc” and in terms of plots in worksheet “PlottheData”
The formulation is given in more detail in the worksheet “Formulation”, which is
also available as a stand-alone document, Rte-bookAgDegNormalFormul.doc.
25
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
MODULE 1 Sub Main
This is the master subroutine that controls the Visual Basic program.
Sub Main()
Clear_Old_Output
Get_Auxiliary_Data
Get_Data
Compute_Ambient_and_Final_Equilibria
Set_Initial_Bed_and_time
Send_Output
j=0
For j = 1 To Nprint
For w = 1 To Ntoprint
Find_Slope_and_Load
Find_New_eta
Next w
More_Output
Next j
End Sub
26
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
MODULE 1 Sub Set_Initial_Bed_and_time
This subroutine sets the initial ambient bed profile.
Sub Set_Initial_Bed_and_time()
For i = 1 To N + 1
x(i) = dx * (i - 1)
eta(i) = Sa * L - Sa * dx * (i - 1)
Next i
time = 0
End Sub
27
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
MODULE 1 Sub Find_Slope_and_Load
This subroutine computes the load at every node.
Sub Find_Slope_and_Load()
Dim i As Integer
Dim taux As Double: Dim qstarx As Double: Dim Hx As Double
Sl(1) = (eta(1) - eta(2)) / dx
Sl(M + 1) = (eta(M) - eta(M + 1)) / dx
For i = 2 To M
Sl(i) = (eta(i - 1) - eta(i + 1)) / (2 * dx)
Next i
For i = 1 To M + 1
Hx = ((Qf ^ 2) * (kc ^ (1 / 3)) / (alr ^ 2) / (B ^ 2) / g / Sl(i)) ^ (3 / 10)
taux = Hx * Sl(i) / Rr / D
If fis * taux <= tausc Then
qstarx = 0
Else
qstarx = alt * (fis * taux - tausc) ^ nt
End If
qt(i) = ((Rr * g * D) ^ 0.5) * D * qstarx
Next i
End Sub
28
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
MODULE 1 Sub Find_New_eta
This subroutine implements the Exner equation to find the bed one time step later.
Sub Find_New_eta()
Dim i As Integer
Dim qtback As Double: Dim qtit As Double: Dim qtfrnt As Double: Dim qtdif
As Double
For i = 1 To M
If i = 1 Then
qtback = qqtf
Else
qtback = qt(i - 1)
End If
qtit = qt(i)
qtfrnt = qt(i + 1)
qtdif = au * (qtback - qtit) + (1 - au) * (qtit - qtfrnt)
eta(i) = eta(i) + dt / (1 - lamp) / dx * qtdif * Inter
Next i
time = time + dt
End Sub
29
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
A SAMPLE COMPUTATION
Calculation of River Bed Elevation Variation with Normal Flow Assumption
(Qf)
(Inter)
(B)
(D)
(lamp)
Calculation of ambient river conditions (before imposed change)
Assumed parameters
Q
70 m^3/s
Flood discharge
If
0.03
Intermittency
The colored boxes:
B
25 m
Channel Width
indicate the parameters you must specify.
D
30 mm
Grain Size
The rest are computed for you.
p
0.35
Bed Porosity
(kc)
kc
(S)
S
75 mm
0.008
The ambient sediment transport
rate is 305,000 tons/year. At time
t = 0 this is increased to 700,000
tons per year. The bed must
aggrade in response.
Roughness Height
If bedforms are absent, set kc = ks, where ks = nk D and nk is an order-one factor (e.g. 3).
Ambient Bed Slope
Otherwise set kc = an appropriate value including the effects of bedforms.
Computed parameters at ambient conditions
H
0.875553 m
Flow depth (at flood)
*
0.141503
Shields number (at flood)
q*
0.232414
Einstein number (at flood)
qt
0.004859 m^2/s
Volume sediment transport rate per unit width (at flood)
Gt
3.05E+05 tons/a
Ambient annual sediment transport rate in tons per annum (averaged over entire year)
Calculation of ultimate conditions imposed by a modified rate of sediment input
Gtf
7.00E+05 tons/a
Imposed annual sediment transport rate fed in from upstream (which must all be carried during floods)
qtf
0.011161 m^2/s
Upstream imposed volume sediment transport rate per unit width (at flood)
ult
0.211523
Ultimate equilibrium Shields number (at flood)
Sult
0.014207
Ultimate slope to which the bed must aggrade
Hult
0.736984 m
Ultimate flow depth (at flood)
Click the button to perform a calculation
Calculation of time evolution toward this ultimate state
L
qt,g
x
t
10000
0.011161
1.67E+02
0.01
m
m^2/s
m
year
length of reach
Ntoprint
sediment feed rate (during floods) at ghost node
Nprint
spatial step
M
u
time step
Duration of calculation
200
5
60
0.5
10
Number of time steps to printout
Number of printouts
Intervals
30
Here 1 = full upwind, 0.5 = central difference
years
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
RESULTS OF SAMPLE COMPUTATION
Bed evolution
160
140
Elevation in m
120
0 yr
2 yr
4 yr
6 yr
8 yr
10 yr
Ultimate
100
80
60
40
20
0
0
2000
4000
6000
Distance in m
8000
10000
31
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
INTERPRETATION
The long profile of a river is a plot of bed elevation  versus down-channel
distance x. The long profile of a river is called upward concave if slope S = /x is decreasing in the streamwise direction; otherwise it is called upward
convex. That is, a long profile is upward concave if
S
 2
 2 0
x
x
upward-convex

upward-concave
Aggrading reaches often show
transient upward concave
profiles. This is because the
deposition of sediment causes the
sediment load to decrease in the
downstream direction. The
decreased load can be carried with
a decreased Shields number *,
and thus according to the normalflow formulation of the present
chapter, a decreased slope:
k q
  
 g

x
1/ 3 2
c
w
2
r



3 / 10
S7 / 10
RD
32
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
INTERPRETATION contd.
The transient long profile of Slide 30 is upward concave because the river is
aggrading toward a new mobile-bed equilibrium with a higher slope. Once the
new equilibrium is reached, the river will have a constant slope (vanishing
concavity). This process is outlined in the next slide (Slide 33), in which all the
input parameters are the same as in Slide 29 except Ntoprint, which is varied so
that the duration of calculation ranges from 1 year (far from final equilibrium) to
250 years (final equilibrium essentially reached).
Slide 34 shows a case where the profile degrades to a new mobile-bed
equilibrium. During the transient process of degradation the long profile of the bed
is downward concave, or upward convex. This is because the erosion which
drives degradation causes the load, and thus the slope to increase in the
downstream direction. The input conditions for Slide 34 are the same as those of
Slide 29, except that the sediment feed rate Gtf is dropped to 70,000 tons per year.
This value is well below the ambient value of 305,000 tons per year (see Slide 29),
forcing degradation and transient downward concavity. In addition, Ntoprint is
varied so that the duration of calculation varies from 1 year to 250 years.
Factors such as subsidence or base level rise can drive equilibrium long profiles
which are upward concave.
33
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
AGGRADATION TO A NEW MOBILE-BED EQUILIBRIUM
Bed evolution
Bed evolution
160
160
0 yr
0.2 yr
0.4 yr
0.6 yr
0.8 yr
1 yr
Ultimate
Elevation in m
120
100
80
0 yr
2 yr
4 yr
6 yr
8 yr
10 yr
Ultimate
140
120
Elevation in m
140
60
40
100
80
60
40
20
20
0
0
0
2000
4000
6000
8000
10000
0
2000
Distance in m
6000
8000
10000
Distance in m
Bed evolution
Bed evolution
160
160
100
80
120
Elevation in m
120
0 yr
50 yr
100 yr
150 yr
200 yr
250 yr
Ultimate
140
0 yr
5 yr
10 yr
15 yr
20 yr
25 yr
Ultimate
140
Elevation in m
4000
60
100
80
60
40
40
20
20
0
0
0
2000
4000
6000
Distance in m
8000
10000
0
2000
4000
6000
Distance in m
8000
10000
34
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
DEGRADATION TO A NEW MOBILE-BED EQUILIBRIUM
Bed evolution
Bed evolution
90
90
80
60
50
40
0 yr
2 yr
4 yr
6 yr
8 yr
10 yr
Ultimate
70
Elevation in m
70
Elevation in m
80
0 yr
0.2 yr
0.4 yr
0.6 yr
0.8 yr
1 yr
Ultimate
30
60
50
40
30
20
20
10
10
0
0
0
2000
4000
6000
8000
10000
0
2000
Distance in m
6000
8000
10000
Distance in m
Bed evolution
Bed evolution
90
90
80
80
0 yr
20 yr
40 yr
60 yr
80 yr
100 yr
Ultimate
60
50
40
0 yr
50 yr
100 yr
150 yr
200 yr
250 yr
Ultimate
70
Elevation in m
70
Elevation in m
4000
30
60
50
40
30
20
20
10
10
0
0
0
2000
4000
6000
Distance in m
8000
10000
0
2000
4000
6000
Distance in m
8000
10000
35
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
ADJUSTING THE NUMBER M OF SPATIAL INTERVALS
AND THE TIME STEP t
The calculation becomes unstable, and the program crashes if the time step t is
too long. The above example resulted in a crash when t was increased from the
value of 0.01 years in Slide 29 to 0.05 years. The larger the value M of spatial
intervals is, the smaller is the maximum value of t to avoid numerical
36
instability. Acceptable values of M and t can be found by trial and error.
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
AN EXTENSION:
RESPONSE OF AN ALLUVIAL RIVER TO VERTICAL FAULTING DUE TO AN
EARTHQUAKE
The code in RTe-bookAgDegNormal.xls represents a plain vanilla version of a
formulation that is easily extended to a variety of other cases. The spreadsheet
RTe-bookAgDegNormalFault.xls contains an extension of the formulation for
sudden vertical faulting of the bed. The bed downstream of the point x = rfL (0 < rf
< 1) is suddenly faulted downward by an amount f at time tf. The eventual
smearing out of the long profile is then computed.

37
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
RESULTS OF SAMPLE CALCULATION WITH FAULTING
Bed evolution
12
10
Elevation in m
8
0 yr
0.05 yr
0.1 yr
0.15 yr
0.2 yr
0.25 yr
6
4
2
0
-2
-4
-6
0
2000
4000
6000
Distance in m
8000
10000
38
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
RESULTS OF SAMPLE CALCULATION WITH FAULTING contd.
In time the fault is erased by degradation upstream and aggradation downstream,
and a new mobile-bed equilibrium is reached.
Bed evolution
12
12
10
10
8
8
0 yr
0.001 yr
0.002 yr
0.003 yr
0.004 yr
0.005 yr
6
4
2
0
Elevation in m
Elevation in m
Bed evolution
0 yr
0.025 yr
0.05 yr
0.075 yr
0.1 yr
0.125 yr
6
4
2
0
-2
-2
-4
-4
-6
-6
0
2000
4000
6000
8000
0
10000
2000
6000
8000
10000
Distance in m
Distance in m
Bed evolution
Bed evolution
12
12
10
10
8
8
0 yr
0.5 yr
1 yr
1.5 yr
2 yr
2.5 yr
6
4
2
0
Elevation in m
Elevation in m
4000
4
2
0
-2
-2
-4
-4
-6
0 yr
5 yr
10 yr
15 yr
20 yr
25 yr
6
39
-6
0
2000
4000
6000
Distance in m
8000
10000
0
2000
4000
6000
Distance in m
8000
10000
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
REFERENCES
Exner, F. M., 1920, Zur Physik der Dunen, Sitzber. Akad. Wiss Wien, Part IIa, Bd. 129 (in
German).
Exner, F. M., 1925, Uber die Wechselwirkung zwischen Wasser und Geschiebe in Flussen,
Sitzber. Akad. Wiss Wien, Part IIa, Bd. 134 (in German).
Lawrence, P., 2003, Bank Erosion and Sediment Transport in a Microscale Straight River, Ph.D.
thesis, University of Paris 7 – Denis Diderot, 167 p.
Meyer-Peter, E. and Müller, R., 1948, Formulas for Bed-Load Transport, Proceedings, 2nd
Congress, International Association of Hydraulic Research, Stockholm: 39-64.
Paola, C., Heller, P. L. & Angevine, C. L., 1992, The large-scale dynamics of grain-size variation
in alluvial basins. I: Theory, Basin Research, 4, 73-90.
Wong, M., 2003, Does the bedload equation of Meyer-Peter and Müller fit its own data?,
Proceedings, 30th Congress, International Association of Hydraulic Research, Thessaloniki,
J.F.K. Competition Volume: 73-80.
For more information see Gary Parker’s e-book:
1D Morphodynamics of Rivers and Turbidity Currents
http://cee.uiuc.edu/people/parkerg/morphodynamics_e-book.htm
40
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
1D CONSERVATION OF BED SEDIMENT FOR SIZE MIXTURES, BEDLOAD ONLY
fi'(z', x, t) = fractions at elevation z' in ith grain size range above datum in bed [1].
Note that over all N grain size ranges:
N
 f  1
i1
i
qbi(x, t) = volume bedload transport rate of sediment in the ith grain size range [L2/T]

 

s (1   p )fidzx  1  s qbi x  qbi

0
t
x  x
 1
qbi
qbi
x
Or thus:
1

qbi
 
(1   p )  fidz  
t 0
x
z'
41
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
ACTIVE LAYER CONCEPT
qbi
qbi
La

x
z'
The active, exchange or surface layer approximation (Hirano, 1972):
Sediment grains in active layer extending from  - La < z’ <  have a constant,
finite probability per unit time of being entrained into bedload.
Sediment grains below the active layer have zero probability of entrainment. 42
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
REDUCTION OF SEDIMENT CONSERVATION RELATION USING THE ACTIVE
LAYER CONCEPT
Fractions Fi in the active layer have no vertical structure.
Fractions fi in the substrate do not vary in time.
Fi ( x, t ) ,   La  z  
fi( x, z, t )  
 fi ( x, z) , z    La
Thus
 
 La
 


fidz  
fidz   fidz  fIi (  L a )  FiL a 

t 0
t 0
t La
t
t
where the interfacial exchange fractions fIi defined as
fIi  fi L
a
describe how sediment is exchanged between the active, or
surface layer and the substrate as the bed aggrades or
degrades.
43
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
REDUCTION OF SEDIMENT CONSERVATION RELATION USING THE ACTIVE
LAYER CONCEPT contd.
Between
q
 
(1   p )  fidz   bi
t 0
x
and
 
 La
 








fidz  
fidz   fidz  fIi (  L a )  FiL a 

t 0
t 0
t La
t
t
it is found that
qbi

 

(1  p )fIi (  La )  FiLa   
t
x
 t

(Parker, 1991).
44
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
REDUCTION contd.
The total bedload transport rate summed over all grain sizes qbT and the
fraction pbi of bedload in the ith grain size range can be defined as
N
qbT   qbi , pbi 
i1
qbi
qbT
The conservation relation can thus also be written as

q p
 

(1  p )fIi (  La )  FiLa    bT bi
t
x
 t

Summing over all grain sizes, the following equation describing the evolution
of bed elevation is obtained:
qbT

(1   p )

t
x
Between the above two relations, the following equation describing the
evolution of the grain size distribution of the active layer is obtained:
L 
q p
q
 F
(1  p )La i  Fi  fIi  a    bT bi  fIi bT
t 
x
x
 t
45
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
EXCHANGE FRACTIONS


fi zL ,
0

a
t
fIi  

Fi  (1  )pbi ,
0
t

where 0    1 (Hoey and Ferguson, 1994; Toro-Escobar et al., 1996). In the
above relations Fi, pbi and fi denote fractions in the surface layer, bedload and
substrate, respectively.
That is:
The substrate is mined as the bed degrades.
A mixture of surface and bedload material is transferred to the substrate as the
bed aggrades, making stratigraphy.
Stratigraphy (vertical variation of the grain size distribution of the substrate)
needs to be stored in memory as bed aggrades in order to compute
46
subsequent degradation.
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
WHY THE CONCERN WITH SEDIMENT MIXTURES?
Rivers often sort their sediment.
An example is downstream fining:
many rivers show a tendency for
sediment to become finer in the
downstream direction.
bed slope
elevation
median bed
material grain size
Long profiles showing
downstream fining and
gravel-sand transition in
the Kinu River, Japan
(Yatsu, 1955)
47
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
WHY THE CONCERN WITH SEDIMENT MIXTURES ? contd.
Downstream fining can also be
studied in the laboratory by forcing
aggradation of heterogeneous
sediment in a flume.
upstream
Downstream fining of a gravel-sand
mixture at St. Anthony Falls
Laboratory, University of Minnesota
(Toro-Escobar et al., 2000)
Many other examples of sediment
sorting also motivate the study of
the transport, erosion and
deposition of sediment mixtures.
downstream
48
National Center for Earth-surface Dynamics
Short Course
Morphology, Morphodynamics and Ecology of Mountain Rivers
December 11-12, 2005
REFERENCES FOR CHAPTER 4
Hirano, M., 1971, On riverbed variation with armoring, Proceedings, Japan Society of Civil
Engineering, 195: 55-65 (in Japanese).
Hoey, T. B., and R. I. Ferguson, 1994, Numerical simulation of downstream fining by selective
transport in gravel bed rivers: Model development and illustration, Water Resources
Research, 30, 2251-2260.
Paola, C., P. L. Heller and C. L. Angevine, 1992, The large-scale dynamics of grain-size variation
in alluvial basins. I: Theory, Basin Research, 4, 73-90.
Parker, G., 1991, Selective sorting and abrasion of river gravel. I: Theory, Journal of Hydraulic
Engineering, 117(2): 131-149.
Toro-Escobar, C. M., G. Parker and C. Paola, 1996, Transfer function for the deposition of poorly
sorted gravel in response to streambed aggradation, Journal of Hydraulic Research, 34(1):
35-53.
Toro-Escobar, C. M., C. Paola, G. Parker, P. R. Wilcock, and J. B. Southard, 2000, Experiments
on downstream fining of gravel. II: Wide and sandy runs, Journal of Hydraulic Engineering,
126(3): 198-208.
Yatsu, E., 1955, On the longitudinal profile of the graded river, Transactions, American
Geophysical Union, 36: 655-663.
49