sms-618, particle dynamics, fall 2009misclab.umeoce.maine.edu/boss/classes/sms_618/sediment... ·...
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SMS-618, Particle Dynamics, Fall 2009
Modeling of suspended sediment transport
From: http://www.usask.ca/geology/classes/geol243/243notes/243week3b.html
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What is sediment transport?
Why does sediment transport take place?
When does sediment transport take place?
Where does sediment transport take place?
Where is the sediment coming from?
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Types of sediment transported:
Total sediment load
Wash load Bed material load
Mo ing as s spended load Mo ing as bed loadMoving as suspended load Moving as bed load
Today’s topic
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What information do we need to know to model sediment transport?
Flow field (‘physics’) Particle field (‘sedimentology’)
Bed and wash material characteristics (e.g. density, size distribution, shape)
Properties of flow away from bottom boundary (wave, mean current), and of the water (e.g. ν).
Within the BBL the two are coupled:
•Stress on bottom due to flow imparts the force that resuspends particles.
Flow is affected by added water density due to suspension of particles•Flow is affected by added water density due to suspension of particles.
•Flow is affected by settling particles.
•Flow is affected by bottom morphology (e.g. ripples).
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What information do we need to know to model sediment transport?
Flow field (‘physics’) Particle field (‘sedimentology’)
Bed and wash material characteristics (e.g. density, size distribution, shape)
Properties of flow away from bottom boundary (wave, mean current), and of the water (e.g. ν).
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The concept of a boundary layer:
Southard, 2000
As flow encounter a wall the velocity right next to the wall has to vanish (no slip).
Away from the wall the velocity is the free flow velocity.
In between we get a ‘boundary layer’.
Laminar boundary layer:
Movie
0zw
xu
=∂∂
+∂∂ Scaling:
UxU
LUU νδ
δν =→2~
2
2
zu
zuw
xuu
∂∂
=∂∂
+∂∂ ν
Non-linear Blasius equ. Can be solved numerically.
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A more ‘realistic’ view: Southard, 2000
A hierarchy of BBLs:
Southard, 2000
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Example: boundary layer in a pipe:
Comparison of laminar (i) and turbulent (ii) velocity profiles in a pipe for:
(a) The same mean velocity
(b) the same driving force (pressure (b) e sa e d g o ce (p essu edifference).
Figure 22.16 from Tritton, D.J. 1977. Physical Fluid Dynamics. Van Nostrand Reinhold, NY. p. 277.
BBL is smaller and more dissipative in the turbulent casein the turbulent case
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Turbulent BBL structure:
The stress in the BBL varies from being dominated by the Reynolds stress away from thewall to being dominated by viscous stress right next the bed.
Mann and Lazier, 1996
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Example: horizontal flow field in a bottom boundary layer
Geostrophy/ buoyancy/ tidallyDriven (frequency ω)Driven (frequency ω)
Transition layer,du/dz~u*/z(~20% of BBL)
Laminar flow, Re<500
BBL).
Constant viscous
0 41 K ’ t t
‘smooth bottom’stress layer, u~z, (~1% of BBL)
Jumars, 1993
Bottom effect parameterized through z0 andu*=(τ0/ρ)1/2. τ0=νdu/dz+ρ<u’w’>
Two parameter fit to velocity profile.
κ~0.41, von Karman’s constant.
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Example: horizontal flow field in a bottom boundary layer
uSouthard, 2000
zu
zu
dzud
κ**
=∝
Ln zu =
u*κ ln
zz0
+ u’τ0
Ln(z0)u*κ
Slope ~ u*/κIntercept l /
Equivalent to assuming: Keddy=κu*z
Intercept ~ u* lnz0 /κZo-roughness length.
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Example: horizontal flow field in a bottom boundary layer
Predicting z0 from D or u*. Knowing z0, BBL depth and u∞ u*.
D-bottom grain sizeJumars & Nowell. 1984. Am. Zool.24: 45-55
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Example: horizontal flow field in a bottom boundary layer
http://cvu.strath.ac.uk/courseware/calf/CALF/bl/equations/eq5a.html
Turbulent boundary layer is more dissipative; Applies more resistance to the flow.Sets up faster.
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Example: horizontal flow field in a bottom boundary layer
Data for sand tracked by an Data for sand tracked by an epifaunalepifaunal bivalve:bivalve: Burst-Sweep cycle:
Nowell, A.R.M., P.A. Jumarsand J.E. Eckman. 1981. Effectsof biological activity on theentrainment of marinesediments. Mar. Geol.42: 155-172.
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Gravity waves:
Eff tEffects: Changes the mean flow field.Change bottom shear stress.
Wave boundary layer is very shallow, δ~(4πνT)1/2, for a 4sec wave, δ~0.7cm. Orientation relative to mean current is important:
4*
2*
2*
4**
2 cos2 wcwwcccw uuuuu ++= φ
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Finally, we get to particles…
(193 )Rouse (1937) approach:
Conservation of particle mass (sources and sinks comes as BCs):
( ) ( ) ( ) ( ) CzCw
yCv
xCu
tCCu
tC sss
s2∇Κ=
∂∂
+∂
∂+
∂∂
+∂∂
=⋅∇+∂∂ v
zyxtt ∂∂∂∂∂
Assume no gradient in x and y, and divide into time-mean and fluctuations:
'; 's s sC C C w w w= + = +
Equation for mean becomes:
( ) ( )' 's sw C w Cw C ∂ +∂ ( ) ( )0
s ssw Cz z
∂= =
∂ ∂
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Rouse’s (1937) approach:
Convert Reynolds’ stress flux into (eddy-)diffusive flux:
' 'CK w C∂= −
Convert Reynolds stress flux into (eddy-)diffusive flux:
s sK w Cz=
∂
Combining we get:
0s sCw C K
z z⎡ ⎤∂ ∂
− =⎢ ⎥∂ ∂⎣ ⎦z z∂ ∂⎣ ⎦
Issues:
ws is a function of sediment size, excess weight, and shape.Ks is not necessarily the same as that of the fluid.Boundary conditionsBoundary conditions.
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Rouse’s (1937) approach; 1D balance:assume no net flux from top and bottom boundary (reduces to 1st order ODE).
Solution (up to a constant of integration, C(z1)):Near the bottom:
:3.03 , ,* ≥≥== αακ KKzuK S
( ) ( ) α/Rz zzCzwdzwzC−⎞⎛
Defining we get:*uwR s κ=
( )( )
( )( )ακακ 111**1
lnln1
s
z
s
zz
zCzC
zz
uw
zdz
uw
zCzC
⎟⎟⎠
⎞⎜⎜⎝
⎛=⇒−=−= ∫
This profile fits well lower 30% of BBL.
Higher up in the water column (post Rouse):
HuconstK ακ== BBLs HuconstK *. ακ==
( )( )
( )( ) ( ) ( )
⎭⎬⎫
⎩⎨⎧ −−=→
−−=−= ∫
sz
s
HzzRzCzC
H
zzwdz
H
w
CzC 1
11
expln ( ) ( ) ( )⎭⎬
⎩⎨∫
BBLBBLzBBL HHuHuzC αακακ 1**1
p1
This profile fits well upper 80% of BBL.
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Comparison with laboratory observations (See Allen, 2001)
( )( )
( )( )
α
ακακ
/
111**1
lnln1
Rs
z
z
s
zz
zCzC
zz
uw
zdz
uw
zCzC
−
⎟⎟⎠
⎞⎜⎜⎝
⎛=⇒−=−= ∫
( )( )
( )( ) ( ) ( )
⎭⎬⎫
⎩⎨⎧ −−=→
−−=−= ∫
BBLBBL
sz
zBBL
s
HzzRzCzC
Hu
zzwdz
Hu
w
zCzC
αακακ1
1*
1
*1
expln1
The two solutions are matched at z~HBBL/5
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Problem with the Rouse equations near the bottom when the sediment concentration is large.
Taylor and Dyer (1977) approach; Add effects of sediment concentration on density. Let’s the eddy coefficient vary relative to that of the unstratified fluid.
K
Lz
KK strats
βγ +=,
3
Where the Monin-Obukov-length, L, is defined as (based on shear stress and buoyancy flux being the two fundamental processes):
''
3*
wguLρκρ
=
β and γ are constant (e.g. 4.7-5.2 and 0.74 respectively, Styles and Glenn, 2000) and z/L is termed the stability parameter.
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Taylor and Dyer’s (1977) approach; Add effects of sediment concentration on density. Let’s the eddy coefficient vary relative to that of the unstratified fluid.
( )−=∑ n
sn C0 '' ρρρ ( )∑ −=⇒ sn Cww '''' 0ρρρ
n-size bin.
( )⎥⎦
⎤⎢⎣
⎡ −+= ∑
∑
nn
sn
nn
C0
00
0
1ρρρρρ
ρρ ∑⇒
nnCww
0ρρ
Since:⎦⎣ n 0ρ
3*uL ρ
=''wg
Lρκ
Assuming all sediment classes have the same density:
( ) ''30
nsns Cwgz
Lz ρρκ −=
Assuming all sediment classes have the same density:
03*uL ρρ
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Taylor and Dyer’s (1977) approach; Add effects of sediment concentration on density. Let’s the eddy coefficient vary relative to that of the unstratified fluid.
Denoting by (with β=5.2 and z/L from above) and Rouse numberand for small roughness length scale z0, close to the bed, where
LzA β=*uwR snn κ=
⎤⎡ ⎫⎧ ⎤⎡
g g 0, ,K=κu*z, the analytical solution for the flow and particle concentration is:
snn
( )( ) ⎥
⎥
⎦
⎤
⎢⎢
⎣
⎡
⎪⎭
⎪⎬⎫
⎪⎩
⎪⎨⎧
⎥⎥⎦
⎤
⎢⎢⎣
⎡−⎟⎟
⎠
⎞⎜⎜⎝
⎛−
++−=⎟⎟⎠
⎞⎜⎜⎝
⎛−
11
1ln1lnln1
000
nR
n
n
nn z
zR
ARRz
zRC
zC
( ) ( ) ⎟⎟⎟
⎠
⎞
⎜⎜⎜
⎝
⎛
⎪⎭
⎪⎬⎫
⎪⎩
⎪⎨⎧
⎥⎥⎦
⎤
⎢⎢⎣
⎡−⎟⎟
⎠
⎞⎜⎜⎝
⎛−
++=−
11
1ln1ln1
00
*nR
n
n
n zz
RAR
Rzzuzu
κ
Note that both flow and concentration field is affected and that for an unsorted sediment there is a need to find a way to characterize the effect of all size classes on velocity (through R ) e g :on velocity (through Rn), e.g.:
∑∑=n
nn
snns CwCw~
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Boundary conditions (needed when there is no continuous field data)
0s sCw C K
⎡ ⎤∂ ∂− =⎢ ⎥
To solve the particle concentration equations we need to BCs.
s sz z⎢ ⎥∂ ∂⎣ ⎦
The top BC is less important (in the limit of infinite ocean, C 0 there. For shallow
BC at (near) the bottom (τcn-critical shear stress):
e op C s ess po a ( e o e ocea , C 0 e e o s a owaters specify no flux. Can incorporate flux from a productive ML if needed.
⎧ SConcentration BC (Sn=(τd- τcn)/τcn ): ( ) ( )
otherwise0
01
,,0
0 >
⎪⎩
⎪⎨⎧
+=−
+ nn
nn
n
SS
StCtC γ
γδδ
A problem with this approach is that γ0 varies by 3 orders of magnitudes across studies and by 2 orders of magnitude within a single study over a short time.
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Boundary conditions
Flux BC:
( ) ( )tJtJC
KCw diin ,0,0 −− +=
∂−− ( ) ( )tJtJ
ZKCw diei
zsnsn ,0,0
0=
+∂ +
( ) ( ) ( )tCwptJSSC
tJ nsnndinne
ei ,0,0,0
,0 +−− −=⎨⎧ >
=( ) ( ) ( )tCwptJotherwise
tJ nsnndiei ,0,0,0
,0⎩⎨
with Ce an empirically determined erosion rate coefficient and pn the probability that a falling particle makes contact with the bed and remains there. Two models for pn are used: pn=1 for all shear stresses, in which case erosion balances diffusion in the BC. The second model assumes:
⎩⎨⎧ >−
=otherwise
p dndnn
ττττ 00
01
⎩The depositional shear stress of class n, τdn, defines the stress below which sediment is able to remain on the bed after contacting it.
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Boundary conditionsBecause the eddy coefficient goes to zero at the boundary, there is no mechanism to raise the sediments into the water column, which, for the flux BC, provides physical solutions only when pn=1and Jdi=0.
This problem is addressed in some models by adding a well-mixed near-bed layerThis problem is addressed in some models by adding a well mixed near bed layer of thickness δa where the eddy coefficient increases (convenient mathematically but not observed, could be justified by a wave BBL).
A th h i t i t i j ti f di t f th b d t iAnother approach is to incorporate injection of sediments from the bed at various heights above the bottom (which are not resolved in the 1-D case and are the result of averaging in x and y). In this case the conservation equation is
CC ⎞⎛ ∂∂∂n
nsn
nsn D
zCK
zzCw +⎟
⎠⎞
⎜⎝⎛
∂∂
∂∂
=∂∂
With for example:
⎟⎟⎠
⎞⎜⎜⎝
⎛−= snn
zADδ
exp
With, for example:
⎠⎝ eδThe BC condition in this case is that erosion equals deposition at the bottom.
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Summary:
•Momentum and material flux are not mutually independent.
1 D t d t t ti d ib d t l b d•1-D steady state equation describe adequately observed data when local data is used in parameter fit.
•Current approaches almost always ignore aggregation dynamics.
•High resolution data (velocity & size fractionated particles) is lacking.
•Current approaches vary from a mix empirical fits to physical approaches tuned with empirical data.
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In case you wondered about who cares, and whether there is money to be made:S i l l (b d i l l h)Some commercial players (based on a simple google search):
Some government agencies in the US funding sediment transport modeling:
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References
Allen, J. R. L., 2001. Physical Sedimentology, Blackburn Press, 272pp.
Boggs, Sam, 2001. Principles of sedimentology and stratigraphy. 3rd edition, Prentice Hall 726ppPrentice Hall, 726pp.
Dyer, K. R., 1986, Coastal and Estuarine Sediment Dynamics. John Wiley & Sons, 342pp.
Hill, P. S., I. N. McCave, 2001, Suspended particle transport in benthic boundary layers. Ch. 4 of The Benthic Boundary Layer edited by B. P. Boudreau and B B Jorgensen Oxford University PressBoudreau and B. B. Jorgensen, Oxford University Press.
Middleton, G. V. and J. B. Southard, 1984, Mechanics of Sediment Movement, SEPM short course, 2nd edition, Providence.
Taylor, P. A., and K. R. Dyer, 1977. Theoretical models of flow near the bed and their implications for sediment transport. Ch. 13. of The Sea, Volume 6, Marine modeling, Edited by E. D. Goldberg, I. N. McCave, J. J. O’Brien, and J.Marine modeling, Edited by E. D. Goldberg, I. N. McCave, J. J. O Brien, and J. H. Steele, John Wiley & Sons.