hydraulics and the environment · 5/26/2010 · summary dynamic interaction of multiple jets...
TRANSCRIPT
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Faculty of EngineeringThe University of Hong Kong May 26, 2010
Hydraulics and the Environment
By
Joseph Hun-wei LeeDepartment of Civil Engineering
The University of Hong Kong
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1. Introduction
2. Mixing of multiple buoyant jets - Coalescing plumes - Rosette buoyant jet group- Turbulent buoyant jet group in crossflow
3. Hydraulic jet for urban flood control - River junction design for flood diversion
4. Urban water environment engineering and theme-based research • Water shortage – desalination• Climate change –urban flood control – high
speed air-water flows• Coastal sedimentation and Shenzhen
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Air pollution
Hong Kong
Tall buildings
Coastal pollution
Clear sky
Population density ranks 4th in the world
Red tide
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Heat Island effect
Urban Flooding
Ocean outfall discharge(Rosette jet group in a current)
Industrial emission
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排放口
射流
Victoria Harbour
Submarine outfall in ScotlandWastewater disposal in a city
1.85 million m3 / day wastewater discharged into Victoria Harbour1.85 million m1.85 million m33 / day / day wastewater wastewater discharged into discharged into Victoria Victoria HHarbourarbour
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(grid size 30.5 cm, nozzle spacing 19.5 cm, water depth 6.1 cm)
Merging of three-dimensional jets (Water Resources Research, Lee and Jirka 1980)
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6 jet discharge (Lai et al 2009)
Alternating diffuser (Liseth 1976)
L
D
Qo, Bo,Mo
zm
Empirical formula for merging height FrLzm ~
Dynamic interaction in multiple buoyant jetsJet-induced velocity/pressure field leads to a change in jet
trajectory and dilution
gDuFr i
)/( ρρΔ=
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Modelling of buoyant jets in complex environment
• Ocean outfall design• Mixing zone analysis• Impact assessment• Post-operation
monitoring
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Critical factors
affecting jet
dilution
Port diameter
Discharge angle
Outfalldesign Port depth
•• •• ••
Number of ports Research challenges
Real time dynamic near-far field coupling
Multiple length scales from near field to far field (0.1 m to 1 km)
•• •• ••
StratificationAmbient
environment Ambient velocity
•• •• ••
Free surface
Tidal circulation
Stochastic environmental risk assessment for entire range of conditions
Complex merging and dilution of multiple buoyant jets in coflow, crossflow and counterflowFlow rateSource
properties Discharge velocity
•• •• ••
Density
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Turbulent jet in a crossflow Section B - B
•Bent-over phase•Vortex pair•Vortex entrainment
•Gaussian•Shear entrainment
Section A - AUo
B
B
Turbulent entrainment
A A
Ua
Q increases Dilution
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Dynamic jet interaction in near field
External flow field of a round jet
Exact Solution of N-S Equations (Squire 1951; Batchelor 1967)
⎟⎟⎠
⎞⎜⎜⎝
⎛−
∂∂
−−∇+∂∂
−=−∂∂
+∂∂
2cot2221
222
2
r
vv
rr
uurp
rvu
rv
ruu θ
θε
ρθ
⎟⎟⎠
⎞⎜⎜⎝
⎛−
∂∂
+∇+∂∂
−=−∂∂
+∂∂
θθε
θρθ 2222
sin
21
r
vv
rup
rruvv
rv
rvu
Boundary layer approximation
(Jet flow)
)''(1 vurrrr
uvxuu ρ
ρ ∂∂
−=∂∂
+∂∂
Potential flow
(Taylor 1958)
(External flow)
Squire (1951)θθνθψ
cos1)cos1(2),(
2
−+−
=c
rr
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Taylor’s analytical solution Distributed point sinks Step size = 10D
Relative error in the order of 0.2 %
)cos1( θψ += r
The external irrotational flow induced by a jet can be modelled as a line sink (Taylor 1958)
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External flow field of multiple jets• Comparison of model and FLUENT solutions
Hypothetical boundaries (for visualization purpose only)
zero pressure boundary
FLUENT Model
• Jet action simulated by point sink distribution of known strength
• Point velocity = sum of velocities induced by each jet
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Velocity comparison for twin jets
• Velocities predicted by the semi-analytical model is in good agreement with the CFD simulation by FLUENT
Velocities at center plane at z = 10D
y
z
z - velocity y - velocity
jet
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Computation of multiple jet interaction
Governing equations for buoyant jet (Ua=0)
Integral jet model for single jet in stagnant fluid - (Q,M,F, x,y,z) (s): jet volume, momentum, buoyancy flux, trajectory
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Discharge parameters:• D = 5 mm s/D = 5 – 15
Test 1: Experiments on coalescing round plumes (Kaye and Linden 2004)
Equal deflection
Predicted trajectory of two equal plumes
(s/D = 15)
Control volume
1st iteration
Final iteration
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Experiments on coalescing round plumes
Predicted trajectory of two unequal plumes
s/D = 10 (buoyancy flux ratio 0.1)
Stronger plume, less deflected
Predicted plume merging height
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External velocity field obtained by superposition of entrainment field of all the jets; pressure field through the Bernoulli’s equation Pressure is incorporated using a control volume approach and an exact momentum balance; jet trajectory obtained by iteration 2
21 qP −=
control volume
Test 2: Rosette buoyant jet group in stagnant water (Roberts et al 1989; Kwon and Seo 2005; Lai and Lee 2008)
NJ1
NJ2
NJ3NJ4
NJ5
NJ6
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Iterative solution of jet trajectory• 1st iteration: single jet
discharge; final iteration (red line): multiple jet discharge
• Interaction increases as number of jets (N) increases for same Fr
Fr = 2
NJ = 2
Rosette Buoyant Jet Group
NJ = 6
Fr = 4
Fr = 2 Fr = 4
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With interaction No interactionCross-section at z = 20D
Induced velocities
Induced pressure
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Summary
Dynamic interaction of multiple jets caused by the jet entrainment field occur in the near field Model predictions are in good agreement with observations:• Coalescing round plumes • Burner-type clustered jet group • Rosette buoyant jet group • Alternating diffuser jets • Tandem jets in crossflow (sink-doublet model)
Experiments and theory suggest negligible jet interaction for K = Uj/Ua ≈ 15
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Merging of a rosette jet group in a crossflow
In the bent-over jet
aUu ≈
Overlapping plumes Reduction in jet cross-sectional area
and entrainment
(The composite dilution concept)
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Mixing of a buoyant jet in Mixing of a buoyant jet in crossflowcrossflow
•Gaussian•Shear entrainmentSection A-A
•Jet bifurcation •Vortex entrainmentSection B-B
Advected jet/plume Advected puff
B
B
Turbulent entrainment
A A
Q increases Dilution
Ua
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Mixing of a plume in Mixing of a plume in crossflowcrossflow
cross section(experiment)
Advected line thermal
cross section(computed)
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JETLAG: Lagrangian jet model
Bent-over phaseAdvected line puff/thermal
Advected jet/plume
E(vortex) = Ua x projected upwind surface area
tUhb kks ΔΔπα2E(shear) =
)2)(/sin554.0057.0(2 2k
klks VU
VF+Δ
+= φα
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Vortex entrainment using projected area hypothesis Evortex = Ua x projected surface area
2D/3D turbulence model calculations show that the external flow of advected line puffs and thermals are like line doublets that entrain all of the oncoming flow
Particletracks
doublet
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JETLAG JETLAG –– general entrainment hypothesis for general entrainment hypothesis for nearnear--far field transition far field transition
Shear entrainment Vortex entrainment
Total entrainment
Three dimensional buoyant jet trajectory
Separation angle φk for determining contribution from shear and vortex entrainment
tUhbE kkss ΔΔ= πα2
)2
)(sin
554.0057.0(2 2k
k
l
ks VU
VF +Δ
+=φ
α
tb
bb
hbUE
kkk
kkkk
kkkkaaf
ΔΔ
+Δ
+−=
)]cos(cos2
coscos
coscos12[
2
22
θφπ
θφπ
φθρ
kfk
s EEM ϕπϕπ
sin)( +−
=Δ
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Prediction of initialmixing of pollutantdischarge in a tidal current
JETLAG/VISJETModel prediction of initial mixing is supported by extensive field data of initial dilution at sea outfalls in the UK, USA and other countries
DimensionlessDilution (S)
Dimensionless depth
Field Data
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Composite Dilution
Mass flux of rosette buoyant jet group
After bent-over by crossflow
Negligible dynamic interaction
Composite dilution
∑=
=n
iiiimmm uCAuCA
1
aUu ≈
m
ii
am
aiim A
CAUA
UCAC ∑∑ ==
oim AAA −= ∑
mo CCS /=
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Merging of multiple
jets
Multiple jet merging and interaction Multiple jet merging and interaction -- composite dilution of jet groupcomposite dilution of jet group
o60=θSingle jetUa
)120,60( oo=θMultiple jet
x = 20D x = 40D
Mixing of rosette jet groups in stratified tidal current
For typical jet to riser diameter ratios of D/Dr ~ 0.1, dynamic jet interaction is insignificant
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Composite Dilution (initial dilution)Dilution of multiple jets can be obtained by superposition of measured or predicted concentration from individual jets Overestimation of dilution without consideration of overlapping area
Without merging effect
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Comparison of measured and VISJET predicted cross-sectional averaged dilutions (Composite Dilution)
Composite dilution of a jet group can be defined by VISJET by computing the extent of jet merging
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Optimal mixing: number of jet nozzles
For same total discharge Q, jet and ambient velocity Uj, Ua, optimal dilution is given by 6 jets per riserDue to plume overlap (kinematic interaction), dilution for N=12 is less than N=6
No. of Jet Surface dilution2 1034 1146 1658 15112 128
x/D
Dilution S
K=17, Fr=13-22
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Hong Kong Hong Kong HarbourHarbour Area Treatment Area Treatment Scheme (HATS) Scheme (HATS)
VISJET is adopted for the design and environmental impact assessment of HATS (1990-2006)
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VISJET VISJET –– interactive virtual reality system for interactive virtual reality system for modellingmodelling of multiple buoyant jet groupsof multiple buoyant jet groups
Prediction of multiple jet merging and interaction
Boston ocean outfall diffuser
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Mixing in the intermediate field can be modeled by coupling a plume model with a 3D circulation model -Distributed Entrainment Sink Approach (DESA)
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Example of 3D Virtual Reality EIA system
Probabilistic ecological risk assessment
WATERMAN – Environmental Impact Assessment and Public Engagement
Impact of Harbour Area Treatment Scheme (HATS) on beach water quality
Monte-carlo simulation for ecological assessment Choi et al, Environmental Science and Technology (2009)
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Registered VISJETin different continents
Asia 42Australia 24Europe 25South America 8North America 30
Worldwide application of Worldwide application of VISJETVISJET
HK
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Yuen Long Bypass Floodway
San HuiNullahSham
Chung Channel
Yuen Long Main Nullah
Yuen Long Bypass Floodway
Kam Tin River
Hydraulic jet theory for urban flood control
Objective: to remove all floodingfrom Yuen Long town (population 341,000) for 1 in 200 year event
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Main Nullah
San HuiNullah
YLBPYLBP
Limited land availability Complex super-/sub-critical flow junctions/transitions
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Yuen Long Bypass Floodway (YLBF) Model
Complicated junction flow; tight land availability
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Complex junction flows create significant backwater upstream, rendering bypass floodway useless!
Example: Yuen Long Bypass Floodway, Hong Kong Jet theory for river junction design
F > 1
F < 1
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Q=90 m3/s
San Hui/Bypass Floodway Junction
Solution: use jet principle to create locally critical flow conditions at San Hui – Bypass Floodway junction
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Proposed design enhances the flood control capacity of Yuen Long from that of a 1 in 10-year to that of a 1 in 200-year flood
Jet theory for flood control - hydraulic structure to create local jet and critical flow
“Hydraulic jet control for river junction design of Yuen Long Bypass Floodway”Arega, Lee and Tang, ASCE Journal of Hydraulic Engineering, 2008
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Fig. 11a) Measured Stages Along Bypass Floodway
2
3
4
5
6
7
8
9
0 200 400 600 800 1000 1200
Chainage from Connection Point with Main Nullah
Stag
es (m
PD)
Bed
Case 4
Case 5
Case 3
Case 2
Sham Chung Junction
Box Culvert
San Hui Junction
Water depth variation along YLBF
Sham Chung channel
San Hui NullahStorm drain
Main Nullah
新墟明渠
San Hui Nullah
Yuen Long bypass
Design using jet principle
Proposed design enhances the flood control capacity of Yuen Long from that of a 1 in 10-year to that of 1 in 200-year flood
Usual design Upstream water level decreases significantly
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Yuen Long Bypass Floodway:
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YLB
F
SHN
YLBF-SHN
Computed contour of depths and velocities vector
Guide wall
Explicit second order high resolution shock-capturing finite volume method
Velocity
level
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Conclusion
Multiple jet interaction is significant in the near field. Dynamic interaction can be satisfactorily treated using a semi-analytical model Mixing of buoyant jet groups in a crossflow can be predicted by considering plume overlapping (kinematic interaction) Buoyant jet theory can be usefully applied for the design of sustainable urban infrastructure • wastewater disposal• drainage and flood control• building ventilation and indoor environment• impact assessment and public engagement
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Proposed Wind Farm
Hong Kong ZhuhaiMacao Bridge Hong Kong
SaiKungZhuhai
Macao
Pearl River Estuary Shenzhen
Dry seasonRiver flow
4000 cumec
Dry seasonRiver flow
4000 cumec
Pearl River ‐ 2200 km; total catchment area 453,700 sq.km.
Annual precipitation 1470 mm; wet season flow 20,000 m3/s
Theme-based Research: Urban Water Environment Engineering
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Environmental impact assessment of an Australiandesalination plant
Australia desalination plant
Hong Kong desalination plant
1) Challenge of Water shortage1) Challenge of Water shortage –– desalination desalination Environmental impact of brine discharges Environmental impact of brine discharges (dense jet) (dense jet)
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Interception of stream flood flow from hillside above the urban and business districtdivert storm flow into a deep tunnel via vertical drop shaftsTransfer the flow to the sea in a drainage tunnel through a portal structureIntake structure, vertical drop shaft, deep drainage tunnel and portal structure
Supercritical Vortex Intake for Storm Water Diversion in HK Island
港島暴雨分流超臨界漩渦進水口
2) Challenge of climate change and urban flood control - Hydraulics of high speed air-water flows
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Intake Structure – design conceptSpace contraints preclude Stilling basin and weir option
optimal engineering design convey the high speed turbulent water flow efficiently and stably into the deep tunnel
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Spiral Vortex Intakesto divert the high speed flow stably and smoothly into the intake system,
Warped Invert Flat Invert
Separation of air and water flow
Water flow
Air flow Air flow
Water flow
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Stability of Spiral Vortex Flow
Unstable Flow with Long Approach Channel
Stable Flow with Short Approach Channel
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1:25 Vortex Intake Model: Highly unstable flow!Normal flow conditions at inlet channel
Shock wave height hm = 270 mm
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Sustainable urban water supply and drainage systems - Hydraulics of two-phase air-water flows
- Rehabilitation of urban infrastructure- Energy conservation - Renewable energy
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Two-phase pipe flowHydraulic transient and geysers in the laboratory
Two-phase flow on high dams (Tai Lam Chung & Three Gorges)
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3) Challenge of coastal erosion and sedimentation
River sedimentation laboratory, Tsinghua University
Hong Kong HarbourHydraulics Laboratory
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To raise the flood standard from 1 in 2-5 years to 1 in 50 years Train (Straighten, widen and deepen) the river in three stagesTotal Investment: HK$ 1.7 billion
Shenzhen River Regulation
Shenzhen RiverShenzhen River
Flooding in 1993Shenzhen
HK
Flooding in 1993Shenzhen
HK
Before training After training
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Rapid Sedimentation of the trained RiverThe trained river is rapidly silted up in 5 yearsFlood conveying capacity reduced to 1 in 10 yearsThe causes are unclear
Sediment
Observed sediment deposition
(2000-2004)
Observed sediment deposition
(2000-2004)
Observed sediment deposition
(2000-2004)
Observed sediment deposition
(2000-2004)
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Integrated 3D numerical hydrodynamic model for Shenzhen River and Deep Bay
Mai Po Marshes
Futian Nature Reserve
Shenzhen River
Mai Po Marshes
Futian Nature Reserve
Shenzhen River
Chan and Lee (2010)
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Residual current – dry season
62
Pre-training
Downstream flow over the water column
Post-training
Surface downstream and bottom upstream gravitational circulation
Favours the input and trapping of sediment from Deep Bay
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A State Key Water Research Laboratory for Hong Kong Researchers –in the PRD?
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UNIVERSITY-GOVERNMENT-INDUSTRY COLLABORATIONAn Opportunity Missed!
Completed1989
HK$12M
GovernmentAuction of Equipment in Oct.2000
Due for Demolition!
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Victoria Harbour model(1,300 sq. m) for studyingeffect of reclamation on tidal flows
Possibilities existed for developing into a LONG TERM R & D facility for studying a wide range of water environment problems
•Basic and applied environmental research•Drainage design and impact•Training of engineers and students •Nucleus for Govt in-house R&D