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Faculty of Engineering The University of Hong Kong May 26, 2010 Hydraulics and the Environment By Joseph Hun-wei Lee Department of Civil Engineering The University of Hong Kong

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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

  • 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

  • Air pollution

    Hong Kong

    Tall buildings

    Coastal pollution

    Clear sky

    Population density ranks 4th in the world

    Red tide

  • Heat Island effect

    Urban Flooding

    Ocean outfall discharge(Rosette jet group in a current)

    Industrial emission

  • 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

  • (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)

  • 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=

  • Modelling of buoyant jets in complex environment

    • Ocean outfall design• Mixing zone analysis• Impact assessment• Post-operation

    monitoring

  • 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

  • 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

  • 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

  • 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)

  • 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

  • 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

  • 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

  • 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

  • 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

  • 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

  • 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

  • With interaction No interactionCross-section at z = 20D

    Induced velocities

    Induced pressure

  • 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

  • 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)

  • 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

  • Mixing of a plume in Mixing of a plume in crossflowcrossflow

    cross section(experiment)

    Advected line thermal

    cross section(computed)

  • 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

  • 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

  • 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

    +−=

    )]cos(cos2

    coscos

    coscos12[

    2

    22

    θφπ

    θφπ

    φθρ

    kfk

    s EEM ϕπϕπ

    sin)( +−

  • 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

  • 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 /=

  • 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

  • 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

  • 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

  • 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

  • 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)

  • 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

  • Mixing in the intermediate field can be modeled by coupling a plume model with a 3D circulation model -Distributed Entrainment Sink Approach (DESA)

  • 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)

  • Registered VISJETin different continents

    Asia 42Australia 24Europe 25South America 8North America 30

    Worldwide application of Worldwide application of VISJETVISJET

    HK

  • 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

  • Main Nullah

    San HuiNullah

    YLBPYLBP

    Limited land availability Complex super-/sub-critical flow junctions/transitions

  • Yuen Long Bypass Floodway (YLBF) Model

    Complicated junction flow; tight land availability

  • 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

  • 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

  • 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

  • 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

  • Yuen Long Bypass Floodway:

  • 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

  • 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

  • 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

  • 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)

  • 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

  • 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

  • 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

  • Stability of Spiral Vortex Flow

    Unstable Flow with Long Approach Channel

    Stable Flow with Short Approach Channel

  • 1:25 Vortex Intake Model: Highly unstable flow!Normal flow conditions at inlet channel

    Shock wave height hm = 270 mm

  • Sustainable urban water supply and drainage systems - Hydraulics of two-phase air-water flows

    - Rehabilitation of urban infrastructure- Energy conservation - Renewable energy

  • Two-phase pipe flowHydraulic transient and geysers in the laboratory

    Two-phase flow on high dams (Tai Lam Chung & Three Gorges)

  • 3) Challenge of coastal erosion and sedimentation

    River sedimentation laboratory, Tsinghua University

    Hong Kong HarbourHydraulics Laboratory

  • 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

  • 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)

  • 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)

  • 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

  • A State Key Water Research Laboratory for Hong Kong Researchers –in the PRD?

  • UNIVERSITY-GOVERNMENT-INDUSTRY COLLABORATIONAn Opportunity Missed!

    Completed1989

    HK$12M

    GovernmentAuction of Equipment in Oct.2000

    Due for Demolition!

  • 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