42
1 Introduction to groundwater modeling Giovanni Formentin [email protected]

Griglia e condizioni al contorno - unimi.it · 2015. 8. 3. · Boundary conditions may vary (e.g. different recharges depending on monthly rainfall, different pumping periods, tidal

  • Upload
    others

  • View
    5

  • Download
    0

Embed Size (px)

Citation preview

  • 1

    Introduction to groundwater modeling

    Giovanni Formentin

    [email protected]

    mailto:[email protected]

  • 2

    Topics

    1. What is a model

    2. Main types of groundwater models

    3. Purpose of a model

    4. Implementation of a flow model

    5. Example of a MODFLOW model

  • 3

    1.What is a model

    A model is a simplified representation of the real world

    Can be physical…

    Rarely used, almost only for didactical purposes

    http://groundwater.unl.edu/Groundwater.shtml

  • 4

    What is a model

    A model is a simplified representation of the real world

    … or mathematical:

    solves the equations governing groundwater flow and the interactions with

    - the surface (RAIN, EVAPOTRANSPIRATION, IRRIGATION…)

    - surficial water bodies (RIVERS, LAKES, SEA…)

    - structures (WELLS, DRAINAGE SYSTEMS, UNDERGROUND WORKS…)

  • Mathematical models

    ANALYTICAL

    • models representing simple conditions, not needing to be solved by numerical methods

    • e.g. homogeneous and isotropic medium, time-constant boundary conditions, no complex overlapping of hydraulic effects

    NUMERICAL

    • the representation (generally in 2D or 3D) of a domain is discretised in space and time

    • e.g. representation of real, existing settings with different layers, varying properties and time-varying conditions

    5

  • 6

    Based on two equations:

    - Continuity equation (flux IN – flux OUT = change in storage)

    - Darcy equation (q = - K * i)

    Space and time need to be discretized

    Space: cells, nodes, elements

    Time: time-steps

    Numerical models can manage:

    – geological heterogeneity

    – aquifer thickness variation

    – complex boundary conditions

    – stationary and transient conditions

    Numerical models

  • 7

    Ky

    Kz

    Kx

    q= -k grad h

    qx = -K dh/dx

    Flux in - flux out = change in fluid mass stored

    Representative Element Volume (REV)

    V = x·y·z

    y

    porous material element, big enough to

    represent the aquifer properties and small

    enough to represent a homogeneous part

    of aquifer

    x

    Mathematical combination of continuity and

    Darcy equationqy = -K dh/dy

    qz = -K dh/dz

    storage

    Numerical models

  • 8

    The equations can be solved basing on different assumptions and

    discretization strategies

    - FINITE DIFFERENCES (e.g. MODFLOW)

    - FINITE ELEMENTS (e.g. SUTRA, FEFLOW)

    - FINITE VOLUMES

    Every formulation has pros and cons in terms of simplicity, flexibility, accuracy,

    computational time

    Numerical models

  • 9

    • Space is discretized through a grid

    Mesh-centered gridBlock-centered grid

    • Each cell is given a property (K, s…) value and may host

    one or more boundary conditions

    • Two types of grids: block-centered grid or mesh-

    centered grid

    M. AndersonM. Anderson

    Finite differences

  • 10

    Finite differences block-centered

    MODFLOW (2-3D; McDonald e Harbaugh):developed by the USGS in 1988, is the most

    widespread code for GW flow simulation.

    Combined with MT3D, RT3D and SEAWAT,

    simulates transport, degradation and density-

    dependent problems

    PLASM (2D)M. Anderson

    M. Anderson

  • 11

    Sutra (Voss, 1984)

    Feflow (Diersch, 1996): a 2-3Dcode for flow, transport and heat

    simulation

    Mathematical Conditions and properties are assigned to nodes of 2D

    elements (triangles or quadratic) or 3D elements (tetrahedral, etc.)

    M. Anderson

    Finite elements

  • 12

    Finite

    Differences

    Finite Elements

    M. Anderson

    M. Anderson

  • 13

    STEADY-STATE

    Time is not considered as a variable

    flux IN – flux OUT = 0 no variation in aquifer storage

    Good to assess the average condition

    TRANSIENT

    Simulates the evolution of a system over time

    Time is divided into steps (“stress periods” in MODFLOW)

    Boundary conditions may vary (e.g. different recharges depending

    on monthly rainfall, different pumping periods, tidal levels in coastal

    models)

    Steady-state and transient models

  • 2. Main types of gw models

    • Groundwater flow (saturated / unsaturated)

    • Solute transport into groundwater

    • Heat transport into groudwater

    • Interaction between freshwater and saltwater(saltwater intrusion)

    14

  • Groundwater flow model

    15

    modified from U.S.G.S.

  • Solute transport

    • Simulates the movement of solutes (metals, ions, organic compounds…) into groundwater

    • Coupling of a flow model with a transport model (e.g. MODFLOW + MT3D)

    • Transport by advection, diffusion, dispersion

    • Degradation can also be simulated

    16

  • Solute transport

    17

    modified from http://www.rgc.ca/

  • Heat transport

    • Simulates the transport of heat into groundwater

    • Coupling of a density-dependent flow model and a transport model (e.g. MODFLOW + SEAWAT)

    • Typical application: simulation of geothermal heatpumps – heating or cooling systems usinggroundwater as heat source or sink

    18

  • Heat transport

    19

    dT (°C)

    Withdrawal well

    Re-immission well

    MODFLOW 2000 + SEAWAT v. 4

  • Saltwater intrusion

    • Simulates the transport of dissolved salt intogroundwater

    • Coupling of a density-dependent flow model and a transport model (e.g. MODFLOW + SEAWAT)

    • Typical application: simulation of saltwater intrusioninto coastal aquifers

    20

  • Saltwater – unconfined aquifer

    21

    (CUSTODIO E., LLAMAS M.R., 1996)

  • Saltwater – Multi-aquifer

    22

  • Seawater Intrusion

    Coastal Aquifer - No Pumping

    Modified from: WRD – Water Replenishment District of Southern California

  • Seawater Intrusion

    Coastal Aquifer - With Pumping

    Modified from: WRD – Water Replenishment District of Southern California

  • Brackish WaterFresh Water

    Sea Level

    Seawater Intrusion

    Coastal Aquifer - Intrusion Advancing

    Modified from: WRD – Water Replenishment District of Southern California

  • Brackish WaterFresh Water

    Sea Level

    Seawater Intrusion – injection well

    Coastal Aquifer - Pumping and Injection

    Modified from: WRD – Water Replenishment District of Southern California

  • Brackish WaterFresh Water

    Sea Level

    Seawater Intrusion – injection well

    Coastal Aquifer - Pumping and Injection

    Modified from: WRD – Water Replenishment District of Southern California

  • 28

    3. Purpose of a model

    PREDICTION

    and DESIGNRESEARCHSYSTEM

    UNDERSTANDING and

    INTERPRETATION

    A flow or transport model can be built for different purposes

  • 29

    System understanding and interpretation

    Implemented to represent and understand the behavior of a hydrogeological system.

    Helpful to:

    – Organize data: while studying the dynamics of a wide regional system, data

    collection and organization in a model allows to create and improve the

    conceptual model, optimizing further data collection.

    – Understand system dynamics: through the implementation of models

    representing theoretical scenarios, it is possible to understand the system

    behavior and GW dynamics

    – Validate the conceptual site model: a numerical model could help to select

    among different conceptual models or to reduce the starting assumptions

    through comparison between real data and model results

  • 30

    Numerical models are a powerful tool to assist in groundwater managing and in the

    design of remediation systems

    Prediction models are implemented to predict GW flow/transport changes caused by

    new stresses applied to the hydrogeological system

    They need a calibration and a validation process, i.e. the comparison between

    simulation results and real data (heads, fluxes, concentrations, temperatures…).

    After calibration/validation assess the ability of the model to represent the real

    system, it can be applied to predict new scenarios:

    – forecast of system evolution deriving from natural changes in water

    balance (climate change, river levels…..) or from human intervention

    (wells, irrigation…)

    – prediction of the effects of remediation actions in contaminated sites

    (e.g. design of a pump & treat system and forecast of its effect on

    contaminant distribution over time)

    Prediction and design

  • 31

    GW resource management

    • To assess and understand system dynamics and mass balance

    • To evaluate GW cross-flow between aquifers

    • To assess interactions between surficial waters and groundwater

    • To authorize new GW exploitations

    • To assess existing aquifer exploitation activities

    assessment of withdrawal impact on GW resources

    and identification of policies of sustainable use

  • 32

    MS

    09

    MS

    31

    MS

    08

    MS

    32

    MS

    07

    MS

    33

    MS

    16

    Sector Flow rate (l/s)

    West 12,1

    29,4Central 15,5

    East 1,8

    Salt water intrusion

    Hydraulic

    barrier

    Mass balance

    Injection wells

  • 33

    = 1° aquifer

    = aquitard/aquiclude

    = 2° aquifer

    = lake

    QUARRY UNDERGROUND TUNNEL

    water pressure

    SLOPE INSTABILITY

  • 34

    4. Implementation of a flow model

    Anderson & Woessner

  • Model purpose definition

    Prediction or interpretation purpose?

    Which ANSWERS we are looking for?

    SCALE OF THE MODEL? Regional or local?

    FLOW OR TRANSPORT? Is fluid density important?

    Can an ANALYTICAL model give good results?

    Are the AVAILABLE DATA enough to support a

    numerical model?

    35

  • 36

    The conceptual model tries to represent in a simplified, but comprehensive, way

    the real flow system

    Simplification is unavoidable: there’s no limit to the complexity of the real world

    Need to find an equilibrium between simplification and detail in order to represent

    just the relevant phenomena

    Some basic rules

    - Analyze the data assessing their reliability

    - Organize the data (better in a GIS)

    - Build a “solid” conceptual model

    - Start simple, adding complexity only if needed

    The conceptual model

  • 37

    Anderson & Woessner

  • 38

    The choice of the code depends on model purposes and hydrogeological site

    characteristics:

    -complexity of the hydrogeological structure

    -flow-transport-density dependent problem etc….

    E E'

    SEZIONE LITOSTRATIGRAFICA E-E'

    E E'

    SEZIONE LITOSTRATIGRAFICA E-E'

    Code selection and model design

  • Model design

    • Model domain

    • Layering and mesh refining where necessary

    • Input of the hydrogeological layers

    • Input of the aquifer properties (hydraulic conductivity K, storage coefficient s…)

    • Input of the boundary conditions (sea, rivers, lakes, wells…)

    39

  • 40

    Variation of properties and boundary conditions to obtain the best agreement

    between measures and model outputs (heads, flow rates, concentrations,

    temperatures…)

    Calibration

  • 41

    After the previous steps it is possible to use the model to understand the system

    dynamics or to predict flow and heads linked to new stress

    The model reliability is evaluated by the simulation of flow/stress conditions

    different from those used in calibration: e.g. different recharge, pumping tests

    etc…

    7. Prediction

    Check of a prediction scenario after the real application of new stresses

    8. Postaudit

    9. Model update

    Collection of relevant data may drive updates in the model structure

    Further steps6. Validation

  • Modflow GUIs

    Modflow is usually run in a Graphical User Interface (GUI)

    ModelMuse (free)

    Groundwater Vistas

    Visual Modflow

    GMS

    42