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Kouli_etal_2008_Groundwater modelling_BOOK.pdf - Pantelis ...

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150<br />

Husam Baalousha<br />

scheme. Clearly, it is a simple and cheap solution compared to project establishment in<br />

reality.<br />

By definition, models simplify reality, and are, therefore, imperfect. The famous<br />

statistician George Box insisted, “ all models are wrong, but some are useful” (Box and<br />

Draper 1987). Applicability of any model and its usage depends on the objectives of that<br />

model. Though they are imperfect, models are very useful in hydrogeology. It is a challenge<br />

to the modeller to represent the real word problem in a simplified form without compromising<br />

the accuracy or making invalid assumptions. Modellers try to get the best representation of<br />

reality by collecting as much data as possible and feeding the models with new data.<br />

<strong>Groundwater</strong> models can be classified into three categories: physical, analogue or<br />

mathematical. Solution of mathematical models can be either analytical or numerical.<br />

Analytical methods do not require much data, but their application is limited to simple<br />

problems. Numerical solutions can handle more complicated problems than analytical<br />

solutions. With the rapid development of computer processors and increasing speed,<br />

numerical <strong>modelling</strong> has become more effective and easy to use.<br />

The most commonly used numerical <strong>modelling</strong> approaches are the “finite difference”<br />

method and the “finite element” method. Each method has its advantages and limitations.<br />

Depending on the problem of concern and the objectives of <strong>modelling</strong>, the appropriate<br />

<strong>modelling</strong> approach can be selected. Finite difference method can produce different results to<br />

finite element method if the problem of concern is complicated. Modelling approach is not<br />

the only factor that affects the model’s results. Other factors like boundary conditions, initial<br />

condition, time and space discritisation, and quality of data influence the results.<br />

This chapter outlines the stepwise methodology of groundwater <strong>modelling</strong>, differences<br />

between <strong>modelling</strong> approaches and difficulties accompany groundwater <strong>modelling</strong>. Common<br />

mistakes in groundwater <strong>modelling</strong> are also discussed.<br />

2.0. Modelling Approach<br />

<strong>Groundwater</strong> Models can be simple, like one-dimensional analytical solutions or spreadsheet<br />

models (Olsthoorn, 1985), or very sophisticated three-dimensional models. It is always<br />

recommended to start with a simple model, as long as the model concept satisfies <strong>modelling</strong><br />

objectives, and then the model complexity can be increased (Hill 2006). Regardless of the<br />

complexity of the model being used, the model development is the same.<br />

The stepwise methodology of groundwater <strong>modelling</strong> is shown in Figure 1. The first step<br />

in <strong>modelling</strong> is identification of model objectives. Data collection and processing is a key<br />

issue in the <strong>modelling</strong> process. The most essential and fundamental step in <strong>modelling</strong>,<br />

however, is model conceptualization. Calibration, verification and sensitivity analysis can be<br />

conducted after model completion and the first run. The following sections explain in detail<br />

each step in groundwater <strong>modelling</strong>.

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