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Kouli_etal_2008_Groundwater modelling_BOOK.pdf - Pantelis ...

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316<br />

Nigel J. Cassidy<br />

resolution minimum is linked to the signal wavelength, which is related to the permittivity of<br />

the sub-surface materials (see later section on material properties). Typically, the resolution<br />

limit is between ½ to ¼ of the signal wavelength and if the sub-surface features become<br />

smaller than this, then the EM energy will become scattered and the recorded GPR signals<br />

will be chaotic, incoherent and difficult to interpret. At feature sizes of less than 1/10 of the<br />

wavelength, then the material property variations are too small to produce reflected or<br />

scattered energy and the material effectively becomes macroscopically uniform in terms of<br />

the propagating GPR wave. This target resolution limit, and its relationship to the macro-tomicroscopic<br />

properties of the sub-surface materials, is very important for groundwater studies<br />

as it establishes the physical size of variations that can be imaged by any given GPR system.<br />

This could be a watertable interface, a high-permeability fluid pathway (e.g., a coarse sandy<br />

layer or lens in a fine sand body), a contaminant plume or any other similar feature. However,<br />

to actually produce a defined reflection in the GPR section, the interface between the two<br />

materials must be sharp enough, and of significant contrast, to result in sufficient energy<br />

being returned back to the receiving antenna. In practical terms, this means that materials<br />

must have permittivity and/or conductivity contrasts of at least 5-10% and physical<br />

boundaries at centimetre scales or less. Diffuse or gradational changes in material properties<br />

(e.g., a large capillary zone or disseminated materials) do not produce defined GPR<br />

reflections because the dimensions of the boundary are not sharp enough. This is a common<br />

problem in groundwater mapping as users often expect to see a strong reflection from the<br />

watertable interface in the GPR sections. This is true in coarse materials (see Figure 3), but in<br />

finer sands and silts, the capillary zone thickness can be tens of centimetres or more and there<br />

will be no distinct watertable reflector (Bano, 2006). That said, the form, velocity and<br />

attenuation of the GPR wave will be altered as it propagates through the capillary zone (or<br />

any diffuse boundary) and it is these properties that more sophisticated GPR studies attempt<br />

to extract from the recorded data.<br />

Table 1. Approximate imaging depth and target size (resolution) of a range of GPR<br />

frequencies in an unsaturated, naturally damp, sandy soil. Values in bold represent the<br />

most common frequencies used in groundwater and hydrological studies<br />

Antenna centre<br />

frequency<br />

(MHz)<br />

Approximate imaging<br />

depth in a damp soil<br />

(metres)<br />

Approximate target size in a<br />

damp soil<br />

(metres)<br />

1500 0.3 0.03<br />

1000 1 0.05<br />

500 2 0.1<br />

250 3 0.2<br />

100 5 0.5<br />

50 10 1<br />

20 20 2<br />

Note that these are only ‘typical’ values for a hypothetical soil. In practice, penetration depths can different to<br />

this and in most cases much shallower.

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