Page 115 - Geochemical Anomaly and Mineral Prospectivity Mapping in GIS
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114                                                             Chapter 4

             concentration-area method, e.g., a concentration-distance method (Li et al., 2003) and a
             summation method (Shen and Cohen,  2005). The concentration-area  method and its
             variants are appropriate for geochemical data analysis in the spatial domain, in which the
             scale-invariant characteristics of  geochemical landscapes are  related to the empirical
             density distributions, spatial variability and geometrical  patterns  of geochemical  data
             sets.
                Other methods for fractal analysis of  geochemical anomalies involve converting
             geochemical data into a function of ‘wave numbers’ in the frequency domain, in which
             the scale-invariant characteristics of geochemical landscapes are represented by means
             of a power spectrum. For details of fractal analysis of geochemical anomalies in the
             frequency domain, readers  are referred to authoritative  explanations by Cheng et al.
             (2000). Nevertheless, Cheng et al. (2000) aver that “because the spatial distribution of
             power spectrum is determined not only by the wave numbers but also by the power-
             spectrum function, it should be characterised by the concentration-area fractal method”.
             This means that the concentration-area fractal  method is a fundamental technique for
             modeling of geochemical anomalies.
                The case study on GIS-based application  of  the concentration-area  fractal  method
             shows the multifractal nature of the  geochemical  landscape in the  Aroroy  district
             (Philippines) based on stream sediment uni-element data. The results of the case study
             illustrate that significant anomalies related to the epithermal Au deposit occurrences are
             modeled better when the geochemical landscape is represented as discrete surfaces rather
             than as continuous surfaces. Perhaps the application of inverse distance moving average
             to derive the  continuous geochemical surfaces from the point stream sediment uni-
             element data is not optimal in this case, particularly because stream sediments do not
             represent continuous geo-objects. The case study demonstrates, nonetheless, that either
             continuous  or discrete geochemical  surfaces  can  be  used in GIS-based concentration-
             area multifractal modeling of significant anomalies in stream sediment uni-element data.
                As shown in the case study, application of traditional methods of spatial interpolation
             to derive continuous  geochemical surfaces can undermine  multifractal analysis  of
             geochemical anomalies. However, methods for multifractal interpolation (Cheng, 1999a)
             and fractal filtering (Xu and Cheng, 2001) have been developed to take into account the
             concentration-area relationship in deriving, from point geochemical data, ‘ready-to-use’
             interpolated maps in which  background and anomalies  are already separated. These
             methods have not been demonstrated here, not only because extensive discussion spatial
             interpolation and  filtering is beyond the scope  of this volume but also because they
             require specialised software, which is  dedicated to  such purposes and which is  not
             available in most commercial or shareware GIS software packages.
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