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Published online 3 January 2006
Published in J Environ Qual 35:21-36 (2006)
DOI: 10.2134/jeq2004.0389
© 2006 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
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Mapping Residual Pyrite after a Mine Spill Using Non Co-Located Spatiotemporal Observations

Karl Vanderlindena,*, Rafaela Ordóñezb, Maria J. Poloc and Juan V. Giráldezc

a CIFA "Las Torres-Tomejil", I.F.A.P.A.-C.I.C.E. (Junta de Andalucía), Ctra. Sevilla-Cazalla, km 12,2, 41200 Alcalá del Río, Sevilla, Spain
b CIFA "Alameda del Obispo", I.F.A.P.A.-C.I.C.E. (Junta de Andalucía), 14080 Córdoba, Spain
c Dep. of Agronomy, University of Córdoba, Avda. Menéndez Pidal, s/n, 14080 Córdoba, Spain



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Fig. 1. Location of the Iberian pyrite belt within Andalusia, Spain, and of the study zone in the province of Seville. The ortho-photograph gives a detailed view of the meander and the monitoring site along the Guadiamar River during the cleanup activities in July 1998.

 


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Fig. 2. Location of the 503 sampling points within the monitoring site depicted in Fig. 1, according to the sampling date. The background gray-scale map represents local relative topography.

 


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Fig. 3. Histograms of pH and EDTA-extractable Cu, before and after the sugar beet foam application in February 2000.

 


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Fig. 4. Circles of correlation, showing the configuration of elevation (elev); normal score (ns) pH; ns soil oxidizable fraction (SOF); and ns EDTA-extractable Fe, Zn, and Cu, in the plane defined by the first two principal components (PC): (a) without rotation and (b) after Varimax rotation.

 


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Fig. 5. Sample variogram surfaces for normal score (ns) pH; ns soil oxidizable fraction (SOF); ns EDTA-extractable Fe, Zn, and Cu; and elevation, elev.

 


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Fig. 6. Directional and omnidirectional sample variograms, with their respective fitted models for normal score (ns) pH; ns soil oxidizable fraction (SOF); and ns EDTA-extractable Fe, Zn, and Cu. The fitted parameters are represented in Table 3.

 


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Fig. 7. Omnidirectional sample cross-variograms and codispersion functions for the pooled normal score (ns)–transformed chemical properties: pH; EDTA-extractable Fe, Zn, and Cu; soil oxidizable fraction (SOF); and elevation (elev).

 


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Fig. 8. Performance of three interpolation methods based on the kriging algorithm for the interpolation of normal score (ns)–transformed soil chemical properties. OKi, ordinary kriging with an isotropic variogram model; OKa, OK with an anisotropic variogram model; and SKlm, simple kriging with local varying means.

 


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Fig. 9. Block kriged normal score maps for pH; soil oxidizable fraction (SOF); and EDTA-extractable Fe, Zn, and Cu. Block dimensions are 2.5 x 2.5 m.

 


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Fig. 10. Classified normal score pH map for September 1999, according to a threshold value of pH = 4.

 





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