Article

Dissolution of arsenopyrite (FeAsS) and galena (PbS) in the presence of desferrioxamine-B at pH 5

Facultad de Química, Universidad Nacional Autónoma de México, Cd. Universitaria, México D. F. CP 04510, México; Instituto de Geografía, Universidad Nacional Autónoma de México, Cd. Universitaria, México D. F. CP 04510, México; Instituto de Investigación en Materiales, Universidad Nacional Autónoma de México, Cd. Universitaria, México D. F. CP 04510, México
Geochimica et Cosmochimica Acta DOI:10.1016/j.gca.2008.02.008 pp.2754-2766

ABSTRACT Microorganisms and higher plants produce biogenic ligands, such as siderophores, to mobilize Fe that otherwise would be unavailable. In this paper, we study the stability of arsenopyrite (FeAsS), one of the most important natural sources of arsenic on Earth, in the presence of desferrioxamine (DFO-B), a common siderophore ligand, at pH 5. Arsenopyrite specimens from mines in Panasqueira, Portugal (100–149 μm) that contained incrustations of Pb, corresponding to elemental Pb as determined by scanning electron microscopy–electron diffraction spectroscopy (SEM–EDX), were used for this study. Batch dissolution experiments of arsenopyrite (1 g L−1) in the presence of 200 μM DFO-B at initial pH (pH0) 5 were conducted for 110 h. In the presence of DFO-B, release of Fe, As, and Pb showed positive trends with time; less dependency was observed for the release of Fe, As, and Pb in the presence of only water under similar experimental conditions. Detected concentrations of soluble Fe, As, and Pb in suspensions containing only water were found to be ca. 0.09 ± 0.004, 0.15 ± 0.003, and 0.01 ± 0.01 ppm, respectively. In contrast, concentrations of soluble Fe, As, and Pb in suspensions containing DFO-B were found to be 0.4 ± 0.006, 0.27 ± 0.009, and 0.14 ± 0.005 ppm, respectively. Notably, the effectiveness of DFO-B for releasing Pb was ca. 10 times higher than that for releasing Fe. These results cannot be accounted for by thermodynamic considerations, namely, by size-to-charge ratio considerations of metal complexation by DFO-B. As determined by SEM–EDX, elemental sample enrichment analysis supports the idea that the Fe–S subunit bond energy is limiting for Fe release. Likely, the mechanism(s) of dissolution for Pb incrustations is independent and occurs concurrently to that for Fe and As. Our results show that dissolution of arsenopyrite leads to precipitation of elemental sulfur, and is consistent with a non-enzymatic mineral dissolution pathway. Finally, speciation analyses for As indicate variability in the As(III)/As(V) ratio with time, regardless of the presence of DFO-B or water. At reaction times <30 h, As(V) concentrations were found to be 50–70%, regardless of the presence of DFO-B. These results are interpreted to indicate that transformations of As are not imposed by ligand-mediated mechanisms. Experiments were also conducted to study the dissolution behavior of galena (PbS) in the presence of 200 μM at pH0 5. Results show that, unlike arsenopyrite, the dissolution behavior of galena shows coupled increases in pH with decreases in metal solubility at t > 80 h. Oxidative dissolution mechanisms conveying sulfur oxidation bring about the production of {H+}. However, dissolution data trends for arsenopyrite and galena indicate {H+} consumption. It is plausible that the formation of Pb species is dependent on {H+} and {OH−}, namely, stable surface hydroxyl complexes of the form (pH50 5.8) and for pH values 5.8 or above.

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    Article: Metalloid Contaminated Microhabitats and their Biodiversity at a Former Antimony Mining Site in Schlaining, Austria
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    ABSTRACT: This paper is on the biological impact of arsenic and antimony on the flora and microflora on a former Sb-mining site in Schlaining (Stadtschlaining, Burgenland, Austria). Several habitats were investigated with respect to biodi-versity and metalloid contamination in soil. Although the overburden of the mining activity had been remediated less than ten years ago, metalloid concentrations occurred in soil up to 1.4‰ As and 3.6% Sb, respectively, in some microhabitats, as determined by Instrumental Neutron Activation Analysis. These metalloids were embedded into a nonuniform minera-logical background. Metalloid mobility could not be explained by common models, indicating that predictions on the mo-bility of geogenic metalloids require additional mineralogical data. The biological effects of this contamination were vari-able. We observed that metalloid resistant strands of microorganisms appeared in the contaminated soil. In cultivation ex-periments, Sb was found to be more toxic than As. Sulphur oxidising strand were more resistant than organotrophic ones and grew even better on cultivation media spiked with 10 ppm As than on the unspiked control. The flora was only par-tially influenced: the lowest biodiversity was found in metalloid richest soils, but moderate contamination resulted in en-hanced species numbers. Only in one case, where the pH-buffering capacity of the soil was exceeded by consumption of the entire carbonate, no embryophytes occurred. This was probably due to extreme pH conditions as well as to metalloid concentrations. Our data support the hypothesis that higher plants are rather affected by extreme soil conditions, which of-ten coincide with As contaminations, than by the contamination itself. A small rivulet in this area contained 26 g/l and thus exceeded the WHO guideline value for As in drinking water by a factor of 2.6. Indeed we observed a diminished bio-diversity in this rivulet.
    Open Environmental Sciences 01/2009; 3:26-41.

Keywords

biogenic ligands
 
contained incrustations
 
dissolution behavior
 
elemental Pb
 
Fe release
 
Fe–S subunit bond energy
 
higher plants
 
initial pH
 
ligand-mediated mechanisms
 
non-enzymatic mineral dissolution pathway
 
Pb incrustations
 
pH 5. Arsenopyrite specimens
 
pH0 5. Results
 
reaction times <30 h
 
scanning electron microscopy–electron diffraction spectroscopy
 
size-to-charge ratio considerations
 
soluble Fe
 
speciation analyses
 
thermodynamic considerations
 
{H+} consumption
 

Hilda Cornejo-Garrido