首页> 外文期刊>Geochimica et Cosmochimica Acta: Journal of the Geochemical Society and the Meteoritical Society >Effects of arsenic incorporation on jarosite dissolution rates and reaction products
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Effects of arsenic incorporation on jarosite dissolution rates and reaction products

机译:砷掺入对黄铁矿溶出速率和反应产物的影响

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Batch dissolution experiments were undertaken on synthetic arsenojarosites at pH 2, pH 8, and in ultra-pure water to better understand the influence of As incorporation on the kinetics and reaction products of jarosite dissolution. Incongruent jarosite dissolution was observed in all experiments. Arsenojarosite lacks the pH dependency observed in K-jarosite dissolution, likely the result of surface arsenate-iron complexes preventing protonation at low pH and repelling hydroxyls at high pH. The stronger bonding of arsenate to iron, compared to sulfate to iron, leads to an enrichment of surface layer arsenate-iron complex sites, inhibiting the dissolution of jarosite with time. The secondary reaction products formed during the dissolution of arsenojarosite include maghemite, goethite, and hematite in ultra-pure water, and ferrihydrite in pH 8 Tris buffered solution. Maghemite initially forms and transitions to hematite with time in ultra-pure water, but increasing arsenic concentrations slow this transition. At pH >3.5, arsenic from the dissolution of arsenojarosite adsorbs onto newly formed reaction products. Arsenic also inhibits the formation of goethite and reduces the crystallinity of the observed maghemite reaction products. The coprecipitation of iron oxides with increasing amounts of arsenic results in a change from spherical to " worm-like" aggregate morphology and provides a sink for arsenic released during arsenojarosite dissolution. This study shows that in open systems with a flush of fresh solution, arsenic incorporation in jarosite results in an increase in dissolution rates. In closed systems, however, increasing surface arsenate-iron complexes inhibit further dissolution of the underlying bulk material, causing a reduction in dissolution rates as arsenic incorporation increases.
机译:在pH 2,pH 8的合成毒砂铁矿和超纯水中进行了批量溶解实验,以更好地了解As掺入对黄铁矿溶解动力学和反应产物的影响。在所有实验中均观察到不一致的黄钾铁矾溶解。毒砂铁矿缺乏在钾铁矾石溶解中观察到的pH依赖性,这可能是表面砷酸盐-铁络合物阻止了低pH的质子化和排斥高pH的羟基的结果。与硫酸盐与铁相比,砷酸盐与铁的更强键合导致表面层砷酸盐-铁络合物位点的富集,从而抑制了黄钾铁矾随时间的溶解。毒砂铁矿溶解过程中形成的次级反应产物包括超纯水中的磁铁矿,针铁矿和赤铁矿,以及pH 8 Tris缓冲溶液中的亚铁酸盐。磁赤铁矿最初会在超纯水中随时间形成并转变为赤铁矿,但砷浓度的增加会减缓这种转变。在pH> 3.5时,砷砷铁矿溶解后的砷吸附到新形成的反应产物上。砷还抑制针铁矿的形成,并降低了观察到的磁赤铁矿反应产物的结晶度。随着砷含量的增加,氧化铁的共沉淀导致球状聚集体形态从“蠕虫状”转变为砷铁矾溶解期间释放的砷。这项研究表明,在充满新鲜溶液的开放式系统中,黄铁矿中掺入砷会增加溶出速率。然而,在封闭系统中,增加的表面砷酸盐-铁络合物会抑制下面的块状物料的进一步溶解,从而随着砷掺入量的增加而导致溶解速率降低。

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