What do we know about the natural sources, transport and sinks of antimony in the environment?

Juraj Majzlan, Montserrat Filella
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Abstract

Limited attention has been given to antimony present in detrital form in the different environmental compartments except for highly polluted systems related in some way to ore deposits. In highly polluted systems, the ultimate sinks of Sb may be the minerals tripuhyite (FeSbO4) or perhaps schafarzikite (FeSb2O4) but how about Sb dynamics in the much more abundant, weakly polluted or ‘non-polluted’ systems? This deficiency in our knowledge is probably related to the perception that the element is mostly present ‘dissolved’ in waters and to a focus on the role of its binding to iron oxyhydroxides in solid phases. Here we evaluate the state of our knowledge in the Sb journey from geological matrices to detrital forms in soils and waters and identify key aspects that require further investigation. In high-temperature environments, Sb demonstrated its striking incompatibility by fractionation into aqueous fluids or sulfide/metallic melts, or by uptake in a few common minerals that accept this element (e.g., rutile or pyrite). In low-temperature environments, Sb enters the structures of minerals with different formation rates and solubilities, creating a confusing impression of being mobile and immobile at the same time. The estimates of Sb concentration in the upper continental crust are scattered and the Sb-bearing mineral(s) there have not yet been identified. Given that sedimentary rocks are consistently enriched in Sb, the carriers could be the clay minerals. In surface water bodies, Sb could be carried predominantly in the particulate fraction, despite the popular belief of the opposite. An important point to consider is the transport of Sb within the suspended particulate matter, not on its surface. In soils, many studies employed sequential extractions to show that Sb accumulates in the ‘residual’ fraction, without ever asking what the nature of this fraction is. Based on these facts (i.e., knowns), we have identified the unknowns regarding detrital Sb on our planet that should preferentially be addressed by future projects if our understanding is to improve.

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我们对环境中锑的自然来源、迁移和吸收汇了解多少?
除了以某种方式与矿床相关的高污染系统外,人们对不同环境区划中以非晶体形式存在的锑关注有限。在高度污染的系统中,锑的最终汇可能是矿物三长石(FeSbO4),也可能是闪锌矿(FeSb2O4),但在含量更丰富的弱污染或 "非污染 "系统中,锑的动态如何?我们之所以缺乏这方面的知识,可能是因为我们认为锑元素主要 "溶解 "在水体中,并将注意力集中在锑元素与固相中的铁氧氢氧化物的结合作用上。在此,我们评估了我们对锑从地质基质到土壤和水体中分离形式的认识状况,并确定了需要进一步研究的关键方面。在高温环境中,锑通过分馏到水流或硫化物/金属熔体中,或被少数几种可接受这种元素的常见矿物(如金红石或黄铁矿)吸收,显示了其惊人的不相容性。在低温环境中,锑会以不同的形成速度和溶解度进入矿物结构中,给人一种既可移动又不可移动的混乱印象。对上部大陆地壳中锑浓度的估计比较零散,尚未确定那里的含锑矿物。鉴于沉积岩一直富含锑,其载体可能是粘土矿物。在地表水体中,锑可能主要以微粒形式携带,尽管人们普遍认为情况恰恰相反。需要考虑的重要一点是锑在悬浮颗粒物中的迁移,而不是在其表面的迁移。在土壤中,许多研究采用连续萃取法来表明锑在 "残留 "部分中累积,却从未询问过这部分的性质。基于这些事实(即已知事实),我们确定了地球上有关碎屑态 Sb 的未知因素,如果要提高我们的认识,未来的项目应优先解决这些未知因素。
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