Abstract

In this study, we propose a growth pathway of scorodite in an atmospheric scorodite synthesis. Scorodite is a non-direct product, which is derived from the transformation of its precursor. Different precursor speciation leads to different crystallinity and morphology of synthesized scorodite. At 10 and 20 g l−1 initial arsenic concentration, the precursor of scorodite is identified as ferrihydrite. At 10 g l−1 initial arsenic concentration, low arsenic concentration is unfavourable to the complex between arsenate and ferrihydrite, inhibiting the transformation of ferrihydrite into scorodite. The synthesized scorodite is 1–3 µm in size. At 20 g l−1 initial arsenic concentration, higher arsenic concentration favours the complex between arsenate and ferrihydrite. The transformation process is accessible. Large scorodite in the particle size of 5–20 µm with excellent crystallinity is obtained. However, the increasing initial arsenic concentration is not always a positive force for the growth of scorodite. When initial arsenic concentration increases to 30 g l−1, Fe(O,OH)6 octahedron preferentially connects to As(O,OH)4 tetrahedron to form or ion. Fe–As complex ions accumulate in solution. Once the supersaturation exceeds the critical value, the Fe–As complex ions deprotonate and form poorly crystalline ferric arsenate. Even poorly crystalline ferric arsenate can also transform to crystalline scorodite, its transformation process is much slower than ferrihydrite. Therefore, incomplete developed scorodite with poor crystallinity is obtained.

Highlights

  • Arsenic is a typical carcinogenic element, which has been identified as a group 1 carcinogen by International Agency for royalsocietypublishing.org/journal/rsos R

  • X-ray diffraction (XRD) patterns of samples synthesized at 10–30 g l−1 initial arsenic concentrations are illustrated in figure 1a–c, respectively

  • The XRD patterns show that scorodite was successfully synthesized at 10–30 g l−1 initial arsenic concentration

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Summary

Introduction

Arsenic is a typical carcinogenic element, which has been identified as a group 1 carcinogen by International Agency for royalsocietypublishing.org/journal/rsos R. Research on Cancer (IARC) [1] It is often accompanied with non-ferrous metal (e.g. Ni, Sn, Pb, Cu 2 and Zn) [2,3]. The occurrence of arsenic release during non-ferrous metal metallurgy poses a huge threat to the environment and human health all around the world [4]. Crystalline scorodite has been considered to be one of the most suitable arsenic immobilization materials because of its low solubility, high arsenic content, high filterability and low water content of precipitates [5,6]. The atmospheric scorodite synthesis by injecting oxygen to a Fe(II)–As(V) mixed solution has become a popular method due to its easy operation, high efficiency for arsenic precipitation and stable products [9,10]. To the best of our knowledge, the mechanism analysis of scorodite growth in this process has not been investigated

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