2017
DOI: 10.15244/pjoes/65470
|View full text |Cite
|
Sign up to set email alerts
|

Release Law of Sb, As, and Hg in Antimony Smelting Slag Under Simulated Acid Rain

Abstract: The exploitation and smelting of heavy metals causes serious environmental pollution, which has received extensive attention from researchers all over the world [1][2][3]. The smelting slag produced by the smelting mines is not only land-occupying, but also causes lasting environmental pollution, for large amounts of harmful elements in the smelting slag are released after rain [4][5][6][7]. As the world's largest antimony (Sb) producer, China produces on average 80% of global Sb annually [8].Xikuangshan (XKS)… Show more

Help me understand this report

Search citation statements

Order By: Relevance

Paper Sections

Select...
2
1
1
1

Citation Types

0
7
0

Year Published

2018
2018
2024
2024

Publication Types

Select...
9

Relationship

3
6

Authors

Journals

citations
Cited by 12 publications
(9 citation statements)
references
References 34 publications
0
7
0
Order By: Relevance
“…Due to the dissolution of the exchangeable fraction, the slag surface was degraded and the internal parts of the slag were exposed, thereby yielding adsorption sites, and some of the dissolved PTMs were re-adsorbed to decrease the concentrations of PTMs. In the late soaking stage, as the internal parts of the slag gradually reacted with the soaking solution, the fractions that were difficult to exchange were released through further oxidation [ 56 ], which was relatively slow. Accordingly, the PTM concentrations increased slowly in the late stages of soaking or leaching.…”
Section: Resultsmentioning
confidence: 99%
“…Due to the dissolution of the exchangeable fraction, the slag surface was degraded and the internal parts of the slag were exposed, thereby yielding adsorption sites, and some of the dissolved PTMs were re-adsorbed to decrease the concentrations of PTMs. In the late soaking stage, as the internal parts of the slag gradually reacted with the soaking solution, the fractions that were difficult to exchange were released through further oxidation [ 56 ], which was relatively slow. Accordingly, the PTM concentrations increased slowly in the late stages of soaking or leaching.…”
Section: Resultsmentioning
confidence: 99%
“…The slight alkalinity highlights the strong acid neutralization capacity with the PTEs forming hydroxides or complexes after dissolution. During the storage of the waste, the PTEs dissolved and released will be reduced in their ability to migrate immediately, and in the long term the hazard potential is localized within the site, but sensitive to future change in environmental conditions [38].…”
Section: Resultsmentioning
confidence: 99%
“…Compared with the original tailing sand in the study area, the pH value of the tailing sand did not change significantly after liquid leaching with different initial pH values. It is possible that the soaking process of sulfide minerals releases H + , while CO 3 2on the surface of the tailing sand reacts with water to produce OH -, and the mineral surface adsorbs Na + , Ca 2+ , etc., creating a buffering effect on acidic and alkali substances [20]. Another reason could be the smaller the particle size of the tailing sand, the faster the reaction rate with the water interface, thus possibly releasing more buffer ions and neutralizing the acidic or alkaline background solution.…”
Section: Variation Characteristics Of Ph Ec and Ehmentioning
confidence: 99%