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Chemical treatment of highly toxic acid mine drainage at a gold mining site in Southwestern Siberia, Russia. / Bortnikova, Svetlana; Gaskova, Olga; Yurkevich, Nataliya и др.

в: Minerals, Том 10, № 10, 867, 10.2020, стр. 1-23.

Результаты исследований: Научные публикации в периодических изданияхстатьяРецензирование

Harvard

Bortnikova, S, Gaskova, O, Yurkevich, N, Saeva, O & Abrosimova, N 2020, 'Chemical treatment of highly toxic acid mine drainage at a gold mining site in Southwestern Siberia, Russia', Minerals, Том. 10, № 10, 867, стр. 1-23. https://doi.org/10.3390/min10100867

APA

Vancouver

Bortnikova S, Gaskova O, Yurkevich N, Saeva O, Abrosimova N. Chemical treatment of highly toxic acid mine drainage at a gold mining site in Southwestern Siberia, Russia. Minerals. 2020 окт.;10(10):1-23. 867. doi: 10.3390/min10100867

Author

Bortnikova, Svetlana ; Gaskova, Olga ; Yurkevich, Nataliya и др. / Chemical treatment of highly toxic acid mine drainage at a gold mining site in Southwestern Siberia, Russia. в: Minerals. 2020 ; Том 10, № 10. стр. 1-23.

BibTeX

@article{32f97975545b4dc29d93a444180fef6b,
title = "Chemical treatment of highly toxic acid mine drainage at a gold mining site in Southwestern Siberia, Russia",
abstract = "The critical environmental situation in the region of southwestern Siberia (Komsomolsk settlement, Kemerovo region) is the result of the intentional displacement of mine tailings with high sulfide concentrations. During storage, ponds of acidic water with incredibly high arsenic (up to 4 g/L) and metals formed on the tailings. The application of chemical methods to treat these extremely toxic waters is implemented: milk of lime Ca(OH)2, sodium sulfide Na2S, and sodium hydroxide NaOH. Field experiments were carried out by sequential adding pre-weighed reagents to the solutions with control of the physicochemical parameters and element concentrations for each solution/reagent ratio. In the experiment with Ca(OH)2, the pH increased to neutral values most slowly, which is contrary to the results from the experiment with NaOH. When neutralizing solutions with NaOH, arsenic-containing phases are formed most actively, arsenate chalcophyllite Cu18Al2(AsO4)4(SO4)3(OH)24·36H2O, a hydrated iron arsenate scorodite, kaatialaite FeAs3O9·8H2O and Mg(H2AsO4)2. A common specificity of the neutralization processes is the rapid precipitation of Fe hydroxides and gypsum, then the reverse release of pollutants under alkaline conditions. The chemistry of the processes is described using thermodynamic modeling. The main species of arsenic in the solutions are iron-arsenate complexes; at the end of the experiments with Ca(OH)2, Na2S, and NaOH, the main species of arsenic is CaAsO4−, the most toxic acid H3AsO3 and AsO43−, respectively. It is recommended that full-scale experiments should use NaOH in the first stages and then Ca(OH)2 for the subsequent neutralization.",
keywords = "Arsenic-containing tailings, Milk of lime, Mine water treatment, Sodium hydroxide, Sodium sulfide, HEAVY-METAL IONS, SCORODITE, RESOURCE RECOVERY, COPPER, MECHANISMS, sodium hydroxide, REMEDIATION, FERRIC IRON, IMMOBILIZATION, arsenic-containing tailings, PRECIPITATION, mine water treatment, sodium sulfide, ARSENIC REMOVAL, milk of lime",
author = "Svetlana Bortnikova and Olga Gaskova and Nataliya Yurkevich and Olga Saeva and Natalya Abrosimova",
year = "2020",
month = oct,
doi = "10.3390/min10100867",
language = "English",
volume = "10",
pages = "1--23",
journal = "Minerals",
issn = "2075-163X",
publisher = "MDPI AG",
number = "10",

}

RIS

TY - JOUR

T1 - Chemical treatment of highly toxic acid mine drainage at a gold mining site in Southwestern Siberia, Russia

AU - Bortnikova, Svetlana

AU - Gaskova, Olga

AU - Yurkevich, Nataliya

AU - Saeva, Olga

AU - Abrosimova, Natalya

PY - 2020/10

Y1 - 2020/10

N2 - The critical environmental situation in the region of southwestern Siberia (Komsomolsk settlement, Kemerovo region) is the result of the intentional displacement of mine tailings with high sulfide concentrations. During storage, ponds of acidic water with incredibly high arsenic (up to 4 g/L) and metals formed on the tailings. The application of chemical methods to treat these extremely toxic waters is implemented: milk of lime Ca(OH)2, sodium sulfide Na2S, and sodium hydroxide NaOH. Field experiments were carried out by sequential adding pre-weighed reagents to the solutions with control of the physicochemical parameters and element concentrations for each solution/reagent ratio. In the experiment with Ca(OH)2, the pH increased to neutral values most slowly, which is contrary to the results from the experiment with NaOH. When neutralizing solutions with NaOH, arsenic-containing phases are formed most actively, arsenate chalcophyllite Cu18Al2(AsO4)4(SO4)3(OH)24·36H2O, a hydrated iron arsenate scorodite, kaatialaite FeAs3O9·8H2O and Mg(H2AsO4)2. A common specificity of the neutralization processes is the rapid precipitation of Fe hydroxides and gypsum, then the reverse release of pollutants under alkaline conditions. The chemistry of the processes is described using thermodynamic modeling. The main species of arsenic in the solutions are iron-arsenate complexes; at the end of the experiments with Ca(OH)2, Na2S, and NaOH, the main species of arsenic is CaAsO4−, the most toxic acid H3AsO3 and AsO43−, respectively. It is recommended that full-scale experiments should use NaOH in the first stages and then Ca(OH)2 for the subsequent neutralization.

AB - The critical environmental situation in the region of southwestern Siberia (Komsomolsk settlement, Kemerovo region) is the result of the intentional displacement of mine tailings with high sulfide concentrations. During storage, ponds of acidic water with incredibly high arsenic (up to 4 g/L) and metals formed on the tailings. The application of chemical methods to treat these extremely toxic waters is implemented: milk of lime Ca(OH)2, sodium sulfide Na2S, and sodium hydroxide NaOH. Field experiments were carried out by sequential adding pre-weighed reagents to the solutions with control of the physicochemical parameters and element concentrations for each solution/reagent ratio. In the experiment with Ca(OH)2, the pH increased to neutral values most slowly, which is contrary to the results from the experiment with NaOH. When neutralizing solutions with NaOH, arsenic-containing phases are formed most actively, arsenate chalcophyllite Cu18Al2(AsO4)4(SO4)3(OH)24·36H2O, a hydrated iron arsenate scorodite, kaatialaite FeAs3O9·8H2O and Mg(H2AsO4)2. A common specificity of the neutralization processes is the rapid precipitation of Fe hydroxides and gypsum, then the reverse release of pollutants under alkaline conditions. The chemistry of the processes is described using thermodynamic modeling. The main species of arsenic in the solutions are iron-arsenate complexes; at the end of the experiments with Ca(OH)2, Na2S, and NaOH, the main species of arsenic is CaAsO4−, the most toxic acid H3AsO3 and AsO43−, respectively. It is recommended that full-scale experiments should use NaOH in the first stages and then Ca(OH)2 for the subsequent neutralization.

KW - Arsenic-containing tailings

KW - Milk of lime

KW - Mine water treatment

KW - Sodium hydroxide

KW - Sodium sulfide

KW - HEAVY-METAL IONS

KW - SCORODITE

KW - RESOURCE RECOVERY

KW - COPPER

KW - MECHANISMS

KW - sodium hydroxide

KW - REMEDIATION

KW - FERRIC IRON

KW - IMMOBILIZATION

KW - arsenic-containing tailings

KW - PRECIPITATION

KW - mine water treatment

KW - sodium sulfide

KW - ARSENIC REMOVAL

KW - milk of lime

UR - http://www.scopus.com/inward/record.url?scp=85091853672&partnerID=8YFLogxK

U2 - 10.3390/min10100867

DO - 10.3390/min10100867

M3 - Article

AN - SCOPUS:85091853672

VL - 10

SP - 1

EP - 23

JO - Minerals

JF - Minerals

SN - 2075-163X

IS - 10

M1 - 867

ER -

ID: 25689153