4.7 Article

Effective treatment of acid mine drainage by constructed wetland column: Coupling walnut shell and its biochar product as the substrates br

Journal

JOURNAL OF WATER PROCESS ENGINEERING
Volume 49, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.jwpe.2022.103116

Keywords

Constructed wetland (CW) model; Acid mine drainage (AMD); Composite substrates; Metal precipitation; Microbial community

Funding

  1. National Natural Science Foundation of China [U2002208]
  2. China Yunnan Provincial R D Programs [202101AS070033, 2019BC001]
  3. Science and Technology Program of Yunnan Province, China [202201AT070182]
  4. Open Research Fund from Yunnan Key Laboratory for Plateau Mountain Ecology and Restoration of Degraded Environments [2018DG005]
  5. College Student Innovation and Entrepreneurship Program in Yunnan University [202004173]

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A novel constructed wetland (CW) system was established using walnut shell and its biochar product as substrates to treat acid mine drainage (AMD) with a pH of 4.0. The system efficiently removed heavy metals from the AMD and increased the pH, although the sulfate removal efficiency was unsatisfactory.
Acid mine drainage (AMD) can cause severe risks to the surrounding environment and ecosystems because of its high metal content and acidity and thus should be disposed of properly. In this study, a novel constructed wetland (CW) model system was established by packing a mixture of walnut shell (WS) and its biochar product as substrates to treat AMD with a pH of 4.0. Sucrose and plant straw broth (PSB) were successively supplemented as external carbon sources to fuel the bacterial sulfate reduction (BSR) process. Heavy metals in the AMD were efficiently removed in the CW column (Cu >99 %, Cd >97 %, Zn >94 %, Cr >93 % and Fe >76 %), and the pH increased from 4.0 to 6.5 despite an unsatisfactory sulfate removal efficiency (<40 %). Among the substrates, biochar exhibited a notably higher metal retention capacity, followed by WS. The relative abundance of sulfate- reducing bacteria (SRB) in the biochar substrate was the highest, followed by that in the WS. The cooperation of organic-degrading bacteria mainly consisting of Cellulomonas, Clostridium and Bacteroides and SRB consortia was responsible for biotic AMD treatment in the CW. A mixture of organic solid waste and biochar is a preferable filler candidate for CW systems treating AMD although further evaluation of its capacity under varying conditions is required

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