Published November 15, 2013 | Version v1
Journal article

Arsenic mineral dissolution and possible mobilization in mineral–microbe–groundwater environment

  • 1. ITO Public Nuisance Research Institute, 1-26-8, Omori Kita, Otaku, Tokyo 142-0016 (Japan)
  • 2. Department of Human Ecology, School of International Health, Graduate School of Medicine, The University of Tokyo,7-3-1, Hongo, Bunkyo-ku, Tokyo 113-0033 (Japan)
  • 3. Department of Earth and Environmental Sciences, National Chung Cheng University, 168 University Road, Ming-Shung, Chiayi County 62102, Taiwan (China)
  • 4. Department of Earth Sciences, National Cheng Kung University, University Road, Tainan, 70101, Taiwan (China)
  • 5. KTH-International Groundwater Arsenic Research Group, Department of Land and Water Resources Engineering, Royal Institute of Technology (KTH) Teknikringen 76,SE-10044 Stockholm (Sweden)
  • 6. Faculty of Engineering and Surveying, University of Southern Queensland, Toowoomba, Queensland 435 (Australia)
  • 7. Department of Biotechnology, Graduate School of Agriculture and Life science, The University of Tokyo, 1-1-1,Yayoi, Bunkyo-ku, Tokyo 113-0033 (Japan)
  • 8. Department of Earth Sciences, Faculty of Science, Kanazawa University, Kakuma, Kanazawa, Ishikawa 920-1192 (Japan)

Description

Highlights: ► Bacteria use arsenic minerals for their growth without supplementary nutrient. ► Enzymatically active bacteria survive in the arsenic contaminated environment. ► Mostly bacillus, coccus and filamentous dissolves the arsenic mineral. ► Except enargite, soluble-As was detected with respect to other arsenic mineral. ► Dissolution: native-As > arsenolite > orpiment > realgar > arsenopyrite > tennantite. -- Abstract: Arsenic (As) is widely distributed in the nature as ores or minerals. It has been attracted much attention for the global public health issue, especially for groundwater As contamination. The aim of this study was to elucidate the characteristics of microbes in groundwater where As-minerals were dissolved. An ex situ experiment was conducted with 7 standard As-minerals in bacteria-free groundwater and stored in experimental vessels for 1 year without supplementary nutrients. The pH (6.7–8.4) and EhS.H.E. (24–548 mV) changed between initial (0 day) and final stages (365 days) of experiment. The dissolution of As was detected higher from arsenolite (4240 ± 8.69 mg/L) and native arsenic (4538 ± 9.02 mg/L), whereas moderately dissolved from orpiment (653 ± 3.56 mg/L) and realgar (319 ± 2.56 mg/L) in compare to arsenopyrite (85 ± 1.25 mg/L) and tennantite (3 ± 0.06 mg/L). Optical microscopic, scanning electron microscopic observations and flurometric enumeration revealed the abundance of As-resistant bacillus, coccus and filamentous types of microorganisms on the surface of most of As-mineral. 4′-6-Diamidino-2-phenylindole (DAPI)-stained epifluorescence micrograph confirmed the presence of DNA and carboxyfluorescein diacetate (CFDA) staining method revealed the enzymatically active bacteria on the surface of As-minerals such as in realgar (As4S4). Therefore, the microbes enable to survive and mobilize the As in groundwater by dissolution/bioweathering of As-minerals

Availability note (English)

Available from http://dx.doi.org/10.1016/j.jhazmat.2012.07.022

Additional details

Identifiers

DOI
10.1016/j.jhazmat.2012.07.022;
PII
S0304-3894(12)00729-7;

Publishing Information

Journal Title
Journal of Hazardous Materials
Journal Volume
262
Journal Page Range
p. 989-996
ISSN
0304-3894
CODEN
JHMAD9

Optional Information

Copyright
Copyright (c) 2012 Elsevier Science B.V., Amsterdam, The Netherlands, All rights reserved.