Department of Soil, Water and Environmental Science, 429 Shantz Bldg. #38, 1177 E. Fourth Street, University of Arizona, Tucson, AZ 85721-0038, USA.
Department of Soil, Water and Environmental Science, 429 Shantz Bldg. #38, 1177 E. Fourth Street, University of Arizona, Tucson, AZ 85721-0038, USA.
Sci Total Environ. 2018 Mar 15;618:357-368. doi: 10.1016/j.scitotenv.2017.11.010. Epub 2017 Nov 10.
Direct revegetation, or phytostabilization, is a containment strategy for contaminant metals associated with mine tailings in semiarid regions. The weathering of sulfide ore-derived tailings frequently drives acidification that inhibits plant establishment resulting in materials prone to wind and water dispersal. The specific objective of this study was to associate pyritic mine waste acidification, characterized through pore-water chemistry analysis, with dynamic changes in microbial community diversity and phylogenetic composition, and to evaluate the influence of different treatment strategies on the control of acidification dynamics. Samples were collected from a highly instrumented one-year mesocosm study that included the following treatments: 1) unamended tailings control; 2) tailings amended with 15% compost; and 3) the 15% compost-amended tailings planted with Atriplex lentiformis. Tailings samples were collected at 0, 3, 6 and 12months and pore water chemistry was monitored as an indicator of acidification and weathering processes. Results confirmed that the acidification process for pyritic mine tailings is associated with a temporal progression of bacterial and archaeal phylotypes from pH sensitive Thiobacillus and Thiomonas to communities dominated by Leptospirillum and Ferroplasma. Pore-water chemistry indicated that weathering rates were highest when Leptospirillum was most abundant. The planted treatment was most successful in disrupting the successional evolution of the Fe/S-oxidizing community. Plant establishment stimulated growth of plant-growth-promoting heterotrophic phylotypes and controlled the proliferation of lithoautotrophic Fe/S-oxidizers. The results suggest the potential for eco-engineering a microbial inoculum to stimulate plant establishment and inhibit proliferation of the most efficient Fe/S-oxidizing phylotypes.
直接植被恢复,或植物稳定化,是一种用于半干旱地区与矿山尾矿有关的污染物金属的遏制策略。硫化物矿石衍生尾矿的风化常常会导致酸化,从而抑制植物的建立,导致这些物质容易被风和水分散。本研究的具体目标是将硫化物矿山废物的酸化与微生物群落多样性和系统发育组成的动态变化联系起来,并评估不同处理策略对控制酸化动态的影响。本研究从一个高度仪器化的一年中尺度实验中采集了样本,该实验包括以下处理措施:1)未处理的尾矿对照;2)添加 15%堆肥的尾矿;以及 3)添加 15%堆肥并种植了滨藜的尾矿。在 0、3、6 和 12 个月时采集尾矿样本,并监测孔隙水化学,作为酸化和风化过程的指示。结果证实,含硫化物的矿山尾矿的酸化过程与细菌和古菌的时间序列有关,从对 pH 敏感的硫杆菌和硫单胞菌到主要由 Leptospirillum 和 Ferroplasma 主导的群落。孔隙水化学表明,当 Leptospirillum 最丰富时,风化速率最高。种植处理最成功地破坏了 Fe/S 氧化群落的演替进化。植物的建立刺激了植物生长促进异养型的生长,并控制了自养型 Fe/S 氧化菌的增殖。研究结果表明,有潜力通过生态工程接种微生物来刺激植物的建立并抑制最有效 Fe/S 氧化菌的增殖。