Abbas Syed Zaghum, Rafatullah Mohd, Ismail Norli, Shakoori Farah R
Division of Environmental Technology, School of Industrial Technology, Universiti Sains Malaysia 11800 Penang Malaysia
Department of Zoology, University of the Punjab New Campus Lahore Pakistan.
RSC Adv. 2018 May 23;8(34):18800-18813. doi: 10.1039/c8ra01711e. eCollection 2018 May 22.
The industrial contamination of marine sediments with chromium, copper and nickel in Penang, Malaysia was addressed with bio-remediation, coupled with power generation, using sediment microbial cells (SMFCs) under various conditions. The efficiency of aerated sediment microbial fuel cells (A-SMFCs) and non-aerated sediment microbial fuel cells (NA-SMFCs) was studied. The A-SMFCs generated a voltage of 580.5 mV between 50 and 60 days, while NA-SMFCs produced a voltage of 510 mV between 60 and 80 days. The cell design point for A-SMFCs was 2 kΩ, while for NA-SMFCs it was 200 Ω. In both SMFCs, the maximum current values relating to forward scanning, reverse scanning and oxidation/reduction peaks were recorded on the 80 day. The anode showed maximum additional capacitance on the 80 day (A-SMFC: 2.7 F cm; and NA-SMFC: 2.2 F cm). The whole cell electrochemical impedance using the Nyquist model was 21 Ω for A-SMFCs and 15 Ω for NA-SMFCs. After glucose enrichment, the impedance of A-SMFCs was 24.3 Ω and 14.6 Ω for NA-SMFCs. After 60 days, the A-SMFCs reduced the maximum amount of Cr(vi) to Cr(iii) ions (80.70%) and Cu(ii) to Cu(i) ions (72.72%), and showed maximum intracellular uptake of Ni(ii) ions (80.37%); the optimum remediation efficiency of NA-SMFCs was after 80 days toward Cr(vi) ions (67.36%), Cu(ii) ions (59.36%) and Ni(ii) ions (52.74%). Both SMFCs showed highest heavy metal reduction and power generation at a pH of 7.0. SEM images and 16S rRNA gene analysis showed a diverse bacterial community in both A-SMFCs and NA-SMFCs. The performance of A-SMFCs showed that they could be exercised as durable and efficient technology for power production and the detoxification of heavy metal sediments. The NA-SMFCs could also be employed where anaerobic fermentation is required.
马来西亚槟城海洋沉积物中铬、铜和镍的工业污染问题,通过生物修复结合发电来解决,具体是在不同条件下使用沉积物微生物电池(SMFCs)。研究了曝气沉积物微生物燃料电池(A - SMFCs)和非曝气沉积物微生物燃料电池(NA - SMFCs)的效率。A - SMFCs在50至60天之间产生了580.5 mV的电压,而NA - SMFCs在60至80天之间产生了510 mV的电压。A - SMFCs的电池设计点为2 kΩ,而NA - SMFCs的为200 Ω。在两个SMFCs中,与正向扫描、反向扫描和氧化/还原峰相关的最大电流值均在第80天记录。阳极在第80天显示出最大附加电容(A - SMFC:2.7 F/cm;NA - SMFC:2.2 F/cm)。使用奈奎斯特模型的全电池电化学阻抗,A - SMFCs为21 Ω,NA - SMFCs为15 Ω。葡萄糖富集后,A - SMFCs的阻抗为24.3 Ω,NA - SMFCs为14.6 Ω。60天后,A - SMFCs将最大量的Cr(vi)还原为Cr(iii)离子(80.70%),将Cu(ii)还原为Cu(i)离子(72.72%),并显示出对Ni(ii)离子的最大细胞内摄取量(80.37%);NA - SMFCs对Cr(vi)离子(67.36%)、Cu(ii)离子(59.36%)和Ni(ii)离子(52.74%)的最佳修复效率出现在80天后。两个SMFCs在pH值为7.0时均表现出最高的重金属还原和发电效率。扫描电子显微镜图像和16S rRNA基因分析表明,A - SMFCs和NA - SMFCs中均存在多样化的细菌群落。A - SMFCs的性能表明,它们可作为一种持久且高效的技术用于发电和重金属沉积物的解毒。NA - SMFCs也可用于需要厌氧发酵的地方。