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Xiaoyuan Zhang, Shaoan Cheng, P. Liang, Xia Huang, B. Logan (2011)
Scalable air cathode microbial fuel cells using glass fiber separators, plastic mesh supporters, and graphite fiber brush anodes.Bioresource technology, 102 1
B. Logan, J. Regan (2006)
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B. Logan (2009)
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Shaoan Cheng, B. Logan (2007)
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Yong Luo, Renduo Zhang, Guangli Liu, Jie-ming Li, Mingchen Li, Cui-ping Zhang (2010)
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Yong Luo, Fang Zhang, Bin Wei, Guangli Liu, Renduo Zhang, B. Logan (2011)
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Fang Zhang, D. Pant, B. Logan (2011)
Long-term performance of activated carbon air cathodes with different diffusion layer porosities in microbial fuel cells.Biosensors & bioelectronics, 30 1
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Hong Liu, Shaoan Cheng, Liping Huang, B. Logan (2008)
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Hong Liu, Shaoan Cheng, B. Logan (2005)
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Liping Huang, Xi-lin Chai, Shaoan Cheng, Guohua Chen (2011)
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Sangeun Oh, B. Min, B. Logan (2004)
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Hong Liu, Shaoan Cheng, B. Logan (2005)
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B. Logan, Shaoan Cheng, Valerie Watson, Garett Estadt (2007)
Graphite fiber brush anodes for increased power production in air-cathode microbial fuel cells.Environmental science & technology, 41 9
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Liping Huang, Linlin Gan, Qingliang Zhao, B. Logan, Hong Lu, Guohua Chen (2011)
Degradation of pentachlorophenol with the presence of fermentable and non-fermentable co-substrates in a microbial fuel cell.Bioresource technology, 102 19
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The combined anaerobic–aerobic conditions in air‐cathode single‐chamber MFCs were used to completely mineralize pentachlorophenol (PCP; 5 mg/L), in the presence of acetate or glucose. Degradation rates of 0.140 ± 0.011 mg/L‐h (acetate) and 0.117 ± 0.009 mg/L‐h (glucose) were obtained with maximum power densities of 7.7 ± 1.1 W/m3 (264 ± 39 W/m2, acetate) and 5.1 ± 0.1 W/m3 (175 ± 5 W/m2, glucose). At a higher PCP concentration of 15 mg/L, PCP degradation rates increased to 0.171 ± 0.01 mg/L‐h (acetate) and 0.159 ± 0.011 mg/L‐h (glucose). However, power was inversely proportional to initial PCP concentration, with decreases of 0.255 W/mg PCP (acetate) and 0.184 W/mg PCP (glucose). High pH (9.0, acetate; 8.0, glucose) was beneficial to exoelectrogenic activities and power generation, whereas an acidic pH = 5.0 decreased power but increased PCP degradation rates (0.195 ± 0.002 mg/L‐h, acetate; 0.173 ± 0.005 mg/L‐h, glucose). Increasing temperature from 22 to 35°C enhanced power production by 37% (glucose) to 70% (acetate), and PCP degradation rates (0.188 ± 0.01 mg/L‐h, acetate; 0.172 ± 0.009 mg/L‐h, glucose). Dominant exoelectrogens of Pseudomonas (acetate) and Klebsiella (glucose) were identified in the biofilms. These results demonstrate that PCP degradation using air‐cathode single‐chamber MFCs may be a promising process for remediation of water contaminated with PCP as well as for power generation. Biotechnol. Bioeng. 2012;109: 2211–2221. © 2012 Wiley Periodicals, Inc.
Biotechnology and Bioengineering – Wiley
Published: Sep 1, 2012
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