Abstract

Mucor indicus with different morphologies was used for ethanol production and Pb2+ biosorption. With increasing Pb2+ concentration in the cultivation medium, the fungus morphology changed from purely filamentous to mostly filamentous and the biosorption capacity was increased. The maximum adsorption capacity predicted by Langmuir model was 118 mg/g for purely filamentous form. All morphologies were also cultivated in the presence of high Pb2+ concentration (300 mg/L) in consecutive stages. After the first stage of cultivation, the live biomass was separated and cultivated in a new medium similar to the first stage and cultivation was performed within five stages. All morphologies of M. indicus were able to grow and produce ethanol in the presence of lead at all stages but with lower yields than those cultivated in the absence of lead. The highest ethanol yields of 0.46 and 0.35 g ethanol per g consumed glucose were obtained by mostly filamentous morphology at the first and the last stages, respectively. The presence of lead decreased the glucose consumption rate of all morphologies and the yeast-like morphology consumed glucose within a shorter time than the other morphologies. Different morphologies were able to adsorb lead ions considerably (97–99%) within the five consecutive stages.

Highlights

  • Energy crises caused by shortage of oil sources, increasing emission of greenhouse gases (GHGs), and global warming have stimulated industrial countries to seek renewable sources of energy (Fasahati et al, 2015; Hosseinpour et al, 2016)

  • The fungus was inoculated with various spore concentrations under two different atmospheric conditions to obtain different morphologies of M. indicus

  • Similar morphologies under the same conditions were reported for M. indicus in the previous studies (Sharifia et al, 2008; Lennartsson et al, 2009)

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Summary

Introduction

Energy crises caused by shortage of oil sources, increasing emission of greenhouse gases (GHGs), and global warming have stimulated industrial countries to seek renewable sources of energy (Fasahati et al, 2015; Hosseinpour et al, 2016). There are several methods for heavy metals removal from wastewater, including chemical precipitation, membrane separation, ion exchange, and reverse osmosis (Guibal et al, 1992). All these conventional methods are expensive and inefficient at low metal ions concentrations (1–100 mg/L) (Majumdar et al, 2010). Adsorbents of biological origin have been considerably used for heavy metals removal, which are available, inexpensive, and effective for dilute streams (Yan and Viraraghavan, 2001; Shroff and Vaidya, 2012; Aryal and Liakopoulou-Kyriakides, 2014)

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