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Anodic vs cathodic potentiostatic control of a methane producing microbial electrolysis cell aimed at biogas upgrading

https://doi.org/10.1016/j.bej.2019.107393Get rights and content

Highlights

  • CO2 removal through Microbial electrolysis cell can be used for biogas upgrading.

  • CO2 removal in the MEC cathode is driven by CH4 generation and CO2 sorption.

  • The anodic fluid dynamics influences the process energy efficiency.

  • The shift of the potentiostatic control enhances the process energy efficiency.

  • No increase of CO2 removed is obtained at cathodic potential lower than −0.9 V vs SHE.

Abstract

A fully biological Microbial Electrolysis Cell (MEC) aimed at biogas upgrading has been operated under different operating conditions in order to enhance CO2 removal from a synthetic biogas. Specifically, CO2 reduction into CH4 occurred at the MEC biocathode with the oxidation of organic substrates in the anodic chamber partially sustaining the energy demand of the process. In the cathode chamber, methane formation was the main driver of current generation which, in turn, sustained alkalinity generation and related CO2 sorption. This study mainly focused on the minimization of the anodic and cathodic overpotentials to maximize the process efficiency. To accomplish this objective, an innovative strategy of MEC polarization was adopted, consisting in the shift of the potentiostatic control of the process from the anode (at +0.2 V vs SHE) to the cathode (at −0.65, −0.90 and −1.00 V vs SHE), along with the control of the fluid dynamic conditions of the anode chamber. An almost complete (99%) energy recovery was obtained by methane production with the cathode potential controlled at −0.65 V vs SHE. Finally, at the MEC cathode, current was utilized to reduce CO2 into CH4 (with a cathodic capture efficiency of about 70%) as well as to promote CO2 sorption into HCO3. The latter represents the main CO2 removal mechanism that accounted for 85% of the CO2 removal.

Introduction

Bioelectrochemical systems are innovative techniques that stand on the utilization of “electroactive” microorganisms as biocatalysts of electrochemical reactions. In particular, the ability of electroactive microorganisms to exchange electrons with a solid state electrode allowed the development of several bioelectrochemical devices with different applications in the environmental field, such as the electricity generation from wastewater treatment [1,2], the removal of target pollutants [[3], [4], [5]], the production of target molecules [6,7] or the desalinization of salty and brackish waters [8,9]. As for the anodic side of bioelectrochemical systems, the ability of exoelectrogens microorganisms on the degradation of organic compounds has been widely explored in the last 20 years [10,11], and the direct electron transfer from microbes to the electrode surface has been identified and characterized by the identification of specific c-type cytochromes or nanowire [[12], [13], [14]]. However, more recently, research on bioelectrochemical systems has been focused on the possibility to drive the cathodic reactions towards the production of target molecules by applying an external electric power [15,16]. As an example, biocathodes can be exploited for the conversion of CO2 into target molecules such as methane [17,18] and short chain volatile fatty acids by using an appropriate inoculum and an electricity source [19,20]. In this case, the bioelectrochemical system, commonly referred to as Microbial Electrolysis Cells (MEC) [21,22], permits to couple CO2 reduction to the generation of valuable products and the utilization of the surplus electricity energy production, giving the possibility to store part of the electrical energy into reduced chemical compounds such us hydrogen [23,24], methane [25]or acetate [26]. In this frame, several authors recently focused their attention on the development of methane producing MEC, the so called bioelectromethanogenesis as an innovative strategy to couple CO2 reutilization and the storage of the surplus electricity produced by renewable source [27,28]. The proposed approached was recently named as Bioelectro Power-to-Gas approach (BPTG) [29,30]. One of the main aspects of BPTG is the availability, for the electromethanogenesis reaction, of concentrated gaseous streams of CO2 from different industrial fields, and one of the most attractive CO2-rich stream is represented by the biogas deriving from anaerobic digestion processes [31]. Biogas is a gas mixture mainly composed by methane and CO2, which is typically utilized for the cogeneration of heat and electric power in stationary applications [32]. CO2 removal from biogas, also named upgrading process, permits to obtain biomethane, which has the same characteristics of natural compressed gas (CNG) and it can be used in automotive engines or injected into the distribution grid [33,34]. The possibility to use a biological approach [35], such as a methane producing MEC, as an innovative biogas upgrading approach has been proposed in the literature by several authors [[36], [37], [38]]. The integration of the anaerobic digestion with a methane producing MEC, has been widely proposed by several authors [39,40], which proposed both in situ and ex situ combination of the two technology. Recently, the main CO2 removal mechanisms in a biocathode have been identified, particularly the sorption of CO2 in the catholyte plays a pivotal role since it that permits the removal of up to 9 mol of CO2 for each mole of methane produced [41]. Indeed, the sorption mechanism is driven by the alkalinity generation in the cathodic chamber due to the ionic transport of different ionic species for the electroneutrality maintenance [42,43]. In the present work, a fully bio-catalyzed microbial electrolysis cell has been deeply studied testing different previously unexplored operating conditions in order to evaluate its performance in terms of both CO2 removal efficiency and energy efficiency. More in detail, the most innovative approach hereby proposed consists in the sequential polarization of the anodic and cathodic chamber of the MEC as a strategy to minimize the overall energy consumption [44]. Also, the anodic fluid dynamics conditions have been found to significantly affect the anode overpotentials and, as a consequence, the energy consumption of the overall process. Finally, three different cathodic potentials (i.e., −0.65, −0.90, and −1.0 V vs. the Standard Hydrogen Electrode) have been investigated to identify the best operating conditions which allow to enhance the process performance, in terms of methane production and CO2 removal, while simultaneously lowering the overall energy consumption.

Section snippets

Microbial electrolysis cell design and setup

The microbial electrolysis cell (MEC) here proposed consisted of two identical Plexiglas chambers bolted together between two Plexiglas plates [45]. The two chambers, representing the anodic and cathodic compartment, were characterized by an internal volume of 0.86 L and separated by a pretreated Fumasep FAD anion exchange membrane (AEM) (Fig. 1).

Each MEC compartment was firstly filled with graphite granules, characterized by a diameter ranging from 2 to 6 mm (El Carb 100, Graphite Sales, Inc,

MEC Start-up and potentiostatic control of the anode @+0.20 V vs. SHE

After the inoculation of the anodic and cathodic chambers, the anode was poised at + 0.20 V in order to promote the selection of electroactive microorganisms able to use graphite electrodes as electron acceptor to oxidize the organic matter. To enhance the electroactive-biomass growth, acetate was continuously fed in the anodic chamber and after 20 days of operation, the electroactivity of the biomass was shown by electricity production. During the start-up period, a hydraulic retention time

Conclusions

An MEC aimed at biogas upgrading has been operated for almost 200 days under a wide range of operating conditions. The analysis of the process performance in terms of CO2 removal and energy efficiency, showed the possibility to minimize the energy consumption of an MEC aimed at biogas upgrading by both controlling the fluid dynamics of the anode chamber as well as shifting the potentiostatic control of the process form the anode to the cathode. The best condition in terms of energy efficiency

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

The authors declare the following financial interests/personal relationships which may be considered as potential competing interests:

Acknowledgments

This work has been carried out with the financial support of the project WE-MET “Sustainable Wastewater treatment coupled to Energy recovery with Microbial Electrochemical Technologies” (ERANET_NEXUS-14-035).

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