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Sustainable Solutions for Environmental Pollution


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process. For instance, using electroactive bacteria (e.g., capable of converting volatile fatty acids to electrons, protons, and carbon dioxide) and electrodes in the EF system can alleviate the challenges, such as accumulation of short-chain volatile fatty acids (SCVFAs) (Lai et al., 2016b) and toxicants (e.g., nitrite, if nitrate is used as an electron acceptor) (Takeno et al., 2007), which are experienced by the conventional fermentation. With such advantages, EF systems present an emerging platform for future biorefinery for the synthesis of various value-added products from organic feedstocks. To date, the EF systems have been implemented for enhancing various biofuels and chemical productions, such as carboxylates, alcohols, solvents, lipids, acetoin, biopolymer, and many more (see Figure 1.1) (Bursac et al., 2017; Choi et al., 2014; Jiang et al., 2020; Lai and Lan, 2020; Liu et al., 2019; Mostafazadeh et al., 2016; Vassilev et al., 2018; Villano et al., 2017). This book chapter presents fundamental mechanisms, applied and scientific aspects of EF to produce different value-added products, and finally, perspectives for future development.

      As discussed earlier, in most cases, the reactions and electron transfers associated with EF are usually performed via syntrophic interactions between the fermentative bacteria and electroactive bacteria (Jiang et al., 2019; Moscoviz et al., 2016). However, sometimes, none of the fermentative bacteria are electroactive (e.g., Clostridium species), in which, the redox mediators, such as neutral red (Choi et al., 2012), methyl viologen (Kim and Kim, 1988), or ferricyanide (Xafenias et al., 2017) are required during the fermentation to impact the extracellular ORP (Choi et al., 2012; Kim and Kim, 1988; Sturm-Richter et al., 2015). When the redox mediators are introduced, they can first, be oxidized or reduced by the fermentative bacteria, then they are recycled or recovered electrochemically by the anode or cathode electrodes (Moscoviz et al., 2016). In this context, the redox mediators are used as electron shuttles, and this process is known as the mediated electron transfer (Gong et al., 2020; Rabaey and Rozendal, 2010; Thrash and Coates, 2008). Furthermore, other studies demonstrated another way to add a redox mediator in CEF, such as using produced H2 at the cathode that can be further used as a one-way electron shuttle (Gong et al., 2020; Xafenias et al., 2015; Zhou et al., 2013; Zhou et al., 2015).

      On the other hand, metabolically engineered fermentative bacterial strains are another feasible option, for instance, by adding the property of electroactivity (Moscoviz et al., 2016). This approach has been confirmed by adopting the strains (e.g., c-type cytochromes CymA, MtrA, STC) from electroactive bacteria (Shewanella oneidensis) to fermentative bacteria (Escherichia coli), where the electron transfer process can be greatly improved (e.g., by 183%) (Sturm-Richter et al., 2015). Alternatively, electroactive bacterial species (e.g., Shewanella oneidensis) can also be engineered to utilize a variety range of substrates and organic wastes to further aid the whole EF processes (Flynn et al., 2010).



Product Feedstock Inoculum System configuration Total working volume (L) Temperature (°C)/initial pH Applied voltage/potential Working electrode Reference
Butanol Glucose C. pasteurianum Dual chamber 900 37/6.7 0-2.6 V Cathode (Mostafazadeh et al., 2016)