Nevertheless, it enabled the photoelectrochemical CO 2 reduction to formate within
an enzyme cascade that led to the methanol production at % 4 lMmin
−1
) [253].
The Methylobacterium extorquens AM1 NAD-dependent Cys-W-FDH has also
been exploited with different approaches to drive the electrochemical CO 2 reduction
[242, 254–258]. Using mediated enzymatic bioelectrocatalysis with gas diffusion
electrodes
15 , current densities of 15–20mAcm
−2 were attained [254, 255]; in a
whole-cell catalyst, M. extorquens was able to electrochemically produced formate
concentrations of up to 60 mM [242].
The R. capsulatus [182] and Cupriavidus oxalaticus [259] NAD-dependent Cys–
Mo–FDH enzymes, on the other hand, have k cat
CO
2 values, of 1.5 s
−1 and % 3 s
−1
,
respectively, but % 25 and % 30 times (respectively) lower than the one for formate
oxidation (R. capsulatus K m
HCOO−
% 280 lM and K m
CO
2 not determined, assays with
100 mM hydrogencarbonate; C. oxalaticus K m
HCOO−
% 100 lM and
K m
HCO3−
% 40 mM). The C. necator NAD-dependent Cys–Mo–FDH, on the contrary, catalyses the reduction of CO 2 with a k cat
CO
2 % 11 s
−1 (K m
CO
2 % 2.7 mM;
K m
NADH
% 45 lM) [260, 261]. To fulfil the potential industry application of this
oxygen-tolerant and robust enzyme, it is necessary to implement a NADH regenerating system that pushes the reaction towards CO 2 reduction (as discussed above; see
Footnote 14) [262]. With the C. necator FDH, this was successfully achieved with
the inclusion of glucose dehydrogenase in the system (Fig. 15), which, while catalysing the re-reduction of NAD
+ to NADH, enabled the continuous electron delivery
to drive the CO 2 reduction and, therefore, improved the reaction yield from 0.2 to 1.8
formate formed/NADH consumed [262].
The E. coli SeCys-Mo-FDH H was also shown to be able to reduce CO 2 [263],
but at rates considerably lower than the ones of formate oxidation, < 1 versus
160 s
−1 [263]. Interestingly, when the reaction is driven electrochemically (protein
film voltammetry), the formate oxidation was only two times higher than the CO 2
reduction, with current densities of 180 versus 80 lAcm
−2 , respectively [263]. This
E. coli enzyme feature has been exploited in fuel cell devices (FDH immobilised in
redox mediators-functionalised redox polymers) [15, 16], where CO 2 could be
reduced with a very high Faradaic efficiency (99%) and a current density of % 60
lAcm
−2
(K m
HCO3−
% 2.5 mM) [16]. Thanks to the FDH H-containing
formate-hydrogen lyase system (Sect. 4.2.2.)
16 , engineered E. coli whole cells
were also used as a “cell factory” to very efficiently produce formate from a gaseous
mixture of CO 2 and dihydrogen (56:44; up to 10 bar) (Fig. 16); an 100% of CO 2
conversion was achieved, with formate (more than 500 mM) being accumulated
outside the bacterial cells [264]. Intact E. coli cells were also used in a microbial
15 Gas diffusion electrodes (GDE) promote electrochemical reactions between the liquid and the
gaseous phase, thus eliminating the limitations arising from slow mass transport when
hydrogencarbonate/carbonate is used as CO 2 source.
16 Under physiological conditions the E. coli formate-hydrogen lyase system catalyses the
formate oxidation to CO 2 coupled to the reduction of protons to dihydrogen (Sect. 4.2.2.); yet,
under a pressurised (up to 10 bar) atmosphere of CO 2 and dihydrogen, engineered E. coli (with
abolished “respiratory” FDH, pyruvate-formate lyase and all major hydrogenases) whole cells
efficiently catalyse the reverse reaction of formate formation.
60
L. B. Maia et al.
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