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Systematic Full-Cycle Engineering Microbial Biofilms to Boost Electricity Production in Shewanella oneidensis
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Feng Li1, 2, Rui Tang1, 2, Baocai Zhang1, 2, Chunxiao Qiao1, 2, Huan Yu1, 2, Qijing Liu1, 2, Junqi Zhang1, 2, Liang Shi3, Hao Song1, 2, *
Research. Vol 6 Article ID 0081
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Research. Vol 6 Article ID 0081
• Research Article •
Systematic Full-Cycle Engineering Microbial Biofilms to Boost Electricity Production in Shewanella oneidensis
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Feng Li1, 2, Rui Tang1, 2, Baocai Zhang1, 2, Chunxiao Qiao1, 2, Huan Yu1, 2, Qijing Liu1, 2, Junqi Zhang1, 2, Liang Shi3, Hao Song1, 2, *
Affiliations
  • 1Frontiers Science Center for Synthetic Biology (Ministry of Education), and Key Laboratory of Systems Bioengineering, Tianjin University, Tianjin 300072, China.
  • 2Collaborative Innovation Center of Chemical Science and Engineering (Tianjin), School of Chemical Engineering and Technology, Tianjin University, Tianjin 300072, China.
  • 3Department of Biological Sciences and Technology, School of Environmental Studies, China University of Geoscience in Wuhan, Wuhan, Hubei 430074, China.
About Author:

† These authors contributed equally to this work.

Published: 2023-03-20 doi: 10.34133/research.0081
Outline
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Electroactive biofilm plays a crucial rule in the electron transfer efficiency of microbial electrochemical systems (MES). However, the low ability to form biofilm and the low conductivity of the formed biofilm substantially limit the extracellular electron transfer rate of microbial cells to the electrode surfaces in MES. To promote biofilm formation and enhance biofilm conductivity, we develop synthetic biology approach to systematically engineer Shewanella oneidensis, a model exoelectrogen, via modular manipulation of the full-cycle different stages of biofilm formation, namely, from initial contact, cell adhesion, and biofilm growth stable maturity to cell dispersion. Consequently, the maximum output power density of the engineered biofilm reaches 3.62 ± 0.06 W m−2, 39.3-fold higher than that of the wild-type strain of S. oneidensis, which, to the best our knowledge, is the highest output power density that has ever been reported for the biofilms of the genetically engineered Shewanella strains.

Feng Li, Rui Tang, Baocai Zhang, Chunxiao Qiao, Huan Yu, Qijing Liu, Junqi Zhang, Liang Shi, Hao Song. Systematic Full-Cycle Engineering Microbial Biofilms to Boost Electricity Production in Shewanella oneidensis[J]. Research, 2023 , 6 (3) : 0081 - . DOI: 10.34133/research.0081
Electroactive biofilm formed by an intimate interfacing biocatalytic machinery of electroactive cells with electrodes plays a vital role in determining the performance of a wide variety of microbial electrochemical systems (MES), which are sustainable technologies for energy and chemicals production [1–5]. Extracellular electron transfer (EET) rate underlies the efficiency of electroactive biofilm [6,7]. However, the EET rate was restricted by the limited ability of biofilm formation and low conductivity of biofilm, rendering applications of MES unpractical [3,6,8–10].
Substantial efforts have been made to elucidate the fundamental molecular mechanisms of EET in biofilm and to optimize EET rate from the perspectives of engineering electroactive cells, optimizing electrode materials, and bioelectrochemical reactor design [7,8,11–20]. Shewanella oneidensis MR-1 is one of the most well-studied metal-reducing exoelectrogens, which can conduct EET via c-type cytochromes (c-Cyts) and flavins as electron shuttles or bound cofactors for outer-membrane c-Cyts (OM c-Cyts) [9,21]. On the basis of these 2 underlying EET mechanisms, a number of synthetic biology strategies were developed to enhance the EET rate in S. oneidensis, including broadening feedstock spectrum [22,23], increasing intracellular electron generation [7,12,24], optimizing conductive c-Cyts systems [14,25–27], and accelerating biosynthesis and secretion of electron shuttles [28,29], which mainly focus on increasing electron generation and promoting EET at a single-cell level. However, improvement of the EET rate between biofilm and electrode at a multicellular level has not been fully explored.
Electroactive biofilms are the conductive microbial communities embedded in a structured, complex, self-produced polymeric matrix on electrode surfaces, which deliver intracellular electrons onto electrode surfaces [30–33]. Previous efforts focused on improving the understanding of biofilm architecture and mechanisms by means of genetic engineering and random transposon insertion methods [34–42]. However, it remains unclear whether manipulation of the full-cycle biofilm formation process could facilitate the thickness and conductivity of electroactive biofilm.
To overcome the limited biofilm-forming ability and low biofilm conductivity of S. oneidensis, we engineered the formation, maturation, and dispersion of biofilm, a developmental and cycling process initiated by planktonic (free-living) microorganisms forming aggregates and/or transitioning to a surface-associated lifestyle undergoing 5 stages, namely, the initial contact stage (I), cell adhesion stage (II), biofilm growth stage (III), stable maturity stage (IV), and dispersion stage (V) (Fig. 1) [43–46]. In this study, we carried out synthetic biology strategies to engineer the initial contact, adhesion, growth, and stable maturity in the full-cycle biofilm development process to promote biofilm-forming ability and enhance the conductivity of S. oneidensis biofilm. To improve the biofilm-forming ability, we enhanced the affinity and coverage of the cell–electrode interfaces in the initial contact stage via regulating the hydrophobicity of extracellular polysaccharides, promoted the cell–cell adhesion in the adhesion stage via increasing the content of “conductive glue” extracellular DNA (eDNA), and increased the vertical extension of biofilm to reinforce a 3-dimensional (3D) structure in the growth stage via regulating the content of bis-(3-5)-cyclic dimeric guanosine monophosphate (c-di-GMP) to enhance the biofilm thickness. To further improve the biofilm conductivity, the synthesis of OM c-Cyts and riboflavin (RF) were strengthened to enhance EET rate of each cell of the natural electroactive biofilm in the stable maturity stage. Then, an engineered Shewanella-reduced graphene oxide (rGO)–carbon nanotubes (CNTs) 3D self-assembled conductive hybrid was constructed to increase the electron collection capacity and reduce internal resistance of an artificial electroactive biofilm in the maturity dispersion stage. The EET rate of the engineered biofilm is characterized by the generation of electricity in microbial fuel cells (MFCs). The output power density of the engineered biofilms was as high as 3.62 ± 0.06 W m−2. To the best our knowledge, this is the highest output power density for a biofilm of S. oneidensis, which is also 39.3-fold of that of S. oneidensis MR-1 (Table S1).
Interaction between microbial cells and electrode surfaces is the key of the initial contact stage of biofilm formation [47]. As the major constituent of extracellular matrix in biofilms, extracellular polysaccharides and agglutination proteins directly affect the hydrophilicity/hydrophobicity of cell surfaces and cell adhesion to electrode surface, respectively, which subsequently determines the biofilm coverage on the hydrophobic carbon electrode [48–50]. Thus, to improve the initial adhesion of bacterial cells to electrode surfaces, we constructed MS1, MS2, and MS12 strains by deleting the genes so1860, so3171, and both of them, respectively. According to previous studies on the comparative genomics of the wild-type (WT) S. oneidensis [51], the genes so1860 and so3171 were found to be involved in the biosynthesis of cell surface polysaccharides. Additionally, we constructed MP1, MP2, and MP3 strains by overexpressing aggA, rbmA, and saeP genes, respectively. The gene aggA was found to encode an extracellular agglutination protein that played a key role in cell aggregation and biofilm formation of S. oneidensis [52], the gene rbmA encoded an adhesive protein involved in facilitating intercellular adhesion during biofilm formation in a typical biofilm pathogen Vibrio cholerae [53], while the gene saeP encoded a membrane-attached lipoprotein required to anchor a cellular membrane that substantially impact biofilm development in the pathogen Staphylococcus aureus (Fig. 2A) [54]. The results showed that output power density decreased in the order of MS2 (634 ± 15.6 mW m−2) > MS1 (549.6 ± 17.2 mW m−2) > MS12 (490.7 ± 13.7 mW m−2) > MP1 (200.2 ± 11.6 mW m−2) ≈ MP2 (192.9 ± 9.4 mW m−2) > MP3 (180.2 ± 9.3 mW m−2) > WT (92 ± 6.5 mW m−2) of S. oneidensis MR-1 (Fig. 2B). Although the enhancement of extracellular agglutination proteins could increase cell-to-cell and cell-to-surface attachment and facilitate biofilm formation, the large amount of nonconductive proteins accumulated on cell surfaces may inhibit interaction between OM c-Cyts, electron shuttles, and electrode surfaces, thus preventing the transportation of electrons from exoelectrogenic cells to electrode surfaces [30,31]. Moreover, the accumulation of agglutination proteins attached on cell surfaces causes strong chemical gradients of nutrients within the biofilm, which would influence bacterial physiology and metabolism, thus limiting the enhancement of EET rate [55,56]. Confocal laser scanning microscope (CLSM) analyses revealed that the biofilm thicknesses of MS1, MS2, and MS12 were 1.4-, 1.7-, and 1.3-fold higher than that of WT, respectively, demonstrating that deletion of these genes enhanced biofilm formation (Fig. 2C). Scanning electron microscope (SEM) analyses also revealed that the cell coverage on the electrode surface by MS1, MS2, and MS12 were 2.9-, 3.0-, and 2.4-fold than WT, respectively (Fig. 2D).
Results of ruthenium red staining (a polysaccharides staining dye that could be visualized by transmission electron microscope (TEM)) and Congo red (a carbohydrate binding dye that inhibited fibril polymerization) assay indicated that the content of cell surface polysaccharides of the recombinant strains with high coverage were impaired (Fig. 2E and F). Analyses of water contact angle (θW) and the affinity of cells to hexadecane showed that cell surface hydrophobicity of strain MS2 was increased by 2-fold, which increased interaction between the cell and the hydrophobic electrode surface and cell coverage on electrode surfaces (Fig. 2G, Figs. S1 and S2, Table S2, and Eq. 2). These results were in agreement with a previous study that concluded that cell surface hydrophobicity influenced the adhesiveness of S. oneidensis cells to graphite felt electrodes [57]. Consequently, the biomass attached on the anode surface of strain MS2 increased by 1.7-fold, as compared to that of WT (Fig. 2H). To further assess the effect of accumulated cells on biofilm electroactivity, we compared the electron accepted capacity (EAC) and the electron donated capacity (EDC) for strains MS1, MS2, MS12, and WT. As compared with WT, the EAC and the EDC of MS2 were increased by 131% and 61%, respectively, which showed enhanced EET capability and higher electrocatalytic activity (Fig. 2I). Similar results were also obtained with strains MS1 and MS12. Collectively, our results suggested that increase of cell surface hydrophobicity strengthened interaction between cells and electrode surfaces, which increased the cell coverage on electrode surfaces, promoted biofilm formation, and consequently enhanced EET rate.
eDNA stabilizes cell–cell interaction and structural integrity of biofilm matrix [58–61]. In addition to the structural role in biofilm, eDNA was also demonstrated to be a potential nutrient, antimicrobial agent, and reservoir for gene transfer [58,62,63]. Under natural conditions, microbial cells can release nucleases to utilize nutrient [64], control biofilm dispersion, defend themselves from extracellular traps [65], and prevent biofilm formation of other pathogens [66]. However, extracellular endonucleases secreted by cells degrade the eDNA and slow the rate of biofilm formation [43,58,62,63,67]. To increase the level of eDNA in biofilms, we constructed ME1, ME2, and ME12 strains in which the extracellular endonuclease genes exeS, exeM, and exeS/exeM were deleted, respectively (Fig. 3A) [63]. ME1, ME2, and ME12 all exhibited more eDNA in biofilms and generated higher output power density (i.e., 515 ± 19.4, 229 ± 12.7, and 271 ± 11.2 mW m−2, respectively) than that of the WT (92 ± 6.5 mW m−2) (Fig. 3B and C). As previous reported, many electron shuttling small molecules, such as pyocyanin (PYO), exhibit eDNA binding capacity to be retained in biofilm, thus promoting rapid electron transfer [28,68]. Given that electron transfer occurs rapidly, while loss of electron shuttling small molecules retained by eDNA to the environment is slow, eDNA promotes efficient electron transfer in biofilm [28]. Thus, the increased levels of eDNA in biofilms substantially enhance the EET rate of microbial biofilms to electrode surfaces. CLSM and SEM analyses revealed that the biofilm thickness and coverage on electrode surfaces decreased in the order of ME1 (155 μm) > ME12 (135 μm) > ME2 (125 μm) > WT (120 μm) (Fig. 3D). These results were consistent with colony morphology observations (Fig. S3).
We further found that the viscosity of the biofilm of ME1, ME2, and ME12 was significantly enhanced by 4.36-, 1.67-, and 2.77-fold over WT, respectively (Fig. 3E), verifying that improving cell–cell interaction forces by accumulating eDNA in the adhesion stage indeed facilitated biofilm formation of S. oneidensis. To analyze the effect of the thermodynamic properties of eDNA accumulation on cell−cell interaction forces, we further calculated and evaluated the interfacial interaction energy (ΔGbwb; Eq. 5) of ME1 [69]. The negative surface free energy of ME1 (−15.18 ± 0.87 mJ m−2) and ME12 (−2.71 ± 0.79 mJ m−2) indicated that the cell–cell interaction of ME1 and ME12 was stronger and more conducive to cell aggregation than that of ME2 (8.23 ± 0.62 mJ m−2) and WT (23.49 ± 0.90 mJ m−2) (Fig. 3F, Figs. S4 and S5, and Table S3). CLSM co-localization images and DNA-binding assay demonstrated that eDNA of ME1 exhibited a stronger bind with polysaccharides and proteins in extracellular polymeric substances (EPS) than that of WT, thus increasing the cell–cell interaction forces and promoting biofilm formation (Fig. 3G and H). Consequently, the biomass attached on the anode surface of ME1, ME2, and ME12 increased by 1.62-, 1.19-, and 1.32-fold, as compared to that of WT, respectively (Fig. 3I). Coincidentally, the internal resistance of ME1, ME2, and ME12 reduced to 26%, 51%, and 43% of WT, respectively (Fig. 3J). With the decrease in internal resistance of the electroactive biofilm, the EAC and EDC of strain ME1 increased by 50% and 44%, as compared to that of WT, respectively (Fig. 3K and Eqs. 6 and 7), which showed enhanced bidirectional electron transfer capability and electrocatalytic activity. Similar results were also obtained with strains ME2 and ME12. Collectively, our results demonstrate that the accumulation of eDNA in the biofilm of S. oneidensis improves biofilm formation via increasing the energy and viscosity of microbial cell–cell interaction energy while facilitating the electron transfer in biofilm. This enhances the EET rate of microbial biofilms to the electrode surfaces.
During the growth stage of biofilm formation, microbial biofilm grows from a monolayer to a 3D structure. c-di-GMP, which is hydrolyzed by phosphodiesterases [70,71], regulates the 3D growth of biofilms. According to previous studies on the comparative genomics of the WT S. oneidensis [72], we constructed MG1 strain by deletion the gene so1942 encoding c-di-GMP hydrolases in S. oneidensis MR-1 to increase the c-di-GMP level (Fig. 4A). MG1 with higher intracellular c-di-GMP level exhibited higher output power density (592 ± 13.1 mW m−2) than that of WT (92 ± 6.5 mW m−2) (Fig. 4B and C). We wondered whether further increase in the accumulation of c-di-GMP would further increase the output power density. In view of this, we constructed MG2 and MG3 strains by deletion another 2 phosphodiesterases (namely, so3491 and so4711) sequentially. The output power density decreased in the order of MG2 (662 ± 10.8 mW m−2) > MG1 (592 ± 13.1 mW m−2) > MG3 (479 ± 11.6 mW m−2) > WT (Fig. 4B), while the intracellular c-di-GMP level decreased in the order of MG2 > MG1 ≈ MG3 > WT (Fig. 4C). Thus, increase of intracellular c-di-GMP level improves output power density.
CLSM analyses revealed that the biofilm thickness and furrows depth of MG1, MG2, and MG3 were 1.5-, 1.7-, and 1.6-fold higher than that of WT (120 μm), respectively (Fig. S6A), demonstrating that c-di-GMP accumulation was conducive to the development of a vertical extension structure in biofilm formation. Three-dimensional fluorescence spectrum comparison further verified that the accumulation of c-di-GMP increased the biofilm matrix content, which promoted the development of vertical extension structure (Fig. 4D and Fig. S7). Moreover, we observed that high intracellular c-di-GMP level inhibited flagella formation and promoted pili formation by analyzing piliation at single-cell level using TEM (Fig. 4E). Strains MG1, MG2, and MG3 showed more pili and less flagellar than that of WT. Analysis of flagellar and pili gene expression by quantitative reverse transcription polymerase chain reaction (qRT-PCR) revealed that the relative expression of flagellar genes in strain MG2 was decreased from 40% to 60%, while pili genes were significantly increased by 1.5- to 1.8-fold than that of the WT (Fig. 4F). These results were consistent with colony morphology observations (Fig. S6B). Thus, the high c-di-GMP level decreased the strain motility by down-regulating flagella expression and promoted strains twitching on electrode surface by up-regulating pili expression, which consequently enhanced biofilm formation.
Consequently, the biomass attached on the anode surface of MG1, MG2, and MG3 increased by 1.3-, 1.7-, and 1.4-fold, as compared to that of WT, respectively (Fig. S6C). Moreover, the accumulation of c-di-GMP positively regulated the expression of c-Cyts involved in the EET conduits of S. oneidensis (Fig. 4G). This result was consistent with a previous study, which found that the cells with elevated c-di-GMP were more conductive than that with low c-di-GMP [73]. Coincidentally, the internal resistance of MG1, MG2, and MG3 reduced to 30%, 28%, and 34% of that from WT, respectively (Fig. 4H). The decrease in internal resistance of MG2 resulted in an increase of 2.05-fold in EAC and 1.85-fold in EDC, as compared to that of WT (Fig. S6D and Eqs. 6 and 7), suggesting a high electron transfer rate between electroactive cells and electrode surfaces. Similar results were also obtained with strains MG1 and MG3. Coincidentally, the accumulation of c-di-GMP strengthened the development of vertical extension structure in biofilm formation by increasing biofilm matrix secretion, inhibiting flagella formation, and facilitating pili formation, which consequently led to enhanced EET rate.
Given that individual deletion of these genes (so3171 encodes cell surface polysaccharide biosynthesis enzymes, exeS encodes extracellular endonucleases, and genes so1942 and so3491 encode c-di-GMP hydrolases) all substantially increased the biofilm formation and conductivity of formed biofilms, we constructed strains SG and SEG in which the genes so3171/so1942/so3491 and so3171/exeS/so1942/so3491 were inactivated, respectively (Fig. 5A and Fig. S8). However, SEG displayed impaired ability for growth and electricity production as compared to SG and WT (Fig. S9), in which the knockout of the gene exeS would cause detriment to cell growth. To circumvent the difficulty associated with SEG, an alternative strain SErG with antisense RNAs expressed in strain SG was used for down-regulating the expression of the gene exeS. The output power density of SErG in MFC was 781 ± 16.5 mW m−2, which was higher than that of SG and WT (Fig. 5B).
The biofilm formation of SErG and WT were compared with CLSM. As shown in Fig. 5C, the cell coverage on the electrode surface of SErG was significantly higher than that of WT at 12, 24, and 48 h after biofilm formation. At 96 h after biofilm formation, SErG exhibited much deeper vertical extension and thicker biofilm than WT. In addition, the c-Cyts level of strain SErG was increased by 2.2-fold, as compared to that of WT (Fig. 5D). Coincidentally, the internal resistance of strain SErG reduced to 26% of that from WT (Fig. 5E), which resulted in an increase of 2.41-fold in EAC and 2.03-fold in EDC, as compared to that WT (Fig. 5F and Eqs. 6 and 7). Thus, combinatorial engineering biofilms substantially increases biofilm thickness and conductivity.
The cell surface exposed cytochromes of Shewanella can act as terminal reductases for external electron-accepting surfaces or intermediary for soluble redox shuttles [74]. However, the inefficient OM c-Cyts system limited the EET rate of S. oneidensis [26]. To increase the EET rate, 3 exogenous OM c-Cyts (OmcC and OmcE of Geobacter sulfurreducens and MtoA of Sideroxydans lithotrophicus) were expressed in SErG, which resulted in SErGC, SErGE, and SErGA, respectively (Fig. 6A). As shown in Fig. 6B, the output power density SErGC, SErGE, and SErGA were 1,002 ± 19.5 mW m−2, 843 ± 17.7 mW m−2, and 638 ± 18.3 mW m−2, respectively, while that for SErG was 781 ± 16.5 mW m−2. Ultraviolet (UV)-visible spectroscopy demonstrated the high expression level of c-Cyts in strains SErGC, SErGE, and SErGA (Fig. 6C). We also calculated the cyclic voltammetry curves (Fig. 6D). The peak current density of SErGC was much higher than that of WT, indicating that more redox species were involved in EET of SErGC. On the basis of Laviron equation (Eq. 8), the calculated average density (or activity) of the OM c-Cyts on the MFC anode with SErGC was 137.61 ± 5.5 μmol m−2 (Fig. 6D), which was 3.1-fold higher that of WT (44.35 ± 3.7 μmol m−2). Thus, overexpression of OM c-Cyts genes omcC resulted in more OM c-Cyts for EET, which may contribute to the improved MFC performance and enhanced direct contact-based catalytic current. However, OM c-Cyts are membrane protein, which would be toxic to the host by strongly heterologous overexpression [13]. As shown in Fig. 6E, heterologous overexpression of OmcC resulted in a lower optical density at 600 nm (OD600) of SErGC than that of WT (Fig. 6E). Thus, we further optimized the ribosome binding site (RBS) sequence to control the translational level of omcC in S. oneidensis. As shown in Fig. 6F, we identified a weak RBS32 (BBa_B0032, iGEM). Change of original RBS with RBS32 resulted in strain SErGC3. The maximum output power density of SErGC3 was 1,176.2 ± 20.4 mW m−2, which was ~12.8-fold higher than that of WT. Most importantly, SErGC3 grew as normally as WT (Fig. 6E). These results clearly demonstrate that the optimized expression of the omcC substantially improves the EET rate to electrodes.
Endogenous electron shuttles flavin mononucleotide (FMN) and RF facilitate EET of S. oneidensis [8,74]. To increase the level of flavins in S. oneidensis, the synthetic flavin biosynthesis gene cluster ribADEHC from Bacillus subtilis was incorporated into SErGC3, resulting in the SErGC3F (Fig. 7A). The flavins yield of strain SErGC3F was ~10-fold higher than that of SErGC3 and WT (Fig. 7B). Meanwhile, the maximum output power density of SErGC3F was 3,073.8 ± 42.1 mW m-2, which was 2.6- and 33.4-fold higher than that of SErGC3 and WT, respectively (Fig. 7C). The internal resistance of SErGC3F reduced to 23% of that of WT (Fig. 7D). The decreased internal resistance resulted in an increase of 2.96-fold in EAC and 2.28-fold in EDC, as compared to that of WT (Fig. 7E and Eqs. 6 and 7). Thus, the improvement of output power density is related to the accumulation of flavin electron shuttles, which is consistent with the Fick’s law (Eq. 9). The output power density of SErGC3F was also higher than that of SErGC3 (Figs. 6B and 7C), which suggested that EET was substantially improved by combinatorial synthesis of cytochromes and electronic shuttles.
As shown in Fig. 7F, the output voltage of MFCs with a multicycle operation revealed that SErGC3F exhibited stable power generation with a maximum voltage of 548.3 ± 10.4 mV, which was much higher than that of the WT (95.3 ± 3.2 mV). The Coulomb efficiency increased by 6.7-fold from 3.7% (WT) to 24.8% (SErGC3F). These results suggest that the biofilms SErGC3F transfer more electrons to electrodes than that of WT (Fig. 7G and Eq. 1).
To further improve the Coulomb efficiency, we employed graphene oxide (GO) to construct an artificial 3D self-assembled artificial biofilm (Fig. 8A). In this artificial biofilm, the bacterial cells were captured by the GO nanosheets by a “fishing” process, where the GO nanosheets acted as nets to catch the bacterial cells. The GO nanosheets were then reduced to rGO by SErGC3F, which self-assembled to form a 3D macroporous conductive network (rG/SErGC3F artificial biofilm). The aggregations were, however, observed in the artificial biofilm of rG/SErGC3F (Fig. S10). These irreversible agglomerates might be formed by π–π stacking between the rG/SErGC3F sheets during the reduction process, which resulted in substantial reduction of surface area [75]. To circumvent this difficulty, we added CNTs to prevent the SErGC3F-G sheets from aggregation. Consequently, artificial biofilm rGC/SErGC3F with 3D conductivity and hierarchical porous was formed. The artificial biofilm rGC/SErGC3F was analyzed by Raman spectra, Fourier transform infrared spectroscopy (FTIR), and x-ray photoelectron spectroscopy (XPS). The Raman and FTIR results showed a structural change upon the reduction of GO by SErGC3F and the attachment of flavins onto rGO (Fig. 8B and C). XPS results confirmed the formation of rGO artificial biofilm (Fig. 8D).
The lactate metabolic rate of artificial biofilm rGC/SErGC3F was 2.2 ± 0.01 mM d−1, which was 2-fold higher than that of WT (1.1 ± 0.01 mM d−1) (Fig. 8E). The increased mass transfer efficiency promoted the cell metabolism and growth. As a result, the measured biomass for artificial biofilm SErGC3F-GC was 1.2- and 1.5-fold than that of artificial biofilm SErGC3F and the WT, respectively (Fig. 8F). The living cells in the biofilm increased by 2.5-fold, as compared to that of the WT (Fig. 8F). Therefore, the construction of artificial biofilm rGC/SErGC3F reduced the spatial and chemical heterogeneity and promoted the formation of biofilm. As revealed by CLSM images, the thickness of artificial biofilm rGC/SErGC3F was 305 μm, which was 2.5-fold higher than that of WT (120 μm) (Fig. 8G). In addition to enhancing EET through increased mass transfer efficiency near the electrode for adhering more bacteria and assisting the formation of dense biofilm, the rGO–biofilm hybrid can also generate and enrich local electron shuttles at a higher concentration around the anode and decreased the diffusion distance of electron shuttles. The maximum output power density of artificial biofilm rGC/SErGC3F was 3620 ± 56.2 mW m−2, 39.3-fold higher than that of WT (92 ± 6.5 mW m−2) (Fig. 8H), which is, to the best our knowledge, the highest output power density that has ever been reported in engineered electroactive biofilm of Shewanella (Table S1). Additionally, the internal resistance of artificial biofilm rGC/SErGC3F reduced to 18% of that of WT (Fig. 8I). The decreased internal resistance of electroactive biofilm resulted in increase of 3.8-fold EAC and 2.9-fold EDC, as compared to that of WT (Fig. 8J and Eqs. 6 and 7). The decreased internal resistance and the increased EAC and EDC values reflect the high electron collection of artificial biofilm rGC/SErGC3F and the formation of a stable electron transfer network. Therefore, the artificial biofilm rGC/SErGC3F exhibited stable power generation with a maximum voltage of 658.1 ± 9.6 mV and a maximum Coulomb efficiency of 30.7%, which were 6.9- and 8.3-fold higher than that of WT, respectively (Fig. S11). Together, these construct artificial conductive channels in rGC/SErGC3F 3D self-assembled artificial biofilm improve electron transfer in biofilm and electron transfer from biofilms to the anode surfaces and diminish the dispersion stage of biofilm.
We rationally designed an artificially electroactive biofilm with high electrical conductivity. This was carried out via systematic engineering biofilms to promote biofilm forming ability and enhance biofilm conductivity from the full-cycle perspective. It included improvement of cell membrane hydrophobicity by improving the interactions between microbial cells and electrode surfaces in the initial contact stage. Accumulation of eDNA was then increased to improve cell–cell interaction forces and structural integrity of biofilm in the adhesion stage. The c-di-GMP level was also increased to reinforce the vertical extension and 3D structure formation of biofilm in the growth stage. By strengthening biofilm formation, the output power density was improved from 92 ± 6.5 mW m−2 (WT) to 781 ± 16.5 mW m−2. Synthesis of OM c-Cyts and RF was strengthened to enhance EET rate of biofilm in the stable maturity stage, leading to an output power density of 3,073.8 ± 42.1 mW m−2 (33.4-fold higher than the WT). On the basis of this, an engineered rGC/SErGC3F 3D self-assembled artificial biofilm was further constructed to increase the electron collection capacity and reduce internal resistance of artificial electroactive biofilm in maturity dispersion stage, resulting the highest record of the output power density 3.62 ± 0.06 W m−2 (39.3-fold higher than the WT), which is, to the best our knowledge, the highest record in engineered S. oneidensis biofilms ever reported. Such artificial electroactive biofilm would lay a foundation for practical applications of electrocatalytic systems in the fields of energy, chemical industry, environments, and bioelectronics.
The sequences of the gene aggA of S. oneidensis, the gene rbmA of V. cholerae, the gene saeP of S. aureus, the genes omcC and omcE of G. sulfurreducens, the gene mtoA of S. lithotrophicus, and the gene ribACDEH of B. subtilis were obtained from the National Center for Biotechnology Information database (Table S7) and expressed in S. oneidensis with codon optimization as previously reported [7]. The information of so_1860, so_3171, exeS, exeM, so_1942, so_3491, and so_4711 genes of S. oneidensis were extracted from the National Center for Biotechnology Information database. The designed gene sequences were synthesized by GENEWIZ in vitro (Suzhou, China).
The strains used in this study are listed in Table. All plasmid constructions were performed in Escherichia coli WM3064 (auxotroph), with 100 μg ml−1 of 2,6-diaminopimelic acid and 50 μg ml−1 of kanamycin added when needed. The obtained genes were assembled into pYYDT as previously constructed in our laboratory [76]. The constructed plasmid was first transformed into E. coli WM3064, a plasmid donor strain. Then, conjugation of plasmid donor strain and S. oneidensis was employed to obtain engineered S. oneidensis. The gene mutant strains of S. oneidensis were constructed using the att-based fusion PCR method [77,78].
To evaluate the capacity of EET, the overnight culture suspension of S. oneidensis was inoculated into fresh Luria–Bertani (LB) broth at 1% inoculum and incubated at 30 °C, 200 rpm, until the OD600 reached ∼2.0. The harvested cells were washed thrice with fresh M9 buffer and subsequently resuspended in 140 ml of electrolyte (M9 buffer was supplemented with 5% LB, 20 mM lactate, 0.5 mM isopropyl-β-d-thiogalactopyranoside, and 50 μg ml−1 of kanamycin). Dual-chamber MFCs (140-ml working volume) were separated using Nafion 117 membranes (DuPont Inc., USA). Carbon cotton was used as the electrodes for the anode (1.0 cm × 1.0 cm) and carbon cloth for cathode (2.5 cm × 3 cm). The cathodic electrolyte was prepared with 50 mM K2HPO4, 50 mM KH2PO4, and 50 mM K3[Fe(CN)6]. The voltage was measured across a 2-kΩ external resistor in the external circuit and recorded using a multimeter (DT9205A).
CNT was adsorbed to the anode by soaking and drying repeatedly. S. oneidensis cell suspension was added according to the method in BES setup and dispersed into the modified anodes. Then, the anode chamber was added with GO to 0.2 mg ml−1, purged with N2 gas, and stirred at 30 °C, 50 rpm to prepare the 3D artificial biofilm. The Raman spectrometer (Horiba, France) with a 632-nm laser source, FTIR spectrometer (MKS6030, MKS), and XPS measurements (ThermoFisher K-Alpha, USA) with a monochromated AlKα radiation were performed after the output voltage of MFC stabilized.
Cyclic voltammetry analysis with a scan rate of 1 mV s−1 and electrochemical impedance spectroscopy (EIS) analysis were performed on a CHI 1000C multichannel potentiostat (CH Instrument, Shanghai, China) in a 3-electrode configuration, and an Ag/AgCl was used as reference electrode. EIS was conducted at a set potential equal to the OCP, with a sinusoidal perturbation of 5-mV amplitude, over a frequency range of 10 mHz to 100 kHz.
The Coulomb efficiency (CE) is defined as a ratio of the Coulombs recovered by the actual current to maximum possible Coulombs of current produced by all substrate consumption [79] as Eq. 1:
CE=Coulombs recoveredTotal coulombs in substrate=MS∫0tbIdtFbESVAn△c=MSItbFbESVAn△c
where Ms is 90.08 g mol−1 (lactate molecular weight), F is 98,485 C mol−1 of electrons (Faraday’s constant), V is 0.14 l (the liquid volume of anode compartment), bES is 4 (the stoichiometric number of moles of electrons produced per mole of lactate), tb (s) is the period of a batch cycle, I (A) is the current, Δc (g l−1) is the change in substrate concentration over time tb.
Anode biofilms were harvested and washed thrice with phosphate-buffered saline (PBS) (pH 6.8). Then, confocal images of anode biofilm were observed using LIVE/DEAD BacLight Bacterial Viability Kit (Invitrogen, U.S.A.) and CLSM (Nikon A1R+) and were analyzed by the Nikon A1R+ software with laser wavelengths of 488 and 561 nm. For the observation of EPS, fluorescein isothiocyanate and concanavalin were used for staining the extracellular protein and extracellular polysaccharide, respectively.
The anode carbon cotton was harvested from operating MFCs and fixed in 2.5% glutaraldehyde for 12 h. The anode carbon cotton was subsequently dehydrated in different concentration gradients of ethanol solution (30%, 50%, 70%, 80%, and 90%) and vacuum-dried overnight. The imaging of the anode biofilm was characterized by SEM (S-4800, Hitachi) with 3-kV acceleration voltage. Samples were divided into small pieces and coated with Au before the SEM observing.
To determine the protein content of the anode biofilm, the anode carbon cotton was vortexed in 3-ml PBS for 2 min and then incubated 20 min at 96 °C to lyse cells. Bicinchoninic acid (BCA) protein assay kit (Solarbio, China) was used for the test of extracts according to the manufacturer’s instructions with 1 mg ml−1 of bovine serum albumin as standard.
Shewanella cells were inoculated onto Congo red plates containing 0.01% (wt vol−1) Congo red and 1.5% (wt vol−1) agar. After growth at 30 °C for 3 d, clearing zones were measured around colonies.
Shewanella cells were harvested from the anode biofilm for preparing ruthenium red-stained samples and were fixed and stained for 5 h at 4 °C as previously reported [72]. Then, the cells were washed with 0.1 M cacodylate buffer (pH 6.5) before a buffer containing 1% osmium tetroxide and 0.05% ruthenium red were being used to postfix at 4 °C for 2 h. The cells were embedded in 1.5% agarose after rinsing with the cacodylate buffer, and a graded ethanol series was used for dehydration. The cells without ruthenium red staining were performed as control. The dehydrated blocks of both experimental group and control group were embedded in Spurr resin. Before staining with lead citrate and uranyl acetate, ultrathin sections were prepared using an ultramicrotome and then fixed on copper meshes. The images of cell were obtained by TEM at 75 kV (H-7000, Hitachi).
Shewanella cells were suspended in 0.15 M NaCl solution until the OD600 reached ∼0.3. Then, the cell suspension was mixed with 0.4-ml hexadecane and vortexed for 60 s. After standing for 15 min at room temperature to allow complete separation of the 2 phases, 1-ml sample of aqueous phase was obtained for measuring the OD600. Affinity, defined as a percentage of cells from aqueous phase to organic phase, is written as Eq. 2:
Affinity(%)=100×[1−(A/A0)]
where A0 and A are the OD600 values of the sample of aqueous phase before and after mixing with organic phase (here, hexadecane), respectively. Each sample was tested 3 times.
Hydrophobicity of the engineered electroactive biofilm was detected by contact angle measurement. Isolated biofilm samples were first prepared by carefully cutting LB solid plate to ensure an undamaged surface of biofilms and then placed onto a glass slide horizontally. The contact angle measurement was performed with 3 liquids (water, diiodomethane, and formamide) (2 μl) at room temperature using an automated goniometer (JC2000DM, Powereach, Shanghai, China) following the sessile drop method (Table S4). Each sample was tested 3 times.
The hydrophobicity of bacteria cell surface can be measured by the surface tension components [69]. According to the Young’s equation, the surface tension is determined by the contact angle. For bacteria, the surface tension is written as Eq. 3:
12(1+cosθ)γL=γbLWγLLW+γb+γL−+γb−γL+
where θ is the contact angle of the droplet on the bacteria lawn, γL is the total surface tension of the liquid, γLW is the Lifshitz–van der Waals surface tension component, and γ+ and γ– are the electron–acceptor and electron–donor component, respectively. The subscript L denotes the liquid used to determine the contact angle; the subscript b stands for the bacterial lawn.
The γb+, γb–, and γbLW can be calculated using 3 known surface tension fluids. The total surface tension (γb) of the bacteria lawn is written as Eq. 4:
γb=γbLW+2γb+γb−
On the basis of the surface tension parameters, the interfacial interaction energy (ΔGbwb) is calculated for the quantitative measurement of cell surface hydrophobicity. A negative value for the free energy (ΔGbwb) between 2 similar surfaces immersed in water is defined as a hydrophobic surface. The free energy (ΔGbwb) between bacteria lawn and water is written as Eq. 5:
△Gbwb=−2γbLW+γwLW2−4γb+γb−+γw+γw−−γb+γw−−γb−γw+
where the subscript w stands for water.
The 3-electrode cell was used for measure, and an Ag/AgCl electrode was used as the reference electrode. The working electrode potential of EAC was set to −0.49 V, and EDC was set to +0.61 V. The EAC and EDC, which are calculated by integrating the reductive and oxidative current peaks, are written as Eqs. 6 and 7:
EAC=∫IredFdtmprotein
EDC=∫IoxFdtmprotein
where Ired (A) is the reductive current, Iox (A) is the oxidative current, F is 98,485 C mol−1 of electrons (Faraday’s constant), and mprotein (gram of protein) is the mass of anode protein. To ensure baseline separation, each sample was tested 3 times with more than 30 min between the analyses.
The supernatant of anode biofilm was harvested after 24 and 48 h of incubation and filter sterilized. The Quant-iT PicoGreen dsDNA Reagent (Invitrogen/Molecular Probes, Darmstadt, Germany) was used to analyze the eDNA in the biofilm supernatant. The quantification of eDNA in the supernatant was determined according to the operation method of the instruction manual.
The viscosity properties of biofilm were analyzed with a DNR rheometer (DHR-2) at room temperature. The biofilm sample scraped from the LB plate was placed on the 25-mm-diameter cone plate (101-μm gap) with strain amplitude ranging from 0.01% to 10% at a constant frequency of 10 rad s−1, and the shear rates ranging from 0.001 to 100 s−1.
The extraction and quantification of c-di-GMP were performed as previously described with modifications [73]. Cell pellets in the mid-log phase were harvested at 4 °C and washed for 2 times using 10 mM PBS. Then, the cell pellets were resuspended in 300-μl ammonium acetate (1 mM, ice-cold). The cell suspension was vortex for 15 s at 4 °C and then centrifuged for 10 min at 4 °C; the supernatant was harvested. This operation was repeated at least 3 times, and all of the supernatants were collected together, which were following vacuum-dried overnight. The white particles that appeared after evaporation were the samples containing c-di-GMP and were stored at −80 °C for testing. The c-di-GMP samples were quantified by high-performance liquid chromatography with a C18 column (2.1 × 40 nm, 5 μm). Specifically, the c-di-GMP was isolated through the gradient elution with the 0.2 ml min−1 of flow rate, in which the mobile phase were A: 0.77 g l−1 of ammonium acetate aqueous solution and B: 0.77 g l−1 of ammonium acetate methanol solution (0 to 9 min, 99% A; 9 to 14 min, 85% A; 14 to 19 min, 75% A; 19 to 26 min, 10% A; 26 to 40 min, 99% A), and the UV detection (253 nm) was used for c-di-GMP detection. All experiments were performed in triplicates.
The cells of the biofilm electrode were harvested and washed 2 times with 0.9% saline. After centrifuging the washed cell pellets at 4 °C, the cells were further removed via filtering collected supernatants through 0.22-μm membranes (ANPEL Laboratory Technologies, China), and the filtrates were collected as loose-bond EPS samples and stored at −20 °C before use. Washed cell pellets were resuspended in 0.9% saline with 26.9 mM Na2-EDTA and stirred at 4 °C for 4 h. Cell pellets were centrifuged (5,000 rpm, 20 min, 4 °C) and resuspended in 0.9% saline. Washed cell pellets were centrifuged (5,000 rpm, 15 min, 4 °C), and the cells were removed via filtering collected supernatants through 0.22-μm membranes. Finally, the obtained filtrates were collected as tight-bond EPS samples and stored at −20 °C before use.
A steady-state fluorescence spectrometer (Jobin Yvon Fluorolog 3-21) was used to measure the 3D excitation-emission matrix spectra. The scanning range of emission spectra was 300 to 550 nm at 0.5-nm increments, and the scanning range of excitation spectra was 200 to 400 nm at 10-nm increments. Ten nanometers was set as the slits of excitation and emission with the scanning speed of 1,200 nm min−1. The ddH2O (double-distilled water) was set as the blank.
Bacterial total RNA of the mid-log phase was isolated using a Bacterial Total RNA Extraction Kit (APEXBIO, China). cDNA was synthesized through the GoScript reverse transcription system (Promega, USA); the target gene expression was quantified through the Sso Advanced SYBR Green Supermix (Bio-Rad, USA). The gyrB acts as the reference gene, of which the expression level was used to normalize the expression levels of the target genes. Primers used for the amplification of target gene were displayed in Table S5. The 2−ΔΔCT method was used for data analysis.
To observe the gliding motility of bacteria, 10 μl of bacterial cells was inoculated on the LB agar plate for 10 h at 30 °C. The bacterial behavior was recorded for further analysis.
The cells of the biofilm electrode were harvested and resuspended by 10 mM PBS for ultrasonication. The c-Cyts in the cell lysate were analyzed and quantified using a UV-visible spectrophotometer (UV-2450, Shimadzu).
The supernatant of the MFCs was centrifuged (35000 rpm for 20 min) and filtered (0.22 μm). The eluted samples were analyzed for RF and lactate using liquid chromatograph-tandem mass spectrometer (Agilent LCMS-1290−6460) and high-performance liquid chromatography, respectively. For the quantification of RF, a Waters XBridge C8 column (2.1 mm × 100 mm; particle size: 3.5 μm) was used in positive ion mode. Lactate was quantified by an organic acid column (Aminex HPX-87H Column, 300 mm × 7.8 mm, Bio-Rad) with a refractive index detector (Waters, Corp.) at 65 °C. H2SO4 (5 mM) acted as the mobile phase at a flow rate of 0.6 ml min−1.
The relationship between the outer-membrane cytochrome density (Γ) and the peak current (Ip) and is written as Eq. 8:
Ip=n2f2AvΓ4RT
where Ip represented the peak current, n is the electron transfer number (here, n = 1), A is the anode area, F is the Faraday’s constant, R is the gas constant, and T is the experiment temperature.
The transport of soluble electron shuttles is mainly carried out by diffusion following Fick’s law and can be shown to reflect current density as Eq. 9:
j=nFDshuttle∆Cshuttle∆z
where j is the current density (A m−2), Dshuttle (m2 s−1) is the diffusion coefficient of the soluble electron shuttle, ∆z (m) is the electron transport distance, ∆Cshuttle (mol m−3) is the concentration gradient of oxidized/reduced shuttle, and nF is the convert coefficient from moles to Coulombs.
1.
Catania C, Karbelkar AA, Furst AL. Engineering the interface between electroactive bacteria and electrodes. Joule. 2021;5:743–747.
2.
Chen H, Dong F, Minteer SD. The progress and outlook of bioelectrocatalysis for the production of chemicals, fuels and materials. Nat Catal. 2020;3:225–244.
3.
Lovley DR, Holmes DE. Electromicrobiology: The ecophysiology of phylogenetically diverse electroactive microorganisms. Nat Rev Microbiol. 2021;20:5–19.
4.
Xu X, Liu Y, Du G, Ledesma-Amaro R, Liu L. Microbial chassis development for natural product biosynthesis. Trends Biotechnol. 2020;38:779–796.
5.
Halan B, Buehler K, Schmid A. Biofilms as living catalysts in continuous chemical syntheses. Trends Biotechnol. 2012;30:453–465.
6.
Logan BE, Rossi R, Ragab A, Saikaly PE. Electroactive microorganisms in bioelectrochemical systems. Nat Rev Microbiol. 2019;17:307–319.
7.
Li F, Li YX, Cao YX, Wang L, Liu CG, Shi L, Song H. Modular engineering to increase intracellular NAD(H/(+)) promotes rate of extracellular electron transfer of Shewanella oneidensis. Nat Commun. 2018;9:3637.
8.
Shi L, Dong H, Reguera G, Beyenal H, Lu A, Liu J, Yu HQ, Fredrickson JK. Extracellular electron transfer mechanisms between microorganisms and minerals. Nat Rev Microbiol. 2016;14:651–662.
9.
Glasser NR, Saunders SH, Newman DK. The colorful world of extracellular electron shuttles. Annu Rev Microbiol. 2017;71:731–751.
10.
Logan BE. Exoelectrogenic bacteria that power microbial fuel cells. Nat Rev Microbiol. 2009;7:375–381.
11.
Edwards MJ, White GF, Butt JN, Richardson DJ, Clarke TA. The crystal structure of a biological insulated transmembrane molecular wire. Cell. 2020;181:665–673.e10.
12.
Kumar A, Hsu LH-H, Kavanagh P, Barrière F, PNL L, Lapinsonnière L, Lienhard JH V, Schröder U, Jiang X, Leech D. The ins and outs of microorganism–electrode electron transfer reactions. Nat Rev Chem. 2017;1:Article 0024.
13.
Lin T, Ding W, Sun L, Wang L, Liu CG, Song H. Engineered Shewanella oneidensis-reduced graphene oxide biohybrid with enhanced biosynthesis and transport of flavins enabled a highest bioelectricity output in microbial fuel cells. Nano Energy. 2018;50:639–648.
14.
Barrozo A, El-Naggar MY, Krylov AI. Distinct electron conductance regimes in bacterial decaheme cytochromes. Angew Chem Int Edit. 2018;57(23):6805–6809.
15.
Yong YC, Yu YY, Zhang X, Song H. Highly active bidirectional electron transfer by a self-assembled electroactive reduced-graphene-oxide-hybridized biofilm. Angew Chem Int Ed Engl. 2014;53(17):4480–4483.
16.
Yong YC, Dong XC, Chan-Par MB, Song H, Chen P. Macroporous and monolithic anode based on polyaniline hybridized three-dimensional graphene for high-performance microbial fuel cells. ACS Nano. 2012;6(3):2394–2400.
17.
Cao BC, Zhao ZP, Peng L, Shiu HY, Ding M, Song F, Guan X, Lee CK, Huang J, Zhu D, et al.Silver nanoparticles boost charge-extraction efficiency in Shewanella microbial fuel cells. Science. 2021;373(6561):1336–1340.
18.
Bird LJ, Kundu BB, Tschirhart T, Corts AD, Su L, Gralnick JA, Ajo-Franklin CM, Glaven SM. Engineering wired life: Synthetic biology for electroactive bacteria. ACS Synth Biol. 2021;10(11):2808–2823.
19.
Lopez JM, Duran L, Avalos JL. Physiological limitations and opportunities in microbial metabolic engineering. Nat Rev Microbiol. 2021;20:35–48.
20.
Patil SA, Haegerhaell C, Gorton L. Cisplatin-induced elongation of Shewanella oneidensis MR-1 cells improves microbe–electrode interactions for use in microbial fuel cells. Energy Environ Sci. 2013;6(9):2626–2630.
21.
Min D, Cheng L, Zhang F, Huang XN, Li DB, Liu DF, Lau TC, Mu Y, Yu HQ. Enhancing extracellular electron transfer of Shewanella oneidensis MR-1 through coupling improved flavin synthesis and metal-reducing conduit for pollutant degradation. Environ Sci Technol. 2017;51(9):5082–5089.
22.
Liu Y, Ding M, Ling W, Yang Y, Zhou X, Li BZ, Chen T, Nie Y, Wang M, Zeng B, et al.A three-species microbial consortium for power generation. Energy Environ Sci. 2017;10(7):1600–1609.
23.
Li F, Li Y, Sun L, Li X, Yin C, An X, Chen X, Tian Y, Song H. Engineering Shewanella oneidensis enables xylose-fed microbial fuel cell. Biotechnol Biofuels. 2017;10:Article 196.
24.
Kracke F, Lai B, Yu SQ, Krömer JO. Balancing cellular redox metabolism in microbial electrosynthesis and electro fermentation—A chance for metabolic engineering. Metab Eng. 2018;45:109–120.
25.
Xu S, Barrozo A, Tender LM, Krylov AI, el-Naggar MY. Multiheme cytochrome mediated redox conduction through Shewanella oneidensis MR-1 cells. J Am Chem Soc. 2018;140(32):10085–10089.
26.
Jiang X, Futera Z, Ali ME, Gajdos F, von Rudorff GF, Carof A, Breuer M, Blumberger J. Cysteine linkages accelerate electron flow through tetra-heme protein STC. J Am Chem Soc. 2017;139(48):17237–17240.
27.
Fereiro JA, Yua X, Pecht I, Sheves M, Cuevas JC, Cahen D. Tunneling explains efficient electron transport via protein junctions. Proc Natl Acad Sci USA. 2018;115(20):E4577–E4583.
28.
Saunders SH, Tse ECM, Yates MD, Otero FJ, Trammell SA, Stemp EDA, Barton JK, Tender LM, Newman DK. Extracellular DNA promotes efficient extracellular electron transfer by pyocyanin in Pseudomonas aeruginosa biofilms. Cell. 2020;182(4):919–932.e19.
29.
Okamoto A, Hashimoto K, Nealson KH. Flavin redox bifurcation as a mechanism for controlling the direction of electron flow during extracellular electron transfer. Angew Chem Int Ed Engl. 2014;53(41):10988–10991.
30.
Xiao Y, Zhang E, Zhang J, Dai Y, Yang Z, Christensen HEM, Ulstrup J, Zhao F. Extracellular polymeric substances are transient media for microbial extracellular electron transfer. Sci Adv. 2017;3(7):Article e1700623.
31.
Xiao Y, Zhao F. Electrochemical roles of extracellular polymeric substances in biofilms. Curr Opin Chem Biol. 2017;4(1):206–211.
32.
Yalcin SE, O'Brien JP, Gu Y, Reiss K, Yi SM, Jain R, Srikanth V, Dahl PJ, Huynh W, Vu D, et al.Electric field stimulates production of highly conductive microbial OmcZ nanowires. Nat Chem Biol. 2020;16(10):1136–1142.
33.
Heijne AT, Pereira MA, Pereira J, Sleutels T. Electron storage in electroactive biofilms. Trends Biotechnol. 2021;39:34–42.
34.
Nadell CD, Drescher K, Foster KR. Spatial structure, cooperation and competition in biofilms. Nat Rev Microbiol. 2016;14:589–600.
35.
Arnaouteli S, Bamford NC, Stanley-Wall NR, Kovács ÁT. Bacillus subtilis biofilm formation and social interactions. Nat Rev Microbiol. 2021;19:600–614.
36.
Arciola CR, Campoccia D, Montanaro L. Implant infections: Adhesion, biofilm formation and immune evasion. Nat Rev Microbiol. 2018;16:397–409.
37.
van Wolferen M, Orell A, Albers SV. Archaeal biofilm formation. Nat Rev Microbiol. 2018;16:699–713.
38.
Wood TK, Hong SH, Ma Q. Engineering biofilm formation and dispersal. Trends Biotechnol. 2011;29:87–94.
39.
Chadwick GL, Jiménez Otero F, Gralnick JA, Bond DR, Orphan VJ. NanoSIMS imaging reveals metabolic stratification within current-producing biofilms. Proc Natl Acad Sci USA. 2019;116:20716–20724.
40.
Chen X, Leite Lobo F, Bian Y, Lu L, Chen X, Tucker MP, Wang Y, Ren ZJ. Electrical decoupling of microbial electrochemical reactions enables spontaneous H2 evolution. Energy Environ Sci. 2020;13:495–502.
41.
Bhokisham N, VanArsdale E, Stephens KT, Hauk P, Payne GF, Bentley WE. A redox-based electrogenetic crispr system to connect with and control biological information networks. Nat Commun. 2020;11(1):2427.
42.
Hirose A, Kouzuma A, Watanabe K. Towards development of electrogenetics using electrochemically active bacteria. Biotechnol Adv. 2019;37(6):107351.
43.
Rumbaugh KP, Sauer K. Biofilm dispersion. Nat Rev Microbiol. 2020;18:571–586.
44.
Armbruster CR, Parsek MR. New insight into the early stages of biofilm formation. Proc Natl Acad Sci USA. 2018;115:4317–4319.
45.
Magalhães RP, Vieira TF, Fernandes HS, Melo A, Simões M, Sousa SF. The biofilms structural database. Trends Biotechnol. 2020;38(9):937–940.
46.
Zhang P, Chen YP, Qiu JH, Dai YZ, Feng B. Imaging the microprocesses in biofilm matrices. Trends Biotechnol. 2019;37:214–226.
47.
O’Toole G, Kaplan HB, Kolter R. Biofilm formation as microbial development. Annu Rev Microbiol. 2000;54:49–79.
48.
Ma L, Conover M, Lu H, Parsek MR, Bayles K, Wozniak DJ. Assembly and development of the Pseudomonas aeruginosa biofilm matrix. PLOS Pathog. 2009;5:e1000354.
49.
Wei Q, Ma LZ. Biofilm matrix and its regulation in Pseudomonas aeruginosa. Int J Mol Sci. 2013;14(10):20983–21005.
50.
Theunissen S, Vergauwen B, Smet LD, Van Beeumen J, Van Gelder P, Savvides SN. The agglutination protein AggA from Shewanella oneidensis MR-1 is a tolc-like protein and forms active channels in vitro. Biochem Biophys Res Commun. 2009;386:380–385.
51.
Kouzuma A, Tajima N, Hashimoto K, Watanabe K. Electrochemical selection and characterization of a high current-generating Shewanella oneidensis mutant with altered cell-surface morphology and biofilm-related gene expression. BMC Microbiol. 2014;14:190.
52.
Windt WD, Gao HC, Krömer W, Damme PV, Dick J, Mast J, Boon N, Zhou J, Verstraete W. AggA is required for aggregation and increased biofilm formation of a hyper-aggregating mutant of Shewanella oneidensis MR-1. Microbiology. 2006;152(Pt. 3):721–729.
53.
Fong JNC, Yildiz FH. Biofilm matrix proteins. Microbiol Spectr. 2015;3:10.
54.
Kavanaugh JS, Flack CE, Lister J, Ricker EB, Ibberson CB, Jenul C, Moormeier DE, Delmain EA, Bayles KW, Horswill AR. Identification of extracellular DNA-binding proteins in the biofilm matrix. mBio. 2019;3(3):e01137-19.
55.
Røder HL, Olsen NMC, Whiteley M, Burmølle M. Unravelling interspecies interactions across heterogeneities in complex biofilm communities. Environ Microbiol. 2020;22:5–16.
56.
Sauer K, Stoodley P, Goeres DM, Hall-Stoodley L, Burmølle M, Stewart PS, Bjarnsholt T. The biofilm life cycle: Expanding the conceptual model of biofilm formation. Nat Rev Microbiol. 2022;20(10):608–620.
57.
Kouzuma A, Meng X-Y, Kimura N, Hashimoto K, Watanabe K. Disruption of the putative cell surface polysaccharide biosynthesis gene SO3177 in Shewanella oneidensisMR-1enhances adhesion to electrodes and current generation in microbial fuel cells. Appl Environ Microbiol. 2010;76(13):4151–4157.
58.
Panlilio H, Rice CV. The role of extracellular DNA in the formation, architecture, stability, and treatment of bacterial biofilms. Biotechnol Bioeng. 2021;118:2129–2141.
59.
D'Alvise PW, Sjøholm OR, Yankelevich T, Jin Y, Wuertz S, Smets BF. Tol plasmid carriage enhances biofilm formation and increases extracellular DNA content in Pseudomonas putida KT2440. FEMS Microbiol Lett. 2010;312(1):84–92.
60.
Gödeke J, Paul K, Lassak J, Thormann KM. Phage-induced lysis enhances biofilm formation in Shewanella oneidensis MR-1. ISME J. 2010;5(4):613–626.
61.
Sahu PK, Iyer PS, Oak AM, Pardesi KR, Chopade BA. Characterization of edna from the clinical strain Acinetobacter baumannii AIIMS 7 and its role in biofilm formation. Sci World J. 2012;2012:973436.
62.
Flemming H-C, Wingender J. The biofilm matrix. Nat Rev Microbiol. 2010;8(9):623–633.
63.
Gödeke J, Heun M, Bubendorfer S, Paul K, Thormann KM. Roles of two Shewanella oneidensis MR-1 extracellular endonucleases. Appl Environ Microbiol. 2011;77(15):5342–5351.
64.
Pinchuk GE, Ammons C, Culley DE, S-MW L, McLean JS, Romine MF, Nealson KH, Fredrickson JK, Beliaev AS. Utilization of DNA as a sole source of phosphorus, carbon, and energy by Shewanella spp.: Ecological and physiological implications for dissimilatory metal reduction. Appl Environ Microbiol. 2008;74(4):1198–1208.
65.
Berends ETM, Horswill AR, Haste NM, Monestier M, Nizet V, von Köckritz-Blickwede M. Nuclease expression by Staphylococcus aureus facilitates escape from neutrophil extracellular traps. J Innate Immun. 2010;2:576–586.
66.
Nijland R, Hall MJ, Burgess JG. Dispersal of biofilms by secreted, matrix degrading, bacterial DNase. PLOS ONE. 2010;5:e15668.
67.
Heun M, Binnenkade L, Kreienbaum M, Thormann KM. Functional specificity of extracellular nucleases of Shewanella oneidensis MR-1. Appl Environ Microbiol. 2012;78:4400–4411.
68.
Das T, Kutty SK, Tavallaie R, Ibugo AI, Panchompoo J, Sehar S, Aldous L, Yeung AWS, Thomas SR, Kumar N, et al.Phenazine virulence factor binding to extracellular DNA is important for Pseudomonas aeruginosa biofilm formation. Sci Rep. 2015;5:8398.
69.
Li Z-R, Sun J, Du Y, Pan A, Zeng L, Maboudian R, Burne RA, Qian P-Y, Zhang W. Mutanofactin promotes adhesion and biofilm formation of cariogenic Streptococcus mutans. Nat Chem Biol. 17(5):576–584.
70.
Jenal U, Reinders A, Lori C. Cyclic di-GMP: Second messenger extraordinaire. Nat Rev Microbiol. 2017;15:271–284.
71.
Mukherjee M, Zaiden N, Teng A, Hu Y, Cao B. Shewanella biofilm development and engineering for environmental and bioenergy applications. Curr Opin Chem Biol. 2020;59:84–92.
72.
Heidelberg JF, Paulsen IT, Nelson KE, Gaidos EJ, Nelson WC, Read TD, Eisen JA, Seshadri R, Ward N, Methe B, et al.Genome sequence of the dissimilatory metal ion–reducing bacterium Shewanella oneidensis. Nat Biotechnol. 2002;20:1118–1123.
73.
Ng CK, Xu J, Cai Z, Yang L, Thompson IP, Huang WE, Cao B. Elevated intracellular cyclic-di-GMP level in Shewanella oneidensis increases expression of c-type cytochromes. Microb Biotechnol. 2020;13:1904–1916.
74.
Okamoto A, Hashinoto K, Nealson KH, Nakamura R. Rate enhancement of bacterial extracellular electron transport involves bound flavin semiquinones. Proc Natl Acad Sci USA. 2013;110(19):7856–7861.
75.
Li Y, Liu J, Chen X, Yuan X, Li N, He W, Feng Y. Enhanced electricity generation and extracellular electron transfer by polydopamine–reduced graphene oxide (PDA–rGO) modification for high-performance anode in microbial fuel cell. Chem Eng J. 2020;387:123408.
76.
Yang Y, Ding Y, Hu Y, Cao B, Rice SA, Kjelleberg S, Song H. Enhancing bidirectional electron transfer of Shewanella oneidensis by a synthetic flavin pathway. ACS Synth Biol. 2015;4:815–823.
77.
Gao T, Shi M, Gao H. Partially reciprocal replacement of FlrA and FlrC in regulation of Shewanella oneidensis flagellar biosynthesis. J Bacteriol. 2018;200:00796-17.
78.
Jin M, Jiang YM, Sun L, Yin J, Fu H, Wu G, Gao H. Unique organizational and functional features of the cytochrome c maturation system in Shewanella oneidensis. PLOS ONE. 2013;8:e75610.
79.
Yan D, Yang X, Yuan W. Electricity and H2 generation from hemicellulose by sequential fermentation and microbial fuel/electrolysis cell. J Power Sources. 2015;289:26–33.
80.
Choi D, Lee SB, Kim S, Min B, Choi IG, Chang IS. Metabolically engineered glucose-utilizing Shewanella strains under anaerobic conditions. Bioresour Technol. 2014;154:59–66.
81.
West EA, Jain A, Gralnick JA. Engineering a native inducible expression system in Shewanella oneidensisto control extracellular electron transfer. ACS Synth Biol. 2017;6(9):1627–1634.
82.
Suo D, Fang Z, Yu YY, Yong Y-C. Synthetic curli enables efficient microbial electrocatalysis with stainless-steel electrode. AICHE J. 2020;66(4):e16897.
83.
Kouzuma A, Oba H, Tajima N, Hashimoto K, Watanabe K. Electrochemical selection and characterization of a high current-generating Shewanella oneidensis mutant withaltered cell-surface morphology and biofilm-related gene expression. BMC Microbiol. 2014;14:190.
84.
Cheng Z, Xiong J, Min D, Cheng L, Liu DF, Li WW, Jin F, Yang M, Yu HQ. Promoting bidirectional extracellular electron transfer of Shewanella oneidensis MR-1 for hexavalent chromium reduction via elevating intracellular cAMP level. Biotechnol Bioeng. 2020;117:1294–1303.
85.
Li F, Li Y, Sun L, Chen X, An X, Yin C, Cao Y, Wu H, Song H. Modular engineering intracellular NADH regeneration boosts extracellular electron transfer of Shewanella oneidensis MR-1. ACS Synth Biol. 2018;7(3):885–895.
86.
Tajima N, Kouzuma A, Hashimoto K, Watanabe K. Selection of Shewanella oneidensis MR-1 gene-knockout mutants that adapt to an electrode-respiring condition. Biosci Biotechnol Biochem. 2011;75(11):2229–2233.
87.
Thormann KM, Duttler S, Saville RM, Hyodo M, Shukla S, Hayakawa Y, Spormann AM. Control of formation and cellular detachment from Shewanella oneidensis MR-1 biofilms by cyclic di-GMP. J Bacteriol. 2006;188(7):2681–2691.
88.
Yu YY, Chen HL, Yong YC, Kim DH, Song H. Conductive artificial biofilm dramatically enhances bioelectricity production in Shewanella-inoculated microbial fuel cells. Chem Commun. 2011;47(48):12825–12827.
89.
Tao L, Xie M, Chiew G, Wang Z, Chen WN, Wang X. Improving electron trans-inner membrane movements in microbial electrocatalysts. Chem Commun. 2016;52:6292–6295.
Year 2023 volume 6 Issue 3
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doi: 10.34133/research.0081
  • Receive Date:2022-09-29
  • Online Date:2026-10-28
  • Published:2023-03-20
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  • Received:2022-09-29
  • Accepted:2023-01-31
Affiliations
    1Frontiers Science Center for Synthetic Biology (Ministry of Education), and Key Laboratory of Systems Bioengineering, Tianjin University, Tianjin 300072, China.
    2Collaborative Innovation Center of Chemical Science and Engineering (Tianjin), School of Chemical Engineering and Technology, Tianjin University, Tianjin 300072, China.
    3Department of Biological Sciences and Technology, School of Environmental Studies, China University of Geoscience in Wuhan, Wuhan, Hubei 430074, China.

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表12种不同金属材料的力学参数
科
Family
属数
Number of
genus
种数
Number of
species
占总种数比例
Percentage of
total species (%)
属
Genus
种数
Number of
species
占总种数比例
Percentage of total
species (%)
鹅膏菌科Amanitaceae 2 11 5.26 鹅膏菌属 Amanita 10 4.78
小菇科 Mycenaceae 2 12 5.74 丝盖伞属 Inocybe 5 2.39
多孔菌科 Polyporaceae 8 14 6.70 蜡蘑属 Laccaria 5 2.39
红菇科 Russulaceae 3 23 11.00 小皮伞属 Marasmius 6 2.87
小菇属 Mycena 11 5.26
光柄菇属 Pluteus 5 2.39
红菇属 Russula 17 8.13
栓菌属 Trametes 5 2.39
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