Metabolic Reconstruction and Modeling Microbial ... · 07/07/2016 · 7 1. Biosciences Division,...
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Metabolic Reconstruction and Modeling Microbial Electrosynthesis 1 2Christopher W. Marshall1,3*, Daniel E. Ross7, Kim M. Handley4#, Pamela B. Weisenhorn1, 3Janaka N. Edirisinghe4, Christopher S. Henry4, Jack A. Gilbert1,3, Harold D. May5,6, and 4R. Sean Norman7* 5 61. Biosciences Division, Argonne National Laboratory, Argonne, Illinois, USA; 72. Department of Ecology and Evolution, The University of Chicago, Chicago, Illinois, 8USA; 93. Department of Surgery, The University of Chicago, Chicago, Illinois, USA; 104. Computing, Environment, and Life Sciences, Argonne National Laboratory, Illinois, 11USA; 125. Department of Microbiology and Immunology, Medical University of South Carolina, 13Charleston, South Carolina, USA; 146. Marine Biomedicine and Environmental Science Center, Medical University of South 15Carolina, Charleston, South Carolina, USA; 167. Department of Environmental Health Sciences, Arnold School of Public Health, 17University of South Carolina, Columbia, South Carolina, USA; 18 19#Present address: Kim M. Handley, School of Biological Sciences, The University of 20Auckland, Auckland, New Zealand. 21*Corresponding authors 22Correspondence: CW Marshall, Department of Surgery (Room O-200C, MC 5030), 23University of Chicago, 5841 S Maryland Ave., Chicago, IL 60637. E-mail: [email protected]. RS Norman, Department of Environmental Health 25Sciences, University of South Carolina, 931 Assembly St., Columbia, SC 29208. E-mail: [email protected] 27 28Running title: Modeling a Microbial Electrosynthetic Community 29 30 31Abstract 32Microbial electrosynthesis is a renewable energy and chemical production platform that 33relies on microbial taxa to capture electrons from a cathode and fix carbon. Yet the 34metabolic capacity of multispecies microbial communities on electrosynthetic 35biocathodes remains unknown. We assembled 13 genomes from a high-performing 36electroacetogenic culture, and mapped their transcriptional activity from a range of 37conditions. This allowed us to create a metabolic model of the primary community 38members (Acetobacterium, Sulfurospirillum, and Desulfovibrio). Acetobacterium was the 39primary carbon fixer, and a keystone member of the community. Based on transcripts 40upregulated near the electrode surface, soluble hydrogenases and ferredoxins from 41Acetobacterium and hydrogenases, formate dehydrogenase, and cytochromes of 42Desulfovibrio were essential conduits for electron flow from the electrode into the 43electrosynthetic community. A nitrogenase gene cluster with an adjacent ferredoxin and 44one of two Rnf complexes within the genome of the Acetobacterium were also 45upregulated on the electrode. Nitrogenase is known to serve as a hydrogenase, thereby 46it would contribute to hydrogen production by the biocathode. Oxygenases of 47microaerobic members of the community throughout the cathode chamber, including 48Sulfurospirillum and Rhodobacteraceae, were expressed. While the reactors were 49maintained anaerobically, this gene expression would support anaerobic growth and 50thus electrosynthesis by scrubbing small amounts of O2 out of the reactor. These 51
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molecular discoveries and metabolic modeling now serve as a foundation for future 52examination and development of electrosynthetic microbial communities. 53 54Introduction 55
A microbial electrosynthesis system (MES) is a bioelectrochemical device that employs 56
microbes to transport electrons from a cathode to protons and/or CO2. Thus, the 57
microbes act as cathode catalysts to generate, or synthesize, a valuable product 58
(Rabaey and Rozendal, 2010). This technology has immense potential, therefore 59
understanding which microbes are capable of cathodic electron transfer and which 60
metabolic pathways are involved in CO2 conversion to chemicals are critical to improving 61
the performance of MESs. Furthermore, this work has broader environmental 62
implications including understanding ecological aspects of one carbon metabolism and 63
extracellular electron transfer relevant to global biogeochemical cycling. Technologically, 64
these MESs could have a significant impact on geoengineering applications such as 65
carbon capture and storage. 66
67
Advances in microbial electrosynthesis and related biocathode-driven processes 68
primarily focus on the production of three compounds: hydrogen 69
(electrohydrogenesis)(Rozendal et al., 2008), methane (electromethanogenesis) (Cheng 70
et al., 2009), and acetate (electroacetogenesis) (Nevin et al., 2010). However, microbial 71
electrosynthesis can be used to generate alcohols and various short-chain fatty acids.\ 72
(Steinbusch et al., 2010). A thorough evaluation of a carbon dioxide fixing aerobic 73
biocathode has also been reported (Wang et al., 2015). To manipulate (and optimize) 74
these systems we must understand the extracellular electron transfer (EET) enzymes or 75
molecules involved in cathode oxidation, and we must determine how these cathodic 76
electron transport components are coupled to energy conservation by the microbial cell. 77
While an increasingly robust body of literature has been established relating to microbial 78
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communities metabolizing with an anodic electron acceptor (Ishii et al., 2013, 2015; Kiely 79
et al., 2011), much is still unclear about the diverse metabolic capabilities of 80
microorganisms and communities growing on a cathode (Tremblay and Zhang, 2015). 81
We used metagenomics, metatranscriptomics, and metabolic flux modeling to elucidate 82
carbon flux and EET mechanisms. We have deciphered the complex interactions 83
between cooperating and competing members of the microbiome, producing 84
opportunities to improve microbial electrosynthesis as well as understand multi-species 85
biofilm communities. 86
87
Materials and Methods 88
Reactor design and operation 89
The reactors containing the microbial communities used for metagenomics and 90
metatranscriptomics in this study were described in detail in two previous studies 91
(Marshall et al., 2012, 2013). Of the five MES reactors previously described, two 92
reactors were selected for further analysis in this study. The first reactor, closed circuit 93
(CC), was operated for 184 days before termination (MES-BW4 from previous 94
manuscript is CC reactor here). The second reactor, open circuit (OC), was operated in 95
closed circuit mode for 141 days before it was left at open circuit for three hours prior to 96
termination, in order to control for biofilm effects of the closed circuit reactor (MES 1a 97
from previous manuscript is OC reactor. The initial source of microorganisms was from a 98
brewery wastewater retention basin that was then subjected to sequential transfers of 99
the graphite and supernatant in bioelectrochemical systems before inoculation into the 100
two MESs described in this study. The brewery wastewater inoculum was allowed to 101
establish on graphite granule cathodes and then repeatedly washed with fresh defined 102
medium containing per liter: 2.5 g NaHCO3, 0.6 g NaH2PO4 * H2O, 0.25 g NH4Cl, 0.212 g 103
MgCl2, 0.1 g KCl, 0.03 g CaCl2, 20 mL vitamin solution, and 20 mL mineral solution. 104
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Subsequent, sludge-free transfers were made into 150 mL volume cathode chambers of 105
MESs containing 30 g of graphite granules, 75 mL of medium, 80% N2 and 20% CO2 or 106
100% CO2 in the headspace, and poised at -590 mV vs. standard hydrogen electrode 107
(SHE) for the duration of the experiments unless otherwise noted. The medium during 108
the initial startup period did not contain sodium 2-bromoethanesulfonate (2-BES), but 10 109
mM 2-BES was periodically used to inhibit methanogenesis and maintain a 110
predominantly acetogenic culture later in the study, including at the time of sampling for 111
metagenome and metatranscriptome analyses (day 181). Upon termination of the 112
experiment, supernatant and bulk granular cathodes were removed for DNA and RNA 113
extraction. All samples were frozen in liquid nitrogen within 5 minutes of applied voltage 114
interruption, except OC which was deliberately left at open circuit for 3 hours prior to 115
freezing. A schematic of the experimental design can be found in Supplementary Figure 116
1. 117
118
DNA/RNA extraction and sequencing 119
DNA and RNA were processed as previously reported and is detailed in the 120
Supplementary Online Methods. Whole genome shotgun sequencing of the cathode-121
associated microbial community from the closed circuit reactor (CCc) and the 122
supernatant community from the closed circuit reactor (CCs) was accomplished with the 123
Illumina MiSeq instrument yielding 250 bp paired-end reads totaling 9,793,154 reads 124
with a total length of 2,325,061,111 bp for the attached microbial community, and 125
5,049,632 reads with a total length of 1,198,063,143 bp for the supernatant microbiome. 126
127
Metagenome assembly and binning 128
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Two metagenomes were assembled and annotated from the closed circuit reactor (CCc 129
and CCs). Near full-length 16S rRNA sequences from the CCc and CCs metagenomes 130
were assembled over 100 iterations of the Expectation-Maximization Iterative 131
Reconstruction of Genes from the Environment (EMIRGE) method (Miller et al., 2011), 132
following initial read mapping to a modified version of the dereplicated version of the 133
SILVA 108 small-subunit (SSU) rRNA database (Quast et al., 2013). During iterations 134
sequences 97% similar were clustered. Representative sequences were searched 135
against the SSURef_111_NR_trunc database using BLASTN. 136
137
SPAdes (Bankevich et al., 2012), Velvet+Metavelvet (Zerbino and Birney, 2008; Namiki 138
et al., 2012), Ray (Boisvert et al., 2012), and IDBA-UD (Peng et al., 2012) community 139
genome assemblies were compared based on total length of the assembly, n50 score, 140
and percent reads mapping back to the assemblies (Supplementary Table 1). Based on 141
the assembly results, the SPAdes assembly was used to further analyze the 142
metagenomes due to the highest percent of reads mapped to a threshold above 1kb 143
(cathode: 95.95%, supernatant: 91.61%) and total assembly size (cathode: 67,511,580 144
bp above 1kb, supernatant: 42,119,276 bp). Following assembly, the SPAdes contigs 145
were analyzed by Prodigal (Hyatt et al., 2010) to predict protein-encoding genes. 146
Prodigal-predicted amino acid sequences were then annotated using UBLAST searches 147
(usearch64(Edgar, 2010)) against the uniref90 database (Suzek et al., 2015) with an e-148
value cutoff of 100. These annotations, along with kmer coverage and GC content were 149
used for preliminary genome binning. Emergent self-organizing maps (ESOM) were 150
used to refine the metagenome bins based on tetranucleotide frequency and contig 151
coverage on contigs greater than 4kb (Dick et al., 2009). Smaller fragments (>1kb) were 152
then projected onto the 4kb ESOM. To further refine the bins the multi-metagenome 153
pipeline (Albertsen et al., 2013) was used, leveraging differential genome coverages 154
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between CCc and CCs to aid contig identification. Results were compared to ESOM 155
bins. Only contigs binned by both ESOM and multi-metagenome pipeline were used for 156
reassemblies of individual genome bins. All reads associated with the contigs in each of 157
the final bins were reassembled as single organism genomes by SPAdes using default 158
options with the addition of the –careful flag and kmer sizes of 65, 77, 99, and 127. All 159
contigs greater than 1kb were uploaded to RAST (Aziz et al., 2008) for final annotation 160
using RASTtk (Brettin et al., 2015). The re-assembled individual genome bins and one 161
large “undetermined” bin were compiled into a combined metagenome for transcript 162
mapping. See Supplementary Table 2 for bin summaries and completeness generated 163
by CheckM (Parks et al., 2015). The RASTtk annotations were compared to annotations 164
(Wu et al., 2011) from Pfam, COG, and a Blastx search of the non-redundant protein 165
sequences database (Camacho et al., 2009). The RAST-annotated protein encoding 166
gene (peg) tags are used as identifiers throughout the manuscript with the bin 167
abbreviation preceding the peg number. See Supplementary Table 3 for all annotations. 168
169
Metatranscriptome 170
Four total metatranscriptomes were recovered from CCc, CCs, OCc, and OCs. The 171
FASTX toolkit was used to filter the reads with a quality score lower than 30 and a length 172
less than 50bp. Quality filtered reads from each sample were mapped to the CCc 173
electrode metagenome contigs using BWA (Li and Durbin, 2009). Raw hit counts 174
mapped to each RAST-annotated protein encoding gene in the combined metagenome 175
were then used to calculate reads per kilobase gene length per millions of mapped reads 176
(RPKM) values. RPKM values for each gene were also normalized to bin coverage 177
based on single copy recA gene abundances (Supplementary Figure 6). This 178
compensated for the abundance variations of the taxa between samples. Quantile 179
normalization was used to evenly distribute the transcript values between sample 180
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conditions. Fold change for differential expression analysis between conditions was 181
calculated by dividing RPKM/RecA-condition1 by RPKM/RecA-condition2. To eliminate 0 182
value errors and over interpretation of very low count genes, an empirically determined 183
threshold value of 0.1 was added to all of the RPKM/RecA values. 184
185
Metabolic model reconstruction, gapfilling, and curation 186
To construct models of our three highest relative abundance genomes (Acetobacterium, 187
Sulfurospirillum, and Desulfovibrio), we imported the RAST-annotated versions of these 188
genomes into the DOE Systems Biology Knowledgebase (KBase). Once in KBase, we 189
used the Build Metabolic Model app, which is based on the ModelSEED algorithm 190
(Henry et al., 2010), to construct one draft model for each genome. Once the draft 191
models were complete, we curated the models based on literature data, KEGG 192
(Kanehisa and Goto, 2000), and MetaCyc (Karp et al., 2002)(Supplementary table 4c). 193
This curation primarily involved the addition of electron utilization pathways 194
(Acetobacterium), addition of electron transport chain reactions (Sulfurospirillum, and 195
Desulfovibrio), and adjustment of reaction directionality to prevent pathways from 196
proceeding in unphysiological directions. 197
198
Next, we applied the Gapfill metabolic model KBase app to identify and fill all the gaps in 199
the metabolic pathways of our models that might prevent them from producing biomass 200
while operating in one of our hypothesized metabolic roles within the microbial 201
community. In this gap-filling process, the model was augmented to include all the 202
reactions contained in the ModelSEED database (available for download from GitHub 203
(https://github.com/ModelSEED/ModelSEEDDatabase/tree/master/Biochemistry). 204
Additionally, all reactions determined to be thermodynamically reversible (Henry et al., 205
2006, 2009; Jankowski et al., 2008) were adjusted to be reversible. Finally, flux balance 206
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analysis (FBA) (Orth et al., 2010) was performed to generate a flux profile that produced 207
biomass while minimizing the flux through all reactions and reaction directions that were 208
not contained in the original model, consistent with previously published algorithms 209
(Dreyfuss et al., 2013; Latendresse, 2014). All reactions and reaction directions not 210
included in the original model that had a nonzero flux in were then added to the model 211
as the gap-filling solution. This subsequently permits the growth of the gap-filled model 212
in the specified condition. Acetobacterium was gapfilled in a condition that reflected the 213
only proposed metabolic role for this organism: direct consumption of electrons to fix 214
CO2 coupled to the production of acetate. The Sulfurospirillum and Desulfovibrio models 215
were gapfilled separately in two distinct conditions reflecting the potential roles proposed 216
for these organisms: (i) autotrophic growth on CO2 and H2; or (ii) heterotrophic growth on 217
acetate. This produced a total of four models: (i) autotrophic Sulfurospirillum; (ii) 218
heterotrophic Sulfurospirillum; (iii) autotrophic Desulfovibrio; and (iv) heterotrophic 219
Desulfovibrio. The detailed composition of the electrosynthetic, autotrophic, and 220
heterotrophic media formulations used in the gapfilling analysis are included in the 221
supplementary material (Supplementary Table 4). 222
223
All models were reconstructed, gapfilled, and curated in the KBase Narrative Interface, 224
and the associated narratives include all parameters and media formulations used 225
(https://narrative.kbase.us/narrative/ws.15248.obj.1). All model data is also available for 226
download from the same narratives. The reactions for each model and condition can 227
also be found in Supplementary Table 4a. 228
229
Prediction of metabolic activity with comparison to expression data 230
Flux balance analysis (FBA) was applied with each of our gapfilled metabolic models to 231
simulate the production of biomass on the same media formulations used in our 232
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gapfilling analysis (electrosynthetic, autotrophic, and heterotrophic media). Thus, we 233
simulated the growth of our gapfilled Acetobacterium model in our electrosynthetic 234
media; we simulated the growth of our autotrophic Sulfurospirillum and Desulfovibrio 235
models in our autotrophic media; and we simulated the growth of our heterotrophic 236
Sulfurospirillum and Desulfovibrio models in our heterotrophic media (all media 237
formulations are listed in Supplementary table 4b). We then maximized the production of 238
biomass in each model, subject to the constraints on nutrient uptake imposed by our 239
media formulations, and once a solution was produced, we minimized the sum of the 240
fluxes comprising the solution, in order to produce a single solution that is both simple 241
and distinct. 242
243
We validated our flux solutions by comparing the active reactions in each flux profile 244
against the actively expressed genes identified based on our transcriptomic data. In 245
order to conduct this comparison, we first needed to classify the genes in our three 246
species as either active or inactive based on the relative abundance of mapped RNA-247
seq reads. This process began by identifying an initial set of universal genes in each 248
species that can be assumed to be always active (e.g. DNA polymerase subunits and 249
tRNA synthetases). These genes are listed in Supplemental table 4d. We ranked these 250
always active genes based on the abundance of reads mapped to them, identifying the 251
number of reads mapped to the gene ranked at the 10th percentile in this list as the 252
threshold expression value. Then in the broader genome, we labeled any gene with 253
mapped reads that exceeded the threshold as active, with all other genes being inactive. 254
Finally, we calculated the binary distance between the transcriptome and flux profiles, 255
excluding any reactions that had been gapfilled, to determine which predicted flux 256
profiles yielded the greatest agreement (i.e. lower binary distance) with the 257
transcriptomic data. 258
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259
We carried out a comparative model analysis on thirty-three KEGG pathway categories 260
involving gene presence and absence, transcriptomic data from CCc, flux analysis, and 261
gap-filled reactions on each pathway category (Figure 3). Carbon fixation pathway 262
categories (i.e. reductive TCA cycle and Wood- Ljungdahl pathways) were lumped into a 263
single category called CO2 fixation. All of the metabolic models, their associated 264
genomes, and the FBA analysis generated in this study are presented using the KBase 265
Narrative Interface (NI) and are accessible at 266
https://narrative.kbase.us/narrative/ws.15248.obj.1. 267
268
Scanning electron microscopy - energy dispersive x-ray spectroscopy (SEM-EDX) 269
Cathodic graphite granules were fixed in 0.1 M sodium cacodylate buffer with 2% 270
gluteraldehyde for three hours, washed in 2.5% osmium tetroxide, and then dehydrated 271
with an ethanol dilution series using 0%, 25%, 50%, 75%, % and 100%. Samples were 272
stored in a desiccator and then coated with Au and Pd using a Denton Vacuum sputter 273
coater. Images were generated using a FEI Quanta 400 Scanning Electron 274
Microscope. 275
276
Data access 277
The metagenomic and metatranscriptome reads can be found in MG-RAST (Meyer et 278
al., 2008) under the ID numbers (and names) 4673464.3-4673467.3 279
(ARPA_metagenome) for the metagenome 280
(http://metagenomics.anl.gov/linkin.cgi?project=15936) and 4536830.3-4536839.3 281
(ARPA_metatranscriptome) for the metatranscriptomes 282
(http://metagenomics.anl.gov/linkin.cgi?project=6065). Assembled contigs for 283
Acetobacterium, Sulfurospirillum, and Desulfovibrio can be accessed at 284
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https://narrative.kbase.us/narrative/ws.15248.obj.1. Raw Illumina sequencing reads have 285
been deposited in the NCBI SRA database under Bioproject PRJNA245339. 286
Additionally, sequencing and assembly files can be found online at 287
https://github.com/sirmicrobe/electrosynthesis. 288
289
Results 290
Performance and compositions of microbial electrosynthesis systems 291
Two high performing MESs inoculated from an established electrosynthetic community 292
were poised at -590 mV vs. a standard hydrogen electrode (SHE), and operated for over 293
100 days, generating an average percentage of total products formed of 65% acetate, 294
34% hydrogen, 0.4% formate, 0.3% propionate and 0.2% butyrate from CO2. At the 295
conclusion of the experiment, one of the two reactors was left at open circuit for three 296
hours to distinguish between transcripts influenced by the supply of electrons from the 297
cathode compared to electrons supplied by hydrogen and/or other free metabolites in 298
the biofilm. Similarly, metatranscriptome samples were taken from the electrode surface 299
and compared to the supernatant. This led to four metatranscriptome samples from two 300
reactors: closed circuit cathode (CCc), closed circuit supernatant (CCs), open circuit 301
cathode (OCc), and open circuit supernatant (OCs). Coulombic efficiencies at time of 302
sampling were 77% and 73% from CC and OC, respectively (Figure 1). Thirteen genome 303
bins spanning 5 different phyla were recovered from the assembled metagenomes taken 304
from the closed circuit MES (Figure 2). Near-complete genomes (89-100% complete) 305
were produced for Sulfurospirillum str. MES7, Acetobacterium str. MES1, Desulfovibrio 306
str. MES5, Methanobacterium str. MES13, Bacteroides str. MES9, Geobacter str. MES3, 307
and Sphaerochaeta str. MES8 (Supplementary Table 2), and a second partially 308
complete (~65%) Desulfovibrio str. MES6 genome was further obtained. 309
Acetobacterium, Sulfurospirillum, and Desulfovibrio combined comprised 40-90% of the 310
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community in each condition, with a Rhodobacteraceae related organism also 311
consistently represented (4-20% relative abundance) (Figure 2, Supplementary Figure 312
2). The 13 annotated genome bins recovered from the CC reactor were used as the 313
basis for transcript mapping and analyses. 314
315
Description of the microbial catalysts 316
Three species, Acetobacterium str. MES1, Sulfurospirillum str. MES7, Desulfovibrio str. 317
MES5, comprised 72% of the total abundance on the active cathode (CCc). The 318
abundance, expression levels, and predominant activity in the reactor (acetogenesis) as 319
well as the known physiology of similar organisms indicates that the Acetobacterium 320
species is the main proponent of carbon fixation on the electrode and thus the keystone 321
species in the microbial community. Genomic and transcriptomic evidence indicates the 322
reconstructed Acetobacterium str. MES1 reduces CO2 to acetate through the Wood-323
Ljungdahl pathway (WLP). WLP-indicative acetyl-CoA synthase/carbon monoxide 324
dehydrogenase (ACS/CODH, aceto.peg.1971-1981) and 5-325
methyltetrahydrofolate:corrinoid iron-sulfur protein methyltransferase (aceto.peg.1978) 326
components were among the most highly expressed genes on the closed circuit 327
electrode surface (Figure 3). Furthermore, the canonical enzyme ACS/CODH had on 328
average >3-fold greater expression on the closed circuit electrode compared to the 329
supernatant as well as higher expression on CCc compared to OCc, indicating that the 330
electrode surface was the major source of acetate production. Interestingly, a 331
Clostridium-type chain elongation pathway(Bruant et al., 2010) was expressed in the 332
Acetobacterium str. MES1 to convert acetyl-CoA to butyrate (aceto.peg.1850-4, 2312), 333
which may explain the butyrate production by the electrosynthetic microbiome 334
(Supplementary Figure 3)(Marshall et al., 2013). 335
336
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Reducing equivalents for the Wood-Ljungdahl pathway, reduced ferredoxin and NADH, 337
were generated by a soluble uptake hydrogenase complex, hydABCDE 338
(aceto.peg.4025-9), which were the most highly expressed Acetobacterium str. MES1-339
associated hydrogenase genes on the electrode. The high expression of hydABCDE and 340
rnfABCDEG gene clusters, suggests Acetobacterium str. MES1 conserves energy 341
similar to A. woodii.(Schuchmann and Müller, 2014) The exception is that MES1 has two 342
Rnf complex copies, one with 15-fold greater gene expression on the electrode surface 343
(high: aceto.peg.2709-14 and low: aceto.peg.926-931). This expression difference is 344
similar to Azotobacter vinelandii whose copy expression disparity is driven by 345
ammonium depletion.(Curatti et al., 2005) Rnf expression positively correlates with 346
nitrogen fixation (nif) gene expression, which is likely because Rnf is required for stable 347
accumulation of the 4Fe4S clusters in nifH.(Jeong and Jouanneau, 2000; Curatti et al., 348
2005) Acetobacterium str. MES1 maintains a nitrogenase gene cluster (nifBEHN) 349
(aceto.peg.248-54) with an adjacent ferredoxin. In fact nifH was in the top 5 most 350
expressed Acetobacterium str. MES1 genes in all conditions, suggesting N-limitation 351
and/or an involvement in electron transfer (Figure 3). As ammonium is depleted, 352
nitrogenase converts protons to hydrogen in the absence of N2 (Ryu et al., 2014), which 353
may contribute to the measured hydrogenesis. This supports previous observations of a 354
lag time between fresh media exchange and the onset of hydrogenesis, and of a positive 355
correlation between Acetobacterium and hydrogen production (LaBelle et al., 2014). It is 356
also possible that electron transfer from the Rnf complex to the nitrogenase for proton 357
reduction is a source of hydrogen production by the electrosynthetic microbiome in this 358
and related studies (LaBelle et al., 2014), and is a potential target for biotechnological 359
exploitation (Ryu et al., 2014). 360
361
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Sulfurospirillum str. MES7 remained consistently abundant (>60% relative abundance) in 362
the supernatant despite frequent exchanges with fresh medium. However, the role of 363
Sulfurospirillum in electrosynthesis has remained elusive (Marshall et al., 2012, 2013). 364
Given its prevalence it must fix CO2 and/or utilize acetate as a carbon source. In support 365
of CO2 fixation, Sulfurospirillum spp. are hypothesized to fix CO2(Goris et al., 2014) and 366
other members of the epsilonproteobacteria can fix CO2 via the reductive tricarboxylic 367
acid (rTCA) cycle (Hügler et al., 2005). As shown here and a recent Sulfurospirillum 368
comparative genomic study (Ross et al., 2016), the Sulfurospirillum str. MES7 assembly 369
contains several genes necessary to overcome the irreversible enzymes of the TCA 370
cycle, including a 2-oxoglutarate oxidoreductase alpha, beta, delta, and gamma subunits 371
(EC 1.2.7.3, sulfuro.peg.1237-40) and fumarate reductase (EC 1.3.5.1, sulfuro.peg.592-372
4). No ATP citrate lyase or citryl-CoA lyase were found, but it does have genes for the 373
conversion of citrate to oxaloacetate + acetate (citrate lyase alpha and beta chains, and 374
citrate (pro-3S)-lyase, EC 4.1.3.6, sulfuro.peg.2133-6), suggesting the possibility of CO2 375
fixation through rTCA. This is also supported by the transcriptional activity of key genes 376
in the rTCA cycle (Supplementary Figure 4). In addition, acetate permease 377
(sulfuro.peg.1580) and acetate kinase (sulfuro.peg.1274) are both highly expressed, 378
indicating either that a supplementary organic carbon source might be required for 379
growth, or that Sulfurospirillum str. MES7 flexibly switches between CO2 fixation and 380
acetate oxidation in the MES reactor. 381
382
By far the most highly expressed genes relating to terminal electron accepting processes 383
in Sulfurospirillum str. MES7 (for any condition) were cytochromes, particularly 384
cytochrome c oxidases. C-type heme-copper oxidases are the final step in the catalytic 385
reduction of oxygen in certain bacteria (Lee et al., 2011) and ccoNOPQ is highly 386
expressed by Sulfurospirillum str. MES7 (sulfuro.peg.1785-8) in all MES conditions. The 387
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high expression of ccoNOPQ suggests Sulfurospirillum str. MES7 is growing 388
microaerobically in the MES, using oxygen as the terminal electron acceptor. This 389
supports the hypothesis that microaerophilic bacteria provide a supportive role to the 390
rest of the community by scrubbing low levels of oxygen that diffuse from the anode 391
chamber. 392
393
Desulfovibrio str. MES5 was the 3rd most abundant taxon, and likely converts CO2 to 394
formate and while using cytochromes, formate dehydrogenase, and/or hydrogenases to 395
accept electrons from the cathode. The high expression of formate dehydrogenase (3-396
fold, dsv-h.peg.194) and cytochromes (6-fold, dsv-h.peg.1195; 6-fold, dsv-h.peg.3868) 397
on the electrode compared to the supernatant supports this hypothesis. The lack of a 398
suitable terminal electron acceptor indicates that Desulfovibrio str. MES5 reduces 399
protons and generates hydrogen gas (Carepo et al., 2002), which is supported by the 400
comparatively high expression of hydrogenases (dsv-h.peg.740-1) on the electrode 401
surface (>3-fold CCc vs. CCs). Furthermore, Desulfovibrio spp. have been shown to 402
interact with a cathode to facilitate electrohydrogenesis.\ (Aulenta et al., 2012; Croese et 403
al., 2011; Yu et al., 2011). It is likely that small amounts of acetate from Acetobacterium 404
str. MES1 are used as a supplementary carbon source for Desulfovibrio str. MES5, but 405
based on the high hydrogenase and low acetate kinase expression pattern the majority 406
of reducing potential comes from the electrode. 407
408
While Acetobacterium str. MES1, Sulfurospirillum str. MES7, and Desulfovibrio str. 409
MES5 can explain most of the activity occurring in the microbial electrosynthesis 410
systems, the remaining genomes have broad metabolic capabilities, but are typically in 411
lower abundance (<7%). We hypothesize that they are consuming detritus, degradation 412
products, and/or short chain fatty acids generated by the abundant organisms. A pan-413
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genome associated with the Rhodobacteraceae family had an expression profile 414
consistent with acetate oxidation and cbb3-type cytochrome c oxidases that could be 415
indicative of microaerobic growth. The latter have been expressed in Rhodobacter sp. 416
growing in microaerobic and anaerobic conditions (Kaplan et al., 2005) and were also 417
found to be upregulated by Shewanella oneidensis MR-1 growing on electrodes 418
(Rosenbaum et al., 2012). While we are hypothesizing that these cytochrome c oxidases 419
in Rhodobacteraceae str. MES12 and Sulfurospirillum str. MES7 are involved in 420
microaerobic growth, given their prominence in this study and others involving 421
bioelectrochemical systems (Rosenbaum et al., 2012), their role in EET should be 422
investigated further. One of two Bacteroides genomes (str. MES10) was closely related 423
(93% sequence identity) to Proteiniphilum acetatigenes, which has been shown to 424
generate acetate when growing on wastewater cell debris(Chen, 2005) and Croese et al. 425
discovered a relatively high abundance of uncultured Bacteroides in a hydrogen 426
producing biocathode community (Croese et al., 2013), suggesting possible productive 427
roles for the Bacteroides str. MES9 and MES10 in the electrosynthetic microbiome. 428
Interestingly, Bacteroides str. MES9 expresses a butanol dehydrogenase (bacteroid-429
h.peg.1751) on the electrode surface, which suggests that changing the operating 430
conditions of the MES could produce biofuels and other valuable products (see 431
Bioprospecting section in supporting materials). Additionally, both Bacteroides genomes 432
and the Sphaerochaeta str. MES8 genome exhibited high expression of ferredoxin 433
genes (bacteroid-h.peg.3284, bacteroid-l.peg.2157, sphaer.peg.2014), which may be 434
used to shuttle electrons for community metabolism. 435
436
Metabolic model reconstructions and analysis 437
Genome-scale metabolic models were constructed for the three dominate species in the 438
electrosynthetic community (see methods): Acetobacterium str. MES1, Sulfurospirillum 439
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17
str. MES7, and Desulfovibrio str. MES5. These models were then used, in combination 440
with flux balance analysis (Orth et al., 2010), to predict the metabolic activity of each of 441
these species during microbial community growth on the electrode. The accuracy of 442
these flux predictions was evaluated by calculating the fraction of active reactions 443
predicted by the models that were associated with actively expressed genes, as 444
determined from the metatranscriptomic data (Table 1 and methods). In this analysis, 445
the Acetobacterium model displayed only one plausible flux profile, which involved 446
carbon fixation and acetate production via the Wood-Ljungdahl pathway using hydrogen, 447
raw electrons, or similar reducing equivalents as an electron source. With this flux 448
profile, there were 338 active reactions with associated genes in Acetobacterium, and for 449
258 (76%) of these reactions, at least one of the associated genes was actively 450
expressed. Most active reactions that lacked expression support were involved in either 451
amino acid biosynthesis or nucleotide metabolisms. The Sulfurospirillum model 452
predicted two alternative theories for the metabolic role of this species: (i) reduction of 453
CO2 through the reductive TCA cycle with hydrogen used as the reducing agent (67% of 454
active reactions associated with at least one expressed gene), and (ii) oxidation of 455
acetate coupled to O2 reduction (66% of active reactions associated with at least one 456
expressed gene). Given the nearly equal agreement of both of these operating with our 457
transcriptome data, and given the high abundance of Sulfurospirillum in our community, 458
it is possible Sulfurospirillum actually performs both roles depending on its context and 459
environment. The Desulfovibrio model also predicted two alternative theories for the 460
metabolic role of this species in our electrosynthetic microbiome: (i) conversion of CO2 461
and electrons/hydrogen to formate (75.7% of active reactions associated with at least 462
one expressed gene), or (ii) consumption of acetate (75.9% of active reactions 463
associated with at least one expressed gene). As with Sulfurospirillum, the expression 464
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data was equally supportive of both metabolic theories, indicating that Desulfovibrio also 465
performs a combination of carbon-fixation and acetate utilization. 466
467
In addition to evaluating the overall evidence supporting each of our predicted flux 468
profiles, the transcriptome data was also applied to evaluate the flux profiles on a 469
pathway-by-pathway basis, enabling a better understanding of model accuracy, and 470
revealing insights into potential interspecies interactions (see Methods and Figure 4). 471
Generally, this analysis showed a large degree of agreement between predicted flux 472
profiles and expression data, with some notable exceptions: (i) the terpenoid pathways 473
in all our models were gap-filled because the models all include ubiquinone as a 474
component of biomass, but there is little evidence for these pathways in our genomes 475
and it is likely these genomes are functioning anaerobically and do not have to produce 476
ubiquinone; (ii) the Acetobacterium and Desulfovibrio models both appear to overuse 477
their pentose-phosphate-pathways compared to what would be expected based on 478
expression data; (iii) the Desulfovibrio model overuses its thiamin pathway and should 479
actually obtain thiamin from an external source according to expression data; (iv) the 480
Sulfurospirillum model overuses its sulfur and nitrogen metabolism pathways; and (v) all 481
three models appear to underutilize the vitamin B6 and fructose and mannose 482
metabolism pathways. 483
484
The pathway-based model analysis (Figure 4) reveals interactions and dependencies 485
among the top genomes. Desulfovibrio appears to require an external source of 486
histidine, thiamin, riboflavin, and folate, while the other genomes could be sources of all 487
four of these compounds due to depletion or absence in the supplied medium. 488
Acetobacterium appears to be unique in making glutathione, and also has far more 489
representation in carbon fixation than the other genomes. In contrast, Sulfurospirillum 490
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appears unique in possessing an active glyoxylate metabolism and the most active TCA 491
cycle. It is interesting to note that all three genomes appear to produce most of their own 492
amino acids, vitamins, and nucleotides, with Desulfovibrio being the least prototrophic of 493
the three. Biochemical reaction equations, compounds, associated flux values, and 494
comparative genomics tools including hypothetical gene knockout experiments for all the 495
models can be found at the KBase Narrative Interface: 496
https://narrative.kbase.us/narrative/ws.15248.obj.1. 497
498
Discussion 499
Metabolic analysis and modeling of this unique microbial community capable of 500
converting CO2 into volatile fatty acid provides a detailed look into how communities 501
actively metabolize on an electrosynthetic biocathode. The genome-wide metabolic 502
capabilities of microorganisms in the community were determined, and a putative 503
metabolic model of the primary community members has been summarized (Figure 5). 504
CO2 fixation and the carbon flux through the electrosynthetic microbiome center on the 505
Wood-Ljungdahl pathway of the Acetobacterium genome, components of which were 506
more active on the closed circuit electrode compared to any other condition tested, 507
demonstrating the importance of electrode-associated growth by Acetobacterium. In 508
addition, reducing equivalents in the form of hydrogen and reduced enzymes (eg. 509
ferredoxin) also stem from the Acetobacterium, alongside major contributions from 510
Desulfovibrio and Sulfurospirillum. Other organisms in the community are contributing to 511
overall fitness by scrubbing toxic compounds (e.g. oxygen) and providing nutrient 512
exchange. Given the proper conditions and applied drivers, this electrosynthetic 513
microbial community has a wide range of biotechnological potential, including the 514
production of alcohols, 2,3-butanediol, and polyhydroxyalkonoates (see supplementary 515
note on bioprospecting and Supplementary Table 4 for more detailed information). 516
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517
Generally, the proposed mechanisms for cathodic electron transfer in the absence of 518
added mediators are analogous to anodic electron transfer, namely that cytochromes 519
are the primary conduit of electrons to and from the microbial cell (Holmes et al., 2006; 520
Leang et al., 2010; Ross et al., 2011; Inoue et al., 2011; Carlson et al., 2012). The role of 521
cytochromes on anodes has been primarily elucidated in pure culture, but 522
metatranscriptomic studies also point to cytochrome involvement in EET to anodes (Ishii 523
et al., 2013, 2015) and even less is known about EET in communities grown on 524
cathodes. In this study, Desulfovibrio str. MES5 has three upregulated cytochromes on 525
the electrode compared to the supernatant: two with a 6-fold increase (dsv-h.peg.1195 526
and dsv-h.peg.3868) and one with a 2.5-fold increase (dsv-h.peg.1225). The latter two 527
were upregulated greater than 2-fold on the closed circuit cathode compared to the open 528
circuit cathode. Additionally, a formate dehydrogenase from Desulfovibrio str. MES5 529
(dsv-h.peg.194) was upregulated nearly 3-fold on the electrode compared to 530
supernatant, >2-fold CCc versus OCc, and could explain formate transiently observed in 531
the supernatant (Supplementary Figure 3) (Marshall et al., 2013)(da Silva et al., 2013). 532
In addition to their involvement in electron transfer at cathode surfaces, cytochromes can 533
also act as natural mediators for hydrogenases (Pereira et al., 1998; Yahata et al., 2006) 534
and could shuttle electrons from the electrode or from electrode-attached hydrogenases 535
to the microbial community. Three NiFe hydrogenases were highly expressed by 536
Desulfovibrio str. MES5 on the electrode compared to the supernatant (dsv-h.peg.740-537
741, >3-fold and 6-fold increase on electrode compared [CCc] to supernatant [CCs]; and 538
dsv-h.peg.1193, 6-fold increase on electrode [CCc] compared to supernatant [CCs]). 539
One of the NiFe hydrogenases (dsv-h.peg.1193) was adjacent to the upregulated high 540
molecular weight cytochrome c (dsv-h.peg.1195). Given the high expression on the 541
cathode compared to supernatant, it is hypothesized that cytochromes, hydrogenases, 542
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and possibly formate dehydrogenases associated with Desulfovibrio str. MES5 act as 543
electron mediators between the electrode and the cell to deliver reducing equivalents. In 544
addition to the well-established role of cell-bound cytochromes in direct electron 545
transport with an electrode (Bond et al., 2012; Pirbadian et al., 2014), free cytochromes 546
have been shown to be integral to anodic electron transfer while still imbedded in the 547
biofilm matrix, and could be assisting electron transport to the community in this 548
electrosynthetic biofilm (Inoue et al., 2011). 549
550
The recent discovery that extracellular enzymes (likely hydrogenases and formate 551
dehydrogenases) may be present in cathodic biofilms and may catalyze electron transfer 552
into microbially-utilizable substrates (hydrogen and formate) adds a new and important 553
piece to solve the EET mechanistic puzzle (Deutzmann et al., 2015). Of the genes highly 554
expressed on the electrode, several redox-active electron carriers (particularly 555
hydrogenases and ferredoxins) had high differential expression on the poised electrode 556
compared to the supernatant and open circuit electrode. A Sulfurospirillum str. MES7 557
ferredoxin (sulfuro.peg.2444) is >2-fold higher on the electrode compared to the 558
supernatant (1.5x higher CCc vs. OCc) and the low abundance Bacteroides str. MES10 559
contains a ferredoxin (bacteroid-l.peg.2157) that is >9-fold upregulated on the electrode 560
compared to supernatant (1.7x higher CCc vs. OCc). Importantly, a ferredoxin from 561
Acetobacterium str. MES1 (aceto.peg.1713) was 7-fold higher on the electrode (CCc) 562
compared to both supernatant conditions (CCs and OCs). Additionally, the highly 563
expressed Acetobacterium str. MES1 hydrogenase gene cluster, hydABCDE 564
(aceto.peg.4025-4029), had >5-fold higher expression per cell on the electrode 565
compared to the supernatant (1.6x higher CCc vs. OCc), despite the presence of 566
hydrogen in the supernatant. The combination of soluble hydrogenases and ferredoxins 567
on the cathode could facilitate cathodic electron transfer into organisms like 568
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Acetobacterium that contain no cytochromes and no obvious means of electron transfer 569
through the cell envelope. 570
571
Despite the lack of a redox-active signal in cell-free cyclic voltammograms and a 572
catalytic wave characteristic of direct electron transfer in the electrosynthetic microbial 573
community (Marshall et al., 2013), SEM-EDX images show extracellular material with 574
elemental signatures of common redox-active enzymes (Supplementary Figure 5). 575
Additionally, no reduction in current or shift in the voltammetric peaks were observed 576
when the supernatant was replaced with fresh medium, suggesting tightly bound 577
electron transfer mechanisms. The discovery of metals such as iron and nickel on the 578
electrode surface could be concentrated enzymes, but microbial or pH induced 579
precipitation of the metals as (hydr)oxides, sulfides, carbonates, phosphates, perhaps 580
even as nanoparticles cannot be ruled out. The latter has been hypothesized by Jourdin 581
et al. who observed copper concentrated on the surface of a microbial electroacetogenic 582
cathode (Jourdin et al., 2016). 583
584
Based on the highly expressed redox active proteins on the electrode (all of the proteins 585
mentioned above are in the top 5% of total genes expressed on the electrode), and the 586
consistent hydrogen production in the reactors (Marshall et al., 2012, 2013; LaBelle et 587
al., 2014), extracellular enzymes and/or concentrated metals are likely functionalizing 588
the electrode while hydrogen, ferredoxins, and/or cytochromes act as shuttles for 589
different organisms in the biofilm. This would explain why microbes lacking an outer 590
membrane can thrive on an electrode, and why previous studies ran electrohydrogenic 591
biocathodes that could sustain hydrogen generation in the absence of a carbon source 592
for over 1000 hours (Rozendal et al., 2008). Further studies are underway to fully 593
characterize functionalization of electrodes by microbes so as to optimize this strategy. 594
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595
The modeling results demonstrate how metabolic models are useful for interpreting 596
expression data in order to predict the role of individual species participating within a 597
mixed microbial community. The model predictions: (i) confirmed the role of 598
Acetobacterium as the primary species utilizing electrons to reduce CO2; (ii) identified 599
the more complex behavior of Sulfurospirillum as both reducing CO2 and utilizing 600
acetate; and (iii) provided more depth and detail into our understanding of the 601
heterotrophic growth of Desulfovibrio. These models refined models should prove to be 602
a resource for ongoing efforts to understand, and ultimately design and refine 603
electrosynthetic microbiomes. 604
605
We have provided insights into the genetic basis of electrosynthetic microbial 606
communities, which can be used for the optimization of microbial electrosynthesis 607
through operational changes and eventual pathway engineering. Furthermore, it was 608
demonstrated that a diverse set of microorganisms could be active in limited niche space 609
with carbon dioxide as the only carbon source and the electrode as the only electron 610
donor. The discovery that predominant members of the community provide an 611
ecosystem service by scrubbing oxygen makes this, and similar, electrosynthetic 612
microbial communities valuable for practical application. If deployed in true carbon-613
capture situations such as power plants or industrial exhaust lines, oxygen scrubbing to 614
protect the electrosynthetic anaerobes will be important. Finally, the comprehensive 615
analysis of the genomes and development of metabolic models provide the framework to 616
boost production rates and elevate this system to a platform chemical synthesis 617
technology. 618
619Acknowledgements 620
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We thank Drew Latta for SEM-EDX work and Fangfang Xia and Sebastien Boisvert for 621initial metagenome assembly advice. C.W.M. was supported in part by an Argonne 622National Laboratory Director's Fellowship. The project was funded by the Department of 623Energy, Advanced Projects Research Agency – Energy (DE-AR0000089) and Office of 624Naval Research: Grant# N00014-15-1-2219. We also acknowledge the University of 625Chicago Research Computing Center for their support. 626 627Conflict of Interest 628The authors declare no competing financial interests. 629 630References 631 632AlbertsenM,HugenholtzP,SkarshewskiA,NielsenKL,TysonGW,NielsenPH.633(2013).Genomesequencesofrare,unculturedbacteriaobtainedbydifferential634coveragebinningofmultiplemetagenomes.NatBiotechnol31:533–538.635
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Table 1. Transcriptome support for metabolic activity predicted by models 833Species Description Active
reactions^ Supported reactions*
Expressed genes
Acetobacterium C02 fixation to acetate 338/1244 258/338 402/954 Sulfurospirillum Reduction of CO2 328/1143 219/328 252/661 Sulfurospirillum Oxidation of acetate 330/1142 218/330 252/661 Desulfovibrio Conversion of CO2 to formate 322/1124 244/322 425/759 Desulfovibrio Consumption of acetate 320/1124 243/320 425/759 ^Active reactions only include reactions with associated genes (gapfilled reactions 834filtered out) 835 *Supported reactions are active reactions (gapfilled reactions filtered out) associated 836with at least one actively expressed gene 837 838
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Figure 1. Reactor performance over time. (A) Acetate production in CC and OC – breaks 839in plotted lines indicate an exchange of the medium, (B) acetate production rate in CC 840and OC, and (C) accounting of the coulombs over a seven day period between medium 841exchanges in CC and OC, numbers are percent coulombic efficiency with total percent 842efficiency averaged over the 7 days in parentheses. 843
844
0
25
50
75
100
125
0 50 100 150Time (days)
Ace
tate
Pro
duct
ion
(mM
)
variableCC_acetate
OC_acetate
0
3
6
9
0 50 100 150Time (days)
Ace
tate
Pro
duct
ion
Rat
e (m
M d
ay −
1)
ReactorCC
OC
A B
C
0
1000
2000
3000
4000
178 180 182 184Time (days)
Cou
lom
bs
acetate_cchydrogen_cctotal_cccoulombs.consumed_ccacetate_ochydrogen_octotal_occoulombs.consumed_oc
123%
89%
81%
73%
73%
74%
77% (84%)
66%
72%
74%
73%
73%
72%
73% (72%)
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Figure 2. (A) Phylogenetic tree of the CCc microbial community using EMIRGE-based 845reconstructed 16S rRNA gene sequences (blue) and relative abundance values in 846parentheses and indicated by the relative size of the blue circle. Sequences were 847aligned using MUSCLE and the evolutionary history was inferred using the Maximum 848Likelihood method based on the Jukes-Cantor model. Bootstrapping support greater 849than 50% is indicated on the tree and is based on 1,000 iterations. (B) ESOM based on 850tetranucleotide frequency in the CC cathode metagenome. 851 852 853
854 855 856
13 Methanobacterium (2.9%)
CP000577 Rhodobacter sphaeroides
8 Sphaerochaeta (1.6%)
U13928 Geobacter sulfurreducens
JX575921 uncultured Petrimonas sp.
X82931 Sulfurospirillum multivorans
EU258744 Mycoplana peli
CP000148Geobacter metallireducens GS-15
AF357916 Sphaerochaeta globosa str. Buddy
AF192154 Desulfovibrio desulfuricans subsp. desulfuricans
KC488627 Ochrobactrum anthropi
GU356639 Rhizobium borbori
13 Methanobacterium2 (1.2%)
AB548675 Dysgonomonas gadei
AB245368 Pedobacter panaciterrae
12 Haematobacter [Rhodobacteraceae](6.8%)
AB669242 uncultured Bacteroidetes bacterium
1 Acetobacterium(30.6%)
AY693830 Porphyromonadaceae uncultured bacterium
3 Geobacter (1.7%)
AF169245 Methanobacterium formicicum
KF309178 Rhodobacter sp. W04
10 Petrimonas [Bacteroid-l](<1%)
AB603520 Desulfovibrio simplex
AB246781 Sulfurospirillum cavolei
AF093061 Methanobacterium palustre
FN646438 uncultured Bacteroidetes bacterium
CP002273 Eubacterium limosum KIST612
AB020205 Sphingobacterium multivorum
CP002987 Acetobacterium woodii DSM 1030
8 Sphaerochaeta2 (1%)
10 Paludibacter [Bacteroid-l](<1%)
AZAO01000007 Desulfovibrio termitidis HI1
KF836224 Sulfurospirillum uncultured bacterium
6 Desulfovibrio-l (4.8%)
2 Desulfuromonadales(<1%)
9 Bacteroid-h (3.1%)
5 Desulfovibrio-h (18.6%)
FN430569 Thioclava sp. JC56
7 Sulfurospirillum (23.9%)
AF276958 Methanobacterium curvum
X96955 Acetobacterium wieringae
CP001197 Desulfovibrio vulgaris str. Miyazaki F
U46860 Geobacter hydrogenophilus
4 Desulfovibrio-ul (<1%)
AB078842 Paludibacter propionicigenes
AF233586 Methanobacterium congolense
HQ012835 Acetobacterium sp. enrichment culture clone DhR2/LM-A07
11 Rhizobium(<1%)
JN944166 Sphaerochaeta sp. GLS2
100
99
10074
86
54
8687
100
10087
73
7354
100
100100
54100
62
80
99 100
100
70 100
100
83
59
100
100
91
77
99
9677
Tree scale: 0.1
A B
122
3
4
56
12
11
78
91013
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Figure 3. Expression profile and comparative expression of important genes. The green 857panel shows relative expression between microorganisms and the red panel compares 858differential expression between condition 859
860
4.63
CCc vs.CCs
CCc vs.OCs
CCc vs.OCc
Log2 Fold Change
2.91
2.29
1.51
0.37
1.57
0.78
0.57
1.09
1.55
1.18
1.40
2.60
3.06
2.23
3.06
3.65
2.23
3.23
−0.33
0.53
2.83
2.86
1.32
0.11
1.71
0.62
−1.05
1.77
0.48
0.30
1.19
2.23
2.08
1.75
3.58
3.39
2.57
2.46
−0.11
−0.83
electrode_v_sup_reca_log
electrode_v_bsup_reca_log
electrode_v_offelectrode_reca_lo
aceto.peg.1713;Ferredoxin
aceto.peg.4025−9;hydABCDE hydrogenase
aceto.peg.2709−14;rnfABCDEG
aceto.peg.926−31;rnfABCDEG
aceto.peg.1972−81;CODH/ACS
aceto.peg.250;Nitrogenase (molybdenum−iron) beta chain
sulfuro.peg.2373;Flagellin
sulfuro.peg.2444;Ferredoxin
dsv−h.peg.194−8;Formate dehydrogenase
dsv−h.peg.200;cytochrome c3
dsv−h.peg.1225;cytochrome c3
dsv−h.peg.3868;Split−Soret cytochrome c
dsv−h.peg.1193−7;NiFe hydrogenase/Carbonic anhydrase
dsv−h.peg.740−1;NiFe hydrogenase
dsv−h.peg.3404;Pyruvate formate−lyase
rhodo.peg.7409;Superoxide dismutase [Mn]
rhodo.peg.4106;Catalase
bacteroid−l.peg.2157;Ferredoxin
bacteroid−h.peg.3284;4Fe−4S ferredoxin iron−sulfur binding
sphaer.peg.2014;Ferredoxin
−4
−2
0
2
4
CCc CCs OCcOCc
Ferredoxin
hydABCDE hydrogenase
rnfABCDEG
rnfABCDEG
CODH/ACS
Nitrogenase beta chain
Flagellin
Ferredoxin
Formate dehydrogenase
cytochrome c3
cytochrome c3
Split−Soret cytochrome c
hydrogenase/Carbonic anhydrase
NiFe hydrogenase
Pyruvate formate−lyase
Superoxide dismutase [Mn]
Catalase
Ferredoxin
Ferredoxin
Ferredoxin
−4
−2
0
2
4
aceto.peg.1713
aceto.peg.4025−9
aceto.peg.2709−14
aceto.peg.926−31
aceto.peg.1972−81
aceto.peg.250
sulfuro.peg.2373
sulfuro.peg.2444
dsv−h.peg.194−8
dsv−h.peg.200
dsv−h.peg.1225
dsv−h.peg.3868
dsv−h.peg.1193−7
dsv−h.peg.740−1
dsv−h.peg.3404
rhodo.peg.7409
rhodo.peg.4106
bacteroid−l.peg.2157
bacteroid−h.peg.3284
sphaer.peg.2014
Expression (RPKM)
OCc OCs
aceto.peg.1713;Ferredoxin
aceto.peg.4025−9;hydABCDE hydrogenase
aceto.peg.2709−14;rnfABCDEG
aceto.peg.926−31;rnfABCDEG
aceto.peg.1972−81;CODH/ACS
aceto.peg.250;Nitrogenase (molybdenum−iron) beta chain
sulfuro.peg.2373;Flagellin
sulfuro.peg.2444;Ferredoxin
dsv−h.peg.194−8;Formate dehydrogenase
dsv−h.peg.200;cytochrome c3
dsv−h.peg.1225;cytochrome c3
dsv−h.peg.3868;Split−Soret cytochrome c
dsv−h.peg.1193−7;NiFe hydrogenase/Carbonic anhydrase
dsv−h.peg.740−1;NiFe hydrogenase
dsv−h.peg.3404;Pyruvate formate−lyase
rhodo.peg.7409;Superoxide dismutase [Mn]
rhodo.peg.4106;Catalase
bacteroid−l.peg.2157;Ferredoxin
bacteroid−h.peg.3284;4Fe−4S ferredoxin iron−sulfur binding
sphaer.peg.2014;Ferredoxin
05001000
7000
05001000
7000
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Figure 4. Pathway flux and model agreement with expression data. The degree of 861agreement between the model-based flux predictions and expression data for each of 862the three metabolic models is shown, both for the entire models and broken down by 863categories of metabolism. In the graph, reactions are divided into five categories based 864on their flux and the expression of their associated genes: (i) reactions that are active 865and associated with at least one expressed gene (dark blue); (ii) reactions that are 866inactive and associated only with unexpressed genes (dark red); (iii) reactions that are 867inactive and associated with one or more expressed genes (green); (iv) reactions that 868are active and associated only with unexpressed genes (purple); and (v) gapfilled 869reactions associated with no genes. The dark blue and dark red categories indicate 870agreement between the models and expression data; purple and green categories 871indicate disagreement. 872
8730% 50% 100% 0% 50% 100% 0% 50% 100%
En(remodel
Centralcarbonmetabolism
Fa7yacidmetabolism
Aminoacidmetabolism
Carbonfixa(on
Electrontransport
Nucleicacidbiosynthesis
Aminoacidbiosynthesis
Bvitaminbiosynthesis
Cellwallandlipidbiosynthesis
Fluxandexpression Nofluxorexpression Expression/Noflux Flux/Noexpression Gapfilling
Acetobacterium Sulfurospirillum Desulfovibrio
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Figure 5. Hypothetical model of key metabolic activities and interactions among 874dominant members of the electrosynthetic microbial community. 875
876 877 878 879 880 881 882 883884885886 887
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