| Literature DB >> 32605988 |
Andy O Leu1, Simon J McIlroy1,2, Jun Ye1, Donovan H Parks1, Victoria J Orphan3, Gene W Tyson4,2.
Abstract
Anaerobic oxidation of methane (AOM) is an important biological process responsible for controlling the flux of methane into the atmosphere. Members of the archaeal family Methanoperedenaceae (formerly ANME-2d) have been demonstrated to couple AOM to the reduction of nitrate, iron, and manganese. Here, comparative genomic analysis of 16 Methanoperedenaceae metagenome-assembled genomes (MAGs), recovered from diverse environments, revealed novel respiratory strategies acquired through lateral gene transfer (LGT) events from diverse archaea and bacteria. Comprehensive phylogenetic analyses suggests that LGT has allowed members of the Methanoperedenaceae to acquire genes for the oxidation of hydrogen and formate and the reduction of arsenate, selenate, and elemental sulfur. Numerous membrane-bound multiheme c-type cytochrome complexes also appear to have been laterally acquired, which may be involved in the direct transfer of electrons to metal oxides, humic substances, and syntrophic partners.IMPORTANCE AOM by microorganisms limits the atmospheric release of the potent greenhouse gas methane and has consequent importance for the global carbon cycle and climate change modeling. While the oxidation of methane coupled to sulfate by consortia of anaerobic methanotrophic (ANME) archaea and bacteria is well documented, several other potential electron acceptors have also been reported to support AOM. In this study, we identify a number of novel respiratory strategies that appear to have been laterally acquired by members of the Methanoperedenaceae, as they are absent from related archaea and other ANME lineages. Expanding the known metabolic potential for members of the Methanoperedenaceae provides important insight into their ecology and suggests their role in linking methane oxidation to several global biogeochemical cycles.Entities:
Keywords: ANME; AOM; Methanoperedenaceaezzm321990; comparative genomics; methane
Mesh:
Substances:
Year: 2020 PMID: 32605988 PMCID: PMC7327174 DOI: 10.1128/mBio.01325-20
Source DB: PubMed Journal: mBio Impact factor: 7.867
Characteristics of the metagenome-assembled genomes
| Bin ID | Genome | No. of | Strain | Compl. | Cont. | %GC | No. of | Source environment and | Accession no. | 16S | |
|---|---|---|---|---|---|---|---|---|---|---|---|
| ASW-1 | 1.52 | 271 | 7,386 | 0.0 | 87.5 | 0.0 | 47.8 | 1,946 | Arsenic-contaminated | N | |
| ASW-2 | 2.63 | 157 | 28,058 | 25.0 | 94.4 | 4.8 | 48.0 | 2,944 | Arsenic-contaminated | N | |
| ASW-3 | 2.51 | 100 | 44,967 | 0.0 | 100.0 | 1.3 | 50.7 | 2,892 | Arsenic-contaminated | N | |
| ASW-4 | 2.24 | 155 | 24,336 | 0.0 | 97.1 | 0.7 | 43.2 | 2,464 | Arsenic-contaminated | N | |
| ASW-5 | 2.97 | 221 | 19,046 | 0.0 | 95.0 | 2.6 | 48.9 | 3,353 | Arsenic contaminated | N | |
| ASW-6 | 2.19 | 68 | 56,691 | 66.7 | 99.4 | 2.0 | 46.6 | 2,472 | Arsenic-contaminated | Y | |
| BLZ1 | 3.74 | 514 | 17,508 | 13.33 | 96.73 | 6.56 | 40.2 | 4,659 | AOM-nitrate bioreactor, | Y | |
| BLZ2 | 3.74 | 85 | 74,304 | 0.0 | 99.4 | 4.6 | 40.3 | 4,041 | AOM-nitrate reactor, | GCA_002487355.1 | N |
| CMD-1 | 1.85 | 116 | 27,949 | 100.0 | 98.0 | 0.7 | 44.9 | 2,261 | Copper mine tailings dam, | N | |
| CMD-2 | 1.45 | 221 | 9,704 | 0.0 | 88.4 | 0.0 | 44.1 | 1,786 | Copper mine tailings dam, | N | |
| HGW-1 | 2.00 | 128 | 24,496 | 33.3 | 96.4 | 2.0 | 43.2 | 2,288 | Groundwater samples, | GCA_002839545.1 | Y |
| IPS-1 | 3.52 | 250 | 27,331 | 10.0 | 97.7 | 5.9 | 44.1 | 3,970 | AOM-nitrate bioreactor | GCA_900196725.1 | Y |
| M.Ferri | 2.91 | 59 | 88,069 | 0.0 | 98.7 | 1.3 | 40.8 | 3,019 | AOM-iron bioreactor, | GCA_003104905.1 | Y |
| M.Nitro | 3.20 | 10 | 54,4976 | 0.0 | 99.7 | 1.3 | 43.2 | 3,428 | AOM-nitrate bioreactor, | GCA_000685155.1 | Y |
| MGW-1 | 2.08 | 161 | 17,186 | 0.0 | 97.4 | 3.6 | 44.8 | 2,488 | Groundwater samples, | Not available | N |
| Mn-1 | 3.59 | 68 | 87,551 | 0.0 | 100.0 | 1.3 | 40.6 | 3,737 | AOM-manganese | N | |
| Mn-2 | 3.32 | 116 | 49,809 | 0.0 | 99.4 | 4.6 | 42.9 | 3,684 | AOM-manganese | N |
Completeness (compl.), contamination (cont.), and strain heterogeneity were estimated using CheckM (33).
Genome accession numbers. For the MAGs assembled in this study the SRA accession numbers are also given.
The BLZ1 genome was not used in analyses, as it is almost identical to the BLZ2 genome (99.5% ANI) and has inferior completeness and contamination values. The BLZ1 bioreactor was the parent system of the BLZ2 bioreactor.
This genome was provided by Yohey Suzuki and is associated with the study of Ino and colleagues (30).
CDSs, coding sequences; N, no; Y, yes.
FIG 1Phylogenetic placement of the Methanoperedenaceae MAGs and distribution of potential terminal electron acceptors. The genome tree was inferred using maximum likelihood with a concatenated set of 122 archaeon-specific marker genes. Black and white dots indicate >90% and >70% bootstrap values, respectively. The scale bar represents amino acid nucleotide changes. Based on GTDB-Tk, the family Methanoperedenaceae includes three genera, including “Ca. Methanoperedens,” which are denoted with brackets. The table to the right of the tree shows the presence/absence of genes associated with potential terminal electron acceptors in each corresponding Methanoperedenaceae genome.
FIG 2Metabolic capabilities of the Methanoperedenaceae. Key metabolic pathways for the anaerobic oxidation of methane, energy conservation mechanisms, hydrogen and formate oxidation, and electron acceptors found within the pangenome of the Methanoperedenaceae. Numbers 1 to 5 indicate the different menaquinone:cytochrome c oxidoreductases conserved in the Methanoperedenaceae MAGs (Data Set S1A). Abbreviations for enzymes and cofactors in the figure are as follows: H4MPT, tetrahydromethanopterin; MFR, methanofuran; Fwd, formyl-methanofuran dehydrogenase; Ftr, formylmethanofuran/H4MPT formyltransferase; Mch, methenyl-H4MPT cyclohydrolase; Mtd, F420-dependent methylene H4MPT dehydrogenase; Mer, F420-dependent methylene-H4MPT reductase; Mtr, Na+-translocating methyl-H4MPT:coenzyme M (CoM) methyltransferase; Mcr, methyl-CoM reductase; F420, F420 coenzyme; Fd, ferredoxin; CoM-SH, coenzyme M; CoB-HS, coenzyme B; Hdr, heterodisulfide reductase; Fpo, F420H2 dehydrogenase; Hyd, type 1 NiFe hydrogenase; Hyh, type 3b NiFe hydrogenase; Fdh, formate dehydrogenase; Nar, nitrate reductase; Nrf, nitrite reductase; Srd, selenate reductase; Sre, sulfur reductase; Arx, arsenite oxidase; Arr, arsenate reductase; DIET, direct interspecies electron transfer.
FIG 3Phylogenetic analysis of the catalytic subunits of the CISM superfamily. Putative genes recovered from the Methanoperedenaceae are indicated in red. The gene tree was inferred by maximum likelihood, and support values were calculated via nonparametric bootstrapping. Black and white dots indicate >90% and >70% bootstrap support, respectively. The scale bar represents amino acid changes. ACTB1, alternate complex III, domain of subunit B; ArrA, arsenate reductase; ArxA, arsenite oxidase; AthL, pyrogallol hydroxytransferase; BisC, biotin sulfoxide reductase; ClrA, chlorate reductase; EbdA, ethylbenzene dehydrogenase; s25dA, C25 dehydrogenase; DmsA, DMSO reductase; DorA, DMSO reductase; NapA, nitrate reductase; NarG, nitrate reductase; NasA, assimilatory nitrate reductase; NarB, assimilatory nitrate reductase; NxrA, nitrite oxidoreductase; PsrA, polysulfide reductase; PhsA, thiosulfate reductase; QrcB, quinone reductase complex; TtrA tetrathionate reductase; DmsA, PcrA, perchlorate reductase; SrdA, Selenate reductase; SreA, sulfur reductase; TorA, trimethylamine N-oxide (TMAO) reductase; XdhA, xanthine dehydrogenase; FdhA, formate dehydrogenase; rhL, resorcinol hydroxylase; Unk, unknown putative reductase. Amino acid sequences are included in Data Set S1B.