Abstract
Aminobacter sp. MSH1 (CIP 110285) can use the pesticide dichlobenil and its recalcitrant transformation product, 2,6-dichlorobenzamide (BAM), as sole source of carbon, nitrogen, and energy. The concentration of BAM in groundwater often exceeds the threshold limit for drinking water, requiring additional treatment in drinking water treatment plants or closure of the affected abstraction wells. Biological treatment with MSH1 is considered a potential sustainable alternative to remediate BAM-contamination in drinking water production. We present the complete genome of MSH1, which was determined independently in two institutes at Aarhus University and KU Leuven. Divergences were observed between the two genomes, i.e. one of them lacked four plasmids compared to the other. Besides the circular chromosome and the two previously described plasmids involved in BAM catabolism, pBAM1 and pBAM2, the genome of MSH1 contained two megaplasmids and three smaller plasmids. The MSH1 substrain from KU Leuven showed a reduced genome lacking a megaplasmid and three smaller plasmids and was designated substrain MK1, whereas the Aarhus variant with all plasmids was designated substrain DK1. A plasmid stability experiment indicate that substrain DK1 may have a polyploid chromosome when growing in R2B medium with more chromosomes than plasmids per cell. Finally, strain MSH1 is reassigned as Aminobacter niigataensis MSH1.
Similar content being viewed by others
Introduction
The occurrence of organic micropollutants in different water compartments threatens both ecosystem functioning as well as future drinking water supplies1. Organic micropollutants are organic chemicals with complex and highly variable structures, and they have in common that they occur in the environment at trace concentrations (in the μg–ng/L range). Organic micropollutants often have unknown ecotoxicological and/or human health effects. They include a multitude of compounds such as pharmaceuticals, pesticides, ingredients of household products and additives of personal care products. In the European Union, the threshold limit for pesticides and relevant transformation products in drinking water is set at 0.1 µg/L2. This threshold is frequently exceeded and forces drinking water treatment plants to invest in expensive physicochemical treatment technologies or to close groundwater extraction wells3. The use of pollutant degrading bacteria in bioaugmentation strategies to remove micropollutants, such as pesticides, from drinking water, is presented as a solution3,4. The groundwater micropollutant 2,6-dichlorobenzamide (BAM), a transformation product of the herbicide dichlobenil, frequently occurs in groundwater in Europe, often exceeding the treshold concentration5. Aminobacter sp. MSH1 (CIP 110285) was enriched and isolated from dichlobenil treated soil sampled from the courtyard of a plant nursery in Denmark. The strain converts dichlobenil to BAM, which is further fully mineralized6. Efforts to elucidate the catabolic pathway for BAM degradation in MSH1 revealed the involvement of two plasmids. The first step of BAM-mineralization involves the hydrolysis of BAM to 2,6-dichlorobenzoic acid (2,6-DCBA) by the amidase BbdA encoded on the 41 kb IncP1-β plasmid pBAM17. Further catabolism of 2,6-DCBA to central metabolism intermediates involves enzymes encoded on the 54 kb repABC family plasmid pBAM28,9. The strain mineralizes BAM at trace concentrations6 and invades biofilms of microbial communities of rapid sand filters used in drinking water treatment plants (DWTPs)10. Moreover, it was successfully used in bioaugmentation of rapid sand filters, both in lab scale and pilot scale biofilration systems, to remove BAM from (ground)water10,11,12,13. On the other hand, long-term population persistence and catabolic activity in the sand filters were impeded, likely due to a combination of predation and wash out13,14, as well as to physiological and genetic changes. Reducing flow rate and improving inoculation strategy have demonstrated prolonged persistence and activity of MSH1 in bioaugmented sand filters15. However, other studies indicate that MSH1 shows a starvation survival response, in the nutrient (especially carbon) limiting environment of DWTPs, leading to reduced specific BAM degrading activity16. Moreover, a substantial loss of plasmid pBAM2 was observed upon prolonged transfer of MSH1 both in R2A medium and in C-limited minimal medium17, indicating that the plasmid is not entirely stable. Moreover, mutants lacking the ability to convert BAM into 2,6-DCBA have been reported7. Clearly, to come to full management of bioaugmentation using MSH1 in DWTP biofiltration units aiming at BAM removal, more knowledge is needed on the physiological as well as genetic adaptations of MSH1 when introduced into the corresponding oligotrophic environment. The elucidation of the full genome sequence is crucial in this.
This paper reports on the full genome sequence of strain MSH1. Since the strain is being studied for several years in different laboratories, the genome was independently sequenced in two different laboratories from different institutes, i.e., KU Leuven, Belgium and Aarhus University, Denmark to infer possible changes. This was indeed the case with the Aarhus strain (DK1) showinga single chromosome and seven plasmids, including the two previously described catabolic plasmids pBAM1 and pBAM2, while KU Leuven strain (MK1) appears a variant that still contained pBAM1 and pBAM2 but lacked four of the five other plasmids. Moreover, the relative sequence coverage of the plasmids compared to the chromosome suggested that there are either multiple copies of the chromosome per cell or that there are, on average, fewer than one copy of six out of the seven plasmids per cell. This was tested in a plasmid stability experiment with substrain DK1 where plasmids were found to be overall stable, with the exception of a single loss event of pUSP1. This supports the hypothesis that MSH1 might have a polyploid chromosome, at least under some growth conditions.
Material and methods
Growth conditions, genomic DNA preparation and sequencing
The genome sequence of strain MSH1 was independently obtained in two different laboratories, i.e., the KU Leuven in Belgium (MK1) and the Aarhus University lab in Roskilde, Denmark (DK1). In both cases, Aminobacter sp. MSH1 was obtained from the strain collection of the laboratory that originally isolated the bacterium6. Sequencing of substrain DK1 at the Roskilde lab was performed as follows. Directly derived from a cryostock obtained from the original lab of MSH1, two ml of a culture grown in R2B were used for extraction of high molecular weight (HMW) DNA using the MasterPure™ DNA Purification Kit (Epicentre, Madison, WI, USA), using the kit’s protocol for cell samples. DNA was eluted in 35 µL 10 mM Tris–HCl (pH 7.5) with 50 mM NaCl. The purity and concentration of extracted DNA were measured with a NanoDrop 2000c and a Qubit® 2.0 fluorometer (Thermo Fisher Scientific, Walther, MA, USA), respectively. An Illumina Nextera XT library was prepared for paired-end sequencing on an Illumina NextSeq 500 with a Mid Output v2 kit (300 cycles) (Illumina Inc., San Diego, CA, USA). Paired-end reads (2 × 151 bp) were trimmed for contaminating adapter sequences and low quality bases (< Q20) at the ends of the reads were removed using Cutadapt (v1.8.3)18. Paired-end reads that overlapped were merged with AdapterRemoval (v2.1.0)19. For Oxford Nanopore sequencing, a library was prepared from the same DNA extract using the Rapid Sequencing kit (SQK-RAD004). This was loaded on an R9.4 flow cell and sequenced using MinKnow (v1.11.5) (Oxford Nanopore Technologies, Oxford, UK). Nanopore reads were basecalled with albacore (v2.1.10) without quality filtering of reads. Only reads longer than 5000 bp were retained and sequencing adapters were trimmed using Porechop (v0.2.3). A hybrid genome assembly with Nanopore and Illumina reads was performed using Unicycler (v0.4.3)20.
The Illumina sequencing of substrain MK1 in the KU Leuven lab was reported previously7,8. Briefly, genomic DNA was isolated from a culture grown on R2B using the Puregene Core kit A (Qiagen, Hilden, Germany), according to the manufacturer’s instructions, except that DNA precipitation was performed with ethanol. A library was constructed for paired-end sequencing using 500 bp inserts and sequencing was performed on the Illumina GAIIx platform. Generated read lengths were 90 bp. The Illumina reads were quality controlled using FastQC21 (v0.11.6) and BBduk22 (v36.47). This included trimming the reads with low scoring regions (Phred < 30), clipping adapters, and removing very short reads (length < 50). For Nanopore sequencing, total genomic DNA was extracted from a culture grown on R2B with 200 mg/L BAM using the DNeasy UltraClean Microbial Kit (Qiagen, Hilden, Germany). Afterwards, the genomic DNA was mechanically sheared using a Covaris g-Tube (Covaris Inc., MA, USA) to an average fragment length of 8 kb. The library for sequencing was prepared using the 1D ligation approach with native 1D barcoding (SQK-LSK109) and sequenced on a MinION R9.4 flow cell using the MinION sequencer (Oxford Nanopore Technologies, Oxford, UK). The Nanopore reads were basecalled with Albacore (v2.0.2), and the barcode sequences were trimmed using Porechop (v0.2.3). Hybrid assembly of genome was performed as reported above.
Genome analyses
For both genomes, automatic gene annotation was done using Prokka23 (v1.14.0). Separately from Prokka, proteins with transmembrane helices were identified using TMHMM v2.024. Genes were assigned to COG functional categories using EggNOG-mapper v4.5.125. Genome comparison was done using EDGAR26. Metabolic pathways were explored using Pathway Tools27 and RAST28. Circularized views of chromosome and plasmids were made using Circos29. MegaX30 was used for protein alignment and tree building. Phylogenetic analysis for strain MSH1 was performed using a clustal-omega31 multiple sequence alignment using 16S ribosomal RNA genes from the set of type strains available in the Phyllobacteriaceae family. The tree was inferred using PhyML32 with a GTR substitution model and a calculation of branch support values (bootstrap value of 1000). Whole-genome-based taxonomic classification was performed with in silico DNA:DNA hybridization using the Type Strain Genome Server (TYGS)33. Furthermore, average nucleotide identity (ANI) values were calculated for MSH1 against all available Aminobacter genomes in NCBI (downloaded January 31, 2021), using FastANI34 and plotted in R with the pheatmap package35. Genomes of the two MSH1 substrains were compared using the Mauve genome alignment software36. Plasmids were characterized with regards to relaxase genes and replicon families using MOB-suite37.
Plasmid (in)stability experiment
To test for plasmid stability, MSH1 substrain DK1 cells from − 80 °C cryostock were streaked on R2A plates and DNA from 1 ml of the cryostock was extracted using MasterPure™ DNA Purification Kit. The cryostock contained MSH1 culture that had been growing to stationary phase. After incubation at 22 °C for 11 days, a single colony from the R2A plate was picked and resuspended in 105 µl phosphate-buffered saline (PBS). From this, 5 µl suspension was inoculated in 25 ml R2B for 72 h. Whole genome sequencing was performed on the remaining 100 µl PBS suspension. After 72 h of growth in R2B, 1 mL broth culture was sampled for DNA extraction, similarly to the DNA extracted for initial DNA sequencing (above), and 100 µL of dilution series 10–5–10–8 of the R2B culture were plated onto R2A and the plates incubated at 22 °C. After 7 days of growth on R2A plates, allowing cells to reach resting stage, DNA was extracted and sequenced, as described above, from 14 individual colonies (originating from a single cell) resuspended in 100 µL PBS. All sequencing was performed on an Illumina NextSeq 550 with a Mid Output v2 kit (300 cycles) using Nextera XT library preparations as described above.
Sequencing adapters and poor quality sequences were trimmed from paired end reads using Trimmomatic (v0.39)38 with the options “ILLUMINACLIP:/usr/share/trimmomatic/NexteraPE-PE.fa:2:30:10 LEADING:3 TRAILING:3 SLIDINGWINDOW:4:15 MINLEN:36”. Trimmed and filtered reads from each replicate MSH1 sample were mapped with bwa (v0.7.17-r1198-dirty)39 to the completely assembled MSH1 genome including plasmids pBAM1-2 and pUSP1-5. Sequencing coverage in 10,000, 1000, and 1 bp windows for all replicons per replicate sample was calculated with samtools (v1.9-166-g74718c2)40 and bedtools (v2.28.0)41. Coverages were similar in all three windows and therefore only the results obtained in 1000 bp windows were used. Coverage data for all replicons were divided by the mean coverage of the chromosome, in order to normalize replicon copy numbers relative to the chromosome. Normalized coverage of all replicons for all replicates were visualized with Circos (v0.69-6)29.
Results and discussion
Genome statistics
The MSH1 genome (based on substrain DK1) consists of a chromosome of 5,301,518 bp and seven plasmids. The genome contains two large plasmids pUSP1 of 367,423 bp and pUSP2 of 365,485 bp, three smaller plasmids pUSP3, pUSP4, and pUSP5 (respectively 97,029 bp, 64,122 bp, and 31,577 bp) and the two previously reported smaller catabolic plasmids pBAM1 and pBAM2 of 40,559 bp and 53,893 bp, respectively (Table 1). A total of 6,257 genes could be predicted of which six rRNAs, 53 tRNAs, and four ncRNAs. A total of 6194 CDS were predicted including 190 pseudogenes (Table 2). Circular views of the chromosome and seven plasmids are shown in Figs. 1 and 2. The KU Leuven variant, designated as substrain MK1, lacked one of the two larger plasmids, i.e. pUSP2, and the three smaller plasmids pUSP3, pUSP4, and pUSP5. Except for the discrepancy in plasmids, the shared genomes (chromosome, pUSP1, pBAM1, and pBAM2) of the two strains have an average nucleotide identity of 99.9925%. In order to determine whether differences in the two assemblies were due to assembly- or sequencing errors, trimmed Illumina datasets from both substrains were mapped to the KU Leuven strain MK1 assembly in CLC Genomics Workbench (Qiagen, Hilden, Germany) and simple sequence variants (SNPs, small deletions and insertions) were detected using either of the two read mappings, with a cutoff of 35% consensus for variant calling. Almost all small sequence variants between the two substrains were explained by heterogeneity in the Illumina reads, indicating that for both substrains, the cultures from which DNA was extracted were already genetically heterogenous. For most small variants, stochasticity appears to determine the final sequence in assemblies. Hence, the actual sequence similarity between the shared genomes of both substrains is even higher than 99.9925% (not considering the plasmids missing in MK1). The BAM-catabolic genes were manually checked for mutations that could indicate differences in degradation potential. A single nucleotide change was noted in the bbdb3 gene on pBAM2, encoding one of three subunits of a TRAP-type transport system potentially involved in the uptake of 2,6-DCBA8. In this gene, a non-synonomous substitution has changed a glycine to an arginine in the resulting protein in MK1. Currently, it is not known if this change has an effect on the putative function of this tripartite transport system. Furthermore, differences were found in the region of plasmid pUSP1 containing an IS30 family insertion sequence with 38 bp flanking, imperfect, inverted repeats (IRs). The repeats appear complete in DK1, but MK1 shows a deletion of 56 bp and 34 bp up- and downstream of the IS30 transposase gene, including partial deletion of the IR at both ends, suggesting that the MK1 substrain has undergone further genetic changes. The deletions flanking the IS30 element on pUSP1 in MK1 may have been caused by a possible intramolecular transposition event42. However, this IS30 element with deletion in the IRs in MK1 may still be functional, as the functional core region of IS30 IRs are only part of the complete IR43.
Circular view of the chromosome of Aminobacter sp. MSH1. From outer to inner circle: CDS on leading strand, scale (ticks: 100 kb), CDS on lagging strand, tRNA (purple) and rRNA (red) (only chromosome), GC plot and GC skew (> 0: green, < 0: red). CDS are colored according to COG functional categories determined with EggNOG mapper 4.5.1.
Circular view of the plasmids of the newly assigned Aminobacter niigataensis MSH1. From outer to inner circle: CDS on leading strand, scale (ticks: 100 kb), CDS on lagging strand, GC plot and GC skew (> 0: green, < 0: red). CDS are colored according to COG functional categories determined with EggNOG mapper 4.5.1. The KU Leuven substrain MK1 lacks plasmids pUSP2-5.
Phylogenetic assignment of MSH1 to Aminobacter niigataensis
A phylogenetic tree based on the 16S rRNA gene sequence indicating the position of MSH1 is shown in Fig. 3. The 1463 bp 16S rRNA gene sequence of MSH1 is 100% identical to that of Aminobacter niigataensis DSM 7050T and 99.6–99.8% to those of other Aminobacter species. The relationship with Aminobacter niigataensis is supported by whole-genome in silico digital DNA:DNA hybridization using TYGS, which reports that MSH1 (Aarhus substrain DK1) is 82.5% (recommended d4 formula) similar to A. niigataensis DSM 7050 (see Supplementary Table S1 online). Finally, ANI values against all available Aminobacter genomes from NCBI (complete and incomplete assemblies; downloaded January 31, 2021), showed an ANI of 98% against A. niigataensis DSM 7050 (Fig. 4). Based on these analyses, we reassign Aminobacter sp. MSH1 as Aminobacter niigataensis MSH1.
Phylogenetic relationships of Aminobacter niigataensis MSH1 based on the 16S rRNA gene sequence. Maximum likehood tree visualized as a cladogram with bootstrap values. This tree was created from a clustal-omega31 multiple sequence alignment using 16S rRNA genes from the set of type strains available in the Phyllobacteriaceae family (NCBI accession numbers between parenthesis). The tree was inferred using PhyML32 with a GTR substitution model and a calculation of branch support values (bootstrap value of 1000). The Variovorax sp. strain WDL1 was used as an outgroup58.
Chromosomally encoded metabolic features of MSH1
We examined the occurrence of basic metabolisms in MSH1 which might be of importance for its fate in bioaugmentation applications. The chromosome of MSH1 possesses all genes required for glycolysis using the Embden-Meyerhof pathway and additionally possesses all genes for glucose metabolism through the Entner-Doudoroff pathway and the pentose phosphate pathway. It also contains all genes of the tricarboxylic acid cycle. MSH1 was previously shown to grow on several carbohydrates with slower growth on succinate and acetic acid as carbon sources compared to glucose, fructose, and glycerol44. These properties might be important when accommodating MSH1 with an auxiliary C-source for improved maintenance in the oligotrophic waters where it finds its main application13,15. On the other hand, MSH1 does not possess genes involved in carbon fixation which rules out autotrophic growth using CO2. MSH1 further displays the catechol ortho-cleavage pathway45 and possesses genes for conversion of benzoate to catechol allowing the organism to grow on benzoate which was confirmed by culturing the strain on benzoate (data not shown). With regards to nitrogen metabolism, MSH1 contains a gene cluster that encodes the transmembrane ammonium channel AmtB as well as its cognate protein GlnK46, indicating that MSH1 can use mineral ammonia as a nitrogen source directly from its environment, in addition to nitrogen released from BAM degradation. In addition, MSH1 carries genes encoding proteins involved in nitrate transport (NrtA and NrtT), located upstream of genes for assimilatory reduction of nitrate (nasDEA) to ammonium suggesting that MSH1 can also use nitrate as a nitrogen source. Ammonia is also released from amino acid metabolism and is further incorporated in L-glutamate for biosynthesis. Furthermore, despite its inability to grow under nitrate reducing conditions6, MSH1 contains a gene cluster which encodes for several proteins (NapAB, NapC, NirK, NorBC) involved in dissimilatory nitrate reduction. However, narG, encoding the typical cytoplasmatic oriented dissimilatory nitrate reductase47, is lacking as well as nosZ for reduction of nitrous oxide to dinitrogen48. The exact function of the gene cluster containing napABC, nirK and norBC is therefore yet unknown. For sulfur metabolism, MSH1 possesses two nearby located gene clusters encoding the ABC transporter complex CysUWA involved in sulfate/thiosulfate import linked with either sbp and cysP49 that encode the periplasmic protein that delivers respectively sulfate and thiosulfate to the ABC transporter complex leading to high affinity uptake. Furthermore, the chromosome contains all genes (cysC, cysH, cisIJ, cysK) necessary for assimilatory sulfate reduction to sulfide and incorporation of sulfide into O-acetylserine to form cysteine49. The assimilation of thiosulfate is less clear but MSH1 encodes for a second homologue of CysK, as well as several glutaredoxin proteins required for incorporating thiosulfate in O-acetylserine and reductive cleavage reaction of its disulfide bond to form cysteine49.
Plasmids of MSH1
Besides the previously described IncP1-β and repABC plasmids, pBAM1 and pBAM27,8, the Aarhus MSH1 substrain DK1 harbors the five pUSP1-5 plasmids (Fig. 2), while the KU Leuven substrain MK1 lacks pUSP2, pUSP3, pUSP4, and pUSP5. Catabolic genes on pBAM1 and pBAM2 enable MSH1 to mineralize the groundwater micropollutant BAM and use it as a source of carbon, nitrogen, and energy for growth. The amidase BbdA on pBAM1 transforms BAM to 2,6-dichlorobenzoic acid (DCBA)7 which is further metabolized by a series of catabolic enzymes encoded by pBAM28,9. As previously discussed8, the gene bbdI encoding the gluthatione dependent thiolytic dehalogenase responsible for removal of one of the chlorines from BAM together with bbdJ encoding gluthatione reductase, occur on pBAM2 in three consecutive, perfect repeats followed by a fourth, imperfect repeat. This, together with the placement of the BAM degradation genes on two separate plasmids (pBAM1 and pBAM2) and the bordering of the catabolic gene clusters by remnants of insertion sequences and integrase genes, suggests that the BAM catabolic genes in MSH1 have been acquired by horizonral gene transfer and then evolved to occur in their observed genomic organisation. In addition, pBAM2 has a considerably lower GC content of 56% compared to the chromosome and other plasmids which are between 60.0 and 64.4% (Table 2), which could indicate that pBAM2 was acquired from another, unknown, unrelated bacterium. It was previously shown that mineralization of DCBA is a common trait in bacteria in sand filters and soils, while BAM to DCBA conversion is the rate limiting step in BAM mineralization and is rare in microbial communities50.
Like pBAM2, plasmids pUSP1, pUSP2, and pUSP3 belong to the repABC family. repABC replicons are known as typical genome components of Alphaproteobacteria species51. The occurrence of more than one repABC replicon in one and the same genome has been described before and the plasmid family has been shown to exist of different incompatability groups. For instance, Rhizobium etli CFN42 has 6 repABC plasmids52,53.
Plasmids pBAM2, pUSP2, pUSP3, and pUSP4 contains Type IV secretion system (T4SS) genes54, while pUSP1 does not. This indicates that pUSP1 is likely not self-transferable, unlike pBAM2, pUSP2, pUSP3, and pUSP4. Besides T4SS genes, plasmid pUSP4 contains a mobABC operon. The 31.6 kbp plasmid pUSP5 lacks conjugative transfer genes and appears to be a mobilizable plasmid with genes encoding a VirD4-like coupling protein and a TraA conjugative transfer relaxase likely involved in nicking at an oriT site and unwinding DNA before transfer. Furthermore, MOB-suite predicted that pBAM1, pUSP2, and pUSP4 have MOBP-type relaxase genes, while pUSP1, pUSP3 and pUSP5 have MOBQ-type relaxase genes.
Specialized functions of plasmids pUSP1-5
In Table 3, all CDS of the different plasmids are categorized according to COGs. Half of the CDS annotated on plasmid pUSP1 (322 CDS) and pUSP2 (346 CDS) are genes primarily associated with the transport and metabolism of amino acids (20% and 12%, resp.), carbohydrates (6% and 6%, resp.) and inorganic compounds (10% and 3%, resp.), and genes for energy production and conversion (9% and 8%, resp.). For the plasmids pUSP3, pUSP4, and pUSP5, CDS categorized under the same COGs are lower than 18%. Together, pUSP1 and pUSP2 accounts for about 17% of all genes in MSH1 related to amino acid, carbohydrate transport and metabolism, and energy production and conversion in MSH1. The transport systems encoded by pUSP1 and pUSP2 include multiple ABC-transporters for N and/or S-containing organic compounds. For amino acids, carbohydrates and inorganic compound metabolism and transport, ABC-type transport systems are predicted for polar amino acids (arginine, glutamine), branched chain amino acids, and multiple sugars. In addition, transport systems for spermidine/putrescine, taurine, aliphatic sulphonates, dipeptides, beta-methyl galactoside, polysialic acid, and phosphate were predicted. Putative functions could be assigned by Prokka to 64.2%, 56.8%, 27.4%, 42.2%, and 34.3% of CDS for pUSP1, pUSP2, pUSP3, pUSP5 and pUSP5, respectively. On pUSP1, found in both MSH1 substrains, multiple genes could be assigned to metabolic subsystems by RAST. These include folate biosynthesis, cytochrome oxidases and reductases, degradation of aromatic compounds (homogentisate pathway), ammonia assimilation, and several genes related to amino acid metabolism. Some of these functions on pUSP1 do not have functional analogs on the chromosome, which may help to explain why pUSP1 was not lost in the KU Leuven substrain MK1, but the other pUSP plasmids were. On pUSP2, which is absent in MSH1 from KU Leuven, some genes are predicted to be involved in acetyl-CoA fermentation to butyrate, creatine degradation, metabolism of butanol, fatty acids, and nitrile, and a few miscellanoues functions. A large number of CDS on pUSP1 (19%), and pUSP2 (23%) are homologues to CDS on the chromosome and could be considered dispensable genes and hence explain the loss in the KU Leuven MK1 substrain. However, although these CDS might be considered homologues, their functionality might differ considerably in terms of substrate specificity and kinetics.
Besides genes encoding conjugative transfer, plasmid replication, and plasmid stability functions, most genes on plasmids pUSP3, pUSP4, and pUSP5 could not be annotated with a function. However, several genes on pUSP3 may have functions related to metabolism of sugars, including inositol and mannose which were not tested in an earlier growth optimization experiment44. On pUSP4, genes encoding a transmembrane amino acid transporter are situated next to an aspartate ammonia-lyase-encoding gene that enables conversion between aspartate and fumarate that may enter the tricarboxylic acid cycle, as described above. A cytochrome bd-type quinol oxidase, encoded by two subunit genes on pUSP5, also occurs in some nitrogen-fixing bacteria where it is responsible for removing oxygen in microaerobic conditions55. Furthermore, a pseudoazurin type I blue copper electron-transfer protein is encoded by a gene on pUSP5, that may act as an electron donor in a denitrification pathway. A chromate transporter, ChrA, encoded by a gene on pUSP5 may confer resistance to chromate56. Future studies should look into whether the lack of plasmids pUSP2-5 in substrain MK1 has phenotypic consequences, with regards to the predicted functions, including metabolism of sugars and aspartate, nitrogen metabolism, and resistance to chromate.
Plasmid stability and chromosome polyploidy
The Illumina sequencing coverage (1000 bp windows) of several plasmids relative to the chromosome (except for pBAM1) was lower than one, i.e., approximately 0.3 to 0.6 per chromosome. This suggests that either not all cells (only three to six out of ten) contain a copy of the same plasmid due to plasmid loss or that there are multiple copies of the chromosome. Previously, in the MK1 substrain, we observed that pBAM2 is not always perfectly inherited by the daughter cells in cultures grown in R2B and R2B containing BAM17. To observe whether plasmid instability explained the copy number relative to the chromosome in the sequenced cultures, sequencing was performed directly on the cryo stock as well as on colonies directly derived from this, mimicking the sequenced cell preparation for whole genome sequencing. We hypothesized that if certain plasmids are not stably inherited (i.e. those with copy numbers 0.3 to 0.6), only part of the cell population will habour those plasmids and picking of multiple colonies from a plate will result in picking of some colonies that have lost one or more plasmids.
The Aarhus MSH1 substrain containing all 7 plasmids was sequenced directly from the cryostock (grown to stationary phase prior to cryopreservation), from a single colony picked from R2A plates after spreading the cryostock (incubated for 7 days), and from the broth R2B culture that had been inoculated with the same single colony from cryostock (incubated for 72 h). Moreover, after spreading the latter R2B culture on an R2A plate and incubated for 11 days, an additional 14 MSH1 colonies were picked for sequencing. All samples represent stationary phase cultures/colonies, considering that MSH1 was previously shown to reach stationary phase after 30–35 hours44. Taking into account a plasmid coverage of 0.3–0.6 per chromosome, we expect that around half of the 14 picked colonies would have lost one or more of the plasmids in the case of poor inheritance. However, only one of the colonies showed loss of a plasmid, i.e., plasmid pUSP1 (Fig. 5) indicating polyploidy of the chromosome rather than unstable inheritance of plasmids. The loss of repABC megaplasmid pUSP1 shows that the possible metabolic features encoded by genes on pUSP1, as described above, are not essential for growth under these conditions, although, remarkably this is the only pUSP plasmid still present in substrain MK1. Interestingly, the plasmid/chromosome-ratio varied according to the growth medium from which DNA was isolated. When growing in R2B (broth), e.g. as done for DNA extraction for genome sequencing and from cryostock and R2B culture (first and third green rings, Supplementary Fig. S1 online), all plasmids, except pBAM1, have a copy number lower than one per chromosome. When DNA was extracted from colonies grown on R2A plates (though resuspended in PBS prior to DNA extraction), plasmid copy numbers were approx. one per chromosome, except for pBAM1 which has a copy number of approx. 2.5 per chromosome.
Coverage in 1000 bp windows of replicons normalized to chromosome coverage (NormCov). A NormCov of 1 indicates a single copy per chromosome of a replicon. A NormCov above 1 indicates that there are more copies of a given plasmid than the chromosome per cell. Points have been slightly jittered horizontally to improve visualization of overlaps.
Except for the single loss of pUSP1, nothing here indicates unstable maintenance of plasmids and subsequent loss. Instead, our results indicate that MSH1 regulates the chromosome copy number according to whether it grows as planktonic bacteria or fixed on an agar plate. The results shown here can be explained by MSH1 being polyploid with regards to its chromosome when growing in broth media. Single-copy plasmids (e.g. pBAM2, pUSP1-5) will thereby have copy numbers lower than one relative to the chromosome, when growing in broth R2B. Polyploidy in prokaryotes have been described before, including in Deinococcus, Borrelia, Azotobacter, Neisseria, Buchnera, and Desulfovibrio57 and may be quite overlooked in many other bacteria. E. coli in stationary phase was shown to have two chromosome copies after growing in rich, complex medium, but only 60% of the cells had two copies in stationary phase after slower growth in a synthetic medium57. It was suggested that monoploidy is not typical for proteobacteria, and that many bacteria are polyploid when growing in exponential phase57. Possible advantages offered by polyploidy include resistance to DNA damage and mutations, global regulation of gene expression by changing chromosome copy number, and finally polyploidy may enable heterozygosity in bacteria where genes mutate to cope with challenging condition while preserving a copy of the original genes. Despite the stability of the plasmids in MSH1, the KU Leuven substrain MK1 lacks plasmids pUSP2-5 and loss of pBAM2 was previously observed17. Although pBAM2 encodes its own T4SS, the multiple loss of pBAM2 and pUSP2-5 in the KU Leuven MSH1 could be hypothetically explained by some uncharacterized plasmid codependence, where one loss leads to another. The dynamics of plasmid loss that has led to formation of the KU Leuven substrain MK1 are still unknown.
Conclusions
The full genome of Aminobacter sp. MSH1, re-identified here as Aminobacter niigataensis MSH1, consisting of a chromosome and seven plasmids, was determined combining both Nanopore and Illumina sequencing. Two smaller plasmids pBAM1 and pBAM2 were previously identified carrying the catabolic genes required for mineralization of the groundwater micropollutant BAM. Both the chromosome and the other five plasmids are described here for the first time. A plasmid stability experiment showed that most plasmids were stably maintained, with exception of a single loss event of plasmid pUSP1. Instead, the results indicate that MSH1 has a polyploid chromosome when growing in broth, thereby reducing plasmid copy numbers per chromosome to below one. When comparing the two sequenced MSH1 substrains, we observed that plasmids pUSP2, pUSP3, pUSP4, and pUSP5 were below detection limits in the KU Leuven variant MK1. Substrain MK1 may previously have lost these plasmids but maintained pUSP1, pBAM1, and pBAM2, thereby retaining its capacity to degrade BAM. Therefore, the Aarhus variant is likely or at least comes closest to the original wild type strain. Future studies on growth and degradation kinetics of the MSH1 and its substrain MK1 lacking several plasmids, can reveal if plasmids pUSP2-5 harbour unknown (favorable) functions or if they impose a metabolic burden on MSH1 and whether or not those plasmids are important for the strains functionality during application. This will help to elucidate which substrain is preferable for bioaugmentation.
Data availability
The genome sequences of strain MSH1 substrains MK1/DK1 are available under the following GenBank accession numbers CP026265/CP028968 (chromosome), CP026268/CP028967 (pBAM1), CP026267/CP028966 (pBAM2), CP026266/CP028969 (pUSP1) and CP028970 (pUSP2), CP028971 (pUSP3), CP028972 (pUSP4) and CP028973 (pUSP5).
References
Schwarzenbach, R. P. et al. The challenge of micropollutants in aquatic systems. Science 80(313), 1072–1077 (2006).
EU. Council Directive 98/83/EC of 3 November 1998 on the quality of water intended for human consumption. Counc. Eur. Union (1998).
Benner, J. et al. Is biological treatment a viable alternative for micropollutant removal in drinking water treatment processes?. Water Res. https://doi.org/10.1016/j.watres.2013.07.015 (2013).
Vandermaesen, J. et al. Application of biodegradation in mitigating and remediating pesticide contamination of freshwater resources: State of the art and challenges for optimization. Appl. Microbiol. Biotechnol. https://doi.org/10.1007/s00253-016-7709-z (2016).
Björklund, E., Anskjær, G. G., Hansen, M., Styrishave, B. & Halling-Sørensen, B. Analysis and environmental concentrations of the herbicide dichlobenil and its main metabolite 2,6-dichlorobenzamide (BAM): A review. Sci. Total Environ. https://doi.org/10.1016/j.scitotenv.2011.02.008 (2011).
Sørensen, S. R., Holtze, M. S., Simonsen, A. & Aamand, J. Degradation and mineralization of nanomolar concentrations of the herbicide dichlobenil and Its persistent metabolite 2,6-dichlorobenzamide by Aminobacter spp. isolated from dichlobenil-treated soils. Appl. Environ. Microbiol. 73, 399–406 (2007).
T’Syen, J. et al. Identification of the amidase BbdA that initiates biodegradation of the groundwater micropollutant 2,6-dichlorobenzamide (BAM) in Aminobacter sp. MSH1. Environ. Sci. Technol. 49, 11703–11713 (2015).
T’Syen, J. et al. Catabolism of the groundwater micropollutant 2,6-dichlorobenzamide beyond 2,6-dichlorobenzoate is plasmid encoded in Aminobacter sp. MSH1. Appl. Microbiol. Biotechnol. 102, 7963–7979 (2018).
Raes, B. et al. Aminobacter sp. MSH1 mineralises the groundwater micropollutant 2,6-dichlorobenzamide through a unique chlorobenzoate catabolic pathway. Environ. Sci. Technol. 53, 10146–10156 (2019).
Horemans, B. et al. Biocarriers improve bioaugmentation efficiency of a rapid sand filter for the treatment of 2,6-dichlorobenzamide (BAM)-contaminated drinking water. Environ. Sci. Technol. 51, 1616–1625 (2016).
Albers, C. N., Feld, L., Ellegaard-Jensen, L. & Aamand, J. Degradation of trace concentrations of the persistent groundwater pollutant 2,6-dichlorobenzamide (BAM) in bioaugmented rapid sand filters. Water Res. 83, 61–70 (2015).
Albers, C. N., Jacobsen, O. S. & Aamand, J. Using 2,6-dichlorobenzamide (BAM) degrading Aminobacter sp. MSH1 in flow through biofilters: Initial adhesion and BAM degradation potentials. Appl. Microbiol. Biotechnol. 98, 957–967 (2013).
Ellegaard-Jensen, L., Albers, C. N. & Aamand, J. Protozoa graze on the 2,6-dichlorobenzamide (BAM)-degrading bacterium Aminobacter sp. MSH1 introduced into waterworks sand filters. Appl. Microbiol. Biotechnol. https://doi.org/10.1007/s00253-016-7710-6 (2016).
Ellegaard-Jensen, L., Horemans, B., Raes, B., Aamand, J. & Hansen, L. H. Groundwater contamination with 2,6-dichlorobenzamide (BAM) and perspectives for its microbial removal. Appl. Microbiol. Biotechnol. https://doi.org/10.1007/s00253-017-8362-x (2017).
Ellegaard-Jensen, L. et al. Bioaugmented sand filter columns provide stable removal of pesticide residue from membrane retentate. Front. Water 2, 55 (2020).
Sekhar, A. et al. Evaluation of the biofilm forming capacity of the 2, 6-dichlorobenzamide (BAM) degrading Aminobacter sp. strain MSH1 at macropollutant and micropollutant BAM concentrations. Commun. Agric. Appl. Biol. Sci. 78, 31–36 (2013).
Horemans, B. et al. Genetic (in)stability of 2,6-dichlorobenzamide catabolism in Aminobacter sp. strain MSH1 biofilms under carbon starvation conditions. Appl. Environ. Microbiol. 83, (2017).
Martin, M. Cutadapt removes adapter sequences from high-throughput sequencing reads. EMBnet J. https://doi.org/10.14806/ej.17.1.200 (2014).
Schubert, M., Lindgreen, S. & Orlando, L. AdapterRemoval v2: Rapid adapter trimming, identification, and read merging. BMC Res. Notes https://doi.org/10.1186/s13104-016-1900-2 (2016).
Wick, R. R., Judd, L. M., Gorrie, C. L. & Holt, K. E. Unicycler: Resolving bacterial genome assemblies from short and long sequencing reads. PLoS Comput. Biol. https://doi.org/10.1371/journal.pcbi.1005595 (2017).
Andrews, S. FastQC: A quality control tool for high throughput sequence data. http://www.bioinformatics.babraham.ac.uk/projects/fastqc/. Babraham Bioinforma. (2010).
Bushnell, B., Rood, J. & Singer, E. BBMerge: Accurate paired shotgun read merging via overlap. PLoS ONE https://doi.org/10.1371/journal.pone.0185056 (2017).
Seemann, T. Prokka: Rapid prokaryotic genome annotation. Bioinformatics 30, 2068–2069 (2014).
Krogh, A., Larsson, B., von Heijne, G. & Sonnhammer, E. L. L. Predicting transmembrane protein topology with a hidden markov model: application to complete genomes11Edited by F. Cohen. J. Mol. Biol. 305, 567–580 (2001).
Huerta-Cepas, J. et al. Fast genome-wide functional annotation through orthology assignment by eggNOG-mapper. Mol. Biol. Evol. 34, 2115–2122 (2017).
Blom, J. et al. EDGAR: A software framework for the comparative analysis of prokaryotic genomes. BMC Bioinform. 10, 154 (2009).
Karp, P. D. et al. Pathway tools version 19.0 update: Software for pathway/genome informatics and systems biology. Brief. Bioinform. 17, 877–890 (2016).
Aziz, R. K. et al. The RAST server: Rapid annotations using subsystems technology. BMC Genom. https://doi.org/10.1186/1471-2164-9-75 (2008).
Krzywinski, M. I. et al. Circos: An information aesthetic for comparative genomics. Genome Res. https://doi.org/10.1101/gr.092759.109 (2009).
Kumar, S., Stecher, G., Li, M., Knyaz, C. & Tamura, K. MEGA X: Molecular evolutionary genetics analysis across computing platforms. Mol. Biol. Evol. 35, 1547–1549 (2018).
Sievers, F. et al. Fast, scalable generation of high-quality protein multiple sequence alignments using Clustal Omega. Mol. Syst. Biol. 7, 539 (2011).
Lethiec, F., Gascuel, O., Duroux, P. & Guindon, S. PHYML Online: A web server for fast maximum likelihood-based phylogenetic inference. Nucleic Acids Res. 33, W557–W559 (2005).
Meier-Kolthoff, J. P. & Göker, M. TYGS is an automated high-throughput platform for state-of-the-art genome-based taxonomy. Nat. Commun. https://doi.org/10.1038/s41467-019-10210-3 (2019).
Jain, C., Rodriguez-R, L. M., Phillippy, A. M., Konstantinidis, K. T. & Aluru, S. High throughput ANI analysis of 90K prokaryotic genomes reveals clear species boundaries. Nat. Commun. https://doi.org/10.1038/s41467-018-07641-9 (2018).
Kolde, R. pheatmap: Pretty Heatmaps. R package version 1.0.12 (2019).
Darling, A. C. E., Mau, B., Blattner, F. R. & Perna, N. T. Mauve: Multiple alignment of conserved genomic sequence with rearrangements. Genome Res. https://doi.org/10.1101/gr.2289704 (2004).
Robertson, J. & Nash, J. H. E. MOB-suite: Software tools for clustering, reconstruction and typing of plasmids from draft assemblies. Microb. Genom. https://doi.org/10.1099/mgen.0.000206 (2018).
Bolger, A. M., Lohse, M. & Usadel, B. Trimmomatic: A flexible trimmer for Illumina Sequence Data. Bioinformatics https://doi.org/10.1093/bioinformatics/btu170 (2014).
Li, H. & Durbin, R. Fast and accurate short read alignment with Burrows-Wheeler transform. Bioinformatics 25, 1754–1760 (2009).
Li, H. et al. The sequence alignment/map format and SAMtools. Bioinformatics 25, 2078–2079 (2009).
Quinlan, A. R. & Hall, I. M. BEDTools: A flexible suite of utilities for comparing genomic features. Bioinformatics 26, 841–842 (2010).
Olasz, F., Stalder, R. & Arber, W. Formation of the tandem repeat (IS 30)2 and its role in IS 30-mediated transpositional DNA rearrangements. MGG Mol. Gen. Genet. https://doi.org/10.1007/BF00281616 (1993).
Olasz, F., Farkas, T., Kiss, J., Arini, A. & Arber, W. Terminal inverted repeats of insertion sequence IS30 serve as targets for transposition. J. Bacteriol. https://doi.org/10.1128/jb.179.23.7551-7558.1997 (1997).
Schultz-Jensen, N. et al. Large-scale bioreactor production of the herbicide-degrading Aminobacter sp. strain MSH1. Appl. Microbiol. Biotechnol. https://doi.org/10.1007/s00253-013-5202-5 (2014).
Harayama, S., Mermod, N., Rekik, M., Lehrbach, P. R. & Timmis, K. N. Roles of the divergent branches of the meta-cleavage pathway in the degradation of benzoate and substituted benzoates. J. Bacteriol. https://doi.org/10.1128/jb.169.2.558-564.1987 (1987).
Zheng, L., Kostrewa, D., Bernèche, S., Winkler, F. K. & Li, X. D. The mechanism of ammonia transport based on the crystal structure of AmtB of Escherichia coli. Proc. Natl. Acad. Sci. U. S. A. https://doi.org/10.1073/pnas.0406475101 (2004).
Sparacino-Watkins, C., Stolz, J. F. & Basu, P. Nitrate and periplasmic nitrate reductases. Chem. Soc. Rev. https://doi.org/10.1039/c3cs60249d (2014).
Bedzyk, L., Wang, T. & Ye, R. W. The periplasmic nitrate reductase in Pseudomonas sp. strain G-179 catalyzes the first step of denitrification. J. Bacteriol. https://doi.org/10.1128/jb.181.9.2802-2806.1999 (1999).
Kawano, Y., Suzuki, K. & Ohtsu, I. Current understanding of sulfur assimilation metabolism to biosynthesize l-cysteine and recent progress of its fermentative overproduction in microorganisms. Appl. Microbiol. Biotechnol. https://doi.org/10.1007/s00253-018-9246-4 (2018).
Vandermaesen, J. et al. Mineralization of the common groundwater pollutant 2,6-dichlorobenzamide (BAM) and its metabolite 2,6-dichlorobenzoic acid (2,6-DCBA) in sand filter units of drinking water treatment plants. Environ. Sci. Technol. https://doi.org/10.1021/acs.est.6b01352 (2016).
Cevallos, M. A., Cervantes-Rivera, R. & Gutiérrez-Ríos, R. M. The repABC plasmid family. Plasmid https://doi.org/10.1016/j.plasmid.2008.03.001 (2008).
González, V. et al. The partitioned Rhizobium etli genome: Genetic and metabolic redundancy in seven interacting replicons. Proc. Natl. Acad. Sci. U. S. A. https://doi.org/10.1073/pnas.0508502103 (2006).
Castillo-Ramírez, S., Vázquez-Castellanos, J. F., González, V. & Cevallos, M. A. Horizontal gene transfer and diverse functional constrains within a common replication-partitioning system in Alphaproteobacteria: The repABC operon. BMC Genom. https://doi.org/10.1186/1471-2164-10-536 (2009).
Cascales, E. & Christie, P. J. The versatile bacterial type IV secretion systems. Nat. Rev. Microbiol. 1, 137–149 (2003).
Juty, N. S., Moshiri, F., Merrick, M., Anthony, C. & Hill, S. The Klebsiella pneumoniae cytochrome bd’ terminal oxidase complex and its role in microaerobic nitrogen fixation. Microbiology 143, 2673–2683 (1997).
Aguilera, S. et al. Essential residues in the chromate transporter ChrA of Pseudomonas aeruginosa. FEMS Microbiol. Lett. 232, 107–112 (2004).
Pecoraro, V., Zerulla, K., Lange, C. & Soppa, J. Quantification of ploidy in proteobacteria revealed the existence of monoploid, (mero-) oligoploid and polyploid species. PLoS ONE 6, e16392 (2011).
Albers, P. et al. Catabolic task division between two near-isogenic subpopulations co-existing in a herbicide-degrading bacterial consortium: consequences for the interspecies consortium metabolic model. Environ. Microbiol. 20, 85–96 (2018).
R Core Team. R: A Language and Environment for Statistical Computing. (2021). https://www.r-project.org/.
Funding
This project (LHH, LEJ, OH, and JAA) was funded by MEM2BIO (Innovation Fund Denmark, Contract No. 5157-00004B) at Aarhus University and DS by the KU Leuven C1 Project No. C14/15/043 and the BELSPO IAP-project μ-manager No. P7/25 at KU Leuven. BH was supported by postdoctoral fellowship Grant 12Q0218N and CL by an SB-FWO PhD fellowship 1S64718N. TKN was supported by AUFF NOVA project ORIGENE.
Author information
Authors and Affiliations
Contributions
L.H.H., T.K.N., B.H. and D.S. initiated, planned, and funded the project. B.H. and T.K.N. wrote the initial draft manuscript. B.H., T.K.N., C.L., J.T., and T.S. performed genome sequencing, assembly annotation, and data analyses. O.H. performed the plasmid stability experiment. V.v.N., R.L., D.S., L.E.J., J.A., and L.H.H. critically reviewed the paper, assisted in data interpretation, and coordinated experiments.
Corresponding authors
Ethics declarations
Competing interests
The authors declare no competing interests.
Additional information
Publisher's note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Supplementary Information
Rights and permissions
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.
About this article
Cite this article
Nielsen, T.K., Horemans, B., Lood, C. et al. The complete genome of 2,6-dichlorobenzamide (BAM) degrader Aminobacter sp. MSH1 suggests a polyploid chromosome, phylogenetic reassignment, and functions of plasmids. Sci Rep 11, 18943 (2021). https://doi.org/10.1038/s41598-021-98184-5
Received:
Accepted:
Published:
DOI: https://doi.org/10.1038/s41598-021-98184-5
Comments
By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate.