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Communication

Genomic, Phylogenetic and Physiological Characterization of the PAH-Degrading Strain Gordonia polyisoprenivorans 135

1
Institute of Biochemistry and Physiology of Microorganisms, Federal Research Center “Pushchino Scientific Center for Biological Research of Russian Academy of Sciences” (FRC PSCBR RAS), 142290 Pushchino, Moscow Region, Russia
2
Pushchino Branch of Federal State Budgetary Educational Institution of Higher Education “Russian Biotechnology University (ROSBIOTECH)”, 142290 Pushchino, Moscow Region, Russia
3
Regional Microbiological Center, Belgorod State University, 308015 Belgorod, Russia
4
Laboratory of Ecological Soil Science, Faculty of Soil Science, Lomonosov Moscow State University, 119991 Moscow, Russia
*
Author to whom correspondence should be addressed.
Biology 2024, 13(5), 339; https://doi.org/10.3390/biology13050339
Submission received: 14 April 2024 / Revised: 7 May 2024 / Accepted: 11 May 2024 / Published: 13 May 2024

Abstract

:

Simple Summary

Polycyclic aromatic hydrocarbons are dangerous environmental pollutants and can be harmful to human health due to their carcinogenicity. The strain Gordonia polyisoprenivorans 135 is able to utilize such compounds and is therefore of interest for application in environmental biotechnology. We look inside the genome structure of this strain, analyze the genetic features of the catabolism of aromatics, and identify differences between the strain and its closest relatives at both the gene and intergenic levels. We also establish that the genome fragment carrying genes of aromatic catabolism is not characteristic of Gordonia polyisoprenivorans, but was most likely acquired externally from other related Actinobacteria. As a result, several interesting features of the evolutionary development of the genus Gordonia are revealed.

Abstract

The strain Gordonia polyisoprenivorans 135 is able to utilize a wide range of aromatic compounds. The aim of this work was to study the features of genetic organization and biotechnological potential of the strain G. polyisoprenivorans 135 as a degrader of aromatic compounds. The study of the genome of the strain 135 and the pangenome of the G. polyisoprenivorans species revealed that some genes, presumably involved in PAH catabolism, are atypical for Gordonia and belong to the pangenome of Actinobacteria. Analyzing the intergenic regions of strain 135 alongside the “panIGRome” of G. polyisoprenivorans showed that some intergenic regions in strain 135 also differ from those located between the same pairs of genes in related strains. The strain G. polyisoprenivorans 135 in our work utilized naphthalene (degradation degree 39.43%) and grew actively on salicylate. At present, this is the only known strain of G. polyisoprenivorans with experimentally confirmed ability to utilize these compounds.

1. Introduction

Polycyclic aromatic hydrocarbons (PAHs) are common environmental pollutants. They appear in soils and aquatic ecosystems from fuel spills [1,2], as components of pesticides and PAH-containing media [3,4,5], in the atmosphere as a result of burning wood, coal, and automobile exhaust [6,7,8,9,10]. PAHs are toxic to humans and animals, and many are carcinogenic [11,12,13]. Removal of excessive amounts of PAHs from ground and aquatic ecosystems is an urgent problem of modern biotechnology.
Many representatives of the order Mycobacteriales of the class Actinomycetia (phylum Actinomycetota) are able to utilize PAHs. This ability has been observed in representatives of the families such as Nocardiaceae [14,15,16,17,18], Dietziaceae [19,20,21], Mycobacteriaceae [22,23] and others. Rhodococcus strains are more commonly known for their ability to degrade PAHs compared to other members of this taxonomic group [24,25,26]. For example, Rhodococcus bacteria in work [27] utilized 43% of PAH mixture (naphthalene, acenaphthene, anthracene, phenanthrene, benzo[a]anthracene, and benzo[a]pyrene, total PAH content 1 g/kg) in soil within 213 days. The strain Rhodococcus sp. A2-3 [28] utilized 89% of fluorene (initial concentration 0.4 g/L) in 7 days.
Gordonia strains (family Gordoniaceae, order Mycobacteriales) are not currently used in environmental biotechnology as much as Rhodococcus. However, the plasticity of genomes and metabolic flexibility of representatives of the genus Gordonia make them interesting for both fundamental studies and practical applications. Gordonia strains are mainly known as degraders of alkanes [29,30,31], but among them there are also degraders of thiophenes [26,32], phthalates [33,34,35] and steroids [36,37,38].
The ability of Gordonia strains to utilize sulfur-containing PAH derivatives has been reported repeatedly. Thus, the strain Gordonia sp. IITR100, using a chain of sequential reactions, converts benzonaphthothiophene via benzo[b]naphtho-[2,1-d] thiophene 11,11-dioxide to 2-phenyl-naphthalen-1-ol [39] and thianthrene via thianthrene 5,5-dioxide to o-hydroxyphenyl phenylsulfone [40]. The utilization of benzothiophenes and dibenzothiophenes is a common ability of members of the genus. Previously, it was believed that this process required the dsz gene cluster for control [41,42]. However, we later demonstrated that growth on thiophenes is also possible in Gordonia strains lacking the dsz cluster [43]. It should be noted that the conversion process of sulfur-containing aromatic compounds affects only the ring with sulfur atoms, as a consequence of which sulfur is extracted from the compound structure. Other aromatic rings remain unavailable for utilization by Gordonia strains; therefore, the ability to desulfurize sulfur-containing aromatic compounds does not necessarily imply the ability to cleave hydrocarbon aromatic rings.
Regarding the degradation of unsubstituted PAHs, there are only a few reports of such ability in representatives of Gordonia. Young et al. [44] observed the growth of Gordonia alkanivorans strain CC-JG39, isolated from oil-contaminated sludge in Taiwan, on naphthalene at a concentration of 1 g/L. G. alkanivorans strain H19 [45] did not grow on naphthalene and phenanthrene, but did grow on pyrene. At the same time, none of the nine strains we investigated as part of our study on the G. alkanivorans pangenome [46] utilized aromatic compounds.
Kurniati et al. [47] observed the ability to degrade pyrene in Gordonia cholesterolivorans strain AMP 10. The strain G. iterans Co17 utilized naphthalene and anthracene in oil with degradation rates of 55.3% and 63.2%, respectively. Hu et al. [48] isolated three strains of Gordonia sp. from PAHs-contaminated soil in China. The strains demonstrated utilization abilities for various PAHs, including pyrene, benzo[a]pyrene, anthracene, naphthalene, phenanthrene, and fluoranthene.
Since the ability to utilize PAHs is rare in Gordonia, unlike a similar ability observed, for example, in Rhodococcus, our interest was piqued by the discovery of a PAH-degrading Gordonia strain, Gordonia polyisoprenivorans 135, isolated in 1998 from soil contaminated with oil, diesel fuel, and chlorinated aromatic compounds (Samara, Russia) [49]. The aim of this work was to study the features of genetic organization and biotechnological potential of G. polyisoprenivorans strain 135 as a degrader of naphthalene and its derivatives.

2. Materials and Methods

2.1. Bacterial Strain, Media and Cultivation Conditions

The strain Gordonia polyisoprenivorans 135 is maintained in the Laboratory of Microbial Physiology of IBPM RAS (Pushchino, Moscow region, Russia). To maintain the strain’s properties as a degrader of aromatic compounds, culture reseeding was performed every 2 months on agarized mineral medium CP1 with salicylate (0.1 g/L).
The CP1 mineral medium [50] had the following composition: (g/L): Na2HPO4, 0.7; KH2PO4, 0.5; NH4NO3, 0.75; MgSO4 × 7H2O, 0.2; MnSO4, 0.001; FeSO4, 0.02. Lysogeny broth (LB) medium consisting of (per liter of distilled water) 10 g of tryptone, 5 g of yeast extract, 5 g of NaCl, and 15 g of agar (Panreac, Spain) was used to test the purity of the bacterial culture and to obtain individual colonies.
The strain was cultured at 28 °C on CP1 medium supplemented with the following carbon and energy sources: naphthalene (2 g/L), benzoate (1 g/L), catechol (0.1 g/L), salicylate (0.1 g/L) on an orbital shaker at 180 rpm. All the reagents were obtained from Sigma-Aldrich (USA). Inoculum was prepared according to the method described in [51], Section 2.3.

2.2. Bioinformatic Analysis of the Genome of G. polyisoprenivorans 135

The protocol for sequencing and assembly of the genome of G. polyisoprenivorans strain 135 is described in [52]. To assess the quality of the genome, CheckM v. 1.2.2 [53] was used. The genome contains a total of 5364 genes, of which 5303 are coding sequences (CDSs). Of the 5303 CDSs, 5168 were CDSs with protein and 135 were pseudogenes. The genome contains a total of 61 RNA genes, of which 49 tRNAs, 3 ncRNAs, and 9 rRNAs. The genomic data for Gordonia polyisoprenivorans strain 135 are available in the GenBank database under accession number CP116236.1 (BioProject PRJNA923796, BioSample SAMN32738803).
The whole-genome tree was built using the TYGS web service [https://tygs.dsmz.de/ (accessed 23 November 2023)] from Genome BLAST Distance Phylogeny (GBDP) distances using “greedy-with-trimming” algorithm. GBDP defines distances between pairs of fully or partially sequenced genomes. The algorithm “greedy-with-trimming” involves removing the overlapping parts of high-scoring segment pairs in either genome [54].
The ANI value was calculated using the EzBioCloud ANI Calculator [55]. DNA-DNA hybridization (DDH) was calculated using the Genome-to-Genome Distance Calculator (GGDC) [54].
The alignment maps were constructed using the program Mauve ver. 2.4.0, (21 December 2014) [56]. PanExplorer software [57] was used to analyze the pangenome and search for unique genes. The genome maps were constructed using Circos (for pangenome analysis) [58], Proksee (accessed on 30 September 2023) [59] and MG2C [60] services. Functional annotation of the genome was performed using KEGG [61]. MGE search was performed using Mobile-OG db [62]. Alien_Hunter [63] was used to detect horizontally transferred regions in the genome. For specific gene finding BLAST search was carried out using “Nucleotide collection (nr/nt)” and “Whole-genome shotgun contigs (WGS)” databases.
Metabolic pathways were drawn using the program ChemDraw Ultra ver. 12.0.2.1076.
To analyze the noncoding pangenome, we used Piggy [64] and Roary [65] with the assistance of GNU Parallel [66]. Rho-dependent terminators were identified using RhoTermPredict [67], while Rho-independent terminators were identified using iTerm-PseKNC [68] and Arnold [69]. Prediction of noncoding RNAs in the genome of the strain was conducted using StructRNAfinder [70] and RNAcentral (https://rnacentral.org/, release 23, accessed on 15 March 2024).
Statistical processing was carried out using R version 3.6.3 (29 February 2020), and visualization of the results was performed using ggplot2 [71].

2.3. Cultivation of G. Polyisoprenivorans Strain 135 and Evaluation of Its Efficiency as a Degrader of Aromatic Compounds

The ability of strain G. polyisoprenivorans 135 to degrade aromatic compounds was tested in 100 mL of mineral medium CP1 [50] containing 2 g/L naphthalene or 0.1 g/L salicylate for 7 days at 27 °C. For inoculum preparation, the strain was grown for 24 h in mineral medium supplemented with 10% w/w potassium acetate as a carbon and energy source. The grown biomass was precipitated and washed with phosphate-buffered saline (PBS) solution. The resulting biomass was then resuspended in PBS solution to a concentration of 1 × 108 CFU/mL using a McFarland turbidity standard. The inoculum was introduced into the experimental system so that the inoculum dose did not exceed 1 × 106 CFU/mL. Cell numbers were estimated by counting colonies grown on LB agar medium at standard serial dilutions during 7 days of cultivation at 27 °C. All the experiments were performed in three independent biological replicates.

2.4. Measurement of Naphthalene Degradation Degree in the Medium

Naphthalene was extracted from the growth medium by mixing with dichloromethane (1:2, v/v). Gas chromatography (Agilent 6890, Agilent Technologies, Santa Clara, CA, USA) with a flame ionization detector was used to estimate the concentration of naphthalene in 100-fold diluted extracts. The equipment of the Collective Use Centre of the Faculty of Soil Science and of the Lomonosov Moscow State University was used. A DB-1 column (30 m × 0.25 mm id, 0.25 μm) was used as the chromatographic column. The oven temperature was increased by 15 °C per minute. The initial temperature was 40 °C.
The maximum temperature was 300 °C, held for 5 min. Mode without flow splitting (in non-splitting mode) was chosen. Injection volume was 1 µL. Helium was used as a makeup gas. Helium flow rate was 1 mL/min.
The correlation coefficient was found to be 0.97. The ANOVA was p = 0.05.
The following formula was used to calculate the degree of naphthalene biodegradation (N):
N = (N0 − Ni)/N0 × 100 [%],
where N0 is the concentration of naphthalene in the experiment without microorganisms after 7 days; Ni is the concentration of naphthalene in the experiment with microorganisms after 7 days.

2.5. Detection of Naphthalene Metabolites

Salicylate and catechol were measured using a high-performance liquid chromatography (HPLC) system (Agilent 1260, Agilent Technologies, Santa Clara, CA, USA) equipped with the UV-detector. The wavelengths were as follows: catechol, 280 nm; salicylate, 300 nm. A Synergi Hydro-RP chromatographic column (150 × 4.6 mm id, 4 µm) was used. The temperature of the column thermostat was 25 °C; the volume of the injected sample was 10 µL. Eluents: A, 90% water: 5% acetonitrile: 5% 0.1% trifluoroacetic acid; B, 95% acetonitrile: 5% 0.1% trifluoroacetic acid. Flow rate, 0.75 mL/min. Elution in gradient mode: 0 min, 5%; 15 min, 15%; 22.5 min, 40%; 25 min, 40%; 25.5 min, 95%; 30 min, 95%.
The presence of naphthalene metabolites was determined on the third, fifth and seventh day of the experiment.

3. Results and Discussion

3.1. Cultural and Morphological Characteristics of the Strain G. polyisoprenivorans 135

The strain G. polyisoprenivorans 135 forms rough colonies that are light beige to cream-colored on agarized media (Figure S1).
Strain 135 was originally identified as Rhodococcus rhodnii based on culture and morphological features and a number of biochemical tests [72]. Misidentification of Gordonia strains as Rhodococcus is a common phenomenon of the past when the methods in place at the time did not distinguish between the two related genera [73]. By ANI value (98.68%) and DDH value (88.40%), the strain is reliably included in the species G. polyisoprenivorans and clusters with the type Gordonia polyisoprenivorans strain on the phylogenetic tree (Figure 1).
At the moment (February 2024), the Genbank database contains 11 assemblies of Gordonia polyisoprenivorans genomes. Three of them belong to the type strain of G. polyisoprenivorans, which is maintained in different culture collections (Table 1).
When identifying strain 135, we used the ATCC BAA-14 assembly (JAAXPC000000000000.1) as a reference due to its superior quality in terms of coverage and number of contigs. In addition to strain 135, the genomes of three G. polyisoprenivorans strains are represented as complete polished assembly, while one strain (HW436) is represented as scaffold (Table 2).
Of the completely assembled genomes, strains G. polyisoprenivorans C and HW436 are the closest to strain 135. The strain Gordonia HW436 was sequenced and studied by Woo et al. [74] as a lignin degrader. Meanwhile, the strain G. polyisoprenivorans C is known as a carbamazepine degrader [75]. Carbamazepine, a widely used medication for epilepsy treatment, is a nitro-substituted three-ring aromatic compound, with the seven-carbon middle ring containing a nitrogen atom [76,77].

3.2. Horizontal Gene Transfer (HGT) Regions in the Genome of G. polyisoprenivorans Strain 135

According to Vos et al. [78], the acquisition of genetic elements is a key driver of bacterial evolutionary development. A clear example of this is the transfer of catabolic plasmids, as well as mobile genetic elements carrying specific metabolic pathways that integrate into chromosomes. As a result of this process, even distantly related taxa give rise to microorganisms with expanded catabolic properties, as well as the formation of an extensive gene pool whose exact source cannot be determined.
We identified 74 horizontal gene transfer (HGT) regions of total length 498 kbp scattered throughout the genome of the strain. These sites can be arranged in groups or single, with the longest one being 27.5 kbp (Figure S2). HGT regions are mainly home to repeat elements, transposases, IS elements and hypothetical proteins, although some catabolic genes, particularly those for the degradation of aromatic compounds, are also present (see below).
Horizontal transfer in Actinobacteria, especially soil bacteria, is a common phenomenon [79,80], but few examples of this event are specifically known in Gordonia strains with respect to catabolic genes. Jung et al. [81] suggested that the plasmid pGKT2 bearing genes of hexahydro-1,3,3-trinitro-1,3,5-triazine (RDX) degradation (gene locus xplAB) was obtained by the strain Gordonia sp. KTR9 during horizontal transfer. The authors demonstrated transfer of the plasmid within the genus (to the recipient strain Gordonia polyisoprenivorans), and successful intergeneric transfer to the strains Rhodococcus jostii RHA1 and Nocardia sp. TW2. Consequently, the recipient strains acquired the ability to utilize RDX.
Heine et al. [82] suggested that the ability to produce glutathione was acquired by G. rubripertincta strain CWB2 during the uptake of plasmids bearing genes for isoprene degradation. This assumption was confirmed by a different GC content region (in contrast to the main chromosome) and the presence of several mobile elements in close proximity to the genes for isoprene degradation. The authors noted a high percentage of similarity of this region with similar parts of the genomes of R. opacus strain 1CP and R. jostii strain RHA1.

3.3. Pangenome Analysis of Strain 135 and Its Closest Relatives

3.3.1. The Pangenome of Coding Regions

The chromosome structures of G. polyisoprenivorans strains 135, C, and HW436 have some differences in the arrangement of elements, but the genomes are generally similar (Figure 2). We found 70,749 SNPs between genomes 135 and HW436, and 79,323 SNPs between genomes 135 and C, which are evenly distributed throughout the genome. Single-nucleotide substitutions in the genome of strain 135 relative to the genomes of related strains account for 1.1–1.3% of the total genome length.
The G. polyisoprenivorans pangenome was analyzed using a dataset comprising three strains: G. polyisoprenivorans 135 and G. polyisoprenivorans C (CP073075.1) which are closely related, and G. polyisoprenivorans VH2 (CP003119.1), which is phylogenetically distinct from this pair. We aimed to identify differences not only between the closest relatives but also to observe which genes are unique to a strain that stands phylogenetically apart from them.
The pangenome of the three strains (Figure 3 and Figure S3) consists of 6259 genes, with 4089 classified as core genes. Dispensable genes, defined as those absent in at least one of the strains [83], comprise 674 genes (10.8%).
The distribution of COG functional categories in the strains is similar (Figure S4). Among the genes unique to strain 135 (Table S1) in pangenome, it is interesting to note those related to the degradation of aromatic compounds (see below).

3.3.2. The Pangenome of Non-Coding Regions

The concept of the pangenome is primarily focused on protein-coding open reading frames (ORFs) [84,85]. However, such an approach automatically excludes non-coding regions, which constitute up to 15% of the total genome length [86,87]. Non-coding regions include structurally important elements of genomes such as promoters, terminators, virulence factors, and non-coding RNAs [88,89]. Acquisition or, conversely, exclusion of these regions from the genome can significantly influence the phenotype.
We analyzed the diversity of non-coding regions in the genome of the strain 135 and the pangenome of G. polyisoprenivorans. For analysis, in addition to strain 135, we included four strains of G. polyisoprenivorans with completely assembled genomes: HW436 (NZ_ARVZ01000001.1), C (CP073075.1), R9 (CP072203.1), and VH2 (CP003119.1).
There are two perspectives on the transfer of intergenic (regulatory) regions. The first suggests that the connection between the coding region and the upstream-located non-coding region prevents them from moving independently of each other [90]. The second allows for the possibility of the separate movement of regulatory regions, a phenomenon known as horizontal regulatory transfer (HRT) [91,92]. Such regulatory regions are referred to as “switched”. During the analysis of the non-coding pangenome (Thorpe et al. [64] proposed the term “panIGRome”), in cases where different intergenic regions corresponded to the same downstream gene in genomes of different strains, we considered such intergenic regions to be switched.
Earlier studies on strains of S. aureus [64] and E. coli [92] have shown that genes with switched upstream intergenic regions exhibit a higher level of expression compared to genes with “native” (i.e., non-switched) intergenic regions.
1834 intergenic regions of 100–1000 bp in length were detected in the genome of the strain 135, 71 of them were considered as switched, meaning they differ in their sequences from the sequences lying between pairs of analogous genes in other strains of G. polyisoprenivorans (Figure S5). The IGR (1730231-1730449) in the region containing genes involved in the catabolism of aromatic compounds measure 218 bp. This IGR partially overlaps with sequences of non-coding RNAs such as the Actinomyces denticolens FMN riboswitch (RFN element) and the Ruminococcus sp. CAG:9-related_41_34 FMN riboswitch (RFN element).

3.3.3. Search for Non-Coding RNAs in the Genome of G. polyisoprenivorans Strain 135

In the genome of the strain, we identified 140 sequences corresponding to families of non-coding RNAs (ncRNAs) from the Rfam database. Further inspection showed that 34 of them corresponded to ncRNAs predicted for Actinobacteria of the genera Gordonia, Rhodococcus, and Mycobacterium. We compared the sequences and localization of elements, potentially corresponding to ncRNAs, with the results obtained from the search for intergenic regions (IGRs).
We discovered a switched non-coding region upstream of the gene encoding 4-hydroxybenzoate 3-monooxygenase. The product of this gene controls the hydroxylation reaction of the aromatic compound 4-hydroxybenzoate [93]. The intergenic region, 197 nucleotides in length, is located between the HTH-type transcriptional regulator kipR and 4-hydroxybenzoate 3-monooxygenase praI. We found two terminators in the region, but sequences corresponding to ncRNAs were absent.
A region 65 nucleotides long, located at coordinates 2407663–2407727, was identified as ykkC-III. This ncRNA is not only found in Gordonia but also in other Actinobacteria, and according to several studies [94,95], it is involved in regulating the removal of guanidine from cells. The Rfam database provides a broader characterization: according to Rfam, ykkC regulates the function of efflux pumps and participates in the removal of toxic compounds, including xenobiotics. We also detected several riboswitches, a 6C RNA sequence with the function of stress response [96], and an F6 sRNA sequence. According to [97], F6 sRNA modifies expression of chaperonins and is induced in starvation conditions.

3.4. Growth Characteristics of Strain 135 on Aromatic Compounds

Some Gordonia strains are known to be able to degrade PAHs [98,99,100]. The strain Gordonia sp. Q8 was capable of degrading not only individual PAHs (naphthalene and pyrene) but also a mixture of naphthalene, phenanthrene, anthracene and pyrene in mineral medium [99]. The strain Gordonia sp. Q8 was capable of degrading naphthalene at a concentration of 0.5 g/L in 3 days by 70% (net of abiotic loss of PAHs). In our results, the degradation rate of naphthalene by the strain 135 was 39.43 ± 5.25% in 5 days relative to the control system without microorganisms. However, the initial level of naphthalene in the system was 2 g/L, which was 4 times higher compared to the data of the article [99]. The results indicate a high biodegradative potential of the strain 135 with respect to naphthalene.
In many prokaryotes, the ability to degrade naphthalene is realized through formation and further consumption of salicylate [101]. The strain G. polyisoprenivorans 135 is capable of growth on salicylate. Moreover, the culture reached the stationary phase on salicylate (0.1 g/L) in 2 days, while on naphthalene this period was 4 days (Figure 4).
Jacques et al. [102] reported a strain of G. polyisoprenivorans capable of utilizing pyrene, anthracene, phenanthrene, but not naphthalene or salicylate. The strain G. polyisoprenivorans strain 135 actively utilizes salicylate, a key metabolite of the naphthalene degradation pathway. At present, this is the only known strain of G. polyisoprenivorans with experimentally confirmed ability to utilize naphthalene and salicylate.

3.5. Assumptions about the Organization of Pathways and Mechanisms of Naphthalene Degradation in the Strain Gordonia Polyisoprenivorans 135

The genetic organization of the PAH catabolism pathway in Gordonia was initially described by Lin et al. [103]. The operon includes genes for rubredoxin, GntR-like and XylR-like regulators, the large (narAa) and small (narAb) subunits of naphthalene dioxygenase, naphthalene dihydrodiol dehydrogenase narB, hydratase aldolase narC, and a gene designated orf7 with unknown function. It is interesting to note that the nar operon in strain Gordonia sp. CC-NAPH129-6 [103] appears to have been acquired through horizontal transfer, as it is located on a 97 kb plasmid. Comparison of the sequences of its elements and phylogenetic markers (16S rRNA, gyrB) led the authors to suggest that Rhodococcus strain could be its donor.
The degradation of naphthalene In Actinobacteria mainly proceeds through salicylate [104,105]. However, there are strains where the naphthalene degradation pathway does not involve salicylate formation, such as Rhodococcus opacus strain M213 [16]. The authors noted that the strain did not utilize salicylate as a carbon and energy source.
Salicylate can be converted to catechol by the action of salicylate 1-hydroxylase [106,107] or gentisate by the action of salicylate 5-hydroxylase [104]. There are also reports of the conversion of salicylate to 2-oxohepta-3,5-dienedioic acid by the action of salicylate 1,2-dioxygenase. Such a reaction has been reported for the Gram-negative strain Pseudaminobacter salicylatoxidans [108], but there are no examples of this reaction in Actinobacteria.
In our work, the strain G. polyisoprenivorans 135 grew actively on salicylate and catechol and did not grow on gentisate; therefore, we hypothesize that the pathway of naphthalene degradation in strain 135 includes the stages of transformation of naphthalene to salicylate and then salicylate to catechol. HPLC-analysis showed no accumulation of metabolites, so we assume that all formed intermediates are immediately utilized in subsequent reactions.
Interestingly, despite the experimentally confirmed ability of strain 135 to utilize naphthalene and salicylate, we found no nar genes previously detected in Gordonia [103]. Analyzing the genomes of other Gordonia strains from the Genbank database, we found nar sequences in the genomes of strains G. namibiensis NBRC 108,229 (BAHE01000003.1), G. metallireducens tSed Te1 (JAJQJP010000036.1), G. rubripertincta BP295 (JAFFGU010000009.1), and three strains of G. paraffinivorans. Based on gene sequences, we assume that nar genes in Gordonia were acquired from Rhodococcus and Streptomyces.
We also did not find salicylate hydroxylase genes in the genome of strain 135. In addition, it is worth mentioning that salicylate hydroxylases are not common in Gordonia strains. According to BLAST search results using the WGS and nr/nt databases as references, these genes were found only in strains Gordonia sp. PDNC005 (CP070351.1), Gordonia sp. MMO (JBBCWK010000002.1), Gordonia malaquae MMO-152 (JBBCUB010000003.1), Gordonia spumicola NBRC 107,696 (BJOV01000003.1), and Gordonia liuliyuniae HY366 (JAKKOR010000002.1). These genes are mostly found in Rhodococcus strains, which, as in the case of the nar operon, suggests acquisition by horizontal transfer. Conversely, despite the presence of the gentisate 1,2-dioxygenase gene in the genome of strain G. polyisoprenivorans 135, the strain is unable to utilize this compound.
We identified genes responsible for ortho- and meta-pathways of catechol degradation in the genome of strain G. polyisoprenivorans 135.
Instead of nar genes, during genome annotation and pangenome analysis we identified six genes potentially involved in the catabolism of aromatic compounds in the genome of strain 135 (Table 3).
The first 4 genes belong to the same region (Figure 5).
The genes encoding enzymes involved in opening and cleavage of aromatic rings in the genome of strain 135 can be divided into the following categories:
1. aromatic ring-hydroxylating dioxygenase group.
These genes encode enzymes that convert aromatic structures to cis-diols [109]. We found 4 such genes in the genome (Table 3). Comparison of the amino acid sequences of these genes did not reveal any relatedness between them.
2. extradiol ring-cleavage dioxygenase group.
Unlike intradiol enzymes, which use non-haem Fe(III) to open an aromatic ring via the ortho-pathway, extradiol enzymes use non-haem Fe(II) and cleave aromatic rings via the meta-pathway (between a hydroxylated carbon atom and an adjacent non-hydroxylated carbon atom) [110,111]. We identified three genes encoding extradiol ring-cleavage dioxygenase in the genome of strain 135.
One of the extradiol dioxygenases, iron-dependent extradiol dioxygenase HsaC, is involved in the degradation of steroid compounds. The enzyme encoded by the hsaC gene catalyzes the meta-cleavage of 3,4-dihydroxy-9,10-seconandrost-1,3,510-triene-9,17-dione (3,4-DHSA) to produce 4,5-9,10-diseco-3-hydroxy-5,9,17-trioxoandrosta-110,2-diene-4-oic acid (4,9-DSHA) [38]. Genes related to steroid catabolism are commonly found in various species of Gordonia genus. Zhang et al. [38] studied the organization of steroid catabolism genes in Gordonia neofelifaecis strain NRRL B-59395, which is a type strain of the G. neofellifaecis species. The ability of strain NRRL B-59395 to transform steroid compounds has been experimentally confirmed [112]. Additionally, in the work of Lee et al. [113] the strain Gordonia sp. JH63 was found to possess genes of cholesterol catabolism.
The extradiol ring-cleavage dioxygenase (WCB38962.1) and aromatic ring-hydroxylating dioxygenase subunit alpha (WCB38965.1) genes are not commonly found in the gene pool of G. polyisoprenivorans. Based on the sequences of these genes, there is no specific bacterial genus in which they would be most frequently found, indicating that they do not have a definite source. Sequences related to these genes are found in bacteria of the genera such as Streptomyces, Rhodococcus, Mycobacterium, and Mycolicibacterium (Table S2). These genes are located at the HGT site of 7501 bp in the coordinates 1,727,500–1,735,000.
Thus, summarizing the experimental data and bioinformatic analysis, we assume the following mechanism of naphthalene utilization by the strain G. polyisoprenivorans 135. The process is carried out through the formation of salicylate, but without its accumulation in the culture medium. The question of genetic control of salicylate conversion to catechol is still open; salicylate 1-hydroxylase is absent in the genome of the strain. According to Roy and Kastner [108], it is possible that extradiol dioxygenases may be involved in the salicylate conversion, the reaction results in the formation of 2,7-dioxo-3-hydroxyhepta-3,5-dienoic acid. However, there are no examples of this reaction in Actinobacteria, so we assume that the involvement of extradiol ring-cleavage dioxygenases is limited to catechol conversion processes. The genes of ortho- and meta-pathways of catechol conversion are represented in the genome.

4. Conclusions

The strain Gordonia polyisoprenivorans 135 possesses an interesting set of genes for the catabolism of aromatic compounds. Interestingly, some of these genes are not typical genes of Gordonia, but belong to the cloud-pangenome of Actinobacteria. Several genes of PAH catabolism are located within horizontally transferred region.
Some sequences of intergenic regions in the genome of strain 135 differ from the IGRs located between the same gene pairs in the genomes of related G. polyisoprenivorans strains. Additionally, we made several predictions of ncRNAs that could potentially be involved in catabolism of pollutants by strain 135. These findings offer deeper insights into the genetic organization of PAH catabolism in Gordonia strains.
The strain G. polyisoprenivorans 135 in our work utilized naphthalene and grew actively on salicylate. At present, this is the only known strain of G. polyisoprenivorans with experimentally confirmed ability to utilize these compounds.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/biology13050339/s1, Figure S1: Colony appearance of the strain Gordonia polyisoprenivorans 135; Figure S2: Circular genomic map of G. polyisoprenivorans 135 chromosome; Figure S3: Gordonia polyisoprenivorans strains in pangenomic comparison; Figure S4: Distribution of COG functional categories; Figure S5: Distribution of switched noncoding intergenic regions in the genome of G. polyisoprenivorans strain 135; Table S1: List of genes unique for the strain G. polyisoprenivorans 135; Table S2: Occurrence of genes (a) extradiol ring-cleavage dioxygenase and (b) aromatic ring-hydroxylating dioxygenase in Actinobacteria genomes.

Author Contributions

Conceptualization, Y.D.; methodology, E.F. and A.B.; software, Y.D.; validation, E.F., A.V. and O.K.; formal analysis, I.S.; investigation, E.F., O.K., R.S. and A.B.; resources, Y.D., R.S. and I.S.; data curation, Y.D. and I.S.; writing—original draft preparation, E.F. and A.V.; writing—review and editing, Y.D., A.V. and E.F.; visualization, E.F.; supervision, Y.D.; project administration, Y.D.; funding acquisition, Y.D. All authors have read and agreed to the published version of the manuscript.

Funding

This work was financially supported by the Russian Science Foundation, grant number 22-74-10082.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The genomic data are available in the GenBank database under accession number CP116236.1 (BioProject PRJNA923796, BioSample SAMN32738803).

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Honda, M.; Suzuki, N. Toxicities of Polycyclic Aromatic Hydrocarbons for Aquatic Animals. Int. J. Environ. Res. Public Health 2020, 17, 1363. [Google Scholar] [CrossRef]
  2. Magalhães, K.M.; Carreira, R.S.; Filho, J.S.R.; Rocha, P.P.; Santana, F.M.; Yogui, G.T. Polycyclic aromatic hydrocarbons (PAHs) in fishery resources affected by the 2019 oil spill in Brazil: Short-term environmental health and seafood safety. Mar. Pollut. Bull. 2022, 175, 113334. [Google Scholar] [CrossRef]
  3. Han, M.; Ma, A.; Dong, Z.; Yin, J.; Shao, B. Organochlorine pesticides and polycyclic aromatic hydrocarbons in serum of Beijing population: Exposure and health risk assessment. Sci. Total. Environ. 2023, 860, 160358. [Google Scholar] [CrossRef]
  4. Roszko, M.; Juszczyk, K.; Szczepańska, M.; Świder, O.; Szymczyk, K. Background levels of polycyclic aromatic hydrocarbons and legacy organochlorine pesticides in wheat sampled in 2017 and 2018 in Poland. Environ. Monit. Assess. 2020, 192, 1–17. [Google Scholar] [CrossRef]
  5. Zhonghua, Z.; Zhang, L.; Wu, J. Polycyclic aromatic hydrocarbons (PAHs) and organochlorine pesticides (OCPs) in sediments from lakes along the middle-lower reaches of the Yangtze River and the Huaihe River of China. Limnol. Oceanogr. 2015, 61, 47–60. [Google Scholar] [CrossRef]
  6. Dandajeh, H.A.; Talibi, M.; Ladommatos, N.; Hellier, P. Polycyclic aromatic hydrocarbon and soot emissions in a diesel engine and from a tube reactor. J. King Saud Univ. Eng. Sci. 2020, 34, 435–444. [Google Scholar] [CrossRef]
  7. Freeman, D.J.; Cattell, F.C.R. Woodburning as a source of atmospheric polycyclic aromatic hydrocarbons. Environ. Sci. Technol. 1990, 24, 1581–1585. [Google Scholar] [CrossRef]
  8. Lim, H.; Silvergren, S.; Spinicci, S.; Rad, F.M.; Nilsson, U.; Westerholm, R.; Johansson, C. Contribution of wood burning to exposures of PAHs and oxy-PAHs in Eastern Sweden. Atmospheric Meas. Tech. 2022, 22, 11359–11379. [Google Scholar] [CrossRef]
  9. Lima, A.L.C.; Farrington, J.W.; Reddy, C.M. Combustion-Derived Polycyclic Aromatic Hydrocarbons in the Environment—A Review. Environ. Forensics 2005, 6, 109–131. [Google Scholar] [CrossRef]
  10. Tan, Y.L.; Quanci, J.F.; Borys, R.D.; Quanci, M.J. Polycyclic aromatic hydrocarbons in smoke particles from wood and duff burning. Atmospheric Environ. Part A Gen. Top. 1992, 26, 1177–1181. [Google Scholar] [CrossRef]
  11. Abdel-Shafy, H.I.; Mansour, M.S.M. A review on polycyclic aromatic hydrocarbons: Source, environmental impact, effect on human health and remediation. Egypt. J. Pet. 2016, 25, 107–123. [Google Scholar] [CrossRef]
  12. Patel, A.B.; Shaikh, S.; Jain, K.R.; Desai, C.; Madamwar, D. Polycyclic Aromatic Hydrocarbons: Sources, Toxicity, and Remediation Approaches. Front. Microbiol. 2020, 11, 562813. [Google Scholar] [CrossRef]
  13. Rabani, M.S.; Habib, A.; Gupta, M.K. Polycyclic Aromatic Hydrocarbons: Toxic Effects and Their Bioremediation Strategies. In Bioremediation and Biotechnology, Vol 4: Techniques for Noxious Substances Remediation; Springer International Publishing: Hoboken, NJ, USA, 2020. [Google Scholar] [CrossRef]
  14. Anan‘ina, L.N.; Yastrebova, O.V.; Demakov, V.A.; Plotnikova, E.G. Naphthalene-degrading bacteria of the genus Rhodococcus from the Verkhnekamsk salt mining region of Russia. Antonie van Leeuwenhoek 2011, 100, 309–316. [Google Scholar] [CrossRef]
  15. Cavalca, L.; Colombo, M.; Larcher, S.; Gigliotti, C.; Collina, E.; Andreoni, V. Survival and naphthalene-degrading activity of Rhodococcus sp. strain 1BN in soil microcosms. J. Appl. Microbiol. 2002, 92, 1058–1065. [Google Scholar] [CrossRef]
  16. Uz, I.; Duan, Y.; Ogram, A. Characterization of the naphthalene-degrading bacterium,Rhodococcus opacusM213. FEMS Microbiol. Lett. 2000, 185, 231–238. [Google Scholar] [CrossRef]
  17. Zeinali, M.; Vossoughi, M.; Ardestani, S. Degradation of phenanthrene and anthracene byNocardia otitidiscaviarumstrain TSH1, a moderately thermophilic bacterium. J. Appl. Microbiol. 2008, 105, 398–406. [Google Scholar] [CrossRef]
  18. Zeinali, M.; Vossoughi, M.; Ardestani, S.K. Naphthalene metabolism in Nocardia otitidiscaviarum strain TSH1, a moderately thermophilic microorganism. Chemosphere 2008, 72, 905–909. [Google Scholar] [CrossRef]
  19. Ausuri, J.; Vitale, G.A.; Coppola, D.; Esposito, F.P.; Buonocore, C.; de Pascale, D. Assessment of the Degradation Potential and Genomic Insights towards Phenanthrene by Dietzia psychralcaliphila JI1D. Microorganisms 2021, 9, 1327. [Google Scholar] [CrossRef]
  20. Chen, W.; Li, J.; Sun, X.; Min, J.; Hu, X. High efficiency degradation of alkanes and crude oil by a salt-tolerant bacterium Dietzia species CN-3. Int. Biodeterior. Biodegradation 2017, 118, 110–118. [Google Scholar] [CrossRef]
  21. Venil, C.K.; Malathi, M.; Devi, P.R. Characterization of Dietzia maris AURCCBT01 from oil-contaminated soil for biodegradation of crude oil. 3 Biotech 2021, 11, 1–13. [Google Scholar] [CrossRef]
  22. Kelley, I.; Freeman, J.P.; Cerniglia, C.E. Identification of metabolites from degradation of naphthalene by a Mycobacterium sp. Biodegradation 1990, 1, 283–290. [Google Scholar] [CrossRef]
  23. Tirkey, S.R.; Ram, S.; Mishra, S. Naphthalene degradation studies using Pseudomonas sp. strain SA3 from Alang-Sosiya ship breaking yard, Gujarat. Heliyon 2021, 7, e06334. [Google Scholar] [CrossRef]
  24. Ma, J.; Zhuang, Y.; Wang, Y.; Zhu, N.; Wang, T.; Xiao, H.; Chen, J. Update on new trend and progress of the mechanism of polycyclic aromatic hydrocarbon biodegradation by Rhodococcus, based on the new understanding of relevant theories: A review. Environ. Sci. Pollut. Res. 2023, 30, 93345–93362. [Google Scholar] [CrossRef]
  25. Peng, T.; Kan, J.; Hu, J.; Hu, Z. Genes and novel sRNAs involved in PAHs degradation in marine bacteria Rhodococcus sp. P14 revealed by the genome and transcriptome analysis. 3 Biotech 2020, 10, 1–10. [Google Scholar] [CrossRef]
  26. Song, X.; Xu, Y.; Li, G.; Zhang, Y.; Huang, T.; Hu, Z. Isolation, characterization of Rhodococcus sp. P14 capable of degrading high-molecular-weight polycyclic aromatic hydrocarbons and aliphatic hydrocarbons. Mar. Pollut. Bull. 2011, 62, 2122–2128. [Google Scholar] [CrossRef]
  27. Krivoruchko, A.; Kuyukina, M.; Peshkur, T.; Cunningham, C.J.; Ivshina, I. Rhodococcus Strains from the Specialized Collection of Alkanotrophs for Biodegradation of Aromatic Compounds. Molecules 2023, 28, 2393. [Google Scholar] [CrossRef]
  28. Wu, P.; Wang, Y.-S. Fluorene degradation by Rhodococcus sp. A2-3 isolated from hydrocarbon contaminated sediment of the Pearl River estuary, China. Ecotoxicology 2021, 30, 929–935. [Google Scholar] [CrossRef]
  29. Ehiosun, K.I.; Godin, S.; Urios, L.; Lobinski, R.; Grimaud, R. Degradation of long-chain alkanes through biofilm formation by bacteria isolated from oil-polluted soil. Int. Biodeterior. Biodegrad. 2022, 175, 105508. [Google Scholar] [CrossRef]
  30. Liu, Y.; Wu, J.; Liu, Y.; Wu, X. Biological Process of Alkane Degradation by Gordonia sihwaniensis. ACS Omega 2021, 7, 55–63. [Google Scholar] [CrossRef]
  31. Piccolo, L.L.; De Pasquale, C.; Fodale, R.; Puglia, A.M.; Quatrini, P. Involvement of an Alkane Hydroxylase System of Gordonia sp. Strain SoCg in Degradation of Solid n -Alkanes. Appl. Environ. Microbiol. 2011, 77, 1204–1213. [Google Scholar] [CrossRef]
  32. Akhtar, N.; Akhtar, K.; Ghauri, M.A. Biodesulfurization of Thiophenic Compounds by a 2-Hydroxybiphenyl-Resistant Gordonia sp. HS126-4N Carrying dszABC Genes. Curr. Microbiol. 2017, 75, 597–603. [Google Scholar] [CrossRef]
  33. Hu, T.; Yang, C.; Hou, Z.; Liu, T.; Mei, X.; Zheng, L.; Zhong, W. Phthalate Esters Metabolic Strain Gordonia sp. GZ-YC7, a Potential Soil Degrader for High Concentration Di-(2-ethylhexyl) Phthalate. Microorganisms 2022, 10, 641. [Google Scholar] [CrossRef]
  34. Kanaujiya, D.K.; Sivashanmugam, S.; Pakshirajan, K. Biodegradation and toxicity removal of phthalate mixture by Gordonia sp. in a continuous stirred tank bioreactor system. Environ. Technol. Innov. 2022, 26, 102324. [Google Scholar] [CrossRef]
  35. Nishioka, T.; Iwata, M.; Imaoka, T.; Mutoh, M.; Egashira, Y.; Nishiyama, T.; Shin, T.; Fujii, T. A Mono-2-Ethylhexyl Phthalate Hydrolase from a Gordonia sp. That Is Able To Dissimilate Di-2-Ethylhexyl Phthalate. Appl. Environ. Microbiol. 2006, 72, 2394–2399. [Google Scholar] [CrossRef]
  36. Drzyzga, O.; Fernández de las Heras, L.; Morales, V.; Navarro Llorens, J.M.; Perera, J. Cholesterol degradation by Gordonia cholesterolivorans. Appl. Environ. Microbiol. 2011, 77, 4802–4810. [Google Scholar] [CrossRef]
  37. Liu, N.; Maser, E.; Zhang, T. Genomic analysis of Gordonia polyisoprenivorans strain R9, a highly effective 17 beta-estradiol- and steroid-degrading bacterium. Chem. Interact. 2021, 350, 109685. [Google Scholar] [CrossRef] [PubMed]
  38. Zhang, Q.; Ren, Y.; He, J.; Cheng, S.; Yuan, J.; Ge, F.; Li, W.; Zhang, Y.; Xie, G. Multiplicity of 3-ketosteroid Δ1-dehydrogenase enzymes in Gordonia neofelifaecis NRRL B-59395 with preferences for different steroids. Ann. Microbiol. 2015, 65, 1961–1971. [Google Scholar] [CrossRef]
  39. Chauhan, A.K.; Ahmad, A.; Singh, S.P.; Kumar, A. Biodesulfurization of benzonaphthothiophene by an isolated Gordonia sp. IITR100. Int. Biodeterior. Biodegrad. 2015, 104, 105–111. [Google Scholar] [CrossRef]
  40. Ahmad, A.; Chauhan, A.K.; Javed, S.; Kumar, A. Desulfurization of thianthrene by a Gordonia sp. IITR100. Biotechnol. Lett. 2014, 36, 2209–2214. [Google Scholar] [CrossRef] [PubMed]
  41. Alves, L.; Marques, S.; Matos, J.; Tenreiro, R.; Gírio, F.M. Dibenzothiophene desulfurization by Gordonia alkanivorans strain 1B using recycled paper sludge hydrolyzate. Chemosphere 2008, 70, 967–973. [Google Scholar] [CrossRef] [PubMed]
  42. Santos, S.C.C.; Alviano, D.S.; Pádula, M.; Leitão, A.C.; Martins, O.B.; Ribeiro, C.M.S.; Sassaki, M.Y.M.; Matta, C.P.S.; Bevilaqua, J.; Sebastián, G.V.; et al. Characterization of Gordonia sp. strain F.5.25.8 capable of dibenzothiophene desulfurization and carbazole utilization. Appl. Microbiol. Biotechnol. 2005, 71, 355–362. [Google Scholar] [CrossRef] [PubMed]
  43. Delegan, Y.; Kocharovskaya, Y.; Frantsuzova, E.; Streletskii, R.; Vetrova, A. Characterization and genomic analysis of Gordonia alkanivorans 135, a promising dibenzothiophene-degrading strain. Biotechnol. Rep. 2021, 29, e00591. [Google Scholar] [CrossRef]
  44. Young, C.-C.; Lin, T.-C.; Yeh, M.-S.; Shen, F.-T.; Chang, J.-S. Identification and Kinetic Characteristics of an Indigenous Diesel-degrading Gordonia alkanivorans Strain. World J. Microbiol. Biotechnol. 2005, 21, 1409–1414. [Google Scholar] [CrossRef]
  45. Isaac, P.; Martínez, F.L.; Bourguignon, N.; Sánchez, L.A.; Ferrero, M.A. Improved PAHs removal performance by a defined bacterial consortium of indigenous Pseudomonas and actinobacteria from Patagonia, Argentina. Int. Biodeterior. Biodegradation 2015, 101, 23–31. [Google Scholar] [CrossRef]
  46. Frantsuzova, E.; Bogun, A.; Shishkina, L.; Vetrova, A.; Solyanikova, I.; Delegan, Y. Pangenome Analysis and Physiological Characterization of Gordonia alkanivorans Strains Capable of Utilizing Persistent Organic Pollutants. Eng. Proc. 2023, 37, 110. [Google Scholar] [CrossRef]
  47. Kurniati, T.H.; Rusmana, I.; Suryani, A.; Mubarik, N.R. Degradation of Polycyclic Aromatic Hydrocarbon Pyrene by Biosurfactant-Producing Bacteria Gordonia cholesterolivorans AMP 10. Biosaintifika J. Biol. Biol. Educ. 2016, 8, 336. [Google Scholar] [CrossRef]
  48. Hu, F.-C.; Li, X.-Y.; Su, Z.-C.; Wang, X.-J.; Zhang, H.-W.; Sun, J.-D. Identification and degradation capability of three pyrene-degrading Gordonia sp. strains. Yingyong Shengtai Xuebao 2011, 22, 1857–1862. [Google Scholar]
  49. Emelyanova, E.V.; Souzina, N.E.; Polivtseva, V.N.; Reshetilov, A.N.; Solyanikova, I.P. Survival and biodegradation activity of Gordonia polyisoprenivorans 135: Basics of a biosensor receptor. Appl. Biochem. Microbiol. 2017, 53, 580–586. [Google Scholar] [CrossRef]
  50. Suzina, N.E.; Sorokin, V.V.; Polivtseva, V.N.; Klyueva, V.V.; Emelyanova, E.V.; Solyanikova, I.P. From Rest to Growth: Life Collisions of Gordonia polyisoprenivorans 135. Microorganisms 2022, 10, 465. [Google Scholar] [CrossRef]
  51. Frantsuzova, E.; Bogun, A.; Solomentsev, V.; Vetrova, A.; Streletskii, R.; Solyanikova, I.; Delegan, Y. Whole Genome Analysis and Assessment of the Metabolic Potential of Gordonia rubripertincta Strain 112, a Degrader of Aromatic and Aliphatic Compounds. Biology 2023, 12, 721. [Google Scholar] [CrossRef]
  52. Frantsuzova, E.; Solomentsev, V.; Vetrova, A.; Travkin, V.; Solyanikova, I.; Delegan, Y. Complete Genome Sequence of Gordonia polyisoprenivorans 135, a Promising Degrader of Aromatic Compounds. Genome Announc. 2023, 12, e0005823. [Google Scholar] [CrossRef]
  53. Parks, D.H.; Imelfort, M.; Skennerton, C.T.; Hugenholtz, P.; Tyson, G.W. CheckM: Assessing the quality of microbial genomes recovered from isolates, single cells, and metagenomes. Genome Res. 2015, 25, 1043–1055. [Google Scholar] [CrossRef]
  54. Meier-Kolthoff, J.P.; Auch, A.F.; Klenk, H.-P.; Göker, M. Genome sequence-based species delimitation with confidence intervals and improved distance functions. BMC Bioinform. 2013, 14, 60. [Google Scholar] [CrossRef]
  55. Yoon, S.-H.; Ha, S.-M.; Lim, J.; Kwon, S.; Chun, J. A large-scale evaluation of algorithms to calculate average nucleotide identity. Antonie van Leeuwenhoek 2017, 110, 1281–1286. [Google Scholar] [CrossRef]
  56. Darling, A.C.E.; Mau, B.; Blattner, F.R.; Perna, N.T. Mauve: Multiple Alignment of Conserved Genomic Sequence with Rearrangements. Genome Res. 2004, 14, 1394–1403. [Google Scholar] [CrossRef]
  57. Dereeper, A.; Summo, M.; Meyer, D.F. PanExplorer: A web-based tool for exploratory analysis and visualization of bacterial pan-genomes. Bioinformatics 2022, 38, 4412–4414. [Google Scholar] [CrossRef]
  58. Krzywinski, M.; Schein, J.; Birol, I.; Connors, J.; Gascoyne, R.; Horsman, D.; Jones, S.J.; Marra, M.A. Circos: An information aesthetic for comparative genomics. Genome Res. 2009, 19, 1639–1645. [Google Scholar] [CrossRef]
  59. Grant, J.R.; Enns, E.; Marinier, E.; Mandal, A.; Herman, E.K.; Chen, C.-Y.; Graham, M.; Van Domselaar, G.; Stothard, P. Proksee: In-depth characterization and visualization of bacterial genomes. Nucleic Acids Res. 2023, 51, W484–W492. [Google Scholar] [CrossRef]
  60. Chao, J.; Li, Z.; Sun, Y.; Aluko, O.O.; Wu, X.; Wang, Q.; Liu, G. MG2C: A user-friendly online tool for drawing genetic maps. Mol. Hortic. 2021, 1, 1–4. [Google Scholar] [CrossRef] [PubMed]
  61. Kanehisa, M.; Goto, S. KEGG: Kyoto Encyclopedia of Genes and Genomes. Nucleic Acids Res. 2000, 28, 27–30. [Google Scholar] [CrossRef] [PubMed]
  62. Brown, C.L.; Mullet, J.; Hindi, F.; Stoll, J.E.; Gupta, S.; Choi, M.; Keenum, I.; Vikesland, P.; Pruden, A.; Zhang, L. mobileOG-db: A Manually Curated Database of Protein Families Mediating the Life Cycle of Bacterial Mobile Genetic Elements. Appl. Environ. Microbiol. 2022, 88, e0099122. [Google Scholar] [CrossRef] [PubMed]
  63. Vernikos, G.S.; Parkhill, J. Interpolated variable order motifs for identification of horizontally acquired DNA: Revisiting the Salmonella pathogenicity islands. Bioinformatics 2006, 22, 2196–2203. [Google Scholar] [CrossRef]
  64. A Thorpe, H.; Bayliss, S.C.; Sheppard, S.K.; Feil, E.J. Piggy: A rapid, large-scale pan-genome analysis tool for intergenic regions in bacteria. GigaScience 2018, 7, 1–11. [Google Scholar] [CrossRef] [PubMed]
  65. Page, A.J.; Cummins, C.A.; Hunt, M.; Wong, V.K.; Reuter, S.; Holden, M.T.G.; Fookes, M.; Falush, D.; Keane, J.A.; Parkhill, J. Roary: Rapid large-scale prokaryote pan genome analysis. Bioinformatics 2015, 31, 3691–3693. [Google Scholar] [CrossRef] [PubMed]
  66. Tange, O. GNU Parallel 20200622 (‘Privacy Shield’). Zenodo. 2020. Available online: https://zenodo.org/records/3956817 (accessed on 15 March 2024).
  67. Di Salvo, M.; Puccio, S.; Peano, C.; Lacour, S.; Alifano, P. RhoTermPredict: An algorithm for predicting Rho-dependent transcription terminators based on Escherichia coli, Bacillus subtilis and Salmonella enterica databases. BMC Bioinform. 2019, 20, 1–11. [Google Scholar] [CrossRef] [PubMed]
  68. Feng, C.-Q.; Zhang, Z.-Y.; Zhu, X.-J.; Lin, Y.; Chen, W.; Tang, H.; Lin, H. iTerm-PseKNC: A sequence-based tool for predicting bacterial transcriptional terminators. Bioinformatics 2018, 35, 1469–1477. [Google Scholar] [CrossRef] [PubMed]
  69. Naville, M.; Ghuillot-Gaudeffroy, A.; Marchais, A.; Gautheret, D. ARNold: A web tool for the prediction of Rho-independent transcription terminators. RNA Biol. 2011, 8, 11–13. [Google Scholar] [CrossRef] [PubMed]
  70. Arias-Carrasco, R.; Vásquez-Morán, Y.; Nakaya, H.I.; Maracaja-Coutinho, V. StructRNAfinder: An automated pipeline and web server for RNA families prediction. BMC Bioinform. 2018, 19, 55–55:7. [Google Scholar] [CrossRef] [PubMed]
  71. Wickham, H. Data Analysis; Springer International Publishing: Berlin/Heidelberg, Germany, 2016; pp. 189–201. [Google Scholar] [CrossRef]
  72. Solyanikova, I.P.; Golovlev, E.L.; Lisnyak, O.V.; Golovleva, L.A. Isolation and characterization of catechol 1,2-dioxygenases from Rhodococcus rhodnii strain 135 and Rhodococcus rhodochrous strain 89: Comparison with analogous en-zymes of the ordinary and modified ortho-cleavage pathways. Biochem. Biokhimiia 1999, 64, 824–831. [Google Scholar]
  73. Frantsuzova, E.; Bogun, A.; Vetrova, A.; Delegan, Y. Methods of Identifying Gordonia Strains in Clinical Samples. Pathogens 2022, 11, 1496. [Google Scholar] [CrossRef]
  74. Woo, H.L.; Hazen, T.C. Enrichment of Bacteria From Eastern Mediterranean Sea Involved in Lignin Degradation via the Phenylacetyl-CoA Pathway. Front. Microbiol. 2018, 9, 922. [Google Scholar] [CrossRef]
  75. Wang, Y.; Gao, J.; Zhou, S.; Lian, M. Microbial degradation of carbamazepine by a newly isolated of Gordonia polyophrenivorans. Environ. Technol. Innov. 2023, 32, 103322. [Google Scholar] [CrossRef]
  76. Chen, G.; Dong, W.; Wang, H.; Zhao, Z.; Wang, F.; Wang, F.; Nieto-Delgado, C. Carbamazepine degradation by visible-light-driven photocatalyst Ag3PO4/GO: Mechanism and pathway. Environ. Sci. Ecotechnol. 2021, 9, 100143. [Google Scholar] [CrossRef] [PubMed]
  77. Li, Y.; Yang, Y.; Lei, J.; Liu, W.; Tong, M.; Liang, J. The degradation pathways of carbamazepine in advanced oxidation process: A mini review coupled with DFT calculation. Sci. Total. Environ. 2021, 779, 146498. [Google Scholar] [CrossRef] [PubMed]
  78. Vos, M.; Hesselman, M.C.; Beek, T.A.T.; van Passel, M.W.; Eyre-Walker, A. Rates of Lateral Gene Transfer in Prokaryotes: High but Why? Trends Microbiol. 2015, 23, 598–605. [Google Scholar] [CrossRef]
  79. Berthold, T.; Centler, F.; Hübschmann, T.; Remer, R.; Thullner, M.; Harms, H.; Wick, L.Y. Mycelia as a focal point for horizontal gene transfer among soil bacteria. Sci. Rep. 2016, 6, 36390. [Google Scholar] [CrossRef]
  80. Maheshwari, M.; Abulreesh, H.H.; Khan, M.S.; Ahmad, I.; Pichtel, J. Horizontal Gene Transfer in Soil and the Rhizosphere: Impact on Ecological Fitness of Bacteria. In Agriculturally Important Microbes for Sustainable Agriculture; Springer: Singapore, 2017; pp. 111–130. [Google Scholar] [CrossRef]
  81. Jung, C.; Crocker, F.; Eberly, J.; Indest, K. Horizontal gene transfer (HGT) as a mechanism of disseminating RDX-degrading activity among Actinomycete bacteria. J. Appl. Microbiol. 2011, 110, 1449–1459. [Google Scholar] [CrossRef] [PubMed]
  82. Heine, T.; Zimmerling, J.; Ballmann, A.; Kleeberg, S.B.; Rückert, C.; Busche, T.; Winkler, A.; Kalinowski, J.; Poetsch, A.; Scholtissek, A.; et al. On the Enigma of Glutathione-Dependent Styrene Degradation in Gordonia rubripertincta CWB2. Appl. Environ. Microbiol. 2018, 84, e00154-18. [Google Scholar] [CrossRef]
  83. Yocca, A.E.; Edger, P.P. Machine learning approaches to identify core and dispensable genes in pangenomes. Plant Genome 2021, 15, e20135. [Google Scholar] [CrossRef]
  84. Gordienko, E.N.; Kazanov, M.D.; Gelfand, M.S. Evolution of Pan-Genomes of Escherichia coli, Shigella spp., and Salmonella enterica. J. Bacteriol. 2013, 195, 2786–2792. [Google Scholar] [CrossRef]
  85. Rouli, L.; Merhej, V.; Fournier, P.-E.; Raoult, D. The bacterial pangenome as a new tool for analysing pathogenic bacteria. New Microbes New Infect. 2015, 7, 72–85. [Google Scholar] [CrossRef] [PubMed]
  86. McCutcheon, J.P.; Moran, N.A. Extreme genome reduction in symbiotic bacteria. Nat. Rev. Microbiol. 2011, 10, 13–26. [Google Scholar] [CrossRef]
  87. Ochman, H.; Caro-Quintero, A. Genome Size and Structure, Bacterial. In Encyclopedia of Evolutionary Biology; Elsevier: Amsterdam, The Netherlands, 2016; pp. 179–185. [Google Scholar] [CrossRef]
  88. Abendroth, U.; Schmidtke, C.; Bonas, U. Small non-coding RNAs in plant-pathogenic Xanthomonas spp. RNA Biol. 2014, 11, 457–463. [Google Scholar] [CrossRef] [PubMed]
  89. Schmidtke, C.; Findeiß, S.; Sharma, C.M.; Kuhfuß, J.; Hoffmann, S.; Vogel, J.; Stadler, P.F.; Bonas, U. Genome-wide transcriptome analysis of the plant pathogen Xanthomonas identifies sRNAs with putative virulence functions. Nucleic Acids Res. 2011, 40, 2020–2031. [Google Scholar] [CrossRef] [PubMed]
  90. Gomes, A.L.C.; Johns, N.I.; Yang, A.; Velez-Cortes, F.; Smillie, C.S.; Smith, M.B.; Alm, E.J.; Wang, H.H. Genome and sequence determinants governing the expression of horizontally acquired DNA in bacteria. ISME J. 2020, 14, 2347–2357. [Google Scholar] [CrossRef] [PubMed]
  91. Koonin, E.V. Horizontal transfer beyond genes. Proc. Natl. Acad. Sci. USA 2014, 111, 15865–15866. [Google Scholar] [CrossRef] [PubMed]
  92. Oren, Y.; Smith, M.B.; Johns, N.I.; Zeevi, M.K.; Biran, D.; Ron, E.Z.; Corander, J.; Wang, H.H.; Alm, E.J.; Pupko, T. Transfer of noncoding DNA drives regulatory rewiring in bacteria. Proc. Natl. Acad. Sci. USA 2014, 111, 16112–16117. [Google Scholar] [CrossRef] [PubMed]
  93. Gatti, D.L.; Palfey, B.A.; Lah, M.S.; Entsch, B.; Massey, V.; Ballou, D.P.; Ludwig, M.L. The Mobile Flavin of 4-OH Benzoate Hydroxylase. Science 1994, 266, 110–114. [Google Scholar] [CrossRef]
  94. Sherlock, M.E.; Breaker, R.R. Biochemical Validation of a Third Guanidine Riboswitch Class in Bacteria. Biochemistry 2017, 56, 359–363. [Google Scholar] [CrossRef]
  95. Sherlock, M.E.; Sadeeshkumar, H.; Breaker, R.R. Variant Bacterial Riboswitches Associated with Nucleotide Hydrolase Genes Sense Nucleoside Diphosphates. Biochemistry 2018, 58, 401–410. [Google Scholar] [CrossRef]
  96. Pahlke, J.; Dostálová, H.; Holátko, J.; Degner, U.; Bott, M.; Pátek, M.; Polen, T. The small 6C RNA of Corynebacterium glutamicum is involved in the SOS response. RNA Biol. 2016, 13, 848–860. [Google Scholar] [CrossRef] [PubMed]
  97. Houghton, J.; Rodgers, A.; Rose, G.; D’halluin, A.; Kipkorir, T.; Barker, D.; Waddell, S.J.; Arnvig, K.B. The Mycobacterium tuberculosis sRNA F6 Modifies Expression of Essential Chaperonins, GroEL2 and GroES. Microbiol. Spectr. 2021, 9, e0109521. [Google Scholar] [CrossRef] [PubMed]
  98. Kummer, C.; Schumann, P.; Stackebrandt, E. Gordonia alkanivorans sp. nov., isolated from tar-contaminated soil. Int. J. Syst. Evol. Microbiol. 1999, 49, 1513–1522. [Google Scholar] [CrossRef] [PubMed]
  99. Qi, Y.-B.; Wang, C.-Y.; Lv, C.-Y.; Lun, Z.-M.; Zheng, C.-G. Removal Capacities of Polycyclic Aromatic Hydrocarbons (PAHs) by a Newly Isolated Strain from Oilfield Produced Water. Int. J. Environ. Res. Public Health 2017, 14, 215. [Google Scholar] [CrossRef] [PubMed]
  100. Xue, Y.; Sun, X.; Zhou, P.; Liu, R.; Liang, F.; Ma, Y. Gordonia paraffinivorans sp. nov., a hydrocarbon-degrading actinomycete isolated from an oil-producing well. Int. J. Syst. Evol. Microbiol. 2003, 53, 1643–1646. [Google Scholar] [CrossRef] [PubMed]
  101. Mullaeva, S.A.; Delegan, Y.A.; Streletskii, R.A.; Sazonova, O.I.; Petrikov, K.V.; Ivanova, A.A.; Dyatlov, I.A.; Shemyakin, I.G.; Bogun, A.G.; Vetrova, A.A. Pseudomonas veronii strain 7–41 degrading medium-chain n-alkanes and polycyclic aromatic hydrocarbons. Sci. Rep. 2022, 12, 1–13. [Google Scholar] [CrossRef] [PubMed]
  102. Jacques, R.J.S.; Okeke, B.C.; Bento, F.M.; Peralba, M.C.R.; Camargo, F.A.O. Characterization of a Polycyclic Aromatic Hydrocarbon–Degrading Microbial Consortium from a Petrochemical Sludge Landfarming Site. Bioremediation J. 2007, 11, 1–11. [Google Scholar] [CrossRef]
  103. Lin, C.-L.; Shen, F.-T.; Tan, C.-C.; Huang, C.-C.; Chen, B.-Y.; Arun, A.; Young, C.-C. Characterization of Gordonia sp. strain CC-NAPH129-6 capable of naphthalene degradation. Microbiol. Res. 2012, 167, 395–404. [Google Scholar] [CrossRef] [PubMed]
  104. Grund, E.; Denecke, B.; Eichenlaub, R. Naphthalene degradation via salicylate and gentisate by Rhodococcus sp. strain B4. Appl. Environ. Microbiol. 1992, 58, 1874–1877. [Google Scholar] [CrossRef]
  105. Tomás-Gallardo, L.; Gómez-Álvarez, H.; Santero, E.; Floriano, B. Combination of degradation pathways for naphthalene utilization in Rhodococcus sp. strain TFB. Microb. Biotechnol. 2013, 7, 100–113. [Google Scholar] [CrossRef]
  106. Costa, D.M.; Gómez, S.V.; de Araújo, S.S.; Pereira, M.S.; Alves, R.B.; Favaro, D.C.; Hengge, A.C.; Nagem, R.A.; Brandão, T.A. Catalytic mechanism for the conversion of salicylate into catechol by the flavin-dependent monooxygenase salicylate hydroxylase. Int. J. Biol. Macromol. 2019, 129, 588–600. [Google Scholar] [CrossRef]
  107. Wang, Z.; Sun, Y.; Shi, Y.; Song, W.; Zhang, C. Cloning, Expression and Characterization of a Mesophilic Catechol 1,2-dioxygenase from Rhodococcus ruber OA1. Biotechnology 2016, 16, 10–18. [Google Scholar] [CrossRef]
  108. Roy, S.; Kästner, J. Catalytic Mechanism of Salicylate Dioxygenase: QM/MM Simulations Reveal the Origin of Unexpected Regioselectivity of the Ring Cleavage. Chem. A Eur. J. 2017, 23, 8949–8962. [Google Scholar] [CrossRef]
  109. Neidle, E.L.; Hartnett, C.; Ornston, L.N.; Bairoch, A.; Rekik, M.; Harayama, S. Nucleotide sequences of the Acinetobacter calcoaceticus benABC genes for benzoate 1,2-dioxygenase reveal evolutionary relationships among multicomponent oxygenases. J. Bacteriol. 1991, 173, 5385–5395. [Google Scholar] [CrossRef]
  110. Broderick, J.B. Catechol dioxygenases. Essays Biochem. 1999, 34, 173–189. [Google Scholar] [CrossRef]
  111. Siegbahn, P.E.M.; Haeffner, F. Mechanism for Catechol Ring-Cleavage by Non-Heme Iron Extradiol Dioxygenases. J. Am. Chem. Soc. 2004, 126, 8919–8932. [Google Scholar] [CrossRef]
  112. Ge, F.; Li, W.; Chen, G.; Liu, Y.; Zhang, G.; Yong, B.; Wang, Q.; Wang, N.; Huang, Z.; Li, W.; et al. Draft Genome Sequence of Gordonia neofelifaecis NRRL B-59395, a Cholesterol-Degrading Actinomycete. J. Bacteriol. 2011, 193, 5045–5046. [Google Scholar] [CrossRef] [PubMed]
  113. Lee, K.; Badaya, S.K.; Singh, R.; Lim, J.Y. Complete Genome Sequence of Gordonia sp. Strain JH63, Isolated from Human Skin. Genome Announc. 2020, 9, 10-1128. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Whole-genome tree demonstrating the position of strain 135 (red) within the species G. polyisoprenivorans and within the genus Gordonia in general.
Figure 1. Whole-genome tree demonstrating the position of strain 135 (red) within the species G. polyisoprenivorans and within the genus Gordonia in general.
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Figure 2. Circos visualization of locally collinear blocks identified between chromosomes of Gordonia polyisoprenivorans 135, C and HW436.
Figure 2. Circos visualization of locally collinear blocks identified between chromosomes of Gordonia polyisoprenivorans 135, C and HW436.
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Figure 3. Distribution of core-genome and accessory genome between G. polyisoprenivorans 135, G. polyisoprenivorans C and G. polyisoprenivorans VH2.
Figure 3. Distribution of core-genome and accessory genome between G. polyisoprenivorans 135, G. polyisoprenivorans C and G. polyisoprenivorans VH2.
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Figure 4. Growth curve of strain 135 on mineral medium with salicylate (blue) and naphthalene (orange).
Figure 4. Growth curve of strain 135 on mineral medium with salicylate (blue) and naphthalene (orange).
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Figure 5. The structure of the region containing genes involved in the catabolism of aromatic compounds in strain 135. Gene products from left to right: IclR family transcriptional regulator, extradiol ring-cleavage dioxygenase WCB38962.1, FAD-dependent oxidoreductase, non-heme iron oxygenase ferredoxin subunit WCB38964.1, aromatic ring-hydroxylating dioxygenase subunit alpha WCB38965.1, dienelactone hydrolase family protein, SDR family oxidoreductase, aromatic-ring-hydroxylating dioxygenase subunit beta WCB38968.1.
Figure 5. The structure of the region containing genes involved in the catabolism of aromatic compounds in strain 135. Gene products from left to right: IclR family transcriptional regulator, extradiol ring-cleavage dioxygenase WCB38962.1, FAD-dependent oxidoreductase, non-heme iron oxygenase ferredoxin subunit WCB38964.1, aromatic ring-hydroxylating dioxygenase subunit alpha WCB38965.1, dienelactone hydrolase family protein, SDR family oxidoreductase, aromatic-ring-hydroxylating dioxygenase subunit beta WCB38968.1.
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Table 1. Comparison of genome assemblies of the type strain of G. polyisoprenivorans maintained in different collections.
Table 1. Comparison of genome assemblies of the type strain of G. polyisoprenivorans maintained in different collections.
NBRC 16320JCM 10675ATCC BAA-14
Genbank acc. NumberBAEI00000000.1BBGD00000000.1JAAXPC000000000.1
Submitted01-DEC-201118-JUN-201406-APR-2020
Sequencing technologyRoche 454Ion PGMIllumina NovaSeq
Coverage16x35x206.9x
GC%66.9065.6066.90
Contigs number113287654
Total length, bp6,285,4784,974,0306,287,369
Table 2. G. polyisoprenivorans strains from the Genbank database with completely assembled genomes. The type strain G. polyisoprenivorans ATCC BAA-14 was used as reference.
Table 2. G. polyisoprenivorans strains from the Genbank database with completely assembled genomes. The type strain G. polyisoprenivorans ATCC BAA-14 was used as reference.
Strain Name135CVH2R9HW436
Genbank acc. NumberCP116236.1CP073075.1CP003119.1, CP003120.1CP072203.1ARVZ01
Total length, Mb5.995.935.846.036.33
Size of plasmid(s), kb--174--
CDS number51685147510052865509
ANI value with type strain, %98.6898.4298.1994.1498.64
DDH value with type strain, %88.3087.9079.4072.6090.40
ANI value with the strain 135, %-98.3998.0193.9498.49
DDH value with the strain 135, %-84.9081.1073.8083.50
Table 3. The genes in the genome of strain 135 involved in the degradation of aromatic compounds. The genes in rows 2–4 are present only in the genome of strain 135, but not in the genomes of strains G. polyisoprenivorans R9, C and VH2.
Table 3. The genes in the genome of strain 135 involved in the degradation of aromatic compounds. The genes in rows 2–4 are present only in the genome of strain 135, but not in the genomes of strains G. polyisoprenivorans R9, C and VH2.
Gene Accession NumberPosition in the GenomeProduct Name
1WCB38965.11730449..1731774aromatic ring-hydroxylating dioxygenase subunit alpha
2WCB38968.11733415..1733933aromatic-ring-hydroxylating dioxygenase subunit beta
3WCB38962.11727528..1728595extradiol ring-cleavage dioxygenase
4WCB38964.11729905..1730231non-heme iron oxygenase ferredoxin subunit
5WCB37763.1226176..227519aromatic ring-hydroxylating dioxygenase subunit alpha
6WCB38820.11559611..1560738aromatic ring-hydroxylating dioxygenase subunit alpha
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Frantsuzova, E.; Bogun, A.; Kopylova, O.; Vetrova, A.; Solyanikova, I.; Streletskii, R.; Delegan, Y. Genomic, Phylogenetic and Physiological Characterization of the PAH-Degrading Strain Gordonia polyisoprenivorans 135. Biology 2024, 13, 339. https://doi.org/10.3390/biology13050339

AMA Style

Frantsuzova E, Bogun A, Kopylova O, Vetrova A, Solyanikova I, Streletskii R, Delegan Y. Genomic, Phylogenetic and Physiological Characterization of the PAH-Degrading Strain Gordonia polyisoprenivorans 135. Biology. 2024; 13(5):339. https://doi.org/10.3390/biology13050339

Chicago/Turabian Style

Frantsuzova, Ekaterina, Alexander Bogun, Olga Kopylova, Anna Vetrova, Inna Solyanikova, Rostislav Streletskii, and Yanina Delegan. 2024. "Genomic, Phylogenetic and Physiological Characterization of the PAH-Degrading Strain Gordonia polyisoprenivorans 135" Biology 13, no. 5: 339. https://doi.org/10.3390/biology13050339

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