Abstract
Over the last two decades, halophilic (organisms that thrive at high salt concentrations) and halotolerant (organisms that have adapted to high salt concentrations) myxobacteria emerged as an important source of structurally diverse secondary metabolites from the marine environment. This review explores the advance of metagenomics analysis and 16S rRNA gene phylogeny of the cultured and uncultured myxobacteria from marine and other salt-environments up to July 2018. The diversity of novel groups of myxobacteria in these environments appears unprecedented, especially in the Sorangiineae and Nannocystineae suborders. The Sandaracinaceae related clade in the Sorangiineae suborder seems more widely distributed compared to the exclusively marine myxobacterial cluster. Some of the previously identified clones from metagenomic studies were found to be related to the Nannocystineae suborder. This understanding provides the foundation for a vital, unexplored resource. Understanding the conditions required to cultivate these yet “uncultured” myxobacteria in the laboratory, while a key next step, offers a significant potential to further expand access to diverse secondary metabolites.
Keywords: marine myxobacteria, metagenomics, uncultured, halophilic organisms, anaerobic, 16S rRNA, Sorangiineae, Nannocystineae, Sandaracinaceae related clades, marine myxobacterial clusters
1. Introduction
The search for marine myxobacteria began over 50 years ago with the first reports appearing in the 1950s [1,2,3]. It took until 1998 that the first truly obligate halophilic and halotolerant groups were reported [4,5,6,7,8,9]. Interest in these species has arisen due to their profound ability to produce secondary metabolites that can serve as leads for drug discovery efforts [10]. Myxobacteria have since been shown to inhabit the marine and estuarine environments often found in sediments or on seagrass and algae [4,5,6,7,8]. Whether they are transient or truly originate from the sea, phylogenetic classifications allow one to determine if a given strain is a halotolerant or halophilic myxobacterium [11]. Strains belonging to the Cystobacterineae-type are predominantly non-halophilic except for halotolerant strains of Myxococcus xanthus, Myxococcus virescens, Myxococcus macrosporus [12], Myxococcus fulvus (strain HW-1) [13], Angiococcus, Corallococcus, and Cystobacter [9]. Isolated myxobacterial strains belonging to the suborder Nannocystineae are unique in that they grow in a wide range of salinity, and hence comprise the obligate halophilic genera Haliangium, Enhygromyxa, and Plesiocystis.
2. Phylogenetic Analysis of Cultured Marine- and Estuarine-Derived Myxobacteria
To date, only five species (Enhygromyxa salina, Haliangium tepidum, H. ochraceum, Plesiocystis pacifica, Pseudenhygromyxa salsuginis), belonging to four new genera of marine and estuarine-derived myxobacteria, have been validly described taxonomically [5,6,7,8]. Each of these five strains belong to the Nannocystineae suborder [14]. Application of the BLAST algorithm to identify similar sequences revealed that several additional strains (e.g., Myxobacterium AT1-02, Genbank AB246767; Myxobacterium AT3-09, Genbank AB246768; Bacterium YC-LK-LKJ6, Genbank KP174648) appear to be related to these taxa. That noted, phylogenetic analysis of cultured strains found by BLAST searching reveals a high diversity in the genus Haliangium, Plesiocystis, and Enhygromyxa, with the latter demonstrating the largest number of isolates (Figure 1, Table 1). Strains AT1-02, AT3-09, and YC-LK-LKJ6 cluster with the Enhygromyxa clade, while other strains such as SHI-1 emerged within the Plesiocystis cluster. Myxobacterium strain SMH-27-4 has been suggested as a novel genus and species, Paraliomyxa miuraensis [15,16]. On the other hand, the halotolerant and genome sequenced strain Myxococcus fulvus HW-1 [13] appears to be closely related to Myxococcus macrosporus based on 16S rRNA gene sequence phylogeny. So far, the culturally described halotolerant myxobacteria were only known in Nannocystineae and Cystobacterineae suborders [7,9,12]. However, obligate halophilic strains were exclusively found in Nannocystineae [5,6,8]. With the ongoing expanse in this field, it is very likely that new isolates will reveal novel species and genera in Nannocystineae.
Table 1.
Bacterial Strains | GenBank Accession Number |
---|---|
Bacterium YC-LK-LKJ6 | KP174648 |
Corallococcus coralloides DSM 2259 T | NR_042329 |
Corallococcus exiguus DSM 14696 T | NR_042330 |
Desulfovibrio desulfuricans MB | NR_036778 |
Enhygromyxa sp. SAB-1 | LC068861 |
Enhygromyxa salina SHK-1 T | NR_024807 |
Enhygromyxa sp. SHK-4 | LC068850 |
Enhygromyxa sp. SHK-11 | LC068851 |
Enhygromyxa sp. SIS-1 | LC068863 |
Enhygromyxa sp. SIW-2 | LC068855 |
Enhygromyxa sp. SIW-3 | LC068856 |
Enhygromyxa sp. SMH-02-3 | LC066680 |
Enhygromyxa salina SMK-1-3 | AB097591 |
Enhygromyxa sp. SMK-2-1 | LC068852 |
Enhygromyxa sp. SMK-5-2 | LC068853 |
Enhygromyxa sp. SMK-9 | LC068854 |
Enhygromyxa sp. SMP-8 | LC068857 |
Enhygromyxa sp. SNB-1 | LC066681 |
Enhygromyxa sp. SNM-1 | LC068862 |
Enhygromyxa sp. SSJ-1 | LC068860 |
Enhygromyxa sp. SYM-1 | LC068858 |
Enhygromyxa sp. SYM-2 | LC068859 |
Enhygromyxa salina DSM 15201 | KP306731 |
Enhygromyxa salina SWB004 | HM769727 |
Enhygromyxa salina SWB005 | HM769728 |
Enhygromyxa salina SWB006 | HM769729 |
Enhygromyxa salina SWB007 | KC818422 |
Haliangium sp. SBP-1 | LC068865 |
Haliangium ochraceum GS1 | EF108312 |
Haliangium ochraceum DSM 14365 T | NR_074917 |
Haliangium ochraceum SMP-2 T | NR_027522 |
Haliangium tepidum SMP-10 T | NR_024781 |
Kofleria sp. DSM 53797 | HF586693 |
Kofleria flava DSM 53745 | HF586692 |
Kofleria flava DSM 53743 | HF586691 |
Kofleria flava DSM 14602 | HF937255 |
Kofleria flava Pl vt1 T | NR_041981 |
Myxobacterium SHI-1 | AB016469 |
Myxobacterium SMH-27-4 (“Paraliomyxa miuraensis”) * | AB252740 |
Myxobacterium AT1-02 | AB246767 |
Myxobacterium AT3-09 | AB246768 |
Myxococcus fulvus HW-1 | CP002830 |
Myxococcus fulvus ATCC 25199 T | NR_043946 |
Myxococcus macrosporus Cc m8 T | AJ233921 |
Myxococcus stipitatus DSM 14675 T | NR_102512 |
Myxococcus virescens DSM 2260 T | NR_043947 |
Myxococcus xanthus ATCC 25232 T | NR_043945 |
Nannocystis exedens DSM 71 T | NR 040928 |
Nannocystis pusilla Na p29 T | NR_117463 |
Nannocystis pusilla B150 | KF739395 |
Plesiocystis pacifica SIR-1 T | NR_024795 |
Plesiocystis sp. SIS-2 | LC068864 |
Pseudenhygromyxa salsuginis SYR-2 T | NR_113269 |
Pyxidicoccus fallax DSM 14698 T | NR_043948 |
* Tentative name proposal based on reference 15 and 16 and T denotes type strain.
3. Diversity of Myxobacteria in the Suborder Sorangiineae as Inferred from Metagenomic Analyses
Previous reports have described the diversity of myxobacteria from the marine environment including the exclusive marine myxobacterial cluster (MMC) [17]. The MMC was detected in 6–60% salinity (sea salt content) indicating their occurrences in brackish (an environment with mixture of fresh and sea water) and marine (referring to the sea or ocean), but not in hypersaline environments. Since this report, more sequences including publicly-deposited JF34-series (GenBank JF344537), KR82-series (GenBank KR825029), and KX0-series (GenBank KX097196) appeared to belong to the MMC cluster. Phylogenetic analysis based on the 16S rRNA gene sequencing revealed that many of these sequences clustered with MMC (Figure 2). Interestingly, many of these clones in the MMC were hypothesized to have an anaerobic lifestyle including AT-s3-66 (GenBank AY225609) and AT-s3-60 (GenBank AY225609) [18]. In addition, clones of the JF34-series clone ANOX-131 (GenBank JF344693) or clone ANOX-089 (GenBank JF344651) [19] were determined to be closely related to MMCf1 and MMCf2 (Figure 2). Since many of these clones were derived from deep sea, methane seeps, and polluted hydrocarbon marine sediments, MMC may potentially comprise an anaerobic group of marine myxobacteria.
Interestingly, Sandaracinaceae related clade (SRC), a neighboring clade to MMC, was shown to be widely distributed in nature (Figure 2). SRC include some of the hydrothermal marine clones PVB_46 (GenBank U15117), described from Pele’s vent in Hawaii, and clones V1F160b (GenBank FJ905758) from the Tonga Arc sub-marine volcano [20]. SRC can also be found in coral, marine cyanobacterial blooms, marine seafloor sediments, sea water, mangrove sediments, hypersaline microbial mats, haloalkaline soil, and salt marsh sediment. They have also been observed in terrestrial soils. Members of the SRC are most likely taxonomically divergent as indicated by the phylogenetic distance between its species as well as their ability to thrive in a wide array of habitats.
Together, the MMC and SRC represent interesting clades in the Sorangiineae suborder. To date, only one strain (Sandaracinus amylolyticus DSM 53668 T) has been cultivated from these clades. The diversity in these environments is perhaps comparable with soil myxobacteria in terms of their potential to represent novel genera and families. While not yet achieved, it is reasonable to expect that screening efforts, similar to those developed for soil myxobacteria, will eventually provide an effective growth medium for laboratory culturing.
4. Diversity of Myxobacteria in the Nannocystineae Suborder
Our understanding of marine myxobacteria arises from studies on strains in the suborder Nannocystineae. However, they only occupy a small percentage of the total diversity, as the majority remains yet to be cultivated under laboratory conditions. Understanding the “uncultured” members of this suborder lies at the forefront of current discovery efforts. Truly halophilic myxobacterial isolates are typically classified as belonging to the genera Haliangium, Plesiocystis, and Enhygromyxa, while the halotolerant isolates belong to the genus Pseudenhygromyxa in Nannocystineae suborder. By exploration of 16S rRNA metagenomics and phylogeny, the Nannocystineae clade is far more environmentally diverse when compared with Sorangiineae. Currently, the diversity of uncultured myxobacteria in this suborder spans from saline-alkaline soil, mangrove soil, hypersaline mats, estuarine sediments to reef, marine and deep sea sediments. Overall, the issue then arises as to how one can gain access to species that have adapted a very specific environmental niche.
As shown in Figure 3, this suborder is divided into major clades I and II. Clade I includes members of the isolated myxobacterial strains in the genera Enhygromyxa, Pseudenhygromyxa, Nannocystis, Haliangium, and Kofleria. It also contains several isolates that have not yet been validated taxonomically. A large portion of the clade I cluster is comprised of yet uncultured species in the Haliangium-Kofleria subclade. This subclade contains the highest level of diversity and arises from deep sea [21,22] and estuarine sediments [23]. Clade II differs from clade I in the fact that not a single isolate has yet been cultured. Clade II species are found throughout a wide variety of different saline ecosystems [19,24,25,26,27,28].
5. Characteristics of Novel Marine Myxobacteria and Parameters to Consider for Their Cultivation
Based on metagenomics data and phylogenetic classification, uncultured marine myxobacteria exhibit some of the following characteristics.
5.1. Structural Features: Rod-Shaped Cells with Blunted Ends
Strains classified within Sorangiineae and Nannocystineae typically exhibit rod-shaped cells with blunted ends (Figure 4a). These suborders are unique for this type of cell shape. Such cells can be differentiated from strains belonging to the Cystobacterineae suborder [29], for which vegetative cells appear as thinner flexuous rods. The uncultured marine Sorangiineae and Nannocystineae cells may have adapted to their aquatic environment to become motile.
5.2. Reproductive Features: Reduction in Forming Fruiting Bodies
Studies to date have shown that fruiting body formation in select halotolerant strains is supported by up to 60% w/v seawater (equivalent to 2% w/v salt in solid medium) [9]. Other studies, however, have shown that fruiting body-bearing spores from halophilic strains including Haliangium tepidum [8,30], Enhygromyxa salina [5,31], and Plesiocystis pacifica [6,31] can still be observed at sea water salinity (~3.5% w/v). Isolation of novel myxobacteria from salt environments should not rely completely on the appearance of fruiting bodies, as this structure may not develop. Further studies have shown that strains belonging to the SRC may not form fruiting bodies as exemplified by Sandaracinus within this clade [32].
5.3. Chemical Predation and Defense: Lack of Microbial Predation and Cellulose Degradation but Agar Degradation
Based on metagenomic analysis of salt-containing environments, uncultured myxobacteria appear to belong to the suborders Sorangiineae (Figure 2) and Nannocystineae (Figure 3). Since these suborders are known for agar degradation, one might expect that these myxobacteria may also share this characteristic (Figure 4b). Microbial lysis is known in myxobacteria, however, this trait may be lost in samples derived from deep sea ecosystems. Since strains have yet to be obtained from deep sea sediments, it is not known whether these myxobacteria can prey on other microorganisms. So far, none of the Nannocystineae isolated to date degrade cellulose, an observation, which is commonly found in terrestrial strains.
5.4. Requirement for Salinity: A Need for Salt and Associate Metal Cations
Marine-derived myxobacteria differ from terrestrial isolates primarily in their salt tolerance (Figure 4c). They seem to have adapted a system to adjust to saline environments using osmolytes such as ectoine, hydroxyectoine, and glycine betaine [33]. In halotolerant Myxococcus strains, salt tolerance was speculated to be acquired by horizontal hdsp gene transfer [34], while Plesiocystis pacifica SIR-I strain makes use of amino acids as osmoprotectant [35]. In addition to modulation of salt levels, isolated marine myxobacteria typically require the addition of cations such as Ca2+, Mg2+, and K+ to support growth.
5.5. Temperature Regulation: Growth Possible in Wider Temperature Range
To date, the isolated marine and estuarine-derived myxobacteria grew at a wider temperature range (5–45 °C) [5,8,31] than terrestrial species. While the aqueous environment of marine species plays a key role in temperature regulation, it is likely that they have highly adapted and evolved to match the temperature of their local environment. For instance, tropical sandy beaches will likely contain marine myxobacteria, which can resist higher temperatures [8] than those collected in frigid seas in the North Atlantic [17].
5.6. Life Cycle: Potentially Slow Growth
Since metagenomic and phylogenetic data revealed that novel myxobacteria in salt-containing environments were positioned in the Sorangiineae and Nannocystineae suborders, it might be expected that they grow much slower when compared with most terrestrial counterparts. In general, cultured members of these suborders may be recognized by their growth after weeks of incubation in the isolation set-ups. One might speculate that these organisms may be microaerophilic, anaerobic, and utilize different carbon sources such as methane, since many of these clones were derived from hydrothermal vents, sub-marine volcanic ash, and deep sea seep sediments.
6. Can Marine Myxobacteria Access Novel Bioactive Secondary Metabolites?
Marine-derived myxobacteria have already demonstrated a strong potential to produce natural products with distinct scaffolds [36,37,38,39,40,41]. Many of these materials display unique structure features as exemplified by the enhygrolides [36], enhygromic acid [37], haliamide [38], haliangicin [39,40], miuraenamide [15,16], salimabromide [41], and the salimyxins [36] (the structures of these materials are provided in the accompaning manuscript [10]). Many of these materials have demonstrated potent biological activity [42]. For instance, enhygrolide A was shown by the König laboratory to inhibit the growth of the Gram-positive bacterium at microgram concentration (MIC, 4 µg mL−1 against Arthrobacter cristallopoietes) [36]. Other studies including those on enhygromic acid (IC50 value of 46 µM, B16 melanoma cells) [37] or haliamide (12 µM, HeLa-S3 cells) [38] have shown activities against the proliferation of tumor cells. Studies on haliangicin have identified antifungal activities with minimal inhibitory concentration (MIC) values comparable to amphotericin and nystatin [40]. While the modes of action of these compounds still remain unexplored, morphology screening efforts identified actin filament stabilizing activity associated with miuraenamide A [43]. While early on, the evidence collected to date indicates that unique bioactive scaffolds can be obtained from marine- and estuarine-derived myxobacteria.
A large percentage of marine myxobacterial strains remain uncultured to-date, as access to these strains remains challenging under laboratory conditions. Furthermore, the potential to produce novel compounds by marine myxobacteria is also reflected in the diversity of the biosynthetic gene clusters encoded in the few available genome sequences [44,45]. Previous studies have shown novel Type I polyketide synthase genes that can be found in marine myxobacteria [46], which indicates the potential of these organisms to produced novel compounds. A further description of the unique complexity of these synthases and their associated natural products has recently been reviewed [10].
7. Conclusions
Myxobacteria appear to be ubiquitous and diverse in nature, and are not just terrestrial but found in marine, estuarine, and a variety of other saline ecosystems. Metagenomic analyses indicate that the marine myxobacteria identified to date occupy only a small portion of the potential Nannocystineae phylogenetic tree. This suggests that a vast diversity of species are unexplored. The development of new methods and tools to culture these species would unveil a yet untapped and robust potential. This, combined with the well-established ability of myxobacteria to produce unique and bioactive molecules, identifies the suborder Nannocystineae as an important resource for future therapeutic evaluation. The suborder Sorangiineae also holds great promise for natural product discoveries. Currently, not a single species of the exclusively MMC have been isolated and cultured. In addition, the SRC appears interesting since it is not well explored and also seems distributed through a vast array of marine environments. Based on metagenomic and phylogenetic analysis, those clones derived from marine deep-sea sediments may return extremophilic myxobacteria with access to halophilic, anaerobic, microaerophilic, piezophilic, or psychrophilic properties. Finding the requirements for salinity, salts, temperature, and dissolved gasses is obviously necessary. Simulating the conditions of an organism’s natural environment is likely key to the successful cultivation of marine myxobacteria. This observation suggests that we explore the development of laboratory culturing systems that operate at sea. Here, one can envision the development of robotic devices that mimic the natural conditions in marine ecosystems such as that in a sponge [47]. Recent discoveries clearly indicate that marine myxobacteria are under explored group of organisms that offer tremendous potential for secondary metabolite and molecular mining, either through the advance of modern devices or classical approaches.
Acknowledgments
We thank the German Center for Infection Research (Deutsches Zentrum für Infektionsforschung, DZIF) for continuous support on anti-infective research (to R.M.) and the Xenobe Research Institute (to J.J.L.C.)
Author Contributions
R.G. searched for the 16S rRNA gene sequences by BLAST and constructed the phylogenetic trees. R.G., J.J.L.C., and R.M. analyzed data, wrote the manuscript and edited it.
Conflicts of Interest
The authors declare no conflict of interest.
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