Next Article in Journal
Antimicrobial and Cytotoxic Assessment of Marine Cyanobacteria - Synechocystis and Synechococcus
Next Article in Special Issue
Actinomycetes from Sediments in the Trondheim Fjord, Norway: Diversity and Biological Activity
Previous Article in Journal
Evaluation of Harmful Algal Bloom Outreach Activities
Previous Article in Special Issue
Cytotoxicity of the Ascidian Cystodytes dellechiajei Against Tumor Cells and Study of the Involvement of Associated Microbiota in the Production of Cytotoxic Compounds
Article Menu

Export Article

Marine Drugs 2007, 5(4), 220-241; doi:10.3390/md504220

Bioactive Compound Synthetic Capacity and Ecological Significance of Marine Bacterial Genus Pseudoalteromonas
John P. Bowman *
Tasmania Institute of Agricultural Research, School of Agricultural Science, University of Tasmania, Sandy Bay, Private Bag 54, Hobart, Tasmania, 7001, Australia
Received: 27 November 2007 / Accepted: 14 December 2007 / Published: 18 December 2007


The genus Pseudoalteromonas is a marine group of bacteria belonging to the class Gammaproteobacteria that has come to attention in the natural product and microbial ecology science fields in the last decade. Pigmented species of the genus have been shown to produce an array of low and high molecular weight compounds with antimicrobial, anti-fouling, algicidal and various pharmaceutically-relevant activities. Compounds formed include toxic proteins, polyanionic exopolymers, substituted phenolic and pyrolle-containing alkaloids, cyclic peptides and a range of bromine-substituted compounds. Ecologically, Pseudoalteromonas appears significant and to date has been shown to influence biofilm formation in various marine econiches; involved in predator-like interactions within the microbial loop; influence settlement, germination and metamorphosis of various invertebrate and algal species; and may also be adopted by marine flora and fauna as defensive agents. Studies have been so far limited to a relatively small subset of strains compared to the known diversity of the genus suggesting that many more discoveries of novel natural products as well as ecological connections these may have in the marine ecosystem remain to be made.
Pseudoalteromonas; antibiotics; biofilms; anti-fouling; marine bacteria

1. Introduction

The genus Pseudoalteromonas was described by Gauthier et al. [35] and represents a clade of marine bacteria defined on the basis of 16S rRNA gene sequence data. Originally many of the Pseudoalteromonas species that are discussed in this review were members of the genus Alteromonas [5, 77] but Alteromonas was taxonomically re-organized based on phylogenetic analysis. Since 1995, 22 additional Pseudoalteromonas species have been described (details available at More recently two Pseudoalteromonas species have been moved into the genus Algicola [50, 74]. The taxonomy and general features of Pseudoalteromonas (ca. 2000/2001) are covered in the 2nd edition of Bergey’s Manual of Systematic Bacteriology [8].
Possessing Gram-negative cell walls, all members of genus Pseudoalteromonas require Na+ ions, form rod-shaped cells, are motile via sheathed polar and/or unsheathed lateral flagella and possess a strictly aerobic, chemoheterotrophic metabolism. This general set of features has coined the common term “alteromonad” that could be potentially used to now describe other marine genera within class Gammaproteobacteria. Genus Pseudoalteromonas groups within a larger clade of marine taxa, located under the umbrella of order Alteromonadales that inhabit all known non-geothermal marine biomes.
One interesting feature of Pseudoalteromonas is that the genus can be divided relatively cleanly into pigmented and non-pigmented species clades (Fig. 1) and that pigmentation correlates with their proclivity for natural product formation [22]. The non-pigmented species form a relatively distinct clade typified by phylogenetic shallowness between most member species. Pigmented species show greater sequence divergence and are concentrated within the other 2 major clades making up the genus (Fig. 1). With more than 2000 Pseudoalteromonas 16S rRNA gene sequences available on nucleotide sequence databases (e.g. the described diversity of the genus still remains largely incomplete.
Studies by Holmström et al. [43] found deeply pigmented strains within a marine bacterial isolate collection were effective in the inhibition of the settlement of various fouling invertebrates and algae. Based on subsequent analyses some of these isolates lead to the general conclusion that pigmented Pseudoalteromonas species possess a broad range of bioactivity associated with the secretion of extracellular compounds, several of which include pigment compounds [44]. This realization provided greater credence to earlier studies of alteromonads that this group of marine bacteria represents a rich source of biologically active substances. Non-pigmented species of Pseudoalteromonas do not appear to share the same extensiveness of bioactive compound synthesis and this may reflect their econiche distribution, which is admittedly still poorly defined. Within the limits of existing knowledge non-pigmented clade species tend to possess unusual and diverse enzymatic activities (carrageenases, chitinases, alginases, cold-active enzymes), generally broader environmental tolerance ranges (temperature, water activity and pH) and substantially greater nutritional versatility compared to the pigmented species [8]. The pigmented species also tend to have more exacting growth requirements (some require amino acids) and have peroxidase activity rather than catalase activity.

2. Ecological Significance

Marine biofilms influence the settlement of a variety of marine invertebrates and algae and may promote cellular metamorphosis. As biofilms can be quite variable in distribution and in species and chemical composition the influence they can have is complex. The activity of marine flora and fauna have been shown to be clearly positively or negatively influenced by experimental monospecific biofilms [17, 82, 98]. This activity is believed to be due mainly to the production of antibiotic compounds as well as stimulatory chemical cues that are so far mostly uncharacterized.
Several known Pseudoalteromonas species and likely many other described and undescribed bacterial species can influence the reproductive success of various marine fauna and flora due to the production of natural anti-fouling substances [17] (Table 1). A survey by Holmström et al. [42] found that the effectiveness of different Pseudoalteromonas species to prevent settlement of fouling invertebrate larvae and algal spores varies considerably (Figure 2).
It was generally observed that algal dwelling species were particularly effective in preventing biofouling suggesting the ability is important for their survival in the marine ecosystem and likely required for effective colonization of various surfaces, especially the surfaces of macroalgal species. P. luteoviolacea [34], P. aurantia [33]; P. citrea [31, 79], P. tunicata, and P. ulvae [2022, 45] are of particular interest as the host of compounds these species form are essentially produced to prevent biofilm residents becoming overwhelmed by other colonizing, potentially fouling species [26, 38]. Species resistant to natural antibiotics have an advantage in colonization [83] though presumably due to the array of compounds that may be formed no one species is likely to have such an edge that they always become numerically dominant in a given econiche. The result could be that antibiotic-producing strains and development of synergisms within biofilm communities may actually encourage the formation of multi-species biofilms. This protects the biofilm community from being overgrown by a single species as well as reducing invasion by other species [12]. The complex community formed has the advantage in that there is an inherent increase in the efficiency of nutrient acquisition, enhanced tolerance to toxic compounds and physicochemical stresses, and presumably excellent opportunities for genetic exchange [78]. Ironically, Pseudoalteromonas species are highly effective biofilm formers and thus may potentially cause biofouling issues [87], however it is still unknown whether their presence controls the type and accumulation level of biofouling species beyond specific habitats such as the surface of marine algal species. Quorum-sensing mechanisms may play an important role in the influencing settlement and subsequent biofilm formation [19, 46] though it is unknown to what extent quorum sensing molecules influence antibiotic production.
Pseudoalteromonas species have been found to inhibit the settlement, germination, growth or even directly lyse the cells of various algal species. Thus the interactions Pseudoalteromonas strains are involved is intricate dictated by the type of ecosystem involved (planktonic, benthic, surficial etc.), physiological state populations of the species involved, and prevailing environmental chemical parameters. At this point in time specific aspects of these ecological networks remain largely unexplored. To make the ecological connections even more manifestly complex strains of Pseudoalteromonas have also been shown to have promotive affects on various marine eukaryotes in regards to their potential reproductive success.
An example of an inhibitory-oriented interaction involves unidentified strains of Pseudoalteromonas [18, 62] that were found to inhibit the growth but not kill various diatom species due to production of antibiotic compounds. One of these compounds was identified as 2-heptyl-4-quinolinol (Fig 6I) [62] that have been found to possess antibacterial activity [101]. Another strain, Pseudoalteromonas sp. 4 produced unknown substances that impeded the motility and surface attachment of a Navicula sp. and Amphora coffeaeformis. These diatoms eventually underwent lysis. This ability could be blocked by enhancing lectin formation by the diatoms leading to stronger biofilm attachment [99]. A further different example involves strain Y, closely related to Pseudoalteromonas piscicida, which produces unidentified brominated antibiotic compounds as well as an unknown low molecular weight compound that can completely lyse algal cells within a matter of hours [64, 92, 93]. This more “aggressive” activity was found to be pronounced on bloom-forming toxin-producing dinoflagellates of the genera Gymnodinium, Chatonella and Heterosigma species, however only ecdysis was observed for Alexandrium species while diatom and other algal species tested were effectively immune. The progress of this lytic effect on Gymnodinium catenatum is shown in Figure 3. It was also observed that cells were attracted in a swarm to lysed cells providing the concept that the compound production is used as a means to generate nutrients in a predatory-like manner. Subsequently it was determined that production of the unknown algicidal factor was triggered by an autoinducer quorum sensing system, possibly an AI-2-type peptide [93] and that it is likely that algicidal activity is maximal during the peak of algal blooms and may thus contribute to bloom dissolution.
Pseudoalteromonas clearly also positively interacts with higher eukaryotes inducing invertebrate larval settlement and subsequent metamorphosis. P. espejiana was observed to induce the settlement and metamorphosis of the hydrozoan Hydractinia echinata [59] possibly due to induction of caspases [88], suggesting Pseudoalteromonas strains may have apoptosis-inducing effects in some marine eukaryotes. Pseudoalteromonas sp. A3, interestingly closely related to P. piscicida, isolated from the crustose coralline algae Hydrolithon onkodes clearly encouraged coral larvae settlement and subsequently induced metamorphosis in the planula of the coral Acropora [75]. The presumed chemical cue for this induction has not yet been discovered, however methanolic extracts of A3 cultures provided induction that was highly variable. A further example includes an extensive survey of marine bacterial isolates from coralline algae and larvae, from which 12 of 17 Pseudoalteromonas strains were found to be effective in inducing the larval settlement of the sea urchin Heliocidaris erythrogramma. It was also observed that the larvae metamorphosed in higher numbers on biofilms consisting of P. luteoviolacea [48] a species known to produce several antibiotic and bioactive compounds. Huang et al. [47] demonstrated that biofilms strongly promoted the settlement of Hydroides elegans larvae suggesting that when in the biofilm state chemical cues are actively formed. It is important to note that biofilm communities are dynamic complex entities. The direct detection of antibiotic compounds formed from artificial laboratory biofilms has been challenging [40] possibly due to lack of replicability of natural biofilms as well as due to the variable abundance of antibiotic-producing taxa.
These examples suggest that chemical substance production may help various Pseudoalteromonas species compete in quite different situations. The advantages derived could include increased access to space for growth or for nutrient access and potentially can occur in marine biofilms or planktonically. It is not clear how significant or prevalent these interactions are for planktonic and benthic sediment associated cells or for cells ensconced in sinking marine aggregates. Mechanistically the processes involved are also poorly understood and how these activities contribute to larger networks of ecological interactions. Thus the questions that involve Pseudoalteromonas are manifold. Keeping with the theme of antibiotics, a popular subject in microbiology, the significance of cell-to-cell proximity, dilution rate and inherent antibiotic resistance within natural settings in regards to natural antibiotics are still open questions. In marine biology a greater interest may exist on what are the different “broadcasted” chemical cues produced by bacteria, including Pseudoalteromonas that may affect the development or growth of eukaryotes as well as other prokaryotes. Assuming chemical cues can be identified we still need know what they do exactly, why and how. The contribution of many different factors suggests that understanding the ecological ramifications and impact of natural bioactive compounds can only be approached at first by specific, controlled experiments focusing on “model” species, a necessary simplification that allows important specific ecologically to better conceived and tested. One such model species that has appeared within the last few years is P. tunicata, a species that possesses an unusually extensive capacity for inhibiting other types of microorganisms and larger eukaryotes and is the focus of the Prof. Staffan Kjelleberg research team at the University of New South Wales, Sydney, Australia.

3 . P. tunicata as a model to study the mechanisms and ecology of natural antibiotic production, anti-fouling activity and biofilm formation

P. tunicata possesses the highest and broadest range of anti-fouling activities observed to date and was first isolated from a tunicate off the coast of Sweden [45] and subsequently found to dwell on a number of marine species, especially macroalgae [20, 44]. Transposon mutagenesis analysis demonstrated the pigment production by the species is linked to this activity [22, 23] and includes both purple and yellow pigments that give P. tunicata a distinctly dark green-color. The purple pigments were found to prevent the settlement of invertebrate larvae (Balanus amphrtite, Hydroides elegans) and algal spores (Ulva lactuca, Polysiphonia sp.) (Figure 2) but remains unidentified. The species P. ulvae, isolated from the surface of the seaweed Ulva lactuca, was found to also inhibit the settlement of invertebrate larvae (Balanus amphritite) and inhibit algal spore germination and settlement [20, 21]. The purple pigment formed by P. ulvae may be chemically similar to the compound(s) found in P. tunicata and other Pseudoalteromonas species [22].
The anti-fouling ability of P. tunicata is linked to its ability to produce a range of inhibitory substances (more details below) including a toxic antibiotic protein (AlpP) [52]; a heat labile anti-algal substance [21]; violet-colored polar compound(s) of <500 Da [43]; an antifungal yellow pigment compound [25] as well as small molecules active against protists and diatoms (unpublished data). WmpR, similar to the Vibrio cholerae cholera toxin regulator ToxR, was found to act as a response regulator activating several genes in P. tunicata including pigment and antifouling compound production, biofilm formation, type IV pili, some ubiquinone and amino acid synthetic genes, a putative Fe3+ complex TonB-type transporter and also a non-ribosomal peptide synthetase that possibly is involved in Fe3+ siderophore synthesis. The wild type strain survives iron starvation better than a ΔWmpR mutant suggesting that the tendency of P. tunicata to colonize surfaces and produce antifoulants is controlled by nutrient related responses, perhaps acquisition of trace iron [23, 96]. P. tunicata appeared to be most effective in colonization when it had access to an exogenous carbon source associated with the colonization surface e.g. cellobiose derived from degradation of the cellulose surface polymer of the macroalgal species [83]. This may suggest the types and levels of nutrient available for growth may also drive colonization.
Population estimates of antifouling species P. tunicata and P. ulvae, able to form toxic protein AlpP, has been made by using real-time PCR targeting Pseudoalteromonas-specific and P.tunicata/P.ulvae-specific 16S rRNA genes as well as detection of the gene coding AlpP [94]. It was found that from various samples collected off the Danish coast that Pseudoalteromonas are abundant, especially in seawater (Figure 4). P. tunicata and P. ulvae, however prefer colonization of various cellulose-producing algal species as suggested by the specific abundance of anti-fouling Pseudoalteromonas spp, positive detection of the alpP gene (Fig. 4) and PCR-DGGE fingerprinting. Almost all of the antifouling species found were related to P. tunicata and P. ulvae but these only made up about 1% of the total Pseudoalteromonas abundance. This may suggest that other species await isolation that could also have anti-fouling roles on the hosts sampled or the specific populations change over time as the biofilm matures. Based on the compiled data shown in Figure 2 [42] the variation in settlement inhibition assays is highly species-specific (and possibly strain-specific) and that marine macrophyta and marine fauna may play host to their own specific anti-fouling microorganisms.

4. Natural product compound production by Pseudoalteromonas spp

Antibiotic substances linked to the genus Pseudoalteromonas go back to the very early days of marine natural product discovery. Over the years several Pseudoalteromonas strains that have been investigated in this regard have been misidentified or misclassified as Pseudomonas, Chromobacterium, Alteromonas etc. With the current rate of bacterial genus and species descriptions from marine samples, it is difficult if not impossible to be certain of genus identities (let alone species) from the limited taxonomic analyses applied in the times prior to routine sequence based bacterial identification. The information below is based on strains that on the basis of existing data can be attributed at a high level of confidence to the genus Pseudoalteromonas.

4.1. Low molecular weight substances

Early discoveries of marine-derived antibiotics included the identification of brominated pyrroles from purple-pigmented alteromonads. 2,3,4-tribromo-5(1’-hydroxy-2’,4’-dibromophenyl)pyrrole was identified from a strain isolated from a Thalassia sp. [65]. Several low weight antibacterial substances were obtained from P. luteoviolacea misclassified initially as Chromobacterium marinum [32]. These included 2,3,4,5-tetrabromopyrrole (Figure 5A), 2,2’,3,3’,4,4’-hexabromobipyrrole (Figure 5B), 2,3,4-tribromo-5(2’-hydroxy-3’,5’-dibromophenyl)pyrrole (also called pentabromopseudilin) (Figure 5C), 2,4-dibromo-6-chlorophenol (Figure 5D), 4-hydroxybenzaldehyde, and n-propyl-4-hydroxybenzoate [2, 11, 24, 32, 34, 37, 85, 86]. One or more of these substances also seem to also have activity against protists [55]. The seawater species P. phenolica was also found to form a brominated biphenyl compound, 3,3’,5,5’-tetrabromo-2,2’-diphenyldiol (Figure 5E) that was inhibitory to methicillin resistant Staphylococcus aureus strains [49].
The yellow pigment of P. tunicata has anti-fungal activity [22] and was identified as a tambjamine-like alkaloid, designated YP1 [25] (Figure 6A). Tambjamines are 4-methoxypyrrole-containing bioactive compounds previously isolated from marine invertebrates and possess antimicrobial, anti-tumorigenic, immunosuppressive, anti-proliferation and ichthyodeterrent activities [61] and are likely produced as natural defensive compounds against predators. Most evidence points to bacteria, colonizing the surface of higher organisms, as the source of these compounds [58]. Indeed, the biosynthetic pathway for YP1 was elucidated in P. tunicata by Burke et al. [10] and is coded by a cluster of 19 genes (tamA to tamS) that code proteins with homology to prodigiosin biosynthetic genes in various other bacteria [100], including the formation of a bipyrrole precursor, 4-methoxybipyrrole-5-carbaldehyde (MPC) from proline, malonyl-CoA and serine. YP1 is formed by condensation of MPC with dodec-3-en-1-amine [10]. A related compound to YP1 acts as an ionophore [97]. The bright red pigments of P. denitrificans and P. rubra identified as cycloprodigiosin HCl (Figure 6F) [36, 56] also acts as an ionophore blocking proton/chloride ion symporters but have been shown to generally uncouple proton translocation [67]. It has significant potential pharmaceutical impact able to suppress immunoproliferation [68], has anti-malarial activity [57] and is able to induce apoptosis in several cancer cell lines [13, 80]. In synergy with other drugs cycloprodigiosin may have an anti-tumorigenic application.
Substituted phenylalkenoic acids referred to as rubrenoic acids (Figure 6E) have also been purified from P. rubra and shown to have bronchodilatatoric activity [41]. The species P. tetraodonis (as well as a number of other bacterial species), isolated from the skin slime of the puffer fish Fugu poecilonorus, was shown to form the notorious tetrodotoxin (Figure 6J) [27, 91], which is an exceptionally potent blocker of voltage-gated, Na+ ion membrane channels. Production of tetrodotoxin by P. tetraodonis was dramatically stimulated under phosphate-limiting growth conditions [28]. Korormycin (Figure 6G), produced by an unidentified Pseudoalteromonas sp., is a heptylated hydroxyquinonolone that has antibiotic activity against various marine bacteria, especially Vibrio spp. It was found to strongly inhibit the respiratory chain-linked Na+-ion translocating NADH-quinone reductase of Vibrio alginolyticus [103].
Butanol extracts of the algal associated species P. issachenkonii cultures were found to inhibit Candida albicans and cause hemolysis. Analysis of ethyl acetate extracts revealed that isatin (indole-2,3-dione) (Figure 6D) was responsible for the anti-fungal activity. A red-brown haemolytic pigment of 269 Da and corresponding to C9H7N3OS3 was also discovered and still awaits complete structural analysis [54]. A possibly misidentified Pseudoalteromonas species designated Alteromonas sp. P7, isolated from the larva of Penaeus monodon was found to be vibriostatic with the antibacterial substance recovered in ethyl acetate but not the culture supernatant suggesting the compound may also be a substituted aromatic compound [1]. A potentially misclassified pigmented Pseudoalteromonas-like species called “Alteromonas rava” was found to form a substituted 6-amino-4H-[1,2]dithiolo[4,3-b]pyrrol-5-one called thiomarinol A (Figure 6H). Various thiomarinol derivatives have been also synthesized that exhibit potent antibacterial activity [89, 90].
The yellow-pigmented species P. piscicida has been described as being able to produce a neuromuscular toxin able to kill a variety of fish and crab species [7, 39, 72], however no recent studies have re-examined or confirmed this property and the toxin compound has never been detected. This may suggest P. piscicida is rarely an opportunistic pathogen. Strains were also described as being able to inhibit the growth of yeast [9]. P. maricaloris, a close relative of P. piscicida isolated from the Coral Sea sponge Fascaplysinopsis reticulata, forms yellow colored dibromo- and bromo-alterochomides (Figure 5F) that possess antimicrobial activity and as well as cytotoxicity against the larvae of a sea urchin [95]. The algicidal strain Y, also closely related to P. piscicida, forms broad spectrum antimicrobial yellow brominated substances that LC-MS analysis revealed to comprise 12 different but likely structurally similar compounds. The molecular weights of the most abundant components ranged from 830–954 [92]. NMR spectral analysis revealed the presence of bromine, aromatic rings, hydroxyl and carbonyl groups. These still so far unidentified substances may also represent other cyclic or acyclic depsipeptide brominated compounds and may be relevant to the observation of other low molecular weight peptide like substances potentially contributing to anti-fouling activity [104]. A variety of diketopiperazines (DKP) are produced by an Antarctic Pseudoalteromonas haloplanktis isolate [73] including a novel compound, cyclo-(D-pipecolinyl-L-isoleucine) (Figure 6C). This novel DKP was inactive in a free radical scavenging assay using 1,1-diphenyl-2-picrylhydrazyl. Another novel DKP, cyclo-(L-phenylalanyl-4R-hydroxyl-L-proline) (Figure 6B) is produced by P. luteoviolacea [53] that exhibited antibacterial activity. The continued examination of peptide like pigment and non-pigment substances from Pseudoalteromonas appears to be necessary as these compounds seem to have a potentially important impact in biological interactions.

4.2 High molecular weight substances

Several Pseudoalteromonas species have been found to secrete proteins and other soluble high molecular weight substances with antibacterial activities that are also autotoxic in nature [3]. This included a 100 kDA protein produced by P. luteoviolacea [34], which was likely also observed in the study of Kamei et al. [55]. The synthesis of this protein appeared to be induced during late exponential to stationary growth [71]. P. rubra was found to form a strongly anthrone-reactive polyanionic substance, possibly a glycoprotein or polysaccharide, which had antibacterial activity, especially to species that did not naturally possess catalase activity. Subsequently it was found that growth inhibition by the antibiotic was due to induction of oxidative stress in target cells through increased O2 uptake and accumulation of hydrogen peroxide [29, 30]. An alteromonad, designated NCIMB 2144, was found to produce an autotoxic, antibacterial 90 kDA thermolabile glycoprotein [4] that could be analogous to that found in P. rubra. P. tunicata strain D2 secretes an autotoxic 190 kDa dimeric protein referred to as AlpP. This protein was found to inhibit a wide range of marine and medically significant bacteria [52] but is particularly potent against strain D2 itself (MIC 4 μg mL−1). However, as cells progress into the stationary growth phase they become increasingly resistant. The autoxicity of AlpP appears to provide a dispersal mechanism to biofilm dwelling P. tunicata, working through a process akin to programmed cell death [6]. The AlpP-autolysis of cells within biofilm substructures seems to provide nutrients for a subpopulation of cells resistant to AlpP with the lysis causing sections of the biofilm to also detach. Survivor cells are actively motile and presumably are dispersed in the water flow and thus can recolonize new surfaces [69, 70]. Observations in other bacteria suggest dispersal mechanisms analogous to this could be relatively common amongst biofilm forming species [6]. An isolate related to P. piscicida, designated X153 has been proposed as an effective probiont, protecting commercial shellfish species from pathogenic Vibrio species. X153 was shown to produce a, unstable tetrameric 280 kDa vibriostatic protein that also appeared to have broad spectrum inhibitory activity against marine bacteria [63]. P. haloplanktis and P. undina strains have also been found to provide probiotic benefits [66, 84] though it is unknown if antibiotic factors are involved.
Some species of Pseudoalteromonas have been rarely implicated as opportunistic pathogens of marine animals including fish and crustacea [14, 76, 81]. This pathogenicity may relate to lipopolysaccharide and other heat labile factors [15] and other virulence determinants such as hemolysins [54] and thrombolysins [16]. The structure of O-specific polysaccharides has been determined for a number of Pseudoalteromonas species, which are notable in being acidic and containing a variety of substituted sugar and non-sugar subunits [60]. It is unknown if these substances have antibiotic or cytotoxic properties in the marine environment.

5. Concluding Remarks

Pseudoalteromonas though it appears to be only one of many marine bacterial genera (either cultured or uncultured) clearly has been shown to possess ecologically- and pharmaceutically-relevant features that are both unusual and intriguing. Greater understanding of the activities of this genus in the marine ecosystem would represent a boon to microbial and marine ecology. More knowledge of the biologically active chemicals formed by Pseudoalteromonas species would also be potentially pharmacologically beneficial. Such research could be performed from a marine biology point of view in order determine the relationships of Pseudoalteromonas to the reproductive success of many invertebrates and algal species. Detection and identification of new chemical cues could be valuable in understanding the interactive ecology of marine fauna and their associated microbiota. It could also be expanded to conservation-oriented dimensions. Negri and colleagues [75] proposed there is a possibility that broadcast chemical producing bacteria like Pseudoalteromonas sp. A3 could be used as a means to re-seed reefs with coral species owing to its positive effects on coral larvae settlement and metamorphosis. It is unknown if any of these undiscovered compounds would have pharmaceutical benefit too or would have other applications. In that respect several broad spectrum antibiotic compounds have been detected from Pseudoalteromonas spp. including pentabromopseudilin, korormycin, thiomarinol A, bromo-alterochromides A and B, tambjamine YP1 etc. Various strains also form compounds with intriguing pharmaceutical properties such as the red pigment cycloprodigiosine HCl. Since these substances have been derived from only a small subset of strains the potential pool of natural product diversity possessed by genus Pseudoalteromonas is likely mostly unrealized.
Proteases from various strains of Pseudoalteromonas, in particular from a strain of P. issachenkonii were recently found to be effective in reducing biofouling by the bryozoan Bugula neritina [19]. The innovative practical application of small and large antibiotic compounds as well as proteinaceous enzymatic substances to combat marine biofouling is progressing through the use of paints and gel-encapsulation [19, 102]. Thus the extensive enzymatic ability of various Pseudoalteromonas (as suggested for some species in Table 1) is also worth noting as this generally unexplored facet can be potentially useful in a practical sense to combat biofouling as well as an ecologically relevant feature.
  • Sample Availability: Available from the author.

References and Notes

  1. Abraham, TJ. Antibacterial marine bacterium deters luminous vibriosis in shrimp larvae. NAGA WorldFish Cent Quart 2004, 27, 28–31. [Google Scholar]
  2. Anderson, RJ; Wolfe, MS; Faulkner, DJ. Autotoxic antibiotic production by a marine Chromobacterium. Mar Biol 1974, 27, 281–285. [Google Scholar]
  3. Ballester, M; Ballester, JM; Belaich, JP. Isolation and characterization of a high molecular weight antibiotic produced by a marine bacterium. Microb Ecol 1977, 3, 289–303. [Google Scholar]
  4. Barja, JL; Lemos, ML; Toranzo, AE. Purification and characterization of an antibacterial substance produced by a marine Alteromonas species. Antimicrob Agents Chemother 1989, 33, 1674–1679. [Google Scholar]
  5. Baumann, L; Baumann, P; Mandel, M; Allen, RD. Taxonomy of aerobic marine eubacteria. J Bacteriol 1972, 110, 402–429. [Google Scholar]
  6. Bayles, KW. The biological role of death and lysis in biofilm development. Nature Rev Microbiol 2007, 5, 721–726. [Google Scholar]
  7. Bein, SJ. A study of certain chromogenic bacteria isolated from “Red Tide” water with a description of a new species. Bull Mar Sci Gulf Caribb 1954, 4, 110–119. [Google Scholar]
  8. Bowman, JP; McMeekin, TA. Brenner, DJ, Krieg, NR, Staley, JT, Garrity, GM, Eds.; Bergey’s Manual of Bacteriology, 2Springer: New York, 2005; Volume 2, pp. 467–478. [Google Scholar]
  9. Buck, JD; Meyers, SP. In vitro inhibition of Rhodotorula minuta by a variant of marine bacterium Pseudomonas piscicida. Helgol Wiss Meeresunters 1966, 13, 171. [Google Scholar]
  10. Burke, C; Thomas, T; Egan, S; Kjelleberg, S. The use of functional genomics for the identification of a gene cluster encoding for the biosynthesis of an antifungal tambjamine in the marine bacterium Pseudoalteromonas tunicata. Env Microbiol 2007, 9, 814–818. [Google Scholar]
  11. Burkholder, PR; Pfister, RM; Leitz, LH. Production of a pyrrole antibiotic by a marine bacterium. Appl Microbiol 1966, 14, 649–653. [Google Scholar]
  12. Burmølle, M; Webb, JS; Rao, D; Hansen, LH; Sorensen, SJ; Kjelleberg, S. Enhanced biofilm formation and increased resistance to antimicrobial agents and bacterial invasion are caused by synergistic interactions in multispecies biofilms. Appl Env Microbiol 2006, 72, 3916–3923. [Google Scholar]
  13. Campàs, C; Dalmau, M; Montaner, B; Barragán, M; Bellosillo, B; Colomer, D; Pons, G; Pérez-Tomás, R; Gil, J. Prodigiosin induces apoptosis of B and T cells from B-cell chronic lymphocytic leukemia. Leukemia 2003, 17, 746–750. [Google Scholar]
  14. Colwell, RR; Sparks, AK. Properties of Pseudomonas enalia, a marine bacterium pathogenic for the invertebrate Crassostrea gigas (Thunberg). Appl Microbiol 1967, 15, 980–986. [Google Scholar]
  15. Costa-Ramos, C; Rowley, AF. Effect of extracellular products of Pseudoalteromonas atlantica on the edible crab Cancer pagurus. Appl Env Microbiol 2004, 70, 729–735. [Google Scholar]
  16. Demina, NS; Veslopolova, EF; Gaenko, GP. Marine-bacteria Alteromonas piscicida produces thrombolytic enzymes. Izv Akad Nauk SSSR Ser Biologich 1990, 3, 415–419. [Google Scholar]
  17. Dobretsov, S; Dahms, H-W; Qian, P-Y. Inhibition of biofouling by marine microorganisms and their metabolites. Biofouling 2006, 22, 43–54. [Google Scholar]
  18. Dobretsov, S; Qian, PY. Effect of bacteria associated with the green alga Ulva reticulata on marine micro- and macrofouling. Biofouling 2002, 18, 217–228. [Google Scholar]
  19. Dobretsov, S; Xiong, HR; Xu, Y; Levin, LA; Qian, PY. Novel antifoulants: Inhibition of larval attachment by proteases. Mar Biotechnol 2007, 9, 388–397. [Google Scholar]
  20. Egan, S; Thomas, T; Holmström, C; Kjelleberg, S. Phylogenetic relationship and antifouling activity of bacterial epiphytes from the marine alga Ulva lactuca. Env Microbiol 2000, 2, 343–347. [Google Scholar]
  21. Egan, S; Holmström, C; Kjelleberg, S. Pseudoalteromonas ulvae sp. nov., a bacterium with antifouling activities isolated from the surface of a marine alga. Int J Syst Evol Microbiol 2001, 51 , 1499–1504. [Google Scholar]
  22. Egan, S; James, S; Holmström, C; Kjelleberg, S. Correlation between pigmentation and antifouling compounds produced by Pseudoalteromonas tunicata. Env Microbiol 2002, 4, 433–442. [Google Scholar]
  23. Egan, S; James, S; Kjelleberg, S. Identification and characterization of a putative transcriptional regulator controlling the expression of fouling inhibitors in Pseudoalteromonas tunicata. Appl Env Microbiol 2002, 68, 372–378. [Google Scholar]
  24. Faulkner, DJ. Sammes, EG, Ed.; In Topics in Antibiotic Chemistry; John Wiley: New York, 1978; Chapter 2. pp. 9–58. [Google Scholar]
  25. Franks, A; Haywood, P; Holmström, C; Egan, S; Kjelleberg, S; Kumar, N. Isolation and structure elucidation of a novel yellow pigment from the marine bacterium Pseudoalteromonas tunicata. Molecules 2005, 10, 1286–1291. [Google Scholar]
  26. Franks, A; Egan, S; Holmström, C; James, S; Lappin-Scott, H; Kjelleberg, S. Inhibition of fungal colonization by Pseudoalteromonas tunicata provides a competitive advantage during surface colonization. Appl Env Microbiol 2006, 72, 6079–6087. [Google Scholar]
  27. Gallacher, S; Birkbeck, TH. A tissue-culture assay for direct detection of sodium-channel blocking toxins in bacterial culture supernates. FEMS Microbiol Lett 1992, 92, 101–108. [Google Scholar]
  28. Gallacher, S; Birkbeck, TH. Effect of phosphate concentration on production of tetrodotoxin by Alteromonas tetraodonis. Appl Env Microbiol 1993, 59, 3981–3983. [Google Scholar]
  29. Gauthier, MJ. Alteromonas rubra sp. nov., a new marine antibiotic-producing bacterium. Int J Syst Bacteriol 1976, 26, 459–466. [Google Scholar]
  30. Gauthier, MJ. Modification of bacterial respiration by a macromolecular polyanionic antibiotic produced by a marine Alteromonas. Antimicrob Agents Chemother 1976, 76, 361–366. [Google Scholar]
  31. Gauthier, MJ. Alteromonas citrea, a new Gram-negative, yellow-pigmented species from seawater. Int J Syst Bacteriol 1977, 27, 349–354. [Google Scholar]
  32. Gauthier, MJ. Validation of the name Alteromonas luteoviolacea. Int J Syst Bacteriol 1982, 32 , 82–86. [Google Scholar]
  33. Gauthier, MJ; Breittmayer, VA. A new antibiotic-producing bacterium from seawater: Alteromonas aurantia sp. nov. Int J Syst Bacteriol 1979, 29, 366–372. [Google Scholar]
  34. Gauthier, MJ; Flatau, GN. Antibacterial activity of marine violet-pigmented Alteromonas with special reference to the production of brominated compounds. Can J Microbiol 1976, 22, 1612–1619. [Google Scholar]
  35. Gauthier, G; Gauthier, M; Christen, R. Phylogenetic analysis of the genera Alteromonas, Shewanella and Moritella using genes coding for small-subunit rRNA sequences and division of the genus Alteromonas into two genera, Alteromonas (emended) and Pseudoalteromonas gen. nov., and proposal of twelve new species combinations. Int J Syst Bacteriol 1995, 45, 755–761. [Google Scholar]
  36. Gerber, NN; Gauthier, MJ. New prodigiosin-like pigment from Alteromonas rubra. Appl Env Microbiol 1979, 37, 1176–1179. [Google Scholar]
  37. Gribble, GW. The diversity of naturally occurring organobromine compounds. Chem Soc Rev 1999, 28, 335–348. [Google Scholar]
  38. Grossart, HP; Kiørboe, T; Tang, K; Ploug, H. Bacterial colonization of particles: growth and interactions. Appl Env Microbiol 2003, 69, 3500–3509. [Google Scholar]
  39. Hansen, AJ; Weeks, OB; Colwell, RR. Taxonomy of Pseudomonas piscicida (Bein) Buck, Meyers and Leifson. J Bacteriol 1965, 89, 752–761. [Google Scholar]
  40. Harder, T; Dobretsov, S; Qian, PY. Waterborne polar macromolecules act as algal antifoulants in the seaweed Ulva reticulata. Mar Ecol Prog Ser 2004, 274, 133–141. [Google Scholar]
  41. Holland, GS; Jamieson, DD; Reichelt, JR; Viset, G; Wells, RJ. Chem Ind (London) 1984, 850.
  42. Holmström, C; Egan, S; Franks, A; McCloy, S; Kjelleberg, S. Antifouling activities expressed by marine surface associated Pseudoalteromonas species. FEMS Microbiol Ecol 2002, 41, 47–58. [Google Scholar]
  43. Holmström, C; James, S; Egan, S; Kjelleberg, S. Inhibition of common fouling organisms by marine bacterial isolates with special reference to the role of pigmented bacteria. Biofouling 1996, 10 , 251–259. [Google Scholar]
  44. Holmström, C; Kjelleberg, S. Marine Pseudoalteromonas species are associated with higher organisms and produce active extracellular agents. FEMS Microbiol Ecol 1999, 30, 285–293. [Google Scholar]
  45. Holmström, C; James, S; Neilan, B; White, D; Kjelleberg, S. Pseudoalteromonas tunicata sp. nov., a bacterium that produces anti-fouling agents. Int J Syst Bacteriol 1998, 48, 1205–1212. [Google Scholar]
  46. Huang, YL; Dobretsov, S; Ki, JS; Yang, LH; Qian, PY. Presence of acylhomoserine lactone in subtidal biofilm and the implication in larval behavioral response in the polychaete Hydroides elegans. Microb Ecol 2007, 54, 384–392. [Google Scholar]
  47. Huang, YL; Dobretsov, S; Xiong, HR; Qian, PY. Effect of biofilm formation by Pseudoalteromonas spongiae on induction of larval settlement of the polychaete Hydroides elegans. Appl Env Microbiol 2007, 73, 6284–6288. [Google Scholar]
  48. Huggett, MJ; Williamson, JE; de Nys, R; Kjelleberg, S; Steinberg, P. Larval settlement of the common Australian sea urchin Heliocidaris erythrogramma in response to bacteria from the surface of coralline algae. Oecologia 2006, 149, 604–619. [Google Scholar]
  49. Isnanetyo, A; Kamei, Y. MC21-A, a bactericidal antibiotic produced by a new marine bacterium, Pseudoalteromonas phenolica sp. nov. O-BC30T against methicillin-resistant Staphylococcus aureus. Antimicrob Agents Chemother 2003, 47, 480–488. [Google Scholar]
  50. Ivanova, EP; Flavier, S; Christen, R. Phylogenetic relationships among marine Alteromonas-like proteobacteria: emended description of the family Alteromonadaceae and proposal of Pseudoalteromonadaceae fam. nov., Colwelliaceae fam. nov., Shewanellaceae fam. nov., Moritellaceae fam. nov., Ferrimonadaceae fam. nov., Idiomarinaceae fam. nov. and Psychromonadaceae fam. nov. Int J Syst Evol Microbiol 2004, 54, 1773–1788. [Google Scholar]
  51. Ivanova, EP; Gorshkova, NM; Zhukova, NV; Lysenko, AM; Zelepuga, EA; Prokof'eva, NG; Mikhailov, VV; Nicolau, DV; Christens, R. Characterization of Pseudoalteromonas distincta-like sea-water isolates and description of Pseudoalteromonas aliena sp nov. Int J Syst Evol Microbiol 2004, 54, 1431–1437. [Google Scholar]
  52. James, SG; Holmström, C; Kjelleberg, S. Purification and characterization of a novel antibacterial protein from the marine bacterium D2. Appl Env Microbiol 1996, 62, 2783–2788. [Google Scholar]
  53. Jiang, Z; Boyd, KG; Mearns-Spragg, A; Adams, DR; Wright, PC; Burgess, JG. Two diketopiperazines and halogenated phenol from cultures of the marine bacterium, Pseudoalteromonas luteoviolacea. Nat Prod Lett 2000, 14, 435–440. [Google Scholar]
  54. Kalinovskaya, NI; Ivanova, EP; Alexeeva, YV; Gorshkova, NM; Kuznetsova, TA; Dmitronek, AD; Nicolau, DV. Low-molecular-weight, biologically active compounds from marine Pseudoalteromonas species. Curr Microbiol 2004, 48, 441–446. [Google Scholar]
  55. Kamei, Y; McCarthy, SA; Kakimoto, D; Johnson, R. Inhibition of Paramecium caudatum by an Alteromonas luteoviolacea antibiotic. Antimicrob Agents Chemother 1986, 30, 301–303. [Google Scholar]
  56. Kawauchi, K; Shibutani, K; Yagisawa, H; Kamata, H; Nakatsuji, S; Anzai, H; Yokoyama, Y; Ikegami, Y; Moriyama, Y; Hirata, H. A possible immunosuppressant, cycloprodigiosin hydrochloride, obtained from Pseudoalteromonas denitrificans. Biochem Biophys Res Comm 1997, 237, 543–547. [Google Scholar]
  57. Kim, HS; Hayashi, M; Shibata, Y; Wataya, Y; Mitamura, T; Horii, T; Kawauchi, K; Hirata, H; Tsuboi, S; Moriyama, Y. Cycloprodigiosin hydrochloride obtained from Pseudoalteromonas denitrificans is a potent antimalarial agent. Biol Pharm Bull 1999, 22, 532–534. [Google Scholar]
  58. König, G; Kehraus, S; Seibert, S; Abdel-Lateff, A; Müller, D. Natural products from marine organisms and their associated microbes. Chembiochem 2006, 7, 229–238. [Google Scholar]
  59. Leitz, T; Wagner, T. The marine bacterium Alteromonas espejiana induces metamorphosis of the hydroid Hydractinia echinata. Mar Biol 1993, 115, 173–178. [Google Scholar]
  60. Leone, S; Silipo, A; Nazarenko, EL; Lanetta, R; Parrilli, M; Molinaro, A. Molecular structure of endotoxins from Gram-negative, marine bacteria: an update. Mar Drugs 2007, 5, 85–112. [Google Scholar]
  61. Lindquist, N; Fenical, W. New tambjamine class alkaloids from the marine ascidian Atapozoa sp. and its nudibranch predators – origins of the tambjamines in atapozoa. Experientia 1991, 47, 504–508. [Google Scholar]
  62. Long, RA; Qureshi, A; Faulkner, DJ; Azam, F. 2-n-pentyl-4-quinolinol produced by a marine Alteromonas sp. and its potential ecological and biogeochemical roles. Appl Environ Microbiol 2003, 69, 568–576. [Google Scholar]
  63. Longeon, A; Peduzzi, J; Barthelemy, M; Corre, S; Nicolas, JL; Guyot, M. Purification and partial identification of novel antimicrobial protein from marine bacterium Pseudoalteromonas species strain X153. Ma Biotech 2004, 6, 633–641. [Google Scholar]
  64. Lovejoy, C; Bowman, JP; Hallegraeff, GM. Algicidal effects of a novel marine Pseudoalteromonas isolate (class Proteobacteria, gamma subdivision) on harmful algal bloom species of the genera Chatonella: Gymnodinium: Heterosigma. Appl Environ Microbiol 1998, 64 , 2806–2813. [Google Scholar]
  65. Lowell, FM. The structure of a bromine rich antibiotic. J Amer Chem Soc 1966, 88, 4510–4511. [Google Scholar]
  66. Maeda, M; Nogami, K; Kanematsu, M; Hirayama, K. The concept of biological control methods in aquaculture. Hydrobiologia 1997, 358, 285–290. [Google Scholar]
  67. Maeshima, M; Nakayasu, T; Kawauchi, K; Hirata, H; Shimmen, T. Cycloprodigiosin uncouples H+-pyrophosphatase of plant vacuolar membranes in the presence of chloride ion. 1999. Plant Cell Physiol 1999, 40, 439–442. [Google Scholar]
  68. Magae, J; Miller, MW; Nagai, K; Shearer, GM. Effect of metacycloprodigiosin, an inhibitor of killer T cells on murine skill and heart transplants. J Antiobiot 1996, 48, 86–90. [Google Scholar]
  69. Mai-Prochnow, A; Evans, F; Dalisay-Saludes, D; Stelzer, S; Egan, S; James, S; Webb, JS; Kjelleberg, S. Biofilm development and cell death in the marine bacterium Pseudoalteromonas tunicata. Appl Env Microbiol 2004, 70, 3232–3238. [Google Scholar]
  70. Mai-Prochnow, A; Webb, JS; Ferrari, BC; Kjelleberg, S. Ecological advantages of autolysis during the development and dispersal of Pseudoalteromonas tunicata biofilms. Appl Env Microbiol 2006, 72, 5414–5420. [Google Scholar]
  71. McCarthy, SA; Johnson, RM; Kakimoto, D. Characterisation of an antibiotic produced by Alteromonas luteoviolacea Gauthier 1982, 85 isolated from Kinko Bay, Japan. J Appl Bacteriol 1994, 77, 426–432. [Google Scholar]
  72. Meyers, SP; Baslow, MH; Bein, SJ; Marks, CE. Studies of Flavobacterium piscicida Bein. I. Growth, toxicity, and ecological considerations. J Bacteriol 1950, 78, 225–230. [Google Scholar]
  73. Mitova, M; Tutino, ML; Infusini, G; Marino, G; De Rosa, S. Extracellular peptides from Antarctic psychrophile Pseudoalteromonas haloplanktis. Mar Biotechnol 2005, 7, 523–531. [Google Scholar]
  74. Nam, YD; Chang, HW; Park, JR; Kwon, HY; Quan, ZX; Park;, YH; Lee, JS; Yoon, JH; Bae, JW. Pseudoalteromonas marina sp. nov., a marine bacterium isolated from tidal flats of the Yellow Sea, and reclassification of Pseudoalteromonas sagamiensis as Algicola sagamiensis comb. nov. Int J Syst Evol Microbiol 2007, 57, 12–18. [Google Scholar]
  75. Negri, A; Webster, NS; Hill, RT; Heyward, AJ. Metamorphosis of broadcast spawning corals in response to bacteria isolated from crustose algae. Mar Ecol Prog Ser 2001, 223, 121–131. [Google Scholar]
  76. Nelson, EJ; Ghiorse, WC. Isolation and identification of Pseudoalteromonas piscicida strain Curad associated with diseased damselfish (Pomacentridae) eggs. J Fish Diseases 1999, 22, 253–260. [Google Scholar]
  77. Novick, NJ; Tyler, ME. Isolation and characterization of Alteromonas luteoviolacea strains with sheathed flagella. Int J Syst Bacteriol 1985, 35, 111–113. [Google Scholar]
  78. O’Toole, G; Kaplan, HB; Kolter, R. Biofilm formation as microbial development. Annu Rev Microbiol 2000, 54, 49–79. [Google Scholar]
  79. Patel, P; Callow, ME; Joint, I; Callow, JA. Specificity in larval settlement – modifying response of bacterial biofilms towards zoospores of the marine alga Enteromorpha. Env Microbiol 2004, 5, 338–349. [Google Scholar]
  80. Perez-Tomas, R; Montaner, B; Llagostera, R; Soto-Cerrato, V. The prodigiosins, proapoptotic drugs with anticancer properties. Biochem Pharmacol 2003, 66, 1447–1452. [Google Scholar]
  81. Pujalte, MJ; Sitja-Bobadilla, A; Macian, MC; Alvarez-Pellitero, P; Garay, E. Occurrence and virulence of Pseudoalteromonas spp. in cultured gilthead sea bream (Sparus aurata L.) and European sea bass (Dicentrarchus labrax L.). Molecular and phenotypic characterisation of P.undina strain U58. Aquaculture 2007, 271, 47–53. [Google Scholar]
  82. Qian, PY; Lau, SCK; Dahms, H-U; Dobretsov, S; Harder, T. Marine biofilms as mediators of colonization by marine macroorganisms: Implications for antifouling and aquaculture. Mar Biotechnol 2007, 9, 399–410. [Google Scholar]
  83. Rao, D; Webb, JS; Kjelleberg, S. Microbial colonization and competition on the marine alga Ulva australis. Appl Env Microbiol 2006, 72, 5547–5555. [Google Scholar]
  84. Riquelme, C; Hayashida, G; Araya, R; Uchida, A; Satomi, M; Ishida, Y. Isolation of a native bacterial strain from the scallop Argopecten purpuratus with inhibitory effects against pathogenic vibrios. J Shellfish Res 1996, 15, 369–374. [Google Scholar]
  85. Sakata, T; Sakaguchi, K; Kakimoto, D. Antiobiotic production by marine pigmented bacteria. I. Antibacterial effect of Alteromonas luteoviolaceus. Mem Fac Fish, Kagoshima Univ 1982, 31, 243–250. [Google Scholar]
  86. Sakata, T; Sakaguchi, K; Kakimoto, D. Antiobiotic production by marine pigmented bacteria. II. Purification and characterization of antibiotic substances of Alteromonas luteoviolacea. Mem Fac Fish, Kagoshima Univ 1986, 35, 29–37. [Google Scholar]
  87. Saravanan, P; Nancharaiah, YV; Venugopalan, VP; Subba Rao, T; Jayachandran, S. Biofilm formation by Pseudoalteromonas ruthenica and its removal by chlorine. Biofouling 2006, 22, 371–381. [Google Scholar]
  88. Seipp, S; Wittig, K; Stiening, B; Bottger, A; Leitz, T. Metamorphosis of Hydractinia echinata (Cnidaria) is caspase-dependent. Int J Dev Biol 2006, 50, 63–70. [Google Scholar]
  89. Shiozawa, H; Kagasaki, T; Kinoshita, T; Haruyama, H; Domon, H; Utsui, Y; Kodama, K; Takahashi, S. Thiomarinol, a new hybrid antimicrobial antibiotic produced by a marine bacterium fermentation, isolation, structure, and antimicrobial activity. J Antibiot 1993, 46, 1834–1842. [Google Scholar]
  90. Shiozawa, H; Shimada, A; Takahashi, S. Thiomarinol D, E, F and G, new hybrid antimicrobial antibiotics produced by a marine bacterium: isolation, structure and antimicrobial activity. J Antibiot 1997, 50, 449–452. [Google Scholar]
  91. Simidu, U; Kita-Tsukamoto, K; Yasumoto, T; Yotsu, M. Taxonomy of marine bacteria that produce tetrodotoxin. Int J Syst Bacteriol 1990, 40, 331–336. [Google Scholar]
  92. Skerratt, JH. Bacterial and algal interaction in a Tasmanian estuary. In PhD Thesis; University of Tasmania, Hobart: Tasmania, Australia, 2001; pp. 219–235. [Google Scholar]
  93. Skerratt, JH; Bowman, JP; Hallegraeff, G; James, S; Nichols, PD. Algicidal bacteria associated with blooms of a toxic dinoflagellate in a temperate Australian estuary. Mar Ecol Prog Ser 2002, 244, 1–15. [Google Scholar]
  94. Skovhus, T; Holmström, C; Kjelleberg, S; Dahllöf, I. Molecular investigation of the distribution, abundance and diversity of the genus Pseudoalteromonas in marine samples. FEMS Microbiol Ecol 2007, 61, 348–361. [Google Scholar]
  95. Sobolevskaya, MP; Smetanina, OF; Speitling, M; Shevchenko, LS; Dmitrenok, PS; Laatsch, H; Kuznetsova, TA; Ivanova, EP; Elyakov, GB. Controlling production of brominated cyclic depsipeptides by Pseudoalteromonas maricaloris KMM 636T. Lett Appl Microbiol 2005, 40, 243–248. [Google Scholar]
  96. Stelzer, S; Egan, S; Larsen, MR; Bartlett, DH; Kjelleberg, S. Unravelling the role of the ToxR-like transcriptional regulator WmpR in the marine antifouling bacterium Pseudoalteromonas tunicata. Microbiology 2006, 152, 1385–1394. [Google Scholar]
  97. Tanigaki, K; Sato, T; Tanaka, Y; Ochi, T; Nishikawa, A; Nagai, K; Kwashima, H; Ohkuma, S. BE-18591 as a new H+/Cl symport ionophore that inhibits immunoproliferation and gastritis. FEBS Lett 2002, 524, 37–42. [Google Scholar]
  98. Wieczorek, SK; Todd, CD. Inhibition and facilitation of the settlement of epifaunal marine invertebrate larvae by microbial biofilm cues. Biofouling 1998, 12, 81–93. [Google Scholar]
  99. Wigglesworth-Cooksey, B; Cooksey, KE. Use of fluorophore-conjugated lectins to study cell-cell interactions in model marine biofilms. Appl Env Microbiol 2005, 71, 428–435. [Google Scholar]
  100. Williamson, N; Simonsen, H; Ahmed, R; Goldet, G; Slater, H; Woodley, L; Leeper, FJ; Salmond, GPC. Biosynthesis of the red antibiotic, prodigiosin, in Serratia: identification of a novel 2-methyl-n-amyl-pyrrole (MAP) assembly pathway, definition of the terminal condensing enzyme, and implications for undecylprodigiosin biosynthesis in Streptomyces. Mol Microbiol 2005, 56, 971–989. [Google Scholar]
  101. Wratten, SJ; Wolfe, MS; Andersen, RJ; Faulkner, DJ. Antibiotic metabolites from a marine pseudomonad. Antimicrob Agents Chemother 1977, 11, 411–414. [Google Scholar]
  102. Yee, LH; Holmström, C; Fuary, ET; Lewin, NC; Kjelleberg, S; Steinberg, PD. Inhibition of fouling by marine bacteria immobilised in kappa-carrageenan beads. Biofouling 2007, 23, 287–294. [Google Scholar]
  103. Yoshikawa, K; Nakayama, Y; Hayashi, M; Unemoto, T; Mochida, K. Korormicin, an antibiotic specific for Gram-negative marine bacteria, strongly inhibits the respiratory chain-linked Na+-translocating NADH: Quinone reductase from the marine Vibrio alginolyticus. J Antiobiot 1999, 52 , 182–185. [Google Scholar]
  104. Zapata, M; Silva, F; Luza, Y; Wilkens, M; Riquelme, C. The inhibitory effect of biofilms produced by wild bacterial isolates to the larval settlement of the fouling ascidia Cionia intestinalis and Pyura praeputialis. Electr J Biotechnol 2007, 10, 149–159. [Google Scholar]
Figure 1. Phylogenetic tree of genus Pseudoalteromonas based on 16S rRNA gene sequences (5’-prime region, poisitions 10 to 509 E. coli equivalent). Nucleotide distances are based on the maximum likelihood algorithm and the tree clustered using the Neighbor-joining procedure (Phylip v. 3.67; Joe Felsenstein; Clades within the genus are demarcated in different color type. Species in green are non-pigmented species. Species in blue and purple, as well as P. ruthenica are predominantly brightly-pigmented species (see Table 1).
Figure 1. Phylogenetic tree of genus Pseudoalteromonas based on 16S rRNA gene sequences (5’-prime region, poisitions 10 to 509 E. coli equivalent). Nucleotide distances are based on the maximum likelihood algorithm and the tree clustered using the Neighbor-joining procedure (Phylip v. 3.67; Joe Felsenstein; Clades within the genus are demarcated in different color type. Species in green are non-pigmented species. Species in blue and purple, as well as P. ruthenica are predominantly brightly-pigmented species (see Table 1).
Marinedrugs 05 00220 g001
Figure 2. The inhibition of invertebrate larvae and algal spore settlement by different Pseudoalteromonas species. Data adapted from Holmström et al. [42].
Figure 2. The inhibition of invertebrate larvae and algal spore settlement by different Pseudoalteromonas species. Data adapted from Holmström et al. [42].
Marinedrugs 05 00220 g002
Figure 3. Anti-algal activity of Pseudoalteromonas species strain Y on the dinoflagellate Gymnodinium catenatum. a) Typical chain form of G. catenatum (time 0–10 minutes). b) Cell chains disassemble into individual cells (T=20 minutes); c) Cells become rounded (T=45 minutes; d) Cell lysis and leakage with strain Y swarming to a lysis cell (T=3 hours). Data and figures adapted from [92, 93].
Figure 3. Anti-algal activity of Pseudoalteromonas species strain Y on the dinoflagellate Gymnodinium catenatum. a) Typical chain form of G. catenatum (time 0–10 minutes). b) Cell chains disassemble into individual cells (T=20 minutes); c) Cells become rounded (T=45 minutes; d) Cell lysis and leakage with strain Y swarming to a lysis cell (T=3 hours). Data and figures adapted from [92, 93].
Marinedrugs 05 00220 g003
Figure 4. Abundance of Pseudoalteromonas (compared to total bacteria; orange bars) and abundance of anti-fouling species P. tunicata and P. ulvae (compared to total Pseudoalteromonas; purple bars) on various marine alga, invertebrates, rocks and in sediment. Error bars are standard deviations of results from 3 separate samples. Numbers in parentheses indicate the number of samples showing the presence of the biofouling species in DGGE analyses. The presence of toxic protein AlpP (as determined by positive PCR results for the alpP gene) is indicated in red type. Data adapted from Skovhus et al. [94].
Figure 4. Abundance of Pseudoalteromonas (compared to total bacteria; orange bars) and abundance of anti-fouling species P. tunicata and P. ulvae (compared to total Pseudoalteromonas; purple bars) on various marine alga, invertebrates, rocks and in sediment. Error bars are standard deviations of results from 3 separate samples. Numbers in parentheses indicate the number of samples showing the presence of the biofouling species in DGGE analyses. The presence of toxic protein AlpP (as determined by positive PCR results for the alpP gene) is indicated in red type. Data adapted from Skovhus et al. [94].
Marinedrugs 05 00220 g004
Figure 5. Brominated compounds formed by Pseudoalteromonas species. See text for more information.
Figure 5. Brominated compounds formed by Pseudoalteromonas species. See text for more information.
Marinedrugs 05 00220 g005
Figure 6. Non-halogenated low molecular weight compounds produced by Pseudoalteromonas species. See text for details.
Figure 6. Non-halogenated low molecular weight compounds produced by Pseudoalteromonas species. See text for details.
Marinedrugs 05 00220 g006
Table 1. Bioactive compound production and associated activities by described Pseudoalteromonas species.
Table 1. Bioactive compound production and associated activities by described Pseudoalteromonas species.
SpeciesPigmented aSourceBioactive compoundsbInhibitory activities [other activities]b
P. aliena+ (melanin)seawaterUnknown compound(s) formedAnti-tumorigenic activity-Ehrlich ascites carcinoma cell line inhibitedc
P. agarivorans-seawater, ascidians-d-d [degrades algal polysaccharides]
P. antarctica-seawater, sea-ice, muddy soils, sediment-None observede,f [novel polysaccharides, cold-active enzymes]
P. atlantica-seawater, marine alga-May cause opportunistic disease in crabs [strong degrader of algal polysaccharides]
P. aurantia+ (yellow)surface of Ulva lactuca, seawaterUnknown compound(s) formedAntimicrobial activity; inhibits settlement of invertebrate larvae
P. byunsanensis-tidal flat sediment--
P. carrageenovora-seawater, marine algaNone observede [strong degrader of algal polysaccharides]
P. citrea+ (yellow, melanin)seawater, mussels, ascidians, spongesUnknown compound(s) formedInhibits settlement of invertebrate larvae; cytotoxic against sea urchin [algal polysaccharide degradation]
P. denitrificans+ (red)seawaterhigh molecular weight polyanionic substance; cycloprodigiosin HClAnti-tumorigenic activity; inhibits T-cell/lymphocyte proliferation; anti-malarial activity; induces settlement of sea urchin Heliocidaris erythrogrammag
P. distincta± (melanin)sponge--
P. elyakovii-mussels, marine alga-None observede,f
P. espejiana-seawater-None observede,f
P. flavipulchra+ (orange)seawater--
P. haloplanktis-seawaternovel diketopiperazines- [Probiotic benefits to shellfish; cold-active enzymes]
P. issachenkonii-marine algaisatin; unknown reddish-brown compoundAnti-fungal activity; hemolytic
P. luteoviolacea+ (purple, yellow)seawater, marine algatoxic antimicrobial protein; brominated pyrrole-containing compounds, 4- benzaldehyde; n-propyl-4-hydroxybenzoateAntimicrobial activity; inhibits algal spore settlement; cytotoxic against sea urchin Strongylocentrotus intermedius; induces settlement of sea urchin Heliocidaris erythrogrammag
P. maricoloris+ (yellow)spongesbromo-alterochromides A and BAntibacterial activity; cytotoxicity against sea urchins
P. marina-tidal flat sediment--
P. mariniglutinosa-diatoms--
P. nigrifaciens± (melanin)seawater, salted foods, mussels--
P. paragorgicola-sponge--
P. peptidolytica+(yellow)seawaterunknown compoundsAntimicrobial activity, hemolytice
P. phenolica+ (brown)seawater3,3’,5,5’-tetra-bromo-2,2- biphenyldiolAntimicrobial activity
P. piscicida (and related bacteria)+ (yellow)estuarine waters, fish samplestoxic protein; possible yellow cyclic/acyclic brominated depsipeptide compounds; unknown anti-algal compound(s)Antibacterial; algicidal activity; possible cytotoxicity [opportunistic fish pathogen; thrombolytic enzymes]
P. rubra+ (red)seawaterhigh molecular weight polyanionic substance; cycloprodigiosin HCl; rubrenoic acidsAntimicrobial activity; anti- tumorigenic activity; inhibits T-cell/lymphocyte proliferation; anti-malarial; bronchodilatatorice,f
P. ruthenica+(pale orange)shellfishunknown compoundsAntimicrobial activity
P. spongiae+ (pale orange)sponge-Strongly induces settlement of Hydroides elegans
P. tetraodonis-puffer fishtetrodotoxinNeurotoxic effectse,f
P. translucida-seawater--
P. tunicata+ (green, purple, yellow)marine alga, tunicatesunknown purple pigment; tambjamine-like alkaloid YP1; toxic protein AlpP; other unknown sunstancesAnti-fungal, anti-algal, antimicrobial, inhibits settlement of invertebrate larvae and algal spores; inhibits protists
P. ulvae+ (purple)marine algaunknown substancesInhibits invertebrate larval settlement and algal spore germination and settlement
P. undina-seawater, fish-hemolytic; [probiotic benefits; possible opportunistic fish pathogen]
aData is obtained from species description papers listed at
bData on natural compounds with known structural data and associated activity are detailed in sections 3 and 4.
cPigments not formed under standard growth conditions. Melanin production is stimulated when grown on L-tyrosine and/or 3,4-dihydroxyl-L-phenylalanine. Butanol extracts inhibited an Ehrlich’s ascites carcinoma cell line [51].
dNo published natural product or bioassay data for these species is available.
eEthyl acetate and butanol extracts negative for antimicrobial and haemolytic activity [54].
fEthyl acetate extracts negative for cytotoxicity against sea urchin Stronglyocentrotus intermedius [54].
gData from Huggett et al. [48].
Mar. Drugs EISSN 1660-3397 Published by MDPI AG, Basel, Switzerland RSS E-Mail Table of Contents Alert
Back to Top