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BioMed Research International
Volume 2013 (2013), Article ID 463894, 12 pages
Cyanobacterial Toxin Degrading Bacteria: Who Are They?
Department of Ichthyology ####^~^~^~^~^~^####x26; Aquatic Environment, School of Agricultural Sciences, University of Thessaly, 384 46 Volos, Greece
Received 21 March 2013; Accepted 21 May 2013
Academic Editor: George Tsiamis
Copyright © 2013 Konstantinos Ar. Kormas and Despoina S. Lymperopoulou. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.
Cyanobacteria are ubiquitous in nature and are both beneficial and detrimental to humans. Benefits include being food supplements and producing bioactive compounds, like antimicrobial and anticancer substances, while their detrimental effects are evident by toxin production, causing major ecological problems at the ecosystem level. To date, there are several ways to degrade or transform these toxins by chemical methods, while the biodegradation of these compounds is understudied. In this paper, we present a meta-analysis of the currently available 16S rRNA and mlrA (microcystinase) genes diversity of isolates known to degrade cyanobacterial toxins. The available data revealed that these bacteria belong primarily to the Proteobacteria, with several strains from the sphingomonads, and one from each of the Methylobacillus and Paucibacter genera. Other strains belonged to the genera Arthrobacter, Bacillus, and Lactobacillus. By combining the ecological knowledge on the distribution, abundance, and ecophysiology of the bacteria that cooccur with toxic cyanobacterial blooms and newly developed molecular approaches, it is possible not only to discover more strains with cyanobacterial toxin degradation abilities, but also to reveal the genes associated with the degradation of these toxins.
Cyanobacteria are some of the most ####^~^~^~^~^~^####x201c;charismatic####^~^~^~^~^~^####x201d; microorganisms in the tree of life. Their ecological importance is widely recognised in the scientific world . Among their remarkable features, though, there is a contradiction, at least for human interests. On one hand, they are considered of pronounced biotechnological interest as they produce several bioactive compounds through their metabolism, from biofuels and biopolymers to drugs [2####^~^~^~^~^~^####x2013;4]. On the other hand, they are capable of producing a wide range of nuisance secondary metabolites, that is, toxins (hereafter cyanotoxins). The toxicity of these compounds, which has been proved for a great variety of organisms , dictates for solutions to the problem caused by the accumulation of cyanotoxins in, mostly, freshwater water bodies all over the world. Although this issue of toxicity has been known for several decades now, there has been little effort towards biotechnological remedies, especially via degradation/transformation by microorganisms. This could be partially due to the notion that cyanotoxins are relatively recalcitrant to chemical degradation  and were thought as nonlabile for biodegradation as well. However, advances in molecular microbial ecology have elucidated that strains of the bacterial genera Sphingomonas, Sphingosinicella, Arthrobacter, Brevibacterium, Rhodococcus, and Burkholderia can degrade microcystins (MC) and nodularins in time scales from hours to days [6, 7]. Moreover, we are now aware of eukaryotic mechanisms of cyanotoxin elimination in animal tissues [8####^~^~^~^~^~^####x2013;10]. This slowly growing body of literature presents many opportunities for deeper investigations into cyanotoxins and their biodegradation.
There is good evidence that toxic cyanobacterial water blooms favour the occurrence of specific members of the bacterioplankton . These prokaryotes, bacteria and Archaea, are excellent candidates for having cyanotoxin-degrading properties. The satellite prokaryotic communities of cyanobacterial water blooms (e.g., [12, 13]) could either degrade and/or assimilate the toxin and their degradation products or could be inhibited by the toxins during the bloom (e.g., [14, 15]). Although there are several well-studied water bodies harbouring toxin-producing Cyanobacteria, their accompanying prokaryotic communities are considerably understudied (e.g., ). Another deficit in our current knowledge in cyanotoxin-degrading prokaryotes in such studies is that despite the fact that natural freshwaters can harbour diverse archaeal assemblages , practically nothing is known about the role of Archaea in cyanotoxin degradation. However, it has been shown recently that hydrogenotrophic methanogens are associated with Microcystis scum degradation , opening, thus, a new line of research for the investigation of the role of Archaea in MC and/or other cyanotoxin degradation.
Microcystins are the most widely distributed and known cyanotoxins. They consist of a group of cyclic heptapeptide hepatotoxins [cyclo-(D-Ala1-X2-D-MeAsp3-Z4-Adda5-D-Glu6-Mdha7)] produced by Cyanobacteria that belong to the genera Microcystis, Anabaena, Nostoc, and Oscillatoria (Planktothrix) [18, 19]. Two of these peptides ( and ) are variable, resulting in more than 70 variants . MC-LR, in which leucine (L) at position 2 and arginine (R) at position 4 are found, is the most toxic among MCs . Conventional water treatment processes (chlorine, permanganate, chloride dioxide, ozone, and advanced oxidation methods) have been found inadequate for the removal of MCs . Recently, more environmental friendly approaches have been applied to MC removal directly from natural eutrophic freshwater systems, involving plant material and minerals . Whilst more advanced and efficient chemical techniques (granular activated carbon, powdered activated carbon, and membrane filtration) exist, they are considered too expensive to employ for the elimination of a contaminant whose presence in the water bodies is occasional and hard to predict . Moreover, MCs####^~^~^~^~^~^####x2019; stable cyclic structure against physicochemical factors renders biodegradation inevitable, as the most sustainable, efficient, and realistic method for their removal . Microbial degradation is the most important mechanism for the removal of MCs in the natural environment and is considered as an alternative water treatment strategy versus the physicochemical one .
To date, only one biodegradation pathway for microcystin by Sphingomonas sp. strain ACM-3962 has been characterized . The mlr gene cluster plays a crucial role in the sequential enzymatic hydrolyses of peptide bonds . This cluster consists of four genes, that is, mlrA, mlrB, mlrC, and mlrD, and codes for at least three intracellular enzymes (Figure 1) .
The mlrA is the most important gene of this cluster because it encodes the enzyme that cleaves the Adda-Arg peptide bond in MC-LR and opens the cyclic structure . The cyclic structure of MC is responsible for its stability against physicochemical and biological factors that contribute to inactivation or degradation, such as pH, temperature, sunlight, and other common proteases . The initial hydrolysis mediated by the mlrA gene results in a substantial reduction in molecular toxicity, which is displayed by the 160-fold reduction of activity of the linear MC-LR towards protein phosphatase compared to that of the cyclic MC-LR. The mlrA gene sequence is very rare with no homologues found in the public databases, and therefore its functional characteristics are difficult to be assigned.
Biochemical characterization has shown that the mlrA gene encodes a metalloprotease , and its activation site consists of a typical to zinc metalloproteases motif, the HXXMECX . It has been speculated that it might as well represent a new protease family with the function of cleaving smaller cyclic peptides . The replacement of the R group by the A (alanine) group at MC-LA does not seem to affect the degradation process, suggesting that the presence of arginine may not be a critical site of cleavage . In a recent study  the translation of the mlrA gene sequence and the alignment of the resulting amino acid sequence with other putative MlrA in the database revealed a zinc-bonding site and a transmembrane region, and the authors introduced the concept of a potential new protein family with unique functions. mlrB encodes a putative serine peptidase which degrades the linear (or acyclo) MC-LR to the tetrapeptide H-Adda-Glu-Mdha-Ala-OH, while MlrC exerts the action of a putative metallopeptidase and degrades the tetrapeptide to Adda or small amino acids . The mlrD gene does not express hydrolytic activity and probably encodes the transporter protein that allows the uptake of MCs into the cell since it exhibits high sequence similarity to the PTR2 family of oligopeptide symporters .
The MC degradation ability is not commonly present in the Sphingomonas genus but only in specific bacterial strains (Table 1) . It has been suggested that the MC-degradation trait was acquired by gene transfer during the evolution of Sphingomonas, based on 16S rRNA gene analyses that relate phylogenetically non-MC-degrading bacteria closer to the MC-degrader strain Y2 . Moreover, Manage et al.  managed to isolate bacteria that belonged to the Actinobacteria phylum (Arthrobacter sp., Brevibacterium sp., and Rhodococcus sp.) capable of degrading MC-LR. The mlr gene cluster was not detected, but this is the first report on bacteria other than Sphingomonadaceae with the ability to degrade MCs. Hu et al.  also isolated a Methylobacillus sp. strain from a cyanobacterial sludge with the ability to completely degrade both MC-LR and MC-RR. To date, 20 different MC-degrading bacteria have been isolated from rivers, lakes, and biological filters, but without simultaneous detection of the mlr gene cluster, which is considered to encode the hydrolytic proteins involved in the initial steps of MC-degradation . It seems that the presence of microbial populations capable of degrading MCs and other peptides is promoted by the prevalence of MC-containing blooms . Therefore, a greater diversity of bacterial genera might be able to degrade MCs with as yet to be characterized degradation mechanisms.
Nodularins are produced by Nodularia spumigena and have been detected mostly in brackish habitats [28, and references therein]. Their structure is similar to that of MCs with the difference that they consist of a pentapeptide [cyclo-(D-MeAsp1-L-Arg2-Adda3-D-Glu4-Mdhb5)] . Consequently, some bacteria which are capable of degrading MCs are also able to degrade NODs (Table 1), possibly due to the similar mode of action of MlrA that cleaves hydrolytically their cyclic structure at the Adda-Arg peptide bond .
Cylindrospermopsin (CYN) is a group of alkaloid cytotoxins which are produced by Cylindrospermopsis raciborskii, Umezakia natans, Anabaena bergii, Anabaena lapponica, Aphanizomenon ovalisporum, Aphanizomenon flosaquae, Raphidiopsis curvata, and Lyngbya wollei. Three studies until now have demonstrated that CYN can be biodegraded in water habitats [55, 56]. Smith et al.  found that a linear relation between the biodegradation rate and the initial concentration of CYN could be established, while Mohamed and Alamri  reported the biodegradation of CYN by a Bacillus strain (AMRI-03) isolated from a cyanobacterial bloom, with rapidly occurring degradation rates, highly dependent on the initial CYN concentration. However, no defined metabolic pathway has been elucidated to date.
Saxitoxins form a group of alkaloid neurotoxins that can be produced by dinoflagellates and many different cyanobacterial genera, including Anabaena, Raphidiopsis, Lyngbya, Planktothrix (Oscillatoria), and Cylindrospermopsis [18, 57]. While there are many studies that report the biotransformation of saxitoxin variants to more toxic ones [58, 59], there is scarcity of literature regarding its biodegradation. Donovan et al.  demonstrated an overall reduction of saxitoxin mixture to 90####^~^~^~^~^~^####x25; by seven unidentified but potential saxitoxin-degrading bacteria that had been isolated from the digestive tracts of blue mussels.
Anatoxin-a is a low molecular weight neurotoxic alkaloid that is produced by cyanobacteria belonging to the genera Anabaena, Aphanizomenon, Microcystis, Planktothrix, Raphidiopsis, Arthrospira, Cylindrospermum, Phormidium, Nostoc, and Oscillatoria . There is limited information on the biodegradation of anatoxin-a. A Pseudomonas sp. isolate was reportedly able to degrade anatoxin-a , while Rapala et al.  also reported a significant (22####^~^~^~^~^~^####x2013;48####^~^~^~^~^~^####x25;) reduction of anatoxin-a in sediments, but no further information on bacteria able to degrade or enzymatic pathways and corresponding genes is available.
1.6. ####^~^~^~^~^~^####x3b2;-N-Methylamino-L-Alanine (BMAA)
BMAA is a highly reactive nonessential amino acid which can be found either free or protein-bound. It is associated with amyotrophic lateral sclerosis and Parkinson dementia complex (ALS/PDC) . Although BMAA is the most recent cyanotoxin discovered to date , it is produced from members from all major cyanobacterial groups  and for this reason it is believed to be widespread in freshwater systems. It has been demonstrated that it accumulates in higher trophic levels, including species that are consumed by humans . As airborne algae and Cyanobacteria  have started to attract the scientific interest in a more focused way , it has been proposed recently that it can be dispersed via aerosolization of Cyanobacteria containing this toxin . To date, no published data exist on the biodegradation on BMAA.
1.7. Nontoxic Nuisance Cyanobacterial Compounds
Apart from the cyanotoxins, the water quality problems in freshwater bodies are also related to the organoleptic traits of water which are easily perceived by consumers due to the altered and usually unpleasant taste and odor. 2-Methylisoborneol (MIB) and geosmin, two cyclic aliphatic tertiary alcohols, are the main responsible compounds that impart such problematic characteristics in waters (earthy/camphorous odour), even though they both do not pose any known hazard for the human health . MIB and geosmin can be produced by a range of Cyanobacteria including Anabaena, Aphanizomenon, Geitlerinema, Symploca, Planktothrix (Oscillatoria), Phormidium, Nostoc, Pseudanabaena, and Lyngbya . There are several studies which elucidate the ability of some bacteria to biodegrade both compounds [71####^~^~^~^~^~^####x2013;74], but no definite metabolic pathway is known. The biodegradation reactions of both compounds seem to be mediated by monooxygenase enzymes in a way similar to the biological Baeyer-Villiger reaction that takes place during the biodegradation of camphor, a bicyclic ketone . This is due to the similarity of their structure to alicyclic alcohols and ketones [75, 76]. The isolation and cloning of the cam operon from a camphor-degrading strain of Pseudomonas putida confirmed this hypothesis , while camphor enrichment of a camphor-degrading bacterial consortium has led to the isolation of all three available secondary metabolites of MIB . Similarly, the biodegradation of geosmin has been reported by cyclohexanol-degrading strains of Nocardia and Acinetobacter, equivalently to the Baeyer-Villiger reaction , while Eaton and Sandusky  demonstrated geosmin biodegradation by two terpene-degrading bacteria, Rhodococcus wratislaviensis DLC-cam and Pseudomonas sp. SBR3-tpnb, but only after their induction with either camphor or terpene.
In this paper, we review the available literature on the molecular diversity of bacterial strains which possess some kind of cyanotoxin-degrading feature or, at least, are naturally associated with toxin-producing Cyanobacteria based on 16S rRNA and mlrA gene sequence diversity. We aimed to depict the major taxa that include such strains as a first step in a focused approach for the isolation and biotechnological development of microorganisms that can degrade cyanotoxins in natural and engineered aquatic systems.
2. Materials and Methods
16S rRNA gene sequences of bacterial isolates that either carry the mlrA gene or grow on/degrade MCs or both were retrieved from GenBank, and phylogenetic trees were constructed using the neighbor-joining algorithm based on distances calculated by the Jukes-Cantor model and implemented in the MEGA5 software . Bootstrapping was performed with 1,000 replicates to assign confidence levels to the tree topology. The sequences were screened for chimeras using the Bellerophon program at http://comp-bio.anu.edu.au/bellerophon/bellerophon.pl/. No putative chimerical sequences were detected.
The search of mlrA sequences in the GeneBank database proved a not so straight forward procedure, as the search by using ####^~^~^~^~^~^####x201c;mlrA####^~^~^~^~^~^####x201d; gives ambiguous results, with some of them being totally irrelevant to the degradation gene. An initial search of the ####^~^~^~^~^~^####x201c;mlrA####^~^~^~^~^~^####x201d; gene turned back several hundreds of sequences. Most of these sequences are associated with Escherichia coli and representatives of the family of Enterobacteriaceae that correspond to genes unrelated to the degradation of microcystins. The majority of these genes are related to transcriptional regulators such as the HTH-type transcriptional regulator, the ABC-transporter, acetyl-xylan esterases, the McrR-like regulator A, and the merR family. Filtering of these results by excluding all E. coli and Enterobacteriaceae bacteria (e.g., mlrA [All Fields] NOT ####^~^~^~^~^~^####x201c;Escherichia####^~^~^~^~^~^####x201d; NOT ####^~^~^~^~^~^####x201c;Shigella####^~^~^~^~^~^####x201d; NOT ####^~^~^~^~^~^####x201c;Klebsiella####^~^~^~^~^~^####x201d; NOT ####^~^~^~^~^~^####x201c;Enterobacter####^~^~^~^~^~^####x201d; NOT ####^~^~^~^~^~^####x201c;Salmonella####^~^~^~^~^~^####x201d; NOT ####^~^~^~^~^~^####x201c;Cronobacter####^~^~^~^~^~^####x201d; NOT ####^~^~^~^~^~^####x201c;Erwinia####^~^~^~^~^~^####x201d; NOT ####^~^~^~^~^~^####x201c;Citrobacter####^~^~^~^~^~^####x201d; NOT ####^~^~^~^~^~^####x201c;Pantoea####^~^~^~^~^~^####x201d;) shrinks the results to a few tenths of sequences that still include some irrelevant sequences similar to those described above. After this stage, manual fishing of the mlrA sequences was necessary. Two sequences of uncultured clones (FJ438526 and FJ438527) were excluded due to their short length (120####^~^~^~^~^~^####x2009;bp). Four more sequences of uncultured clones were excluded (AB600656, AB600658, AB600663, and AB600668) due to the high number of potential but short amino acid (1####^~^~^~^~^~^####x2013;157####^~^~^~^~^~^####x2009;aa) ORFs into which they could be translated. The MlrA sequences we used consisted of 184 or more amino acids.
The amino-acid sequences of the mlrA gene-carrying bacterial strains were retrieved from the GenBank (http://www.ncbi.nlm.nih.gov/nuccore), and their phylogenetic relationship was inferred using the neighbor-joining method. The evolutionary distances were computed using the Poisson correction method. Bootstrapping was performed with 1,000 replicates. Sphingopyxis sp. C-1####^~^~^~^~^~^####x2032;s amino-acid sequence was not available in the database and was translated by the nucleotide sequence with the EMBOSS (Sixpack)####^~^~^~^~^~^####x5f;program (http://www.ebi.ac.uk/Tools/st/). There were a total of 157 informative positions in the final dataset.
3. Results and Discussion
Our intention was to identify ways to enhance the development of biotechnological tools for biodegradation of cyanotoxins by reviewing the current literature and mining databases for possible new prokaryotes of interest. The bulk of the existing data deal with microcystins. Our analysis revealed that the ubiquitous ####^~^~^~^~^~^####x3b1;- and ####^~^~^~^~^~^####x3b2;-Proteobacteria and Actinobacteria include the majority of potential cyanotoxin-degrading bacteria (Figure 2). Based on their phylogenetic taxonomy, the few recently found strains capable of degrading microcystin or carrying the mlrA gene were closely affiliated to known species or genera (Figure 2). The analysis of the MlrA protein diversity (Figure 3) showed that all the available sequences also belong to closely related members of the Sphingomonadaceae (####^~^~^~^~^~^####x3b1;-Proteobacteria), but there are also several strains that cannot be assigned to known bacterial taxa.
The majority of the taxa with cyanotoxin degradation capability are known to have multiple other biodegradation traits. Strains of the genus Rhodococcus are known for degrading xenobiotics in various aquatic and terrestrial habitats and also for producing surfactants . The strains that belonged to the Sphingomonadaceae family were affiliated with the genera Sphingosinicella, Sphingopyxis, Sphingomonas, and Novosphingobium. The sphingomonads are not new to biotechnological applications. They are involved with novel catalyses, bioremediation, fossil fuel desulfurization, novel enzymes, biotin, and polysaccharide production. Their ability to degrade hazardous organic compounds, for example, PCBs, creosote, pentachlorophenol, herbicides, and the conversion of commonly occurring organics to novel or specialty chemicals, is a key feature for the group, especially in contaminated soils and sediments [80, and references therein]. Despite their biotechnological significance and their widespread distribution, their ecology is insufficiently studied. This could be due to their ability to utilize a wide array of organic-often refractory substances, their metabolic diversity, and their ability to grow in oligotrophic conditions, with the latter being more obvious in the marine environment. These features also hinder their successful cultivation. The metabolic diversity of this group is indicated by the lack of a culture medium specific for sphingomonads, leaving the molecular approaches more appropriate for their study. They are more frequently found in freshwater habitats like rivers, ponds, lakes, and groundwater, but the majority of the available strains have been isolated from contaminated to heavily contaminated sites [80, and references therein]. Since these strains have been found to carry the mlrA gene and/or grow on microcystin, it is plausible to consider them as some of the most active####^~^~^~^~^~^####x2014;and promising for future applications####^~^~^~^~^~^####x2014;players in the degradation of microcystin.
Microcystins and nodularins####^~^~^~^~^~^####x2019; biosynthesis is also carried out by nonribosomal peptide synthetases (NRPS) and type I polyketide synthases (PKS-I) . These extraordinary enzymes (along with their products) are evolved rapidly through multiple mechanisms . On the other hand, the ability of the cooccurring bacterioplankton in cyanobacterial water blooms to degrade/assimilate toxins (e.g., [14, 15]) along with the metabolic diversity, but insufficiently studied ecology, of bacteria such as the sphingomonads [80, and references therein] is well documented. These two adversary forces might have an important ecological function and might be able to drive the coevolution of the NRPS/PKS-I enzymes and the cyanotoxin biodegradation pathways in a water bloom, leading to a ####^~^~^~^~^~^####x201c;race of arms####^~^~^~^~^~^####x201d; against cyanotoxins. Moreover, the retrieval of bacteria such as Actinobacteria that lack the known mlr gene cluster  implies the existence of more genes, and thus pathways, associated with the degradation of these toxins.
The genus Arthrobacter (Figure 2), originating mostly from soil, is known in biotechnology mostly because of its nutritional versatility of growing on a wide array of organic compounds, including herbicides, pesticides, n-alkanes, aromatic compounds, and lower alcohols [83, and references therein], its potential for bioremediating their heavy metals (Cd, Co, Cu, Ni, and Pb) , and also for the production of surfactants, glutamic acid, ####^~^~^~^~^~^####x3b1;-ketoglutaric acid, and riboflavin [79, 83]. The ability of Arthrobacter to degrade microcystins renders this genus an important one in future biotechnological quests. Similar features are also found in Brevibacterium spp. (Figure 2), a genus that is taxonomically and physiologically similar to Arthrobacter, and until recently, frequently confused with it .
Bacillus spp. have been one of the pillars of biotechnology for several decades now. Although they possess numerous biodegradation competences, to date only one isolate (Figure 2) seems to be associated with the microcystin degradation. This by no means diminishes the biotechnological value of this genus; the reason for the underrepresentation of Bacillus spp. is possibly due to the fact that the Firmicutes is a minor phylum in freshwater habitats  where most toxic cyanobacterial blooms occur.
Apart from the above-mentioned strains with already well-recognised biodegradation potential, the Methylobacillus sp. and Paucibacter sp. (Figure 2) can be considered important emerging genera of microcystin degraders. This suggests that with ongoing research and the application of appropriate methodology new taxa of degraders can be revealed.
It has been shown that freshwater harbors a vast and distinguishable bacterial diversity from other aquatic habitats [84, 85]. However, our meta-analysis showed that, to date, only a few bacterial species bear the mlrA gene, a proxy for microcystin degradation potential. Moreover, several of these bacteria are not abundant in the ecosystems where microcystins and other cyanotoxins are found. This could partially explain our perceived concept of the nonlabile nature of microcystins and possibly of other cyanotoxins. However, it could also be related to the methodological approaches used so far to isolate such degraders. The most common practice involves culture-dependent approaches with the toxin being the sole carbon and/or energy source (e.g., [39, 48]). We believe that novel/recent molecular methodologies provide valuable complementary information because they overcome culturing limitations, and in silico approaches are not dependent on metabolic traits of the taxa containing genes for microcystin degradation.
Nowadays there are several omics methodologies that can be tailored to specific scientific quests. Future investigations targeting microorganisms with cyanotoxin degradation could include (a) genomic analysis of the available strains, like the case of Sphingosinicella microcystinivorans ; gene mining of such genomes could depict the relevant degradation pathways; (b) metagenomic libraries of habitats where the sphingomonads are either abundant or with bacterial communities occurring in close association with toxic cyanobacterial blooms and followed by metatranscriptomics libraries of the same samples where the MlrA and other related enzymes have been proved to be transcribed (c) single-cell genomics (SCG). SCG is of particular interest to biotechnology and bioprospecting due to its ability to attribute specific####^~^~^~^~^~^####x2014;often novel####^~^~^~^~^~^####x2014;biochemical pathways to specific cells/species . Recently, a SSG study revealed for the first time a great extent of the metabolic potential of a ubiquitous freshwater actinobacterial species . In the case of cyanotoxin degraders, for example, it would be feasible to assign the biodegradation pathway of cyanotoxins to specific bacteria (i.e., single-cells) from any toxic cyanobacterial water bloom, regardless of their cultivability. The application of such approaches, along with the development of standardized and easy-to-use analytical methods for the measurement of multiple cyanotoxins from the same sample, could speed progress towards the standardized usage of specific cyanotoxin degraders. Finally, special attention should be paid to other toxins than the microcystins, as some of these are, at least, of equal potency, distribution, and persistence in the environment.
The authors thank the two anonymous reviewers for their comments on the originally submitted version of this paper.
- B. A. Whitton, Ed., Ecology of Caynobacteria II. Their Diversity in Space and Time, Springer, Dordrecht, The Netherlands, 2012.
- R. M. M. Abed, S. Dobretsov, and K. Sudesh, “Applications of cyanobacteria in biotechnology,” Journal of Applied Microbiology, vol. 106, no. 1, pp. 1–12, 2009.
- D. C. Ducat, J. C. Way, and P. A. Silver, “Engineering cyanobacteria to generate high-value products,” Trends in Biotechnology, vol. 29, no. 2, pp. 95–103, 2011.
- T. L. Simmons, E. Andrianasolo, K. McPhail, P. Flatt, and W. H. Gerwick, “Marine natural products as anticancer drugs,” Molecular Cancer Therapeutics, vol. 4, no. 2, pp. 333–342, 2005.
- M. Pelaez, M. G. Antoniou, X. He et al., “Sources and occurrence of cyanotoxins worldwide,” in Xenobiotics in the Urban Water Cycle, D. Fatta-Kassinos, K. Bester, and K. Kümmerer, Eds., pp. 101–127, Springer, New York, NY, USA, 2010.
- H. Mazur-Marzec and M. Pliński, “Do toxic cyanobacteria blooms pose a threat to the Baltic ecosystem?” Oceanologia, vol. 51, no. 3, pp. 293–319, 2009.
- H. Kato, K. Tsuji, and K. Harada, “Microbial degradation of cyclic peptides produced by bacteria,” Journal of Antibiotics, vol. 62, no. 4, pp. 181–190, 2009.
- I. R. Falconer, T. Buckley, and M. T. Runnegar, “Biological half-life, organ distribution and excretion of 125I-labelled toxic peptide from the blue-green alga Microcystis aeruginosa,” Australian Journal of Biological Sciences, vol. 39, no. 1, pp. 17–21, 1986.
- W. P. Brooks and G. A. Codd, “Distribution of Microcystic aeruginosa peptide toxin and interactions with hepatic microsomes in mice,” Pharmacology and Toxicology, vol. 60, no. 3, pp. 187–191, 1987.
- N. A. Robinson, J. G. Pace, C. F. Matson, G. A. Miura, and W. B. Lawrence, “Tissue distribution, excretion and hepatic biotransformation of microcystin-LR in mice,” Journal of Pharmacology and Experimental Therapeutics, vol. 256, no. 1, pp. 176–182, 1991.
- H. Li, P. Xing, and Q. L. Wu, “The high resilience of the bacterioplankton community in the face of a catastrophic disturbance by a heavy Microcystis bloom,” FEMS Microbiology Ecology, vol. 82, pp. 192–201, 2012.
- K. A. Kormas, E. Vardaka, M. Moustaka-Gouni et al., “Molecular detection of potentially toxic cyanobacteria and their associated bacteria in lake water column and sediment,” World Journal of Microbiology and Biotechnology, vol. 26, no. 8, pp. 1473–1482, 2010.
- L. Shi, Y. Cai, F. Kong, and Y. Yu, “Specific association between bacteria and buoyant Microcystis colonies compared with other bulk bacterial communities in the eutrophic Lake Taihu, China,” Environmental Microbiology Reports, vol. 4, pp. 669–678, 2012.
- K. A. Berg, C. Lyra, K. Sivonen et al., “High diversity of cultivable heterotrophic bacteria in association with cyanobacterial water blooms,” ISME Journal, vol. 3, no. 3, pp. 314–325, 2009.
- C. Dziallas and H. Grossart, “Microbial interactions with the cyanobacterium Microcystis aeruginosa and their dependence on temperature,” Marine Biology, vol. 159, pp. 2389–2398, 2012.
- E. O. Casamayor and C. Borrego, “Archaea,” in Encyclopedia of Inland Waters, G. E. Likens, Ed., vol. 3, pp. 167–181, Elsevier, Oxford, UK, 2009.
- P. Xing, H. Li, Q. Liu, and L. Zheng, “Composition of the archaeal community involved in methane production during the decomposition of Microcystis blooms in the laboratory,” Canadian Journal of Microbiology, vol. 58, pp. 1153–1158, 2012.
- K. Sivonen and J. Jones, “Cyanobacterial toxins,” in Toxic Cyanobacteria in Water. A Guide to Their Public Health Consequences, Monitoring and Management, I. Chorus and J. Bartram, Eds., E & FN Spon on behalf of the World Health Organization, 1999.
- I. R. Falconer, Cyanobacterial Toxins in Drinking Water Supplies: Cylindrospermopsins and Microcystins, CRC Press, Boca Raton, Fla, USA, 2005.
- C. Edwards and L. A. Lawton, “Bioremediation of cyanotoxins,” Advances in Applied Microbiology, vol. 67, pp. 109–129, 2009.
- S. Imanishi, H. Kato, M. Mizuno, K. Tsuji, and K. Harada, “Bacterial degradation of microcystins and nodularin,” Chemical Research in Toxicology, vol. 18, no. 3, pp. 591–598, 2005.
- A. A. de la Cruz, M. G. Antoniou, A. Hiskia et al., “Can we effectively degrade microcystins?—implications on human health,” Anti-Cancer Agents in Medicinal Chemistry, vol. 11, no. 1, pp. 19–37, 2011.
- D. K. Kim, K. E. O'Shea, and W. J. Cooper, “Degradation of MTBE and related gasoline oxygenates in aqueous media by ultrasound irradiation,” Journal of Environmental Engineering, vol. 128, no. 9, pp. 806–812, 2002.
- L. Eleuterio and J. R. Batista, “Biodegradation studies and sequencing of microcystin-LR degrading bacteria isolated from a drinking water biofilter and a fresh water lake,” Toxicon, vol. 55, no. 8, pp. 1434–1442, 2010.
- D. G. Bourne, P. Riddles, G. J. Jones, W. Smith, and R. L. Blakeley, “Characterisation of a gene cluster involved in bacterial degradation of the cyanobacterial toxin microcystin LR,” Environmental Toxicology, vol. 16, no. 6, pp. 523–534, 2001.
- G. J. Jones and P. T. Orr, “Release and degradation of microcystin following algicide treatment of a Microcystis aeruginosa bloom in a recreational lake, as determined by HPLC and protein phosphatase inhibition assay,” Water Research, vol. 28, no. 4, pp. 871–876, 1994.
- T. Saito, K. Okano, H. Park et al., “Detection and sequencing of the microcystin LR-degrading gene, mlrA, from new bacteria isolated from Japanese lakes,” FEMS Microbiology Letters, vol. 229, no. 2, pp. 271–276, 2003.
- L. Ho, E. Sawade, and G. Newcombe, “Biological treatment options for cyanobacteria metabolite removal—a review,” Water Research, vol. 46, no. 5, pp. 1536–1548, 2012.
- J. Chen, L. B. Hu, W. Zhou et al., “Degradation of microcystin-LR and RR by a Stenotrophomonas sp. strain EMS isolated from Lake Taihu, China,” International Journal of Molecular Sciences, vol. 11, no. 3, pp. 896–911, 2010.
- P. M. Manage, C. Edwards, B. K. Singh, and L. A. Lawton, “Isolation and identification of novel microcystin-degrading bacteria,” Applied and Environmental Microbiology, vol. 75, no. 21, pp. 6924–6928, 2009.
- R. Stepanauskas, “Single cell genomics: an individual look at microbes,” Current Opinion in Microbiology, vol. 15, pp. 613–620, 2012.
- S. M. K. Nybom, S. J. Salminen, and J. A. O. Meriluoto, “Removal of microcystin-LR by strains of metabolically active probiotic bacteria,” FEMS Microbiology Letters, vol. 270, no. 1, pp. 27–33, 2007.
- S. M. K. Nybom, S. J. Salminen, and J. A. O. Meriluoto, “Specific strains of probiotic bacteria are efficient in removal of several different cyanobacterial toxins from solution,” Toxicon, vol. 52, no. 2, pp. 214–220, 2008.
- L. Hu, F. Zhang, C. Liu, and M. Wang, “Biodegradation of microcystins by Bacillus sp. strain EMB,” Energy Procedia, vol. 16, pp. 2054–2059, 2012.
- D. G. Bourne, G. J. Jones, R. L. Blakeley, A. Jones, A. P. Negri, and P. Riddles, “Enzymatic pathway for the bacterial degradation of the cyanobacterial cyclic peptide toxin microcystin LR,” Applied and Environmental Microbiology, vol. 62, no. 11, pp. 4086–4094, 1996.
- H. Ishii, M. Nishijima, and T. Abe, “Characterization of degradation process of cyanobacterial hepatotoxins by a gram-negative aerobic bacterium,” Water Research, vol. 38, no. 11, pp. 2667–2676, 2004.
- A. M. Valeria, E. J. Ricardo, P. Stephan, and D. A. Wunderlin, “Degradation of microcystin-RR by Sphingomonas sp. CBA4 isolated from San Roque reservoir (Córdoba-Argentina),” Biodegradation, vol. 17, no. 5, pp. 447–455, 2006.
- T. Saitou, N. Sugiura, T. Itayama, Y. Inamori, and M. Matsumura, “Degradation characteristics of microcystins by isolated bacteria from Lake Kasumigaura,” Journal of Water Supply, vol. 52, no. 1, pp. 13–18, 2003.
- T. Maruyama, H. Park, K. Ozawa et al., “Sphingosinicella microcystinivorans gen. nov., sp. nov., a microcystin-degrading bacterium,” International Journal of Systematic and Evolutionary Microbiology, vol. 56, no. 1, Article ID 63789, pp. 85–89, 2006.
- H. Park, Y. Sasaki, T. Maruyama, E. Yanagisawa, A. Hiraishi, and K. Kato, “Degradation of the cyanobacterial hepatotoxin microcystin by a new bacterium isolated from a hypertrophic lake,” Environmental Toxicology, vol. 16, no. 4, pp. 337–343, 2001.
- D. Hoefel, L. Ho, P. T. Monis, G. Newcombe, and C. P. Saint, “Biodegradation of geosmin by a novel Gram-negative bacterium; isolation, phylogenetic characterisation and degradation rate determination,” Water Research, vol. 43, no. 11, pp. 2927–2935, 2009.
- L. Ho, A. Gaudieux, S. Fanok, G. Newcombe, and A. R. Humpage, “Bacterial degradation of microcystin toxins in drinking water eliminates their toxicity,” Toxicon, vol. 50, no. 3, pp. 438–441, 2007.
- L. Ho, D. Hoefel, C. P. Saint, and G. Newcombe, “Isolation and identification of a novel microcystin-degrading bacterium from a biological sand filter,” Water Research, vol. 41, no. 20, pp. 4685–4695, 2007.
- J. Wang, P. Wu, J. Chen, and H. Yan, “Biodegradation of microcystin-RR by a new isolated Sphingopyxis sp. USTB-05,” Chinese Journal of Chemical Engineering, vol. 18, no. 1, pp. 108–112, 2010.
- M. Zhang, G. Pan, and H. Yan, “Microbial biodegradation of microcystin-RR by bacterium Sphingopyxis sp. USTB-05,” Journal of Environmental Sciences, vol. 22, no. 2, pp. 168–175, 2010.
- H. Yan, J. Wang, J. Chen, W. Wei, H. Wang, and H. Wang, “Characterization of the first step involved in enzymatic pathway for microcystin-RR biodegraded by Sphingopyxis sp. USTB-05,” Chemosphere, vol. 87, no. 1, pp. 12–18, 2012.
- Y. Jiang, J. Shao, X. Wu, Y. Xu, and R. Li, “Active and silent members in the mlr gene cluster of a microcystin-degrading bacterium isolated from Lake Taihu, China,” FEMS Microbiology Letters, vol. 322, no. 2, pp. 108–114, 2011.
- K. Okano, K. Shimizu, Y. Kawauchi et al., “Characteristics of a microcystin-degrading bacterium under alkaline environmental conditions,” Journal of Toxicology, vol. 2009, Article ID 954291, 8 pages, 2009.
- A. Ramani, K. Rein, K. G. Shetty, and K. Jayachandran, “Microbial degradation of microcystin in Florida's freshwaters,” Biodegradation, vol. 23, no. 1, pp. 35–45, 2012.
- G. A. F. Lemes, R. Kersanach, L. da S. Pinto, O. A. Dellagostin, J. S. Yunes, and A. Matthiensen, “Biodegradation of microcystins by aquatic Burkholderia sp. from a South Brazilian coastal lagoon,” Ecotoxicology and Environmental Safety, vol. 69, no. 3, pp. 358–365, 2008.
- L. B. Hu, J. D. Yang, W. Zhou, Y. F. Yin, J. Chen, and Z. Q. Shi, “Isolation of a Methylobacillus sp. that degrades microcystin toxins associated with cyanobacteria,” New Biotechnology, vol. 26, no. 3-4, pp. 205–211, 2009.
- J. Rapala, K. A. Berg, C. Lyra et al., “Paucibacter toxinivorans gen. nov., sp. nov., a bacterium that degrades cyclic cyanobacterial hepatotoxins microcystins and nodularin,” International Journal of Systematic and Evolutionary Microbiology, vol. 55, no. 4, pp. 1563–1568, 2005.
- H. Yan, G. Pan, H. Zou, X. Li, and H. Chen, “Effective removal of microcystins using carbon nanotubes embedded with bacteria,” Chinese Science Bulletin, vol. 49, no. 16, pp. 1694–1698, 2004.
- S. Takenaka and M. F. Watanabe, “Microcystin LR degradation by Pseudomonas aeruginosa alkaline protease,” Chemosphere, vol. 34, no. 4, pp. 749–757, 1997.
- M. J. Smith, G. R. Shaw, G. K. Eaglesham, L. Ho, and J. D. Brookes, “Elucidating the factors influencing the biodegradation of cylindrospermopsin in drinking water sources,” Environmental Toxicology, vol. 23, no. 3, pp. 413–421, 2008.
- Z. A. Mohamed and S. A. Alamri, “Biodegradation of cylindrospermopsin toxin by microcystin-degrading bacteria isolated from cyanobacterial blooms,” Toxicon, vol. 60, pp. 1390–1395, 2012.
- S. A. Murray, T. K. Mihali, and B. A. Neilan, “Extraordinary conservation, gene loss, and positive selection in the evolution of an ancient neurotoxin,” Molecular Biology and Evolution, vol. 28, no. 3, pp. 1173–1182, 2011.
- Y. Kotaki, “Screening of bacteria which convert gonyautoxin 2,3 to saxitoxin,” Nippon Suisan Gakkaishi, vol. 55, p. 1239, 1989.
- N. Kayal, G. Newcombe, and L. Ho, “Investigating the fate of saxitoxins in biologically active water treatment plant filters,” Environmental Toxicology, vol. 23, no. 6, pp. 751–755, 2008.
- C. J. Donovan, J. C. Ku, M. A. Quilliam, and T. A. Gill, “Bacterial degradation of paralytic shellfish toxins,” Toxicon, vol. 52, no. 1, pp. 91–100, 2008.
- J. Osswald, S. Rellán, A. Gago, and V. Vasconcelos, “Toxicology and detection methods of the alkaloid neurotoxin produced by cyanobacteria, anatoxin-a,” Environment International, vol. 33, no. 8, pp. 1070–1089, 2007.
- J. Kiviranta, K. Sivonen, K. Lahti, R. Luukkainen, and S. I. Niemelae, “Production and biodegradation of cyanobacterial toxins—a laboratory study,” Archiv Für Hydrobiologie, vol. 121, pp. 281–294, 1991.
- J. Rapala, K. Lahti, K. Sivonen, and S. I. Niemela, “Biodegradability and adsorption on lake sediments of cyanobacterial hepatotoxins and anatoxin-a,” Letters in Applied Microbiology, vol. 19, no. 6, pp. 423–428, 1994.
- S. Jonasson, J. Eriksson, L. Berntzon et al., “Transfer of a cyanobacterial neurotoxin within a temperate aquatic ecosystem suggests pathways for human exposure,” Proceedings of the National Academy of Sciences of the United States of America, vol. 107, no. 20, pp. 9252–9257, 2010.
- S. J. Murch, P. A. Cox, and S. A. Banack, “A mechanism for slow release of biomagnified cyanobacterial neurotoxins and neurodegenerative disease in Guam,” Proceedings of the National Academy of Sciences of the United States of America, vol. 101, no. 33, pp. 12228–12231, 2004.
- P. A. Cox, S. A. Banack, S. J. Murch et al., “Diverse taxa of cyanobacteria produce β-N-methylamino-L-alanine, a neurotoxic amino acid,” Proceedings of the National Academy of Sciences of the United States of America, vol. 102, no. 14, pp. 5074–5078, 2005.
- S. Genitsaris, K. A. Kormas, and M. Moustaka-Gouni, “Airborne algae and cyanobacteria: occurrence and related health effects,” Frontiers in Bioscience, vol. 3, pp. 772–787, 2011.
- S. Genitsaris, M. Moustaka-Gouni, and K. A. Kormas, “Airborne microeukaryote colonists in experimental water containers: diversity, succession, life histories and established food webs,” Aquatic Microbial Ecology, vol. 62, no. 2, pp. 139–152, 2011.
- E. W. Stommel, N. C. Field, and T. A. Caller, “Aerosolization of cyanobacteria as a risk factor for amyotrophic lateral sclerosis,” Medical Hypotheses, vol. 80, pp. 142–145, 2012.
- F. Jüttner and S. B. Watson, “Biochemical and ecological control of geosmin and 2-methylisoborneol in source waters,” Applied and Environmental Microbiology, vol. 73, no. 14, pp. 4395–4406, 2007.
- A. Saito, T. Tokuyama, A. Tanaka, T. Oritani, and K. Fuchigami, “Microbiological degradation of (-)-geosmin,” Water Research, vol. 33, no. 13, pp. 3033–3036, 1999.
- D. Hoefel, L. Ho, W. Aunkofer et al., “Cooperative biodegradation of geosmin by a consortium comprising three gram-negative bacteria isolated from the biofilm of a sand filter column,” Letters in Applied Microbiology, vol. 43, no. 4, pp. 417–423, 2006.
- R. W. Eaton and P. Sandusky, “Biotransformations of 2-methylisoborneol by camphor-degrading bacteria,” Applied and Environmental Microbiology, vol. 75, no. 3, pp. 583–588, 2009.
- R. W. Eaton and P. Sandusky, “Biotransformations of (+/−)−geosmin by terpene-degrading bacteria,” Biodegradation, vol. 21, no. 1, pp. 71–79, 2009.
- P. W. Trudgill, “Microbial degradation of the alicyclic ring: structural relationships and metabolic pathways,” in Microbial Degradation of Organic Compounds, D. T. Gibson, Ed., pp. 131–180, Marcel Dekker, New York, NY, USA, 1984.
- B. E. Rittmann, C. J. Gantzer, and A. Montiel, “Biological treatment to control taste-and-odor compounds in drinking water treatment,” in Advances in Taste-and-Odor Treatment and Control, I. H. Suffet, J. Mallevialle, and E. Kawczynski, Eds., American Water Works Association Research Foundation, Denver, Colo, USA, 1995.
- E. Oikawa, A. Shimizu, and Y. Ishibashi, “2-methylisoborneol degradation by the cam operon from Pseudomonas putida PpG1,” Water Science and Technology, vol. 31, no. 11, pp. 79–86, 1995.
- K. Tamura, D. Peterson, N. Peterson, G. Stecher, M. Nei, and S. Kumar, “MEGA5: molecular evolutionary genetics analysis using maximum likelihood, evolutionary distance, and maximum parsimony methods,” Molecular Biology and Evolution, vol. 28, no. 10, pp. 2731–2739, 2011.
- M. Fingerman and R. Nagabhushanam, Bioremediation of Aquatic and Terrestrial Ecosystem, Science Publishers, Enfield, NH, USA, 2005.
- D. L. Balkwill, J. K. Fredrickson, and M. F. Romine, “Sphingomonas and related genera,” in The Prokaryotes. Third Edition. A Handbook on the Biology of Bacteria, M. Dworkin, S. Falkow, E. Rosenberg, K.-H. Schleifer, and E. Stackenbrandt, Eds., vol. 7 of Proteobacteria: Delta and Epsilon subclasses. Deeply rooting Bacteria, pp. 605–629, Springer, Berlin, Germany, 2006.
- K. Nikolouli and D. Mossialos, “Bioactive compounds synthesized by non-ribosomal peptide synthetases and type-I polyketide synthases discovered through genome-mining and metagenomics,” Biotechnology Letters, vol. 34, no. 8, pp. 1393–1403, 2012.
- G. D. Amoutzias, Y. Van de Peer, and D. Mossialos, “Evolution and taxonomic distribution of nonribosomal peptide and polyketide synthases,” Future Microbiology, vol. 3, no. 3, pp. 361–370, 2008.
- D. Jones and R. M. Keddie, “The genus Arthrobacter,” in The Prokaryotes. Third Edition. A Handbook on the Biology of Bacteria, M. Dworki, S. Falkow, E. Rosenberg, K.-H. Schleifer, and E. Stackenbrandt, Eds., vol. 3 of Proteobacteria: Delta and Epsilon subclasses. Deeply rooting Bacteria, pp. 945–960, Springer, Berlin, Germany, 2006.
- R. J. Newton, S. E. Jones, A. Eiler, K. D. McMahon, and S. Bertilsson, “A guide to the natural history of freshwater lake bacteria,” Microbiology and Molecular Biology Reviews, vol. 75, no. 1, pp. 14–49, 2011.
- A. Barberán and E. O. Casamayor, “Global phylogenetic community structure and β-diversity patterns in surface bacterioplankton metacommunities,” Aquatic Microbial Ecology, vol. 59, no. 1, pp. 1–10, 2010.
- S. L. Garcia, K. D. McMahon, M. Martinez-Garcia et al., “Metabolic potential of a single cell belonging to one of the most abundant lineages in freshwater bacterioplankton,” The ISME Journal, vol. 7, pp. 137–147, 2013.