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Review

Research Progress in the Biosynthetic Mechanisms of Marine Polyether Toxins

State Key Laboratory of NBC Protection for Civilian, Beijing 102205, China
*
Author to whom correspondence should be addressed.
These authors contributed equally to this work.
Mar. Drugs 2019, 17(10), 594; https://doi.org/10.3390/md17100594
Submission received: 26 September 2019 / Revised: 17 October 2019 / Accepted: 18 October 2019 / Published: 22 October 2019
(This article belongs to the Special Issue Toxins as Marine-Based Drug Discovery)

Abstract

:
Marine polyether toxins, mainly produced by marine dinoflagellates, are novel, complex, and diverse natural products with extensive toxicological and pharmacological effects. Owing to their harmful effects during outbreaks of marine red tides, as well as their potential value for the development of new drugs, marine polyether toxins have been extensively studied, in terms of toxicology, pharmacology, detection, and analysis, structural identification, as well as their biosynthetic mechanisms. Although the biosynthetic mechanisms of marine polyether toxins are still unclear, certain progress has been made. In this review, research progress and current knowledge on the biosynthetic mechanisms of polyether toxins are summarized, including the mechanisms of carbon skeleton deletion, pendant alkylation, and polyether ring formation, along with providing a summary of mined biosynthesis-related genes. Finally, future research directions and applications of marine polyether toxins are discussed.

1. Introduction

Marine polyether toxins, mainly produced by dinoflagellates, are natural polyketide compounds with novel and complex structures, unique biological activities, and extensive pharmacological effects, which have attracted great interest among marine biologists and pharmacologists [1,2]. The most striking feature of marine polyether toxins is the presence of one or more ether rings in their molecules, with ring sizes ranging from five- to nine-membered rings. According to their ether ring arrangement and molecular structure, marine polyether toxins are divided into linear, ladder-like (or fused), and macrolide polyethers, the typical examples of which are palytoxins (PLTXs), okadaic acid (OA), pectenotoxins (PTXs), maitotoxins (MTXs), brevetoxins (BTXs), ciguatoxins (CTXs), spirolides, gymnodimines, and pinnatoxins [3,4].
Marine polyether toxins are usually associated with harmful algal blooms, causing severe adverse effects on human health, tourism, wild fish stocks, and aquaculture [4,5,6,7]. For example, BTXs were isolated from the red tide-forming dinoflagellate Karenia brevis. The compound can then be enriched in fish, shellfish, and other organisms through the food chain, leading to a large number of fish and shellfish deaths [8,9]. BTXs function by blocking voltage-sensitive sodium channels (VSSCs), which makes this compound a potent neurotoxin [10,11]. CTXs, originally isolated from dinoflagellate Gambierdiscus spp., are the main factor causing ciguatera fish poisoning (CFP). CTXs have been shown to interact with the same VSSCs as BTXs do, and both are considered highly potent neurotoxins [12,13]. CTXs accumulate throughout the food chain up to higher predators, and may ultimately reach human consumers, thus causing neurological, gastrointestinal, and cardiovascular disorders. Estimates of the number of people who suffer from CFP poisoning annually range from 50,000 to 500,000 [14,15,16]. OA, which was isolated from dinoflagellate Prorocentrum lima and Dinophysis spp., is now widely distributed in coastal seas globally. This toxin can lead to diarrhetic shellfish poisoning upon the ingestion of contaminated shellfish by humans [17,18,19].
In addition to their toxicity and harmfulness, marine polyether toxins show special pharmacological activities, with the potential for new drug development or as tools for studying disease-related signaling pathways. BTXs, as a neuroagonist, was shown to increase the plasticity of neurons, revealing its potential to treat diseases such as apoplexy, neurodegeneration, and mucociliary dysfunction [20]. OA has the inhibitory activity against serine/threonine protein phosphatase and can regulate intracellular signaling pathways, which opens up a possibility for its use against Alzheimer’s disease and other neurodegenerative disorders associated with memory impairment [21,22,23]. In addition, OA is a potent inhibitor of tumorigenesis, causing cell growth inhibition and apoptosis of lung and colon cancer cells, and may thus be an important candidate for anticancer drug screening [24,25]. PTXs have demonstrated significant anti-tumor activity against human lung, colon, and breast cancer cells, and are considered potential chemotherapeutic molecules against p53-mutant type tumors [26,27,28].
Therefore, studying and exploring the biosynthetic mechanisms of marine polyether toxins could deepen our understanding of the biogenesis and evolution of these compounds, contribute to the effective monitoring, intervention, and elimination of phycotoxins, as well as lay a foundation for the development of new marine-derived drugs or drug precursors. This review focuses on the latest research progress in carbon skeleton deletion, pendant alkylation, polyether ring formation, and newly discovered genes related to the biosynthesis of marine polyether toxins.

2. Carbon Skeleton Deletion

Marine polyether toxins are mostly derived from dinoflagellates. It is generally known that the genomes of dinoflagellates are large and complex, with a large number of introns and redundant sequences, and are thus difficult to sequence and annotate and carry out genetic manipulations. Therefore, the biosynthetic mechanisms of marine polyether toxins have not yet been elucidated [29]. Research on the biosynthetic mechanisms of these compounds has mainly been based on isotope labeling experiments, used to identify pathways, or on transcriptome sequencing, used to discover biosynthetic genes. Fortunately, some progress has been made in related research.
Marine polyether toxins belong to a large family of polyketides, the synthesis of which is catalyzed by polyketide synthases (PKSs). The generalities of polyketide biosynthesis have been extensively reviewed over decades [30,31] and will only be briefly described here. Typically, PKS builds carbon chains in a manner similar to fatty acid synthase (FAS), in which the starting substrate, generally acetyl coenzyme A (acetyl CoA), is extended through a series of sequential Claisen ester condensations with malonyl CoA. The ketosynthase (KS) domain, which performs the condensation reaction between acyl units, along with acyl transferase (AT) and an acyl carrier protein (ACP) forms the core structure of FAS and PKS. Other domains that modify the acyl-units after condensation is dehydratase (DH), enoylreductase (ER), and ketoreductase (KR), which are selectively present or absent in PKS, however essential for FAS. The thioesterase (TE) domain hydrolyzes the polyketide chain from ACP, ultimately releasing the polyketide compound from the megasynthase. So far, three types of PKSs have been described [31]. In type I PKSs (modular), catalytic domains are organized in sequential modules on a single polypeptide (multi-domain protein), where each module contains all required domains for each step and is only used once during polyketide assembly, analogous to FASs in animals and fungi. Type II PKSs consist of multi protein complexes where each catalytic domain is present on a separate peptide and functions as a mono-domain protein in an iterative fashion, analogous to type II FASs in bacteria and plants. Type III PKSs, also known as chalcone synthases, are self-contained homodimeric enzymes where each monomer performs a specific function in an iterative manner without the use of ACP.
Based on 13C isotope labeling studies of acetate precursors and determination of their chemical structures, it is obvious that marine polyether compounds are produced in dinoflagellates via polyketide synthesis pathways, with acetate being the main extension unit [32,33,34,35]. However, the polyketide chain is not assembled by successive addition of acetate units as in a typical polyketide, rather that the chain contains both intact and cleaved acetate units where the acetate carboxyl or methyl carbons are deleted. This particular phenomenon seems to be common because it has been observed in every dinoflagellate polyketide studied to date, such as BTXs [32,33,34], OA and its derivatives [36,37,38,39,40], goniodomins [41], amphidinols [42,43], amphidinolides [44,45], yessotoxins [46,47], and spirolides [48] (Figure 1), and so can be regarded as a new paradigm in dinoflagellate polyketide biosynthesis. In addition, there are usually multiple acetate deletion steps occurring in a single dinoflagellate polyether. In BTX biosynthesis, there are 12 deletion steps, with 11 carboxyl carbons of acetate units deleted and one methyl carbon deleted. In OA biosynthesis, there are two carboxyl carbon deletion steps. In yessotoxin biosynthesis, there are up to 15 deletion steps, with all carboxyl carbons deleted (Figure 1).

2.1. Carbon Deletion Mediated by Intermediate Metabolites from the Tricarboxylic Acid (TCA) Cycle

To date, there exist three hypotheses regarding the mechanism of carbon deletion in dinoflagellate polyketides. The first suggests that acetate units in the carbon skeleton are not really cleaved or deleted but are converted to new extension units through other pathways prior to condensation with the polyketide chain. In particular, some intermediate metabolites from the tricarboxylic acid (TCA) cycle, such as succinate and α-ketoglutarate, may participate in the growing polyketide chain [33,34] (Figure 2). It is known that one-step oxidative decarboxylation occurs when acetyl CoA is added in the TCA cycle to form succinate and α-ketoglutarate, which corresponds to the deletion of carboxyl carbon in an acetate unit. The participation of succinate and α-ketoglutarate in the BTX biosynthesis was detected via 13C isotope labeling experiments, although the location of these units in the BTX carbon skeleton has not been determined. However, this postulate suffers from the fact that the nascent polyketide chain would have to detach from and then reattach to the PKS enzyme. Moreover, a detailed quantitative evaluation of isotope enrichment during BTX biosynthesis from single- and doubly-labeled acetate established that all carbons, including the deleted ones, were equally enriched [49]. Similar results have also been found for OA biosynthesis [50]. These findings indicated that all acetate building units were derived from the same biogenetic bank, and it seemed unlikely that other biogenetic precursors were involved because this would lead to variations in isotope enrichment along the polyketide chain.

2.2. Carbon Deletion Through Favorskii-Type Rearrangement

The second presumption suggests that carboxyl carbons of intact acetate units are deleted from the nascent polyketide chain through a Favorskii-type rearrangement, catalyzed by a cytochrome P450 enzyme or flavin monooxygenase [50,51] (Figure 3). Briefly, the methyl carbon of acetate unit is first oxidized by a P450 enzyme or flavin monooxygenase to form an α-keto group. Then, the neighboring methyl group attacks the electrophilic keto-carbon and forms a cyclopropanone intermediate, followed by a flavin-derived peroxide reaction and a release of the carboxyl carbon as carbon dioxide. Hence, this rearrangement yields a shortened chain with a deletion of the carboxyl carbon. The Favorskii-type rearrangement, resulting in the excision of a carbon from the polyketide chain, is extremely rare in other polyketides and has only been noted in early labeling studies of the bacterial product enterocin [52], the fungal products aspyrone [53] and asperlactone [54], and the myxobacterial products ambruticin [55] and wailupemycin A [56,57]. The P450 enzyme or monooxygenase mediating Favorskii-type rearrangement in these polyketides have been identified [58,59,60]. In the cases of enterocin, aspyrone, and asperlactone, the carboxyl carbon is not completely deleted from the molecule but is retained as a carboxyl side group, whereas in ambruticin and wailupemycin A, the carboxyl group is actually lost. To date, no analogous isozymes or homologous genes mediating the Favorskii-type rearrangement of marine polyether toxins have been identified in dinoflagellates.

2.3. Carbon Deletion via Specific Functional Modules within PKS

According to the third proposed mechanism, the carbon chain is formed exactly as in normal polyketides. During the polyketide elongation process, the terminal β-keto-group is reduced to an alcohol and dehydrated to an α,β-unsaturated acid. Then, the nascent polyketide chain is attached to a special module, which contains three key enzyme domains, TE, epoxidase (EP), and decarboxylase (DC). The polyketide chain is first subjected to TE and detached from PKS, then the double bond undergoes epoxidation, and the resulting glycidic acid structure can undergo facile decarboxylation to form an aldehyde with one less carbon. If the decarboxylation occurs oxidatively, the product is a carboxylic acid with one less carbon, which, after thioesterification, can undergo further elongation [49] (Figure 4). This hypothesis seems reasonable, but it requires a special PKS module. At present, the corresponding EP and DC domains have not been identified. In addition, the extended polyketide chain needs to be dissociated from PKS, then reactivated, and connected to PKS again after decarboxylation. The related reaction and its regulatory mechanism have not yet been studied.
The three hypotheses offer clues and references for studying the dinoflagellate polyketide chain construction mechanism, among which the second proposition involving the Favorskii-type rearrangement seems the most reasonable, as this carbon-deletion process would not interrupt the nascent polyketide chain extension process, nor would it involve the detachment from and subsequent reattachment to the PKS enzyme. Obviously, this process could also take place if the chain has been released from the PKS enzyme. More definitive elucidation must be based on the investigation of genes and enzymes mediating carbon skeleton deletions, such as the FAD-dependent oxygenase, cytochrome P450, or flavin monooxygenase. In addition, more detailed isotope labeling experiments should be carried out to obtain biosynthetic information by precisely tracking the intermediate metabolites.

3. Pendant Alkylation

3.1. α-Alkylation

In the majority of bacterial and fungal polyketides, pendant methyl groups occur through the incorporation of propionate or the addition of the electrophilic methyl group of S-adenosyl methionine (SAM), catalyzed by the methyl transferase enzyme located in the polyketide biosynthetic gene cluster [61,62]. This reaction is described as α-alkylation because pendant alkylation occurs at a nucleophilic α-carbon in the polyketide chain (Figure 5A). In isotope labeling experiments of polyether compounds derived from dinoflagellates, α-alkylation could also be found. For example, there are four pendant methyl groups derived from methionine in BTX (Figure 1).

3.2. β-Alkylation

In addition to α-alkylation, there is another type of methylation, which occurs at the electrophilic β-carbon of acetate units in the polyketide chain. Isotope labeling experiments showed that pendant methyl groups were derived from the methyl carbon of acetate, and this process is called β-alkylation. Apparently, β-alkylation regularly occurs in dinoflagellate polyethers, as every dinoflagellate polyether studied to date contains at least one β-alkylation site. For example, there are three β-alkylation sites in BTX, four in OA, and two in yessotoxin (Figure 1). In addition to polyether toxins from dinoflagellates, β-alkylation has also been reported for other polyketides, such as myxobacterial compounds myxopyronin A [63] and myxovirescin A [64,65,66], cyanobacterial products curacin [67] and jamaicamide [68], and the bacterial metabolites pederin [69], bacillaene [70,71], difficidin [72], leinamycin [73,74], and mupirocin [75,76]. One β-alkylation step occurs during the synthesis of mupirocin, a metabolite of Pseudomonas aeruginosa, through an aldol condensation reaction catalyzed by 3-hydroxy-3-methylglutaryl-CoA (HMG-CoA) synthase, which was identified by gene sequencing and functional analysis. When HMG-CoA synthase is mutated, the β-alkylation reaction cannot occur, and the carbon chain cannot be extended, resulting in a truncated mutant product mupirocin H [75,76]. This finding suggests that HMG-CoA synthase is responsible for catalyzing the β-alkylation reaction. Gene sequencing showed that the gene for HMG-CoA synthase was incorporated into the polyketide biosynthetic gene cluster.
To study the β-alkylation mechanism of OA, all three hydrogen atoms in the acetate methyl carbon were labeled with deuterium (CD3). The results showed that only two deuterium isotopes were present in the pendant methyl group of OA. Therefore, it is speculated that acetate is first activated to malonate, and then malonate is condensed with the β-carbonyl site of the new carbon chain through an aldol condensation catalyzed by HMG-CoA synthase (Figure 5B) [50]. Therefore, although there is still no evidence at the molecular and genetic levels, it is reasonable to conclude that a similar mechanism involving HMG-CoA synthase, as found in various bacteria, is responsible for the β-alkylation reaction of dinoflagellate polyethers.

3.3. Pseudo α-Alkylation

It is noteworthy that five of the six methyl groups in the side chain of OA are located in the β-carbonyl site and originate from the β-alkylation reaction discussed above, while the last methyl group (C-10 position) occurs at the methyl carbon (α-carbon) of a cleaved acetate unit in the polyketide chain. Isotope labeling experiments indicated that the methyl group was derived from acetate but not from methionine. Therefore, this special type of alkylation is referred to as pseudo α-alkylation. It is presumed that the pseudo α-alkylation reaction proceeds via an acetate unit, which first undergoes the deletion of the carboxyl carbon, followed by the oxidation of the retained, methyl group to a carbonyl group. Finally, similar to the process of β-alkylation, HMG-CoA synthase catalyzes aldol condensation of the carbonyl group with activated malonate to form a methyl side chain [50]. Notably, pseudo α-alkylation is very common in the process of dinoflagellate polyether biosynthesis, and every dinoflagellate polyether studied to date contains at least one pseudo α-alkylation site (Figure 1).
Therefore, β-alkylation (including pseudo α-alkylation) is a common paradigm in dinoflagellate polyketide studies. Analysis of other β-alkylation examples and biosynthetic pathways from various bacteria showed that HMG-CoA synthase is the key enzyme catalyzing the β-alkylation reaction. Thus, transcriptome sequencing, gene probe capture techniques, and bioinformatics analysis are needed to find homologous HMG-CoA synthase genes in dinoflagellates and determine their function.

4. Polyether Ring Formation

A distinct feature of dinoflagellate polyether compounds is the presence of a number of five- to nine-membered spiral or fused polyether rings. According to their ether ring arrangement and molecular structure, dinoflagellate-derived compounds can be divided into linear, macrolide, and fused polyethers [3]. Thus, OA belongs to linear polyethers with one five-membered ring and six six-membered rings. BTXs are fused polyethers with eight six-membered rings, two seven-membered rings, and one eight-membered ring. Spirolides are macrolide polyethers with one five-membered ring and five six-membered rings (Figure 1). Based on the unique size, number, and spatial configuration of ether rings in dinoflagellate polyether compounds, which are quite different from other polyether compounds (such as polyether antibiotics), a unique mechanism of ring formation may exist in dinoflagellates.

4.1. Baldwin’s Rules for Ether Ring Formation

In order to describe the ring formation mechanism, it is necessary to understand the ring formation rules proposed by Baldwin [77], which states that the number of atoms in the ring is generally three to eight. The terms exo and endo are used to indicate the position (inside and outside the ring, respectively) of the bond broken during the ring closure in the newly formed ring. The terms tet (tetrahedral), trig (trigonal), and dig (digonal) are used to indicate the geometry of the electrophilic carbon in the ring, with tet corresponding to sp3 hybridization, trig to sp2 hybridization, and dig to sp hybridization. The rationalization of Baldwin’s ring formation rules usually has a three-dimensional electron effect. Whether the reaction is favored or disfavored is mainly determined by the molecular dynamic equilibrium, and the most advantageous type of ring formation usually follows the principle of minimum free energy. The common types of ring formation are shown in Figure 6. If the breaking position is at a carbonyl group or a double bond, and the latter is outside the ring, the condensation of the intramolecular hydroxyl group with the sp2 hybrid carbon forms an exo-trig cyclization type, which is usually favored (Figure 6A). When the double bond breaking position is inside the ring, and the ring size is 6-7, the condensation of the intramolecular hydroxyl group with the sp2 hybrid carbon represents an endo-trig cyclization type reaction, which is usually favored, but is disfavored when the ring size is 3-5 (Figure 6B). If the breaking position is at a hydroxyl group or an epoxide bond, and the latter is outside the ring, the condensation of intramolecular hydroxyl group with the sp3 hybrid carbon follows an exo-tet cyclization type reaction, which is usually favored (Figure 6C). When the epoxide bond is inside the ring, the condensation of intramolecular hydroxyl group with the sp3 hybrid carbon follows an endo-tet cyclization type reaction, which is usually disfavored (Figure 6D). Overall, the Baldwin rules for cyclization reasonably explain when polyether ring formation is thermodynamically favored or disfavored. However, enzymes are capable of overcoming kinetic barriers and catalyzing reactions in a thermodynamically disfavored direction.

4.2. Examples from Polyether Antibiotics Relevant to Polyether Formation

So far, polyether antibiotics from Streptomyces, such as monensin A, nanchangmycin, lasalocid A, and salinomycin, have been found to have the highest structural similarity to dinoflagellate polyether compounds. Polyether antibiotics are catalyzed by PKS and also contain multiple ether rings, providing some reference for studying the mechanisms of dinoflagellate ether ring formation. Based on early isotope labeling experiments, Cane and Westley proposed a possible mechanism for the biosynthesis of polyether antibiotics in 1983 [78,79,80,81]. First, acetic acid, propionic acid, or butyric acid units are selectively condensed by PKS to form acyclic polyene intermediates in the all E (trans) configuration. Then, epoxides are formed by epoxidation of double bonds, followed by the breakage and re-closure of epoxy bonds to form the characteristic ether bonds and spiral ring structures. After a series of post-modification processes, such as glycosylation, O-methylation, and hydroxylation, mature polyether antibiotics are produced. The hypothesis was later confirmed by successive discovery and analysis of several antibiotic biosynthetic gene clusters and by validation of functional genes [82,83,84,85,86,87,88,89,90]. The key genes responsible for polyether formation were discovered in all the polyether antibiotic biosynthetic gene clusters, among which epoxidases catalyze the conversion of polyene intermediates to epoxides, and epoxide hydrolases are responsible for the opening of epoxy bonds and the formation of ether rings. In the monensin A gene cluster, MonCI has the function of epoxidation, catalyzing epoxidation of the three double bonds of triene intermediates [88,89], while MonBI and MonBII are responsible for catalyzing the hydrolysis of epoxides and the formation of ether rings [91]. The ether rings are formed through 6-exo-trig and 5-exo-tet cyclization reactions, which are favored as discussed above, and conform to Baldwin’s cyclization rules (Figure 7A). In the lasalocid A biosynthetic gene cluster, Lsd18 catalyzes the epoxidation of diene intermediates [87,90], while Lsd19 catalyzes the hydrolysis of epoxides and the formation of ether rings [92]. Among the two ether rings, the first one (C18–C19 epoxy bond) is formed via a 5-exo-tet cyclization reaction, which conforms to Baldwin’s cyclization rules and is favored, but the second one (C22–C23 epoxy bond) is formed via a 6-endo-tet cyclization reaction, which is disfavored from the chemical energy standpoint, indicating a need for enzyme participation. The Oikawa team [93,94] analyzed the crystal structure of Lsd19 and its substrate binding to elucidate the catalytic mechanism. Lsd19 consists of two homologous domains, namely Lsd19A and Lsd19B. A series of site-directed mutagenesis experiments showed that Lsd19A recognizes the C18–C19 epoxy bond and catalyzes 5-exo-tet cyclization at this site. Next, Lsd19B catalyzes the opening of C22–C23 epoxy bond and formation of the six-membered ether ring via a 6-endo-tet cyclization reaction. In vitro experiments also confirmed that Lsd19 could catalyze the conversion of epoxidized lasalocid precursors to lasalocid A via 5-exo-tet and 6-endo-tet cyclization reactions, while in the absence of Lsd19, isolasalocid but not lasalocid A was obtained through two-step 5-exo-tet cyclization reactions catalyzed by trichloroacetic acid [92] (Figure 7B). Therefore, epoxide hydrolases could overcome the endo-tet cyclization reaction, which is disfavored in terms of the chemical energy, and catalyze the epoxide hydrolysis to form an ether ring.

4.3. Ether Ring Formation in OA

Although no experimental data have been reported so far elucidate the functions of epoxidases and epoxide hydrolases in dinoflagellate ether ring formation, several isotope labeling studies indicated the origin of oxygen atoms in the OA carbon skeleton and provided some clues for understanding the mechanism of OA ether ring formation (Figure 8). Needham et al. [39] used 13C and 18O isotopes to label acetate (1-13C, 18O2) and glycolic acid (2-13C, 18O), respectively, during OA biosynthesis. The results showed that the oxygens at the C-4 and C-27 positions were derived from acetate, which indicated that the carbonyl group of acetate was retained or reduced to a hydroxyl group during the condensation reaction, while the oxygen at the C-38 position was derived from glycolic acid. Murata et al. [35] used 18O isotopes to label acetate (1-18O2) and free oxygen (18O2) in OA biosynthesis. The results showed that the oxygens at the C-4, C-8, C-19, and C-27 positions were derived from acetate, while those at the other positions, except C-1 (hydroxyl group) and C-38 (oxygen), were derived from free oxygen (18O2), suggesting the involvement of hydroxylation or epoxidation reactions. Izumikawa et al. [95] used 18O-labeled water (H2O-18O) in OA biosynthesis and found that the oxygens at the C-1, C-7, C-8, C-19, C-24, C-34, and C-38 positions were labeled, indicating that the oxygens at these locations may have undergone reversible hydration with water and exchange with oxygen in water. Based on these experiments, it can be concluded that oxygens at multiple sites in OA are derived from different sources. For example, the oxygens at C-8 and C-19 positions are derived from both acetate and water. This finding indicates that carbonyl groups are formed at these positions during the extension of an acetate unit, and then the carbonyl groups undergo reversible hydration with water and exchange with oxygen in water. The oxygens at the C-1, C-7, C-24, and C-34 positions are derived from both oxygen and water, indicating that the carbons at the C-1 and C-34 positions may be first oxidized to a carbonyl group, and then reversibly hydrated with water, while the carbons at the C-7 and C-24 positions are oxidized to a hydroxyl group, and free oxygen may be generated by photosynthesis of water. Meanwhile, in addition to being derived from acetate and water, the oxygen at the C-8 position is also derived from the oxygen, which is puzzling, as it is unlikely that free oxygen is needed if the acetate unit has provided a carbonyl group. The C-38 oxygen, derived from glycolic acid, may also come from water, which is difficult to explain. Thus, these results need further experimental verification.
Nevertheless, based on the above results, it is possible to infer the mechanism of each ether ring formation in OA [96]. As shown in Figure 8, based on the intensity of 18O isotope and the composition of glycolic acid in the G ring, the ring formation proceeds in the order from G to F ring, and the G ring is the initiation ring. First, the hydroxyl group at the C-38 position attacks the carbonyl group at the C-34 position, forming the G ring via a 6-exo-trig cyclization reaction. Then, the F ring is formed via a 6-endo-trig cyclization reaction. Both steps are favored in terms of chemical energy. Next, the C, D, and E ring formation proceed in the order from right to left. As the D and E rings are fused rings, and according to isotope labeling experiments, C-19 should be a carbonyl group, while the C-22 and C-23 carbons should form an epoxy bond. First, the hydroxyl group at C-26 position attacks the epoxy bond and forms the E ring via a 6-endo-tet cyclization reaction. Then, the hydroxyl group at C-23 position attacks the carbonyl group at C-19 position via a 6-exo-trig cyclization reaction to form the D ring. Subsequently, the hydroxyl group at C-19 position attacks the hydroxyl group at C-16 position to form the C ring via a 5-exo-tet cyclization reaction. Only 6-endo-tet cyclization is disfavored, while the other two steps are favored. Finally, the order of the A and B ring formation should proceed from left to right, contrary to that of the other rings. Based on isotope labeling experiments, the C-4 oxygen is only derived from acetate, indicating the presence of a hydroxyl group at this position, while the C-8 oxygen is derived from both acetate and water, indicating the presence of a carbonyl group at this position, which suggests that the C-4 hydroxyl group attacks the carbonyl group at the C-8 position and forms the A ring via a 6-exo-trig cyclization reaction. Then, the C-8 hydroxyl group attacks the C-12 hydroxyl group and forms the B ring via a 6-exo-tet cyclization reaction. Both steps are favored in terms of chemical energy. As Figure 8 shows, there are both spiral and fused rings in the carbon skeleton of OA, and their cyclization reactions are separate and different. The spiral ring formation often follows the favored exo-trig or exo-tet route, while the fused rings are usually formed via endo-tet reactions and involve epoxy bonds. In addition, according to the mechanism of ether ring formation in polyether antibiotics, the formation of the OA polyether should also require epoxidases, which is responsible for the formation of epoxy bonds, and epoxide hydrolases, which is responsible for the opening of epoxy bonds and ring formation. Although the structure of OA is relatively simple, the diversity of its ring formation reactions provides a reference for studying the ring formation mechanism of more complex polyether compounds.

4.4. Ether Ring Formation in Fused Polyethers

The typical characteristic of more complex, fused polyether compounds is the presence of a series of fused ether rings, showing a typical syn-trans configuration. It is presumed that these ether rings are formed by continuous endo-tet cyclization of trans polyepoxides, which are produced through oxidization of all-E polyene precursors [97,98] (Figure 9A). For example, CTX has 11 continuous fused rings (A to K) and two spiral rings (L and M). It is presumed that polyether rings are first condensed by PKS and then modified through multiple steps to form a polyketide polyene precursor. Except for the first double bond, the other double bonds in the E configuration are all oxidized to form all-trans polyepoxides catalyzed by epoxidases. The polyepoxide intermediates are then cyclized by epoxide hydrolase to form 11 consecutive fused rings via successive endo-tet cyclization reactions, followed by 6-exo-trig and 5-exo-tet reactions to form the terminal spiral rings (Figure 9B). The 6-exo-trig and 5-exo-tet cyclization reactions are favored, while the 11 successive endo-tet cyclization reactions are disfavored. Vilotijevic and Jamison [99] found that polyepoxide precursors, containing an initial ether ring, could spontaneously undergo 6-endo-tet cascade cyclization in vitro in an aqueous environment with neutral pH to form the fused ring structure. Water acted as a catalyst and possibly stabilized the conformation of the ether ring through hydrogen bonds, thus facilitating the nucleophilic attack of hydroxyl groups via the 6-endo-tet route to form the ether rings, with the initiation ether ring providing the template and the hydroxyl group for nucleophilic reactions. This discovery suggests that the water molecule plays a role in promoting the activity of epoxide hydrolase for the formation of polycyclic fused ethers, resulting in the disfavored 6-endo-tet cyclization reactions.
Thus, the mechanisms of ether ring formation differ in various dinoflagellate polyether structures, such as linear, macrolide, or fused polyethers. In linear and macrolide polyethers, rings are usually 5- or 6-membered as in polyether antibiotics, and are mainly connected as a spiroketal feature, or separated by at least one single bond [3,78]. Thus, these ether rings are usually formed via the favored exo cyclization reaction and conform to Baldwin’s rules. Certainly, epoxidases and epoxide hydrolases may also be needed to catalyze specific reactions, even though these rings can be formed spontaneously from the chemical energy standpoint [88,89,90,91,92]. In the more complex fused polyethers, such as CTXs and BTXs, there are a series of successive fused ether rings, varying in size from 5- to 9-membered rings [3,4]. Thus, fused ether rings are formed via the disfavored endo-tet cyclization reaction and must rely on catalytic enzymes, such as epoxide hydrolases. Therefore, discovering and characterizing the functions of these enzymes is essential for the elucidation of the mechanisms of dinoflagellate polyether ring formation.

5. Gene Mining

The above-discussed biosynthetic mechanisms of marine polyether compounds have mostly been proposed based on the results of early isotope labeling studies, in the absence of information on genes and enzymes involved in catalytic reaction steps. As the genome sequences of dinoflagellates are very long and complex, it is difficult to uncover the biosynthesis-related genes. At present, most studies are based on transcriptome sequencing of dinoflagellates. With the rapid development of high-throughput sequencing technologies, the dinoflagellate transcriptome has been increasingly sequenced and annotated, which provides the basis for studying biosynthetic mechanisms.

5.1. New Single-Domain Type I PKS

Snyder et al. [100] amplified the KS domain gene sequences of PKS from seven dinoflagellates for the first time, using a degenerate PCR method. Three of the dinoflagellates examined are confirmed polyether producers, including the benthic dinoflagellates P. lima and P. hoffmanianum, which produce OA, and the planktonic dinoflagellate K. brevis, which produces the fused polyether BTXs. The other four strains have not been demonstrated to produce polyketides, yet they belong to polyketide-producing genera. These gene sequences determined are highly homologous to type I PKS gene sequence, as shown by bioinformatic comparative analysis. Subsequently, flow cytometry and fluorescence probe in situ hybridization techniques were used to demonstrate that two of the gene sequences were localized exclusively to K. brevis, providing further evidence that the gene sequences were derived from dinoflagellates [101]. Monroe and Van Dolah [102] identified eight full-length PKS gene sequences of K. brevis by constructing and sequencing a cDNA library and using expressed sequence tags and rapid amplification of cDNA ends techniques. Six of the sequences were single KS domain sequences, one was KR domain sequence, and the last one encoded both ACP and KS domains. Sequence alignment showed that these sequences were homologous to those of type I PKSs. Despite the sequence homology, the structure of dinoflagellate PKS differs from that of the typical type I PKSs, containing multi domains, but is similar to that of type II PKSs. Therefore, the dinoflagellate PKS characterized by the presence of single-domain structure is called the ‘new type I PKS’. Kohli et al. [103] used second generation high-throughput sequencing technology to sequence and assemble transcriptomes of two dinoflagellates (Gambierdiscus australes and G. belizeanus) producing MTXs. More than 300 type I PKS-related sequences were identified through sequence alignment analysis, including PKS (KS, KR, ER, AT, and ACP), TE, and methyltransferase genes, all of which encoded single-domain proteins. In addition, other single-domain type I PKS-related genes were identified in other dinoflagellates [104,105,106,107,108], suggesting that type I PKS with a single-domain structure may be a prominent feature of dinoflagellates.

5.2. Typical Multi-Domain Type I PKS

In addition to the discovery of type I PKS with a single-domain structure, several studies have found PKSs with multi-domain structure in dinoflagellates. Lopez-Legentil et al. [109] constructed a fosmid genomic library of the dinoflagellate K. brevis by nested PCR and cloned 18 gene sequences with the single-KS domain. Furthermore, a multi-domain NRPS-PKS hybridization sequence was identified, of which the NRPS consists of three modules, including a condensation domain, an adenylation domain, and a peptidyl carrier protein domain, while the PKS is composed of KS, AT, KR, ACP, and TE domains, suggesting that the heterozygous gene module may catalyze the synthesis of some amine-containing polyether compounds. Beedessee et al. [110] identified 25 type I PKS genes by genome and transcriptome sequencing analysis of the dinoflagellate Symbiodinium minutum, among which 15 were single-domain sequences (KS), and 10 were multi-domain modular PKS sequences, containing one NRPS-PKS hybrid sequence. Subsequently, Kohli et al. [111,112] used the second generation high-throughput sequencing technology to sequence the transcriptomes of K. brevis, G. polynesiensis, and G. excentricus. Using sequence alignment and phylogenetic analysis, hundreds of type I PKS genes were identified, including not only single-domain sequences but also multi-domain sequences. In addition, epoxidases, epoxide hydrolases, and methyltransferases were identified. These results provide a wealth of genetic information for the study of the biosynthetic mechanisms of dinoflagellate polyether compounds. Thus, with the rapid development of high-throughput sequencing technologies and the improvement of gene cloning methods, genes related to polyether biosynthesis, including PKS, are constantly being excavated in dinoflagellates. From the early discovery of genes encoding single-domain PKS to the later discovery of multi-domain modular genes, these results suggest that the structure of PKS in dinoflagellates is characterized by diversity. They have not only the typical structural characteristic of multi-domain modular type I PKS, but also the characteristic of single-domain sequence similar to type II PKS gene, which indicates that the catalytic mechanisms of dinoflagellate PKS are different from those of the two types of PKSs or may combine catalytic mechanisms of both. These findings also illustrate the complexity of the biosynthetic mechanisms of dinoflagellate polyether compounds at the genetic level and the difficulties in analyzing their biosynthetic pathways. Although a large number of PKS genes have been discovered, most of the gene sequences are incomplete, and their functions have not been characterized. The catalytic mechanisms of PKS in biosynthetic pathway are still unclear, making it necessary to study numerous enzymatic reactions in vitro, as well as to develop methods of genetic manipulation for dinoflagellates.

6. Prospect

Owing to their novel structures and unique biological activities, dinoflagellate polyethers have good prospects for drug development. These compounds also include red tide toxins, which pose a major threat to marine fisheries, environment and human health. Therefore, dinoflagellate polyethers have attracted extensive attention from researchers. On the one hand, research on the biosynthetic mechanisms can provide a basis for the development of monitoring technologies or biosensors for this kind of algal toxin. For example, fluorescent probes and gene chips can be designed for in situ, real-time, and high-throughput monitoring of specific gene sequences (KS, epoxide hydrolase, etc.). Real-time fluorescent quantitative PCR or fluorescent antibody, which are sensitive and reliable even at low toxin concentrations, can be used for detection of the expression level of functional enzymes in biosynthetic pathways, so as to give early warning and effective prevention of the growth of the poisonous algae. In addition, blocking methods can be designed for their biosynthetic pathways, such as inhibiting the activity of functional enzymes, silencing or knocking out genes related to biosynthesis, so as to control or even eliminate algae toxin production. On the other hand, studies of dinoflagellate polyethers can lay the foundations for the development of tools to study disease signaling pathways or new marine-derived drugs. Dinoflagellate polyethers can act on various ion channels and play an important role in the nervous system, thus potentially representing powerful tools for pharmacological and neuroscience research. These compounds may also have the potential for the development of new cardiovascular drugs, neurological injury treatment drugs as well as anti-cancer drugs. Through analysis of the biosynthetic mechanisms of dinoflagellate polyethers and the discovery of biosynthesis-related genes, it may be possible to reconstruct their biosynthetic pathways in heterologous hosts using metabolic engineering and synthetic biological methods and also create new compounds by inserting, deleting, or modifying PKS modules and domains.
Previous isotope labeling studies revealed the origins of carbon and oxygen atoms in the carbon skeleton of several dinoflagellate polyether compounds. Subsequently, numerous PKS genes were identified through gene cloning and transcriptome sequencing, which further confirmed that dinoflagellate polyether compounds were produced through biosynthetic pathways catalyzed by PKS. However, due to the lack of mature genetic manipulation tools, gene function characterization, and genome sequencing, the specific biosynthetic mechanisms of dinoflagellate polyether compounds, including carbon skeleton deletion, pendant alkylation, and polyether ring formation, are still unclear, instead, remain speculations based on their structures and available isotope labeling experimental data. Therefore, it is of prime importance to develop approaches to the genetic manipulation of dinoflagellates, in combination with more advanced sequencing technologies, to allow deeper insights into their genomes, as well as the acquisition of more complete information on biosynthesis-related genes and enzymes, such as monooxygenases, HMG-CoA synthases, epoxidases, epoxide hydrolases, and methyltransferases. At the same time, in vitro experiments should be carried out to identify the genes and characterize the functions of key enzymes or other proteins involved in the biosynthetic pathways. In addition, more information can be learned about the biosynthetic mechanisms of dinoflagellate polyether compounds from studies of other polyketide compounds, especially polyether antibiotics, which will be beneficial for understanding the more complex biosynthetic mechanisms of dinoflagellate polyether compounds.

Author Contributions

All authors contributed substantially to the preparation of this review. X.W. and G.Y. drafted the manuscript. Y.L., J.C. and H.J. edited and revised the manuscript. All authors approved the manuscript in its current form.

Funding

This research received no external funding.

Acknowledgments

We would like to thank Editage (www.editage.cn) for English language editing.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Nicolaou, K.C.; Frederick, M.O.; Aversa, R.J. The continuing saga of the marine polyether biotoxins. Angew. Chem. Int. Ed. Engl. 2008, 47, 7182–7225. [Google Scholar] [CrossRef] [PubMed]
  2. Assunção, J.; Guedes, A.; Malcata, F. Biotechnological and Pharmacological Applications of Biotoxins and Other Bioactive Molecules from Dinoflagellates. Mar. Drugs 2017, 15, 393. [Google Scholar] [CrossRef] [PubMed]
  3. Rasmussen, S.A.; Andersen, A.J.C.; Andersen, N.G.; Nielsen, K.F.; Hansen, P.J.; Larsen, T.O. Chemical Diversity, Origin, and Analysis of Phycotoxins. J. Nat. Prod. 2016, 79, 662–673. [Google Scholar] [CrossRef] [Green Version]
  4. Ajani, P.; Harwood, D.; Murray, S. Recent Trends in Marine Phycotoxins from Australian Coastal Waters. Mar. Drugs 2017, 15, 33. [Google Scholar] [CrossRef] [PubMed]
  5. Tamele, I.; Silva, M.; Vasconcelos, V. The Incidence of Marine Toxins and the Associated Seafood Poisoning Episodes in the African Countries of the Indian Ocean and the Red Sea. Toxins 2019, 11, 58. [Google Scholar] [CrossRef] [PubMed]
  6. Morabito, S.; Silvestro, S.; Faggio, C. How the marine biotoxins affect human health. Nat. Prod. Res. 2017, 32, 621–631. [Google Scholar] [CrossRef]
  7. Farabegoli, F.; Blanco, L.; Rodríguez, L.; Vieites, J.; Cabado, A. Phycotoxins in Marine Shellfish: Origin, Occurrence and Effects on Humans. Mar. Drugs 2018, 16, 188. [Google Scholar] [CrossRef]
  8. Landsberg, J.; Flewelling, L.; Naar, J. Karenia brevis red tides, brevetoxins in the food web, and impacts on natural resources: Decadal advancements. Harmful Algae 2009, 8, 598–607. [Google Scholar] [CrossRef]
  9. Fleming, L.E.; Kirkpatrick, B.; Backer, L.C.; Walsh, C.J.; Nierenberg, K.; Clark, J.; Reich, A.; Hollenbeck, J.; Benson, J.; Cheng, Y.S.; et al. Review of Florida red tide and human health effects. Harmful Algae 2011, 10, 224–233. [Google Scholar] [CrossRef] [Green Version]
  10. Baden, D.G.; Bourdelais, A.J.; Jacocks, H.; Michelliza, S.; Naar, J. Natural and Derivative Brevetoxins: Historical Background, Multiplicity, and Effects. Environ. Health. Perspect. 2005, 113, 621–625. [Google Scholar] [CrossRef]
  11. Poli, M.; Mende, T.J.; Baden, D.G. Brevetoxins, unique activators of voltage-sensitive sodium channels, bind to specific sites in rat brain synaptosomes. Mol. Pharmacol. 1986, 30, 129–135. [Google Scholar] [PubMed]
  12. Holmes, M. The origin of ciguatera—An update. Ciguatera Inf. Bull. Noumea 1992, 2, 8–9. [Google Scholar]
  13. Lombet, A.; Bidard, J.N.; Lazdunski, M. Ciguatoxin and brevetoxins share a common receptor site on the neuronal voltage-dependent Na+ channel. FEBS. Lett. 1987, 219, 355–359. [Google Scholar] [CrossRef]
  14. Crump, J.A.; McLay, C.L.; Chambers, S.T. Ciguatera fish poisoning. Postgrad. Med. J. 1999, 75, 678–679. [Google Scholar] [CrossRef]
  15. Lehane, L.; Lewis, R.J. Ciguatera: Recent advances but the risk remains. Int. J. Food. Microbiol. 2000, 61, 91–125. [Google Scholar] [CrossRef]
  16. Friedman, M.; Fernandez, M.; Backer, L.; Dickey, R.; Bernstein, J.; Schrank, K.; Kibler, S.; Stephan, W.; Gribble, M.; Bienfang, P. An updated review of ciguatera fish poisoning: Clinical, epidemiological, environmental, and public health management. Mar. Drugs 2017, 15, 72. [Google Scholar] [CrossRef]
  17. Alexander, J.; Audunsson, G.; Benford, D.; Cockburn, A.; Cradevi, J.; Dogliotti, E.; Domenico, A.; Fernandez-Cruz, M.; Fink-Gremmels, J.; Furst, P. Marine biotoxins in shellfish-okadaic acid and analogues. EFSA J. 2008, 589, 1–62. [Google Scholar]
  18. Cetinkaya, F.; Mus, T.E. Shellfish Poisoning and Toxins. J. Biol. Environ. Sci. 2012, 6, 115–119. [Google Scholar]
  19. Reguera, B.; Riobó, P.; Rodríguez, F.; Díaz, P.; Pizarro, G.; Paz, B.; Franco, J.; Blanco, J. Dinophysis toxins: Causative organisms, distribution and fate in shellfish. Mar. Drugs 2014, 12, 394–461. [Google Scholar] [CrossRef]
  20. George, J.; Baden, D.G.; Gerwick, W.H.; Murray, T.F. Bidirectional influence of sodium channel activation on NMDA receptor–dependent cerebrocortical neuron structural plasticity. Proc. Natl. Acad. Sci. USA 2012, 109, 19840–19845. [Google Scholar] [CrossRef]
  21. Kamat, P.K.; Rai, S.; Swarnkar, S.; Shukla, R.; Nath, C. Molecular and cellular mechanism of okadaic acid (OKA)-induced neurotoxicity: A novel tool for Alzheimer’s disease therapeutic application. Mol. Neurobiol. 2014, 50, 852–865. [Google Scholar] [CrossRef] [PubMed]
  22. Koehler, D.; Shah, Z.A.; Williams, F.E. The GSK3β inhibitor, TDZD-8, rescues cognition in a zebrafish model of okadaic acid-induced Alzheimer’s disease. Neurochem. Int. 2019, 122, 31–37. [Google Scholar] [CrossRef] [PubMed]
  23. Koehler, D.; Williams, F.E. Utilizing zebrafish and okadaic acid to study Alzheimer’s disease. Neural Regen. Res. 2018, 13, 1538. [Google Scholar] [PubMed]
  24. Wang, R.; Lv, L.; Zhao, Y.; Yang, N. Okadaic acid inhibits cell multiplication and induces apoptosis in a549 cells, a human lung adenocarcinoma cell line. Int. J. Clin. Exp. Med. 2014, 7, 2025. [Google Scholar] [PubMed]
  25. Ferron, P.J.; Hogeveen, K.; Fessard, V.; Hégarat, L. Comparative analysis of the cytotoxic effects of okadaic acid-group toxins on human intestinal cell lines. Mar. Drugs 2014, 12, 4616–4634. [Google Scholar] [CrossRef] [PubMed]
  26. Chae, H.D.; Choi, T.S.; Kim, B.M.; Jung, J.H.; Bang, Y.J.; Shin, D.Y. Oocyte-based screening of cytokinesis inhibitors and identification of pectenotoxin-2 that induces Bim/Bax-mediated apoptosis in p53-deficient tumors. Oncogene 2005, 24, 4813. [Google Scholar] [CrossRef]
  27. Park, S.S.; Park, S.K.; Lim, J.H.; Choi, Y.H.; Kim, W.J.; Moon, S.K. Esculetin inhibits cell proliferation through the Ras/ERK1/2 pathway in human colon cancer cells. Oncol. Rep. 2011, 25, 223–230. [Google Scholar]
  28. Kim, G.Y.; Kim, W.J.; Choi, Y.H. Pectenotoxin-2 from marine sponges: A potential anti-cancer agent—A review. Mar. Drugs 2011, 9, 2176–2187. [Google Scholar] [CrossRef]
  29. Wisecaver, J.H.; Hackett, J.D. Dinoflagellate genome evolution. Annu. Rev. Microbiol. 2011, 65, 369–387. [Google Scholar] [CrossRef]
  30. Weissman, K.J. Introduction to polyketide biosynthesis. Methods Enzymol. 2009, 459, 3–16. [Google Scholar]
  31. Kohli, G.S.; John, U.; Van Dolah, F.M.; Murray, S.A. Evolutionary distinctiveness of fatty acid and polyketide synthesis in eukaryotes. ISME J. 2016, 10, 1877. [Google Scholar] [CrossRef] [PubMed]
  32. Lee, M.S.; Repeta, D.J.; Nakanishi, K.; Zagorski, M.G. Biosynthetic origins and assignments of carbon 13 NMR peaks of brevetoxin B. J. Am. Chem. Soc. 1986, 108, 7855–7856. [Google Scholar] [CrossRef] [PubMed]
  33. Chou, H.N.; Shimizu, Y. Biosynthesis of brevetoxins. Evidence for the mixed origin of the backbone carbon chain and possible involvement of dicarboxylic acids. J. Am. Chem. Soc. 1987, 109, 2184–2185. [Google Scholar] [CrossRef]
  34. Lee, M.S.; Qin, G.; Nakanishi, K.; Zagorski, M.G. Biosynthetic studies of brevetoxins, potent neurotoxins produced by the dinoflagellate Gymnodinium breve. J. Am. Chem. Soc. 1989, 111, 6234–6241. [Google Scholar] [CrossRef]
  35. Murata, M.; Izumikawa, M.; Tachibana, K.; Fujita, T.; Naoki, H. Labeling pattern of okadaic acid from 18O2 and [18O2] acetate elucidated by collision-induced dissociation tandem mass spectrometry. J. Am. Chem. Soc. 1998, 120, 147–151. [Google Scholar] [CrossRef]
  36. Norte, M.; Padilla, A.; Fernández, J.J. Studies on the biosynthesis of the polyether marine toxin dinophysistoxin-1 (DTX-1). Tetrahedron Lett. 1994, 35, 1441–1444. [Google Scholar] [CrossRef]
  37. Needham, J.; McLachlan, J.L.; Walter, J.A.; Wright, J.L.C. Biosynthetic origin of C-37 and C-38 in the polyether toxins okadaic acid and dinophysistoxin-1. J. Chem. Soc. Chem. Commun. 1994, 22, 2599–2600. [Google Scholar] [CrossRef]
  38. Norte, M.; Padilla, A.; Fernández, J.J.; Souto, M.L. Structural determination and biosynthetic origin of two ester derivatives of okadaic acid isolated from Prorocentrum lima. Tetrahedron 1994, 50, 9175–9180. [Google Scholar] [CrossRef]
  39. Needham, J.; Hu, T.; McLachlan, J.L.; Walter, J.A.; Wright, J.L. Biosynthetic studies of the DSP toxin DTX-4 and an okadaic acid diol ester. J. Chem. Soc. Chem. Commun. 1995, 1623–1624. [Google Scholar] [CrossRef]
  40. Vilches, T.S.; Norte, M.; Daranas, A.H.; Fernández, J.J. Biosynthetic studies on water-soluble derivative 5c (DTX5c). Mar. Drugs 2012, 10, 2234–2245. [Google Scholar] [CrossRef]
  41. Murakami, M.; Okita, Y.; Matsuda, H.; Okino, T.; Yamaguchi, K. From the dinoflagellate Alexandrium hiranoi. Phytochemistry 1998, 48, 85–88. [Google Scholar] [CrossRef]
  42. Houdai, T.; Matsuoka, S.; Murata, M.; Satake, M.; Ota, S.; Oshima, Y.; Rhodes, L.L. Acetate labeling patterns of dinoflagellate polyketides, amphidinols 2, 3 and 4. Tetrahedron 2001, 57, 5551–5555. [Google Scholar] [CrossRef]
  43. Meng, Y.; Van Wagoner, R.M.; Misner, I.; Tomas, C.; Wright, J.L. Structure and biosynthesis of amphidinol 17, a hemolytic compound from Amphidinium carterae. J. Nat. Prod. 2010, 73, 409–415. [Google Scholar] [CrossRef] [PubMed]
  44. Kobayashi, J.; Tsuda, M. Amphidinolides, bioactive macrolides from symbiotic marine dinoflagellates. Nat. Prod. Rep. 2004, 21, 77–93. [Google Scholar] [CrossRef] [PubMed]
  45. Kobayashi, J. Amphidinolides and its related macrolides from marine dinoflagellates. J. Antibiot. 2008, 61, 271. [Google Scholar] [CrossRef]
  46. Yamazaki, M.; Tachibana, K.; Satake, M. Complete 13C-labeling pattern of yessotoxin a marine ladder-frame polyether. Tetrahedron 2011, 67, 877–880. [Google Scholar] [CrossRef]
  47. Yamazaki, M.; Izumikawa, M.; Tachibana, K.; Satake, M.; Itoh, Y.; Hashimoto, M. Origins of oxygen atoms in a marine ladder-frame polyether: Evidence of monooxygenation by 18O-labeling and using tandem mass spectrometry. J. Org. Chem. 2012, 77, 4902–4906. [Google Scholar] [CrossRef]
  48. MacKinnon, S.L.; Cembella, A.D.; Burton, I.W.; Lewis, N.; LeBlanc, P.; Walter, J.A. Biosynthesis of 13-Desmethyl Spirolide C by the Dinoflagellate Alexandrium ostenfeldii. J. Org. Chem. 2006, 71, 8724–8731. [Google Scholar] [CrossRef]
  49. Shimizu, Y. Microalgal metabolites. Curr. Opin. Microbiol. 2003, 6, 236–243. [Google Scholar] [CrossRef]
  50. Wright, J.L.; Hu, T.; McLachlan, J.; Needham, J.; Walter, J. Biosynthesis of DTX-4: Confirmation of a polyketide pathway, proof of a baeyer-villiger oxidation step, and evidence for an unusual carbon deletion process. J. Am. Chem. Soc. 1996, 118, 8757–8758. [Google Scholar] [CrossRef]
  51. Macpherson, G.R.; Burton, I.W.; LeBlanc, P.; Walter, J.A.; Wright, J.L. Studies of the Biosynthesis of DTX-5a and DTX-5b by the Dinoflagellate Prorocentrum maculosum: Regiospecificity of the Putative Baeyer−Villigerase and Insertion of a Single Amino Acid in a Polyketide Chain. J. Org. Chem. 2003, 68, 1659–1664. [Google Scholar] [CrossRef] [PubMed]
  52. Seto, H.; Sato, T.; Urano, S.; Uzawa, J.; Yonehara, H. Utilization of 13C-13C coupling in structural and biosynthetic studies. VII1) the structure and biosynthesis of vulgamycin. Tetrahedron Lett. 1976, 17, 4367–4370. [Google Scholar] [CrossRef]
  53. Simpson, T.J.; Holker, J.S. The biosynthesis of a pyrone metabolite of Aspergillus melleus an application of long-range 13C-13C coupling constants. Tetrahedron Lett. 1975, 16, 4693–4696. [Google Scholar] [CrossRef]
  54. Brereton, R.G.; Garson, M.J.; Staunton, J. Biosynthesis of fungal metabolites: Asperlactone and its relationship to other metabolites of Aspergillus melleus. J. Chem. Soc. Perkin Trans. 1984, 1027–1033. [Google Scholar] [CrossRef]
  55. Reichenbach, H.; Höfle, G. Biologically active secondary metabolites from myxobacteria. Biotechnol. Adv. 1993, 11, 219–277. [Google Scholar] [CrossRef]
  56. Piel, J.; Hertweck, C.; Shipley, P.R.; Hunt, D.M.; Newman, M.S.; Moore, B.S. Cloning, sequencing and analysis of the enterocin biosynthesis gene cluster from the marine isolate ‘Streptomyces maritimus’: Evidence for the derailment of an aromatic polyketide synthase. Chem. Biol. 2000, 7, 943–955. [Google Scholar] [CrossRef]
  57. Xiang, L.; Kalaitzis, J.A.; Nilsen, G.; Chen, L.; Moore, B.S. Mutational analysis of the enterocin Favorskii biosynthetic rearrangement. Org. Lett. 2002, 4, 957–960. [Google Scholar] [CrossRef]
  58. Xiang, L.; Kalaitzis, J.A.; Moore, B.S. EncM, a versatile enterocin biosynthetic enzyme involved in Favorskii oxidative rearrangement, aldol condensation, and heterocycle-forming reactions. Proc. Natl. Acad. Sci. USA 2004, 101, 15609–15614. [Google Scholar] [CrossRef] [Green Version]
  59. Walsh, C.T.; Wencewicz, T.A. Flavoenzymes: Versatile catalysts in biosynthetic pathways. Nat. Prod. Rep. 2013, 30, 175–200. [Google Scholar] [CrossRef]
  60. Julien, B.; Tian, Z.Q.; Reid, R.; Reeves, C.D. Analysis of the ambruticin and jerangolid gene clusters of Sorangium cellulosum reveals unusual mechanisms of polyketide biosynthesis. Chem. Biol. 2006, 13, 1277–1286. [Google Scholar] [CrossRef]
  61. Liu, T.; Cane, D.E.; Deng, Z. The enzymology of polyether biosynthesis. Methods Enzymol. 2009, 459, 187–214. [Google Scholar] [PubMed]
  62. Herbst, D.A.; Townsend, C.A.; Maier, T. The architectures of iterative type I PKS and FAS. Nat. Prod. Rep. 2018, 35, 1046–1069. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  63. Kohl, W.; Irschik, H.; Reichenbach, H.; Höfle, G. Antibiotika aus gleitenden bakterien, XXII. Die biosynthese des antibiotikums myxopyronin A aus myxococcus fulvus stamm Mx f50. Liebigs. Ann. Chem. 1984, 1984, 1088–1093. [Google Scholar] [CrossRef]
  64. Simunovic, V.; Zapp, J.; Rachid, S.; Krug, D.; Meiser, P.; Müller, R. Myxovirescin A Biosynthesis is Directed by Hybrid Polyketide Synthases/Nonribosomal Peptide Synthetase, 3-Hydroxy-3-Methylglutaryl-CoA Synthases, and trans-Acting Acyltransferases. ChemBioChem 2006, 7, 1206–1220. [Google Scholar] [CrossRef] [PubMed]
  65. Calderone, C.T.; Iwig, D.F.; Dorrestein, P.C.; Kelleher, N.L.; Walsh, C.T. Incorporation of nonmethyl branches by isoprenoid-like logic: Multiple β-alkylation events in the biosynthesis of myxovirescin A1. Chem. Biol 2007, 14, 835–846. [Google Scholar] [CrossRef]
  66. Simunovic, V.; Müller, R. 3-Hydroxy-3-methylglutaryl-CoA-like synthases direct the formation of methyl and ethyl side groups in the biosynthesis of the antibiotic myxovirescin A. ChemBioChem 2007, 8, 497–500. [Google Scholar] [CrossRef]
  67. Chang, Z.; Sitachitta, N.; Rossi, J.V.; Roberts, M.A.; Flatt, P.M.; Jia, J.; Sherman, D.H.; Gerwick, W.H. Biosynthetic Pathway and Gene Cluster Analysis of Curacin A, an Antitubulin Natural Product from the Tropical Marine Cyanobacterium Lyngbya m ajuscula. J. Nat. Prod. 2004, 67, 1356–1367. [Google Scholar] [CrossRef]
  68. Edwards, D.J.; Marquez, B.L.; Nogle, L.M.; McPhail, K.; Goeger, D.E.; Roberts, M.A.; Gerwick, W.H. Structure and biosynthesis of the jamaicamides, new mixed polyketide-peptide neurotoxins from the marine cyanobacterium Lyngbya majuscula. Chem. Biol. 2004, 11, 817–833. [Google Scholar] [CrossRef]
  69. Piel, J. A polyketide synthase-peptide synthetase gene cluster from an uncultured bacterial symbiont of Paederus beetles. Proc. Natl. Acad. Sci. USA 2002, 99, 14002–14007. [Google Scholar] [CrossRef]
  70. Calderone, C.T.; Kowtoniuk, W.E.; Kelleher, N.L.; Walsh, C.T.; Dorrestein, P.C. Convergence of isoprene and polyketide biosynthetic machinery: Isoprenyl-S-carrier proteins in the pksX pathway of Bacillus subtilis. Proc. Natl. Acad. Sci. USA 2006, 103, 8977–8982. [Google Scholar] [CrossRef]
  71. Butcher, R.A.; Schroeder, F.C.; Fischbach, M.A.; Straight, P.D.; Kolter, R.; Walsh, C.T.; Clardy, J. The identification of bacillaene, the product of the PksX megacomplex in Bacillus subtilis. Proc. Natl. Acad. Sci. USA 2007, 104, 1506–1509. [Google Scholar] [CrossRef]
  72. Chen, X.H.; Vater, J.; Piel, J.; Franke, P.; Scholz, R.; Schneider, K.; Koumoutsi, A.; Hitzeroth, G.; Grammel, N.; Strittmatter, A.W. Structural and functional characterization of three polyketide synthase gene clusters in Bacillus amyloliquefaciens FZB 42. J. Bacteriol. 2006, 188, 4024–4036. [Google Scholar] [CrossRef]
  73. Liu, T.; Huang, Y.; Shen, B. Bifunctional acyltransferase/decarboxylase LnmK as the missing link for β-alkylation in polyketide biosynthesis. J. Am. Chem. Soc. 2009, 131, 6900–6901. [Google Scholar] [CrossRef] [PubMed]
  74. Huang, Y.; Huang, S.X.; Ju, J.; Tang, G.; Liu, T.; Shen, B. Characterization of the lnmKLM genes unveiling key intermediates for β-alkylation in leinamycin biosynthesis. Org. Lett. 2010, 13, 498–501. [Google Scholar] [CrossRef] [PubMed]
  75. El-Sayed, A.K.; Hothersall, J.; Cooper, S.M.; Stephens, E.; Simpson, T.J.; Thomas, C.M. Characterization of the mupirocin biosynthesis gene cluster from Pseudomonas fluorescens NCIMB 10586. Chem. Biol. 2003, 10, 419–430. [Google Scholar] [CrossRef]
  76. Gurney, R.; Thomas, C.M. Mupirocin: Biosynthesis, special features and applications of an antibiotic from a Gram-negative bacterium. Appl. Microbiol. Biotechnol. 2011, 90, 11–21. [Google Scholar] [CrossRef] [PubMed]
  77. Baldwin, J.E. Rules for ring closure. J. Chem. Soc. Chem. Commun. 1976, 734–736. [Google Scholar] [CrossRef]
  78. Day, L.; Chamberlin, J.; Gordee, E.; Chen, S.; Gorman, M.; Hamill, R.; Ness, T.; Weeks, R.; Stroshane, R. Biosynthesis of monensin. Antimicrob. Agents Chemother. 1973, 4, 410–414. [Google Scholar] [CrossRef]
  79. Cane, D.E.; Hubbard, B.R. Polyether biosynthesis. 3. Origin of the carbon skeleton and oxygen atoms of lenoremycin. J. Am. Chem. Soc. 1987, 109, 6533–6535. [Google Scholar] [CrossRef]
  80. Cane, D.E.; Liang, T.C.; Hasler, H. Polyether biosynthesis. Origin of the oxygen atoms of monensin A. J. Am. Chem. Soc. 1981, 103, 5962–5965. [Google Scholar] [CrossRef]
  81. Cane, D.E.; Liang, T.C.; Hasler, H. Polyether biosynthesis. 2. Origin of the oxygen atoms of monensin A. J. Am. Chem. Soc. 1982, 104, 7274–7281. [Google Scholar] [CrossRef]
  82. Sun, Y.; Zhou, X.; Dong, H.; Tu, G.; Wang, M.; Wang, B.; Deng, Z. A complete gene cluster from Streptomyces nanchangensis NS3226 encoding biosynthesis of the polyether ionophore nanchangmycin. Chem. Biol. 2003, 10, 431–441. [Google Scholar] [CrossRef]
  83. Leadlay, P.; Staunton, J.; Oliynyk, M.; Bisang, C.; Cortes, J.; Frost, E.; Hughes-Thomas, Z.; Jones, M.; Kendrew, S.; Lester, J. Engineering of complex polyketide biosynthesis—Insights from sequencing of the monensin biosynthetic gene cluster. J. Ind. Microbiol. Biotechnol. 2001, 27, 360–367. [Google Scholar] [CrossRef] [PubMed]
  84. Harvey, B.M.; Mironenko, T.; Sun, Y.; Hong, H.; Deng, Z.; Leadlay, P.F.; Weissman, K.J.; Haydock, S.F. Insights into polyether biosynthesis from analysis of the nigericin biosynthetic gene cluster in Streptomyces sp. DSM4137. Chem. Biol. 2007, 14, 703–714. [Google Scholar] [CrossRef]
  85. Demydchuk, Y.; Sun, Y.; Hong, H.; Staunton, J.; Spencer, J.B.; Leadlay, P.F. Analysis of the tetronomycin gene cluster: Insights into the biosynthesis of a polyether tetronate antibiotic. ChemBioChem 2008, 9, 1136–1145. [Google Scholar] [CrossRef]
  86. Smith, L.; Hong, H.; Spencer, J.B.; Leadlay, P.F. Analysis of specific mutants in the lasalocid gene cluster: Evidence for enzymatic catalysis of a disfavoured polyether ring closure. ChemBioChem 2008, 9, 2967–2975. [Google Scholar] [CrossRef]
  87. Migita, A.; Watanabe, M.; Hirose, Y.; Watanabe, K.; Tokiwano, T.; Kinashi, H.; Oikawa, H. Identification of a gene cluster of polyether antibiotic lasalocid from Streptomyces lasaliensis. Biosci. Biotechnol. Biochem. 2009, 73, 169–176. [Google Scholar] [CrossRef]
  88. Oliynyk, M.; Stark, C.B.; Bhatt, A.; Jones, M.A.; Hughes-Thomas, Z.A.; Wilkinson, C.; Oliynyk, Z.; Demydchuk, Y.; Staunton, J.; Leadlay, P.F. Analysis of the biosynthetic gene cluster for the polyether antibiotic monensin in Streptomyces cinnamonensis and evidence for the role of monB and monC genes in oxidative cyclization. Mol. Microbiol. 2003, 49, 1179–1190. [Google Scholar] [CrossRef]
  89. Bhatt, A.; Stark, C.B.; Harvey, B.M.; Gallimore, A.R.; Demydchuk, Y.A.; Spencer, J.B.; Staunton, J.; Leadlay, P.F. Accumulation of an E, E, E-triene by the monensin-producing polyketide synthase when oxidative cyclization is blocked. Angew. Chem. Int. Ed. Engl. 2005, 44, 7075–7078. [Google Scholar] [CrossRef]
  90. Minami, A.; Shimaya, M.; Suzuki, G.; Migita, A.; Shinde, S.S.; Sato, K.; Watanabe, K.; Tamura, T.; Oguri, H.; Oikawa, H. Sequential enzymatic epoxidation involved in polyether lasalocid biosynthesis. J. Am. Chem. Soc. 2012, 134, 7246–7249. [Google Scholar] [CrossRef]
  91. Gallimore, A.R.; Stark, C.B.; Bhatt, A.; Harvey, B.M.; Demydchuk, Y.; Bolanos-Garcia, V.; Fowler, D.J.; Staunton, J.; Leadlay, P.F.; Spencer, J.B. Evidence for the role of the monB genes in polyether ring formation during monensin biosynthesis. Chem. Biol. 2006, 13, 453–460. [Google Scholar] [CrossRef] [PubMed]
  92. Shichijo, Y.; Migita, A.; Oguri, H.; Watanabe, M.; Tokiwano, T.; Watanabe, K.; Oikawa, H. Epoxide hydrolase Lsd19 for polyether formation in the biosynthesis of lasalocid A: Direct experimental evidence on polyene-polyepoxide hypothesis in polyether biosynthesis. J. Am. Chem. Soc. 2008, 130, 12230–12231. [Google Scholar] [CrossRef] [PubMed]
  93. Minami, A.; Migita, A.; Inada, D.; Hotta, K.; Watanabe, K.; Oguri, H.; Oikawa, H. Enzymatic epoxide-opening cascades catalyzed by a pair of epoxide hydrolases in the ionophore polyether biosynthesis. Org. Lett. 2011, 13, 1638–1641. [Google Scholar] [CrossRef] [PubMed]
  94. Hotta, K.; Chen, X.; Paton, R.S.; Minami, A.; Li, H.; Swaminathan, K.; Mathews, I.I.; Watanabe, K.; Oikawa, H.; Houk, K.N. Enzymatic catalysis of anti-Baldwin ring closure in polyether biosynthesis. Nature 2012, 483, 355. [Google Scholar] [CrossRef]
  95. Izumikawa, M.; Murata, M.; Tachibana, K.; Fujita, T.; Naoki, H. 18O-Labelling pattern of okadaic acid from H218O in dinoflagellate Prorocentrum lima elucidated by tandem mass spectrometry. Eur. J. Biochem. 2000, 267, 5179–5183. [Google Scholar] [CrossRef]
  96. Van Wagoner, R.M.; Satake, M.; Wright, J.L. Polyketide biosynthesis in dinoflagellates: What makes it different? Nat. Prod. Rep. 2014, 31, 1101–1137. [Google Scholar] [CrossRef]
  97. Gallimore, A.R.; Spencer, J.B. Stereochemical uniformity in marine polyether ladders - Implications for the biosynthesis and structure of maitotoxin. Angew. Chem. Int. Ed. Engl. 2006, 45, 4406–4413. [Google Scholar] [CrossRef]
  98. Nakanishi, K. The chemistry of brevetoxins: A review. Toxicon 1985, 23, 473–479. [Google Scholar] [CrossRef]
  99. Vilotijevic, I.; Jamison, T.F. Epoxide-opening cascades promoted by water. Science. 2007, 317, 1189–1192. [Google Scholar] [CrossRef]
  100. Snyder, R.; Gibbs, P.; Palacios, A.; Abiy, L.; Dickey, R.; Lopez, J.V.; Rein, K. Polyketide synthase genes from marine dinoflagellates. Mar. Biotechnol. 2003, 5, 1–12. [Google Scholar]
  101. Snyder, R.V.; Guerrero, M.A.; Sinigalliano, C.D.; Winshell, J.; Perez, R.; Lopez, J.V.; Rein, K.S. Localization of polyketide synthase encoding genes to the toxic dinoflagellate Karenia brevis. Phytochemistry 2005, 66, 1767–1780. [Google Scholar] [CrossRef] [PubMed]
  102. Monroe, E.A.; Van Dolah, F.M. The toxic dinoflagellate Karenia brevis encodes novel type I-like polyketide synthases containing discrete catalytic domains. Protist 2008, 159, 471–482. [Google Scholar] [CrossRef] [PubMed]
  103. Kohli, G.S.; John, U.; Figueroa, R.I.; Rhodes, L.L.; Harwood, D.T.; Groth, M.; Bolch, C.J.; Murray, S.A. Polyketide synthesis genes associated with toxin production in two species of Gambierdiscus (Dinophyceae). BMC Genom. 2015, 16, 410. [Google Scholar] [CrossRef] [PubMed]
  104. Eichholz, K.; Beszteri, B.; John, U. Putative monofunctional type I polyketide synthase units: A dinoflagellate-specific feature? PLoS ONE 2012, 7, e48624. [Google Scholar] [CrossRef] [PubMed]
  105. Salcedo, T.; Upadhyay, R.J.; Nagasaki, K.; Bhattacharya, D. Dozens of toxin-related genes are expressed in a nontoxic strain of the dinoflagellate Heterocapsa circularisquama. Mol. Biol. Evol. 2012, 29, 1503–1506. [Google Scholar] [CrossRef]
  106. Pawlowiez, R.; Morey, J.; Darius, H.; Chinain, M.; Van Dolah, F. Transcriptome sequencing reveals single domain Type I-like polyketide synthases in the toxic dinoflagellate Gambierdiscus polynesiensis. Harmful Algae 2014, 36, 29–37. [Google Scholar] [CrossRef]
  107. Kimura, K.; Okuda, S.; Nakayama, K.; Shikata, T.; Takahashi, F.; Yamaguchi, H.; Skamoto, S.; Yamaguchi, M.; Tomaru, Y. RNA sequencing revealed numerous polyketide synthase genes in the harmful dinoflagellate Karenia mikimotoi. PLoS ONE 2015, 10, e0142731. [Google Scholar] [CrossRef]
  108. Meyer, J.M.; Rödelsperger, C.; Eichholz, K.; Tillmann, U.; Cembella, A.; McGaughran, A.; John, U. Transcriptomic characterisation and genomic glimps into the toxigenic dinoflagellate Azadinium spinosum, with emphasis on polykeitde synthase genes. BMC Genom. 2015, 16, 27. [Google Scholar] [CrossRef]
  109. López-Legentil, S.; Song, B.; DeTure, M.; Baden, D.G. Characterization and localization of a hybrid non-ribosomal peptide synthetase and polyketide synthase gene from the toxic dinoflagellate Karenia brevis. Mar. Biotechnol. 2010, 12, 32–41. [Google Scholar] [CrossRef]
  110. Beedessee, G.; Hisata, K.; Roy, M.C.; Satoh, N.; Shoguchi, E. Multifunctional polyketide synthase genes identified by genomic survey of the symbiotic dinoflagellate, Symbiodinium minutum. BMC Genom. 2015, 16, 941. [Google Scholar] [CrossRef]
  111. Van Dolah, F.M.; Kohli, G.S.; Morey, J.S.; Murray, S.A. Both modular and single-domain Type I polyketide synthases are expressed in the brevetoxin-producing dinoflagellate, Karenia brevis (Dinophyceae). J. Phycol. 2017, 53, 1325–1339. [Google Scholar] [CrossRef] [PubMed]
  112. Kohli, G.S.; Campbell, K.; John, U.; Smith, K.F.; Fraga, S.; Rhodes, L.L.; Murray, S.A. Role of Modular Polyketide Synthases in the Production of Polyether Ladder Compounds in Ciguatoxin-Producing Gambierdiscus polynesiensis and G. excentricus (Dinophyceae). J. Eukaryot. Microbiol. 2017, 64, 691–706. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Isotope distribution in some marine polyether toxins following incorporation of 13C-labeled acetate, methionine, and glycolate. The carbon backbone contains intact acetate units as well as ones that have been cleaved within the chain. The pendant methyl groups are either derived from S-adenosyl methionine (SAM) or from acetate by the 3-hydroxy-3-methylglutaryl-CoA (HMG-CoA) pathway.
Figure 1. Isotope distribution in some marine polyether toxins following incorporation of 13C-labeled acetate, methionine, and glycolate. The carbon backbone contains intact acetate units as well as ones that have been cleaved within the chain. The pendant methyl groups are either derived from S-adenosyl methionine (SAM) or from acetate by the 3-hydroxy-3-methylglutaryl-CoA (HMG-CoA) pathway.
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Figure 2. One of the proposed hypotheses for the carbon deletion mechanism in dinoflagellate polyketides. Succinate and α-ketoglutarate, intermediate metabolites from the tricarboxylic acid (TCA) cycle, may participate in the growing polyketide chain.
Figure 2. One of the proposed hypotheses for the carbon deletion mechanism in dinoflagellate polyketides. Succinate and α-ketoglutarate, intermediate metabolites from the tricarboxylic acid (TCA) cycle, may participate in the growing polyketide chain.
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Figure 3. Proposed mechanism for the deletion of the carboxyl carbon from an intact acetate unit via the Favorskii-type rearrangement.
Figure 3. Proposed mechanism for the deletion of the carboxyl carbon from an intact acetate unit via the Favorskii-type rearrangement.
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Figure 4. Proposed mechanism for the deletion of the carboxyl carbon from an intact acetate unit via specific functional modules within polyketide synthases (PKSs).
Figure 4. Proposed mechanism for the deletion of the carboxyl carbon from an intact acetate unit via specific functional modules within polyketide synthases (PKSs).
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Figure 5. Two mechanisms of pendant alkylation of polyketides. (A) The upper reaction uses methylmalonic acid as a building block, while the lower one shows a methyl group derived from SAM. (B) A proposed mechanism for the introduction of a methyl side chain from a malonate unit via an HMG-CoA based enzyme.
Figure 5. Two mechanisms of pendant alkylation of polyketides. (A) The upper reaction uses methylmalonic acid as a building block, while the lower one shows a methyl group derived from SAM. (B) A proposed mechanism for the introduction of a methyl side chain from a malonate unit via an HMG-CoA based enzyme.
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Figure 6. Mechanisms of ether ring formation relevant to dinoflagellate polyethers according to Baldwin’s rules. (A) Exo-trig cyclization of a hydroxyl group to a carbonyl group or a double bond. (B) Endo-trig cyclization of a hydroxyl group to a double bond. (C) Exo-tet cyclization of a hydroxyl group to a hydroxyl group or the opening of an epoxide. (D) Endo-tet cyclization of the opening of an epoxide.
Figure 6. Mechanisms of ether ring formation relevant to dinoflagellate polyethers according to Baldwin’s rules. (A) Exo-trig cyclization of a hydroxyl group to a carbonyl group or a double bond. (B) Endo-trig cyclization of a hydroxyl group to a double bond. (C) Exo-tet cyclization of a hydroxyl group to a hydroxyl group or the opening of an epoxide. (D) Endo-tet cyclization of the opening of an epoxide.
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Figure 7. (A) Shows the mechanism of monensin A polyether ring formation. (B) Shows the mechanism of lasalocid A polyether ring formation. Enzyme-catalyzed cyclization produces the disfavored endo-tet product (up, blue) whereas acid-catalyzed cyclization produces the favored exo-tet product (below, red).
Figure 7. (A) Shows the mechanism of monensin A polyether ring formation. (B) Shows the mechanism of lasalocid A polyether ring formation. Enzyme-catalyzed cyclization produces the disfavored endo-tet product (up, blue) whereas acid-catalyzed cyclization produces the favored exo-tet product (below, red).
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Figure 8. Possible mechanism for the ether ring formation in okadaic acid (OA) based on several isotopic labeling studies using (18O)-labeled acetate, O2, and water.
Figure 8. Possible mechanism for the ether ring formation in okadaic acid (OA) based on several isotopic labeling studies using (18O)-labeled acetate, O2, and water.
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Figure 9. Possible mechanism of ether ring formation in fused-ring polyethers. (A) The syn–trans pattern of fused polyether ring formation. A polyene produced by PKS undergoes epoxidation and epoxide cyclization to form a fused polyether. (B) Proposed mechanism of ciguatoxins (CTXs) polyether ring formation.
Figure 9. Possible mechanism of ether ring formation in fused-ring polyethers. (A) The syn–trans pattern of fused polyether ring formation. A polyene produced by PKS undergoes epoxidation and epoxide cyclization to form a fused polyether. (B) Proposed mechanism of ciguatoxins (CTXs) polyether ring formation.
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Wan, X.; Yao, G.; Liu, Y.; Chen, J.; Jiang, H. Research Progress in the Biosynthetic Mechanisms of Marine Polyether Toxins. Mar. Drugs 2019, 17, 594. https://doi.org/10.3390/md17100594

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Wan X, Yao G, Liu Y, Chen J, Jiang H. Research Progress in the Biosynthetic Mechanisms of Marine Polyether Toxins. Marine Drugs. 2019; 17(10):594. https://doi.org/10.3390/md17100594

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Wan, Xiukun, Ge Yao, Yanli Liu, Jisheng Chen, and Hui Jiang. 2019. "Research Progress in the Biosynthetic Mechanisms of Marine Polyether Toxins" Marine Drugs 17, no. 10: 594. https://doi.org/10.3390/md17100594

APA Style

Wan, X., Yao, G., Liu, Y., Chen, J., & Jiang, H. (2019). Research Progress in the Biosynthetic Mechanisms of Marine Polyether Toxins. Marine Drugs, 17(10), 594. https://doi.org/10.3390/md17100594

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