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Maitotoxin: An Enigmatic Toxic Molecule with Useful Applications in the Biomedical Sciences


Abstract and Figures

Many marine invertebrates produce potent toxins, turning themselves poisonous as a defense strategy against predators. In contrast, other organisms can become poisonous by accumulating toxins from their own prey. Dinoflagellates are aquatic photosynthetic microbial eukaryotes, and some species produce highly toxic metabolites. These dinoflagellate toxins bioaccumulate up the food chain in various consumer organisms. Many filter-feeding organisms such as bivalves accumulate such toxins with no apparent adverse effects on them1 but causing intoxication when ingested by their predators, including fish and marine mammals, and ultimately also when humans consume contaminated seafood. Four major groups of dinoflagellate toxins have been described, namely, saxitoxins, ladder-shaped polyether compounds, long-chain polyketides, and macrolides.2 The dinoflagellate species Gambierdiscus toxicus produces several potent polyether toxins, some of which were initially identified in connection with a common type of food poisoning called ciguatera, caused by consumption of certain contaminated tropical and subtropical fish. Ciguatera involves a combination of gastrointestinal, neurological, and cardiovascular disorders. The two most common toxin classes associated with ciguatera are ciguatoxin (CTx) and maitotoxin (MTx), and they are among the most lethal natural substances known to man. Most of the neurological symptoms of ciguatera are caused by CTx, which exert their effects due primarily to the activation of voltage-gated sodium channels, causing cell membrane depolarization. MTx displays diverse pharmacological activities, which seem to be derived from its ability to activate Ca2+-uptake processes in a variety of cell types. MTx is the largest and most toxic known nonbiopolymeric toxin, with a molecular weight of 3422 Da. MTx is a very interesting compound given its extremely potent biological activity, and it has been used as a powerful pharmacological tool for the elucidation ofCa2+-dependent cellular processes.
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Maitotoxin: An Enigmatic Toxic Molecule with
Useful Applications in the Biomedical Sciences
Juan G. Reyes, Claudia Sánchez-Cárdenas, Waldo Acevedo-Castillo,
Patricio Leyton, Ignacio López-González, Ricardo Felix,
MaríaA. Gandini, Marcela B. Treviño, and Claudia L. Treviño
23.1 Introduction
Many marine invertebrates produce potent toxins, turning themselves poisonous as a defense strategy
against predators. In contrast, other organisms can become poisonous by accumulating toxins from their
own prey. Dinoagellates are aquatic photosynthetic microbial eukaryotes, and some species produce
highly toxic metabolites. These dinoagellate toxins bioaccumulate up the food chain in various con-
sumer organisms. Many lter-feeding organisms such as bivalves accumulate such toxins with no appar-
ent adverse effects on them1 but causing intoxication when ingested by their predators, including sh and
marine mammals, and ultimately also when humans consume contaminated seafood.2
Four major groups of dinoagellate toxins have been described, namely, saxitoxins, ladder-shaped poly-
ether compounds, long-chain polyketides, and macrolides.2 The dinoagellate species Gambierdiscus
toxicus produces several potent polyether toxins, some of which were initially identied in connection
with a common type of food poisoning called ciguatera, caused by consumption of certain contaminated
tropical and subtropical sh. Ciguatera involves a combination of gastrointestinal, neurological, and
cardiovascular disorders. The two most common toxin classes associated with ciguatera are ciguatoxin
(CTx) and maitotoxin (MTx), and they are among the most lethal natural substances known to man.2
23.1 Introduction .................................................................................................................................. 677
23.2 History .......................................................................................................................................... 678
23.3 Natural Origin .............................................................................................................................. 679
23.4 Toxicology .................................................................................................................................... 679
23.5 Synthesis ...................................................................................................................................... 680
23.5.1 Biosynthesis of Ladder-Shaped Polyether Compounds .................................................. 680
23.5.2 Chemical Synthesis of Maitotoxin .................................................................................. 681
23.6 Mechanisms of Action ................................................................................................................. 683
23.6.1 MTx and Plasma Membrane Channel Activation ........................................................... 683
23.6.2 MTx Interaction with Membranes ................................................................................... 683
23.7 MTx Bioactivity and Applications ............................................................................................... 684
23.7.1 Insulinotropic Actions of MTx ........................................................................................ 685
23.7.2 MTx as Interleukin-1β Secretagogue and Oncotic Death Inducer .................................. 686
23.7.3 MTx and Sperm Physiology ............................................................................................ 687
23.8 Final Remarks .............................................................................................................................. 688
Acknowledgments .................................................................................................................................. 689
References .............................................................................................................................................. 689
678 Seafood and Freshwater Toxins: Pharmacology, Physiology, and Detection
Most of the neurological symptoms of ciguatera are caused by CTx, which exert their effects due
primarily to the activation of voltage-gated sodium channels, causing cell membrane depolarization.1
MTx displays diverse pharmacological activities, which seem to be derived from its ability to activate
Ca2+-uptake processes in a variety of cell types.3 MTx is the largest and most toxic known nonbiopoly-
meric toxin, with a molecular weight of 3422 Da. MTx is a very interesting compound given its extremely
potent biological activity, and it has been used as a powerful pharmacological tool for the elucidation of
Ca2+-dependent cellular processes.
23.2 History
The discovery of MTx is closely related to the characterization of ciguatera, a food-borne illness caused
by the consumption of sh contaminated with certain dinoagellate toxins. Ciguatera symptoms can
vary with the geographic origin of the contaminated sh. Gastrointestinal symptoms—such as diarrhea,
vomiting, and abdominal pain—occur rst, usually within 24 h of eating implicated sh. Neurological
symptoms may occur at the same time or may follow several days later and include thermal sense inver-
sion, characterized by the feeling of receiving an electric shock when touching cold water, pain and
weakness in the lower extremities, and circumoral and peripheral paresthesia.
This mode of poisoning was called “ciguatera” after cigua, a snail commonly occurring in the
Caribbean Sea.4,5 Ciguatera occurs worldwide in tropical and subtropical regions causing 20,000–50,000
victims per year. The agents causing this condition bioaccumulate in sh as they are transferred up the
food chain, to be nally consumed by humans. Ancient references to toxic diseases conditions similar
to “ciguatera” are found in Homer’s Odyssey (ca. 800 BC), in reports of a pandemic occurring in China
(600 BC), and in the chronicles written by Pedro Martir de Anglería in 1555.6
MTx was discovered in 1965 by Bagnis, who reported that the human symptoms caused by inges-
tion of contaminated herbivorous sh were different from those caused by carnivorous sh, primarily
involving gastrointestinal discomfort and less neurological disorders. The molecule responsible for these
symptoms was discovered upon examination of the toxic constituents in the surgeonsh Ctenochaetus
striatus and was named after the Tahitian namesake of this species—“maito.”7 MTx is a polyketide-
derived polycyclic ether consisting of four extended fused-ring systems termed polyether ladders (molec-
ular formula C164H256O68S2Na2) (Figure 23.1).
Me Me
Me Me Me
Me Me
FIGURE 23.1 Structure of MTx. (Taken from Treviño, C.L. et al., Maitotoxin: A unique pharmacological tool for eluci-
dating Ca2+-dependent mechanisms, in: Botana, L.M. (ed.), Seafood and Freshwater Toxins: Pharmacology, Physiology
and Detection, 2nd edn., CRC Press, Boca Raton, F L, pp. 503–516, 2008.) The grey region was utilized for the theoretical
molecular dynamics calculations in t he section M Tx interaction with membranes.
679Maitotoxin: An Enigmatic Toxic Molecule with Useful Applications in the Biomedical Sciences
23. 3 Natural Origin
The marine dinoagellate G. toxicus is a single-celled phytoplanktonic organism, and it may be found on
the surface of algae in tropical waters worldwide. Among other toxins, it produces CTx and MTx, which
accumulate through the food chain as carnivorous sh consume contaminated herbivorous reef sh.
MTx toxin accumulates primarily in the liver and viscera of shes, but not in their esh.8 Higher concen-
trations of toxins can be found in large predatory sh such as barracuda, grouper, amberjack, snapper,
and shark. Because the sh industry has no borders and marine products are shipped to many countries,
ciguatera sh poisoning can occur almost anywhere. People who live in or travel to endemic areas should
avoid consumption of barracuda or moray eel, should be cautious with grouper and red snapper, and are
advised to enquire about local sh associated with ciguatera. Since there is no reliable way to “decon-
taminate” or even to distinguish contaminated sh by smell or appearance, it is wise to avoid eating the
viscera of any reef sh and to prevent consumption of large predacious reef sh.9,10.
The temperatures of the northern Caribbean and extreme southeastern Gulf of Mexico have been
predicted to increase 2.5°C–3.5°C during the next years.11 Higher temperatures favor G. toxicus growth12
and are also likely to alter sh migration patterns. Ciguatera outbreaks have been correlated with sea-
surface temperature increases in the south Pacic Ocean.13
After Yasumoto discovered in 1977 that the dinoagellate G. toxicus was responsible for producing
MTx, he cultivated this organism for 10 years in order to have enough material to isolate this toxin and
to determine its structure.14,15 For some years, MTx was commercially available for experimentation and
was used to study Ca2+ dynamics in diverse cell types (see Section 23.7). Having this tool commercially
available again would certainly continue to be useful for research purposes.
23.4 Toxicology
Human ingestion of seafood contaminated with toxins produced by marine phytoplankton10,16,17 can
cause a variety of diseases. These toxins can have a wide range of acute and chronic health effects not
just in humans but also in other animal species. Given that these compounds are tasteless, odorless, and
heat and acid stable, conventional food testing methods fail to detect and destroy them in contaminated
Ciguatera can cause mild to severe symptoms lasting from a few days and up to years. Around 400
species of sh are considered to be ciguateric and contain distinct combinations and quantities of toxins.
Classical ciguateric symptoms include gastrointestinal and neurological disorders, abdominal cramps,
diarrhea, nausea, vomiting, temperature reversal, and itching. The toxins can even be passed on to a fetus
or to a newborn child, via placental or breast milk transmission, respectively.9,10
Most of the neurological symptoms of ciguatera are due to CTx, while MTx is considered to be less
important in the generation of ciguatera symptoms given that it is less concentrated in shes. However, it
should be noted that the observed toxicity differences could also be the result of chemical modications
of the toxins possibly occurring as they pass through the food chain, and it is therefore difcult to estab-
lish a direct relationship between the various symptoms and a particular toxin. Diagnosis of ciguatera is
based solely on the presence of the general symptoms in correlation to patients with a recent history of
sh ingestion.
In contrast to the lipid-soluble CTxs, MTx is water soluble, and it apparently does not accumulate in
the esh of shes but rather in organs such as the liver.18 MTx has a very low oral potency as compared
to its high lethality when injected intraperitoneally (i.p.), and pure MTx is even more toxic than CTx.
For example, in mice, CTx is lethal at 0.45 μg/kg i.p. and MTx at a dose of 0.15 μg/kg i.p. However, the
precise lethal dose depends on the mouse strain, the sample source, and even the sample preparation pro-
cedure, as MTx binds to glass and plastic and thus its exact concentration may be underestimated. Mice
injected i.p. with MTx display reduced body temperature, piloerection, dyspnea, progressive paralysis,
slight tremors or convulsions, and long death times. High doses of MTx produce CTx-like symptoms,
such as gasping with convulsions and shorter death times.
680 Seafood and Freshwater Toxins: Pharmacology, Physiology, and Detection
Three different MTx molecules have been isolated from a variety of strains of G. toxicus. Injection
of MTx-1 and MTx-2 in mice exerted similar symptoms, except that MTx-2 exhibited shorter death
times. MTx-3 induced additional symptoms such as intense gasping that ameliorated near death; how-
ever, further purication of MTx-3 by HPLC reduced the gasping symptoms, suggesting that additional
bioactive components may be present in the crude preparation.19 The death times produced by MTx-1
and MTx-3 were very similar. Desulfonation of MTx (solvolysis) reduces the toxicity of all three forms
about 200-fold.19,20
Efforts to develop a radioimmunoassay (RIA) or enzyme-linked immunosorbent assay (ELISA) to
detect CTx have been made over the past few years, such as the Hokama enzyme immunoassay stick
test.21 There is a commercial kit called Cigua-Check® that may be used by sherman or restaurants to
prevent ingestion of contaminated sh. Unfortunately, this kit only detects CTx. Detection can be con-
rmed by nding CTx and MTx in contaminated sh samples by high-performance liquid chromatog-
raphy and mass spectrometry, although this process is costly and not widely available in high risk areas,
such as small islands.
To date, there is no antidote for ciguatera, but medications such as amitriptyline have been used to
diminish some of the symptoms of chronic ciguatera, including fatigue and paresthesias. There are sev-
eral palliative remedies including medicinal teas used in both the Indo-Pacic and West Indies regions.
However, none of these treatments have been properly standardized to provide effective treatment.9,10
Patients are also advised to avoid alcohol, nuts, and nut oil for at least 6 months after the intoxication in
order to avoid reappearance of symptoms.
23. 5 Synthesis
23.5.1 Biosynthesis of Ladder-Shaped Polyether Compounds
The structural similarities among dinoagellate-produced polyether ladder toxins including breve-
toxins, CTxs, yessotoxins, and MTxs strongly suggest that their biosynthetic pathways may share
similar strategies. In the case of brevetoxins, experimental studies on their biosynthetic pathways are
starting to unveil the biochemical reactions involved in the production of such complex polyethers.
Based on tracing studies using radiolabeled carbon precursors, it is now clear that polyketides in
general are assembled from acetyl-CoA or malonyl-CoA precursors; they a lso contain carbon units
derived from methionine and from some la rger carbon unit precursors, such as glycolate.22 The car-
bon chain formed from the aforementioned precursors appears to be interrupted by C-1 deletions of
acetate-der ived carbon atoms. Although a Favorskii-like rearrangement has been suggested to be
involved in the ring size reduction observed in polyether ladder toxins, such proposed catalytic mech-
anism (which in vitro takes place with halogenated compounds and under strong basic conditions)
has not yet been unequivocally demonstrated. In this biosynthetic pathway, and similarly to bacterial
polyether synthesis, polyketide synthases appear to play a n important role. This family of enzymes
catalyzes the synthesis of complex natural products from precursors such as acetyl-CoA, propionyl-
CoA, and methylmalonyl-CoA through a biosynthetic strategy resembling the one used for fatty acid
(FA) biosynthesis.23 Thus, polyketides are built by a series of successive condensations of simple
precursors, decarboxylations, reductions, and rea rrangements. However, unlike FA biosynthesis, in
which the FA chain is subjected to the whole series of intermediate reactions, the partial chemical
processing of intermediaries in polyketide biosynthesis can give rise to a complex pattern of func-
tional groups associated to the polyether chain. Furthermore, different dinoagellate species can use
different combinations of starter CoA-activated precursors and chain-extension substrates during
polyketide biosynthesis, which at least in some cases involve the generation of specic chiral centers
and cyclization. Despite the proposed existence of similar polyether ladder biosynthetic pathways in
different dinoagellate species, suggested by their products’ structural similarities.22, 24 Dening the
specic reactions of any such pathway has proven a very difcult task. This challenge stems from
the diversity of chemica l structures found in this family of compounds, from the diversity of species
within this phylum of alveolate euka ryotes, and from the particularly complex genetic organization
681Maitotoxin: An Enigmatic Toxic Molecule with Useful Applications in the Biomedical Sciences
observed in these organisms, including multigene phylogenies, diverse plastid endosymbiotic rela-
tionships, and chromatin conguration.22 ,25 –28 It has been suggested that for polyether ladder toxins,
the par ticipating acetate units can enter the tricarboxylic acid (TCA) cycle, and some TCA interme-
diate could be the actual precursor involved in the condensation process.29 In fact, to the best of our
knowledge, there a re thus far no reports of specic studies on MTx biosynthesis. Further more, it is
likely that the toxins isolated from the organs of herbivorous shes represent a chem ically modied
version of the toxins originally synthesized by the dinoagellates.3 0–32
The cyclization process in these compounds is probably associated to the formation of an epox-
ide intermediate presumably catalyzed by epoxidases and epoxide hydrolases.33, 34 The accompany-
ing polyepoxide process proposed for marine polyether ladder toxins has clear precedents in several
reports on epoxide and cycle formation during antibiotic polyether biosynthesis.35 Although the pro-
cess whereby 10 or more epoxides are formed and then coordinated to a polyepoxide cascade to yield
polyether ladder toxins still remains unclear, an oxidase-catalyzed tandem epoxide formation and
epoxide protection, followed by a hydrolase-catalyzed epoxide opening and cycle rea rrangement, is
likely involved.
23.5.2 Chemical Synthesis of Maitotoxin
The chemical structures of marine toxins in general—and MTx in particular—are very interesting and
represent a formidable challenge for organic synthesis.36 The appearance in the literature of the struc-
ture of brevetoxin-B (the rst marine polycyclic ether to be isolated and characterized37) awoke a large
interest in synthetic organic chemists. The structure of brevetoxin-B is characterized by several fused
polycyclic ethers containing ether rings with 6, 7, and 8 units, in addition to 23 chiral centers, certainly
a daring task for chemical synthesis. It contains 32 fused ether rings, 28 hydroxyl groups, 21 methyl
groups, 98 chiral centers, and 2 sulfates.3,38 –4 0
The efforts of chemical synthesis have been directed toward developing new methods that
allow synthesis of only part of these molecules by initially building structural fragments of these
ladder-shaped polyether toxins. Great progress in the synthesis of several marine polycyclic ethers
has been accomplished since the year 2000.41,42 They designed a remarkable synthetic strategy involv-
ing an efcient iterative method for the stereoselective construction of transfused polycyclic ethers
based on induced reductive cyclization of β-alcoxy-acrylate by samarium iodide (SmI2). In the case
of the synthesis of the ring systems of MTx, the stereoselectivity was accomplished by state transition
chelation (Figure 23.2).42– 46
Oxepane ring formation also was stereoselectively synthesized through this reaction generating a sin-
gle product with an 84% yield (Figure 23.3).
FIGURE 23.2 Transition state of the cyclization induced by SmI2. (From Sakamoto, Y. et al., Org. Lett., 3, 2749, 2001;
Nakata, T., Chem. Rec., 10, 159, 2010.)
THF, rt
FIGURE 23.3 Synthesis of polycyclic et hers based on cyclizat ion induced by SmI2. (From Nakata, T., Chem. Rec., 10,
159, 2010.)
682 Seafood and Freshwater Toxins: Pharmacology, Physiology, and Detection
Moreover, the trans-membered fused polycyclic 6,7,6 and 6,7,7,6 ethers were iteratively synthesized
using this cyclization induced by SmI2 strategy (Figure 23.4).42
Additionally, in 1998, Dr. Nicolaou’s research group (La Jolla, CA) reported the complete synthe-
sis of brevetoxin-A, another ladder-shaped polyether compound, the rst stereoselective synthesis
of pyrans involving the opening of epoxides with a hydroxyl group. This synthesis route has the
particularity of overcoming the natural preference for cyclization to an unwanted product 5-exo by
placing one CC bond adjacent to the epoxy fragment. Thus, under these conditions, the structure
shown in Figure 23.5 exclusively undergoes ring closure to produce a 6-endo by pyran system instead
of 5-exo product. The selectivity observed is attributed to the π orbital stabilization generated by a
carbon atom next to the electron-decient transition state provoking an endo attack; this effect would
be absent during the exo attack.47
Using similar synthetic strategies, this same research group has accomplished the stereoselective syn-
thesis of ladder-shaped portions of a large part of MTx.40,41,48–50 Altogether, between Dr. Nakata’s and Dr.
Nicolaou’s group, 29 out of the 32 rings of MTx have been chemically synthesized.
Although thus far no complete chemical synthesis has been achieved for MTx, complete synthesis has
been successful for some of the other ladder-shaped polycyclic ester toxins. New methods such as bio-
mimetic cascades, cross-coupling reactions catalyzed by palladium, and radical reactions could provide
additional tools for approaching the laboratory synthesis of this type of compounds.
FIGURE 23.4 Examples of ethers synthesized by iterative strategy induced cyclization 6,7,6 and 6,7,7,6 membered poly-
cyclic ethers. (From Nakata, T., Chem. Rec., 10, 159, 2010.)
6-Endo (65%)
FIGURE 23.5 Reactions involved for the formation of cyclic ethers. (From Nicolaou, K. et al., J. Am. Chem . Soc., 108,
2468, 1986; Nicolaou, K.C. et al., J. Am . Chem . Soc., 130, 7466, 2008.)
683Maitotoxin: An Enigmatic Toxic Molecule with Useful Applications in the Biomedical Sciences
23.6 Mechanisms of Action
23.6.1 MTx and Plasma Membrane Channel Activation
After the early work of Dr. Yasumoto’s group,51–53 it became clear that MTx acted on mammalian cells
inducing entry of external Ca2+, and based on pharmacological criteria, it was proposed that MTx activated
voltage-gated Ca2+ (Cav) channels.54–57 Consistent with this proposal, MTx-induced Ca2+ entry was absent
in broblast that lacked these channels.55 However, even this early work on the mechanisms of action of
MTx pointed out some peculiar aspects of the toxins effects, such as a delay of about 2 min in the induction
of Ca2+ entry observed in certain cell types55 or the reported inhibition of Na+-K+-ATPase induced by the
toxin.58 Furthermore, it was soon reported that MTx was able to induce inositol triphosphate (IP3) release
independently of its action on Ca2+ channels.59 These results were corroborated by Gusovsky et al.60–63 in
several cell lines, showing also that MTx activated phosphoinositide (PI) breakdown in a Ca2+-dependent
manner but it was not inhibited by Cav channel blockers, suggesting the activation of phospholipase C
(PLC) or the activation of other Ca2+ channels. The fact that MTx action on PI breakdown was not mim-
icked by Ca2+ ionophores supported the notion that MTx activated PLC directly. However, in the work of
Gusovsky et al.64 using HL60 cells, it became clear that MTx action on PI turnover was associated to a Ca2+-
induced activation of PLC, rather than a direct PLC activation by MTx. Furthermore, the work of Pin et al.65
suggested that the effects of MTx on gamma-aminobutyric acid (GABA) release in striatal neurons were
associated to a Ca2+-dependent Na+ inux, introducing the notion of an additional cellular target for MTx.
Similar results of a Ca2+-dependent Na+ inux was reported by Sladescek et al.66 The pleiotropic effects and
action mechanisms of MTx on different cells was reviewed by Hamilton and Perez.67
Although the effects of MTx were pleiotropic, they all seemed to involve an intracellular Ca2+ increase.
The fact that MTx activated cation channels was clear from direct voltage-clamp current measurements
(e.g., [38,68–81]). Some of the proposed channels were Cav and also nonselective cation channels such as
store-operated channels (SOCs). Furthermore, in some cells such as skin broblasts, MTx seems to activate
large conducting channels82,83 leading to cell lysis. Hence, the action of MTx would be highly dependent on
the channel expression prole of each cell type and also on the MTx concentration used (e.g., [84]). Due to
scope limitations in this review, we have excluded a discussion of all cellular effects downstream of the MTx
interaction with membranes, on which a wealth of data is undoubtedly available in the literature.
The ability of MTx to activate Cav and other cationic channels posed the question as to whether
the toxin was activating channels by inserting itself in the membrane and perturbing the phospholipid
membrane structure (see MTx interaction with membranes in the following texts) or whether it had spe-
cic interactions with the proteins forming the channels. Murata et al.85 reported that either a removal
of the sulfated residues from MTx or a hydrogenation of the molecule decreased (by several orders of
magnitude) its ability to induce Ca2+ entry or PI breakdown in insulinoma or glioma cells. When these
MTx derivatives were used together with intact MTx, they acted as blockers of the MTx effect. The work
of Konoki et al.86 describing inhibition of MTx-induced Ca2+ entry in glioma C6 cells by brevetoxin
and synthetic fragments of MTx (corresponding to a sulfated portion, rings EF-GH, and rings LM-NO)
strongly suggested that MTx acted on specic sites to activate Ca2+ entry in these cells. Interestingly,
the sulfated fragment of MTx (EF-GH rings, and hence, a portion expected to remain in the aqueous
phase or at the lipid–water interphase) was more potent in inhibiting MTx effects on Ca2+ uptake than
the LM-NO rings. Recent work by Oishi et al.87 clearly showed that an articial ladder-shaped heptacy-
clic polyether was the most potent substance described to date capable of inhibiting MTx-induced Ca2+
inux in glioma C6 cells, strongly suggesting the existence of a specic MTx binding site in these cells.
However, this work did not give insight into the molecular mechanisms of action of MTx.
23.6.2 MTx Interaction with Membranes
The insertion of MTx in membranes was rst suggested by Konoki et al.,88 with rings
RSTUVWXYZABCDEF inserted in and spanning the phospholipid bilayer and rings
ABCDEFGHIJKLMNOPQ containing the sulfated parts of the molecule—staying in the aqueous
684 Seafood and Freshwater Toxins: Pharmacology, Physiology, and Detection
environment. This work was later cited by Murata et al.,89 Nicolau et al.,90 and Nicolau and Aversa91
to discuss the properties of MTx. This association of MTx with phospholipid membranes was deduced
from the structural properties of MTx and by analogy to the properties of other ladder-shaped polyether
toxins.89 However, to the best of our efforts, we were unable to nd the specic model or program used
to estimate MTx distribution in phospholipid membranes. Thus, in order to theoretically estimate the
stability of the relatively hydrophobic portion of MTx in a phosphatidylcholine phospholipid membrane,
we performed force eld parameterization of rings P–F and molecular dynamics as shown in the follow-
ing texts. The molecular structure of MTx was taken from Nicolau and Frederic4 0 (Figure 23.1). Partial
parameterization with the CHARMM force eld was accomplished taking different sections of the mol-
ecule from ring P to F using the CCPN web applications ( The 1-palmitoyl-2-
oleoyl-sn-glycero-3-phosphocholine (DOPC) bilayer was built with visual molecular dynamics (VMD
1.9).92 The mentioned fragment of MTx was distributed in the center of the bilayer, and the program not
(just) another molecular dynamics (NAMD) allowed to iteratively locate the molecule to acquire a con-
formation giving steady values of potential energy parameters (
This modeling clearly shows that rings P–F and tail were stable within the lipid bilayer (Figures 23.6
and 23.7), and this conformation is likely restricted and modied by the more hydrophilic portion of MTx
(see also Murata et al.89). This distribution of the hydrophobic portion of MTx is consistent with the pro-
posed role of this part of MTx (or similar portions of ladder-shaped polyether toxins) in the interaction
with integral membrane α-helices.89,93 However, these results do not exclude that the hydrophilic por-
tion of MTx, anchored in the membrane by the hydrophobic portion, could also interact externally with
channels86 or, as we could cautiously propose, that both mechanisms could be responsible for activation
of different types of channels in biological membranes.
23.7 MTx Bioactivity and Applications
Ca2+ is an ubiquitous secondary intracellular messenger responsible for mediating a multitude of cellular
responses as diverse as proliferation, development, contraction, secretion, and fertilization. Ca2+ action is
quite simple: cells at rest have an intracellular concentration of 100 nM but are activated when this level
rises to 1 μM. However, the universality of Ca2+ as an intracellular messenger depends on its remark-
able capacity to create a wide range of spatial and temporal signals.
FIGURE 23.6 The initial position of MTx in the 1-palmitoyl-2-oleoyl-sn-glycero-3- phosphocholine (POPC) membrane
was set with the plane of the molecule parallel to the POPC/water inter phase. This position and conformation as well as the
environment were then allowed to drif t with molecula r dyna mics calculations toward steady states with minimal energy
conformations. Water molecules: oxygen = red, hydrogen = white. Phospholipids: light blue large chains. MTx: darker blue
at the center of the bilayer. ( PRG.base?tipo:doc,dir:PRG.curriculum,par:ctrevino)
685Maitotoxin: An Enigmatic Toxic Molecule with Useful Applications in the Biomedical Sciences
MTx has attracted much attention given its powerful bioactivity involving disruption of Ca2+ homeo-
stasis. MTx is not only one of the most potent toxins, but it also possesses multiple activities that appear
to be linked to elevation of intracellular Ca2+ concentration. Thus, the toxin serves as a versatile tool for
studies on cellular events associated with intracellular Ca2+ changes that are of particular interest, includ-
ing hormone secretion, programmed cell death activation, and fertilization.
23.7.1 Insulinotropic Actions of MTx
Although some hormones such as insulin-like growth factor and adiponectin have hypoglycemic effects,94
insulin has long been considered the only hypoglycemic agent in mammals. Insulin is synthesized and
secreted by pancreatic β-cells located in specialized structures, the islets of Langerhans. In general, β-cells
adjust insulin secretion to the prevailing blood glucose levels by a process called glucose-stimulated insu-
lin secretion (GSIS). Inside pancreatic β-cells, glucose metabolism induces insulin secretion by altering
the cellular array of messenger molecules. ATP is particularly important given its role in regulating cation
channel activity dependent upon its hydrolysis.
t= 20 ps
5,000 10,000 15,000 20,000 25,000 30,000 35,000
E (kcal/mol)
t= 40 ps t= 60 ps
FIGURE 23.7 (a) Plot of energy (kcal/mol) versus the molecular simulation steps (1 ps corresponds to 500 steps). Each
curve corresponds to the different components of potential energy: binding energy (blue line), angles (red line), electro-
static energy (green line), and kinetic energy (orange line). (b) Spatial distribution of MTx in the 1,2-dioleoyl-sn-glycero-3-
phosphocholine (DOPC) membrane at 20, 40, and 60 ps. From the potential energy curves and the molecular images, it can
be seen that this portion of MTx is stably located within the hydrophobic portion of the phospholipid bilayer at 40 ps, with
a location a nd dynamics that certainly would be restricted by the hydrophilic portion that is expected to be located at the
water/phospholipid interface. (See also Murata, M. et al., Bull. Chem. Soc. Jpn., 81, 307, 2008.)
686 Seafood and Freshwater Toxins: Pharmacology, Physiology, and Detection
ATP-dependent K+ (KATP) channels play a key role in insulin secretion. Under euglycemic conditions,
KATP channels are maintained in an open state, resulting in K+ efux and thus clamping the resting mem-
brane potential close to −70 mV. When glucose is elevated, ATP levels increase and displace bound ADP
on KATP channels, which results in channel closure. These events lead to a small membrane depolariza-
tion that activates voltage-dependent Ca2+ channels, which trigger Ca2+ inux and raise the intracellular
Ca2+ concentration, thus promoting insulin secretion.95,96
Several reports have shown that some members of the transient receptor potential (TRP) channel
family, which mediate nonselective cationic currents (NSCCs), are expressed, and might contribute to
pancreatic β-cell function. Although the role of TRP channels in β-cells remains largely enigmatic, these
channels may provide an alternative for the depolarizing background membrane conductance required
for the cells to depolarize upon KATP channel closure.96 Indeed, it has been reported that thermosensitive
TRPM2, TRPM4, and TRPM5 channels control insulin secretion levels by sensing intracellular Ca2+
increase, NAD+ metabolites, or hormone receptor activation.97
In addition to glucose, insulin secretion may be regulated by diverse chemical messengers such as
neurotransmitters and hormones,96 as well as by exogenous substances such as toxins that act on ion
channels. Hence, some peptide toxins present in the venom of marine organisms may affect NSCCs and
serve as potential insulinotropic agents. For example, it has been shown that the activity of TRPV1, a
channel that modulates insulin secretion in β-cells, is affected by crude cell-free extracts obtained from
marine invertebrates.98,99 Interestingly, one of these extracts has shown insulinotropic activity.100
By activating NSCCs, MTx has also shown insulinotropic activity in insulinoma cells. The time
course of these currents is very similar to that evoked by incretin hormones such as glucagon-like pep-
tide-1 (GLP-1), which stimulate glucose-dependent insulin secretion by activating cAMP-mediated sig-
naling pathways.101 Likewise, NSCCs in insulinoma cells can be attenuated by application of a Ca2+
SOC blocker SKF 96365, suggesting a contribution of the mammalian TRP-related channels in these
currents.102 The ability to activate NSCCs in insulin-secreting cells stresses the role of MTx as a helpful
tool for the analysis of ion channels and insulin secretion.103 Likewise, the role of MTx as a novel blood
glucose-lowering agent remains an interesting topic for future research.
23.7.2 MTx as Interleukin-1β Secretagogue and Oncotic Death Inducer
Most inammatory reactions are mediated by cytokines, including IL-1, IL-6, TNF-α, and TGF-β. The
term interleukin-1 (IL-1) refers to two cytokines, IL-1α and IL-1β, which are the master cytokines of
local and systemic inammation.104,105 In particular, IL-1β is primarily synthesized in activated macro-
phages as an immature protein that remains cytosolic until converted through proteolytic cleavage by
caspase-1 into its mature active form, which can then be exported outside the cell.
Given its ability to induce cell death secondary to its disruption of Ca2+ homeostasis, MTx is likely to
trigger innate immune responses and inammation in vivo. Indeed, it has been suggested that the toxic
effect of MTx during shellsh seafood poisoning may involve a component mediated by secretion of
proinammatory cytokine IL-1β. In line with this, Verhoef and coworkers106 reported that MTx induces
a biphasic release of IL-1β from bacterial lipopolysaccharide-primed macrophages. At subnanomolar
concentrations, MTx induced mature IL-1β release via a mechanism that can be blocked by high extra-
cellular K+ or nominally zero extracellular Ca2+. MTx may therefore represent an exceptional tool for
studying specic components of the innate immune response and/or the physiology of inammatory
effector cells such as monocytes, macrophages, and neutrophils. One representative example of this
type of application is the work by Mariathasan and colleagues.107 These authors found that cryopyrin is
responsible for assembly of the so-called inammasome, a cytosolic complex of proteins that activates
caspase-1 to process the proinammatory cytokine IL-1β. Cryopyrin is essential for inammasome acti-
vation in response to signaling pathways triggered by specic bacterial infections as well as by MTx.
It is worth mentioning here that there are several human diseases caused by different mutations in the
cryopyrin gene, including familial cold autoinammatory syndrome, Muckle–Wells syndrome, as well as
chronic infantile neurological cutaneous and articular syndrome.108 Mutations in the cryopyrin gene are
associated with gain of function leading to an enhanced and faster production of IL-1β. In this scenario, MTx
could be used as a probe to study possible mechanisms of release and implications of IL-1β overproduction.
687Maitotoxin: An Enigmatic Toxic Molecule with Useful Applications in the Biomedical Sciences
Likewise, the second phase of IL-1β release induced by MTx from macrophages occurs at nanomolar
concentrations.106 In this case, MTx produces secretion of unprocessed IL-1β, which is indicative of cell
lysis. Interestingly, cell death induced by MTx shares some elements involved in the signaling cascade
activated by stimulation of purinergic receptors of the P2Z/P2X7 type.82,83,109 As discussed earlier, MTx
initially activates Ca2+-permeable channels and then induces the formation of large cytolytic/oncotic
pores (COPs) that allow molecules <800 Da to enter the cell. These effects are similar to those observed
upon activation of P2Z/P2X7 receptors in a variety of cell types, raising the intriguing possibility that
MTx and P2Z/P2X7 receptor stimulation activate a common cytolytic pore.
Given the high permeability of the MTx-induced channels for Ca2+ transport and the structural simi-
larity of MTx with palytoxin—a marine peptide toxin that converts the plasmalemmal Na+/K+-ATPase
(NKA) pump into a channel—it has been proposed that MTx may activate another member of the P-type
ATPase family, specically the plasmalemmal Ca2+-ATPase (PMCA) pump. The results obtained by
Sinkins and colleagues110 are consistent with this idea and suggest that MTx binds to PMCA and con-
verts the pump into a Ca2+-permeable nonselective cation channel. Therefore, MTx could be used as a
cell death inducer to unveil some of the molecular mechanisms involved in this process. For instance,
whether or not the channel mode of operation of the PMCA plays a role in pathological cell death could
be an interesting possibility for future investigations.
23.7.3 MTx and Sperm Physiology
Fertilization is fundamental for the preservation of life by sexual reproduction. The ability of the sperm
and the oocyte to recognize, adhere to, and fuse with each other is a crucial aspect of fertilization. All
these processes are largely determined by nicely orchestrated ionic uxes.111 Hence, it is well known that
raises in intracellular Ca2+ play crucial roles in sperm functions such as capacitation, motility, and the
acrosome reaction.111
The acrosome reaction is a secretory process triggered in sperm by components of the outer layer of
the egg, and in many species it must occur before the sperm can fertilize the egg. However, the mecha-
nisms responsible for increasing intracellular Ca2+ and resulting in the biochemical events that trigger
the acrosome reaction are not fully understood. Two different types of Ca2+ channels have been proposed
to participate in mammalian sperm acrosome reaction: one necessary for a fast transient change in Ca2+
levels and another needed to sustain an elevated intracellular Ca2+ concentration. The membrane path-
way responsible for the rst phase of Ca2+ entry seems to belong to the Cav channel family, while the
sustained Ca2+ inux may be carried through a store depletion-operated pathway.112,113 Interestingly, it
has been reported that several TRP channels are expressed in sperm and may be important for the sus-
tained Ca2+ entry that drives the acrosome reaction.113–115
Evidence obtained in our laboratory indicated that MTx activates a Ca2+ inux that induces the
mammalian acrosome reaction. The data initially suggested that the actions of MTx were comparable
to those of other agents that promote a sustained increase in intracellular Ca2+ and drive the mam-
malian sperm acrosome reaction, including the physiological ligands of the zona pellucida (ZP).116
More recently, however, we found differences in the acrosome reaction induced by MTx and the ZP
in human and mouse sperm. Our data indicated that the acrosome reaction induced by the physiologi-
cal ligands and by MTx occurred through distinct pathways.117 By using specic PLC antagonists,
the participation of a PLC-dependent signaling pathway in the ZP-induced acrosome reaction was
conrmed. In contrast, the use of PLC in hibitors blocked the acrosome reaction induced by MTx in
mouse but not in human sperm, unveiling species-specic variants of the acrosome reaction induced
by the toxin.
Lastly, MTx has also been instrumental in unveiling of some of the mechanisms of the spermato-
genic cell regulation exerted by Sertoli cells. We have previously shown that glucose and lactate, two
substrates secreted by Sertoli cells toward the adluminal compartment in the seminiferous tubules,
can modulate the activity of MTx-sensitive Ca2+ channels in enzymatically dissociated rat spermato-
cytes and spermatids.118 By inducing changes in intracellular Ca2+, both substrates can activate a Ca2+/
calmodulin-dependent protein kinase that results in the phosphorylation of MTx-sensitive channels.
We have recently developed in our laboratory a methodology to study Ca2+ signaling in spermatogenic
688 Seafood and Freshwater Toxins: Pharmacology, Physiology, and Detection
cells by preparing slices of seminiferous tubules. This methodology has the advantage of preserving
tissue architecture and intercellular connections,119 and we demonstrated that Ca2+ signaling differs in
dissociated spermatogenic cells compared to spermatogenic cells inside the tubules. Here, we show
that MTx induces a generalized Ca2+ increase when applied to this seminiferous tubule slice (STS)
preparation, which can be used to further study spermatogenic cell Ca2+ dynamics in a physiological
environment that preserves cell interactions within the tubule (Figure 23.8). The knowledge generated
using this approach could have relevant implications for the understanding of the physiological process
of spermatogenic cell regulation by Sertoli cells, as well as the hormonal control that they may exert on
spermatogenesis, which is not possible to study in vitro.
23.8 Final Remarks
MTx has inspired vast experimentation by organic a nd biological researchers due to its st ructura l
complexity and intricate mode of action. However, k nowledge of both its organic and biochemi-
cal synthesis, as well as of its biological ta rget(s), rema ins incomplete. The current lack of com-
mercially available MTx underscores the importance for achieving its organic synthesis, so t hat it
can become readily available again for studies on Ca2+ dyna mics in different systems and also to
help identify its putative receptor(s). This would lead to a better understanding of the molecular
mechanisms involved in MTx action, which in tur n may help explain the apparent discrepancies in
its functional modalities. Knowledge in this area could also help to nd appropriate treatment or an
antidote for ciguatera.
500 seg
+ MTx
50 nM
0 seg
200 seg
+ MTx
50 nM
80 μM
400 600
T (seg)(d) (e)
FIGURE 23.8 STSs are obtained as reported. Briey, the Tunica albuginea is removed from mice testis and the semi-
niferous tubules are mechanically dispersed with tweezers in a Petri dish containing Ringer solution (in mM: 125NaCl,
2.5KCl, 2CaCl2, 1MgCl2, 1.25NaH2PO4, 26NaHCO3, 12 glucose, gassed with 5% CO2, 95% O2, adjusted to pH 7.4). The
dispersed tubules are embedded in agar (low melting point, 3%) to form a cube that is mounted on the plate of a vibratome,
and 160 μM thick slices are obtained. STSs were loaded with uo 4-AM (20 μM) immobilized with a nylon mesh, placed on
the stage of a microscope, and continuously per fused (2 mL/min) with gassed physiological solution at room temperature.
Fluorescence images were acquired (for equipment deta ils, see [119]) every second with an exposure/illumination time of
10 ms for a total of 10 min (600 images). Pseudocolored uorescence image obta ined from the recording of STS before
(a) and after addition of 50 nM MTx (b and c). Fluorescence traces obta ined from three different cells in the STS shown
in (a) and (d). Fluorescence image (black and white) of the same STS after incubation with uo 4-AM (e). (From Sánchez-
Cárdenas, C. et al., Biol. Reprod., 87, 92, 2012.)
689Maitotoxin: An Enigmatic Toxic Molecule with Useful Applications in the Biomedical Sciences
The authors would like to thank José Luis de la Vega, Yoloxochitl Sánchez, and Shirley Ainsworth for
technical assistance. This work was supported by grants DGAPA-UNAM (IN202212 to CT, IN217210 to
ILG) and CONACyT (99333 to CT, 84362 to ILG) and Fondecyt (1110267 to JGR).
1. Plakas, S.M. and Dickey, R.W. 2010. Advances in monitoring and toxicity assessment of brevetoxins in
molluscan shellsh. Toxicon: Ofcial Journal of the International Society on Toxinology, 56, 137–149.
2. Fusetani, N. and Kem, W. 2009. Marine toxins: An overview. Progress in Molecular and Subcellular
Biology, 46, 1–44.
3. Yasumoto, T. 2001. The chemistry and biological function of natural marine toxins. The Chemical
Record, 1, 228–242.
4. Halstead, B.W. 1988. Poisonous and Venous Marine Animals of the World. Darwin Press, Princeton, NJ,
p. 1168.
5. Hashimoto, Y. 1979. Marine organisms which cause food poisoning. In Marine Toxins and Other
Bioactive Marine Metabolites. Japan Scientic Society Press, Tokyo, Japan, pp. 91–105.
6. Rey, J. 2007. Ciguatera. Available at: http://edis.ifas.u.edu/ENY-741 (accessed October 2007).
7. Yasumoto, T., Bagnis, R., and Vernoux, J. 1976. Toxicity of the surgeonshes-II properties of the princi-
pal water soluble toxin. Bulletin of the Japanese Society of Scientic Fisheries, 42, 359–366.
8. Yasumoto, T. 1971. Toxicity of the surgeonshes. Bulletin of the Japanese Society of Scientic Fisheries,
37, 724–734.
9. Friedman, M.A., Fleming, L.E., Fernandez, M., Bienfang, P., Schrank, K., Dickey, R., Bottein, M.-Y.
et al. 2008. Ciguatera sh poisoning: Treatment, prevention and management. Marine Drugs, 6,
10. Skinner, M.P., Brewer, T.D., Johnstone, R., Fleming, L.E., and Lewis, R.J. 2011. Ciguatera sh poisoning
in the Pacic Islands (1998 to 2008). PLoS Neglected Tropical Diseases, 5, e1416.
11. Sheppard, C. and Rioja-Nieto, R. 2005. Sea surface temperature 1871–2099 in 38 cells in the Caribbean
region. Marine Environmental Research, 60, 389–396.
12. Chateau-Degat, M., Chinain, M., Cerf, N., Gingras, S., Hubert, B., and Dewailly, E. 2005. Seawater
temperature, Gambierdiscus spp. variability and incidence of ciguatera poisoning in French Polynesia.
Harmful Algae, 4, 1053–1062.
13. Hale, S., Weinstein, P., and Woodward, A. 1999. Ciguatera (sh poisoning), el niño and the pacic sea
surface temperatures. Ecosystem Health, 5, 20–25.
14. Yokoyama, A., Murata, M., Oshima, Y., Iwashita, T., Yasumoto, T., and Chemistry, F. 1988. Some chemi-
cal properties of maitotoxin, a putative calcium channel agonist isolated from a marine dinoagellate.
Biochemistry Journal, 187, 184–187.
15. Murata, M. and Yasumoto, T. 2000. The structure elucidation and biological activities of high molecu-
lar weight algal toxins: Maitotoxin, prymnesins and zooxanthellatoxins. Natural Product Reports, 17,
16. Falkoner, I. 1993. Algal Toxins in Seafood and Drinking Water. Academic Press, San Diego, CA, p. 224.
17. Baden, D., Fleming, L.E., and Bean, J.A. 1995. Marine toxins. In Handbook of Clinical Neurology:
Intoxications of the Nervous System Part II. Natural Toxins and Drugs. F.A. de Wolff (Ed). Elsevier
Press, Amsterdam, the Netherlands, pp. 141–175.
18. Lewis, R. 2006. Ciguatera: Australian perspectives on a global problem. Toxicon, 48, 799–809.
19. Holmes, M. and Lewis, R. 1994. Purication and characterization of large and small maitotoxins from
cultured Gambierdiscus toxicus. Natural Toxins, 2, 64–72.
20. Holmes, M., Lewis, R., and Gillespie, N. 1990. Toxicity of Australian and French Polynesian strains of
Gambierdiscus toxicus (Dinophyceae) grown in culture: Characterization of a new type of maitotoxin.
Toxicon, 28, 1159–1172.
21. Hokama, Y. 1985. A rapid, simplied enzyme immunoassay stick test for the detection of ciguatoxin and
related polyethers from sh tissues. Toxicon, 23, 939–946.
22. Kellmann, R., Stüken, A., Orr, R.J.S., Svendsen, H.M., and Jakobsen, K.S. 2010. Biosynthesis and
molecular genetics of polyketides in marine dinoagellates. Marine Drugs, 8, 1011–1048.
690 Seafood and Freshwater Toxins: Pharmacology, Physiology, and Detection
23. Khosla, C., Gokhale, R.S., Jacobsen, J.R., and Cane, D.E. 1999. Tolerance and specicity of polyketide
synthases. Annual Review of Biochemistry, 68, 219–253.
24. Hotta, K., Chen, X., Paton, R.S., Minami, A., Li, H., Swaminathan, K., Mathews, I.I. et al. 2012.
Enzymatic catalysis of anti- Baldwin ring closure in polyether biosynthesis. Nature, 483, 355–358.
25. Murray, S.A., Garby, T., Hoppenrath, M., and Neilan, B.A. 2012. Genetic diversity, morphological unifor-
mity and polyketide production in dinoagellates (Amphidinium, Dinoagellata). PloS One, 7, e38253.
26. Van Wagoner, R.M., Deeds, J.R., Tatters, A.O., Place, A.R., Tomas, C.R., and Wright, J.L.C. 2010.
Structure and relative potency of several karlotoxins from Karlodinium venecum. Journal of Natural
Products, 73, 1360–1365.
27. Monroe, E.A. and Van Dolah, F.M. 2008. The toxic dinoagellate Karenia brevis encodes novel type
I-like polyketide synthases containing discrete catalytic domains. Protist, 159, 471–482.
28. Kubota, T., Iinuma, Y., and Kobayashi, J. 2006. Cloning of polyketide synthase genes from amphidino-
lide-producing dinoagellate Amphidinium sp. Biological & Pharmaceutical Bulletin, 29, 1314–1318.
29. Shimizu, Y., Yorimitsu, A., Maruyama, Y., Kubota, T., Aso, T., and Bronson, R.A. 1998. Prostaglandins
induce calcium inux in human spermatozoa. Molecular Human Reproduction, 4, 555–561.
30. Kwong, R.W.M., Wang, W.-X., Lam, P.K.S., and Yu, P.K.N. 2006. The uptake, distribution and elimina-
tion of paralytic shellsh toxins in mussels and sh exposed to toxic dinoagellates. Aquatic Toxicology
(Amsterdam, the Netherlands), 80, 82–91.
31. Monteiro, A. and Costa, P.R. 2011. Distribution and selective elimination of paralytic shellsh toxins in
different tissues of Octopus vulgaris. Harmful Algae, 10, 732–737.
32. Costa, P.R., Pereira, P., Guilherme, S., Barata, M., Nicolau, L., Santos, M.A., Pacheco, M., and Pousão-
Ferreira, P. 2012. Biotransformation modulation and genotoxicity in white seabream upon exposure to
paralytic shellsh toxins produced by Gymnodinium catenatum. Aquatic Toxicology (Amsterdam, the
Netherlands), 106–107, 42–47.
33. Liu, T., Cane, D.E., and Deng, Z. 2009. The enzymology of polyether biosynthesis. Methods in
Enzymology, 459, 187–214.
34. Minami, A., Migita, A., Inada, D., Hotta, K., Watanabe, K., Oguri, H., and Oikawa, H. 2011. Enzymatic
epoxide-opening cascades catalyzed by a pair of epoxide hydrolases in the ionophore polyether biosyn-
thesis. Organic Letters, 13, 1638–1641.
35. Minami, A., Shimaya, M., Suzuki, G., Migita, A., Shinde, S.S., Sato, K., Watanabe, K., Tamura, T.,
Oguri, H., and Oikawa, H. 2012. Sequential enzymatic epoxidation involved in polyether lasalocid bio-
synthesis. Journal of the American Chemical Society, 134, 7246–7249.
36. Yasumoto, T. 2001. The chemistry and biological function of natural marine toxins. Chemical Record
(New York), 1, 228–242.
37. Nakanishi, K. 1985. The chemistry of brevetoxins: A review. Toxicon, 23, 473–479.
38. Murata, M., Sasaki, M., Yokoyama, A., Iwashita, T., Gusovsky, F., Daly, J., and Yasumoto, T. 1992.
Partial structures and binding studies of maitotoxin, the most potent marine toxin. Bulletin de la Societe
de Pathologie Exotique, 85, 470–473.
39. Murata, M. and Yasumoto, T. 2000. The structure elucidation and biological activities of high molecu-
lar weight algal toxins: Maitotoxin, prymnesins and zooxanthellatoxins. Natural Product Reports, 17,
40. Nicolaou, K.C. and Frederick, M.O. 2007. On the structure of maitotoxin. Angewandte Chemie
(International ed. in English), 46, 5278–5282.
41. Nicolaou, K.C., Frederick, M.O., Burtoloso, A.C., Denton, R.M., Rivas, F., Cole, K.P., Aversa, R.J.,
Gibe, R., Umezawa, T., and Suzuki, T. 2008. Chemical synthesis of the GHIJKLMNO ring system of
Maitotoxin. Journal of the American Chemical Society, 130, 7466–7476.
42. Nakata, T. 2010. SmI2-induced cyclizations and their applications in natural product synthesis. Chemical
Record (New York), 10, 159–172.
43. Sakamoto, Y., Matsuo, G., Matsukura, H., and Nakata, T. 2001. Stereoselective syntheses of the CʹDʹEʹFʹ-
ring system of maitotoxin and the FG-ring system of gambierol. Organic Letters, 3, 2749–2752.
44. Morita, M., Haketa, T., Koshino, H., and Nakata, T. 2008. Synthetic studies on maitotoxin. 2.
Stereoselective synthesis of the WXYZAʹ-ring system. Organic Letters, 10, 1679–1682.
45. Morita, M., Ishiyama, S., Koshino, H., and Nakata, T. 2008. Synthetic studies on maitotoxin. 1.
Stereoselective synthesis of the CʹDʹEʹFʹ-ring system having a side chain. Organic Letters, 10,
691Maitotoxin: An Enigmatic Toxic Molecule with Useful Applications in the Biomedical Sciences
46. Satoh, M., Koshino, H., and Nakata, T. 2008. Synthetic studies on maitotoxin. 3. Stereoselective synthesis
of the BCDE-ring system. Organic Letters, 10, 1683–1685.
47. Nicolaou, K., Yang, Z., Shi, G., Gunzner, J., Agrios, K., and Gärtner, P. 1998. Total synthesis of breve-
toxin A. Nature, 392, 264–269.
48. Nicolaou, K.C., Gelin, C.F., Seo, J.H., Huang, Z., and Umezawa, T. 2010. Synthesis of the QRSTU
domain of maitotoxin and its 85-epi- and 86-epi-diastereoisomers. Journal of the American Chemical
Society, 132, 9900–9907.
49. Nicolaou, K.C., Aversa, R.J., Jin, J., and Rivas, F. 2010. Synthesis of the ABCDEFG ring system of
Maitotoxin. Journal of the American Chemical Society, 132, 6855–6861.
50. Nicolaou, K.C., Seo, J.H., Nakamura, T., and Aversa, R.J. 2011. Synthesis of the cʹdʹeʹfʹ domain of mai-
totoxin. Journal of the American Chemical Society, 133, 214–219.
51. Miyahara, J., Akau, C., and Yasumoto, T. 1979. Effects of ciguatoxin and maitotoxin on the isolated
guinea pig atria. Research Communications in Chemical Pathology and Pharmacology, 25, 177–180.
52. Takahashi, M., Ohizumi, Y., and Yasumoto, T. 1982. Maitotoxin, a Ca2+ channel activator candidate. The
Journal of Biological Chemistry, 257, 7287–7289.
53. Ohizumi, B.Y.Y. and Yasumotot, T. 1983. Contractile response of the rabbit aorta TO maitotoxin, the
most potent marine toxin. Journal of Physiology, 337, 711–721.
54. Miyamoto, T., Ohizumi, Y., Washio, H., and Yasumoto, Y. 1984. Potent excitatory effect of maitotoxin on
Ca channels in the insect skeletal muscle. Pugers Arch, 400, 439–441.
55. Freedman, S.B., Miller, R.J., Miller, D.M., and Tindall, D.R. 1984. Interactions of maitotoxin with
voltage-sensitive calcium channels in cultured neuronal cells. Proceedings of the National Academy of
Sciences of the United States of America, 81, 4582–4585.
56. Schettini, G., Koike, K., Login, I., Judd, A., Cronin, M., Yasumoto, T., and MacLeod, R. 1984. Maitotoxin
stimulates hormonal release and calcium ux in rat anterior pituitary cells in vitro. American Journal of
Physiology Endocrinology and Metabolism, 247, E520–E525.
57. Kobayashi, M., Ohizumi, Y., and Yasumoto, T. 1985. The mechanism of action of maitotoxin in relation to
Ca2+ movements in guinea-pig and rat cardiac muscles. British Journal of Pharmacology, 86, 385–391.
58. Legrand, A. and Bagnis, R. 1984. Effects of highly puried maitotoxin extracted from dinoagellate
Gambierdiscus toxicus on action potential of isolated rat heart. Journal of Molecular and Cellular
Cardiology, 16, 663–666.
59. Berta, P., Sladeczek, F., Derancourt, J., Durand, M., Travo, P., and Haiech, J. 1986. Maitotoxin stimulates
the formation of inositol phosphates in rat aortic myocytes. FEBS Letters, 197, 349–352.
60. Gusovsky, F., Yasumoto, T., and Daly, J. 1987. Maitotoxin stimulates phosphoinositide breakdown in
neuroblastoma hybrid NCB-20 cells. Cellular and Molecular Neurobiology, 7, 317–322.
61. Gusovsky, F., Daly, J.W., Yasumoto, T., and Rojas, E. 1988. Differential effects of maitotoxin on ATP secre-
tion and on phosphoinositide breakdown in rat pheochromocytoma cells. FEBS Letters, 233, 139–142.
62. Gusovsky, F., Yasumoto, T., and Daly, J.W. 1989. Maitotoxin, a potent, general activator of phosphoinosit-
ide breakdown. FEBS Letters, 243, 307–312.
63. Gusovsky, F., Yasumoto, T., and Daly, J. 1989. Calcium-dependent effects of maitotoxin on phosphoinositide
breakdown and on cyclic AMP accumulation in PCi 2 and NCB-20 cells. Molecular Pharmacology, 36, 44–53.
64. Gusovsky, F., Bitran, J.A., Yasumoto, T., and Daly, J.W. 1990. Mechanism of maitotoxin- stimulated phos-
phoinositide breakdown in HL-60 cells. The Journal of Pharmacology and Experimental Therapeutics,
252, 466–473.
65. Pin, J., Yasumoto, T., and Bockaert, J. 1988. Maitotoxin-evoked gamma-aminobutyric acid release is due
not only to the opening of calcium channels. Journal of Neurochemistry, 50, 1227–1237.
66. Sladeczek, F., Schmidt, B.H., Alonso, R., Vian, L., Tep, A., Yasumoto, T., Cory, R.N., and Bockaert, J.
1988. New insights into maitotoxin action. European Journal of Biochemistry, 174, 663–670.
67. Hamilton, S. and Perez, M. 1987. Toxins that affect voltage-dependent calcium channels. Biochemical
Pharmacology, 36, 3325–3329.
68. Kobayashi, M., Ochi, R., and Ohizumi, Y. 1987. Maitotoxin-activated single calcium channels in guinea-
pig cardiac cells. British Journal of Pharmacology, 92, 665–671.
69. Yoshii, M., Tsunoo, A., Kuroda, Y., Wu, C.H., and Narahashi, T. 1987. Maitotoxin-induced membrane
current in neuroblastoma cells. Brain Research, 424, 119–125.
70. Murata, M., Gusovsky, F., Yasumoto, T., and Daly, J. 1992. Selective stimulation of Ca2+ ux in cells by
maitotoxin. The European Journal of Pharmacology, 227, 43–49.
692 Seafood and Freshwater Toxins: Pharmacology, Physiology, and Detection
71. Xi, D., Van Dolah, F.M., and Ramsdell, J.S. 1992. Maitotoxin induces a calcium-dependent membrane
depolarization in GH4C1 pituitary cells via activation of type L voltage-dependent calcium channels. The
Journal of Biological Chemistry, 267, 25025–25031.
72. Nishio, M., Kigoshi, S., Muramatsu, I., and Yasumoto, T. 1993. Ca(2+)- and Na(+)- dependent depolariza-
tion induced by maitotoxin in the craysh giant axon. General Pharmacology, 24, 1079–1083.
73. Worley III, J.F., Mcintyre, M.S., Spencer, B., and Dukes, I.D. 1994. Depletion of intracellular Ca2+ stores
activates a maitotoxin-sensitive nonselective cationic current in beta-cells. The Journal of Biological
Chemistry, 269, 32055–32058.
74. Musgrave, I.F., Seifert, R., and Schultz, G. 1994. Maitotoxin activates cation channels distinct from the
receptor-activated non-selective cation channels of HL-60 cells. The Biochemical Journal, 301 (Pt 2),
75. Dietl, P. and Volkl, H. 1994. Maitotoxin activates a nonselective cation channel and Ca2+ entry in MDCK
renal epithelial cells. Molecular Pharmacology, 45, 300–305.
76. Young, R., McLaren, M., and Ramsdell, J. 1995. Maitotoxin increases voltage independent chloride and
sodium currents in GH4C1 rat pituitary cells. Natural Toxins, 3, 419–427.
77. Nishio, M., Muramatsu, I., and Yasumoto, T. 1996. Na(+)-permeable channels induced by maitotoxin in
guinea-pig single ventricular cells. European Journal of Pharmacology, 297, 293–298.
78. Estacion, M., Nguyen, H.B., Gargus, J.J., Estacion, M., and Bryant, H. 1996. Calcium is permeable
through a maitotoxin-activated nonselective cation channel in mouse L cells Calcium is permeable
through a maitotoxin-activated nonselective cation channel in mouse L cells. The American Journal of
Physiology-Cell Physiology, 270, 1145–1152.
79. Bielfeld-Ackermann, A., Range, C., and Korbmacher, C. 1998. Maitotoxin (MTX) activates a nonselec-
tive cation channel in Xenopus laevis oocytes. Pügers Archiv: European Journal of Physiology, 436,
80. Cataldi, M., Secondo, A., D’Alessio, A., Taglialatela, M., Hofmann, F., Klugbauer, N., Di Renzo, G., and
Annunziato, L. 1999. Studies on maitotoxin-induced intracellular Ca(2+) elevation in Chinese hamster
ovary cells stably transfected with cDNAs encoding for L- type Ca(2+) channel subunits. The Journal of
Pharmacology and Experimental Therapeutics, 290, 725–730.
81. Martínez-françois, J.R., Morales-tlalpan, V., and Vaca, L. 2002. Characterization of the maitotoxin-acti-
vated cationic current from human skin broblasts. Journal of Physiology, 538, 79–86.
82. Schilling, W.P., Sinkins, W.G., and Estacion, M. 1999. Maitotoxin activates a nonselective cation chan-
nel and a P2Z/P2X7-like cytolytic pore in human skin broblasts Maitotoxin activates a nonselective
cation channel and a P2Z/P2X7-like cytolytic pore in human skin broblasts. The American Journal of
Physiology, 277, C755–C765.
83. Schilling, W.P., Wasylyna, T., Dubyak, G.R., Humphreys, B.D., and Sinkins, W.G. 1999. Maitotoxin and
P2Z/P2X7 purinergic receptor stimulation activate a common cytolytic pore. The American Journal of
Physiology, 277, C766–C776.
84. Egido, W., Castrejón, V., Antón, B., and Martínez, M. 2008. Maitotoxin induces two dose-dependent
conductances in Xenopus oocytes. Comparison with nystatin effects as a pore inductor. Toxicon: Ofcial
Journal of the International Society on Toxicology, 51, 797–812.
85. Murata, M., Gusovsky, F., Sasaki, M., Yokoyama, A., Yasumoto, T., and Daly, J. 1991. Effect of mai-
totoxin analogues on calcium inux and phosphoinositide breakdown in cultured cells. Toxicon, 29,
86. Konoki, K., Hashimoto, M., Nonomura, T., Sasaki, M., Murata, M., and Tachibana, K. 1998. Inux in rat
glioma inhibition of maitotoxin-induced Ca2+ inux in rat glioma C6 cells by brevetoxins and synthetic
fragments of maitotoxin. Journal of Neurochemistry, 70, 409–416.
87. Oishi, T., Konoki, K., Tamate, R., Torikai, K., Hasegawa, F., Matsumori, N., and Murata, M. 2012.
Articial ladder-shaped polyethers that inhibit maitotoxin-induced Ca2+ inux in rat glioma C6 cells.
Bioorganic & Medicinal Chemistry Letters, 22, 3619–3622.
88. Konoki, K., Hashimoto, M., Murata, M., and Tachibana, K. 1999. Maitotoxin-induced calcium inux
in erythrocyte ghosts and rat glioma C6 cells, and blockade by gangliosides and other membrane lipids.
Chemical Research in Toxicology, 12, 993–1001.
89. Murata, M., Matsumori, N., Konoki, K., and Oishi, T. 2008. Structural features of dinoagellate
toxins underlying biological activity as viewed by NMR. Bulletin of the Chemical Society of Japan,
81, 307–319.
693Maitotoxin: An Enigmatic Toxic Molecule with Useful Applications in the Biomedical Sciences
90. Nicolaou, K.C., Frederick, M.O., and Aversa, R.J. 2008. The continuing saga of the marine polyether
biotoxins. Angewandte Chemie (International ed. in English), 47, 7182–7225.
91. Nicolaou, K. and Aversa, R.J. 2011. Maitotoxin: An inspiration for synthesis. Israel Journal of Chemistry,
51, 359–377.
92. Humphrey, W., Dalke, A., and Schulten, K. 1996. VMD: Visual molecular dynamics. Journal of
Molecular Graphics, 14, 33–38, 27–28.
93. Mori, M., Oishi, T., Matsuoka, S., Ujihara, S., Matsumori, N., Murata, M., Satake, M., Oshima, Y.,
Matsushita, N., and Aimoto, S. 2005. Ladder-shaped polyether compound, desulfated yessotoxin, inter-
acts with membrane-integral alpha-helix peptides. Bioorganic & Medicinal Chemistry, 13, 5099–5103.
94. Yamauchi, T., Kamon, J., Waki, H., Terauchi, Y., Kubota, N., Hara, K., Mori, Y. et al. 2001. The fat-
derived hormone adiponectin reverses insulin resistance associated with both lipoatrophy and obesity.
Nature Medicine, 7, 941–946.
95. McTaggart, J.S., Clark, R.H., and Ashcroft, F.M. 2010. The role of the KATP channel in glucose homeo-
stasis in health and disease: More than meets the islet. The Journal of Physiology, 588, 3201–3209.
96. Rorsman, P. and Braun, M. 2013. Regulation of insulin secretion in human pancreatic islets. Annual
Review of Physiology, 75, 1–25.
97. Uchida, K. and Tominaga, M. 2011. The role of thermosensitive TRP (transient receptor potential) chan-
nels in insulin secretion. Endocrine Journal, 58, 1021–1028.
98. Akiba, Y., Kato, S., Katsube, K., Nakamura, M., Takeuchi, K., Ishii, H., and Hibi, T. 2004. Transient
receptor potential vanilloid subfamily 1 expressed in pancreatic islet beta cells modulates insulin secre-
tion in rats. Biochemical and Biophysical Research Communications, 321, 219–225.
99. Cuypers, E., Yanagihara, A., Karlsson, E., and Tytgat, J. 2006. Jellysh and other cnidarian envenom-
ations cause pain by affecting TRPV1 channels. FEBS Letters, 580, 5728–5732.
100. Diaz-Garcia, C.M., Fuentes-Silva, D., Sanchez-Soto, C., Domínguez-Pérez, D., García- Delgado, N.,
Varela, C., Mendoza-Hernández, G., Rodriguez-Romero, A., Castaneda, O., and Hiriart, M. 2012. Toxins
from Physalia physalis (Cnidaria) raise the intracellular Ca2+ of beta-cells and promote insulin secretion.
Current Medicinal Chemistry, 19, 5414–5423.
101. Leech, C.A. and Habener, J.F. 1997. Insulinotropic glucagon-like peptide-1-mediated activation of
non-selective cation currents in insulinoma cells is mimicked by maitotoxin. The Journal of Biological
Chemistry, 272, 17987–17993.
102. Roe, M.W., Worley, J.F., Qian, F., Tamarina, N., Mittal, A.A., Dralyuk, F., Blair, N.T., Mertz, R.J.,
Philipson, L.H., and Dukes, I.D. 1998. Characterization of a Ca2+ release- activated nonselective cation
current regulating membrane potential and [Ca2+]i oscillations in transgenically derived beta-cells. The
Journal of Biological Chemistry, 273, 10402–10410.
103. Holz, G.G., Leech, C.A. and Habener, J.F. 2000. Insulinotropic toxins as molecular probes for analysis
of glucagon-like peptide-1 receptor-mediated signal transduction in pancreatic beta-cells. Biochimie.
82(9–10), 915–926.
104. Dinarello, C.A., Simon, A., and Van der Meer, J.W.M. 2012. Treating inammation by blocking interleu-
kin-1 in a broad spectrum of diseases. Nature Reviews: Drug Discovery, 11, 633–652.
105. Gabay, C., Lamacchia, C., and Palmer, G. 2010. IL-1 pathways in inammation and human diseases.
Nature Reviews Rheumatology, 6, 232–241.
106. Verhoef, P.A., Kertesy, S.B., Estacion, M., Schilling, W.P., and Dubyak, G.R. 2004. Maitotoxin induces
biphasic interleukin-1beta secretion and membrane blebbing in murine macrophages. Molecular
Pharmacology, 66, 909–920.
107. Mariathasan, S., Weiss, D.S., Newton, K., McBride, J., O’Rourke, K., Roose-Girma, M., Lee, W.P.,
Weinrauch, Y., Monack, D.M., and Dixit, V.M. 2006. Cryopyrin activates the inammasome in response
to toxins and ATP. Nature, 440, 228–232.
108. Federici, S., Caorsi, R., and Gattorno, M. 2012. The autoinammatory diseases. Swiss Medical Weekly,
142, 13602.
109. Verhoef, P.A., Estacion, M., Schilling, W., and Dubyak, G.R. 2003. P2X7 receptor-dependent blebbing
and the activation of Rho-effector kinases, caspases, and IL-1 beta release. Journal of Immunology
(Baltimore, MD: 1950), 170, 5728–5738.
110. Sinkins, W.G., Estacion, M., Prasad, V., Goel, M., Shull, G.E., Kunze, D.L., and Schilling, W.P. 2009.
Maitotoxin converts the plasmalemmal Ca(2+) pump into a Ca(2+)-permeable nonselective cation channel.
The American Journal of Physiology Cell Physiology, 297, C1533–C1543.
694 Seafood and Freshwater Toxins: Pharmacology, Physiology, and Detection
111. Darszon, A., Nishigaki, T., Beltran, C., and Trevino, C.L. 2011. Calcium channels in the development,
maturation, and function of spermatozoa. Physiological Review, 91, 1305–1355.
112. O’Toole, C.M., Arnoult, C., Darszon, A., Steinhardt, R.A., and Florman, H.M. 2000. Ca(2+) entry through
store-operated channels in mouse sperm is initiated by egg ZP3 and drives the acrosome reaction.
Molecular Biology of the Cell, 11, 1571–1584.
113. Jungnickel, M.K., Marrero, H., Birnbaumer, L., Lemos, J.R., and Florman, H.M. 2001. Trp2 regulates
entry of Ca2+ into mouse sperm triggered by egg ZP3. Natural Cell Biology, 3, 499–502.
114. Trevino, C.L., Serrano, C.J., Beltran, C., Felix, R., and Darszon, A. 2001. Identication of mouse trp
homologs and lipid rafts from spermatogenic cells and sperm. FEBS Letters, 509, 119–125.
115. Sutton, K.A., Jungnickel, M.K., Wang, Y., Cullen, K., Lambert, S., and Florman, H.M. 2004. Enkurin is
a novel calmodulin and TRPC channel binding protein in sperm. Devision of Biology, 274, 426–435.
116. Treviño, C.L., De la Vega-Beltrán, J.L., Nishigaki, T., Felix, R., and Darszon, A. 2006. Maitotoxin
potently promotes Ca2+ inux in mouse spermatogenic cells and sperm, and induces the acrosome reac-
tion. Journal of Cellular Physiology, 206, 449–456.
117. Chávez, J.C., De Blas, G.A., De la Vega-Beltrán, J.L., Nishigaki, T., Chirinos, M., González-González,
M.E., Larrea, F., Solís, A., Darszon, A., and Treviño, C.L. 2011. The opening of maitotoxin-sensitive
calcium channels induces the acrosome reaction in human spermatozoa: Differences from the zona pel-
lucida. Asian Journal of Andrology, 13, 159–165.
118. Reyes, J., Osses, N., Knox, M., Darszon, A., and Trevino, C. 2010. Glucose and lactate regulate mai-
totoxin-activated Ca2+ entry in spermatogenic cells: The role of intracellular [Ca2+]. FEBS Letters, 584,
119. Sánchez-Cárdenas, C., Guerrero, A., Treviño, C.L., Hernández-Cruz, A., and Darszon, A. 2012. Acute
slices of mice testis seminiferous tubules unveil spontaneous and synchronous Ca2+ oscillations in germ
cell clusters. Biology of Reproduction, 87, 92.
120. Treviño, C.L., Escobar, L., Vaca, L., Morales-Tlalpan, V., Ocampo, A.Y., and Darszon, A. 2008.
Maitotoxin: A unique pharmacological tool for elucidating Ca2+-dependent mechanisms. In Seafood and
Freshwater Toxins: Pharmacology, Physiology and Detection, 2nd edn. L.M. Botana (ed.). CRC Press,
Boca Ratón, FL, pp. 503–516.
121. Nicolaou, K., Duggan, M., and Hwang, C. 1986. New synthetic technology for the construction of oxo-
cenes. Journal of American Chemical Society, 108, 2468–2469.
... Their findings indicated that MTX's mode of action is the activation of cellular calcium channels. The structures and analogues were previously described by Reyes et al. [120]. ...
... Although the mode of action of KTX has not been studied specifically, this toxin showed massive potential as a piscicide and copepod-killing agent owing to its ichthyotoxicity and toxicity in copepods, respectively. MTX has attracted much attention due to its bioactivity, which involves disruption of cellular calcium homeostasis [120]. Reyes et al. [120] previously described in detail the biomedical applications of MTXs, wherein they proposed MTXs as a tool for analyzing ion channels and insulin secretion, interleukin-1β secretagogue and oncotic death induction, and sperm acrosome reaction induction [120]. ...
... MTX has attracted much attention due to its bioactivity, which involves disruption of cellular calcium homeostasis [120]. Reyes et al. [120] previously described in detail the biomedical applications of MTXs, wherein they proposed MTXs as a tool for analyzing ion channels and insulin secretion, interleukin-1β secretagogue and oncotic death induction, and sperm acrosome reaction induction [120]. OA is a selective inhibitor of the protein phosphatases PP1 and PP2A; thus, it can be used as a powerful probe for the study of regulatory mechanisms and neurotoxicity. ...
Dinoflagellates are an important group of phytoplanktons, characterized by two dissimilar flagella and distinctive features of both plants and animals. Dinoflagellate-generated harmful algal blooms (HABs) and associated damage frequently occur in coastal areas, which are concomitant with increasing eutrophication and climate change derived from anthropogenic waste and atmospheric carbon dioxide, respectively. The severe damage and harmful effects of dinoflagellate phycotoxins in the fishing industry have been recognized over the past few decades, and the management and monitoring of HABs have attracted much attention, leaving aside the industrial application of their valuable toxins. Specific modes of action of the organisms' toxins can effectively be utilized for producing beneficial materials, such as Botox and other therapeutic agents. This review aims to explore the potential industrial applications of marine dinoflagellate phycotoxins; furthermore, this review focuses on their modes of action and summarizes the available knowledge on them.
... This is the largest and most potent secondary metabolite ever isolated from the genus Gambierdiscus (G. pacificus, G. australes, and G. toxicus), and it comes in three different forms: MTX-1, MTX-2, and MTX-3 [144][145][146]. MTX is thought to be a powerful disruptor of Ca 2+ homeostasis, with a wide range of pharmacological properties on a variety of cell lines [144]. ...
... pacificus, G. australes, and G. toxicus), and it comes in three different forms: MTX-1, MTX-2, and MTX-3 [144][145][146]. MTX is thought to be a powerful disruptor of Ca 2+ homeostasis, with a wide range of pharmacological properties on a variety of cell lines [144]. It has the ability to initiate intracellular cascades of events such as membrane depolarization in excitable cells, insulin and neurotransmitter secretion, and phosphoinositide breakdown, which is imperative in cell lipids and cell signaling, programmed cell death, and fertilization, making it a useful tool for cell biology research, particularly when trying to understand Ca 2+ dependent cellular developments [143,[147][148][149]. ...
... It has the ability to initiate intracellular cascades of events such as membrane depolarization in excitable cells, insulin and neurotransmitter secretion, and phosphoinositide breakdown, which is imperative in cell lipids and cell signaling, programmed cell death, and fertilization, making it a useful tool for cell biology research, particularly when trying to understand Ca 2+ dependent cellular developments [143,[147][148][149]. In vivo, MTX seems to play a pivotal role in innate immune responses and inflammation in mice, making it a useful tool for studying specific aspects of the innate immune response and/or the physiology of inflammatory effector cells [144,150]. In Xenopus laevis oocytes, MTX was recently discovered to be a selective activator of an exact transient receptor potential (TRP) [151]. ...
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Phytoplankton are prominent organisms that contain numerous bioactive substances and secondary metabolites, including toxins, which can be valuable to pharmaceutical, nutraceutical, and biotechnological industries. Studies on toxins produced by phytoplankton such as cyanobacteria, diatoms, and dinoflagellates have become more prevalent in recent years and have sparked much interest in this field of research. Because of their richness and complexity, they have great potential as medicinal remedies and biological exploratory probes. Unfortunately, such toxins are still at the preclinical and clinical stages of development. Phytoplankton toxins are harmful to other organisms and are hazardous to animals and human health. However, they may be effective as therapeutic pharmacological agents for numerous disorders, including dyslipidemia, obesity, cancer, diabetes, and hypertension. In this review, we have focused on the properties of different toxins produced by phytoplankton, as well as their beneficial effects and potential biomedical applications. The anticancer properties exhibited by phytoplankton toxins are mainly attributed to their apoptotic effects. As a result, phytoplankton toxins are a promising strategy for avoiding postponement or cancer treatment. Moreover, they also displayed promising applications in other ailments and diseases such as Alzheimer’s disease, diabetes, AIDS, fungal, bacterial, schizophrenia, inflammation, allergy, osteoporosis, asthma, and pain. Preclinical and clinical applications of phytoplankton toxins, as well as future directi
... These difficulties in obtaining samples for biochemical analysis due to the animal treatment, sudden dead and the poor condition of some of the animals treated before sacrifice do not allow these parameters to be compared. The approach to obtain data about the acute i.p. toxicity of MTX1 yielded an estimated LD 50 of 1107 ng/kg after a 96-h observation period, a result that should be taken into account in view of the huge range of LD 50 doses reported so far for MTX1 which vary from 50 to 200,000 ng/kg (Munday et al. 2017;Murata et al. 1994;Reyes et al. 2014;Yokoyama et al. 1988). In agreement with previous studies on the i.p. toxicity of MTX1 (Murata et al. 1993), the lowest i.p. dose employed in this work, 0.2 μg/kg, already caused lethargy, piloerection (1/3 mice), and stretching (two out of three animals), however, at this dose, neither alterations in ALT, AST, CK and LDH parameters nor in the electrolyte balance were observed. ...
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Ciguatoxins are marine compounds that share a ladder-shaped polyether structure produced by dinoflagellates of the genus Gambierdiscus and Fukuyoa, and include maitotoxins (MTX1 and MTX3), ciguatoxins (CTX3C) and analogues (gambierone), components of one of the most frequent human foodborne illness diseases known as ciguatera fish poisoning. This disease was previously found primarily in tropical and subtropical areas but nowadays, the dinoflagellates producers of ciguatoxins had spread to European coasts. One decade ago, the European Food Safety Authority has raised the need to complete the toxicological available data for the ciguatoxin group of compounds. Thus, in this work, the in vivo effects of ciguatoxin-related compounds have been investigated using internationally adopted guidelines for the testing of chemicals. Intraperitoneal acute toxicity was tested for maitotoxin 1 at doses between 200 and 3200 ng/kg and the acute oral toxicity of Pacific Ciguatoxin CTX3C at 330 and 1050 ng/kg and maitotoxin 1 at 800 ng/kg were also evaluated showing not effects on mice survival after a 96 h observation period. Therefore, for the following experiments the oral subchronic doses were between 172 and 1760 ng/kg for gambierone, 10 and 102 ng/kg for Pacific Ciguatoxin CTX3C, 550 and 1760 ng/kg for maitotoxin 3 and 800, 2560 and 5000 ng/kg for maitotoxin 1. The results presented here raise the need to reevaluate the in vivo activity of these agents. Although the intraperitoneal lethal dose of maitotoxin 1 is assumed to be 50 ng/kg, without chemical purity identifications and description of the bioassay procedures, in this work, an intraperitoneal lethal dose of 1107 ng/kg was obtained. Therefore, the data presented here highlight the need to use a common procedure and certified reference material to clearly establish the levels of these environmental contaminants in food.
... They have been successfully isolated from fish tissue and proven to be voltage-gated sodium channel activators and voltage-gated potassium channels blockers, whose mechanism of action accounts for the diverse range of observed symptoms associated with ciguatera poisoning [4,[14][15][16]. In contrast, even though maitotoxins have been shown to increase calcium ion influx through excitable membranes, resulting in cell depolarization, hormone and neurotransmitter secretion, and breakdown of phosphoinositides, they are water soluble and do not readily accumulate in the food chain [17]. As maitotoxins have primarily been isolated from fish liver tissues, with only trace amounts present in the flesh [18], they are only considered potentially significant in cases when fish livers are being consumed, as may be the case in some highly CP endemic regions. ...
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Ciguatera poisoning is caused by the ingestion of fish or shellfish contaminated with ciguatoxins produced by dinoflagellate species belonging to the genera Gambierdiscus and Fukuyoa. Unlike in the Pacific region, the species producing ciguatoxins in the Atlantic Ocean have yet to be definitely identified, though some ciguatoxins responsible for ciguatera have been reported from fish. Previous studies investigating the ciguatoxin-like toxicity of Atlantic Gambierdiscus species using Neuro2a cell-based assay identified G. excentricus as a potential toxin producer. To more rigorously characterize the toxin profile produced by this species, a purified extract from 124 million cells was prepared and partial characterization by high-resolution mass spectrometry was performed. The analysis revealed two new analogs of the polyether gambierone: sulfo-gambierone and dihydro-sulfo-gambierone. Algal ciguatoxins were not identified. The very low ciguatoxin-like toxicity of the two new analogs obtained by the Neuro2a cell-based assay suggests they are not responsible for the relatively high toxicity previously observed when using fractionated G. excentricus extracts , and are unlikely the cause of ciguatera in the region. These compounds, however, can be useful as biomarkers of the presence of G. excentricus due to their sensitive detection by mass spectrometry.
... Harvesting of microalgal biomass and large-scale culturing for purification of CTXs and MTXs continues to be an important process towards providing the necessary toxin amounts for full structural characterization and production of (certified) reference materials [16]. With sufficient material available, novel therapeutic applications can be explored by the pharmaceutical industry for new drug development based on the unique affinity for CTXs on mammalian sodium channels [349,350] or MTXs for the study of calcium channel-dependent processes, innate immune response, and physiology of inflammatory effector cells [351]. Moreover, sufficient amounts of microalgal material would allow investigations into the presence of a variety of large molecules, middle molecular-weight compounds, and natural products for bioorganic/biochemical research [352]. ...
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Globally, the livelihoods of over a billion people are affected by changes to marine ecosystems, both structurally and systematically. Resources and ecosystem services, provided by the marine environment, contribute nutrition, income, and health benefits for communities. One threat to these securities is ciguatera poisoning; worldwide, the most commonly reported non-bacterial seafood-related illness. Ciguatera is caused by the consumption of (primarily) finfish contaminated with ciguatoxins, potent neurotoxins produced by benthic single-cell microalgae. When consumed, ciguatoxins are biotransformed and can bioaccumulate throughout the food-web via complex pathways. Ciguatera-derived food insecurity is particularly extreme for small island-nations, where fear of intoxication can lead to fishing restrictions by region, species, or size. Exacerbating these complexities are anthropogenic or natural changes occurring in global marine habitats, e.g., climate change, greenhouse-gas induced physical oceanic changes, overfishing, invasive species, and even the international seafood trade. Here we provide an overview of the challenges and opportunities of the 21st century regarding the many facets of ciguatera, including the complex nature of this illness, the biological/environmental factors affecting the causative organisms, their toxins, vectors, detection methods, human-health oriented responses, and ultimately an outlook towards the future. Ciguatera research efforts face many social and environmental challenges this century. However, several future-oriented goals are within reach, including digital solutions for seafood supply chains, identifying novel compounds and methods with the potential for advanced diagnostics, treatments, and prediction capabilities. The advances described herein provide confidence that the tools are now available to answer many of the remaining questions surrounding ciguatera and therefore protection measures can become more accurate and routine.
... Regarding water-soluble compounds produced by Gambierdiscus spp., which can be present in digestive viscera (see CTX classification), the mode of action of MTX is by inserting in the plasma membrane to increase massive influx of calcium (Reyes et al., 2014). Gambierol potently blocked K v channels in several models, whereas it had mild or no effect on Na v channels (Inoue et al. 2003;Ghiaroni et al. 2005Ghiaroni et al. , 2006Louzao et al. 2006;Cuypers et al. 2008;Schlumberger et al. 2010b;Cao et al. 2014). ...
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Rome, 19-23 November 2018, Food Safety and Quality Series, 9
... The toxic effects of the dinoflagellate extracts tested on mitochondrial bioenergetics, expressed by the significant inhibitory action on the mitochondrial respiratory chain for complex I, can be correlated with what is known for their toxicity. For instance, CTXs and MTXs (produced by Gambierdiscus) are amongst the most potent natural toxins known, which predominantly target the voltage-dependent Na + channel (Lombet et al., 1987) and cellular Ca 2+ disruption (Reyes et al., 2014). In fact, G. excentricus effects on mitochondria bioenergetics were detected at concentrations notably lower than those of the other dinoflagellate species, thus demonstrating its much higher toxicity, which is in line with data obtained at the cellular level . ...
Even though marine dinoflagellates are important primary producers, many toxic species may alter the natural equilibrium of aquatic ecosystems and even generate human intoxication incidents, as they are the major causative agents of harmful algal blooms. In order to deepen the knowledge regarding benthic dinoflagellate adverse effects, the present study aims to clarify the influence of Gambierdiscus excentricus strain UNR-08, Ostreopsis cf. ovata strain UNR-03 and Prorocentrum lima strain UNR-01 crude extracts on rat mitochondrial energetic function and permeability transition pore (mPTP) induction. Our results, expressed in number of dinoflagellate cell toxic compounds tested in a milligram of mitochondrial protein, revealed that 934 cells mg prot − 1 of G. excentricus, and 7143 cells mg prot − 1 of both O. cf. ovata and P. lima negatively affect mitochondrial function, including by decreasing ATP synthesis-related membrane potential variations. Moreover, considerably much lower concentrations of dinoflagellate extracts (117 cells mg prot − 1 of G. excentricus, 1429 cells mg prot − 1 of O. cf. ovata and 714 cells mg prot − 1 of P. lima) produced mPTP-induced swelling in Ca 2+-loaded isolated mitochondria. The present study clearly demonstrates the toxicity of G. excentricus, O. cf. ovata and P. lima extracts at the mitochondrial level, which may lead to mitochondrial failure and consequent cell toxicity, and that G. excentricus always provide much more severe effects than O. cf. ovata and P. lima.
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Marine phycotoxins are a multiplicity of bioactive compounds which are produced by microalgae and bioaccumulate in the marine food web. Phycotoxins affect the ecosystem, pose a threat to human health, and have important economic effects on aquaculture and tourism worldwide. However, human health and food safety have been the primary concerns when considering the impacts of phycotoxins. Phycotoxins toxicity information, often used to set regulatory limits for these toxins in shellfish, lacks traceability of toxicity values highlighting the need for predefined toxicological criteria. Toxicity data together with adequate detection methods for monitoring procedures are crucial to protect human health. However, despite technological advances, there are still methodological uncertainties and high demand for universal phycotoxin detectors. This review focuses on these topics, including uncertainties of climate change, providing an overview of the current information as well as future perspectives.
Azaspiracids (AZAs) are a group of biotoxins produced by the marine dinoflagellates Azadinium and Amphidoma spp. that can accumulate in shellfish and cause food poisoning in humans. Of the 60 AZAs identified, levels of AZA1, AZA2, and AZA3 are regulated in shellfish as a food safety measure based on occurrence and toxicity. Information about the metabolism of AZAs in shellfish is limited. Therefore, a fraction of blue mussel hepatopancreas was made to study the metabolism of AZA1–3 in vitro. A range of AZA metabolites were detected by liquid chromatography–high-resolution tandem mass spectrometry analysis, most notably the novel 22α-hydroxymethylAZAs AZA65 and AZA66, which were also detected in naturally contaminated mussels. These appear to be the first intermediates in the metabolic conversion of AZA1 and AZA2 to their corresponding 22α-carboxyAZAs (AZA17 and AZA19). α-Hydroxylation at C-23 was also a prominent metabolic pathway, producing AZA8, AZA12, and AZA5 as major metabolites of AZA1–3, respectively, and AZA67 and AZA68 as minor metabolites via double-hydroxylation of AZA1 and AZA2, but only low levels of 3β-hydroxylation were observed in this study. In vitro generation of algal toxin metabolites, such as AZA3, AZA5, AZA6, AZA8, AZA12, AZA17, AZA19, AZA65, and AZA66 that would otherwise have to be laboriously purified from shellfish, has the potential to be used for the production of standards for analytical and toxicological studies.
Azaspiracids (AZA) are lipophilic marine biotoxins associated with shellfish poisoning which are produced by some species of Amphidomataceae. Diversity and global biogeography of this family are still poorly known. In summer 2017 plankton samples were collected from the central Labrador Sea and western Greenland coast from 64° N (Gothaab Fjord) to 75° N for the presence of Amphidomataceae and AZA. In the central Labrador Sea, light microscopy revealed small Azadinium-like cells (9200 cells l⁻¹). Clonal strains established from plankton samples and scanning electron microscopy of fixed plankton samples revealed at least eight species of Amphidomataceae: Azadinium obesum, Az. trinitatum, Az. dexteroporum, Az. spinosum, Az. polongum, Amphidoma languida, Azadinium spec., and a new species described here as Azadinium perforatum sp. nov. The new species differed from other Azadinium species by the presence of thecal pores on the pore plate. All samples, including cultured strains, filtered seawater samples, and solid phase adsorption toxin tracking (SPATT) samplers deployed during the expedition in a continuous water-sampling system (FerryBox), were negative for AZA. DNA samples and PCR assays were positive for Amphidomataceae from most stations, whereas species-specific assays for three toxigenic species were rarely positive (two stations for Az. poporum, one station for Am. languida). The results highlight the presence of Amphidomataceae in the area but the lack of toxins and low abundance of toxigenic species currently indicate a low risk of toxic Amphidomataceae blooms in Arctic coastal waters.
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Specimens of surgeonfish Ctenochaetus striatus collected in Tahiti contained a water-soluble toxin in addition to ciguatoxin. The water-soluble toxin was tentatively named maitotoxin (MT) after the Tahitian name for surgeonfish maito. Purification of MT was achievable by the standard purification procedures for polar lipids. The toxin was eluted from a silicic acid column with chloroform-methanol (6:4) and from a cellulose column with chloroform-methanol-methanol-water (5:15:1). Upon gel-filtration through Sephadex G-25, it appeared in the fractions near void volume. Acid hydrolysis of the toxin afforded fatty acids, glucose and galactose, and 15 amino acids. The minimum lethal dose to mice by ip injection was estimated to be 15-20mg/kg. Guppies put in 40 ppm solution of MT died within 150min. These chemical and physiological properties indicated a close similarity of MT to the ichthyotoxin produced by the phytoflagellate Prymnesium parvum.
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Marine dinoflagellates are a rich source of structurally and biologically intriguing secondary metabolites. Among those, maitotoxin may be one of the best known examples, which is the largest natural product known to date and possesses the most potent toxicity known amongst non-proteinaceous compounds. Structural studies of maitotoxin are reviewed with a particular focus on the configuration and mode of action of this unique toxin. In addition, there are many marine natural products which bind to biomembranes to exert their biological activities. To gain a better understanding of their mode of action, conformation, and bimoleeular interaction occurring in biomembranes are particularly important. Recent results from NMR studies of membrane systems in the authors' group are reviewed briefly.
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Cholera toxin, pertussis toxin, mastoparan, maitotoxin, and alpha-latrotoxin are complex protein or polyether-based toxins of bacterial, insect, or phytoplankton origin that act with high potency at the endocrine pancreas to stimulate secretion of insulin from beta-cells located in the islets of Langerhans. The remarkable insulinotropic properties of these toxins have attracted considerable attention by virtue of their use as selective molecular probes for analyses of beta-cell stimulus-secretion coupling. Targets of the toxins include heptahelical cell surface receptors, GTP-binding proteins, ion channels, Ca(2+) stores, and the exocytotic secretory apparatus. Here we review the value of insulinotropic toxins from the perspective of their established use in the study of signal transduction pathways activated by the blood glucose-lowering hormone glucagon-like peptide-1 (GLP-1). Our analysis of one insulinotropic toxin (alpha-latrotoxin) leads us to conclude that there exists a process of molecular mimicry whereby the 'lock and key'analogy inherent to hormone-receptor interactions is reproduced by a toxin related in structure to GLP-1.
In the beginnings of the fourteenth century, some sailors traveling across the Atlantic Ocean became sick after eating sh, even if they were fresh. Upon other neurological disorders, some of these sailors felt an inversion of thermal sense, a characteristic symptom named “dry ice sensation.” Upon touching the cold seawater, the sailor would feel as if he was receiving an electric shock. This mode of poisoning was later called “ciguatera” after cigua, a snail commonly occurring in the Caribbean Sea [1,2]. However, most of the neurological symptoms of ciguatera are due to ciguatoxin (CTX), a very potent brevetoxin-type polyether compound [3,4].
Maitotoxin (MTX), the most potent marine toxin known, produced a dose-dependent positive inotropic effect on guinea-pig isolated left atria and rat ventricle strips at concentrations of 0.1 ng to 4 ng ml-1. MTX (4 ng ml-1) also exhibited a positive chronotropic effect on guinea-pig right atria. The MTX-induced inotropic effect was almost abolished by Co2+ or verapamil, but was little affected by propranolol, reserpine or tetrodotoxin. The tissue Ca content of guinea-pig left atria was increased by MTX (2-30 ng ml-1) in a dose-dependent manner, and this increase was markedly inhibited by Co2+ or verapamil. Furthermore, on the rat isolated cardiac myocytes MTX (0.01-10 ng ml-1) caused an arrhythmogenic effect which was followed by their transformation into irreversibly rounded cells. The effects of MTX on the isolated cells were inhibited by verapamil or Ca2+-free solution. These results suggest that the excitatory effects of MTX on heart muscle are caused by a direct action on the cardiac muscle membrane mainly due to an increase in Ca2+ permeability.
[GRAPHICS] The stereoselective syntheses of the C 'D 'E 'F ' -ring system of maitotoxin and the FG-ring system of gambierol were accomplished. The key steps involve 6-endo-cyclization of methylepoxide, Sml(2)-induced reductive cyclization, 6-endo-cyclization of vinylepoxide, and formation of the lactone ring.
Octopus (Octopus vulgaris, Cuvier) plays a central role in the marine food web, being an important consumer with high metabolic rates and at the same time an important food item for higher predators. After harmful algal blooms, octopus can accumulate high levels of marine toxins trough trophic interrelationships. The aim of this study is to characterize the distribution of paralytic shellfish toxins (PSTs) in selected tissues of the O. vulgaris, in order to assess the translocation of toxins among organs with different physiological functions. Different retention times and selective elimination of particular toxin analogues were also investigated. Twenty three specimens of O. vulgaris were captured in Peniche (NW coast of Portugal) after PSTs have been detected in molluscan bivalves. Tissue matrices were dissected from organs with digestive function (digestive gland, stomach and salivary glands) and excretory function (kidneys and branchial hearts) and analyzed for toxin determination. Toxin analysis was carried out by high performance liquid chromatography with fluorescence detection (LC-FLD). PSTs were found in all tissues analyzed. The highest toxin concentrations were found in the digestive gland, reaching a maximum of 2980μ−1. The toxin profile was constituted by dcSTX, B1, C1+2, dcGTX2+3, dcNEO, STX and GTX2+3. A lower number of toxins were identified in the remaining organs, with B1 and dcSTX compromising more than 90% in molar fraction. Decarbamoyl saxitoxin was the most abundant toxin detected in digestive gland, stomach and salivary glands, while B1 was dominant in organs with excretory function. A positive correlation of concentrations of B1 and dcSTX were found in the organs analyzed. Results indicate that B1 and dcSTX are assimilated into the digestive gland in a similar proportion. Selective elimination of toxins with higher elimination of B1 and retention of dcSTX is suggested. This study contributes to better understanding of the dynamics of PSTs in O. vulgaris and the fate of PSTs in the food web.