Inhibitor Report for: Guanitoxin

Changes in environmental conditions in aquatic ecosystems caused by anthropic actions can modify the composition of primary producers, promoting the excessive proliferation of cyanobacteria. These organisms can form cyanobacterial blooms, which directly affect aquatic life. The present study investigated the mutagenicity of the cyanobacterium Sphaerospermopsis torques-reginae (strain ITEP-024), guanitoxin-producing (natural organophosphate), and sublethal effects on fish in relevant environment concentrations. For this, the Ames test (Salmonella/microsome) was performed as a mutagenic assay for extracts of the ITEP-024 strain. Specimens of Oreochromis niloticus (Teleostei: Cichlidae) were subjected to acute 96 h exposure to different concentrations of aqueous extract of the strain: C = control group; T1 = 31.25 mg/L; T2 = 62.5 mg/L; T3 = 125 mg/L; and T4 = 250 mg/L. Genotoxic, biochemical, osmoregulatory, and physiologic biomarkers were analyzed. Our results showed that the cyanobacterium had a weak mutagenic response for the TA102 strain of Salmonella with and without metabolic activation by S9. Strains TA98 and TA100 were not affected. Fish from treatments T3 and T4 showed changes in oxidative stress (CAT, SOD, and GST enzymes), inhibition of the enzyme acetylcholinesterase activity, micronucleus formation, and osmoregulatory disorders. No guanitoxin accumulation was detected in the different tissues of O. niloticus by LC-MS/MS. Our results showed unprecedented mutagenicity data of the guanitoxin-producing cyanobacteria by the Ames test and biochemical, osmoregulatory, and genotoxic disorders in fish, providing efficient aquatic contamination biomarkers. Despite the great concern related to the presence of guanitoxin in blooms in freshwater ecosystems, its concentration is not yet regulated, and thus there is no monitoring agenda in current legislation.

Anatoxin-a(S) is the most potent natural neurotoxin produced by fresh water cyanobacteria. It is also the least understood and monitored. Although this potent cholinesterase inhibitor was first reported in the 1970s and connected with animal poisonings, the lack of chemical standards and identified biosynthetic genes together with limited diagnostics and acute reactivity of this naturally-occurring organophosphate have limited our understanding of its environmental breadth and human health implications. Anatoxin-a(S) irreversibly inhibits acetylcholinesterase much like other organophosphate agents like paraoxon. It is however often confused with the similarly named anatoxin-a that has a completely different chemical structure, mechanism of action, and biosynthesis. Herein we propose renaming of anatoxin-a(S) to clarify its distinct structure and mechanism and to draw renewed attention to this potent natural poison. We propose the new name guanitoxin (GNT) to emphasize its distinctive guanidino organophosphate chemical structure.

Calves, rats, ducks, and goldfish given lethal oral doses of bacteria-free lyophilized cell suspensions of toxic Anabaena flos-aquae died as a result of respiratory arrest. Experiments with selected animals and pharmacological preparations showed that the main effect of the toxin was production of a sustained postsynaptic depolarizing neuromuscular blockade.

Changes in environmental conditions in aquatic ecosystems caused by anthropic actions can modify the composition of primary producers, promoting the excessive proliferation of cyanobacteria. These organisms can form cyanobacterial blooms, which directly affect aquatic life. The present study investigated the mutagenicity of the cyanobacterium Sphaerospermopsis torques-reginae (strain ITEP-024), guanitoxin-producing (natural organophosphate), and sublethal effects on fish in relevant environment concentrations. For this, the Ames test (Salmonella/microsome) was performed as a mutagenic assay for extracts of the ITEP-024 strain. Specimens of Oreochromis niloticus (Teleostei: Cichlidae) were subjected to acute 96 h exposure to different concentrations of aqueous extract of the strain: C = control group; T1 = 31.25 mg/L; T2 = 62.5 mg/L; T3 = 125 mg/L; and T4 = 250 mg/L. Genotoxic, biochemical, osmoregulatory, and physiologic biomarkers were analyzed. Our results showed that the cyanobacterium had a weak mutagenic response for the TA102 strain of Salmonella with and without metabolic activation by S9. Strains TA98 and TA100 were not affected. Fish from treatments T3 and T4 showed changes in oxidative stress (CAT, SOD, and GST enzymes), inhibition of the enzyme acetylcholinesterase activity, micronucleus formation, and osmoregulatory disorders. No guanitoxin accumulation was detected in the different tissues of O. niloticus by LC-MS/MS. Our results showed unprecedented mutagenicity data of the guanitoxin-producing cyanobacteria by the Ames test and biochemical, osmoregulatory, and genotoxic disorders in fish, providing efficient aquatic contamination biomarkers. Despite the great concern related to the presence of guanitoxin in blooms in freshwater ecosystems, its concentration is not yet regulated, and thus there is no monitoring agenda in current legislation.

Anatoxin-a(S) is the most potent natural neurotoxin produced by fresh water cyanobacteria. It is also the least understood and monitored. Although this potent cholinesterase inhibitor was first reported in the 1970s and connected with animal poisonings, the lack of chemical standards and identified biosynthetic genes together with limited diagnostics and acute reactivity of this naturally-occurring organophosphate have limited our understanding of its environmental breadth and human health implications. Anatoxin-a(S) irreversibly inhibits acetylcholinesterase much like other organophosphate agents like paraoxon. It is however often confused with the similarly named anatoxin-a that has a completely different chemical structure, mechanism of action, and biosynthesis. Herein we propose renaming of anatoxin-a(S) to clarify its distinct structure and mechanism and to draw renewed attention to this potent natural poison. We propose the new name guanitoxin (GNT) to emphasize its distinctive guanidino organophosphate chemical structure.

The detection of cyanotoxins, such as the anatoxin-a(s), is essential to ensure the biological safety of water environments. Here, we propose the use of Nauphoeta cinerea cockroaches as an alternative biological model for the biomonitoring of the activity of anatoxin-a(s) in aquatic systems. In order to validate our proposed model, we compared the effects of a cyanobacterial extract containing anatoxin-a(s) (CECA) with those of the organophosphate trichlorfon (Tn) on biochemical and physiological parameters of the nervous system of Nauphoeta cinerea cockroaches. In brain homogenates from cockroaches, CECA (5 and 50mug/g) inhibited acetylcholinesterase (AChE) activity by 53+/-2% and 51+/-7%, respectively, while Tn (5 and 50mug/g) inhibited AChE activity by 35+/-4% and 80+/-9%, respectively (p<0.05; n=6). Moreover, CECA at concentrations of 5, 25, and 50microg/g decreased the locomotor activity of the cockroaches, diminishing the distance travelled and increasing the frequency and duration of immobile episodes similarly to Tn (0.3mug/g) (p<0.05, n=40, respectively). CECA (5, 25 and 50mug/g) induced an increase in the leg grooming behavior, but not in the movement of antennae, similarly to the effect of Tn (0.3mug/g). In addition, both CECA (50microg/200mul) and Tn (0.3microg/200mul) induced a negative chronotropism in the insect heart (37+/-1 and 47+/-8 beats/min in 30min, respectively) (n=9, p>0.05). Finally, CECA (50microg/g), Tn (0.3microg/g) and neostigmine (50microg/g) caused significant neuromuscular failure, as indicated by the monitoring of the in vivo neuromuscular function of the cockroaches, during 100min (n=6, p<0.05, respectively). In conclusion, sublethal doses of CECA provoked entomotoxicity. The Tn-like effects of CECA on Nauphoeta cinerea cockroaches encompass both the central and peripheral nervous systems in our insect model. The inhibitory activity of CECA on AChE boosts a cascade of signaling events involving octopaminergic/dopaminergic neurotransmission. Therefore, this study indicates that this insect model could potentially be used as a powerful, practical, and inexpensive tool to understand the impacts of eutrophication and for orientating decontamination processes.

Anatoxin-a(s) is a guanidinemethyl phosphate ester isolated from the freshwater cyanobacterium (blue-green algae) Anabaena flos-aquae strain NRC 525-17. Previous work has shown anatoxin-a(s) to be a potent irreversible inhibitor of electric eel acetylcholinesterase (AChE, EC 3.1.1.7). Anatoxin-a(s) has been shown to be an active site-directed inhibitor of AChE, which is resistant to reactivation by oximes because of the enzyme-oxime adduct formation. In vivo pretreatment with physostigmine and high concentrations of pyridine 2-aldoxime methochloride (2-PAM) were the only effective antagonists against a lethal dose of anatoxin-a(s). Anatoxin-a(s) is very toxic and it is produced by cyanobacteria during its blooms. Purified toxin has an LD50 (i.p) of approximately 20-50 g/kg body weight in mice. Toxicoses associated with cholinesterase-inhibiting anatoxin-a(s) have been observed in humans, animals, birds and fish. Anatoxin-a(s) induces clinical signs of hypercholinergic preponderance, such as salivation, lacrimation, urinary incontinence, defecation, convulsion, fasciculation, and respiratory arrest.

Worldwide development of cyanobacterial blooms has significantly increased in marine and continental waters in the last century due to water eutrophication. This phenomenon is favoured by the ability of planktonic cyanobacteria to synthesize gas vesicles that allow them to float in the water column. Besides, benthic cyanobacteria that proliferate at the bottom of lakes, rivers and costal waters form dense mats near the shore. Cyanobacterial massive proliferation is of public concern regarding the capacity of certain cyanobacterial strains to produce hepatotoxic and neurotoxic compounds that can affect public health, human activities and wild and stock animals. The cholinergic synapses and voltage-gated sodium channels constitute the targets of choice of cyanobacterial neurotoxins. Anatoxin-a and homoanatoxin-a are agonists of nicotinic acetylcholine receptors. Anatoxin-a(s) is an irreversible inhibitor of acetylcholinesterase. Saxitoxin, kalkitoxin and jamaicamide are blockers of voltage-gated sodium channels, whereas antillatoxin is an activator of such channels. Moreover the neurotoxic amino acid l-beta-N-methylamino-l-alanine was shown to be produced by diverse cyanobacterial taxa. Although controversial, increasing in vivo and in vitro evidence suggest a link between the ingestion of l-beta-N-methylamino-l-alanine and the development of amyotrophic lateral sclerosis/Parkinsonism-dementia complex, a neurodegenerative disease. This paper reviews the occurrence of cyanobacterial neurotoxins, their chemical properties, mode of action and biosynthetic pathways.

Anatoxin-a(s) is a potent irreversible inhibitor of the enzyme acetylcholinesterase with a unique N-hydroxyguanidine methylphosphate ester chemical structure. Determination of this toxin in environmental samples is hampered by the lack of specific methods for its detection. Using the toxic strain of Anabaena lemmermani PH-160 B as positive control, the fragmentation characteristics of anatoxin-a(s) under collision-induced dissociation conditions have been investigated and new LC-MS/MS methods proposed. Recommended ion transitions for correct detection of this toxin are 253>58, 253>159, 235>98 and 235>96. Chromatographic separation is better achieved under HILIC conditions employing a ZIC-HILIC column. This method was used to confirm for the first time the production of anatoxin-a(s) by strains of Anabaena oumiana ITEP-025 and ITEP-026. Considering no standard solutions are commercially available, our results will be of significant use for the correct identification of this toxin by LC-MS/MS.

Bioassays are little used to detect individual toxins in the environment because, compared to analytical methods, these assays are still limited by several problems, such as the sensitivity and specificity of detection. We tentatively solved these two drawbacks for detection of anatoxin-a(s) by engineering an acetylcholinesterase to increase its sensitivity and by using a combination of mutants to obtain increased analyte specificity. Anatoxin-a(s), a neurotoxin produced by some freshwater cyanobacteria, was detected by measuring the inhibition of acetylcholinesterase activity. By using mutated enzyme, the sensitivity of detection was brought to below the nanomole-per-liter level. However, anatoxin-a(s) is an organophosphorous compound, as are several synthetic molecules which are widely used as insecticides. The mode of action of these compounds is via inhibition of acetylcholinesterase, which makes the biotest nonspecific. The use of a four-mutant set of acetylcholinesterase variants, two mutants that are sensitive to anatoxin-a(s) and two mutants that are sensitive to the insecticides, allows specific detection of the cyanobacterial neurotoxin.

Anatoxin-a(s) is a hazardous toxin released by cyanobacteria during bacterial blooms. A simple and fast method to detect this hazardous compound using a biosensor based on the electrochemical detection of the activity of acetylcholinesterase was developed. Among several acetylcholinesterases, electric eel enzyme was found to be the most sensitive to anatoxin-a(s) and was thus used to build disposable amperometric sensors. The system displayed a detection limit of 1 microg/L anatoxin-a(s). No unspecific effect was noticed with real water samples but spiked toxin was accurately detected. Oxime reactivation was used to discriminate between the toxin and potential insecticides present in the sample.

Toxic freshwater cyanobacteria can contaminate water supplies and adversely effect humans, agricultural livestock, and wildlife. Toxicity is strain-specific so morphological observations alone cannot predict the hazard level. Two microtiter plate based bioassays have emerged for measuring saxitoxin (STX) and its derivatives, commonly found in the freshwater cyanobacteria Anabaena and Aphanizomenon. They use radioactively labeled STX binding by sodium channels, STX's pharmacological target, or an unrelated protein, saxiphilin. These bioassays were challenged with extracts of toxic and nontoxic strains of Anabaena circinalis, and the results were compared with HPLC analysis. Both radioreceptor assays had detection limits of 2 microg STX equivalents (STXeq)/L, which is belowthe concentration proposed for a health alert, namely 3 microg STXeq/L. In all cases, statistically significant correlations existed between all toxicity measurements of the same extracts with the methods used herein. Sodium channel and saxiphilin assays however predicted less toxicity relative to HPLC analysis. The only exception to this was the equivalency observed between saxiphilin measurement and HPLC quantitation corrected for mammalian toxicity. Saxiphilin assay predicted toxicity in one strain was 3 orders of magnitude more than by sodium channel assay, and no STX was detected by HPLC. Lack of acetylcholinesterase inhibition showed this bioactivity was not anatoxin-a(S), a toxin also produced by this A. circinalis with some resemblance to the region of STX bound by saxiphilin. Presence of anatoxin-a(S) was predicted for another strain by this same acetylcholinesterase assay that, if confirmed by chemical analysis, would be the first report of anatoxin-a(S) in an Australian cyanobacterium.

Ten natural bloom samples of cyanobacteria from the Danish lakes Knud so (5), Ravn so (4), and Salten Langso (1) collected during 1993-1995 were assayed for toxicity by mouse bioassay, for acetylcholinesterase inhibiting activity by a colorimetric method, and for microcystins by enzyme-linked immunosorbent assay. In the mouse bioassay, seven samples were neurotoxic, two were non-toxic and one gave a protracted toxic response. One of the non-toxic and the single protracted toxic sample both contained anticholinesterase activity equivalent to 4 micrograms anatoxin-a(s) g-1. The neurotoxic samples contained equivalents to 20-3300 micrograms anatoxin-a(s) g-1. The highest anticholinesterase activities (equivalent to 2300 and 3300 micrograms anatoxin-a(s) g-1, respectively) were found in samples collected from Lake Knud so in connection with bird-kills in 1993 and 1994. Small amounts of microcystins (0.1-0.9 microgram g-1) were detected in all samples but one. All Lake Knud so and Lake Ravn so samples were dominated by Anabaena lemmermannii, and the Lake Salten Langso sample by several species of Anabaena. Gel filtration profiles indicated similarity between the toxic component from the Lake Knud so 1994 bloom with registered bird-kills and anatoxin-a(s) isolated from Anabaena flos-aquae NRC-525-17. Anticholinesterase-producing cultures of A. lemmermannii were isolated from the Lake Knud so 1993 bloom. These laboratory cultures produced anatoxin-a(s) equivalents of 29-743 micrograms g-1. Other cultures of A. lemmermannii isolated from Lake Knud so and Lake Ravn so were hepatotoxic or non-toxic. Dead birds collected from Lake Knud so during the neurotoxic 1993 Anabaena bloom possibly died from cyanobacterial toxicosis. The stomach contents contained colonies and single trichomes of Anabaena, and anticholinesterase activities equivalent to 2.1-89.7 micrograms anatoxin-a(s) kg-1 body weight and microcystins (53-95 ng kg-1) were also detected.

Experimental investigations were carried out with cultured and lyophilized material of the toxigenic strain Oscillatoria NIVA-CYA 92. This organism is classified as Phormidium formosum (Boryex Gom.) Anagnet kom. Aqueous extracts of the algal material, containing the bioactive secondary amine alkaloid 2-(propan-1-oxo-1-yl)-9-azabicyclo(4,2,1)non-2ene (homoanatoxin-a) in an amount of 2.57 micrograms/mg lyophilized material, were tested for acute in vivo toxicity in mice, and for toxicity on neuromuscular transmission by means of electrophysiological methods on the isolated phrenic-nerve hemidiaphragm from rat and in the frog rectus abdominis assay. Acute toxic effects in mice were observed by i.p. and oral (by gavage) administration. Lethal doses were in the range 112-225 and 1125-2250 mg of freeze-dried algal material per kg body weight (i.e. 288-578 and 2890-5780 micrograms homoanatoxin-a/ kg body weight), respectively. The nerve-initiated muscle contractions in the rat diaphragm were blocked by about 0.125 mg cyanophyte material per ml bath solution (i.e. 0.32 microgram homoanatoxin-a/ml or 1.8 microM), but muscle contractions, although slightly reduced, could still be elicited by direct electrical stimulation of the muscle. The compound action potentials recorded from the main phrenic-nerve trunk were not affected. An additive blocking effect on partly curarized preparations was observed and cholinesterase inhibition by physostigmine (eserine) transiently augmented the muscle twitch contraction in preparations partly blocked by the extract. Intracellular recordings from single muscle fibers of homoanatoxin-a-treated rat hemidiaphragm disclosed a partial depolarization and a decrease in the endplate potential to subthreshold level simultaneously with a decrease and then complete disappearance of the miniature endplate potentials. The neuromuscular transmission block was reversed by washing. The extract produced muscle contractions in the frog rectus abdominis assay. Homoanatoxin-a in the algal material was readily absorbed from the gastrointestinal tract in mice. Blockade of the neuromuscular transmission of the respiratory muscle may partly explain the acute toxic effects observed in mice. Thus, the main target of the homoanatoxin-a action at the mammalian neuromuscular junction was traced to the postsynaptic nicotinic acetylcholine receptor channel complex, where it reduced the sensitivity to the transmitter substance.

The reversibility of inhibition of plasma, red blood cell (RBC), and diaphragm cholinesterase (ChE) and clinical signs in mice given anatoxin-a(s) [antx-a(s)], a ChE inhibitor from Anabaena flos-aquae NRC-525-17, were characterized and compared with the effects of 2 known ChE inhibitors, the organophosphorus compound paraoxon and the carbamate pyridostigmine bromide. To follow recovery of ChE activity, mice were given either a control solution or an LD40 dose of one of the toxicants ip and killed at time points up to 8 d postdosing. After dosing, mice were monitored for diarrhea, fasciculations, respiratory difficulty, salivation, and tremors. In general, clinical signs in mice given antx-a(s) persisted longer than in mice given pyridostigmine and were more similar in duration to the clinical signs in mice given paraoxon. Histologic lesions were not detected in tissues of mice killed after administration of antx-a(s). Anatoxin-a(s) inhibited lesions were diaphragm ChE for greater than 1 but less than 2 d and RBC ChE for 8 d. The time required for recovery from Antx-a(s)-induced inhibition of ChE in plasma, RBC, and diaphragm was similar to or longer than that with paraoxon and longer than that with pyridostigmine. Based on the duration of antx-a(s) induced clinical signs and ChE inhibition in mice, antx-a(s) appears to be an in vivo irreversible inhibitor of ChE.

Anatoxin-a(s) is a guanidine methyl phosphate ester (unprotonated molecular ion equals 252 daltons) isolated from the freshwater cyanobacterium (blue-green alga) Anabaena flos-aquae strain NRC 525-17. Previous work has shown anatoxin-a(s) to be a potent irreversible inhibitor of electric eel acetylcholinesterase (EC 3.1.1.7, AChE). In the present study the interaction of anatoxin-a(s) with AChE was investigated by protection studies and since similarities have been noted between anatoxin-a(s) and the synthetic organophosphate anticholinesterases, the ability of reactivators to reactivate the inhibited enzyme was investigated. Treatments directed toward eliminating poisoning symptoms and in vivo protection from anatoxin-a(s) poisonings were investigated using oxime reactivators and atropine or pretreatment with a carbamate and atropine. Anatoxin-a(s) was shown to be an active site-directed inhibitor of acetylcholinesterase which is resistant to oxime reactivation due to the structure of its enzyme adduct. In vivo pretreatment with physostigmine and high concentrations of 2-PAM were the only effective antagonists against a lethal dose of anatoxin-a(s).

The pathophysiologic effects of anatoxin-a(s) from the cyanobacterium Anabaena flos-aquae NRC-525-17 were investigated in anaesthetized adult male Sprague Dawley rats given the toxin by continuous intravenous infusion until death. Rats (n = 6) pretreated with atropine sulfate (50 mg/kg) intraperitoneally survived significantly longer (P less than 0.05) than non-atropinized rats (n = 6), suggesting that the muscarinic effects of anatoxin-a(s) were important in the lethal syndrome. In contrast to rats only given toxin, rats that were pretreated with atropine had a decrease in heart rate and mean blood pressure that followed profound reductions in respiratory tidal and minute volume, suggesting that neuromuscular blockade of the muscles of respiration was the cause of death. Even when survival time of rats was increased by pretreatment with atropine, phrenic nerve amplitude increased, indicating a lack of a depressive effect of anatoxin-a(s) on central mediation of respiration. Rats (n = 3) continuously ventilated during toxin infusion survived a dose more than 4 fold greater than a consistently lethal dose of the toxin. Thus, the cardiovascular effects of anatoxin-a(s) alone could not account for the death of rats. Electromyographic activity recorded from the diaphragms of rats (n = 5) during continuous toxin administration revealed an increase in muscular electrical activity that became more random and finally decreased prior to death, suggesting a toxin-induced neuromuscular blockade in vivo which ultimately was the cause of death of the anatoxin-a(s) dosed rats.

Adult male Long-Evans rats were injected intraperitoneally with 1.5, 3.0 or 9.0 micrograms/kg of anatoxin-a(s) that had been extracted from laboratory-grown Anabaena flos-aquae NRC-525-17, 800 micrograms/kg of paraoxon, or a control solution. Blood, anterior spinal cord, and brain cerebellar, cortical, medullary, midbrain, hippocampal, hypothalamic, olfactory and striatal cholinesterase activity was determined in rats that died prior to 2 hours or were anesthetized and killed at 2 hours. Unlike paraoxon, anatoxin-a(s) did not cause detectable inhibition of cholinesterase in the central nervous system, but did cause inhibition of cholinesterase in blood, suggesting that anatoxin-a(s) is strictly a peripheral cholinesterase inhibitor.

The effects of anatoxin-a(s) [antx-a(s)] from the cyanobacterium Anabaena flos-aquae NRC-525-17 on mean arterial blood pressure, heart rate, respiratory rate, tidal volume, minute volume, and phrenic nerve activity were evaluated in anesthetized Sprague-Dawley rats. Anatoxin-a(s) was administered by continuous intravenous infusion. The initial effect of the toxin was to slow the heart rate and reduce arterial blood pressure, followed by much more pronounced reductions in these parameters. The marked decline in heart rate and blood pressure frequently occurred before there was a large decrease in respiratory minute volume [reduced by only 15.4 +/- 3% (mean +/- S.E.) compared to the predose period], suggesting that antx-a(s) has an important muscarinic action on the cardiovascular system in vivo. Phrenic nerve amplitude increased, but, nevertheless, tidal and minute volumes decreased progressively, indicating that antx-a(s), unlike most low-molecular-weight organophosphorus cholinesterase inhibitors, does not have any remarkable inhibitory action on central mediation of respiration.

Anatoxin-a(s), an alkaloid neurotoxin from the freshwater cyanobacterium, Anabaena flos-aquae NRC-525-17, was compared to paraoxon, physostigmine and pyridostigmine for effects on brain cholinesterase after i.p. injection into Balb/c mice. The duration of clinical signs in mice injected with anatoxin-a(s) persisted longer than in mice given the carbamates and was comparable with that of paraoxon. Anatoxin-a(s) did not inhibit brain cholinesterase activity suggesting that this toxin is unable to cross the blood-brain barrier.

Cyanobacteria (blue-green algae) implicated in the deaths of 9 dogs at Richmond Lake, SD, on Aug 26, 1985, were analyzed. The dominant cyanobacterial species from the water sample was Anabaena flos-aquae. The lyophilized bloom material or the high-performance liquid chromatography purified toxin peak, when administered to mice IP, induced clinical signs of salivation, lacrimation, urinary incontinence, defecation, convulsion, fasciculation, and respiratory arrest. Further comparison of the semipurified bloom toxin with an irreversible anticholinesterase anatoxin-a(s), produced by A flos-aquae strain NRC-525-17, revealed the bloom toxin and anatoxin-a(s) had similar properties on high-performance liquid chromatography and on the inhibition of electric eel acetylcholinesterase (EC 3.1.1.7).

Anatoxin a(s) [antx-a(s)] given intraperitoneally to Sprague-Dawley rats at different doses (0.1-1.0 mg/kg) caused signs of severe cholinergic overstimulation. Assays of rat blood acetylcholinesterase (AChE) revealed a dose-dependent inhibition. The in vitro inhibition of electric eel acetylcholinesterase (AChE, E.C. 3.1.1.7) and horse serum butyrylcholinesterase (BUChE, E.C. 3.1.1.8) by antx-a(s) was time- and concentration-dependent. The inhibition of electric eel AChE follows first order kinetics, indicative of irreversible inhibition. The irreversibility of electric eel AChE inhibition was confirmed by a plot of Vmax versus total enzyme concentration [ET]. The kinetics of inhibition of cholinesterase by antx-a(s) supports the previous pharmacological findings that antx-a(s) is an anticholinesterase and that signs of intoxication by it are primarily due to cholinesterase inhibition.

Calves, rats, ducks, and goldfish given lethal oral doses of bacteria-free lyophilized cell suspensions of toxic Anabaena flos-aquae died as a result of respiratory arrest. Experiments with selected animals and pharmacological preparations showed that the main effect of the toxin was production of a sustained postsynaptic depolarizing neuromuscular blockade.