Chemistry:Anatoxin-a

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Anatoxin-a
Anatoxin-a.png
Ball-and-stick model of the anatoxin-a molecule
Names
IUPAC name
1-(9-azabicyclo[4.2.1]non-2-en-2-yl)ethan-1-one
Other names
Anatoxin A
Identifiers
3D model (JSmol)
ChEMBL
ChemSpider
KEGG
UNII
Properties
C10H15NO
Molar mass 165.232
Except where otherwise noted, data are given for materials in their standard state (at 25 °C [77 °F], 100 kPa).
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Infobox references
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Anatoxin-a, also known as Very Fast Death Factor (VFDF), is a secondary, bicyclic amine alkaloid and cyanotoxin with acute neurotoxicity. It was first discovered in the early 1960s in Canada, and was isolated in 1972. The toxin is produced by multiple genera of cyanobacteria and has been reported in North America, South America, Central America, Europe, Africa, Asia, and Oceania. Symptoms of anatoxin-a toxicity include loss of coordination, muscular fasciculations, convulsions and death by respiratory paralysis. Its mode of action is through the nicotinic acetylcholine receptor (nAchR) where it mimics the binding of the receptor's natural ligand, acetylcholine. As such, anatoxin-a has been used for medicinal purposes to investigate diseases characterized by low acetylcholine levels. Due to its high toxicity and potential presence in drinking water, anatoxin-a poses a threat to animals, including humans. While methods for detection and water treatment exist, scientists have called for more research to improve reliability and efficacy. Anatoxin-a is not to be confused with guanitoxin (formerly anatoxin-a(S)), another potent cyanotoxin that has a similar mechanism of action to that of anatoxin-a and is produced by many of the same cyanobacteria genera, but is structurally unrelated.[1]

History

Anatoxin-a was first discovered by P.R. Gorham in the early 1960s, after several herds of cattle died as a result of drinking water from Saskatchewan Lake in Ontario, Canada, which contained toxic algal blooms. It was isolated in 1972 by J.P. Devlin from the cyanobacteria Anabaena flos-aquae.[2]

Occurrence

Anatoxin-a is a neurotoxin produced by multiple genera of freshwater cyanobacteria that are found in water bodies globally.[3] Some freshwater cyanobacteria are known to be salt tolerant and thus it is possible for anatoxin-a to be found in estuarine or other saline environments.[4] Blooms of cyanobacteria that produce anatoxin-a among other cyanotoxins are increasing in frequency due to increasing temperatures, stratification, and eutrophication due to nutrient runoff.[5] These expansive cyanobacterial harmful algal blooms, known as cyanoHABs, increase the amount of cyanotoxins in the surrounding water, threatening the health of both aquatic and terrestrial organisms.[6] Some species of cyanobacteria that produce anatoxin-a don't produce surface water blooms but instead form benthic mats. Many cases of anatoxin-a related animal deaths have occurred due to ingestion of detached benthic cyanobacterial mats that have washed ashore.[7]

Anatoxin-a producing cyanobacteria have also been found in soils and aquatic plants. Anatoxin-a sorbs well to negatively charged sites in clay-like, organic-rich soils and weakly to sandy soils. One study found both bound and free anatoxin-a in 38% of aquatic plants sampled across 12 Nebraskan reservoirs, with much higher incidence of bound anatoxin-a than free.[8]

Experimental studies

In 1977, Carmichael, Gorham, and Biggs experimented with anatoxin-a. They introduced toxic cultures of A. flos-aquae into the stomachs of two young male calves, and observed that muscular fasciculations and loss of coordination occurred in a matter of minutes, while death due to respiratory failure occurred anywhere between several minutes and a few hours. They also established that extensive periods of artificial respiration did not allow for detoxification to occur and natural neuromuscular functioning to resume. From these experiments, they calculated that the oral minimum lethal dose (MLD) (of the algae, not the anatoxin molecule), for calves is roughly 420 mg/kg body weight.[9]

In the same year, Devlin and colleagues discovered the bicyclic secondary amine structure of anatoxin-a. They also performed experiments similar to those of Carmichael et al. on mice. They found that anatoxin-a kills mice 2–5 minutes after intraperitoneal injection preceded by twitching, muscle spasms, paralysis and respiratory arrest, hence the name Very Fast Death Factor.[10] They determined the LD50 for mice to be 250 µg/kg body weight.[1]

Electrophysiological experiments done by Spivak et al. (1980) on frogs showed that anatoxin-a is a potent agonist of the muscle-type (α1)2βγδ nAChR. Anatoxin-a induced depolarizing neuromuscular blockade, contracture of the frog's rectus abdominis muscle, depolarization of the frog sartorius muscle, desensitization, and alteration of the action potential. Later, Thomas et al., (1993) through his work with chicken α4β2 nAChR subunits expressed on mouse M 10 cells and chicken α7 nAChR expressed in oocytes from Xenopus laevis, showed that anatoxin-a is also a potent agonist of neuronal nAChR.[1]

Toxicity

Effects

Laboratory studies using mice showed that characteristic effects of acute anatoxin-a poisoning via intraperitoneal injection include muscle fasciculations, tremors, staggering, gasping, respiratory paralysis, and death within minutes. Zebrafish exposed to anatoxin-a contaminated water had altered heart rates.[11]

There have been cases of non-lethal poisoning in humans who have ingested water from streams and lakes that contain various genera of cyanobacteria that are capable of producing anatoxin-a. The effects of non-lethal poisoning were primarily gastrointestinal: nausea, vomiting, diarrhea, and abdominal pain.[12] A case of lethal poisoning was reported in Wisconsin after a teen jumped into a pond contaminated with cyanobacteria.[13]

Exposure routes

Oral

Ingestion of drinking water or recreational water that is contaminated with anatoxin-a can pose fatal consequences since anatoxin-a was found to be quickly absorbed through the gastrointestinal tract in animal studies.[14] Dozens of cases of animal deaths due to ingestion of anatoxin-a contaminated water from lakes or rivers have been recorded, and it is suspected to have also been the cause of death of one human.[15] One study found that anatoxin-a is capable of binding to acetylcholine receptors and inducing toxic effects with concentrations in the nano-molar (nM) range if ingested.[16]

Dermal

Dermal exposure is the most likely form of contact with cyanotoxins in the environment. Recreational exposure to river, stream, and lake waters contaminated with algal blooms has been known to cause skin irritation and rashes.[17] The first study that looked at in vitro cytotoxic effects of anatoxin-a on human skin cell proliferation and migration found that anatoxin-a exerted no effect at 0.1 µg/mL or 1 µg/mL, and a weak toxic effect at 10 µg/mL only after an extended period of contact (48 hours).[18]

Inhalation

No data on inhalation toxicity of anatoxin-a is currently available, though severe respiratory distress occurred in a water skier after they inhaled water spray containing a fellow cyanobacterial neurotoxin, saxitoxin.[19] It is possible that inhalation of water spray containing anatoxin-a could pose similar consequences.

Mechanism of toxicity

Anatoxin-a is an agonist of both neuronal α4β2 and α4 nicotinic acetylcholine receptors present in the CNS as well as the (α1)2βγδ muscle-type nAchRs that are present at the neuromuscular junction.[1] (Anatoxin-a has an affinity for these muscle-type receptors that is about 20 times greater than that of acetylcholine.[2]) However, the cyanotoxin has little effect on muscarinic acetylcholine receptors; it has a 100 fold lesser selectivity for these types of receptors than it has for nAchRs.[20] Anatoxin-a also shows much less potency in the CNS than in neuromuscular junctions. In hippocampal and brain stem neurons, a 5 to 10 times greater concentration of anatoxin-a was necessary to activate nAchRs than what was required in the PNS.[20]

In normal circumstances, acetylcholine binds to nAchRs in the post-synaptic neuronal membrane, causing a conformational change in the extracellular domain of the receptor which in turn opens the channel pore. This allows Na+ and Ca2+ ions to move into the neuron, causing cell depolarization and inducing the generation of action potentials, which allows for muscle contraction. The acetylcholine neurotransmitter then dissociates from the nAchR, where it is rapidly cleaved into acetate and choline by acetylcholinesterase.[21]

The effects of anatoxin-a on nicotinic acetylcholine receptors at the neuromuscular junction

Anatoxin-a binding to these nAchRs cause the same effects in neurons. However, anatoxin-a binding is irreversible, and the anatoxin-a nAchR complex cannot be broken down by acetylcholinesterase. Thus, the nAchR is temporarily locked open, which leads to overstimulation due to the constant generation of action potentials.[20]

Two enantiomers of anatoxin-a, the positive enantiomer, (+)-anatoxin-a, is 150 fold more potent than the synthetic negative enantiomer, (−)-anatoxin-a.[20] This is because (+)-anatoxin-a, the s-cis enone conformation, has a distance a 6.0 Å between its nitrogen and carbonyl group, which corresponds well to the 5.9 Å distance that separate the nitrogen and oxygen in acetylcholine.[1]

Respiratory arrest, which results in a lack of an oxygen supply to the brain, is the most evident and lethal effect of anatoxin-a.[20] Injections of mice, rats, birds, dogs, and calves with lethal doses of anatoxin-a have demonstrated that death is preceded by a sequence of muscle fasciculations, decreased movement, collapse, exaggerated abdominal breathing, cyanosis and convulsions.[2] In mice, anatoxin-a also seriously impacted blood pressure and heart rate, and caused severe acidosis.[1]

Cases of toxicity

Flamingos at Lake Bogoria

Many cases of wildlife and livestock deaths due to anatoxin-a have been reported since its discovery. Domestic dog deaths due to the cyanotoxin, as determined by analysis of stomach contents, have been observed at the lower North Island in New Zealand in 2005,[22] in eastern France in 2003,[23] in California of the United States in 2002 and 2006,[24] in Scotland in 1992, in Ireland in 1997 and 2005,[2] in Germany in 2017[25] an 2020[26] In each case, the dogs began showing muscle convulsions within minutes, and were dead within a matter of hours. Numerous cattle fatalities arising from the consumption of water contaminated with cyanobacteria that produce anatoxin-a have been reported in the United States, Canada, and Finland between 1980 and the present.[2]

A particularly interesting case of anatoxin-a poisoning is that of lesser flamingos at Lake Bogoria in Kenya. The cyanotoxin, which was identified in the stomachs and fecal pellets of the birds, killed roughly 30,000 flamingos in the second half of 1999, and continues to cause mass fatalities annually, devastating the flamingo population. The toxin is introduced into the birds via water contaminated with cyanobacterial mat communities that arise from the hot springs in the lake bed.[27]

Synthesis

Laboratory synthesis

Cyclic expansion of tropanes

The first biologically occurring initial substance for tropane expansion into anatoxin-a was cocaine, which has similar stereochemistry to anatoxin-a. Cocaine is first converted into the endo isomer of cyclopropane, which is then photolytically cleaved to obtain an alpha, beta unsaturated ketone. Through the use of diethyl azodicarboxylate, the ketone is demethylated and anatoxin-a is formed. A similar, more recent synthesis pathway involves producing 2-tropinone from cocaine and treating the product with ethyl chloroformate producing a bicyclic ketone. This product is combined with trimethylsilyldiazylmethane, an organoaluminum Lewis acid and trimethylsinyl enol ether to produce tropinone. This method undergoes several more steps, producing useful intermediates as well as anatoxin-a as a final product.[2]

Cocaine, a precursor for anatoxin-a synthesis.
Cocaine, a precursor for anatoxin-a synthesis

Cyclization of cyclooctenes

The first and most extensively explored approach used to synthesize anatoxin-a in vitro, cyclooctene cyclization involves 1,5-cyclooctadiene as its initial source. This starting substance is reacted to form methyl amine and combined with hypobromous acid to form anatoxin-a. Another method developed in the same laboratory uses aminoalcohol in conjunction with mercuric (II) acetate and sodium borohydride. The product of this reaction was transformed into an alpha, beta ketone and oxidized by ethyl azodicarboxylate to form anatoxin-a.[2]

Enantioselective enolization strategy

This method for anatoxin-a production was one of the first used that does not utilize a chimerically analogous starting substance for anatoxin formation. Instead, a racemic mixture of 3-tropinone is used with a chiral lithium amide base and additional ring expansion reactions in order to produce a ketone intermediate. Addition of an organocuprate to the ketone produces an enol triflate derivative, which is then lysed hydrogenously and treated with a deprotecting agent in order to produce anatoxin-a. Similar strategies have also been developed and utilized by other laboratories.[2]

Intramolecular cyclization of iminium ions

Iminium ion cyclization utilizes several different pathways to create anatoxin-a, but each of these produces and progresses with a pyrrolidine iminium ion. The major differences in each pathway relate to the precursors used to produce the imium ion and the total yield of anatoxin-a at the end of the process. These separate pathways include production of alkyl iminium salts, acyl iminium salts and tosyl iminium salts.[2]

Enyne metathesis

Enyne metathesis of anatoxin-a involves the use of a ring closing mechanism and is one of the more recent advances in anatoxin-a synthesis. In all methods involving this pathway, pyroglutamic acid is used as a starting material in conjunction with a Grubb's catalyst. Similar to iminium cyclization, the first attempted synthesis of anatoxin-a using this pathway used a 2,5-cis-pyrrolidine as an intermediate.[2]

Biosynthesis

Anatoxin-a is synthesized in vivo in the species Anabaena flos-aquae,[2] as well as several other genera of cyanobacteria. Anatoxin-a and related chemical structures are produced using acetate and glutamate. Further enzymatic reduction of these precursors results in the formation of anatoxin-a. Homoanatoxin, a similar chemical, is produced by Oscillatoria formosa and utilizes the same precursor. However, homoanatoxin undergoes a methyl addition by S-adenosyl-L-methionine instead of an addition of electrons, resulting in a similar analogue.[1] The biosynthetic gene cluster (BGC) for anatoxin-a was described from Oscillatoria PCC 6506 in 2009.[28]

Stability and degradation

Anatoxin-a is unstable in water and other natural conditions, and in the presence of UV light undergoes photodegradation, being converted to the less toxic products dihydroanatoxin-a and epoxyanatoxin-a. The photodegradation of anatoxin-a is dependent on pH and sunlight intensity but independent of oxygen, indicating that the degradation by light is not achieved through the process of photo-oxidation.[20]

Studies have shown that some microorganisms are capable of degrading anatoxin-a. A study done by Kiviranta and colleagues in 1991 showed that the bacterial genus Pseudomonas was capable of degrading anatoxin-a at a rate of 2–10 μg/ml per day.[29] Later experiments done by Rapala and colleagues (1994) supported these results. They compared the effects of sterilized and non-sterilized sediments on anatoxin-a degradation over the course of 22 days, and found that after that time vials with the sterilized sediments showed similar levels of anatoxin-a as at the commencement of the experiment, while vials with non-sterilized sediment showed a 25-48% decrease.[20]

Detection

There are two categories of anatoxin-a detection methods. Biological methods have involved administration of samples to mice and other organisms more commonly used in ecotoxicological testing, such as brine shrimp (Artemia salina), larvae of the freshwater crustacean Thamnocephalus platyurus, and various insect larvae. Problems with this methodology include an inability to determine whether it is anatoxin-a or another neurotoxin that causes the resulting deaths. Large amounts of sample material are also needed for such testing. In addition to the biological methods, scientists have used chromatography to detect anatoxin-a. This is complicated by the rapid degradation of the toxin and the lack of commercially available standards for anatoxin-a.[20]

Public health

Despite the relatively low frequency of anatoxin-a relative to other cyanotoxins, its high toxicity (the lethal dose is not known for humans, but is estimated to be less than 5 mg for an adult male[30]) means that it is still considered a serious threat to terrestrial and aquatic organisms, most significantly to livestock and to humans. Anatoxin-a is suspected to have been involved in the death of at least one person.[15] The threat posed by anatoxin-a and other cyanotoxins is increasing as both fertilizer runoff, leading to eutrophication in lakes and rivers, and higher global temperatures contribute to a greater frequency and prevalence of cyanobacterial blooms.[20]

Water regulations

The World Health Organization in 1999 and EPA in 2006 both came to the conclusion that there was not enough toxicity data for anatoxin-a to establish a formal tolerable daily intake (TDI) level, though some places have implemented levels of their own.[31][32]

United States

Drinking water advisory levels

Anatoxin-a is not regulated under the Safe Drinking Water Act, but states are allowed to create their own standards for contaminants that are unregulated. Currently there are four states that have set drinking water advisory levels for anatoxin-a as seen in the table below.[33] On October 8, 2009 the EPA published the third Drinking Water Contaminant Candidate List (CCL) which included anatoxin-a (among other cyanotoxins), indicating that anatoxin-a may be present in public water systems but is not regulated by the EPA. Anatoxin-a's presence on the CCL means that it may need to be regulated by the EPA in the future, pending further information on its health effects in humans.[34][31]

Drinking Water Advisory Levels
State Concentration (µg/L)
Minnesota 0.1
Ohio 20
Oregon 0.7
Vermont 0.5
Recreational water advisory levels

In 2008 the state of Washington implemented a recreational advisory level for anatoxin-a of 1 µg/L in order to better manage algal blooms in lakes and protect users from exposure to the blooms.[35]

Canada

The Canadian province of Québec has a drinking water Maximum Accepted Value for anatoxin-a of 3.7 µg/L.[36]

New Zealand

New Zealand has a drinking water Maximum Accepted Value for anatoxin-a of 6 µg/L.[37]

Water treatment

As of now, there is no official guideline level for anatoxin-a,[38] although scientists estimate that a level of 1 μg l−1 would be sufficiently low.[39] Likewise, there are no official guidelines regarding testing for anatoxin-a. Among methods of reducing the risk for cyanotoxins, including anatoxin-a, scientists look favorably on biological treatment methods because they do not require complicated technology, are low maintenance, and have low running costs. Few biological treatment options have been tested for anatoxin-a specifically, although a species of Pseudomonas, capable of biodegrading anatoxin-a at a rate of 2–10 μg ml−1 d−1, has been identified. Biological (granular) activated carbon (BAC) has also been tested as a method of biodegradation, but it is inconclusive whether biodegradation occurred or if anatoxin-a was simply adsorbing the activated carbon.[38] Others have called for additional studies to determine more about how to use activated carbon effectively.[40]

Chemical treatment methods are more common in drinking water treatment compared to biological treatment, and numerous processes have been suggested for anatoxin-a. Oxidants such as potassium permanganate, ozone, and advanced oxidation processes (AOPs) have worked in lowering levels of anatoxin-a, but others, including photocatalysis, UV photolysis,[40] and chlorination,[41] have not shown great efficacy.

Directly removing the cyanobacteria in the water treatment process through physical treatment (e.g., membrane filtration) is another option because most of the anatoxin-a is contained within the cells when the bloom is growing. However, anatoxin-a is released from cyanobacteria into water when they senesce and lyse, so physical treatment may not remove all of the anatoxin-a present.[42] Additional research needs to be done to find more reliable and efficient methods of both detection and treatment.[40]

Laboratory uses

Anatoxin-a is a very powerful nicotinic acetylcholine receptor agonist and as such has been extensively studied for medicinal purposes. It is mainly used as a pharmacological probe in order to investigate diseases characterized by low acetylcholine levels, such as muscular dystrophy, myasthenia gravis, Alzheimer disease, and Parkinson disease. Further research on anatoxin-a and other less potent analogues are being tested as possible replacements for acetylcholine.[2]

Genera of cyanobacteria that produce anatoxin-a

See also

References

  1. ↑ 1.0 1.1 1.2 1.3 1.4 1.5 1.6 "Neurotoxic cyanobacterial toxins". Toxicon 56 (5): 813–28. October 2010. doi:10.1016/j.toxicon.2009.07.036. PMID 19660486. 
  2. ↑ 2.00 2.01 2.02 2.03 2.04 2.05 2.06 2.07 2.08 2.09 2.10 2.11 "Anatoxin‐a and Analogues: Discovery, Distribution, and Toxicology.". Phycotoxins: Chemistry and Biochemistry. Blackwell Publishing. March 2007. pp. 141–58. doi:10.1002/9780470277874.ch8. ISBN 978-0-470-27787-4. 
  3. ↑ 3.0 3.1 3.2 "Freshwater neurotoxins and concerns for human, animal, and ecosystem health: A review of anatoxin-a and saxitoxin". The Science of the Total Environment 736: 139515. September 2020. doi:10.1016/j.scitotenv.2020.139515. PMID 32485372. Bibcode: 2020ScTEn.736m9515C. 
  4. ↑ "Health Effects Support Document for the Cyanobacterial Toxin Anatoxin-A". June 2015. https://www.epa.gov/sites/production/files/2017-06/documents/anatoxin-a-report-2015.pdf. 
  5. ↑ "Harmful cyanobacterial blooms: causes, consequences, and controls". Microbial Ecology 65 (4): 995–1010. May 2013. doi:10.1007/s00248-012-0159-y. PMID 23314096. 
  6. ↑ "Cyanobacterial Toxins of the Laurentian Great Lakes, Their Toxicological Effects, and Numerical Limits in Drinking Water". Marine Drugs 15 (6): 160. June 2017. doi:10.3390/md15060160. PMID 28574457. 
  7. ↑ "Cyanobacterial toxins: Anatoxin-a". November 2019. https://www.who.int/water_sanitation_health/water-quality/guidelines/chemicals/anatoxin-a-gdwq-bd-for-review-20191122.pdf. 
  8. ↑ "Co-occurrence of the cyanotoxins BMAA, DABA and anatoxin-a in Nebraska reservoirs, fish, and aquatic plants". Toxins 6 (2): 488–508. January 2014. doi:10.3390/toxins6020488. PMID 24476710. 
  9. ↑ "Two laboratory case studies on the oral toxicity to calves of the freshwater cyanophyte (blue-green alga) Anabaena flos-aquae NRC-44-1". The Canadian Veterinary Journal 18 (3): 71–5. March 1977. PMID 404019. 
  10. ↑ "Anatoxin-a, a toxic alkaloid from Anabaena flos-aquae NRC-44h". Canadian Journal of Chemistry 55 (8): 1367–1371. 2011-02-04. doi:10.1139/v77-189. 
  11. ↑ "Cyanotoxins: bioaccumulation and effects on aquatic animals". Marine Drugs 9 (12): 2729–72. December 2011. doi:10.3390/md9122729. PMID 22363248. 
  12. ↑ "Algae and Medicine" (in en). Algae and Man. Boston, MA: Springer US. 1964. pp. 368–412. doi:10.1007/978-1-4684-1719-7_17. ISBN 978-1-4684-1721-0. http://link.springer.com/10.1007/978-1-4684-1719-7_17. Retrieved 2020-10-25. 
  13. ↑ Weirich CA, Miller TR (2014). "Freshwater harmful algal blooms: toxins and children's health". Current Problems in Pediatric and Adolescent Health Care 44 (1): 2–24. doi:10.1016/j.cppeds.2013.10.007. PMID 24439026. 
  14. ↑ "A review of: "Detection Methods for Cyanobacterial Toxins"" (in en). Chemistry and Ecology 11 (4): 275–276. 1995. doi:10.1080/02757549508039077. ISSN 0275-7540. 
  15. ↑ 15.0 15.1 "Toxicological Reviews of Cyanobacterial Toxins: Anatoxin-A". National Center for Environmental Assessment (U.S. Environmental Protection Agency). November 2006. http://ofmpub.epa.gov/eims/eimscomm.getfile?p_download_id=459566. Retrieved 2018-09-22. 
  16. ↑ "The Chemistry and Pharmacology of Anatoxin-a and Related Homotropanes with respect to Nicotinic Acetylcholine Receptors" (in en). Marine Drugs 4 (3): 228–254. 2006-04-06. doi:10.3390/md403228. 
  17. ↑ "Phytoremediation of anatoxin-a by aquatic macrophyte Lemna trisulca L". Chemosphere 112: 305–10. October 2014. doi:10.1016/j.chemosphere.2014.04.064. PMID 25048920. Bibcode: 2014Chmsp.112..305K. 
  18. ↑ "Effects of cylindrospermopsin, its decomposition products, and anatoxin-a on human keratinocytes". The Science of the Total Environment 765: 142670. October 2020. doi:10.1016/j.scitotenv.2020.142670. PMID 33069473. 
  19. ↑ "Potential impact on human health of toxic cyanobacteria 1" (in en). Phycologia 35 (sup6): 6–11. 1996. doi:10.2216/i0031-8884-35-6S-6.1. ISSN 0031-8884. 
  20. ↑ 20.0 20.1 20.2 20.3 20.4 20.5 20.6 20.7 20.8 "Toxicology and detection methods of the alkaloid neurotoxin produced by cyanobacteria, anatoxin-a". Environment International 33 (8): 1070–89. November 2007. doi:10.1016/j.envint.2007.06.003. PMID 17673293. 
  21. ↑ Neuroscience (5th ed.). Sunderland, Massachusetts: Sinauer Associates, Inc.. 2012. 
  22. ↑ "First report of homoanatoxin-a and associated dog neurotoxicosis in New Zealand". Toxicon 50 (2): 292–301. August 2007. doi:10.1016/j.toxicon.2007.03.025. PMID 17517427. 
  23. ↑ "First report in a river in France of the benthic cyanobacterium Phormidium favosum producing anatoxin-a associated with dog neurotoxicosis". Toxicon 45 (7): 919–28. June 2005. doi:10.1016/j.toxicon.2005.02.031. PMID 15904687. 
  24. ↑ "Diagnosis of anatoxin-a poisoning in dogs from North America". Journal of Veterinary Diagnostic Investigation 20 (1): 89–92. January 2008. doi:10.1177/104063870802000119. PMID 18182518. 
  25. ↑ Fastner, Jutta; Beulker, Camilla; Geiser, Britta; Hoffmann, Anja; Kröger, Roswitha; Teske, Kinga; Hoppe, Judith; Mundhenk, Lars et al. (February 2018). "Fatal Neurotoxicosis in Dogs Associated with Tychoplanktic, Anatoxin-a Producing Tychonema sp. in Mesotrophic Lake Tegel, Berlin" (in en). Toxins 10 (2): 60. doi:10.3390/toxins10020060. PMID 29385106. 
  26. ↑ Bauer, F.; Fastner, J.; Bartha-Dima, B.; Breuer, W.; Falkenau, A.; Mayer, C.; Raeder, U. (2020). "Mass Occurrence of Anatoxin-a- and Dihydroanatoxin-a-Producing Tychonema sp. In Mesotrophic Reservoir Mandichosee (River Lech, Germany) as a Cause of Neurotoxicosis in Dogs". Toxins 12 (11): 726. doi:10.3390/toxins12110726. PMID 33233760. 
  27. ↑ "Contribution of hot spring cyanobacteria to the mysterious deaths of Lesser Flamingos at Lake Bogoria, Kenya". FEMS Microbiology Ecology 43 (2): 141–8. March 2003. doi:10.1111/j.1574-6941.2003.tb01053.x. PMID 19719674. 
  28. ↑ Méjean, Annick; Mann, Stéphane; Maldiney, Thomas; Vassiliadis, Gaëlle; Lequin, Olivier; Ploux, Olivier (2009-05-13). "Evidence that Biosynthesis of the Neurotoxic Alkaloids Anatoxin-a and Homoanatoxin-a in the Cyanobacterium Oscillatoria PCC 6506 Occurs on a Modular Polyketide Synthase Initiated by l-Proline". Journal of the American Chemical Society (American Chemical Society (ACS)) 131 (22): 7512–7513. doi:10.1021/ja9024353. ISSN 0002-7863. PMID 19489636. 
  29. ↑ "Production and biodegradation of cyanobacterial toxins-a laboratory study.". Archiv für Hydrobiologie 121 (3): 281–94. 1991. doi:10.1127/archiv-hydrobiol/121/1991/281. https://researchportal.helsinki.fi/en/publications/production-and-biodegradation-of-cyanobacterial-toxins-a-laborato. 
  30. ↑ "Brief review of natural nonprotein neurotoxins.". ASA Newsletter 89 (2): 16–24. 2002. http://www.asanltr.com/newsletter/02-2/articles/Neurotoxins.htm. 
  31. ↑ 31.0 31.1 31.2 "2015 Drinking Water Health Advisories for Two Cyanobacterial Toxins". June 2015. https://19january2017snapshot.epa.gov/sites/production/files/2015-06/documents/cyanotoxins-fact_sheet-2015.pdf. 
  32. ↑ Chorus, Ingrid, ed (1999). Toxic cyanobacteria in water: a guide to their public health consequences, monitoring, and management. London: E & FN Spon. ISBN 0-419-23930-8. OCLC 40395794. 
  33. ↑ "Rules and Regulations: Drinking Water HABs Response Plan" (in en-US). 2018-02-12. https://deq.utah.gov/drinking-water/rules-and-regulations-habs. 
  34. ↑ "Drinking Water Contaminant Candidate List 3-Final". 2009-10-08. https://www.federalregister.gov/documents/2009/10/08/E9-24287/drinking-water-contaminant-candidate-list-3-final. 
  35. ↑ "Washington State Recreational Guidance for Microcystins (Provisional) and Anatoxin-a (Interim/Provisional)". July 2008. https://www.doh.wa.gov/portals/1/documents/4400/334-177-recguide.pdf. 
  36. ↑ "Vulnerability of Quebec drinking-water treatment plants to cyanotoxins in a climate change context". Journal of Water and Health 8 (3): 455–65. September 2010. doi:10.2166/wh.2009.207. PMID 20375475. https://iwaponline.com/jwh/article/8/3/455/18125/Vulnerability-of-Quebec-drinkingwater-treatment. 
  37. ↑ "State of knowledge and concerns on cyanobacterial blooms and cyanotoxins". Environment International 59: 303–27. September 2013. doi:10.1016/j.envint.2013.06.013. PMID 23892224. 
  38. ↑ 38.0 38.1 "Biological treatment options for cyanobacteria metabolite removal--a review". Water Research 46 (5): 1536–48. April 2012. doi:10.1016/j.watres.2011.11.018. PMID 22133838. 
  39. ↑ "The toxicity of cyanobacterial toxins in the mouse: II anatoxin-a". Human & Experimental Toxicology 18 (3): 168–73. March 1999. doi:10.1177/096032719901800306. PMID 10215107. 
  40. ↑ 40.0 40.1 40.2 "A review of cyanobacteria and cyanotoxins removal/inactivation in drinking water treatment". Analytical and Bioanalytical Chemistry 397 (5): 1705–14. July 2010. doi:10.1007/s00216-010-3709-5. PMID 20502884. 
  41. ↑ "State of the art on cyanotoxins in water and their behaviour towards chlorine". Toxicon 55 (4): 677–91. April 2010. doi:10.1016/j.toxicon.2009.10.028. PMID 19874838. 
  42. ↑ "Widespread anatoxin-a detection in benthic cyanobacterial mats throughout a river network". PLOS ONE 13 (5): e0197669. 2018-05-18. doi:10.1371/journal.pone.0197669. PMID 29775481. Bibcode: 2018PLoSO..1397669B. 
  43. ↑ Centre (AWQC), Australian Water Quality (2015-12-04). "Notification of Recent Name Changes for Cyanobacteria Adopted and Reported by AWQC" (in en-AU). https://www.awqc.com.au/news/notification-of-recent-name-changes-for-cyanobacteria-adopted-and-reported-by-awqc. 
  44. ↑ 44.0 44.1 44.2 44.3 44.4 44.5 "Harmful cyanobacterial blooms: causes, consequences, and controls". Microbial Ecology 65 (4): 995–1010. May 2013. doi:10.1007/s00248-012-0159-y. PMID 23314096. http://link.springer.com/10.1007/s00248-012-0159-y. 
  45. ↑ "Hepatotoxin (microcystin) and neurotoxin (anatoxin-a) contained in natural blooms and strains of cyanobacteria from Japanese freshwaters". Natural Toxins 1 (6): 353–60. 1993. doi:10.1002/nt.2620010606. PMID 8167957. 
  46. ↑ "Anatoxin-a producing Tychonema (Cyanobacteria) in European waterbodies". Water Research 69: 68–79. February 2015. doi:10.1016/j.watres.2014.11.006. PMID 25437339. http://nbn-resolving.de/urn:nbn:de:bsz:352-0-286858. 

Further reading

External links



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