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Anabaena

Potentially toxic species known to occur in New Zealand

Anabaena circinalis
Anabaena flos-aquae
Anabaena lemmermanii
Anabaena spiroides
Anabaena planktonica
Anabaena smithii
Anabaena affinis
Anabaena aphanizomanioides
Anabaena oscillariodies
Other Anabaena sp?

Other names

Blue-green algae

Description

Planktonic or attached to moist substrates. Trichromes solitary or aggregated in floccose masses or united in a thin mucilaginous stratum; straight, flexuous, circinate, spirally coiled or irregulary twisted.

Anabaena species often form thick, wind-concentrated surface blooms or scums especially during summer months when there is warm, sunny weather and if the water is nutrient rich..

Similar plants

Other cyanobacteria.

Distribution

In the North Island Anabaena blooms have been reported in lakes in the Rotorua area including Rotorua, Roitoiti, Rotoehu, Okaro, Opuri, Ngahewa. Blloms have occurred on Lake Taupo, Lake Waitawa, Lake Maraetai, Kimihia (Waikato) and the Waikato River, Lake Orakai (Napier), Lake Henely (Masterton), Karori Reservior (Wgtn)

In the South Island blooms have been reported on Lakes Roundabout, Lake Hayes, Lake Johston, Lake Wakatipu, Lake Waihola, Butchers Dam, Woods Dam and Tomahawk Lagoon.

Toxin

Anabaena sp. can produce the hepatotoxic cyclic peptide microcycystin and the neurotoxins anatoxin-a (a nicotinic depolarising alkaloid neurotoxin which is potent and fast-acting), anatoxin-a(S) (an organophosphorus cholinesterase inhibitor, responsible for the voluminous salivation sometimes observed) and saxitoxins.

Anabaena species that produce neurotoxin may kill within 1 to 2 minutes of ingestion. One study estimates the oral minimum lethal dose to be 420 mg/kg body weight.

Sensitivity and animal size influence the toxicity, with monogastric animals being less sensitive than ruminants and birds. There are be both toxic and non-toxic strains within the species.

Anabaena sp. in New Zealand are believed to produce microcystins. Further work is currently underway at Massey & Victoria University, ESR and Agresearch to establish whether anatoxins and saxitoxins are produced by Anabaena species in New Zealand.

Species affected

Cattle, sheep, dogs and other pets, honey bees, laboratory mice and rats, chickens, ducks, pheasants, goldfish, wildfowl, humans

Clinical signs - acute

Clinical signs depend on the quantity and type of toxin being produce by the Anabaena sp.. The range of clinical signs can be wide especially if more than one type of cyanotoxin is involved.

Anatoxin-a mimics the effect of acetylcholine. The onset of clinical signs is abrupt (within 60 minutes). Signs include lethargy, muscle tremors, hyperpnoea, cyanosis, paralysis, hyperaesthesis, convulsions and death within 30 minutes after signs appear as a result of respiratory arrest. Anatoxin ?a (S) is an anticholinesterase, and has not been recorded in New Zealand. Exposure causes an increase in salivation, lacrimation, ataxia, diarrhoea, dyspnoea and death within an hour. Signs similar to anatoxin-a may also occur.

There are no specific lesions in animals that die of cyanobacterial neurotoxicoses.

Saxitoxins block nerve cell sodium channels. They cause paralysis, respiratory depression and respiratory failure. In people incoordination, confused speech, nausea, vomiting, eye irritation, and respiratory distress may occur. In severe cases respiratory paralysis requires artificial respiration. Hepatotoxins (eg microcystins, nodularin) cause intrahepatic haemorrhage and liver damage. Sometimes convulsions, paralysis or muscle tremors precede death. Depending on the amount of toxin ingested signs can be acute or chronic. The liver may appear normal, but is usually enlarged and dark red from congestion and intrahepatic haemorrhage. Histologically, a widespread centrilobular to midzonal necrosis is observed.

Clinical signs - chronic

In animals that live for a few hours death from liver failure caused by hyperkalaemia or hypoglycaemia may occur within a few days.

Post mortem signs

Cyanobacteria may be found in the stomach and intestines, and there is often a greenish stain on the mouth, nose, legs and feet. Liver damage may be exhibited as a pale tan liver with focal, subcapsular haemorrhagic plaques, or as diffuse reddening. Hepatomegaly is mostly due to intrahepatic haemorrhage. Hepatocytes may show vacuolation and swelling, there is narrowing of sinusoids and loss of tubular arrangements. Necrosis in the liver begins around the centrilobular vein and proceeds to the periportal regions. The kidneys may show severe tubular degeneration and intratubular eosinophilic casts. Debris from disassociated hepatocytes may be found in the pulmonary vessels and kidneys. Pronounced haemorrhage from small vessels under the skin.

Diagnosis

History, clinical signs and post mortem findings. Some laboratories are able to assay for the toxins, or microscopic examination may reveal the cyanobacteria.

Differential diagnosis

Other toxicants which are inhibitors of cholinesterase (eg carbamate and organophosphate insecticides, Solanum species, etc), have nicotinic effects (eg nicotine sulphate, tobacco, hemlock, levamisole etc) or other hepatogenous photosensitisers (eg sporodesmin, pyrrolizidine alkaloid plants etc).

Treatment

Animals are often found dead or die before treatment can be given if the neurotoxin is present. Decontamination (eg activated charcoal) is important and removal of animals from the contaminated water supply is essential. Affected animals should be placed out of direct sunlight in a protected area. Atropine may be administered in an attempt to negate the effects of anatoxin-a (s), and artificial respiration may prolong life. There is as yet no therapeutic antagonist effective against anatoxin-a or the saxitoxins. Treatment with the anticholinesterases edrophonium chloride and neostigmine were shown to have no apparent effect on the toxin-induced neuromuscular blockade. There is no specific treatment for hepatotoxins. Symptomatic treatment may be of use, eg intravenous fluids may help prevent dehydration. Copper sulphate or other algicidal treatments may be added to the water in an attempt to control the cyanobacteria. To detoxify the water copper sulphate or calcium hypochlorite can be added at 12kg (70%) per 1000L, this is still safe for stock to drink, but toxin may persist after algae are killed. Care should be taken when applying management options such as algicides, as some techniques can results in the death of the cyanobacteria, causing a massive release of the cyanotoxins from the cells, thus escalating any potential risks.

Prognosis

Invariably fatal.

Prevention

Avoid contaminated water.


References

Baker, P. (1991) Identification of Common Noxious Cyanobacteria. Part I ? Nostocales. Australian Centre for Water Treatment and Water Quality Research. Research Report No. 29.
Christoffersen, K. and C. W. Burns (2000). "Toxic cyanobacteria in New Zealand lakes and toxicity to indigenous zooplankton." Internationale Vereinigung fur Theoretische und Angewandte Limnologie Verhandlungen 27(5): 3222-3225
Chorus, I. and J. Bartram (1999). Toxic Cyanobacteria in Water - A Guide to their Public Health Consequences, Monioring and Management. London, E and FN Spon.
Etheredge, M. K. and R. D. Pridmore (1987). The freshwater planktonic Blue-Greens (Cyanophyta/Cyanobacteria) of New Zealand - A taxonmic guide. Hamilton, Water and Soil: 122.
Gonus, T. (1999). "Cyanobacterial (Blue-Green algal) poisoning of livestock wth special reference to South Africa." Elsenburg Journal 1/2.
Gunn, G. J., A. G. Rafferty, et al. (1992). "Fatal canine neurotoxicosis attributed to blue-green algae (cyanobacteria)." The Veterinary Record 130(14): 301-302.
Negri AP. Jones GJ. Hindmarsh M. Sheep mortality associated with paralytic shellfish poisons from the cyanobacterium Anabaena circinalis. Toxicon. 33(10):1321-9, 1995
Park HD. Watanabe MF. Harda K. Nagai H. Suzuki M. Watanabe M. Hayashi H. Hepatotoxin (microcystin) and neurotoxin (anatoxin-a) contained in natural blooms and strains of cyanobacteria from Japanese freshwaters. Natural Toxins. 1(6):353-60, 1993.
Pridmore, R. D. and M. K. Etheredge (1987). "Planktonic cyanobacteria in New Zealand inland waters: Distribution and population dynamics." New Zealand Journal of Marine and Freshwater Research 21(3): 491-502.
Van Halderen, A., W. R. Harding, et al. (1995). "Cyanobacterial (blue-green algae) poisoning of livestock in the western Cape Province of South Africa." Journal of the South African Veterinary Association 66(4): 260-264.
Wood, S. (2001) Cyanobacteria - an underestimated risk to animal health in New Zealand? Vetscript, December 2001, pp4 - 5


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