Page 813 - Veterinary Toxicology, Basic and Clinical Principles, 3rd Edition
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772 SECTION | XI Bacterial and Cyanobacterial Toxins




  VetBooks.ir  MISCELLANEOUS FRESHWATER                         Australia, New Zealand, and Asia (Hawkins et al., 1997;
                                                                Saker and Griffiths, 2001; Fastner et al., 2003), but it
             CYANOBACTERIAL TOXINS
                                                                should be considered a potential worldwide problem.
             Although microcystin and anatoxin poisonings comprise
             the majority of cases reported in animals, other cyanotoxins  Cylindrospermopsin and deoxycylindrospermopsin have
                                                                been produced by C. raciborskii (Ohtani et al., 1992), and
             are of concern. Dermatotoxic cyanobacterial toxins have  7-epicylindrospermopsin  has  been  produced  by
             been reported to cause “swimmers’ itch” in Hawaii  Aphanizomenon ovalisporum (Banker et al., 1997). After
             (Serdula et al., 1982) and have recently been associated  oral exposure, the LD 50 of cylindrospermopsin obtained
             with dermatitis in a dog (Puschner et al., 2017).  with culture extracts of C. raciborskii ranged from 4.4 to
             In the documented case a dog developed severe pruritis,  6.9 mg/kg in equivalent cylindropsermopsin (Seawright
             urticarial, and malaise after swimming in a freshwater  et al., 1999; Shaw et al., 2000).
             lake  in  California.  Phycological  and  toxicological  Nodularins are cyclic pentapeptides that lead to severe
             evaluation revealed the presence of Anabaena/Trichormus  hepatotoxicosis in the same way as microcystins (Harding
             sp.  and   Lyngbya  sp.  and   debromoaplysiatoxin.  et al., 1995; Ufelmann and Schrenk, 2015). In addition,
             Debromoaplysiatoxin can be produced in the marine and  nodularin is a more potent tumor promoter than microcys-
             freshwater environment and is a known dermatotoxin  tin (Sueoka et al., 1997; IARC, 2006; Ufelmann and
             (Kaneshima et al., 1983). In addition, debromoaplysiatoxin  Schrenk, 2015). The only cyanobacterium species known
             exposure may occur along with exposure to other cyanotox-  to produce nodularin is Nodularia spumigena. This cyano-
             ins and result in a complex clinical presentation. Saxitoxins  bacterium can form extensive blooms in the Baltic Sea
             and derived forms belong to the group of paralytic shellfish  and in brackish waters in the summer (Francis, 1878;
             poisoning (PSP) toxins and have been produced by a num-  Sivonen et al., 1989). The risk of nodularin intoxication is
             ber of freshwater cyanobacteria, including A. flos-aquae,  twofold because toxin exposure can occur not only
             Cylindrospermopsis  raciborskii,  Anabaena  circinalis,  through recreational or drinking water but also via con-
             Lyngbya wollei, Planktothrix sp., and Aphanizomenon grac-  tamination of seafood (Van Buynder et al., 2001). In cases
             ile (Carmichael et al., 1997; Kaas and Henriksen, 2000;  of acute hepatotoxicity, exposure to microcystins as well
             Molica et al., 2005; Ballot et al., 2010). All saxitoxin ana-  as nodularins must be considered.
             logs have high toxicity in mammals by blocking voltage-  β-N-methylamino-l-alanine  (BMAA),  a  neurotoxic
             gated sodium channels, leading to respiratory arrest, neuro-  amino acid found globally is thought to be produced by all
             muscular weakness, and cardiovascular shock. Massive fish  cyanobacterial taxa and has been implicated in avian vacu-
             mortalities have been linked to saxitoxins produced by both  olar myelinopathy (Bidigare et al., 2009). BMAA can
             freshwater  cyanobacteria  and  marine  dinoflagellates  bioaccumulate in food chains such as fish and seafood and
             (Pearson et al., 2010; Moustaka-Gouni et al., 2017).  is of considerable human health concern because of its
             Whereas intoxications of birds and cats have been associ-  ability to destroy motor neurons in the brain, leading to
             ated with ingestion of PSP contaminated fish and clams  neurodegenerative diseases likes Parkinson’s disease,
             (Landsberg, 2002), there is only one confirmed report of  Alzheimer’s, and ALS, commonly referred to as the human
             PSP toxin-associated mammalian mortality from exposure  amyotrophic  lateral  sclerosis parkinsonism dementia
             to contaminated freshwater (Negri et al., 1995). Fourteen  complex of Guam (Guam ALS-PD) and lathyrism (Bradley
             sheep showed signs of trembling, recumbency, and death in  and Mash, 2009). Birds with avian vacuolar myelinopathy
             Australia after exposure to toxic concentrations of PSPs  develop ataxia, tilting, weakness, and death, and they have
             produced by A. circinalis. Because PSP toxins are produced  characteristic postmortem lesions of bilateral symmetrical
             by several species of freshwater cyanobacteria, terrestrial  vacuolation of the white matter of the brain and spinal cord
             animals and humans are at risk of being exposed to these  (Thomas et al., 1998). Monitoring of water for BMAA is a
             toxins. Thus, it is important to reliably evaluate animals  critical tool to assess nutrient reduction and to develop
             with neurologic signs after access to freshwater for possible  control strategies.
             PSP exposure because the risk certainly exists.
                Another cyanotoxin, the alkaloid cylindrospermopsin,
             has caused deaths in cattle (Saker et al., 1999) and severe  CONCLUDING REMARKS
             gastrointestinal disease in humans. Cylindrospermopsin is  AND FUTURE DIRECTIONS
             a potent inhibitor of protein synthesis and can lead to var-
             ious degrees of injury to the liver, kidneys, adrenal gland,  The frequency and extent of harmful cyanobacterial
             intestine, lung, thymus, and heart (Griffiths and Saker,  blooms appears to increase with the addition of nutrients
             2003). Furthermore, this cyanotoxin is of particular con-  to surface freshwater ecosystems throughout the world.
             cern because of its mutagenic and possibly carcinogenic  As demonstrated in Table 57.1, numerous cyanobacterial
             activities. Cylindrospermopsin has been found in Europe,  species have the potential to produce a number of toxins
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