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Potential developmental toxicity of anatoxin‐a, a cyanobacterial toxin
Author(s) -
Rogers E. H.,
Hunter E. S.,
Moser V. C.,
Phillips P. M.,
Herkovits J.,
Muñoz L.,
Hall L. L.,
Chernoff N.
Publication year - 2005
Publication title -
journal of applied toxicology
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.784
H-Index - 87
eISSN - 1099-1263
pISSN - 0260-437X
DOI - 10.1002/jat.1091
Subject(s) - toxicity , toxin , biology , developmental toxicity , neurotoxin , acute toxicity , physiology , toxicology , pharmacology , medicine , gestation , endocrinology , microbiology and biotechnology , pregnancy , genetics
Abstract Some 2000 species of cyanobacteria (blue‐green algae) occur globally in aquatic habitats. They are able to survive under a wide range of environmental conditions and some produce potent toxins. Toxin production is correlated with periods of rapid growth (blooms) and 25%–70% of blooms may be toxic. Anatoxin‐a is an alkoloid neurotoxin that acts as a potent neuro‐muscular blocking agent at the nicotinic receptor. Acute toxicity, following consumption of contaminated water, is characterized by rapid onset of paralysis, tremors, convulsions and death. Human exposures may occur from recreational water activities and dietary supplements, but are primarily through drinking water. The current studies were conducted to examine the effect of in utero exposure on postnatal viability, growth and neurodevelopment, to evaluate the potential of in vitro embryotoxicity, and to explore the synergistic relationship between anatoxin‐a and the algal toxin microcystin‐LR by the oral route. The results of preliminary studies on amphibian toxicity are also reported. Time‐pregnant mice received 125 or 200 µg kg −1 anatoxin‐a by intraperitoneal injection on gestation days (GD) 8–12 or 13–17. Pup viability and weight were monitored over a 6‐day period. Maternal toxicity (decreased motor activity) was observed at 200 µg kg −1 in both treatment periods. There were no significant treatment‐related effects on pup viability or weight on postnatal day (PND) 1 or 6. The GD 13–17 pups were evaluated on PND 6, 12 and 20 for standard markers of neurodevelopmental maturation (righting reflex, negative geotaxis and hanging grip time). No significant postnatal neurotoxicity was observed. In vitro developmental toxicity was evaluated in GD 8 mouse embryos exposed to 0.1–25 µ m anatoxin‐a for 26–28 h. Perturbations in mouse yolk sac vasculature were noted from the 1.0 µ m concentration in the absence of significant embryonic dysmorphology. Potential algal toxin synergism was tested in mice receiving either 0, 500 or 1000 µg kg −1 microcystin‐LR by gavage and ∼50 min later receiving either 0, 500, 1000 or 2500 µg kg −1 anatoxin‐a by the same route. No deaths occurred at any dose and no definitive signs of intoxication were observed. Stages 17 and 25 toad embryos ( Bufo arenarum ) were exposed to 0.03–30.0 mg l −1 of anatoxin‐a for 10 days. Adverse effects included a dose‐dependent transient narcosis, edema and loss of equilibrium. Most notable was the occurrence of 100% mortality at the high dose in both groups 6–13 days post‐exposure. The observed delay between initial exposure and death is highly unusual for anatoxin‐a. Published in 2005 by John Wiley & Sons, Ltd.