Potent inhibition of sperm motility by palytoxin

Palytoxin, produced by a stationary marine animal and one of the most toxic substances known, was used as a spear poison in ancient Hawaii to cause death by cardiovascular contracture. We report here that the motility of hamster caudal epididymal (HCE) and other sperm can be inhibited by as little as 10⁻¹³ M palytoxin in a time-dependent manner. This inhibition manifested itself as a loss in flagellar amplitude, often accompanied by an increase in beat frequency, resulting in a loss of forward progression and ultimately cessation of movement. Similar effects were observed in sperm from guinea pigs, rabbit, cattle, sea urchins and man. Preincubation with palytoxin did not prevent the induction of motility from quiescence in HCE sperm when free calcium ion was added. However, regardless of the timing of palytoxin addition this very vigorous motility disappeared shortly after it appeared. These, plus earlier observations showing palytoxin did not cause lysis under similar conditions or inhibit the progressive motility of demembranated sperm axoneme preparations, suggest both that this large molecule acts via the plasma membrane to cause its exceedingly toxic effects and that spermatozoa may be useful for the investigation of the mechanism of action of palytoxin.     

Examining the Use of Mass Transplantation of Brooding and Spawning Corals to Support Natural Coral Recruitment in Sulawesi/Indonesia

Coral transplantation is frequently advocated as a possible means of coral reef rehabilitation. One of the purported benefits of transplantation is a positive effect of transplants on coral recruitment by sexual reproduction of transplants (“seeding”) and/or settlement cues generated by the presence of live coral (“attraction”). However, evidence for this assertion is scarce. Here, we investigated the effect of coral transplantation on larval recruitment. A total of 6,164 fragments of four coral species (acroporids and pocilloporids) were transplanted at three sites in North Sulawesi, Indonesia. Coral recruitment onto limestone settlement plates was examined every 3 months and on concrete structures at the end of the study (≥15 months) in the presence and absence of transplants. Transplant survival after 1 year ranged between 20 and 30% for pocilloporids and between 40 and 80% for acroporids. Transplantation had no consistent effect on the number of coral recruits on the settlement plates or on the concrete structures. Recruitment was relatively high compared to other locations in the region and fluctuated seasonally, with increased rates in all treatments during peaks of reproduction. We conclude that, in the presence of high background recruitment and detrimental environmental conditions, coral transplantation may not be an effective method to boost coral recruitment. The provision of stable substrate for settlement in the form of artificial reefs, combined with improved management to reduce chronic stressors, constitutes a better use of resources.