Comparative sensitivity of the cnidarian Exaiptasia pallida and a standard toxicity test suite: testing whole effluents intended for ocean disposal.

The sea anemone Exaiptasia pallida (formally Aiptasia pulchella) has been identified as a valuable test species for tropical marine ecotoxicology. Here, the sensitivities of newly developed endpoints for E. pallida to two unidentified whole effluents were compared to a standard suite of temperate toxicity test species and endpoints that are commonly used in toxicological risk assessments for tropical marine environments. For whole effluent 1 (WE1), a 96-h lethal concentration 50 % (LC50) of 40 (95 % confidence intervals, 30-54) % v/v and a 12-day LC50 of 12 (9-15) % v/v were estimated for E. pallida, exhibiting a significantly higher sensitivity than standard sub-lethal endpoints in Allorchestes compressa (96-h effective concentration 50 % (EC50) of >100 % v/v for immobilisation) and Hormosira banksii (72-h EC50 of >100 % v/v for germination), and a similar sensitivity to Mytilus edulis galloprovincialis larval development with a 48-h LC50 of 29 (28-30) % v/v. Sub-lethal effects of whole effluent 2 (WE2) on E. pallida pedal lacerate development resulted in an 8-day EC50 of 7 (3-11) % v/v, demonstrating comparable sensitivity of this endpoint to standardised sub-lethal endpoints in H. banksii (72-h EC50 of 11 (10-11) % v/v for germination), M. edulis galloprovincialis (48-h EC50 for larval development of 12 (9-14) % v/v) and Heliocidaris tuberculata (1-h EC50 of 13 (12-14) % v/v for fertilisation; 72-h EC50 of 26 (25-27) % v/v for larval development) and a significantly higher sensitivity than A. compressa immobilisation (96-h EC50 of >100 % v/v). The sensitivity of E. pallida compared to a standard test species suite highlights the value in standardising the newly developed toxicity test methods for inclusion in routine toxicological risk assessment of complex whole effluents. Importantly, this species provides an additional taxonomic group to the test species that are currently available for tropical marine ecotoxicology and, being a cnidarian, may represent important tropical marine environments including coral reefs.

Effects of copper on the fertilization success of the soft coral Lobophytum compactum.

This study provides the first information on the effects of various concentrations of copper on the fertilization success of gametes from the soft coral Lobophytum compactum. Two experiments were conducted to determine the effect of copper on fertilization success during the mass coral spawning in 2004 on the Great Barrier Reef (GBR). The results from the first experiment showed a surprising resistance to copper with control treatments showing 90% fertilization compared to 65% fertilization in measured copper concentrations up to 132 microg/L. Copper concentrations of 69 microg/L and higher resulted in significantly reduced fertilization success when compared to the controls. Copper doses were increased in experiment 2 and the EC50 value for copper effects on fertilization success was 261 microg/L (208-328 microg/L, 95% confidence limits). In this follow-up experiment, fertilization success was significantly lower than the controls after exposure to copper concentrations of 117 microg/L and above. The EC50 value reported here is much higher than those found in the literature on fertilization experiments conducted on hard coral gametes and also for the fertilization success of other marine organisms, including sea urchins, oysters and fish.

Development of a sublethal test to determine the effects of copper and lead on scleractinian coral larvae.

A new sublethal toxicity test was developed in this study to measure the effect of copper and lead on the motility of coral larvae. Larval motility was significantly affected by copper and lead doses immediately after dosing. The copper EC50 values for motility of Goniastrea aspera brain coral larvae (12 h, 21 microg/L; 24 h, 16 microg/L; 48 h, 22 microg/L) were much lower than the copper LC50 values for G. aspera larval survival (6 h, 260 microg/L, and 24 h, 121 microg/L, for 5-day-old larvae and 6 h, 248 microg/L, and 24 h, 136.64 microg/L, for 6-day-old larvae) during the early part of the experiments. However, at later times, the LC50 values (48 h, 40 microg/L, for 5-day-old larvae and 48- h, 87 microg/L, for 6-day-old larvae) were similar to the EC50 values for larval motility. The lead 72-h EC50 value for G. aspera larval motility (2900 microg/L) was much lower than the lead 72-h LC50 value for larval survival (9890 microg/L). The results show that larval motility can be a useful parameter to measure in order to determine the sublethal effects of trace metals on coral larvae.

Trace metals in the living and nonliving components of scleractinian corals.

Trace metals in coral tissue and skeleton have been investigated in various ways since the early seventies. More recently it has been suggested that the symbiotic zooxanthellae may play an important role in the accumulation and regulation of trace metals. Furthermore gamete development and mucus production may influence the metal accumulation and loss in corals. Many studies have attempted to use the annual growth bands in coral skeletons to investigate historical pollution events. However the relationship between the metal concentrations in the surrounding environment and the incorporation of this into coral skeleton is not well understood. This paper explains a method for investigating metal loads in coral tissue, zooxanthellae and skeleton. Furthermore, it presents new information suggesting that zooxanthellae accumulate most metals (Al, Fe, As, Mn, Ni, Cu, Zn, Cd, Pb) in greater concentrations than the coral tissue. Coral skeletons had consistently lower metal concentration than the zooxanthellae, tissue and gametes. The loss of zooxanthellae during stress events may have a significant contribution to the total metal loads in corals. The use of corals as biomonitors should carefully factor in zooxanthellae densities and gamete development before conclusions are drawn.