Bruckner Andrew W, Hill Ronald L
Khaled bin Sultan Living Oceans Foundation, 8181 Professional Place, Suite 215, Landover, Maryland 20785, USA.
Dis Aquat Organ. 2009 Nov 16;87(1-2):19-31. doi: 10.3354/dao02120.
Remote reefs off southwest Puerto Rico have experienced recent losses in live coral cover of 30 to 80%, primarily due to the decline of Montastraea annularis and M. faveolata from disease and bleaching. These species were formerly the largest, oldest, and most abundant corals on these reefs, constituting over 65% of the living coral cover and 40 to 80% of the total number of colonies. From 1998 to 2001, outbreaks of yellow band disease (YBD) and white plague (WP) affected 30 to 60% of the M. annularis (complex) colonies. Disease prevalence declined beginning in 2002, and then increased immediately following the 2005 mass bleaching event. Colonies of M. annularis (complex) have been reduced in abundance by 24 to 32%, and remaining colonies are missing more than half their tissue. Both M. annularis and M. faveolata have failed to recruit, resheeting has been minimal, and exposed skeletal surfaces are being colonized by macroalgae, bioeroding sponges, and hydrozoans. Other scleractinian corals were smaller in size (mean = 28 cm diameter) and exhibited lower levels of partial mortality; these taxa were affected to a lesser extent by coral diseases and bleaching-associated tissue loss over the last decade. The numbers of small colonies (1 to 9 cm) of these species identified since 2005 also exceeded numbers of larger colonies that died. These reefs appear to be exhibiting shifts in species assemblages, with replacement of M. annularis (complex) by shorter-lived brooding species and other massive and plating corals (Agaricia, Porites, Meandrina, Eusmilia, Diploria, and Siderastrea spp.). To avoid a catastrophic and permanent loss of the dominant, slow-growing reef-building corals, the causes and effects of diseases need to be better understood, and possible control mechanisms must be developed. In particular, steps must be taken to mitigate environmental and anthropogenic stressors that increase the spread and severity of disease.
波多黎各西南部偏远的珊瑚礁近期活珊瑚覆盖率下降了30%至80%,主要原因是环纹菊珊瑚和蜂巢菊珊瑚因疾病和白化而减少。这些物种以前是这些珊瑚礁上最大、最古老且数量最多的珊瑚,占活珊瑚覆盖率的65%以上,占珊瑚群体总数的40%至80%。1998年至2001年,黄带病(YBD)和白瘟病(WP)的爆发影响了30%至60%的环纹菊珊瑚(复合体)群体。疾病流行率从2002年开始下降,然后在2005年大规模白化事件后立即上升。环纹菊珊瑚(复合体)的群体数量减少了24%至32%,剩余群体的组织损失超过一半。环纹菊珊瑚和蜂巢菊珊瑚都未能成功繁殖,重新生长的情况极少,裸露的骨骼表面正被大型藻类、生物侵蚀海绵和水螅虫占据。其他石珊瑚的尺寸较小(平均直径 = 28厘米),部分死亡率较低;在过去十年中,这些分类群受珊瑚疾病和与白化相关的组织损失的影响较小。自2005年以来发现的这些物种的小群体(1至9厘米)数量也超过了死亡的较大群体数量。这些珊瑚礁似乎正在经历物种组合的转变,寿命较短的孵育物种以及其他块状和平板珊瑚(阿加西珊瑚属、孔珊瑚属、脑珊瑚属、真叶珊瑚属、 Diploria属和铁星珊瑚属物种)取代了环纹菊珊瑚(复合体)。为避免占主导地位、生长缓慢的造礁珊瑚遭受灾难性的永久性损失,需要更好地了解疾病的成因和影响,并开发可能的控制机制。特别是,必须采取措施减轻增加疾病传播和严重程度的环境和人为压力源。