Edmunds Peter J
Department of Biology, California State University, 18111 Nordhoff Street, Northridge, CA 91330-8303, USA.
Oecologia. 2005 Dec;146(3):350-64. doi: 10.1007/s00442-005-0210-5. Epub 2005 Oct 27.
To date, coral death has been the most conspicuous outcome of warming tropical seas, but as temperatures stabilize at higher values, the consequences for the corals remaining will be mediated by their demographic responses to the sub-lethal effects of temperature. To gain insight into the nature of these responses, here I develop a model to test the effect of increased temperature on populations of three pocilloporid corals at One Tree Island, near the southern extreme of the Great Barrier Reef (GBR). Using Seriatopora hystrix, S. caliendrum and Pocillopora damicornis as study species, the effects of temperature on growth were determined empirically, and the dynamics of their populations determined under natural temperatures over a 6-month period between 1999 and 2000 [defined as the study year (SY)]. The two data sets were combined in a demographic test of the possibility that the thermal regime projected for the southern GBR in the next 55-83 years--warmer by 3 degrees C than the study year (the SY+3 regime), which is equivalent to 1.4 degrees C warmer than the recent warm year of 1998--would alter coral population trajectories through the effects on coral growth alone; the analyses first were completed by species, then by family after pooling among species. Laboratory experiments showed that growth rates (i.e., calcification) varied significantly among species and temperatures, and displayed curvilinear thermal responses with growth maxima at approximately 27.1 degrees C. Based on these temperature-growth responses, the SY+3 regime is projected to: (1) increase annualized growth rates of all taxa by 24-39%, and defer the timing of peak growth from the summer to the autumn and spring, (2) alter the intrinsic rate of population growth (lambda) for S. hystrix (lambda decreases 26%) and S. caliendrum (lambda increases 5%), but not for P. damicornis, and (3) have a minor effect on lambda (a 0.3% increase) for the Pocilloporidae, largely because lambda varies more among species than it does between temperatures. Ten-year population projections suggest that the effects of a sub-lethal increase in temperature (i.e., the SY+3 regime) are relatively small compared to the interspecific differences in population dynamics, but nevertheless will alter the population size and increase the relative abundance of large colonies at the expense of smaller colonies for all three species, as well as the Pocilloporidae. These effects may play an important role in determining the nuances of coral population structure as seawater warms, and their significance may intensity if the coral species pool is depleted of thermally sensitive species by bleaching.
迄今为止,珊瑚死亡一直是热带海洋变暖最为显著的后果,但随着温度稳定在更高水平,剩余珊瑚所受的影响将由它们对温度亚致死效应的种群统计学响应来介导。为深入了解这些响应的本质,我在此构建了一个模型,以测试温度升高对大堡礁(GBR)南端附近一树岛的三种鹿角珊瑚种群的影响。以刺鹿角珊瑚、卡氏鹿角珊瑚和多孔鹿角珊瑚作为研究物种,通过实验确定了温度对生长的影响,并在1999年至2000年的6个月期间(定义为研究年份(SY))自然温度条件下测定了它们的种群动态。将这两组数据结合起来,进行了一项种群统计学测试,以检验未来55 - 83年大堡礁南部预测的热状况——比研究年份温暖3摄氏度(SY + 3状况),相当于比1998年最近的温暖年份高1.4摄氏度——是否仅通过对珊瑚生长的影响就会改变珊瑚种群轨迹;分析首先按物种进行,然后在物种合并后按科进行。实验室实验表明,生长速率(即钙化速率)在物种和温度之间存在显著差异,并呈现出曲线形的热响应,在约27.1摄氏度时生长达到最大值。基于这些温度 - 生长响应,预计SY + 3状况将:(1)使所有分类单元的年化生长速率提高24 - 39%,并将生长峰值时间从夏季推迟到秋季和春季,(2)改变刺鹿角珊瑚(λ降低26%)和卡氏鹿角珊瑚(λ增加5%)的种群内禀增长率,但对多孔鹿角珊瑚没有影响,(3)对鹿角珊瑚科的λ有轻微影响(增加0.3%),主要是因为λ在物种间的变化大于在温度间的变化。十年种群预测表明,与种群动态的种间差异相比,温度亚致死性升高(即SY + 3状况)的影响相对较小,但仍将改变种群大小,并以牺牲较小群体为代价增加所有三个物种以及鹿角珊瑚科中大型群体的相对丰度。随着海水变暖,这些影响可能在决定珊瑚种群结构的细微差别方面发挥重要作用,如果珊瑚物种库因白化而耗尽对热敏感的物种,其重要性可能会增强。