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Stability of eelgrass (Zostera marina L.) depth limits: influence of habitat type

机译:鳗草(Zostera marina L.)深度极限的稳定性:生境类型的影响

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Seagrass meadows are generally considered stable although few studies have specified and tested this statement. On the basis of a large monitoring dataset from Danish coastal waters, we aimed to test whether the stability of deep eelgrass populations changes along a eutrophication gradient extending from inner bays over outer bays to open coastal waters. We defined stability in terms of the 'stability properties' of 'constancy', 'resilience', and/or 'persistence'. Our data allowed us to investigate the stability property constancy expressed as temporal variability in eelgrass depth limits over a time scale of 10 years. We hypothesised that colonisation depths were large and relatively constant along open coasts because of low and relatively constant levels of nutrients and turbidity. Conversely, colonisation depths were hypothesised to be low and variable in protected bays due to higher and more variable levels of nutrients and turbidity. We found that depth limits increased from inner bays towards open coastal waters, matching declines in nutrient concentration and increases in water clarity and oxygen concentration. Stability expressed as constancy of depth limits did not differ significantly between habitat types, and neither did stability of physicochemical variables. However, when data from all habitat types were analysed together, they showed that eelgrass populations at the depth limit were significantly more constant and thus, in this respect, more stable when occurring in deep waters as compared to shallow waters. Areas of good water quality may thus obtain the double benefit of deeper-growing and more stable eelgrass populations. The most likely reason why this pattern did not appear at habitat-type level is that the habitat types studied represented wide spatial variation in water quality and depth limit. We conclude that the question of whether eelgrass populations are stable depends on the stability property and the ecological situation in question. Populations may be considered unstable in terms of inter-annual variation but stable in terms of long-term persistence. Therefore, the common statement that eelgrass populations are stable is not universally true.
机译:尽管很少有研究指定并测试了这种说法,但通常认为海草草甸是稳定的。基于丹麦沿海水域的大型监测数据集,我们旨在检验深鳗草种群的稳定性是否沿着从内海湾到外海湾到沿海开放水域的富营养化梯度变化。我们根据“稳定性”,“弹性”和/或“持久性”的“稳定性”定义了稳定性。我们的数据使我们能够研究在10年的时间尺度内以鳗草深度极限的时间变化表示的稳定性属性的恒定性。我们假设由于营养物质和浑浊度较低且相对恒定,在开阔海岸地区定居深度较大且相对恒定。相反,由于营养物和浊度的水平越来越高,假设在受保护的海湾定居深度很低并且变化很大。我们发现,从内湾到开阔的沿海水域,深度限制增加了,营养物浓度下降了,水的澄清度和氧气浓度也增加了。以深度极限恒定表示的稳定性在生境类型之间没有显着差异,理化变量的稳定性也没有显着差异。但是,将所有栖息地类型的数据一起分析时,他们发现,深水区的鳗草种群明显更稳定,因此在深水区比浅水区更稳定。因此,水质良好的地区可能会获得越深越稳定的鳗gra种群数量的双重好处。这种模式没有出现在生境类型水平上的最可能原因是所研究的生境类型代表了水质和深度极限的广泛空间变化。我们得出结论,鳗e种群是否稳定取决于稳定特性和所讨论的生态状况。就年际变化而言,种群可能被认为是不稳定的,但就长期持久性而言,种群是稳定的。因此,关于鳗gra种群稳定的普遍说法并不普遍。

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