Leinaas Hans Petter, Christie Hartvig
Norwegian Institute for Nature Research, Blindern, P.O. Box 1037, N-0315, Oslo, Norway.
Oecologia. 1996 Mar;105(4):524-536. doi: 10.1007/BF00330016.
Stability properties of the barren state of a kelp forest-sea urchin system were studied in northern Norway. The ability of the sea urchin Strongylocentrotus droebachiensis to maintain high population densities and recover from perturbations, and the succession of kelp forest revegetation, were studied experimentally by reducing the sea urchin density on a barren skerry. Additional information was obtained from community changes following a natural, but patchy, sea urchin mortality that varied between sites. On the barren grounds, high sea urchin densities (30 50 per m) is maintained by annual recruitment. Severe reductions of sea urchin densities initiated luxuriant kelp growth, while more moderate reductions allowed establishment of opportunistic algae (during spring and early summer), but no kelps. Succession of algal growth, after the severe decline in sea urchin densities, followed a predictable pattern. At first the substrate was colonized by filamentous algae, but within few weeks they were outcompeted by the fast growing kelp Laminaria saccharina. After 3-4 years of the removal experiment, the slower-growing, long-lived kelp L. hyperborea became increasingly dominant. Increased food availability after reduction in sea urchin density led to increased individual growth of the remaining sea urchins. However, the population density did not increase, neither from recruitment nor immigration from adjacent areas with high sea urchin densities. Possibly, early establishment of a dense kelp stand, may represent a breakpoint in the ability of sea urchins to reestablish a barren state. The ability of L. saccharina quickly to invade and monopolize an area may have both positive and negative effects on the succession towards the climax L. hyperborea kelp forest. Competitive interactions may slow the process, but development of a dense stand of L. saccharina will also reduce grazing risk on scattered recruits of the more slowly growing L. hyperborea.
在挪威北部对海带森林 - 海胆系统的贫瘠状态的稳定性特征进行了研究。通过降低荒礁上的海胆密度,对球海胆维持高种群密度以及从干扰中恢复的能力,以及海带森林植被恢复的演替过程进行了实验研究。还从不同地点自然发生但分布不均的海胆死亡后的群落变化中获取了更多信息。在贫瘠区域,每年的补充使得海胆密度维持在较高水平(每平方米30 - 50个)。海胆密度的大幅降低引发了海带的繁茂生长,而适度降低则使得机会性藻类得以生长(在春季和初夏),但没有海带生长。海胆密度大幅下降后,藻类生长的演替遵循可预测的模式。起初,丝状藻类在基质上定殖,但几周内它们就被快速生长的糖海带所取代。去除海胆实验进行3 - 4年后,生长较慢、寿命较长的 hyperborea海带变得越来越占优势。海胆密度降低后食物供应增加,导致剩余海胆个体生长加快。然而,种群密度并未增加,既没有因补充,也没有因来自海胆密度高的相邻区域的迁入。可能是早期形成密集的海带林代表了海胆重新建立贫瘠状态能力的一个转折点。糖海带迅速入侵并垄断一个区域的能力可能对向高潮期的hyperborea海带林的演替既有积极影响也有消极影响。竞争相互作用可能会减缓这一过程,但密集的糖海带林的形成也会降低对生长较慢的hyperborea海带分散幼苗的啃食风险。