亚马逊河白水河流原始演替梯度上的鸟类群落动态

S. Robinson, J. Terborgh
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Because the ear- liest successional stage (Tessaria) covered only small (<3 ha) areas on any given me- ander tongue, we censused six additional stands to characterize their bird communities. Species richness increased along the successional gradient, but not uniformly. Struc- turally simple Tessaria stands (stage 1) contained more diverse communities of breeding birds than the next two successional stages, which appeared to have few resources avail- able to birds. After stage 3, breeding species richness increased by 31-71 species per successional stage as a distinct canopy layer formed (stage 4), fruiting trees became more available (stages 5-6) and the vertical structure of the forest became fully developed (stage 7: 71 more species than stage 6). Early successional bird communities (stages 1- 3) were dominated by a few very abundant insectivores and omnivores, but wanderers from the adjacent forest plus Nearctic and austral migrants seasonally outnumbered breeding residents. Many species that breed in Tessaria stands were restricted to just one or two of the seven stands censused. The middle stages of succession had the highest estimated richness, abundance, and biomasses of nectarivores and frugivores. Nectarivore abundance reflected the huge stands of Heliconia that dominate the understory of mid- successional stages. Bark foragers reached their highest abundance in late successional stages as the dominant canopy tree species of middle successional stages (e.g., Cedrela odorata) began to die off, but remained standing. Middle successional stages lacked many of the insectivores characteristic of more structurally complex mature forest. Among the missing species were understory Mockers, ant-followers, ground foragers, and many arboreal insectivores that participate in canopy flocks. Species of early and middle stages tended to be more abundant on average than those of mature forest. 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引用次数: 67

摘要

1983年和1985年,在秘鲁东南部马努河(Manu River)河曲形成的初演替早期和中期两个样地(40 ha和80 ha)采用点图方法对鸟类进行了普查。我们划分了7个不同的演替阶段,从开放海滩上生长的第一个植物群落(第1阶段)开始,到成熟的洪泛平原森林(第7阶段)。每个演替阶段在结构和区系上都更加复杂。一个样地以早期演替(1 ~ 5)为主,另一个样地以中后期(5 ~ 6)为主。我们用雾网来补充点图数据,以调查非领土物种,主要是食蚁兽和食果动物。由于最早的演替阶段(Tessaria)在任何给定的山舌上都只覆盖很小(<3公顷)的区域,因此我们对另外6个林分进行了普查,以确定其鸟类群落的特征。物种丰富度沿演替梯度增加,但不均匀。结构简单的Tessaria林(阶段1)比接下来的两个演替阶段包含了更多样化的繁殖鸟类群落,在这两个演替阶段鸟类可利用的资源似乎很少。在第3阶段之后,随着不同冠层的形成(第4阶段)、果树的可利用性增加(第5-6阶段)和森林垂直结构的充分发展(第7阶段),每个演替阶段的繁殖物种丰富度增加了31-71种。早期演替鸟类群落(阶段1—阶段3)以少数非常丰富的食虫动物和杂食性动物为主,但来自邻近森林的候鸟以及新北极和南方的候鸟季节性地超过了繁殖的居民。许多在苔属林分繁殖的物种被限制在被调查的七个林分中的一个或两个。演替中期食蚁兽和果食蚁兽的丰富度、丰度和生物量最高。蜜食性丰富反映了演替中期林下占主导地位的巨型海桐林。树皮觅食者在演替后期达到最高丰度,演替中期的优势冠层树种(如雪松)开始死亡,但仍保持直立状态。演替中期缺乏结构更为复杂的成熟森林所特有的许多食虫动物。在消失的物种中有林下嘲笑者、蚂蚁追随者、地面觅食者和许多参与林冠群的树栖食虫者。早期和中期的物种平均比成熟林更丰富。早演替和晚演替的鸟类群落几乎没有共同的物种,许多同系物沿着演替梯度分离。然而,早期演替植被特征的大多数物种也在许多其他类型的自然和人为干扰中被发现。马努河的Tessaria海滩缺乏亚马逊河系统中较大河流同一演替阶段特有的大多数物种。演替中期的物种相对较少,但其中一些物种是西南亚马逊特有的稀有物种。洪泛平原的许多特征物种在第4-6阶段达到了它们的丰度高峰。因此,对西亚马逊地区异常高的物种丰富度的贡献可能比以前认识到的更大。这些结果表明,保护自然的、没有水坝的蜿蜒河流对于保护亚马逊地区的鸟类多样性很重要。中期演替洪泛平原森林的采伐和农业开发可能对区域鸟类群落产生负面影响。并不是所有处于演替早期和中期阶段的物种都适应了人类产生的次生演替。热带鸟类群落的多样性和丰富性在受到干扰后可能需要数百年才能完全恢复
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BIRD COMMUNITY DYNAMICS ALONG PRIMARY SUCCESSIONAL GRADIENTS OF AN AMAZONIAN WHITEWATER RIVER
We used spot-map methods to census birds in two plots (40 ha and 80 ha) representing the early and middle stages of primary succession generated by the meandering of the Manu River in southeastern Peru in 1983 and 1985. We distinguished seven distinct successional stages beginning with the first plant communities growing on open beaches (Tessaria: stage 1) and proceeding through mature floodplain forest (stage 7). Each successional stage was more structurally and floristically complex. One plot was dominated by early successional vegetation (stages 1-5) and the other was domi- nated by middle-to-late stages (5-6). We supplemented spot-map data with mist netting to census nonterritorial species, principally nectarivores and frugivores. Because the ear- liest successional stage (Tessaria) covered only small (<3 ha) areas on any given me- ander tongue, we censused six additional stands to characterize their bird communities. Species richness increased along the successional gradient, but not uniformly. Struc- turally simple Tessaria stands (stage 1) contained more diverse communities of breeding birds than the next two successional stages, which appeared to have few resources avail- able to birds. After stage 3, breeding species richness increased by 31-71 species per successional stage as a distinct canopy layer formed (stage 4), fruiting trees became more available (stages 5-6) and the vertical structure of the forest became fully developed (stage 7: 71 more species than stage 6). Early successional bird communities (stages 1- 3) were dominated by a few very abundant insectivores and omnivores, but wanderers from the adjacent forest plus Nearctic and austral migrants seasonally outnumbered breeding residents. Many species that breed in Tessaria stands were restricted to just one or two of the seven stands censused. The middle stages of succession had the highest estimated richness, abundance, and biomasses of nectarivores and frugivores. Nectarivore abundance reflected the huge stands of Heliconia that dominate the understory of mid- successional stages. Bark foragers reached their highest abundance in late successional stages as the dominant canopy tree species of middle successional stages (e.g., Cedrela odorata) began to die off, but remained standing. Middle successional stages lacked many of the insectivores characteristic of more structurally complex mature forest. Among the missing species were understory Mockers, ant-followers, ground foragers, and many arboreal insectivores that participate in canopy flocks. Species of early and middle stages tended to be more abundant on average than those of mature forest. Early-/and late-successional bird communities had few species in common, and many congeners segregated along this successional gradient. Most species characteristic of early successional vegetation, however, were also found in many other kinds of natural and anthropogenic disturbances. The Tessaria beaches of the Manu lacked most species endemic to the same successional stage on the larger rivers in the Amazon system. Mid-successional stages had relatively fewer species restricted to them, but some of these species are rare and endemic to southwestern Amazonia. Many char- acteristic species of floodplains reached their peak abundances in stages 4-6. Mid-suc- cessional stages, therefore, may play a greater role in contributing to the unusually high species richness of western Amazonia than had previously been recognized. These results point to the importance of preserving natural, undammed meandering rivers in conserving the avian diversity of Amazonia. Logging and agricultural devel- opment of mid-successional floodplain forests probably has a negative impact on regional bird communities. Not all species of the early and middle stages of succession have adapted to human-generated secondary succession. Recovery of the full diversity and richness of tropical bird communities following disturbance may take several hundred
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