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首页> 外文期刊>Ecological Applications >Seed rain under tree islands planted to restore degraded lands in a tropical agricultural landscape
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Seed rain under tree islands planted to restore degraded lands in a tropical agricultural landscape

机译:为恢复热带农业景观中退化的土地而种植的树岛下的种子雨

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Planting native tree seedlings is the predominant restoration strategy for accelerating forest succession on degraded lands. Planting tree "islands" is less costly and labor intensive than establishing larger plantations and simulates the nucleation process of succession. Assessing the role of island size in attracting seed dispersers, the potential of islands to expand through enhanced seed deposition, and the effect of planting arrangements on seed dispersal by birds and bats informs restoration design. Determining the relative importance of local restoration approach vs. landscape-level factors (amount of surrounding forest cover) helps prioritize methods and locations for restoration. We tested how three restoration approaches affect the arrival of forest seeds at 11 experimental sites spread across a gradient of surrounding forest cover in a 100-km_2area of southern Costa Rica. Each site had three 50 X 50 m treatments: (1) control (natural regeneration), (2) island (planting tree seedlings in patches of three sizes: 16 m~2, 64 m ~2, and 144 m~2), and (3) plantation (planting entire area). Four tree species were used in planting (Terminalia amazonia, Vochysia guatemalensis, Erythrina poeppigiana, and Inga edulis). Seed rain was measured for 18 months beginning ~2 years after planting. Plantations received the most zoochorous tree seeds (266.1 ± 64.5 seeds-m~(-2')yr~(-1) [mean ± SE]), islands were intermediate (210.4 ± 52.7 seeds.m ~(-2)yr~(-1)), and controls were lowest (87.1 ± 13.9 seeds.m~(-2)yr~(-1)). Greater tree seed deposition in the plantations was due to birds (0.51 ± 0.18 seeds'm~(-2)'d ~(-1)), not bats (0.07 ± 0.03 seeds-m~(-2)'d ~(-1)). Seed rain was primarily smallseeded, early-successional species. Large and medium islands received twice as many zoochorous tree seeds as small islands and areas away from island edges, suggesting there is a minimum island size necessary to increase seed deposition and that seed rain outside of planted areas is strongly reduced. Planting design was more important for seed deposition than amount of forest cover within the surrounding 100- and 500-m radius areas. Establishing plantations and large islands facilitates the arrival of early-successional tree seeds and represents a broadly applicable strategy for increasing seed rain on abandoned agricultural lands. However, more intensive restoration approaches may be necessary for establishment of dispersal-limited species.
机译:种植原生树苗是加速退化土地上森林演替的主要恢复策略。与建立较大的人工林并模拟演替成核过程相比,种植树木“孤岛”的成本和劳动强度较低。评估岛屿大小在吸引种子分散器中的作用,岛屿通过增强种子沉积而扩展的潜力以及种植安排对鸟类和蝙蝠传播种子的影响,有助于进行恢复设计。确定本地恢复方法与景观水平因素(周围的森林覆盖量)的相对重要性有助于确定恢复方法和位置的优先级。我们测试了三种恢复方法如何影响森林种子到达哥斯达黎加南部100 km_2区域中周围森林覆盖梯度的11个实验点。每个站点进行3次50 X 50 m处理:(1)对照(自然再生),(2)岛(在三种尺寸的斑块上种植树苗:16 m〜2、64 m〜2和144 m〜2), (3)种植(种植整个区域)。种植中使用了四种树种(Terminalia amazonia,Vochysia guatemalensis,Erythrina poeppigiana和Inga edulis)。播种后约2年开始测量18个月的种子降雨。人工林收到的针叶树种子最多(266.1±64.5种子-m〜(-2')yr〜(-1)[平均值±SE]),岛屿中等(210.4±52.7种子.m〜(-2)yr〜 (-1)),而对照最低(87.1±13.9种子.m〜(-2)yr〜(-1))。人工林中更大的树木种子沉积是由于鸟类(0.51±0.18种子-m〜(-2)'d〜(-1)),而不是蝙蝠(0.07±0.03种子-m〜(-2)'d〜( -1))。种子雨主要是小种子,早期成功种。大中型岛屿获得的食虫性树木种子数量是小岛和远离岛屿边缘地区的两倍,这表明增加种子沉积所需的最小岛屿面积非常大,并且种植面积以外的种子雨量大大减少。种植设计对种子的沉积比半径100和500米半径区域内的森林覆盖量更为重要。建立人工林和大岛有利于早期成功的树木种子的到来,并代表了广泛应用的策略,用于增加废弃农业土地上的种子雨量。但是,可能需要更密集的恢复方法来建立扩散受限的物种。

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