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首页> 外文期刊>Journal of Sustainable Forestry >Can timber production be compatible with conservation of forest biodiversity? -- Two case studies of plant biodiversity in managed neotropical forests.
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Can timber production be compatible with conservation of forest biodiversity? -- Two case studies of plant biodiversity in managed neotropical forests.

机译:木材生产能否与森林生物多样性保护相适应? -关于新热带雨林中植物生物多样性的两个案例研究。

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摘要

A variety of practices can greatly diminish the impacts of forest management on biodiversity. A case study from a subtropical humid forest reserve in the province of Misiones, Argentina, is presented to illustrate a uniform spacing method of forestharvest, which is contrasted with the prevalently used minimum diameter cutting method (this extracts commercial species only if they have a minimum diameter specified per species, in the range of 40-55 cm dbh -- diameter at breast height). In the uniform spacing method, trees are selected for extraction or marked for retention according to their scarcity, their horizontal distribution, and their characteristics to serve as seed trees. Three years after harvesting, the forest cut by uniform spacing hadthe highest density of seedlings of total as well as of commercial species, and it also exhibited high diversity of understorey plants other than trees. A case study of a silvicultural experiment carried out by CATIE in Costa Rica is also presented, focusing on the effects of logging followed by postharvest silvicultural treatments on forest species richness and composition during the first 6-7 yr following logging and the 5 yr following the silvicultural treatments. The logging operation was carried out under strict planning and control for sustainability, in 1989 and 1990; the total harvestable volume was 23 m3/ha, but actual harvest intensity was 42% of this. There were 3 postharvest silvicultural interventions: (1) a control, with no further treatment after logging; (2) a poison girdling applied in 1991 to eliminate most non-commercial trees ?0 cm dbh, and a subsequent liberation of potential crop trees; and (3) a shelterwood treatment applied in 1992, which maintained a high canopy while creating conditions for the regeneration of more light-demanding commercial species by chainsaw thinning the middle storeys. The forest studied exhibited marked compositional variation in relation to a topographical gradient after the implementation of the experiment; such beta- or ecosystem diversity should be taken into account in all future evaluations of the effect of forest management on plant biodiversity. Postharvest silvicultural treatments caused an immediate reduction in species-richness ?0 cm dbh in 1.0 ha due to the chance elimination of species represented by one or a small number of individuals in the plots, and may affect overall species composition in the medium term as they are directed to favouring commercial species by decreasing competition from non-commercial species. Species richness declined under both silvicultural treatments, although no changes of species-richness or composition as a result of silvicultural treatment were evident in the forest understorey (individuals 2.5-9.9 cm dbh). The only detectable changes in understorey plant biodiversity were caused by the felling and extraction of timber, and these changes were restricted to the very localized areas disturbed by these management operations. The application of low-intensity logging methods with selection of remnant trees requires detailed pre- and post-harvest forest inventories and follow up of treatments to ensure successful regeneration and growth of desired species. The Costa Rican study shows that different forest management operations (logging and silviculture in this case) may have different effects on plant biodiversity; this perspective should be applied to future studies so that the balance between production and conservation in tropical forests will be betterunderstood. Long-term follow up is needed to assess the true effects of forest management on biodiversity, including natural regeneration as well as growth dynamics of trees, until a whole harvest cycle is completed.
机译:各种做法可以大大减少森林管理对生物多样性的影响。本文以阿根廷米西奥内斯(Misiones)省亚热带湿润森林保护区的案例研究为例,说明了均匀的森林采伐间距方法,该方法与普遍使用的最小直径采伐方法形成对比(此方法仅在具有最小采伐量的情况下才提取商业物种)每个物种指定的直径,范围为40-55 cm dbh-乳房高度的直径)。在均匀间距方法中,根据树木的稀缺性,水平分布和它们的特性,选择要提取的树木或标记为保留的树木,以用作种子树。采伐三年后,以均等间距砍伐的森林的总树苗和商品树苗的密度最高,除树木以外,其下层植物的多样性也很高。还介绍了由CATIE在哥斯达黎加进行的一次造林实验的案例研究,重点是伐木后采伐后进行造林处理对伐木后的前6-7年和伐木后的5年内森林物种丰富度和组成的影响。造林治疗。 1989年和1990年在严格的计划和控制下进行了伐木作业,以实现可持续性;总收获量为23立方米/公顷,但实际收获强度为此的42%。采后有3种造林干预措施:(1)对照,伐木后无需进一步治疗; (2)于1991年采用了有毒的除草剂,以消灭大多数0 cm dbh以下的非商业树木,并随后解放了可能的农作物树木; (3)1992年采用的防护林处理,保持了较高的树冠,同时通过电锯使中间层变薄,创造了条件,使更多光需求的商业物种得以再生。实验实施后,所研究的森林相对于地形梯度表现出明显的成分变化;将来在对森林管理对植物生物多样性的影响的所有评估中都应考虑到这种beta或生态系统的多样性。收获后的造林处理导致1.0公顷的物种丰富度立即降低了0 cm dbh,这是因为该地块中一个或少数几个个体所代表的物种有机会被淘汰,并可能在中期影响总体物种组成,因为它们旨在通过减少与非商业物种的竞争来偏向商业物种。在这两种造林方式下,物种丰富度都下降了,尽管在林下层(个体为2.5-9.9 cm dbh)下,没有发现由于造林方式引起的物种丰富度或组成的变化。在底层植物生物多样性中唯一可检测到的变化是由砍伐和砍伐木材引起的,这些变化仅限于受这些管理活动干扰的局部地区。低强度伐木方法与残树的选择相结合,需要详细的收获前和收获后森林清单以及后续处理措施,以确保所需物种的成功再生和生长。哥斯达黎加的研究表明,不同的森林经营活动(在这种情况下为伐木和造林)可能对植物生物多样性产生不同的影响。这种观点应运用于未来的研究,以便更好地理解热带森林生产与保护之间的平衡。需要长期采取后续行动,以评估森林管理对生物多样性的真正影响,包括自然更新以及树木的生长动态,直到完成整个收获周期为止。

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