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首页> 外文期刊>Australian Forestry >Overstorey growth response to thinning, burning and fertiliser in 10-13-year-old rehabilitated jarrah (Eucalyptus marginata) forest after bauxite mining in south-western Australia.
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Overstorey growth response to thinning, burning and fertiliser in 10-13-year-old rehabilitated jarrah (Eucalyptus marginata) forest after bauxite mining in south-western Australia.

机译:在澳大利亚西南部的铝土矿开采后,10-13岁的翻新的jarrah( Eucalyptus marginata )森林对稀疏,燃烧和化肥的过度生长响应。

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摘要

Silvicultural treatment of dense stands of regrowth jarrah (Eucalyptus marginata) and marri (Corymbia calophylla [Eucalyptus calophylla]) established following bauxite mining in the jarrah forests of Western Australia may be required for both timber production and catchment water yield objectives. In 10- to 13-year-old rehabilitation stands, four thinning treatments (1500-2500 (unthinned), 1111, 625 and 400 stems ha-1 retained) were applied in summer and either burnt by a prescribed fire in the following autumn or left unburnt. Fertilizer was also applied in a factorial combination with thinning and burning treatments. Tree growth was assessed 4 years after treatment. Mean individual tree diameter growth (under bark) was 0.48 cm year-1 in unthinned stands, rising exponentially to 1.44 cm year-1 when stands were thinned to 400 stems ha-1 (4.2 m2 ha-1 basal area under bark (baub)). Application of fertilizer in unburnt plots further increased growth rates of the two heaviest thinnings by 18 and 25% compared to equivalent unburnt and thinned treatments. Maximum stand basal area growth under bark (basal area under bark increment (baubi)) of 2 m2 ha-1 year-1 was achieved with thinning to 1111 stems ha-1 (7.6 m2 ha-1 baub). However, the heaviest thinning to 4.2 m2 ha-1 achieved 76% of maximum stand growth whilst increasing diameter growth of the best 100 retained trees per hectare from 1.4 cm year-1 to 2 cm year-1 under bark, potentially shortening crop rotation. The heaviest thinning also increased the time for leaf area index to return post-treatment to pre-treatment levels to a predicted 7 years compared with 5 years when thinned to 1111 stems ha-1, which may extend the duration of any increased stream flow related to thinning. Burning in autumn reduced the effect of thinning such that mean diameter increment under bark was only 1.0 cm year-1 at the heaviest thinning, and there was no fertilizer effect. Autumn burning after thinning also stimulated dense understorey and tree coppice regeneration and is therefore not recommended.
机译:可能需要对西澳大利亚的jarrah森林中的铝土矿开采后建立的茂密的再生长生jarrah( Eucalyptus marginata )和marri( Corymbia calophylla [Eucalyptus calophylla ])林分进行造林处理用于木材生产和集水的目标。在10到13岁的康复林中,夏季进行了4种间伐处理(保留了1500 2500>(未保留)1111、625和400茎ha -1 ),并通过接下来的秋天开明的火或不燃。肥料还与稀释和燃烧处理结合使用。处理4年后评估树木生长。在未稀疏的林分中,平均个体树径增长(在树皮下)为0.48 cm year -1 ,当林分稀疏到400茎ha <时,指数增长到1.44 cm year -1 。 sup> -1 (树皮下有4.2 m 2 ha -1 基面积(鲍勃))。与等量的未燃烧和稀化处理相比,在未燃烧的地块中施肥使两个最重的间伐材料的生长速度进一步提高了18%和25%。树皮下的最大立足基面积增长(树皮下的基面积增加(baubi))达到2 m 2 ha -1 年 -1 减薄至1111茎ha -1 (7.6 m 2 ha -1 鲍勃)。但是,最重的稀疏到4.2 m 2 ha -1 实现了林分最大生长的76%,同时使每公顷最好的100棵保留树木的直径生长从1.4 cm年开始<树皮下的sup> -1 到2 cm年 -1 ,可能会缩短作物轮作。最重的间伐还使叶片面积指数恢复到处理前水平的时间延长至预计的7年,而稀疏至1111个茎ha -1 的5年增加了5年,这可能会延长与稀疏有关的任何增加的水流持续时间。秋季燃烧减少了疏伐的效果,因此在最大的疏伐下,树皮下的平均直径增量仅为1.0 cm year -1 ,而没有施肥效果。疏伐后的秋季燃烧也刺激了茂密的林下层和树木小灌木林的再生,因此不建议使用。

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