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首页> 外文期刊>The Forestry Chronicle >Snag abundance 20, 30, and 40 years following fire and harvesting in boreal forests
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Snag abundance 20, 30, and 40 years following fire and harvesting in boreal forests

机译:北方森林火灾和砍伐后20、30和40年的断枝丰度

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摘要

The retention of standing dead trees (snags) has become an important conservation concern, especially when forest management efforts attempt to emulate natural disturbance. We investigate the abundance of snags within Ontario's boreal forest following 10-20, 21-30, and 31-40 years of both fire and forest harvest disturbance over a 24 000-km(2) area. Fire frequency varied considerably, with 90% of the fires in the study area occurring in the 1970s. We did not detect differences in basal area of snags (m(2)/km(2)) between burned and harvested stands. However, differences occurred in dead-stem density (number/km(2)); the burned stands produced more snags in the 21- to 30-year post-disturbance class and the harvested stands produced more snags in the 31- to 40-year post-disturbance class. Similarly, the distribution of diameter classes of snags differed between the burned and harvested stands. In size classes greater than 32 cm (diameter at breast height), we found more snags in the harvested forests 21-40 years following disturbance. We did not find differences in the basal area of snags between disturbance types, whether they were hardwood or softwood. However, hardwood snags occurred in greater abundance in the larger diameter classes. Our findings are limited by the changing timber harvest treatments (selective harvest, clearcut, and ecological cut), the small number of disturbance events, and the variety of stand compositions. More research is required on the ecological factors influencing snag abundance to improve development of local forest management plans and to design landscapes that conserve forest structure and biodiversity.
机译:保留死木(树桩)已成为重要的保护问题,尤其是在森林管理工作试图模仿自然干扰时。我们调查了在24000 km(2)区域火灾和森林采伐扰动10-20年,21-30年和31-40年后,安大略省北方森林中大量的障碍物。火灾频率变化很大,研究区域90%的火灾发生在1970年代。我们没有发现燃烧和收获林分之间断枝的基础面积(m(2)/ km(2))的差异。但是,死杆密度不同(数量/ km(2));被烧毁的林分在扰乱后21至30年的等级中产生更多的障碍,而收割的林分在扰乱后31至40年的类别中产生更多的障碍。类似地,在燃烧和收获林分之间,粗枝的直径等级分布也不同。在大于32厘米(胸径的直径)的尺寸等级中,我们在干扰后21至40年内发现了更多的收获林。我们没有发现扰动类型(硬木或软木)之间的断枝基部区域存在差异。但是,在较大直径的类别中,硬木碎屑的出现更为丰富。我们的发现受到不断变化的木材采伐处理方式(选择性采伐,砍伐和生态采伐),少量干扰事件以及林分组成变化的限制。需要对影响断枝丰度的生态因素进行更多研究,以改善当地森林管理计划的制定并设计保护森林结构和生物多样性的景观。

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