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首页> 外文期刊>Ecology: A Publication of the Ecological Society of America >Forest dynamics after successive spruce budworm outbreaks in mixedwood forests
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Forest dynamics after successive spruce budworm outbreaks in mixedwood forests

机译:混材林中连续发生云杉芽虫爆发后的森林动态

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In order to assess the long-term spatiotemporal influence of the spruce budworm in sub-boreal mixedwood forests, we studied the effect of three successive outbreaks in a region of western Quebec, Canada. We used dendrochronology to detect past outbreaks in three areas ( 111 - 185 ha), based on the recruitment age of balsam fir ( Abies balsamea) and on growth patterns of white spruce ( Picea glauca), the two main host species of this defoliating insect. We also used a series of aerial photographs taken between 1935 and 2003 to evaluate overstory mortality and post-outbreak succession patterns in these same areas. Individual outbreaks had a spatially homogenous impact on host species throughout the region, but successive outbreaks differed in intensity: the two outbreaks around 1910 and 1980 caused widespread mortality in the overstory, but an outbreak around 1945 had little impact, probably because the forest mosaic had not yet recuperated from the 1910 outbreak. No clear outbreak was detected in the later part of the 19th century. In portions of the study areas where the 1910 outbreak had a major impact, between 36% and 50% of the stands were reoccupied by balsam fir stands in the period up to the 1980 outbreak ( cyclic succession), the rest being at least partly replaced by nonhost species such as Betula spp. Changes in forest composition after the 1910 outbreak were mostly associated with upper-slope positions in all study areas. The 1980 outbreak also had a higher impact than earlier outbreaks in lower-slope positions dominated by black spruce ( Picea mariana) - balsam fir mixtures. These results suggest that, at the regional scale, the abundance of mature or over-mature balsam fir stands does not determine the outbreak cycle. When an outbreak occurs, however, its impact will be strongly constrained by forest characteristics such as stand composition and structure, which are themselves influenced by previous disturbances and slope position.
机译:为了评估云杉芽虫在亚北方杂木林中的长期时空影响,我们研究了加拿大魁北克西部地区连续三次爆发的影响。根据香脂冷杉(Abies balsamea)的募集年龄和白云杉(Picea glauca)的生长模式,我们使用树轮年代学方法检测了三个地区(111-185公顷)过去的疫情,这是该落叶昆虫的两个主要寄主物种。我们还使用了一系列在1935年至2003年之间拍摄的航空照片,以评估这些地区的过度故事死亡率和暴发后的演替模式。个别暴发对整个区域的寄主物种在空间上具有同质性影响,但随后的暴发强度不同:1910年和1980年的两次暴发在楼上造成了广泛的死亡,但1945年左右的暴发几乎没有影响,可能是因为森林镶嵌尚未从1910年爆发中恢复过来。在19世纪后期,没有发现明显的疫情。在1910年疫情造成重大影响的研究区域中,直到1980年爆发之前,苦瓜冷杉林分重新占据了36%至50%的林分(周期性演替),其余的至少部分被替代了由非寄主物种,例如桦属。 1910年爆发后森林组成的变化主要与所有研究区域的上坡位置有关。在由黑云杉(云杉(Picea mariana))-苦瓜混合物控制的低坡度位置,1980年的爆发比早期爆发的影响更大。这些结果表明,在区域范围内,成熟或过度成熟的苦瓜杉木林的丰富程度并不能决定爆发周期。但是,当爆发时,其影响将受到森林特征(如林分组成和结构)的强烈限制,而林分本身又受先前的干扰和斜坡位置的影响。

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