哈萨克斯坦北部松林间伐对保护性松林生物可持续性的影响

A. Dancheva, S. Zalesov
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引用次数: 0

摘要

本文介绍了70多年来在哈萨克斯坦北部哈萨克高地进行的松林砍伐的结果及其对生物可持续性的影响(以国家自然公园“Burabay”为例)。研究对象为生长在干燥森林条件下的高密度成熟松林。研究结果表明,在生命状态指标(VSI)、复合估计指标(CEI)和树木长细系数(H/D)的平均值上,大部分林段的松林表现为“减弱”。在疏伐强度较大和非常大的林分中,用树木长细系数(H/D)评价松林为健康林分。论证了松林的重要地位和林业实践的最大可信指标是林木长细系数。评价了高强度间伐后松林树木长细系数和H/D值小于100的树木数量最多(占树木总数的70%)。森林中大量H/D < 100的树木表明森林内树木之间的竞争较弱,对自然和人为因素具有较高的抵抗力。得到的数据表明,强间伐对松树径向生长的增加有积极的影响。建议在哈萨克斯坦北部干旱生长条件下形成可持续的松林,分两步间伐,在25-30年和40-50年期间破坏26 - 35%的蓄积量,随后增加砍伐。
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Influence of thinning on protective pineries biosustainability in Northern Kazakhstan
The article presents the results of thinnings in pineries of the Kazakh uplands in Northern Kazakhstan carried out for an over 70-year period and their influence on biosustainability (on the example of the state national natural park «Burabay»). The research objects are high-density mature pine forests growing in dry forest conditions. The results of research have shown that to the average values of the vital status indicator (VSI), the complex estimated indicator (CEI) and the tree slenderness coefficient (H/D), pine stands in most sections are characterized as «weakened». In forest stands after thinning of strong and very strong intensity of thinning in terms of tree slenderness coefficient (H/D) the pine forests is assessed as healthy. It is proved that the vital status maximum credible indicators of the pine forests and the implementation of forestry practices in them is the tree slenderness coefficient. The largest number of trees (up to 70 % of the total number of trees) with tree slenderness coefficient an H/D value of less than 100 in the pine forest after very high intensity thinning is evaluated. A large number of trees with H/D < 100 in the forests proves a weak competition between trees in the forests and higher resistance to natural and anthropogenic factors are proved. The data obtained show a positive effect of strong thinning on the increase in the radial growth of pine trees. For formation of sustainable pine forests in dry growing conditions in Northern Kazakhstan with thinning one-two steps with 26–35 % of the stock volumes destruction at the age of 25–30 years and 40–50 years, and with subsequent increment felling in them is recommended.
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