Cultivating Siberian Stone Pine Plantations under Wild Animal Damage Conditions

G. Terekhov, Elena M. Andreeva, S. Stetsenko
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Abstract

The research of 26-year-old mixed plantations of Siberian spruce and Siberian stone pine cultivated by biogroups of about 300 pcs/ha (2–5 stone pine seedlings alternating 4–9 spruce seedlings in a row) has shown that the damage rate by moose to them is much lower than to pure stone pine plantations or the mixed ones of Siberian stone pines and Scots pines we have studied before. The share of biogroups containing damaged stone pine trees is 18 %. A third of this number is plantations with damage to all the trees. This is most pronounced in biogroups of 4 to 5 stone pines as well as in case of frequent alternation of biogroups in a row. 76 % living stone pines have been preserved (89.3 % of them without damage to the stem). About two thirds of them (about 500 pcs/ha) grow in the crown of spruce trees adjacent to stone pine biogroups. Prolonged exposure to growing in a spruce tree crown negatively affects the growth of a stone pine’s central shoot and crown. We are the first in the Middle Urals to propose a scheme for cultivating sustained productive mixed plantations of Siberian stone pines and Siberian spruce trees (or Norway spruce trees). Stone pines are planted in biogroups of 2–3 seedlings, beginning the planting strictly on one side of the site. The first biogroup in odd-numbered rows (1, 2, 3, 5, etc.) is planted after 3 spruce seedlings from the beginning of the row, the second and subsequent biogroups in these rows – after 9 spruce seedlings. The first biogroup in even-numbered rows (2, 4, 6, 8, etc.) is planted after 9 spruce seedlings from the beginning of the row, maintaining this sequence until the end of the row. Every row in mixed plantations is concluded with planting no less than 3 spruce seedlings. During silvicultural treatment procedures natural regeneration is completely removed: softwoods – by mechanical means, and hard woods – by ringing or injection of environmentally friendly water-based chemicals. These measures reduce or eliminate the appearance of coppice and, accordingly, food reserve for wild animals. Spruce trees adjacent to stone pine biogroups are cut down while lightening and thinning, which creates the possibility for the growth of stone pines. The proposed method for cultivating plantations of Siberian stone pines and Siberian spruce trees has been patented. It can be introduced into silvicultural practice in the taiga zone where stone pines are grown.
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在野生动物破坏条件下栽培西伯利亚石松
对 26 年树龄的西伯利亚云杉和西伯利亚石松混合种植园进行的研究表明,与我们以前研究过的纯石松种植园或西伯利亚石松和苏格兰松混合种植园相比,驼鹿对这些种植园的破坏率要低得多。含有受损石松的生物群占 18%。其中三分之一是所有树木都受损的种植园。这种情况在由 4 到 5 棵松树组成的生物群以及在生物群频繁交替的情况下最为明显。76% 的活体石松被保存下来(其中 89.3% 的石松茎干未受损伤)。其中约三分之二(约 500 株/公顷)生长在与石松生物群相邻的云杉树冠中。长期生长在云杉树冠中会对石松中心枝和树冠的生长产生负面影响。我们是乌拉尔中部地区第一个提出培育西伯利亚石松和西伯利亚云杉(或挪威云杉)持续高产混合种植园计划的国家。石松以 2-3 株树苗为一组,严格按照地块的一侧开始种植。奇数行(1、2、3、5 等)中的第一个生物组在从该行开始种植 3 棵云杉树苗后种植,这些行中的第二个及以后的生物组在种植 9 棵云杉树苗后种植。偶数行(2、4、6、8 等)中的第一个生物组在该行开始的 9 棵云杉树苗之后种植,保持这一顺序直到该行结束。混交林的每一行最后都要种植不少于 3 棵云杉树苗。在造林处理过程中,自然再生的云杉将被完全清除:软木--通过机械方法,硬木--通过环剥或注入环保型水基化学品。这些措施减少或消除了灌木丛的出现,因此也减少或消除了野生动物的食物储备。与石松生物群相邻的云杉被砍伐,同时进行减光和疏伐,这为石松的生长提供了可能。建议的西伯利亚石松和西伯利亚云杉人工林培育方法已获得专利。该方法可在种植石松的泰加地带的造林实践中采用。
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