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    罗也, 王君, 杨雨春, 何怀江, 刘婷. 东北胡桃楸次生林生长随林龄和林分密度的变化规律[J]. 北京林业大学学报. DOI: 10.12171/j.1000-1522.20230171
    引用本文: 罗也, 王君, 杨雨春, 何怀江, 刘婷. 东北胡桃楸次生林生长随林龄和林分密度的变化规律[J]. 北京林业大学学报. DOI: 10.12171/j.1000-1522.20230171
    Luo Ye, Wang Jun, Yang Yuchun, He Huaijiang, Liu Ting. Growth changes of Juglans mandshurica secondary forest with stand age and stand density in Northeast China[J]. Journal of Beijing Forestry University. DOI: 10.12171/j.1000-1522.20230171
    Citation: Luo Ye, Wang Jun, Yang Yuchun, He Huaijiang, Liu Ting. Growth changes of Juglans mandshurica secondary forest with stand age and stand density in Northeast China[J]. Journal of Beijing Forestry University. DOI: 10.12171/j.1000-1522.20230171

    东北胡桃楸次生林生长随林龄和林分密度的变化规律

    Growth changes of Juglans mandshurica secondary forest with stand age and stand density in Northeast China

    • 摘要:
      目的 通过研究胡桃楸次生林生长随林龄和林分密度的变化规律,探讨胡桃楸不同龄组生长的适宜林分密度,以期为胡桃楸次生林经营提供数据支持。
      方法 本研究在东被三省东部张广才岭(ZGCL)、老爷岭(LYL)、长白山(CBS)和哈达岭(HDL)4个调查地区,设置不同的胡桃楸林龄、林分密度调查样地,分析其胸径(DBH)、树高、蓄积等指标与林龄和林分密度的关系。
      结果 (1)长白山地区胡桃楸平均胸径、平均树高和蓄积量值均最大,显著大于其他地区(P < 0.05),各指标大小关系为CBS > LYL > ZGCL > HDL。(2)通过模型拟合,林龄与胡桃楸胸径、树高、蓄积以逻辑斯蒂模型拟合效果最优(R2值分别达到0.983 2、0.962 2和0.973 1),林分密度与胡桃楸胸径、树高、蓄积以二次项模型拟合最优(R2值分别达到0.833 6、0.665 9和0.858 7)。(3)各地区胡桃楸胸径、树高和蓄积大小均随着林龄的增加呈现出逐渐增大的趋势,且前期增速较大,当达到50年之后,增速变缓。(4)各地区胡桃楸胸径、树高和蓄积大小均随着林分密度的增加呈现出逐渐降低的趋势,低密度下降低趋势较小,超过一定密度后,降低速度较大。(5)4个地区胡桃楸生长情况表现为, < 40年时,在450 ~ 550株/hm2的中等林分密度下生长效果最好, > 40年时,在350 ~ 450株/hm2的低林分密度下生长效果最好,即胡桃楸林龄越大,对于林分密度的要求越高。
      结论 初步探明了不同地区胡桃楸不同林龄的适宜控制密度,即可通过人工抚育和疏伐等方式控制不同林龄段林分密度,满足胡桃楸的生长空间。该结果可为胡桃楸次生林经营提供一定支撑。

       

      Abstract:
      Objective To research the suitable stand density for the growth of secondary forest of Juglans mandshurica in different age groups by understanding the growth changes of J. mandshurica with stand age and stand density, in order to provide theoretical support for the subsequent management of secondary forests of J. mandshurica.
      Method Survey plots of different stand age and stand density for J. mandshurica were set up in Zhangguangcailing (ZGCL), Laoyeling (LYL), Changbai Mountain (CBS) and Hadaling (HDL) of the eastern part of the three Northeastern Provinces, to analyze the relationship between diameter at breast height (DBH), tree height and accumulation with stand age and stand density.
      Result (1) The average DBH, average tree height and accumulation of J. mandshurica were the largest in Changbai Mountain, which were significantly larger than those in other areas (P < 0.05), and the relationship between each index was CBS > LYL > ZGCL > HDL. (2) According to the model fitting, logistic model was the best fitting method for stand age with DBH, tree height and accumulation of J. mandshurica, (R2 values of 0.983 2, 0.962 2, and 0.973 1, respectively). The quadratic model was the best fitting method for stand density with DBH, tree height and accumulation of J. mandshurica (R2 values of 0.833 6, 0.665 9 and 0.858 7, respectively). (3) The DBH, tree height and accumulation of J. mandshurica were increasing with age in each region, and the increase rate was faster in the early stage. However, the growth rate slowed down after reaching 50 years. (4) The DBH and tree height of J. mandshurica decreased with increase stand density in each region, and the decreasing trend was smaller at low density, but the decreasing speed was higher when the density exceeds a certain level; (5) The growth of J. mandshurica in the four regions showed that the best growth effect was achieved at a moderate stand density of 450-550 tree/ha at < 40 years old, and at a low stand density of 350-450 tree/ha at > 40 years old. That is, the older the J. mandshurica, the higher the requirement for stand density.
      Conclusion The results preliminarily revealed the suitable control density for different ages of J. mandshurica stand in different regions, which can be controlled through artificial nurturing and thinning to meet the growth space of J. mandshurica trees. These findings can serve as a basis for the management of J. mandshurica secondary forests.

       

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