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    李婷婷, 崔国发, 杨文化, 蔡体久, 成克武. 水曲柳引种栽植20年后生长表现及其影响[J]. 北京林业大学学报, 2022, 44(9): 30-39. DOI: 10.12171/j.1000-1522.20220188
    引用本文: 李婷婷, 崔国发, 杨文化, 蔡体久, 成克武. 水曲柳引种栽植20年后生长表现及其影响[J]. 北京林业大学学报, 2022, 44(9): 30-39. DOI: 10.12171/j.1000-1522.20220188
    Li Tingting, Cui Guofa, Yang Wenhua, Cai Tijiu, Cheng Kewu. Growth performance and its influence of Fraxinus mandshurica after 20 years of introduction and planting[J]. Journal of Beijing Forestry University, 2022, 44(9): 30-39. DOI: 10.12171/j.1000-1522.20220188
    Citation: Li Tingting, Cui Guofa, Yang Wenhua, Cai Tijiu, Cheng Kewu. Growth performance and its influence of Fraxinus mandshurica after 20 years of introduction and planting[J]. Journal of Beijing Forestry University, 2022, 44(9): 30-39. DOI: 10.12171/j.1000-1522.20220188

    水曲柳引种栽植20年后生长表现及其影响

    Growth performance and its influence of Fraxinus mandshurica after 20 years of introduction and planting

    • 摘要:
        目的  明确水曲柳引种栽植20年后的适应性、生长表现及其对群落物种多样性的影响,为水曲柳的引种和立地环境选择、引种地物种多样性保护提供科学依据。
        方法  采用典型样地调查法,对北京市喇叭沟门自然保护区内引种栽植20年的水曲柳散生个体、水曲柳纯林、水曲柳混交林及其他阔叶林、沟谷草甸进行调查,分析水曲柳个体适应性、生长表现和不同群落类型的物种多样性。
        结果  (1)水曲柳在不同环境或群落类型中的成活保存率Sp均大于90%,能够正常生长并开花结果;(2)水曲柳个体胸径、树高、冠幅、干性及冠长率等形态指标在不同群落或环境中存在差异,活力度值B排序结果为水曲柳散生个体 > 水曲柳混交林 > 水曲柳纯林;(3)水曲柳纯林和水曲柳混交林物种多样性低于其他阔叶林和沟谷草甸群落类型。
        结论  (1)水曲柳在引种栽植20年后进入中龄阶段,仍表现出较强的环境适应性,存活率较高,在林缘及道边散生个体的生长表现最好,在混交林和纯林中受林分郁闭度过高影响,水曲柳生长表现相对较差;(2)水曲柳具有较强的耐阴性和竞争力,进入中龄后在水曲柳纯林和水曲柳混交林中形成较高的乔木层郁闭度,导致灌草层物种减少,不利于当地物种多样性的保护;(3)在喇叭沟门自然保护区引种栽植水曲柳时,应选择沟谷下部弃耕地或道路两侧绿化用地,对于沟谷草甸和其他次生林环境不宜栽植水曲柳。

       

      Abstract:
        Objective  This study was conducted to clarify the adaptability and growth performance of Fraxinus mandshurica after 20 years of introduction and planting and its impact on species diversity of the community, so as to provide scientific basis for the introduction and site environment selection of Fraxinus mandshurica, and the biodiversity protection of the introduced site.
        Method  By the method of typical sample investigation, 3 types of Fraxinus mandshurica (scattered individuals, pure forest and mixed forest) and 2 other community types (broadleaved mixed forests and gully meadows) were investigated in Labagoumen Nature Reserve in Beijing to analyze the individual adaptability, growth performance of Fraxinus mandshurica and the species diversity of different community types. The sampled Fraxinus mandshurica had been introduced and planted for 20 years in the study site.
        Result  (1) The survival and preservation rate (Sp) of Fraxinus mandshurica was greater than 90% in different sampling types, and some individuals had begun to grow and blossom normally; (2) morphological indexes such as DBH, tree height, crown width, trunk straightness and crown length ratio of Fraxinus mandshurica individuals were different in varied sampling types, the order of vigorous degree (B) was as follows: Fraxinus mandshurica scattered individuals > Fraxinus mandshurica mixed forest > Fraxinus mandshurica pure forest; (3) the species diversity of Fraxinus mandshurica pure forest and Fraxinus mandshurica mixed forest was lower than that of broadleaved forest and gully meadow community types.
        Conclusion  (1) Fraxinus mandshurica has entered the middle-age stage and shows strong environmental adaptability and high survival rate after 20 years of introduction and planting. The growth performance of scattered individuals at the forest edge and roadside was better than that of individuals in mixed forest and pure forest due to higher canopy density and individual competition of the latter; (2) Fraxinus mandshurica has strong shade tolerance and competitiveness. After entering the middle age, it forms a high canopy density in the pure and mixed Fraxinus mandshurica forests, resulting in the reduction of species in the shrub and grass layer, which is not conducive to the protection of local species diversity; (3) when introducing and planting Fraxinus mandshurica in Labagoumen Nature Reserve, the abandoned farmland in the lower part of the gully or the greening land on both sides of the road should be selected, the gully meadows and other secondary forest environments are not suitable for planting Fraxinus mandshurica.

       

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