生物多样性 ›› 2016, Vol. 24 ›› Issue (3): 252-261. DOI: 10.17520/biods.2015282
王慧杰1, 常顺利1,*(), 张毓涛2, 谢锦1, 何平1, 宋成程1, 孙雪娇1
收稿日期:
2015-10-21
接受日期:
2016-01-11
出版日期:
2016-03-20
发布日期:
2016-04-05
通讯作者:
常顺利
基金资助:
Huijie Wang1, Shunli Chang1,*(), Yutao Zhang2, Jin Xie1, Ping He1, Chengcheng Song1, Xuejiao Sun1
Received:
2015-10-21
Accepted:
2016-01-11
Online:
2016-03-20
Published:
2016-04-05
Contact:
Chang Shunli
摘要:
密度制约是维持自然森林群落物种共存的重要机制之一。雪岭云杉(Picea schrenkiana)是天山森林群落的单优种, 在我国温带森林中占有重要地位。本文基于对天山雪岭云杉8 ha森林动态监测样地的两次调查结果, 分析了该样地群落物种组成的动态变化, 运用点格局方法分析了雪岭云杉个体在不同龄级的空间分布格局及其关联性, 探讨了该群落的密度制约效应。结果表明: (1)该样地内, DBH ≥ 1 cm的木本植物在2009年有11,835株, 2014年为11,050株, 5年间的个体死亡率为8.82%, 补员率为2.19%, 个体株数净减少6.63%。(2)使用双关联函数g(r)分析了不同龄级雪岭云杉的空间分布格局, 发现幼龄树和中龄树在0-40 m尺度上主要呈现聚集分布, 但随着尺度增大聚集强度逐渐减小; 老龄树在0-2 m及4 m尺度上呈随机分布, 在其他尺度上呈聚集分布, 但聚集程度较小。(3)用“案例-对照”设计的方法, 排除生境异质性的影响后, 将幼龄树和中龄树作为案例, 老龄树作为对照, 对比幼龄树、中龄树与老龄树的分布格局, 发现雪岭云杉幼龄树和中龄树在0-40 m尺度上呈现额外的聚集, 随着径级的增大, 这种额外的聚集强度逐渐减小, 即表现出密度制约效应。(4)老龄树与中龄树、幼龄树的空间关联性相同, 在0-40 m尺度上均呈明显负关联。
王慧杰, 常顺利, 张毓涛, 谢锦, 何平, 宋成程, 孙雪娇 (2016) 天山雪岭云杉森林群落的密度制约效应. 生物多样性, 24, 252-261. DOI: 10.17520/biods.2015282.
Huijie Wang, Shunli Chang, Yutao Zhang, Jin Xie, Ping He, Chengcheng Song, Xuejiao Sun (2016) Density-dependent effects in Picea schrenkiana forests in Tianshan Mountains. Biodiversity Science, 24, 252-261. DOI: 10.17520/biods.2015282.
物种 Species | 生长型 Growth form | 多度 Abundance | 重要值 Importance value (%) | 平均胸径 Mean DBH (cm) | 死亡数 Number of dead individual | 补员数 Number of recruited individual | 胸径净增长 DBH net growth (cm) | |||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
2009 | 2014 | 2009 | 2014 | 2009 | 2014 | |||||||||
雪岭云杉 Picea schrenkiana | 乔木 Tree | 11,731 | 10,962 | 92.88 | 92.51 | 13.16 | 14.25 | 1,010 | 241 | 1.03 | ||||
密叶杨 Populus talassica | 乔木 Tree | 5 | 5 | 0.42 | 0.41 | 9.20 | 10.88 | 0 | 0 | 1.68 | ||||
天山桦 Betula tianschanica | 乔木 Tree | 1 | 0 | 0.14 | 0.00 | 4.90 | 5.20 | 1 | 0 | - | ||||
天山花楸 Sorbus tianschanica | 乔木 Tree | 31 | 25 | 1.45 | 2.58 | 8.31 | 7.81 | 8 | 2 | 0.68 | ||||
小檗 Berberis heteropoda | 灌木 Shrub | 34 | 40 | 2.22 | 2.74 | 2.11 | 2.05 | 8 | 14 | 0.16 | ||||
忍冬 Lonicera hispida | 灌木 Shrub | 27 | 17 | 2.08 | 1.63 | 4.91 | 5.94 | 11 | 1 | 0.80 | ||||
栒子 Cotoneaster melanocarpus | 灌木 Shrub | 4 | 0 | 0.54 | 0.00 | 5.56 | 0.00 | 4 | 0 | - | ||||
蔷薇 Rosa spinosissima | 灌木 Shrub | 2 | 1 | 0.27 | 0.13 | 4.60 | 3.30 | 2 | 1 | - | ||||
合计 Total | 11,835 | 11,050 | 100 | 100 | 1,044 | 259 |
表1 2009和2014年天山雪岭云杉8 ha森林动态监测样地的群落动态
Table 1 Community dynamics in the 8-ha Picea schrenkiana forest dynamics plot in Tianshan Mountains in 2009 and 2014
物种 Species | 生长型 Growth form | 多度 Abundance | 重要值 Importance value (%) | 平均胸径 Mean DBH (cm) | 死亡数 Number of dead individual | 补员数 Number of recruited individual | 胸径净增长 DBH net growth (cm) | |||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
2009 | 2014 | 2009 | 2014 | 2009 | 2014 | |||||||||
雪岭云杉 Picea schrenkiana | 乔木 Tree | 11,731 | 10,962 | 92.88 | 92.51 | 13.16 | 14.25 | 1,010 | 241 | 1.03 | ||||
密叶杨 Populus talassica | 乔木 Tree | 5 | 5 | 0.42 | 0.41 | 9.20 | 10.88 | 0 | 0 | 1.68 | ||||
天山桦 Betula tianschanica | 乔木 Tree | 1 | 0 | 0.14 | 0.00 | 4.90 | 5.20 | 1 | 0 | - | ||||
天山花楸 Sorbus tianschanica | 乔木 Tree | 31 | 25 | 1.45 | 2.58 | 8.31 | 7.81 | 8 | 2 | 0.68 | ||||
小檗 Berberis heteropoda | 灌木 Shrub | 34 | 40 | 2.22 | 2.74 | 2.11 | 2.05 | 8 | 14 | 0.16 | ||||
忍冬 Lonicera hispida | 灌木 Shrub | 27 | 17 | 2.08 | 1.63 | 4.91 | 5.94 | 11 | 1 | 0.80 | ||||
栒子 Cotoneaster melanocarpus | 灌木 Shrub | 4 | 0 | 0.54 | 0.00 | 5.56 | 0.00 | 4 | 0 | - | ||||
蔷薇 Rosa spinosissima | 灌木 Shrub | 2 | 1 | 0.27 | 0.13 | 4.60 | 3.30 | 2 | 1 | - | ||||
合计 Total | 11,835 | 11,050 | 100 | 100 | 1,044 | 259 |
图2 天山雪岭云杉8 ha森林动态监测样地内不同龄级(径级)雪岭云杉的空间分布格局。(A)幼龄树(1 cm ≤ DBH ≤ 12.5 cm); (B)中龄树(12.5 cm < DBH ≤ 22.5 cm); (C)老龄树(DBH > 22.5 cm)。
Fig. 2 Spatial distribution patterns of Picea schrenkiana with different ages (DBH) in the 8-ha forest dynamics plot in Tianshan Mountains. (A) Young tree (1 cm ≤ DBH ≤ 12.5 cm); (B) Medium tree (12.5 cm < DBH ≤ 22.5 cm); (C) Mature tree (DBH > 22.5 cm).
图3 天山雪岭云杉8 ha森林动态监测样地内不同龄级(径级)雪岭云杉个体空间分布格局的尺度依赖性。(A)幼龄树(1 cm ≤ DBH ≤ 12.5 cm); (B)中龄树(12.5 cm < DBH ≤ 22.5 cm); (C)老龄树(DBH > 22.5 cm)。实线为99%置信区间的包迹线, 点线为实际点格局。
Fig. 3 Scale dependency of spatial patterns of Picea schrenkiana with different ages (DBH) in the 8-ha forest dynamics plot in Tianshan Mountains. (A) Young trees (1 cm ≤ DBH ≤ 12.5 cm); (B) Medium trees (12.5 cm < DBH ≤ 22.5 cm); (C) Mature trees (DBH > 22.5 cm). Solid lines show 99% simulation envelopes and solid lines with points represent the point pattern.
图4 天山雪岭云杉8 ha森林动态监测样地密度制约效应分析。(A)幼龄树(1 cm ≤ DBH ≤ 12.5 cm)作为案例, 老龄树(DBH > 22.5 cm)作为对照; (B)中龄树(12.5 cm < DBH ≤ 22.5 cm)作为案例, 老龄树作为对照; (C)从幼龄树到中龄树聚集格局的变化。实线为99%置信区间的包迹线, 点线为实际点的格局。
Fig. 4 Density-dependence analyses of the 8-ha Picea schrenkiana forest dynamics plot in Tianshan Mountains. (A) Young trees (1 cm ≤ DBH ≤ 12.5 cm) serve as case and mature trees (DBH > 22.5 cm) as control; (B) Medium trees (12.5 cm < DBH ≤ 22.5 cm) serve as case and mature trees as control; (C) The pattern changes from young trees to medium trees. Solid lines show 99% simulation envelopes and solid lines with points represents the point pattern.
图5 天山雪岭云杉8 ha森林动态监测样地内不同龄级(径级)雪岭云杉的空间关联性。(A)幼龄树(1 cm ≤ DBH ≤ 12.5 cm)与老龄树(DBH > 22.5 cm); (B)中龄树(12.5 cm < DBH ≤ 22.5 cm)与老龄树。实线为99%置信区间的包迹线, 点线为实际点的格局。
Fig. 5 Spatial association of Picea schrenkiana with different ages (DBH) in the 8-ha forest dynamics plot in Tianshan Mountains. (A) Young (1 cm ≤ DBH ≤ 12.5 cm) and mature (DBH > 22.5 cm) trees; (B) Medium (12.5 cm < DBH ≤ 22.5 cm) and mature trees. Solid lines show 99% simulation envelopes and solid lines with points represents the point pattern.
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