川西王朗亚高山暗针叶林25.2 hm2动态监测样地物种组成与群落结构特征

doi:10.17521/cjpe.2022.0094

植物生态学报 ›› 2022, Vol. 46 ›› Issue (9): 1005-1017.DOI: 10.17521/cjpe.2022.0094

所属专题：青藏高原植物生态学：植被生态学；青藏高原植物生态学：数据论文；植被生态学

川西王朗亚高山暗针叶林25.2 hm²动态监测样地物种组成与群落结构特征

樊凡¹^,², 赵联军³, 马添翼¹, 熊心雨²^,⁴, 张远彬⁵, 申小莉⁶^,^*(), 李晟¹^,²^,^*()

¹北京大学生命科学学院, 北京 100871
²北京大学生态研究中心, 北京 100871
³王朗国家级自然保护区, 四川平武 622550
⁴北京大学城市与环境学院, 北京 100871
⁵中国科学院成都山地灾害与环境研究所, 成都 610041
⁶中国科学院植物研究所植被与环境变化国家重点实验室, 北京 100093

收稿日期:2022-03-15 接受日期:2022-05-31 出版日期:2022-09-20 发布日期:2022-10-19
通讯作者: 申小莉,李晟
作者简介:李晟, shengli@pku.edu.cn)
* (申小莉, xlshen@ibcas.ac.cn;

Community composition and structure in a 25.2 hm² subalpine dark coniferous forest dynamics plot in Wanglang, Sichuan, China

FAN Fan¹^,², ZHAO Lian-Jun³, MA Tian-Yi¹, XIONG Xin-Yu²^,⁴, ZHANG Yuan-Bin⁵, SHEN Xiao-Li⁶^,^*(), LI Sheng¹^,²^,^*()

¹School of Life Sciences, Peking University, Beijing 100871, China
²Institute of Ecology, Peking University, Beijing 100871, China
³Wanglang National Nature Reserve, Pingwu, Sichuan 622550, China
⁴College of Urban and Environmental Sciences, Peking University, Beijing 100871, China
⁵Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041, China
⁶State Key Laboratory of Vegetation and Environmental Change, Institute of Botany, Chinese Academy of Sciences, Beijing 100093, China

Received:2022-03-15 Accepted:2022-05-31 Online:2022-09-20 Published:2022-10-19
Contact: SHEN Xiao-Li,LI Sheng

1. 附录I 王朗样地木本植物物种多度、胸高断面积及重要值.pdf(297KB)

摘要/Abstract

摘要：

川西亚高山暗针叶林是中国寒温性针叶林的重要代表。以云杉(Picea spp.)和冷杉(Abies spp.)为优势树种的暗针叶林是青藏高原东缘亚高山森林的主体, 也是我国长江上游重要的生态屏障。该研究基于川西王朗保护区亚高山暗针叶林25.2 hm²动态监测样地的首轮清查数据, 分析样地木本植物组成和群落结构特征。依照全球森林观测网络(ForestGEO)的标准技术规范, 建立面积为25.2 hm² (700 m × 360 m)的暗针叶林固定监测样地, 对胸径≥1 cm的木本植物进行挂牌标记、坐标定位、物种鉴定和检尺。主要结果有: 样地内共标记独立的木本植物个体56 574株, 分属15科27属46种, 其中针叶树4种, 常绿阔叶树6种, 落叶阔叶树36种; 每hm²个体数≤1的稀有种共13个, 占样地物种总数的28.26%, 占样地总个体数的0.16%。该群落以针叶树岷江冷杉(A. fargesii var. faxoniana, n = 9 440)和紫果云杉(P. purpurea, n = 1 645)为建群种和乔木层优势种, 重要值分别占总数的26.03%和10.69%, 其单位面积内的胸高断面积分别占总胸高断面积(37.87 m²·hm^-2)的55.22%和24.84%。落叶阔叶树个体数占比最多(78.48%), 其中紫萼山梅花(Philadelphus purpurascens)、红脉忍冬(Lonicera nervosa)、冷地卫矛(Euonymus frigidus)为灌木层主要优势种。常绿阔叶树个体仅268株, 均为杜鹃属(Rhododendron)植物。木本植物的径级组成具有典型老龄林特征。单株最大胸径出现在紫果云杉, 达到127.07 cm。紫果云杉平均单株胸高断面积(0.14 ± 0.18) m²显著高于岷江冷杉(0.056 ± 0.11) m²。所有标记个体的径级分布呈倒“J”形, 表明群落处于稳定和正常生长状态。点格局分析的结果表明5个优势种(重要值占比>5%)均呈聚集分布, 但随着空间尺度的增加, 物种聚集程度变小, 趋向于随机分布。该研究的结果为深入研究川西亚高山暗针叶林的多样性维持与更新机制和该类型森林生态系统的保护与管理提供了基础信息。

关键词: CForBio网络, 亚高山暗针叶林, 岷山, 物种组成, 群落结构, 点格局分析

Abstract:

Aims Subalpine dark coniferous forests are an important representative of the cold-temperate coniferous forests in China. Dark coniferous forests dominated by spruce (Piceaspp.) and fir (Abies spp.) are the main body of subalpine forests on the eastern edge of the Qingzang Plateau and an important ecological defense in the upper reaches of the Yangtze River in China. In this study, we examined the community composition and structure of such a dark coniferous forest based on the first census data of the 25.2 hm² Wanglang forest dynamics plot in western Sichuan.

Methods The plot was established following the standard protocol of Forest Global Earth Observation Network (ForestGEO) and all free-standing stems with diameter at breast height (DBH) ≥ 1 cm were tagged, mapped, measured and identified to species.

Important findings A total of 56 574 individuals belonging to 46 species, 27 genera and 15 families are tagged, including 4 coniferous species, 6 evergreen broad-leaved species and 36 deciduous broad-leaved species. There are 13 rare species (≤1 individuals per hm²), accounting for 28.26% of the total number of species and 0.16% of the total number of individuals in the plot. Abies fargesiivar. faxoniana(9 440 individuals) and P. purpurea (1 645 individuals) are the dominant and constructive species in canopy, accounting for 26.03% and 10.69% of the total importance value, and 55.22% and 24.84% of the total basal area (37.87 m²·hm^-2), respectively. The number of individuals of deciduous broad-leaved species accounted for 78.48% of the total individuals. Among them, Philadelphus purpurascens, Lonicera nervosaand Euonymus frigidusare the dominant species in shrub layer. The number of individuals of evergreen broad-leaved species is 268, and all these species belong to genus Rhododendron. The composition of the size distribution shows typical characteristics of old-growth forests. Picea purpurea is the largest tree species (max DBH = 127.07 cm) and the mean basal area (0.14 ± 0.18) m² is much higher than that of A. fargesiivar. faxoniana(0.056 ± 0.11) m². The size class distribution of all woody species shows an inverse J-shaped distribution, indicating that the community is in a stable and healthy recruitment state. Results of the point pattern analysis reveal that the five dominant tree species (important values ≥5) all show aggregated distribution patterns. However, as the spatial scale increases, all five species tend to be randomly distributed. The results of this study provide basic information for future studies on the diversity maintenance and regeneration mechanisms of subalpine dark coniferous forests in western Sichuan, and the conservation and management of this unique forest ecosystem.

Key words: CForBio network, subalpine dark coniferous forest, Minshan Mountains, species composition, community structure, point pattern analysis

樊凡, 赵联军, 马添翼, 熊心雨, 张远彬, 申小莉, 李晟. 川西王朗亚高山暗针叶林25.2 hm²动态监测样地物种组成与群落结构特征. 植物生态学报, 2022, 46(9): 1005-1017. DOI: 10.17521/cjpe.2022.0094

FAN Fan, ZHAO Lian-Jun, MA Tian-Yi, XIONG Xin-Yu, ZHANG Yuan-Bin, SHEN Xiao-Li, LI Sheng. Community composition and structure in a 25.2 hm² subalpine dark coniferous forest dynamics plot in Wanglang, Sichuan, China. Chinese Journal of Plant Ecology, 2022, 46(9): 1005-1017. DOI: 10.17521/cjpe.2022.0094

导出引用管理器 EndNote|Ris|BibTeX

链接本文: https://www.plant-ecology.com/CN/10.17521/cjpe.2022.0094

https://www.plant-ecology.com/CN/Y2022/V46/I9/1005

图/表 7

图1 王朗样地位置图。

Fig. 1 Location of Wanglang plot. AM, alpine meadow; BR, bare rock; CBF, conifer broad-leaved mixed forest; CF, conifer forest; DF, deciduous broad-leaved forest; ND, no data; SL, shrubland.

图2 王朗样地海拔(A)和挂牌木本植物(B)分布图。由于林下竹丛过于密集, 导致工作人员在进行背包雷达扫描时无法直立行走, 因此样地边缘存在部分海拔空白值。B用大小一致的黑点标记已挂牌木本植株。

Fig. 2 Altitude (A) and distribution of all tagged individual woody plants (B) in Wanglang plot. Blank values in A are due to the inaccessibility caused by the dense bamboo understory during the backpack radar scanning. Each dot represents an individual tagged woody plant in B.

表1 王朗25.2hm2森林动态监测样地与其他7个不同纬度、不同植被类型样地特征的比较

Table 1 Comparison of the major characteristics of Wanglang 25.2hm2 forest dynamics plot with seven other plots of different latitudes and vegetation types

图3 王朗样地木本植物物种累积曲线(20 m × 20 m样方总数= 630)。灰色区域表示95%置信区间。

Fig. 3 Species accumulation curve of woody plants in Wanglang plot (20 m × 20 m quadrat number = 630)。Grey shadow areas represent the 95% confidence intervals.

图4 王朗样地内所有挂牌木本植物、针叶乔木、落叶乔木及灌木/藤本物种的径级分布。

Fig. 4 Diameter at breast height (DBH) distributions of all tagged woody plants, coniferous trees, deciduous trees, and shrubs and vines in Wanglang plot.

图5 王朗样地内重要值排序前5位木本植物的径级分布。

Fig. 5 Diameter at breast height (DBH) distributions of the top five woody species according to the rank of important value in Wanglang plot.

图6 王朗样地5种优势木本植物的空间分布和点格局分析。A1-E1, 各优势种的空间分布。A2-E2, 与完全空间随机分布模型对比的G函数分析结果。gobs(r), 观测值; gtheo(r), 理论值; 灰色区域为95%置信区间。

Fig. 6 Spatial distributions and the results of point pattern analysis of the five dominant woody species in Wanglang plot. A1-E1, Spatial distributions of individual woody plants. A2-E2, Results of G-function analysis compared with complete spatial random distribution model. gobs(r), observed value; gtheo(r), theoretical values from simulated null model; grey area is 95% confidence interval.

参考文献 55

[1]	Baddeley A, Rubak E, Turner R (2015). Spatial Point Patterns: Methodology and Applications with R. CRC Press, Boca Raton.
[2]	Binder K, Heermann D, Roelofs L, Mallinckrodt AJ, McKay S (1993). Monte Carlo simulation in statistical physics. Computers in Physics, 7, 156-157. DOI URL
[3]	Chen GP, Xian JR, Yu XY (2021). Effect of forest gap on accumulations and allocations of root biomass in Abies faxoniana regeneration seedlings. Acta Ecologica Sinica, 41, 5685-5694.
	[陈国鹏, 鲜骏仁, 俞筱押 (2021). 林窗对岷江冷杉更新幼苗根系生物量积累与分配的影响. 生态学报, 41, 5685-5694.]
[4]	Condit R (1995). Research in large, long-term tropical forest plots. Trends in Ecology & Evolution, 10, 18-22. DOI URL
[5]	Condit R (1998). Tropical Forest Census Plots: Methods and Results from Barro Colorado Island, Panama and a Comparison with Other Plots. Springer Science & Business Media, New York.
[6]	Condit R, Ashton PS, Baker P, Bunyavejchewin S, Gunatilleke S, Gunatilleke N, Hubbell SP, Foster RB, Itoh A, LaFrankie JV, Lee HS, Losos E, Manokaran N, Sukumar R, Yamakura T (2000). Spatial patterns in the distribution of tropical tree species. Science, 288, 1414-1418. DOI URL
[7]	Davies SJ, Abiem I, Salim KA, Aguilar S, Allen D, Alonso A, Anderson-Teixeira K, Andrade AC, Arellano G, Ashton PS, Baker PJ, Baker ME, Baltzer JL, Basset Y, Bissiengou P, et al. (2021). ForestGEO: understanding forest diversity and dynamics through a global observatory network. Biological Conservation, 253, 108907. DOI: 10.1016/j.biocon.2020.108907. DOI
[8]	Getzin S, Wiegand T, Wiegand K, He FL (2008). Heterogeneity influences spatial patterns and demographics in forest stands. Journal of Ecology, 96, 807-820. DOI URL
[9]	Gotelli NJ, Colwell RK (2001). Quantifying biodiversity: procedures and pitfalls in the measurement and comparison of species richness. Ecology Letters, 4, 379-391. DOI URL
[10]	Greig-Smith P (1983). Quantitative Plant Ecology: Vol. 9. University of California Press , Oakland, USA.
[11]	Han JJ, Xiao WF, Luo JC (2000). Effects of different cutting methods on regeneration and habitat for spruce-fir forests. Scientia Silvae Sinicae, 36(Sp.1), 90-96.
	[韩景军, 肖文发, 罗菊春 (2000). 不同采伐方式对云冷杉林更新与生境的影响. 林业科学, 36(专刊1), 90-96.]
[12]	Hao ZQ, Li BH, Zhang J, Wang XG, Ye J, Yao XL (2008). Broad-leaved Korean pine (Pinus koraiensis) mixed forest plot in Changbaishan (CBS) of China: community composition and structure. Journal of Plant Ecology (Chinese Version), 32, 238-250.
	[郝占庆, 李步杭, 张健, 王绪高, 叶吉, 姚晓琳 (2008). 长白山阔叶红松林样地(CBS): 群落组成与结构. 植物生态学报, 32, 238-250.] DOI
[13]	He FL, Legendre P, LaFrankie JV (1997). Distribution patterns of tree species in a Malaysian tropical rain forest. Journal of Vegetation Science, 8, 105-114. DOI URL
[14]	Holt RD, Grover J, Tilman D (1994). Simple rules for interspecific dominance in systems with exploitative and apparent competition. The American Naturalist, 144, 741-771. DOI URL
[15]	Hu YH, Sha LQ, Blanchet FG, Zhang JL, Tang Y, Lan GY, Cao M (2012). Dominant species and dispersal limitation regulate tree species distributions in a 20-ha plot in Xishuangbanna, Southwest China. Oikos, 121, 952-960. DOI URL
[16]	Huang H, Chen ZF, Liu DT, He GX, He RH, Li DZ, Xu K (2017). Species composition and community structure of the Yulongxueshan (Jade Dragon Snow Mountains) forest dynamics plot in the cold temperate spruce-fir forest, Southwest China. Biodiversity Science, 25, 255-264. DOI
	[黄华, 陈智发, 刘德团, 和国星, 和荣华, 李德铢, 许琨 (2017). 玉龙雪山寒温性云冷杉林动态监测样地的物种组成及群落结构. 生物多样性, 25, 255-264.] DOI
[17]	Hubbell SP, Foster RB (1986). Commonness and Rarity in a Neotropical Forest, Implications for Tropical Trees Conservation. Sinauer, Saunderland, UK.
[18]	Janzen DH (1970). Herbivores and the number of tree species in tropical forests. The American Naturalist, 104, 501-528. DOI URL
[19]	Jiang YX (1963). Community characteristics and their classification principles of subalpine dark coniferous forest in western Sichuan. Acta Phytoecologica et Geobotanica Sinica, 1, 42-50.
	[蒋有绪 (1963). 川西亚高山暗针叶林的群落特点及其分类原则. 植物生态学与地植物学丛刊, 1, 42-50.]
[20]	Jiang YX, Guo QS, Ma J (1998). Taxonomy and Community Characteristics of Forest Communities in China. Science Press, Beijing.
	[蒋有绪, 郭泉水, 马娟 (1998). 中国森林群落分类及其群落学特征. 科学出版社, 北京.]
[21]	Kang DW, Liu XM, Tan LY, Kang W (2010). Population structure of Abies faxoniana in Wanglang Nature Reserve, Sichuan. Journal of Hebei Forestry Science, (3), 15-17.
	[康东伟, 刘夏明, 谭留夷, 康文 (2010). 四川省王朗自然保护区岷江冷杉种群结构特征研究. 河北林业科技, (3), 15-17.]
[22]	Kang YY, Li RS, Gao YL (2015). Spatial pattern of dominant and main companion tree species in an Abies faxoniana forest in Wanglang Nature Reserve. Journal of West China Forestry Science, 44(2), 48-53.
	[康瑶瑶, 李瑞生, 高永龙 (2015). 王朗自然保护区岷江冷杉林优势种与主要伴生种的空间格局. 西部林业科学, 44(2), 48-53.]
[23]	Laura ED, Jane C, Forest I, Stephanie P, Steven DG, Peter BR (2019). When do ecosystem services depend on rare species? Trends in Ecology & Evolution, 34, 746-758. DOI URL
[24]	Larson AJ, Franklin JF (2010). The tree mortality regime in temperate old-growth coniferous forests: the role of physical damage. Canadian Journal of Forest Research, 40, 2091-2103. DOI URL
[25]	Li CB (1990). Forest Ecology Research in Sichuan. Sichuan Science and Technology Press, Chengdu.
	[李承彪 (1990). 四川森林生态研究. 四川科技出版社, 成都.]
[26]	Li SZ (2018). History of Wanglang: Wanglang National Nature Reserve in Sichuan (1965-2015). Sichuan Science and Technology Press, Chengdu.
	[李晟之 (2018). 王朗志: 四川王朗国家级自然保护区志(1965-2015). 四川科学技术出版社, 成都.]
[27]	Liu HF, Li L, Sang WG (2011). Species composition and community structure of the Donglingshan forest dynamic plot in a warm temperate deciduous broad-leaved secondary forest, China. Biodiversity Science, 19, 232-242. DOI
	[刘海丰, 李亮, 桑卫国 (2011). 东灵山暖温带落叶阔叶次生林动态监测样地: 物种组成与群落结构. 生物多样性, 19, 232-242.] DOI
[28]	Lutz JA, Larson AJ, Freund JA, Swanson ME, Bible KJ (2013). The importance of large-diameter trees to forest structural heterogeneity. PLOS ONE, 8, e82784. DOI: 10.1371/journal.pone.0082784. DOI
[29]	Lutz JA, Larson AJ, Swanson ME, Freund JA (2012). Ecological importance of large-diameter trees in a temperate mixed- conifer forest. PLOS ONE, 7, e36131. DOI: 10.1371/journal.pone.0036131. DOI
[30]	Lyons KG, Brigham CA, Traut BH, Schwartz MW (2005). Rare species and ecosystem functioning. Conservation Biology, 19, 1019-1024. DOI URL
[31]	Ma KP (2015). Biodiversity monitoring in China: from CForBio to Sino BON. Biodiversity Science, 23, 1-2. DOI
	[马克平 (2015). 中国生物多样性监测网络建设: 从CForBio到Sino BON. 生物多样性, 23, 1-2.] DOI
[32]	Ma KP (2017). Forest dynamics plot is a crosscutting research platform for biodiversity science. Biodiversity Science, 25, 227-228. DOI
	[马克平 (2017). 森林动态大样地是生物多样性科学综合研究平台. 生物多样性, 25, 227-228.] DOI
[33]	Marsh AS, Arnone III JA, Bormann BT, Gordon JC (2000). The role of Equisetum in nutrient cycling in an Alaskan shrub wetland. Journal of Ecology, 88, 999-1011. DOI URL
[34]	Mi XC, Swenson NG, Valencia R, Kress WJ, Erickson DL, Pérez ÁJ, Ren HB, Su SH, Gunatilleke N, Gunatilleke S, Hao ZQ, Ye WH, Cao M, Suresh HS, Dattaraja HS, et al. (2012). The contribution of rare species to community phylogenetic diversity across a global network of forest plots. The American Naturalist, 180, E17-E30.
[35]	Potapov P, Hansen MC, Laestadius L, Turubanova S, Yaroshenko A, Thies C, Smith W, Zhuravleva I, Komarova A, Minnemeyer S, Esipova E (2017). The last frontiers of wilderness: tracking loss of intact forest landscapes from 2000 to 2013. Science Advances, 3, e1600821. DOI: 10.1126/sciadv.1600821. DOI
[36]	Qin YZ, Zhang JX, Liu JM, Liu MT, Wan D, Wu H, Zhou Y, Meng HJ, Xiao ZQ, Huang HD, Xu YZ, Lu ZJ, Qiao XJ, Jiang MX (2018). Community composition and spatial structure in the Badagongshan 25 ha Forest Dynamics Plot in Hunan Province. Biodiversity Science, 26, 1016-1022. DOI
	[秦运芝, 张佳鑫, 刘检明, 刘梦婷, 万丹, 吴浩, 周阳, 孟红杰, 肖之强, 黄汉东, 徐耀粘, 卢志军, 乔秀娟, 江明喜 (2018). 湖南八大公山25 ha常绿落叶阔叶混交林动态监测样地群落组成与空间结构. 生物多样性, 26, 1016-1022.] DOI
[37]	Shen GZ, Li JQ, Jiang SW (2004). Structure and dynamics of subalpine forests in giant panda habitat. Acta Ecologica Sinica, 24, 1294-1299.
	[申国珍, 李俊清, 蒋仕伟 (2004). 大熊猫栖息地亚高山针叶林结构和动态特征. 生态学报, 24, 1294-1299.]
[38]	Shen GZ, Li JQ, Ren YL, Ma YF (2002). Disturbances and subalpine forest structure in giant panda’s habitat. Journal of Beijing Forestry University, 24(5), 115-119.
	[申国珍, 李俊清, 任艳林, 马宇飞 (2002). 大熊猫栖息地亚高山针叶林结构和干扰关系研究. 北京林业大学学报, 24(5), 115-119.]
[39]	Shen L, Yang H, Kang XG, Yue G (2013). Effects of selective cutting intensity on spatial distribution pattern of natural spruce-fir forests. Journal of Central South University of Forestry & Technology, 33(1), 68-74.
	[沈林, 杨华, 亢新刚, 岳刚 (2013). 择伐强度对天然云冷杉林空间分布格局的影响. 中南林业科技大学学报, (1), 68-74.]
[40]	Stoyan D, Stoyan H (1994). Fractals, Random Shapes and Point Fields: Methods of Geometrical Statistics. Wiley-Blackwell, Hoboken, USA.
[41]	Tan LY, Zhao ZJ, Kang DW, Kang W, Li JQ (2011). A study on the relationship between the radial growth of Picea purpuea and the climatic factors in Wanglang National Nature Reserve. Journal of Sichuan Agricultural University, 29, 29-34.
	[谭留夷, 赵志江, 康东伟, 康文, 李俊清 (2011). 王朗自然保护区紫果云杉径向生长与气候因子的关系. 四川农业大学学报, 29, 29-34.]
[42]	Taylor AH, Huang JY, Zhou SQ (2004). Canopy tree development and undergrowth bamboo dynamics in old-growth Abies- Betula forests in southwestern China: a 12-year study. Forest Ecology and Management, 200, 347-360. DOI URL
[43]	Taylor AH, Jiang SW, Zhao LJ, Liang CP, Miao CJ, Huang JY (2006). Regeneration patterns and tree species coexistence in old-growth Abies-Picea forests in southwestern China. Forest Ecology and Management, 223, 303-317. DOI URL
[44]	Taylor AH, Qin ZS (1992). Tree regeneration after bamboo die-back in Chinese Abies-Betula forests. Journal of Vegetation Science, 3, 253-260. DOI URL
[45]	The Editorial Committee of Vegetation of China (1980). Vegetation of China. Science Press, Beijing.
	[中国植被编辑委员会 (1980). 中国植被. 科学出版社, 北京.]
[46]	Wang YJ, Tao JP, Li Y, Yu XH, Xi Y (2007). Effects of Fargesia nitida on species diversity and trees regeneration in different forest cycles of subalpine forest in Wolong Nature Reserve. Scientia Silvae Sinicae, 43(2), 1-7.
	[王永健, 陶建平, 李媛, 余小红, 席一 (2007). 华西箭竹对卧龙亚高山森林不同演替阶段物种多样性与乔木更新的影响. 林业科学, 43(2), 1-7.]
[47]	Wu ZY, Zhou ZK, Li DZ, Peng H, Sun H (2003). The areal-types of the world families of seed plants. Acta Botanica Yunnanica, 25, 245-257.
	[吴征镒, 周浙昆, 李德铢, 彭华, 孙航 (2003). 世界种子植物科的分布区类型系统. 云南植物研究, 25, 245-257.]
[48]	Xie FL, Zhou Q, Shi H, Shu X, Zhang KR, Li T, Feng SY, Zhang QF, Dang HS (2019). Species composition and community characteristics of a 25 ha forest dynamics plot in deciduous broad-leaved forest, Qinling Mountains, north-central China. Biodiversity Science, 27, 439-448. DOI
	[谢峰淋, 周全, 史航, 舒枭, 张克荣, 李涛, 冯水园, 张全发, 党海山 (2019). 秦岭落叶阔叶林25 ha森林动态监测样地物种组成与群落特征. 生物多样性, 27, 439-448.] DOI
[49]	Ye WH, Cao HL, Huang ZL, Lian JY, Wang ZG, Li L, Wei SG, Wang ZM (2008). Community structure of a 20 hm² lower subtropical evergreen broadleaved forest plot in Dinghushan, China. Journal of Plant Ecology (Chinese Version), 32, 274-286.
	[叶万辉, 曹洪麟, 黄忠良, 练琚愉, 王志高, 李林, 魏识广, 王章明 (2008). 鼎湖山南亚热带常绿阔叶林20公顷样地群落特征研究. 植物生态学报, 32, 274-286.] DOI
[50]	Yuan RJ, Wang BR, Yang SH (2007). Comparative study on Picea and Abies in Hengduan mountainous areas. Journal of West China Forestry Science, 36(1), 16-21.
	[袁睿佳, 王宝荣, 杨树华 (2007). 横断山区云杉林与冷杉林的对比研究. 西部林业科学, 36(1), 16-21.]
[51]	Zeng XW, Yu B, Wu J, Hong Y, Da L, Yang H (2014). Analysis of structure characteristics of main tree species in spruce-fir overcutting forest. Forest Research, 27, 481-486.
	[曾祥谓, 玉宝, 乌吉斯古楞, 红玉, 达楞巴雅尔, 杨浩 (2014). 云冷杉过伐林主要树种结构特征分析. 林业科学研究, 27, 481-486.]
[52]	Zhan XJ, Li M, Zhang ZJ, Goossens B, Chen YP, Wang HJ, Bruford MW, Wei FW (2006). Molecular censusing doubles giant panda population estimate in a key nature reserve. Current Biology, 16, 451-452. PMID
[53]	Zhao CM, Chen QH, Qiao YK, Pan KW (2004). Structure and spatial pattern of a natural Abies faxoniana population on the eastern edge of Qinghai-Tibetan Plateau. Acta Phytoecologica Sinica, 28, 341-350.
	[赵常明, 陈庆恒, 乔永康, 潘开文 (2004). 青藏高原东缘岷江冷杉天然群落的种群结构和空间分布格局. 植物生态学报, 28, 341-350.] DOI
[54]	Zhou ML, Zhang Q, Kang XG, Yang YJ, Wang QJ (2016). Dynamic response to selective cutting intensity on tree species structure and species diversity in a natural spruce-fir forest. Plant Science Journal, 34, 56-66.
	[周梦丽, 张青, 亢新刚, 杨英军, 王全军 (2016). 云冷杉天然林乔木树种组成及物种多样性对择伐强度的动态响应. 植物科学学报, 34, 56-66.]
[55]	Zhu Y, Zhao GF, Zhang LW, Shen GC, Mi XC, Ren HB, Yu MJ, Chen JH, Chen SW, Fang T, Ma KP (2008). Community composition and structure of Gutianshan forest dynamic plot in a mid-subtropical evergreen broad-leaved forest, East China. Journal of Plant Ecology (Chinese Version), 32, 262-273.
	[祝燕, 赵谷风, 张俪文, 沈国春, 米湘成, 任海保, 于明坚, 陈建华, 陈声文, 方腾, 马克平 (2008). 古田山中亚热带常绿阔叶林动态监测样地——群落组成与结构. 植物生态学报, 32, 262-273.] DOI

川西王朗亚高山暗针叶林25.2 hm²动态监测样地物种组成与群落结构特征

Community composition and structure in a 25.2 hm² subalpine dark coniferous forest dynamics plot in Wanglang, Sichuan, China

全文

PDF (PC)

附录附件

可视化

摘要/Abstract

引用本文

使用本文

图/表 7

参考文献 55

相关文章 15

编辑推荐

Metrics

本文评价

[1]	刘瑶钟全林徐朝斌程栋梁郑跃芳邹宇星张雪郑新杰周云若. 不同大小刨花楠细根功能性状与根际微环境关系[J]. 植物生态学报, 2024, 48(预发表): 0-0.
[2]	董劭琼, 侯东杰, 曲孝云, 郭柯. 柴达木盆地植物群落样方数据集[J]. 植物生态学报, 2024, 48(4): 534-540.
[3]	薛志方, 刘彤, 王立生, 宋继虎, 陈宏阳, 徐玲, 袁也. 额尔齐斯河流域主要支流平原河谷林群落结构及特征[J]. 植物生态学报, 2024, 48(3): 390-402.
[4]	肖兰, 董标, 张琳婷, 邓传远, 李霞, 姜德刚, 林勇明. 渤海无居民海岛主要植被类型群落特征[J]. 植物生态学报, 2024, 48(1): 127-134.
[5]	王雨婷, 刘旭婧, 唐驰飞, 陈玮钰, 王美娟, 向松竹, 刘梅, 杨林森, 傅强, 晏召贵, 孟红杰. 神农架极小种群植物庙台槭群落特征及种群动态[J]. 植物生态学报, 2024, 48(1): 80-91.
[6]	任悦, 高广磊, 丁国栋, 张英, 赵珮杉, 柳叶. 不同生长期樟子松外生菌根真菌群落物种组成及其驱动因素[J]. 植物生态学报, 2023, 47(9): 1298-1309.
[7]	冯可, 刘冬梅, 张琦, 安菁, 何双辉. 旅游干扰对松山油松林土壤微生物多样性及群落结构的影响[J]. 植物生态学报, 2023, 47(4): 584-596.
[8]	席念勋, 张原野, 周淑荣. 群落生态学中的植物-土壤反馈研究[J]. 植物生态学报, 2023, 47(2): 170-182.
[9]	赵长兴, 赵维俊, 张兴林, 刘思敏, 牟文博, 刘金荣. 祁连山排露沟流域青海云杉种群种内竞争与促进作用分析[J]. 植物生态学报, 2022, 46(9): 1027-1037.
[10]	王姝文, 李文怀, 李艳龙, 严慧, 李永宏. 放牧家畜类型对内蒙古典型草原植物多样性和群落结构的影响[J]. 植物生态学报, 2022, 46(8): 941-950.
[11]	冯继广, 张秋芳, 袁霞, 朱彪. 氮磷添加对土壤有机碳的影响: 进展与展望[J]. 植物生态学报, 2022, 46(8): 855-870.
[12]	金伊丽, 王皓言, 魏临风, 侯颖, 胡景, 吴铠, 夏昊钧, 夏洁, 周伯睿, 李凯, 倪健. 青藏高原植物群落样方数据集[J]. 植物生态学报, 2022, 46(7): 846-854.
[13]	余秋伍, 杨菁, 沈国春. 浙江天童常绿阔叶林林冠结构与群落物种组成的关系[J]. 植物生态学报, 2022, 46(5): 529-538.
[14]	谢育杭, 贾璞, 郑修坛, 李金天, 束文圣, 王宇涛. 驯化对作物微生物组多样性和群落结构的影响及作用途径[J]. 植物生态学报, 2022, 46(3): 249-266.
[15]	周亮, 杨君珑, 杨虎, 窦建德, 黄维, 李小伟. 宁夏蒙古扁桃群落特征与分类[J]. 植物生态学报, 2022, 46(2): 243-248.