Interspecific relationship and canonical correspondence analysis within woody plant communities in the karst mountains of Southwest Guangxi, southern China
-
摘要: 基于桂西南喀斯特山地木本植物群落11个样方(20 m×20 m)取样调查，运用生态位理论、种间关系原理、双向指示种分析(TWINSPAN)和典范对应分析(CCA)方法，探讨主要木本植物间的种间联结性和相关性及其与环境因子之间的关系。结果表明：桂西南喀斯特山地木本植物群落中麻栎、枫香、蚬木占优势地位，罗伞树-鹅掌柴、九节-琴叶榕、澄广花-鱼骨木的生态位重叠度分别在3种木本植物群落中最大。麻栎次生林群落总体种间关系表现为不显著正关联，χ2检验统计显示正关联种对数有50对，负关联种对数有52对，无关联种对数有3对，正负关联比为0.96，检验显著率为6.67%。枫香次生林群落总体种间关系表现为不显著负关联，χ2检验统计显示正关联种对数有96对，负关联种对数有113对，无关联种对数有1对，正负关联比为0.85，检验显著率为8.10%。蚬木次生林群落总体种间关系表现为显著正关联，正关联种对数有19对，负关联种对数有17对，正负关联比为1.12，检验显著率为8.33%。CCA前瞻选择显示土壤pH值、全磷、坡向、土壤全钾、海拔是影响桂西南喀斯特山地木本植物群落物种组成与分布最重要的因子，总体上可以对76.95%的环境因子进行解释。物种间的正联结性越显著，其生态位重叠程度越高，反之，物种间的负联结性越显著，其生态位重叠程度则越低。
-
关键词:
- 喀斯特 /
- 生态位 /
- 种间联结性 /
- 双向指示种分析(TWINSPAN) /
- 典范对应分析(CCA)
Abstract: The interspectific associations of main woody plant species and the relationships between environmental factors and plant communities were investigated in the karst mountains of Southwest Guangxi, southern China. Eleven sampling plots (20 m×20 m in size each) were established in three forest communities (Quercus acutissima forest, Liquidambar formosana forest, and Excentrodendron hsienmu forest) in the study site, and statistic methods including niche theory, interspecific relation principle, two-way indicator species analysis and canonical correspondence analysis were used. The results showed that Quercus acutissima, Liquidambar formosana, and Excentrodendron hsienmu were dominant species in the study area. The largest niche overlap was observed between Ardisia quinquegona and Schefflera octophylla, between Psychotria rubra and Ficus pandurata, and between Orophea hainanensis and Canthium dicoccum for the Quercus acutissima natural secondary forest, Liquidambar formosana natural secondary forest and Excentrodendron hsienmu natural secondary forest, respectively. No significant positive correlations were found in terms of the overall interspecific associations among dominant woody plant species in Quercus acutissima natural secondary forest. The χ2 test showed that the number of species pairs in positive association was 50, the number of species pairs in negative association was 52, and the number of species pairs in non-association was 3, the association ratio was 0.96, and the significance rate of test was 6.67%. The overall interspecific associations were negative correlations among dominant woody plant species in Liquidambar formosana natural secondary forest, but the correlations were not significant. The χ2 test showed that the number of species pairs in positive association was 96, the number of species pairs in negative association was 113, the number of species pairs in non-association was 1, the association ratio was 0.85, and the significance rate of test was 8.10%. The overall interspecific associations were significantly positive correlations among dominant woody plant species in Excentrodendron hsienmu natural secondary forests. The χ2 test showed that the number of species pairs in positive association was 19, the number of species pairs in negative association was 17, the association ratio was 1.12, and the significance rate of test was 8.33%. By CCA analysis, soil pH, total phosphorus, slope aspect, soil total potassium and elevation were the most important factors affecting species composition and distribution in plant communities in the study area, which accounted for about 76.95% of the variation. Our study indicates that the more significantly positive the associations between plant species are, the higher the degree of niche overlap is. In contrast, the more significantly negative the associations between plant species are, the lower the degree of niche overlap is. -
-
![]()
图 1 桂西南喀斯特山地木本植物群落11个样方的TWINSPAN分类树状图
Figure 1. Dendrogram of the TWINSPAN classification of 11 plots within woody plant communities in the karst mountains of Southwest Guangxi
![]()
图 2 麻栎次生林主要木本植物种间联结性半矩阵图
△0.5≤AC; □0.1≤AC＜0.5;○-0.1≤AC＜0.1;☆-0.5≤AC＜-0.1;◇AC＜-0.5;AC为联结系数。+正关联; -负关联; ★极显著正关联; ◆极显著负关联; ■显著正关联; ▼显著负关联; ●无关联。下同。种号同表 2。
Figure 2. Semi-matrix of interspecific association for dominant woody plants in the Quercus acutissima natural secondary forest
AC is association coefficient; + Positive correlation; -Negative correlation; ★Positive correlation with extreme significance; ◆ Negative correlation with extreme significance; ■Significantly positive correlation; ▼Significantly negative correlation; ●Non-correlation. The same below. Species No. was the same as Tab. 2.
![]()
![]()
![]()
图 5 物种和环境因子的典范对应分析(CCA)排序
图中物种序号同表 1。Elv.海拔; Slo.坡度; Asp.坡向; Pos.坡位; pH. pH值; SOM.土壤有机质; TN.全氮; TP.全磷; TK.全钾。
Figure 5. Canonical correspondence analysis(CCA)ordination diagram of species and environmental factors
Species were the same as Tab. 1. Elv, elevation; Slo, slope degree; Asp, slope aspect; Pos, slope postion; pH, pH value; SOM, soil organic matter; TN, total nitrogen; TP, total phosphorus; TK, total potassium.
表 1 43种木本植物
Table 1 43 kinds of woody plants
编号No. 物种名Species S1 猴耳环Pithecellobium clypearia S2 山茶Camellia japonica S3 麻栎Quercus acutissima S4 广西密花树Rapanea kwangsiensis S5 黄杞Engelhardtia roxburghiana S6 亮叶猴耳环Archidendron lucidum S7 罗伞树Ardisia quinquegona S8 鹅掌柴Schefflera octophylla S9 水锦树Wendlandia uvariifolia S10 银柴Aporosa dioica S11 九节Psychotria rubra S12 龙眼Dimocarpus longan S13 枫香Liquidambar formosana S14 毛果算盘子Glochidion eriocarpum S15 粗叶榕Ficus hirta S16 艾胶算盘子Glochidion lanceolarium S17 苎麻Boehmeria nivea S18 烟斗柯Lithocarpus corneus S19 杜茎山Maesa japonica S20 粗糠柴Mallotus philippensis S21 西南木荷Schima wallichii S22 南方荚蒾Viburnum fordiae S23 水东哥Saurauia tristyla S24 灰毛浆果楝Cipadessa cinerascens S25 扁担杆Grewia biloba S26 孱槁树Litsea glutinosa S27 黄皮Clausena lansium S28 三叉苦Evodia lepta S29 化香树Platycarya strobilacea S30 琴叶榕Ficus pandurata S31 蚬木Excentrodendron hsienmu S32 榔榆Ulmus parvifolia S33 黄牛木Cratoxylum cochinchinense S34 岩柿Diospyros dumetorum S35 鱼骨木Canthium dicoccum S36 澄广花Orophea hainanensis S37 九里香Murraya exotica S38 菜豆树Radermachera sinica S39 山黄皮Clausena excavata S40 山石榴Catunaregam spinosa S41 扣匹Uvaria tonkinensis S42 海南大风子Hydnocarpus hainanensis S43 三角榄Canarium bengalense 
下载: 导出CSV
表 2 麻栎次生林主要木本植物的重要值及生态位宽度
Table 2 Importance value and niche breadth of dominant woody plants in the Quercus acutissima natural secondary forests
排序
Rank物种
Species重要值
Importance value(Ⅳ)生态位宽度
Niche breadth(Bi)1 麻栎Quercus acutissima 19.26 0.940 2 黄杞
Engelhardtia roxburghiana15.44 0.844 3 罗伞树
Ardisia quinquegona14.19 0.917 4 猴耳环
Pithecellobium clypearia9.48 0.702 5 水锦树
Wendlandia uvariifolia8.61 0.944 6 鹅掌柴
Schefflera octophylla7.98 0.888 7 亮叶猴耳环
Archidendron lucidum5.85 0.425 8 广西密花树
Rapanea kwangsiensis3.52 0.859 9 毛果算盘子
Glochidion eriocarpum2.63 0.812 10 九节
Psychotria rubra2.56 0.886 11 烟斗柯
Lithocarpus corneus1.99 0.376 12 山茶
Camellia japonica1.52 0.400 13 枫香
Liquidambar formosana1.50 0.613 14 粗叶榕
Ficus hirta1.43 0.915 15 银柴
Aporosa dioica1.32 0.725
下载: 导出CSV
表 3 枫香次生林主要木本植物的重要值及生态位宽度
Table 3 Importance value and niche breadth of dominant woody plants in the Liquidambar formosana natural secondary forest
排序
Rank物种
Species重要值
Importance value(Ⅳ)生态位宽度
Niche breadth(Bi)1 枫香Liquidambar formosana 26.67 0.839 2 鹅掌柴Schefflera octophylla 12.07 0.440 3 罗伞树Ardisia quinquegona 10.70 0.557 4 灰毛浆果楝
Cipadessa cinerascens9.85 0.878 5 杜茎山Maesa japonica 5.37 0.866 6 西南木荷
Schimawallichii Choisy3.95 0.539 7 菜豆树Radermachera sinica 3.69 0.287 8 粗糠柴Mallotus philippensis 3.08 0.559 9 黄皮Clausena lansium 2.73 0.594 10 艾胶算盘子
Glochidion lanceolarium2.00 0.459 11 九里香Murraya exotica 1.75 0.400 12 九节Psychotria rubra 1.59 0.442 13 南方荚蒾Viburnum fordiae 1.34 0.372 14 水东哥Saurauia tristyla 1.28 0.580 15 琴叶榕Ficus pandurata 1.25 0.370 16 黄牛木
Cratoxylum cochinchinense1.25 0.279 17 粗叶榕Ficus hirta 1.22 0.520 18 山黄皮
Clausena excavataBurm1.15 0.358 19 毛果算盘子
(G.eriocarpum)1.14 0.590 20 山石榴Catunaregam spinosa 1.08 0.329 21 水锦树
Wendlandia uvariifolia1.01 0.510
下载: 导出CSV
表 4 蚬木次生林主要木本植物的重要值及生态位宽度
Table 4 Importance value and niche breadth of dominant woody plants in the Excentrodendron hsienmu natural secondary forest
排序
Rank物种
Species重要值
Importance vlue(Ⅳ)生态位宽度
Niche breadth(Bi)1 蚬木
Excentrodendron hsienmu74.63 0.986 2 澄广花Orophea hainanensis 8.77 0.677 3 鱼骨木Canthium dicoccum 3.35 0.660 4 岩柿Diospyros dumetorum 2.62 0.333 5 榔榆Ulmus parvifolia 2.57 0.333 6 九里香Murraya exotica 2.08 0.507 7 鹅掌柴Schefflera octophylla 1.44 0.333 8 黄牛木
Cratoxylum cochinchinense1.31 0.333 9 菜豆树Radermachera sinica 1.11 0.664
下载: 导出CSV
表 5 麻栎次生林主要木本植物生态位重叠
Table 5 Niche overlap of dominant woody plants in the Quercus acutissima natural secondary forest
物种序号
Species No.1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 1 1.000 2 0.811 1.000 3 0.981 0.853 1.000 4 0.873 0.580 0.762 1.000 5 0.996 0.802 0.961 0.911 1.000 6 0.962 0.862 0.997 0.708 0.936 1.000 7 0.447 0.849 0.465 0.350 0.466 0.469 1.000 8 0.947 0.859 0.991 0.670 0.916 0.999 0.461 1.000 9 0.830 0.797 0.748 0.903 0.871 0.708 0.716 0.673 1.000 10 0.910 0.944 0.964 0.621 0.883 0.976 0.628 0.978 0.716 1.000 11 0.691 0.282 0.540 0.945 0.742 0.472 0.090 0.427 0.753 0.341 1.000 12 0.424 0.839 0.445 0.324 0.442 0.451 1.000 0.443 0.697 0.613 0.064 1.000 13 0.760 0.579 0.631 0.959 0.816 0.571 0.498 0.527 0.951 0.527 0.907 0.476 1.000 14 0.882 0.990 0.919 0.646 0.869 0.925 0.768 0.922 0.806 0.978 0.360 0.755 0.609 1.000 15 0.704 0.910 0.678 0.665 0.731 0.661 0.932 0.641 0.918 0.754 0.432 0.921 0.763 0.873 1.000 注:物种序号同表 2。Note:species No. was the same as Tab. 2
下载: 导出CSV
表 6 枫香次生林主要木本植物生态位重叠
Table 6 Niche overlap of dominant woody plants in the Liquidambar formosana natural secondary forest
物种序号
SpeciesNo.1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 1 1.000 2 0.439 1.000 3 0.604 0.221 1.000 4 0.927 0.453 0.778 1.000 5 0.806 0.727 0.612 0.753 1.000 6 0.549 0.973 0.237 0.507 0.834 1.000 7 0.385 0.000 0.960 0.597 0.405 0.000 1.000 8 0.626 0.283 0.722 0.714 0.750 0.409 0.645 1.000 9 0.919 0.283 0.474 0.901 0.558 0.360 0.277 0.515 1.000 10 0.468 0.234 0.891 0.676 0.619 0.281 0.876 0.906 0.360 1.000 11 0.486 0.850 0.211 0.344 0.805 0.897 0.000 0.248 0.180 0.142 1.000 12 0.615 0.658 0.206 0.400 0.868 0.799 0.000 0.459 0.313 0.219 0.901 1.000 13 0.652 0.392 0.173 0.430 0.789 0.594 0.000 0.630 0.437 0.293 0.623 0.896 1.000 14 0.636 0.282 0.764 0.695 0.793 0.415 0.690 0.984 0.465 0.906 0.329 0.534 0.664 1.000 15 0.581 0.574 0.189 0.341 0.826 0.722 0.000 0.414 0.261 0.178 0.878 0.992 0.890 0.505 1.000 16 0.715 0.000 0.527 0.721 0.242 0.000 0.416 0.134 0.790 0.182 0.000 0.000 0.000 0.144 0.000 1.000 17 0.671 0.754 0.291 0.489 0.833 0.826 0.059 0.268 0.386 0.136 0.956 0.910 0.674 0.356 0.899 0.257 1.000 18 0.514 0.000 0.967 0.699 0.413 0.000 0.974 0.595 0.439 0.808 0.000 0.000 0.000 0.636 0.000 0.612 0.115 1.000 19 0.633 0.948 0.314 0.592 0.784 0.939 0.063 0.260 0.463 0.200 0.885 0.716 0.443 0.283 0.650 0.275 0.878 0.123 1.000 20 0.378 0.087 0.922 0.561 0.535 0.130 0.952 0.798 0.214 0.954 0.116 0.178 0.212 0.843 0.172 0.198 0.125 0.877 0.092 1.000 21 0.805 0.365 0.263 0.705 0.701 0.528 0.066 0.715 0.796 0.392 0.335 0.607 0.819 0.662 0.551 0.290 0.441 0.130 0.423 0.196 1.000 注:物种序号同表 3。Note:species No. was the same as Tab. 3
下载: 导出CSV
表 7 蚬木次生林主要木本植物生态位重叠
Table 7 Niche overlap of dominant woody plants in the Excentrodendron hsienmu natural secondary forest
物种序号
Species No.1 2 3 4 5 6 7 8 9 1 1.000 2 0.783 1.000 3 0.810 0.948 1.000 4 0.493 0.438 0.181 1.000 5 0.493 0.438 0.181 1.000 1.000 6 0.770 0.209 0.324 0.271 0.271 1.000 7 0.493 0.438 0.181 1.000 1.000 0.271 1.000 8 0.493 0.438 0.181 1.000 1.000 0.271 1.000 1.000 9 0.870 0.664 0.838 0.708 0.000 0.720 0.000 0.000 1.000 注:物种序号同表 4。Note: species No. was the same as Tab. 4.
下载: 导出CSV
表 8 桂西南喀斯特山地木本植物群落的总体关联性
Table 8 Overall interspecific associations within woody plant communities in the karst mountains of Southwest Guangxi
林分类型
Forest type方差比率
Variance ratio(VR)检验统计量Test
statistics(χ 0.952 N，x 2 0.05N) 测度结果
Measurement result麻栎次生林
Quercus acutissima natural secondary forest1.004 48.172 (33.098，65.171) 不显著正关联No significantly positive correlation 枫香次生林
Liquidambar formosana natural secondary forest0.905 72.370 (60.391，101.879) 不显著负关联
No significantly negative correlation蚬木次生林
Excentrodendron hsienmu natural secondary forest1.689 81.072 (33.098，65.171) 显著正关联
Significantly positive correlation
下载: 导出CSV
表 9 环境因子与CCA排序轴的相关系数
Table 9 Correlation coefficients between environmental factors and CCA ordination axes
项目Item 第1轴Axis 1 第2轴Axis 2 第3轴Axis 3 第4轴Axis 4 海拔Elevation, Elv -0.294 9 -0.702 9* -0.518 5 -0.293 4 坡度Slope degree, Slo 0.117 4 -0.641 3* 0.626 0* -0.308 0 坡向Slope aspect, Asp -0.004 4 -0.904 4 *** -0.338 3 -0.104 6 坡位Slope position, Pos 0.336 3 0.108 2 -0.268 5 -0.011 3 pH值pH value, pH 0.486 2 -0.717 5 ** 0.377 4 0.032 2 土壤有机质Soil organic matter, SOM 0.344 2 -0.355 2 0.654 9* -0.324 5 全氮Total nitrogen, TN 0.362 2 -0.420 5 0.619 3* -0.311 5 全磷Total phosphorus, TP 0.598 8* -0.475 3 0.575 3 -0.059 6 全钾Total potassium, TK -0.603 4* 0.445 2 -0.576 7* 0.091 7 特征值Eigenvalue 0.763 0.557 0.293 0.256 物种-环境相关Species-environment correlation 0.995 0.996 0.999 0.997 物种环境关系的方差累积比例/% Cumulative percentage variance of species-environment 31.43 54.36 66.42 76.95 所有典范轴的显著性检验Test of significance of all canonical axes 0.002 0 注:*表示在P＜0.05水平上显著相关, **表示在P＜0.01水平上极显著相关, ***表示在P＜0.001水平上极显著相关。Notes: * means correlation is significant at P＜0.05 level; **means correlation is significant at P＜0.01 level; ***means correlation is significant at P＜0.001 level.
下载: 导出CSV
-
[1] 宋同清, 彭晚霞, 曾馥平, 等.木论喀斯特峰丛洼地森林群落空间格局及环境解释[J].植物生态学报, 2010, 34(3):298-308. doi: 10.3773/j.issn.1005-264x.2010.03.007 SONG T Q, PENG W X, ZENG F P, et al. Spatial pattern of forest communities and environmental interpretation in Mulun National Nature Reserve, karst cluster-peak depression region[J]. Chinese Journal of Plant Ecology, 2010, 34(3): 298-308. doi: 10.3773/j.issn.1005-264x.2010.03.007
[2] 宋同清, 彭晚霞, 杜虎, 等.中国西南喀斯特石漠化时空演变特征、发生机制与调控对策[J].生态学报, 2014, 34(18):5328-5341. http://d.old.wanfangdata.com.cn/Periodical/stxb201418024 SONG T Q, PENG W X, DU H, et al. Occurrence, spatial-temporal dynamics and regulation strategies of karst rocky desertificationin southwest China[J]. Acta Ecologica Sinica, 2014, 34(18): 5328-5341. http://d.old.wanfangdata.com.cn/Periodical/stxb201418024
[3] 曾馥平, 彭晚霞, 宋同清, 等.桂西北喀斯特人为干扰区植被自然恢复22年后群落特征[J].生态学报, 2007, 27(12):5110-5119. doi: 10.3321/j.issn:1000-0933.2007.12.020 ZENG F P, PENG W X, SONG T Q, et al. Changes in vegetation after 22 years natural restoration in the karst disturbed area in Northwest Guangxi[J]. Acta Ecologica Sinica, 2007, 27(12): 5110-5119. doi: 10.3321/j.issn:1000-0933.2007.12.020
[4] 文丽, 宋同清, 杜虎, 等.中国西南喀斯特植物群落演替特征及驱动机制[J].生态学报, 2015, 35(17):5822-5833. http://d.old.wanfangdata.com.cn/Periodical/stxb201517028 WEN L, SONG T Q, DU H, et al. The succession characteristics and its driving mechanism of plant community in karst region, Southwest China[J]. Acta Ecologica Sinica, 2015, 35(17): 5822-5833. http://d.old.wanfangdata.com.cn/Periodical/stxb201517028
[5] 谭秋锦, 宋同清, 彭晚霞, 等.峡谷型喀斯特不同生态系统的土壤微生物数量及生物量特征[J].生态学报, 2014, 34(12):3302-3310. http://d.old.wanfangdata.com.cn/Periodical/stxb201412018 TAN Q J, SONG T Q, PENG W X, et al. Characteristics of soil microbial populations and biomass under different ecosystems in a canyon karst region[J]. Acta Ecologica Sinica, 2014, 34(12): 3302-3310. http://d.old.wanfangdata.com.cn/Periodical/stxb201412018
[6] 卢成阳, 彭晚霞, 宋同清, 等.喀斯特峰丛洼地不同生态系统土壤微生物与养分的耦合关系[J].生态学杂志, 2013, 32(3):522-528. http://d.old.wanfangdata.com.cn/Periodical/stxzz201303002 LU C Y, PENG W X, SONG T Q, et al. Coupling relationships between soil microbe and soil nutrient under different ecosystems in depression between karst hills[J]. Chinese Journal of Ecology, 2013, 32(3) : 522-528. http://d.old.wanfangdata.com.cn/Periodical/stxzz201303002
[7] 曾昭霞, 王克林, 刘孝利, 等.桂西北喀斯特森林植物-凋落物-土壤生态化学计量特征[J].植物生态学报, 2015, 39(7):682-693. http://d.old.wanfangdata.com.cn/Periodical/zwstxb201507004 ZENG Z X, WANG K L, LIU X L, et al. Stoichiometric characteristics of plants, litter and soils in karst plant communities of Northwest Guangxi[J]. Chinese Journal of Plant Ecology, 2015, 39(7) : 682-693. http://d.old.wanfangdata.com.cn/Periodical/zwstxb201507004
[8] 俞月凤, 何铁光, 彭晚霞, 等.喀斯特峰丛洼地不同类型森林养分循环特征[J].生态学报, 2015, 35(22):7531-7542. http://d.old.wanfangdata.com.cn/Periodical/stxb201522027 YU Y F, HE T G, PENG W X, et al. Dynamics of nutrient elements in different types of forests in depressions between karst hills[J]. Acta Ecologica Sinica, 2015, 35(22) : 7531-7542. http://d.old.wanfangdata.com.cn/Periodical/stxb201522027
[9] 杜虎, 彭晚霞, 宋同清, 等.桂北喀斯特峰丛洼地植物群落特征及其与土壤的耦合关系[J].植物生态学报, 2013, 37(3):197-208. http://d.old.wanfangdata.com.cn/Periodical/zwstxb201303002 DU H, PENG W X, SONG T Q, et al. Plant community characteristics and its coupling relationships with soil in depressions between karst hills, North Guangxi[J]. Chinese Journal of Plant Ecology, 2013, 37(3) : 197-208. http://d.old.wanfangdata.com.cn/Periodical/zwstxb201303002
[10] 简敏菲, 刘琪景, 朱笃, 等.九连山常绿阔叶林乔木优势种群的种间关联性分析[J].植物生态学报, 2009, 33(4): 672-680. doi: 10.3773/j.issn.1005-264x.2009.04.005 JIAN M F, LIU Q J, ZHU D, et al. Inter-specie correlations among dominant populations of tree layer species in evergreen broad-leaved forest in Jiulianshan Mountain of subtropical China[J]. Chinese Journal of Plant Ecology, 2009, 33(4) : 672-680. doi: 10.3773/j.issn.1005-264x.2009.04.005
[11] 周刘丽, 张晴晴, 赵延涛, 等.浙江天童枫香树群落不同垂直层次物种间的联结性与相关性[J].植物生态学报, 2015, 39(12):1136-1145. doi: 10.17521/cjpe.2015.0110 ZHOU L L, ZHANG Q Q, ZHAO Y T, et al. Species association and correlation between vertical layers in the Liquidambar formosana community in Tiantong Region, Zhejiang Province[J]. Chinese Journal of Plant Ecology, 2015, 39(12) : 1136-1145. doi: 10.17521/cjpe.2015.0110
[12] 刘珏宏, 高慧, 张丽红, 等.内蒙古锡林郭勒草原大针茅-克氏针茅群落的种间关联特征分析[J].植物生态学报, 2010, 34(9):1016-1024. doi: 10.3773/j.issn.1005-264x.2010.09.002 LIU Y H, GAO H, ZHANG L H, et al. Comparative analysis of inter-specific association within the Stipa grandis-S. krylovii community in typical steppe of Inner Mongolia, China[J]. Chinese Journal of Plant Ecology, 2010, 34(9) : 1016-1024. doi: 10.3773/j.issn.1005-264x.2010.09.002
[13] 郑超超, 伊力塔, 张超, 等.浙江江山公益林物种种间关系及CCA排序[J].生态学报, 2015, 35(22):7511-7521. http://d.old.wanfangdata.com.cn/Periodical/stxb201522025 ZHENG C C, YI L T, ZHANG C, et al. Interspecific relationship and canonical correspondence analysis of the dominant species in ecological service forest of Jiangshan City in Zhejiang Province[J]. Acta Ecologica Sinica, 2015, 35(22) : 7511-7521. http://d.old.wanfangdata.com.cn/Periodical/stxb201522025
[14] 孙越, 夏富才, 何怀江, 等.长白山东北坡长白落叶松-白桦次生林群落结构特征[J].北京林业大学学报, 2016, 38(12):28-38. doi: 10.13332/j.1000-1522.20160088 SUN Y, XIA F C, HE H J, et al. Community structure features of the larch-birch secondary forest on the northeastern slope of Changbai Mountain, Northeast China[J]. Journal of Beijing Forestry University, 2016, 38(12): 28-38. doi: 10.13332/j.1000-1522.20160088
[15] 鲍士旦.土壤农化分析[M].北京:中国农业出版社, 2000. BAO S D. Analysis of soil agricultural chemical[M]. Beijing: China Agriculture Press, 2000.
[16] 孙儒泳, 李庆芬, 牛翠娟, 等.基础生态学[M].北京:高等教育出版社, 2002. SUN R Y, LI Q F, NIU C J, et al. Primary ecology[M]. Beijing: Higer Education Press, 2002.
[17] LEVINS R. Evolution in changing environments some theoretical explorations[M]. Princeton: Princeton University Press, 1968.
[18] PIANKA E R. The structure of Lizard communities[J]. Annual Review of Ecology and Systematics, 1973, 4 : 53-74. doi: 10.1146/annurev.es.04.110173.000413
[19] SCHLUTER D. A variance test for detecting species associations, with some example applications[J]. Ecology, 1984, 65(3) : 998-1005. doi: 10.2307/1938071
[20] DICE L R. Measure of the amount of ecologic association between species[J]. Ecology, 1945, 26(3) : 297-302. doi: 10.2307/1932409
[21] 张金屯.数量生态学[M].北京:科学出版社, 2004. ZHANG J T. Numerical ecology[M]. Beijing: Science Press, 2004.
[22] 丁文慧, 李秀珍, 姜俊彦, 等.崇明东滩南部河口盐沼植物群落种间关系的数量分析[J].应用生态学报, 2016, 27(5):1417-1426. http://d.old.wanfangdata.com.cn/Periodical/yystxb201605010 DING W H, LI X Z, JIANG J Y, et al. Numerical analysis of inter-specific relationships in the estuary salt marsh plant community of southern Chongming Dongtan, Shanghai[J]. Chinese Journal of Applied Ecology, 2016, 27(5) : 1417-1426. http://d.old.wanfangdata.com.cn/Periodical/yystxb201605010
[23] 刘世梁, 马克明, 傅伯杰, 等.北京东灵山地区地形土壤因子与植物群落关系研究[J].植物生态学报, 2003, 27(4):496-502. doi: 10.3321/j.issn:1005-264X.2003.04.011 LIU S L, MA K M, FU B J, et al. The relationship between landform, soil characteristics and plant community structure in the Donglinshan Mountain region, Beijing[J]. Chinese Journal of Plant Ecology, 2003, 27(4) : 496-502. doi: 10.3321/j.issn:1005-264X.2003.04.011
[24] 潘高, 张合平, 潘登.南方红壤丘陵区3种森林群落内主要草本植物种群生态位特征[J].草业科学, 2015, 32(12):2094-2106. doi: 10.11829/j.issn.1001-0629.2015-0246 PAN G, ZHANG H P, PAN D. Niche characteristics of herb populations within three forest types in hilly red soil region of southern China[J]. Pratacultural Science, 2015, 32(12) : 2094-2106. doi: 10.11829/j.issn.1001-0629.2015-0246
[25] 赵天梁.山西崦山自然保护区侧柏林植物生态位特征[J].北京林业大学学报, 2015, 37(8):24-30. http://d.old.wanfangdata.com.cn/Periodical/bjlydxxb201508004 ZHAO T L. Niche characteristics of dominants in Platycladus orientalis forests in Yanshan Nature Reserve, Shanxi[J]. Journal of Beijing Forestry University, 2015, 37(8):24-30. http://d.old.wanfangdata.com.cn/Periodical/bjlydxxb201508004
[26] 胡文强, 黄世能, 李家湘, 等.南岭石坑崆山顶矮林乔木优势种群的种间关联性[J].生态学杂志, 2013, 32(10): 2665-2671. http://d.old.wanfangdata.com.cn/Periodical/stxzz201310021 HU W Q, HUANG S N, LI J X, et al. Interspecific associations among dominant tree populations in an elfin forest community in Shikengkong of Nanling Mountains, China[J]. Chinese Journal of Ecology, 2013, 32(10) : 2665-2671. http://d.old.wanfangdata.com.cn/Periodical/stxzz201310021
[27] 龚直文, 亢新刚, 顾丽, 等.长白山云冷杉针阔混交林两个演替阶段乔木的种间联结性[J].北京林业大学学报, 2011, 33(5):28-33. http://j.bjfu.edu.cn/article/id/9643 GONG Z W, KANG X G, GU L, et al. Interspecific association among arbor species in two succession stages of spruce-fir conifer and broadleaved mixed forest in Changbai Mountain, Northeast China[J]. Journal of Beijing Forestry University, 2011, 33(5): 28-33. http://j.bjfu.edu.cn/article/id/9643
[28] 奇凯, 张春雨, 侯继华, 等.赤峰市沙地油松林草本植物多样性及种间关联动态[J].生态学报, 2010, 30(18): 5106-5112. http://d.old.wanfangdata.com.cn/Periodical/stxb201018032 QI K, ZHANG C Y, HOU J H, et al. Dynamics of species diversity and interspecific associations of herbaceous plants in a Pinus tabulaeform is forest on a sandy site in Chifeng, China[J]. Acta Ecologica Sinica, 2010, 30(18) : 5106-5112. http://d.old.wanfangdata.com.cn/Periodical/stxb201018032
[29] 杜乐山, 杨红晓, 郭晓蕾, 等.黄连木群落种间联结指数-等级格局模型研究[J].北京林业大学学报, 2013, 35(5):37-45. http://j.bjfu.edu.cn/article/id/9944 DU L S, YANG H X, GUO X L, et al. Interspecific associations of Pistacia chinensis community and association index-rank pattern model[J]. Jounal of Beijing Forestry University, 2013, 35(5):37-45. http://j.bjfu.edu.cn/article/id/9944
[30] HOPFENSPERGER K N, BURGIN urgin J, SCHOEPFER Ⅴ A, et al. Impacts of saltwater incursion on plant communities, anaerobic microbial metabolism, and resulting relationships in a restored freshwater wetland[J]. Ecosystems, 2014, 17(5) : 792-807. doi: 10.1007/s10021-014-9760-x
[31] 余敏, 周志勇, 康峰峰, 等.山西灵空山小蛇沟林下草本层植物群落梯度分析及环境解释[J].植物生态学报, 2013, 37(5):373-383. http://d.old.wanfangdata.com.cn/Periodical/zwstxb201305001 YU M, ZHOU Z Y, KANG F F, et al. Gradient analysis and environmental interpretation of understory herb-layer communities in Xiaoshegou of Lingkong Mountain, Shanxi, China[J]. Chinese Journal of Plant Ecology, 2013, 37(5) : 373-383. http://d.old.wanfangdata.com.cn/Periodical/zwstxb201305001
[32] 臧润国, 井学辉, 丁易, 等.新疆阿尔泰山小东沟林区木本植物群落数量分类、排序及其环境解释[J].林业科学, 2010, 46(2):24-31. http://www.wanfangdata.com.cn/details/detail.do?_type=perio&id=lykx201002005 ZANG R G, JING X H, DING Y, et al. Quantitative classification, ordination and environmental analysis of woody plant communities in Xiaodonggou forest area of the Altai Mountain, Xingjiang[J]. Scientia Silvae Sinicae, 2010, 46(2) : 24-31. http://www.wanfangdata.com.cn/details/detail.do?_type=perio&id=lykx201002005
[33] 刘秋锋, 康慕谊, 刘全儒.中条山混沟地区森林乔木种的数量分类与环境解释[J].植物生态学报, 2006, 30(3) :383-391. doi: 10.3321/j.issn:1005-264X.2006.03.003 LIU Q F, KANG M Y, LIU Q R. Quantitative classification and environmental interpretation of forest tree species in Hungou, Zhongtiao Mountain[J]. Chinese Journal of Plant Ecology, 2006, 30(3) : 383-391. doi: 10.3321/j.issn:1005-264X.2006.03.003
[34] 朱源, 康慕谊.排序和广义线性模型与广义可加模型在植物种与环境关系研究中的应用[J].生态学杂志, 2005, 24(7):807-811. doi: 10.3321/j.issn:1000-4890.2005.07.018 ZHU Y, KANG M Y. Application of ordination and GLM/GAM in the research of the relationship between plant species and environment[J]. Chinese Journal of Ecology, 2005, 24(7) : 807-811. doi: 10.3321/j.issn:1000-4890.2005.07.018
-
期刊类型引用(2)
1. 苏岫，王祥，宋德瑞，李飞，杨正先，张浩. 基于改进光谱角法的红树林高分遥感分类方法研究. 海洋环境科学. 2021(04): 639-646 . 
百度学术
2. 陈冀岱，牛树奎. 多时相高分辨率遥感影像的森林可燃物分类和变化分析. 北京林业大学学报. 2018(12): 38-48 . 本站查看
其他类型引用(3)
计量
- 文章访问数: 3138
- HTML全文浏览量: 528
- PDF下载量: 43
- 被引次数: 5
