生态环境学报 ›› 2022, Vol. 31 ›› Issue (1): 37-43.DOI: 10.16258/j.cnki.1674-5906.2022.01.005
收稿日期:
2021-06-01
出版日期:
2022-01-18
发布日期:
2022-03-10
通讯作者:
*作者简介:
刘小菊(1979年生),女,教授,博士,研究方向为森林、草地生态和园林植物栽培。E-mail: liuxiaoju317@163.com
基金资助:
LIU Xiaoju*(), CHU Jiangtao, ZHANG Yue, SHAN Qi
Received:
2021-06-01
Online:
2022-01-18
Published:
2022-03-10
摘要:
喀纳斯泰加林植被的生长和分布受火干扰和环境因子的共同作用,为了解喀纳斯泰加林林下柳兰分布与生态因子的关系,促进种群扩繁,共设置了35个样地进行调查和分析。建立柳兰重要值与生态因子矩阵,利用CCA分析法对不同火烧林分中柳兰的生长分布状况与林火烈度、火后时间、海拔、坡度、坡向、郁闭度、土壤pH值、速效钾、土壤有机质、灌木层盖度、草本层盖度和草本层物种多样性指数等20个生态因子的关系进行了分析。结果显示,第一轴主要反映林火烈度、海拔、坡向,灌木层盖度、pH值、有机质、全钾和速效钾的变化;第二轴主要反映林火烈度、火后时间、草本层盖度、坡向、坡位、土壤容重、电导率、有机质、有效磷和全氮的变化。对柳兰分布有显著影响的生态因子是林火烈度、有机质、海拔、坡向、灌木层盖度、土壤容重、全钾和速效钾,前两轴的累计贡献率为72.48%。柳兰适合在土壤呈弱酸性、海拔低、阳坡、土壤容重小、土壤有机质、全钾和速效钾含量高的环境中生长。柳兰是阳性植物,是火烧后的先锋植物。对影响柳兰分布的生态因子进行定量分离,结果发现环境因子和火干扰因子对柳兰样地物种分布的解释能力为88.2%,显示出较好的排序效果。喀纳斯泰加林受人为干扰较少,柳兰所在植物群落与环境保持了良好的对应关系,生态因子与物种分布呈显著相关(P=0.003),表明CCA排序结果可以解释生态因子对物种分布的影响程度。
中图分类号:
刘小菊, 褚江涛, 张越, 单奇. 环境因子和火干扰因子对喀纳斯泰加林柳兰分布的影响[J]. 生态环境学报, 2022, 31(1): 37-43.
LIU Xiaoju, CHU Jiangtao, ZHANG Yue, SHAN Qi. Effects of Environmental Factors and Fire Disturbance Factors on Distribution of Chamerion angustifolium in Kanas Taiga[J]. Ecology and Environment, 2022, 31(1): 37-43.
序号 No. | 物种 Species | 相对频度 Relative frequency/% |
---|---|---|
1 | 柳兰 Chamerion angustifolium | 100.00 |
2 | 黑穗薹草 Carex atrata | 100.00 |
3 | 老芒麦 Elymus sibiricus | 97.14 |
4 | 白花砧草 Galium boreale | 97.14 |
5 | 寄奴花 Cerastium pauciflorum | 88.57 |
6 | 直立老鹳草 Geranium rectum | 80.00 |
7 | 四籽野豌豆 Vicia tetrasperma | 80.00 |
8 | 圆叶鹿蹄草 Pyrola rotundifolia | 80.00 |
9 | 野火球 Trifolium lupinaster | 62.46 |
10 | 薄蒴草 Lepyrodiclis holosteoides | 51.43 |
表1 柳兰样地的主要草本物种
Table1 Main herb species in Chamerion angustifolium plots
序号 No. | 物种 Species | 相对频度 Relative frequency/% |
---|---|---|
1 | 柳兰 Chamerion angustifolium | 100.00 |
2 | 黑穗薹草 Carex atrata | 100.00 |
3 | 老芒麦 Elymus sibiricus | 97.14 |
4 | 白花砧草 Galium boreale | 97.14 |
5 | 寄奴花 Cerastium pauciflorum | 88.57 |
6 | 直立老鹳草 Geranium rectum | 80.00 |
7 | 四籽野豌豆 Vicia tetrasperma | 80.00 |
8 | 圆叶鹿蹄草 Pyrola rotundifolia | 80.00 |
9 | 野火球 Trifolium lupinaster | 62.46 |
10 | 薄蒴草 Lepyrodiclis holosteoides | 51.43 |
统计量 Statistic | 第一轴 Axis 1 | 第二轴 Axis 2 | 第三轴 Axis 3 | 第四轴 Axis 4 |
---|---|---|---|---|
特征值 Eigenvalues | 0.0127 | 0.005 | 0.0036 | 0.0026 |
对物种分布解释百分比 Explained variation (cumulative)/% | 22.75 | 31.71 | 38.13 | 42.88 |
物种分布与生态因子的相关性Pseudo-canonical correlation | 0.8028 | 0.7707 | 0.8419 | 0.7316 |
生态因子的累计解释量 Explained fitted variation (cumulative)/% | 40.97 | 72.48 | 80.98 | 86.88 |
表2 CCA序轴的特征根及其与环境因子和火干扰因子之间的关系
Table 2 Eigenvalues and correlation coefficients of environmental factors and fire disturbance factors for first four axes of CCA
统计量 Statistic | 第一轴 Axis 1 | 第二轴 Axis 2 | 第三轴 Axis 3 | 第四轴 Axis 4 |
---|---|---|---|---|
特征值 Eigenvalues | 0.0127 | 0.005 | 0.0036 | 0.0026 |
对物种分布解释百分比 Explained variation (cumulative)/% | 22.75 | 31.71 | 38.13 | 42.88 |
物种分布与生态因子的相关性Pseudo-canonical correlation | 0.8028 | 0.7707 | 0.8419 | 0.7316 |
生态因子的累计解释量 Explained fitted variation (cumulative)/% | 40.97 | 72.48 | 80.98 | 86.88 |
生态因子Ecological factors | 第一轴 Axis 1 | 第二轴Axis 2 | 生态因子Ecological factors | 第一轴Axis 1 | 第二轴Axis 2 |
---|---|---|---|---|---|
Se | -0.3523* | 0.2409* | W | 0.108 0 | 0.0346 |
PT | -0.133 | 0.1531 | BD | 0.145 0 | -0.2539* |
AL | -0.7043** | 0.0174 | C | -0.0078 | -0.1975 |
SA | 0.2135* | 0.1279 | pH | 0.3070* | -0.0623 |
SG | -0.1408 | 0.0596 | AP | 0.0205 | -0.1137 |
SL | 0.0469 | 0.1641 | SOM | 0.4645** | 0.2405* |
CD | 0.1170 | -0.1024 | TN | 0.0896 | -0.1475 |
HC | -0.1197 | -0.1051 | AK | 0.3832* | 0.0238 |
SC | -0.3158* | 0.0869 | TK | 0.3679* | 0.0295 |
表3 CCA排序轴与环境因子和火干扰因子的相关系数
Table 3 Correlation coefficients of the CCA ordination axes and the environmental and fire disturbance factors
生态因子Ecological factors | 第一轴 Axis 1 | 第二轴Axis 2 | 生态因子Ecological factors | 第一轴Axis 1 | 第二轴Axis 2 |
---|---|---|---|---|---|
Se | -0.3523* | 0.2409* | W | 0.108 0 | 0.0346 |
PT | -0.133 | 0.1531 | BD | 0.145 0 | -0.2539* |
AL | -0.7043** | 0.0174 | C | -0.0078 | -0.1975 |
SA | 0.2135* | 0.1279 | pH | 0.3070* | -0.0623 |
SG | -0.1408 | 0.0596 | AP | 0.0205 | -0.1137 |
SL | 0.0469 | 0.1641 | SOM | 0.4645** | 0.2405* |
CD | 0.1170 | -0.1024 | TN | 0.0896 | -0.1475 |
HC | -0.1197 | -0.1051 | AK | 0.3832* | 0.0238 |
SC | -0.3158* | 0.0869 | TK | 0.3679* | 0.0295 |
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