生态环境学报 ›› 2025, Vol. 34 ›› Issue (2): 247-255.DOI: 10.16258/j.cnki.1674-5906.2025.02.007
刘嘉怡1(), 张军1, 张帆2, 张慧2, 王梓晗2, 刘菊红1, 吕世杰2,*(
)
收稿日期:
2024-09-18
出版日期:
2025-02-18
发布日期:
2025-03-03
通讯作者:
*吕世杰。E-mail: lshj123@163.com作者简介:
刘嘉怡(2001年生),女,硕士研究生,研究方向为生物统计。E-mail: 8987081@qq.com
基金资助:
LIU Jiayi1(), ZHANG Jun1, ZHANG Fan2, ZHANG Hui2, WANG Zihan2, LIU Juhong1, LÜ Shijie2,*(
)
Received:
2024-09-18
Online:
2025-02-18
Published:
2025-03-03
摘要:
探究不同围封年限对短花针茅荒漠草原优势种群种间联结性的影响可以为荒漠草原的科学管理和生态恢复提供理论支持和实践指导,有助于推动荒漠草原生态系统的可持续管理和保护。以短花针茅(Stipa breviflora)荒漠草原为研究对象,选取了围封年限分别为1、10、19、25 a的4个草地,运用双因素方差、方差比率法、χ2统计量、联结系数(AC)、共同出现百分率(PC)以及Dice指数(DI)研究方法,研究了围封对短花针茅荒漠草原优势种群种间联结性的影响。结果表明,1)空间尺度变化对于短花针茅、无芒隐子草(Cleistogenes songorica)和碱韭(Allium polyrhizum)出现频率无显著影响,围封年限变化对荒漠草原植物群落中优势种的出现频率具有显著影响。2)在不同的空间尺度下,优势种的总体联结性多表现为负联结且多数不显著,仅在小尺度中期围封时表现为显著负联结。围封年限增加会改变优势种的总体联结性,随着围封年限的增加优势种总体联结性由正转负,优势种总体亲和性下降。3)围封年限增加也会改变优势种的种间联结性,由协同共存转变为竞争共存。4)优势种的AC值多为负,而PC值与DI值多处于[0.6, 1],表明优势种不仅具有优势地位且存在竞争关系。
中图分类号:
刘嘉怡, 张军, 张帆, 张慧, 王梓晗, 刘菊红, 吕世杰. 围封对短花针茅荒漠草原优势种群种间联结性的影响[J]. 生态环境学报, 2025, 34(2): 247-255.
LIU Jiayi, ZHANG Jun, ZHANG Fan, ZHANG Hui, WANG Zihan, LIU Juhong, LÜ Shijie. Effects of Enclosure on Interspecific Association of Dominant Species of Stipa breviflora in Desert Steppe[J]. Ecology and Environment, 2025, 34(2): 247-255.
来源 | 因变量 | 自由度 df | 频率 | |
---|---|---|---|---|
F | p | |||
空间 | 短花针茅 S. breviflora | 2 | 1.85 | 0.24 |
无芒隐子草 C. songorica | 2 | 2.22 | 0.19 | |
碱韭 A. polyrhizum | 2 | 0.38 | 0.70 | |
处理 | 短花针茅 S. breviflora | 3 | 113.42 | <0.01 |
无芒隐子草 C. songorica | 3 | 95.49 | <0.01 | |
碱韭 A. polyrhizum | 3 | 462.77 | <0.01 |
表1 优势种群频度双因素方差分析
Table 1 Two-way analysis of variance for frequency of dominant population
来源 | 因变量 | 自由度 df | 频率 | |
---|---|---|---|---|
F | p | |||
空间 | 短花针茅 S. breviflora | 2 | 1.85 | 0.24 |
无芒隐子草 C. songorica | 2 | 2.22 | 0.19 | |
碱韭 A. polyrhizum | 2 | 0.38 | 0.70 | |
处理 | 短花针茅 S. breviflora | 3 | 113.42 | <0.01 |
无芒隐子草 C. songorica | 3 | 95.49 | <0.01 | |
碱韭 A. polyrhizum | 3 | 462.77 | <0.01 |
空间尺度 | 围封 年限/a | 短花针茅 S. breviflora | 无芒隐子草 C. songorica | 碱韭 A. polyrhizum |
---|---|---|---|---|
30 m×30 m | 1 | 88.24% | 94.12% | 98.82% |
10 | 61.18% | 88.24% | 97.65% | |
19 | 69.41% | 94.12% | 98.82% | |
25 | 54.12% | 100.00% | 75.29% | |
35 m×35 m | 1 | 84.96% | 95.58% | 99.12% |
10 | 57.52% | 87.61% | 98.23% | |
19 | 69.03% | 95.58% | 99.12% | |
25 | 51.33% | 100.00% | 76.11% | |
40 m×40 m | 1 | 80.69% | 94.48% | 98.62% |
10 | 56.55% | 84.83% | 96.55% | |
19 | 72.41% | 93.79% | 99.31% | |
25 | 51.72% | 100.00% | 77.93% |
表2 优势种群在不同空间尺度及围封年限下出现的频率
Table 2 The frequency of dominant populations in different spatial scales and enclosure years
空间尺度 | 围封 年限/a | 短花针茅 S. breviflora | 无芒隐子草 C. songorica | 碱韭 A. polyrhizum |
---|---|---|---|---|
30 m×30 m | 1 | 88.24% | 94.12% | 98.82% |
10 | 61.18% | 88.24% | 97.65% | |
19 | 69.41% | 94.12% | 98.82% | |
25 | 54.12% | 100.00% | 75.29% | |
35 m×35 m | 1 | 84.96% | 95.58% | 99.12% |
10 | 57.52% | 87.61% | 98.23% | |
19 | 69.03% | 95.58% | 99.12% | |
25 | 51.33% | 100.00% | 76.11% | |
40 m×40 m | 1 | 80.69% | 94.48% | 98.62% |
10 | 56.55% | 84.83% | 96.55% | |
19 | 72.41% | 93.79% | 99.31% | |
25 | 51.72% | 100.00% | 77.93% |
空间尺度 | 围封年限/a | VR | W |
---|---|---|---|
30 m×30 m | 1 | 0.89 | 76.05 |
10 | 1.01 | 85.58 | |
19 | 0.84* | 71.44*1) | |
25 | 0.86 | 72.87 | |
35 m×35 m | 1 | 0.91 | 102.42 |
10 | 1.05 | 118.17 | |
19 | 0.87 | 98.64 | |
25 | 0.83 | 93.82 | |
40 m×40 m | 1 | 1.06 | 153.66 |
10 | 1.05 | 152.41 | |
19 | 0.85 | 123.70 | |
25 | 0.82 | 119.16 |
表3 不同空间尺度及围封年限下的方差比率VR及W统计量
Table3 Variance ratio and W statistics at different spatial scales and enclosure years
空间尺度 | 围封年限/a | VR | W |
---|---|---|---|
30 m×30 m | 1 | 0.89 | 76.05 |
10 | 1.01 | 85.58 | |
19 | 0.84* | 71.44*1) | |
25 | 0.86 | 72.87 | |
35 m×35 m | 1 | 0.91 | 102.42 |
10 | 1.05 | 118.17 | |
19 | 0.87 | 98.64 | |
25 | 0.83 | 93.82 | |
40 m×40 m | 1 | 1.06 | 153.66 |
10 | 1.05 | 152.41 | |
19 | 0.85 | 123.70 | |
25 | 0.82 | 119.16 |
围封年限/a | 空间尺度 | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
30 m×30 m | 35 m×35 m | 40 m×40 m | |||||||||
物种 | 1 | 2 | 物种 | 1 | 2 | 物种 | 1 | 2 | |||
1 | 2 | 0.02 | 2 | 0.10 | 2 | 1.71×10−3 | |||||
3 | 1.43 | 3.56 | 3 | 0.96 | 4.96*1) | 3 | 0.05 | 1.48 | |||
10 | 2 | 0.18 | 2 | 0.80 | 2 | 0.82 | |||||
3 | 0.16 | 0.35 | 3 | 0.25 | 0.30 | 3 | 2.36 | 0.88 | |||
19 | 2 | 1.06 | 2 | 1.08 | 2 | 2.33 | |||||
3 | 0.18 | 3.56 | 3 | 0.17 | 4.96* | 3 | 0.25 | 3.32 | |||
25 | 2 | 0.48 | 2 | 2.58 | 2 | 0.42 | |||||
3 | 1.16 | 8.70×10−5 | 3 | 2.58 | 1.08 | 3 | 3.93* | 0.01 |
表4 不同空间尺度及围封年限下种群间χ 2统计量矩阵
Table4 χ 2 statistical matrix among populations at different spatial scales and enclosure years
围封年限/a | 空间尺度 | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
30 m×30 m | 35 m×35 m | 40 m×40 m | |||||||||
物种 | 1 | 2 | 物种 | 1 | 2 | 物种 | 1 | 2 | |||
1 | 2 | 0.02 | 2 | 0.10 | 2 | 1.71×10−3 | |||||
3 | 1.43 | 3.56 | 3 | 0.96 | 4.96*1) | 3 | 0.05 | 1.48 | |||
10 | 2 | 0.18 | 2 | 0.80 | 2 | 0.82 | |||||
3 | 0.16 | 0.35 | 3 | 0.25 | 0.30 | 3 | 2.36 | 0.88 | |||
19 | 2 | 1.06 | 2 | 1.08 | 2 | 2.33 | |||||
3 | 0.18 | 3.56 | 3 | 0.17 | 4.96* | 3 | 0.25 | 3.32 | |||
25 | 2 | 0.48 | 2 | 2.58 | 2 | 0.42 | |||||
3 | 1.16 | 8.70×10−5 | 3 | 2.58 | 1.08 | 3 | 3.93* | 0.01 |
图2 不同空间尺度及围封年限下3个物种的联结系数AC
Figure 2 Association coefficient of 3 species at different spatial scales and enclosure years △?1≤AC≤?0.6, □?0.6≤AC<?0.3, ○?0.3≤AC<0, ●0<AC<0.3, ■0.3≤AC<0.6
图3 不同空间尺度及围封年限下3个物种的共同出现百分率PC
Figure 3 Percentage of co-occurrence of 3 species at different spatial scales and enclosure years ●0.2≤PC<0.4, ■0.4≤PC<0.6, ▲0.6≤PC≤1
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