生物多样性 ›› 2021, Vol. 29 ›› Issue (5): 596-604. DOI: 10.17520/biods.2020292
所属专题: 生物入侵
收稿日期:
2020-07-21
接受日期:
2021-02-24
出版日期:
2021-05-20
发布日期:
2021-04-22
通讯作者:
赵彩云
作者简介:
* E-mail: zhaocy@craes.org.cn基金资助:
Chaodan Guo, Jinfang Zhu, Xiaoyan Liu, Caiyun Zhao*(), Junsheng Li
Received:
2020-07-21
Accepted:
2021-02-24
Online:
2021-05-20
Published:
2021-04-22
Contact:
Caiyun Zhao
摘要:
自然保护区是抵御外来物种入侵的重要屏障, 然而人类活动可能增加外来入侵物种扩散的风险, 导致自然保护区面临不同程度的入侵。为了对比研究自然保护区内外以及不同保护区之间外来入侵草本植物的分布格局及其与人类活动的关系, 本文基于贵州省四个国家级自然保护区(赤水桫椤、习水、梵净山和麻阳河) 380个样方的调查数据, 运用双因素方差分析和非度量多维标度分析方法分析了保护区内外的外来入侵草本植物多样性和物种组成差异, 并利用冗余分析探讨了影响不同保护区内外来入侵草本植物分布的关键人类活动因子。赤水桫椤、习水、梵净山和麻阳河4个保护区共调查发现外来入侵草本植物46种, 隶属于18科37属, 其中, 4个保护区内分别有16、18、7和20种, 保护区外分别有17、10、24和20种。赤水桫椤和梵净山保护区外的外来入侵草本植物丰富度、Shannon-Wiener多样性指数和Simpson优势度指数显著高于保护区内, 而习水和麻阳河保护区内外差异不显著。梵净山保护区内的Pielou均匀度指数显著高于保护区外, 其余保护区内外差异不显著。四个保护区内外的外来入侵草本植物物种组成无明显差异。保护区内的居民量和道路长度是影响保护区内外来入侵草本植物分布格局差异的主要原因。研究结果表明, 不同保护区对外来草本植物入侵的抵御能力不同, 而人类活动程度的差异是导致其不同的原因之一。建议加强自然保护区内及周边区域人类活动管控, 减缓外来入侵植物的扩散。
郭朝丹, 朱金方, 柳晓燕, 赵彩云, 李俊生 (2021) 贵州典型自然保护区内外外来入侵草本植物的比较. 生物多样性, 29, 596-604. DOI: 10.17520/biods.2020292.
Chaodan Guo, Jinfang Zhu, Xiaoyan Liu, Caiyun Zhao, Junsheng Li (2021) Contrasting biodiversity of invasive herbs inside and outside nature reserves in Guizhou. Biodiversity Science, 29, 596-604. DOI: 10.17520/biods.2020292.
保护区 Reserves (R) | 样地位置 Plot location (P) | 保护区 × 样地位置 R × P | ||||
---|---|---|---|---|---|---|
F | P | F | P | F | P | |
df | (3, 372) | (1, 372) | (3, 372) | |||
物种丰富度 Species richness | 2.572 | 0.054 | 46.38 | < 0.001 | 4.61 | 0.004 |
Shannon-Wiener指数 Shannon-Wiener index | 4.36 | 0.005 | 39.06 | < 0.001 | 4.99 | 0.002 |
Simpson优势度指数 Simpson dominance index | 4.83 | 0.003 | 32.28 | < 0.001 | 4.86 | 0.003 |
Pielou均匀度指数 Pielou evenness index | 0.82 | 0.484 | 10.07 | 0.002 | 1.56 | 0.200 |
表1 贵州4个国家级自然保护区内外及不同保护区对外来入侵草本植物多样性影响的双因素方差分析结果
Table 1 Two-way ANOVA results of the effects of inside and outside the four national nature reserves and different nature reserves in Guizhou on the diversity of invasive herbs
保护区 Reserves (R) | 样地位置 Plot location (P) | 保护区 × 样地位置 R × P | ||||
---|---|---|---|---|---|---|
F | P | F | P | F | P | |
df | (3, 372) | (1, 372) | (3, 372) | |||
物种丰富度 Species richness | 2.572 | 0.054 | 46.38 | < 0.001 | 4.61 | 0.004 |
Shannon-Wiener指数 Shannon-Wiener index | 4.36 | 0.005 | 39.06 | < 0.001 | 4.99 | 0.002 |
Simpson优势度指数 Simpson dominance index | 4.83 | 0.003 | 32.28 | < 0.001 | 4.86 | 0.003 |
Pielou均匀度指数 Pielou evenness index | 0.82 | 0.484 | 10.07 | 0.002 | 1.56 | 0.200 |
图1 贵州4个国家级自然保护区内外外来入侵草本植物多样性指数(平均值 ± 标准误)。不同小写字母表示差异显著(P < 0.05)。
Fig. 1 Diversity index of invasive herbs inside and outside the four national nature reserves in Guizhou (mean ± SE). Different lowercase letters represent significant differences (P < 0.05).
图2 贵州4个国家级自然保护区内外外来入侵草本植物组成非度量多维标度分析(nMDS)结果
Fig. 2 Non-metric multidimensional scaling analysis (nMDS) ordination for composition of invasive alien herbs inside and outside the four national nature reserves in Guizhou
图3 贵州4个国家级自然保护区内外来入侵植物影响因素的冗余分析(RDA)排序图
Fig. 3 Redundancy analysis (RDA) of influencing factors on invasive alien plants inside the four national nature reserves in Guizhou
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