生物多样性 ›› 2015, Vol. 23 ›› Issue (4): 471-478. DOI: 10.17520/biods.2014251 cstr: 32101.14.biods.2014251
李有志1,2,3, 崔丽娟1,3,,A;*(), 潘旭1,3, 宁宇1,3, 李伟1,3, 康晓明1,3, 李凯1,3, 孙宝娣1,3, 于菁菁1,3
收稿日期:
2014-12-03
接受日期:
2015-05-19
出版日期:
2015-07-20
发布日期:
2015-08-03
通讯作者:
崔丽娟
作者简介:
# 共同第一作者
基金资助:
Youzhi Li1,2,3, Lijuan Cui1,3,*(), Xu Pan1,3, Yu Ning1,3, Wei Li1,3, Xiaoming Kang1,3, Kai Li1,3, Baodi Sun1,3, Jingjing Yu1,3
Received:
2014-12-03
Accepted:
2015-05-19
Online:
2015-07-20
Published:
2015-08-03
Contact:
Cui Lijuan
About author:
# Co-first authors
摘要:
辽河口湿地是我国典型的滨海湿地, 在过去几十年受人为过度干扰, 植被变化明显。本研究拟通过野外实地调查揭示辽河口湿地植物多样性及功能型的空间格局。结果表明, 潮上带的物种丰富度和Shannon-Wiener指数均高于潮间带。与潮上带相比, 潮间带的盐生植物与湿生植物比例较高, 而中性植物、甜土植物、中生植物与旱生植物的比例较低。物种丰富度、Shannon-Wiener指数以及中性植物、甜土植物、中生植物、旱生植物的比例均随着与海岸线距离的增加而增加, 盐生植物、湿生植物比例则与之相反。对所调查样地与植物物种的主成分分析(PCA)表明, 潮上带主要为芦苇(Phragmites australis)、刺儿菜(Cirsium setosum)、山莴苣(Lagedium sibiricum)等中性和甜土植物, 潮间带为盐地碱蓬(Suaeda salsa)、扁秆藨草(Scirpus planiculmis)、水烛(Typha angustifolia)等盐生植物。可见, 盐度与水位是决定辽河口湿地植物多样性及物种功能型的关键生态因子。
李有志, 崔丽娟, 潘旭, 宁宇, 李伟, 康晓明, 李凯, 孙宝娣, 于菁菁 (2015) 辽河口湿地植物多样性及物种功能型空间分布格局. 生物多样性, 23, 471-478. DOI: 10.17520/biods.2014251.
Youzhi Li, Lijuan Cui, Xu Pan, Yu Ning, Wei Li, Xiaoming Kang, Kai Li, Baodi Sun, Jingjing Yu (2015) Spatial distribution of plant diversity and functional groups in the Liaohe estuary. Biodiversity Science, 23, 471-478. DOI: 10.17520/biods.2014251.
潮上带 Supralittoral zone | 潮间带 Intertidal zone | 自由度 df | F | ||
---|---|---|---|---|---|
多样性指数 Diversity indices | 物种丰富度 Species richness | 2.73 ± 0.17 | 1.25 ± 0.10 | 21 | 61.11*** |
Shannon-Wiener指数 Shannon-Wiener index | 0.58 ± 0.04 | 0.04 ± 0.02 | 21 | 165.59*** | |
盐分功能型比例 Percentage of functional types by salt (%) | 盐生植物 Halophyte | 32.00 ± 2.23 | 84.10 ± 8.30 | 21 | 23.14*** |
中性植物 Neutral plants | 59.25 ± 3.50 | 15.13 ± 8.38 | 21 | 15.12** | |
甜土植物 Glycophyte | 8.75 ± 2.51 | 0.77 ± 0.76 | 21 | 13.42** | |
水分功能型比例 Percentage of functional types by water (%) | 湿生植物 Hygrophyte | 64.29 ± 4.70 | 99.23 ± 1.04 | 21 | 81.89*** |
中生植物 Mesophyte | 22.50 ± 5.21 | 0.77 ± 0.77 | 21 | 27.52*** | |
旱生植物 Xerophyte | 13.21 ± 3.49 | 0 | 21 | 24.04*** |
表1 辽河口湿地植物多样性及物种功能型方差分析(平均值±标准误)
Table 1 ANOVA of plant diversity and species functional types in Liaohe estuary wetlands (mean ± SE)
潮上带 Supralittoral zone | 潮间带 Intertidal zone | 自由度 df | F | ||
---|---|---|---|---|---|
多样性指数 Diversity indices | 物种丰富度 Species richness | 2.73 ± 0.17 | 1.25 ± 0.10 | 21 | 61.11*** |
Shannon-Wiener指数 Shannon-Wiener index | 0.58 ± 0.04 | 0.04 ± 0.02 | 21 | 165.59*** | |
盐分功能型比例 Percentage of functional types by salt (%) | 盐生植物 Halophyte | 32.00 ± 2.23 | 84.10 ± 8.30 | 21 | 23.14*** |
中性植物 Neutral plants | 59.25 ± 3.50 | 15.13 ± 8.38 | 21 | 15.12** | |
甜土植物 Glycophyte | 8.75 ± 2.51 | 0.77 ± 0.76 | 21 | 13.42** | |
水分功能型比例 Percentage of functional types by water (%) | 湿生植物 Hygrophyte | 64.29 ± 4.70 | 99.23 ± 1.04 | 21 | 81.89*** |
中生植物 Mesophyte | 22.50 ± 5.21 | 0.77 ± 0.77 | 21 | 27.52*** | |
旱生植物 Xerophyte | 13.21 ± 3.49 | 0 | 21 | 24.04*** |
图4 样方与植物物种的主成分分析。图中数字1-61表示野外调查样方。s1, 芦苇; s2, 刺儿菜; s3, 山莴苣; s4, 野大豆; s5, 碱蓬; s6, 地肤; s7, 尖头叶藜; s8, 鹅绒藤; s9, 扁杆藨草; s10, 白茅; s11, 罗布麻; s12, 木贼; s13, 拂子茅; s14, 黄花蒿; s15, 西伯利亚蓼; s16, 藜; s17, 盐地碱蓬; s18, 歧茎蒿; s19, 小果酸模; s20, 水烛; s21, 稗; s22, 野青茅; s23, 糙叶薹草。
Fig. 4 PCA analysis between investigation plots and plant species. The numbers of 1-61 in figure indicated field plots. s1, Phragmites australis; s2, Cirsium setosum; s3, Lagedium sibiricum; s4, Glycine soja; s5, Suaeda glauca; s6, Kochia scoparia; s7, Chenopodium acuminatum; s8, Cynanchum chinense; s9, Scirpus planiculmis; s10, Imperata cylindrica; s11, Apocynum venetum; s12, Equisetum hyemale; s13, Calamagrostis epigeios; s14, Artemisia annua; s15, Polygonum sibiricum; s16, Chenopodium album; s17, Suaeda salsa; s18, Artemisia igniaria; s19, Rumex microcarpus; s20, Typha angustifolia; s21, Echinochloa crusgalli; s22, Deyeuxia arundinacea; s23, Carex scabrifolia.
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