广东三水云东海国家湿地公园鸟类多样性初步研究

doi:10.16258/j.cnki.1674-5906.2021.11.004

生态环境学报 ›› 2021, Vol. 30 ›› Issue (11): 2142-2149.DOI: 10.16258/j.cnki.1674-5906.2021.11.004

所属专题：生物多样性专题汇编

广东三水云东海国家湿地公园鸟类多样性初步研究

佟富春¹(), 邓适彦¹, 黄子峻¹^,², 何欣瞳¹, 莫晓东¹, 邓露茜¹, 李涓¹, 任雅文¹, 肖以华²^,^*()

1.华南农业大学林学与风景园林学院,广东广州 510642
2.中国林业科学研究院热带林业研究所,广东广州 510520

收稿日期:2021-03-26 出版日期:2021-11-18 发布日期:2021-12-29
通讯作者: * 肖以华,男,副研究员,从事城市森林研究。E-mail: jxxiaoyihua@126.com
* 肖以华,男,副研究员,从事城市森林研究。E-mail: jxxiaoyihua@126.com
作者简介:佟富春（1973年生）,女（满族）,副教授,博士,从事野生动物研究。E-mail: fuchuntong@scau.edu.cn
基金资助:
国家科技支撑计划(2015BAD07B06-8);华南农业大学大学生科技创新项目(S202010564118)

Preliminary Study of Avian Diversity in Yundonghai National Wetland Park of Sanshui, Guangdong Province

TONG Fuchun¹(), DENG Shiyan¹, HUANG Zijun¹^,², HE Xintong¹, MO Xiaodong¹, DENG Luxi¹, LI Juan¹, REN Yawen¹, XIAO Yihua²^,^*()

1. College of Forestry and Landscape Architecture, South China Agricultural University, Guangzhou 510642, China
2. Research Institute of Tropical Forestry, Chinese Academy of Forestry, Guangzhou 510520, China

Received:2021-03-26 Online:2021-11-18 Published:2021-12-29

摘要/Abstract

摘要：

湿地是水陆相互作用形成的独特生态系统,是野生鸟类栖息、繁殖等活动的重要场所,在鸟类迁徙中具有非常重要的作用。但随着城市化进程的加速,湿地面积的退化和丧失,严重影响了鸟类栖息活动。在此背景下,开展云东海国家级湿地公园鸟类多样性调查,对鸟类尤其是候鸟及其停歇地和迁徙地的科学保护具有重要意义。2020年1—12月,采用样线法对广东三水云东海国家湿地公园内村庄和鱼塘区、稻田区、滩涂湿地和湖心岛区、芦苇丛区4种生境中的鸟类进行逐月调查,分析其群落结构和多样性及动态规律。（1）共记录到鸟类72种,隶属于12目32科56属。其中,国家一级重点保护鸟类1种,国家二级重点保护鸟类7种,IUCN极危（CR）物种1种,附录Ⅱ物种5种。在72种鸟类中,优势种2种,常见种19种。以雀形目,留鸟和食虫鸟类种数最多,分别为42种、39种和45种。（2）不同生境中的鸟类种数、数量和生物量具有显著差异：鸟类种数从多到少依次为滩涂湿地和湖心岛区、稻田区、村庄和鱼塘区、芦苇丛区（P<0.01）;鸟类数量从多到少依次为稻田区、滩涂湿地和湖心岛区、村庄和鱼塘区、芦苇丛区（P<0.05）;鸟类生物量从多到少依次为滩涂湿地和湖心岛区、稻田区、芦苇丛区、村庄和鱼塘区（P<0.01）。（3）在不同季节中,鸟类种类从多到少依次为冬季、秋季、春季、夏季,鸟类数量从多到少依次为春季、冬季、秋季、夏季。鸟类生物量从高到低依次为春季、秋季、夏季、冬季。（4）滩涂湿地和湖心岛区的Shannon-Wiener指数、Pielou指数和Simpson指数均为最高,稻田区最低。滩涂湿地和湖心岛区的Margalef指数最高,村庄和鱼塘区最低;冬季的Shannon-Wiener指数和Margalef指数最高,夏季的最低。结果表明,云东海国家湿地公园鸟类资源丰富,在保护候鸟和维持鸟类多样性方面发挥着重要生态作用。

关键词: 鸟类, 多样性, 生境, 季节, 保护, 云东海国家湿地公园

Abstract:

Wetland is a unique natural complex formed by interaction of land and water, which is an important habitat for perching and breeding to wild birds. Moreover, it plays an overwhelmingly crucial function for birds’ migration. However, due to the irrational exploitation under background of urbanization, the loss and degradation of wetland area are fast. Therefore, the investigation of bird diversity has great significance for scientific preservation of birds in Yundonghai National Wetland Park, especially for migratory birds and their rest, breeding and food. The avian diversity in different habitats, namely villages and fish ponds, paddy fields, tidal flat wetlands and lake island, reeds area were monthly investigated from January 2020 to December 2020 by line transects. The dynamics of bird community structure and diversity were also analyzed. The findings are as the followings: (1) A list of 72 bird species containing 12 orders, 32 families and 56 orders of the wetland park was made. Among these,1 species of national class I and 7 species of class II in the List of Key Protected Wild Animals in China, respectively. One critically endangered species (CR) belongs to the IUCN and 5 species were in the Appendices II. Among the 72 bird species, 2 species and 19 species were the dominant and common species, respectively. Most birds belong to Passeriformes, resident birds and insectivorous birds, with 42, 39 and 45 species, respectively. (2) There were significant differences among bird species, quantity, and biomass in different habitats. The bird species was shown in tidal flat wetlands and lake island>paddy>villages and fish ponds>reeds (P<0.01). The bird population was presented in the order of paddy>tidal flat wetlands and lake island>villages and fish ponds>reeds (P<0.05). However, the biomass of birds was demonstrated in tidal flat wetlands and lake island>paddy>villages and fish ponds> reeds (P< 0.01). (3) There were significant differences in bird species, quantity and biomass among different seasons. The declining trends of bird species, quantity and biomass were in the orders of winter>fall>spring>summer, spring>winter>fall>summer, and spring>fall>summer>winter, respectively. (4) The Shannon Wiener index, Pielou evenness index and Simpson index were higher in the tidal flat wetlands than the other habitats, but the lowest in the paddy. The Margalef index was the highest in the tidal flat wetlands and lake island, and the lowest in the Villages and fish ponds. The Shannon Wiener index and Margalef index were the highest in the winter, and the lowest in the summer. However, the Pielou evenness index was the highest in the spring, and the lowest in the winter. The results manifested that Yundonghai National Wetland Park was rich in bird resources and played an important role in the ecological protection of migratory birds and the maintenance of bird diversity.

Key words: birds, diversity, habitat, season, preservation, Yundonghai National Wetland Park

中图分类号:

Q959.7
X176

佟富春, 邓适彦, 黄子峻, 何欣瞳, 莫晓东, 邓露茜, 李涓, 任雅文, 肖以华. 广东三水云东海国家湿地公园鸟类多样性初步研究[J]. 生态环境学报, 2021, 30(11): 2142-2149.

TONG Fuchun, DENG Shiyan, HUANG Zijun, HE Xintong, MO Xiaodong, DENG Luxi, LI Juan, REN Yawen, XIAO Yihua. Preliminary Study of Avian Diversity in Yundonghai National Wetland Park of Sanshui, Guangdong Province[J]. Ecology and Environment, 2021, 30(11): 2142-2149.

图/表 7

参考文献 30

[1]	BLUMSTEIN D T, 2006. Developing an evolutionary ecology of fear: How life history and natural history traits affect disturbance tolerance in birds[J]. Animal Behaviour, 71(2): 389-399.
[2]	CHEN A, SUI X, WANG D S, et al., 2016. Landscape and avifauna changes as an indicator of Yellow River Delta Wetland restoration[J]. Ecological Engineering, 86: 162-173.
[3]	CHI Y, SHI H H, ZHENG W, et al., 2017. Archipelago bird habitat suitability evaluation based on a model of form-structure-function-disturbance[J]. Journal of Coastal Conservation, 21(4): 473-488.
[4]	LIU W W, GUO Z L, JIANG B, et al., 2020. Improving wetland ecosystem health in China[J]. Ecological Indicators, DOI: 10.1016/j.ecolind. 2020.106184.
[5]	SICA Y V, QUINTANA R D, BERNARDOS J N, et al., 2020. Wetland Bird Response to Habitat Composition and Configuration at Multiple Spatial Scales[J]. Wetlands, 40(6): 2513-2525.
[6]	WU T, PERRINGS C, SHANG C W, et al., 2020. Protection of wetlands as a strategy for reducing the spread of avian influenza from migratory waterfowl[J]. Ambio, 49(4): 939-949.
[7]	XU Y J, SI Y L, WANG Y Y, et al., 2019. Loss of functional connectivity in migration networks induces population decline in migratory birds[J]. Ecological Applications, 29(7): e1960.
[8]	ZHANG W Y, LI X H, YU L, et al., 2018. Multi-scale habitat selection by two declining East Asian waterfowl species at their core spring stopover area[J]. Ecological Indicators, 87: 127-135.
[9]	弓慧琼, 2020. 太原市汾河湿地鸟类多样性及其生境改造初探[D]. 太原: 山西大学: 93.
	GONG H Q, 2020. A Preliminary Survey on Bird Diversity and Habitat Renovation of Fenhe Wetland in Taiyuan City[D]. Taiyuan: Shanxi University: 93.
[10]	韩春荣, 刘培中, 雷光春, 等, 2020. 内蒙古龙游湾国家湿地公园鸟类动态变化及空间分布格局[J]. 湿地科学与管理, 16(4): 58-61.
	HAN C R, LIU P Z, LEI G C, et al., 2020. The Dynamic Change and Spatial Distribution Pattern of Birds in Longyouwan National Wetland Park in Inner Mongolia[J]. Wetland Science & Management, 16(4): 58-61.
[11]	胡喻华, 张春霞, 华国栋, 等, 2020. 广东省湿地的植物多样性研究[J]. 林业与环境科学, 36(5): 79-83.
	HU Y H, ZHANG C X, HUA G D, et al., 2020. Diversity on Wetland Plants in Guangdong[J]. Forestry and Environmental Science, 36(5): 79-83.
[12]	黄帅, 龚大洁, 李隆, 等, 2020. 民勤石羊河国家湿地公园鸟类多样性调查及分析[J]. 干旱区资源与环境, 34(2): 168-174.
	HUANG S, GONG D J, LI L, et al., 2020. Investigation and analysis of bird diversity in Shiyanghe national wetland park, Minqin[J]. Journal of Arid Land Resources and Environment, 34(2): 168-174.
[13]	季芳, 孙红梅, 袁倩敏, 等, 2016. 中山市风水林生态条件对鸟类多样性的生态影响及保护作用[J]. 生态环境学报, 25(11): 1871-1878.
	JI F, SUN H M, YUAN Q M, et al., 2016. Ecological and conservational effects of Fengshui Woods on avian diversity in Zhongshan, China[J]. Ecology and Environmental Sciences, 25(11): 1871-1878.
[14]	季缘, 2020. 广州海珠国家湿地公园二期水鸟栖息地改造设计研究[D]. 广州: 华南理工大学: 149.
	JI Y, 2020. Guangzhou Haizhu National Wetland Park Phase II Waterbird Habitat Restoration Design Research[D]. Guangzhou: South China University of Technology: 149.
[15]	孔颖, 2020. 我国鸟类迁徙路线上的湿地资源现状及保护对策[J]. 环境与发展, 32(3): 201-202, 207.
	KONG Y, 2020. The status and conservation strategy for our wetland resources in the bird’s migration routes of China[J]. Environment and Development, 32(3): 201-202, 207.
[16]	雷瑛, 李文飞, 刘思晨, 等, 2019. 佛山市近50年降雨的时空变化特征[J]. 广东气象, 41(3): 10-13.
	LEI Y, LI W F, LIU S C, et al., 2019. Characteristics of spatiotemporal variations of precipitation of Foshan over the past 50 years[J]. Guangdong Meteorology, 41(3): 10-13.
[17]	李凡, 李森, 罗平, 等, 2005. 三水云东海湿地的变迁及其保护利用[J]. 热带地理, 25(2): 146-150.
	LI F, LI S, LUO P, et al., 2005. The changes of the Yundonghai wetland in Sanshui and its protection and utilization[J]. Tropical Geography, 25(2): 146-150.
[18]	刘晶, 牛俊英, 邹业爱, 等, 2015. 上海浦东东滩鸟类栖息地生态修复区的水鸟群落变化[J]. 长江流域资源与环境, 24(2): 219-226.
	LIU J, NIU J Y, ZOU Y A, et al., 2015. Changes in the waterbird community of the ecological restored wetlands in Pudong Dongtan, Shanghai[J]. Resources and Environment in the Yangtze Basin, 24(2): 219-226.
[19]	刘阳, 陈水华, 2021. 中国鸟类观察手册[M]. 长沙: 湖南科学技术出版社: 686.
	LIU Y, CHEN S H, 2021. The CNG Field Guide to the Birds of China[M]. Changsha: Hunan Science& Technology Press: 686.
[20]	刘钊, 彭秋燕, 杨倩梨, 2020. 广东中山翠亨国家湿地公园鸟类群落多样性分析[J]. 热带林业, 48(2): 42-47.
	LIU Z, PENG Q Y, YANG Q L, 2020. Bird community diversity in Cuiheng National Wetland Park of Zhongshan City, Guangdong Province, China[J]. Tropical Forestry, 48(2): 42-47.
[21]	罗祖奎, 李扬, 徐曦, 2021. 鸟类群落结构及分布研究--以贵阳市观山湖区为例[J]. 河南师范大学学报 (自然科学版), 49(5): 104-111.
	LUO Z K, LI Y, XU X, 2021. Study on the bird community structure and distribution in Guanshanhu District of Guiyang City[J]. Journal of Henan Normal University (Natural Science Edition), 49(5): 104-111.
[22]	马嘉, 高宇, 陈茜, 等, 2019. 城市湿地公园的鸟类栖息地生境营造策略研究--以北京莲石湖公园为例[J]. 中国城市林业, 17(5): 69-73.
	MA J, GAO Y, CHEN Q, et al., 2019. Ecological design strategy of bird habitat in urban wetland park: A case study of Beijing Lianshi Lake Park[J]. Journal of Chinese Urban Forestry, 17(5): 69-73.
[23]	唐虹, 冯永军, 刘金成, 等, 2018. 广州海珠湿地生态修复过程中的鸟类多样性研究[J]. 野生动物学报, 39(1): 86-91.
	TANG H, FENG Y J, LIU J C, et al., 2018. Bird diversity during city ecological restoration at Haizhu Wetland, Guangzhou[J]. Chinese Journal of Wildlife, 39(1): 86-91.
[24]	王伟恒, 邹发生, 彭逸生, 等, 2019. 广东星湖国家湿地公园鸟类群落及其栖息地监测调查[J]. 地球 (8): 105-108.
	WANG W H, ZOU F S, PENG Y S, et al., 2019. Bird community and habitat investigating in Xinghu National Park, Guangdong province[J]. Earth (8): 105-108.
[25]	王彦平, 宋云枫, 钟雨倩, 等, 2021. 中国鸟类的生活史和生态学特征数据集[J]. 生物多样性, 29(9): 1149-1153.
	WANG Y P, SONG Y F, ZHONG Y X, et al., 2021. Adataset on the life-history and ecological traits of Chinese birds[J]. Biodiversity Science, 29(9): 1149-1153.
[26]	杨勇, 温俊宝, 胡德夫, 2011. 鸟类栖息地研究进展[J]. 林业科学, 47(11): 172-180.
	YANG Y, WEN J B, HU D F, 2011. A Review on Avian Habitat Research[J]. Scientia Silvae Sinicae, 47(11): 172-180.
[27]	尹新新, 田学根, 王定跃, 等, 2013. 深圳市公园绿地植物群落多样性特征分析[J]. 湖北民族学院学报 (自然科学版), 31(4): 366-369.
	YIN X X, TIAN X G, WANG D Y, et al., 2013. Diversity Analysis on the Plant Community Characteristics of Urban Park in Shenzhen[J]. Journal of Hubei Minzu University (Nature Science Edition), 31(4): 366-369.
[28]	张鹏骞, 张志明, 白加德, 等, 2020. 北京南海子麋鹿苑鸟类多样性研究[J]. 生态学报, 40(5): 1740-1749.
	ZHANG P Q, ZHANG Z M, BAI J D, et al., 2020. Bird diversity in Nan-Haizi Milu Park of Beijing, China[J]. Acta Ecologica Sinica, 40(5): 1740-1749.
[29]	张强, 马克明, 李金亚, 等, 2017. 不同尺度下停歇点湿地对迁徙水鸟的影响研究综述[J]. 生态学报, 37(8): 2520-2529.
	ZHANG Q, MA K M, LI J Y, et al., 2017. The effect of stopover wetlands on migratory waterbirds at different scales: A review[J]. Acta Ecologica Sinica, 37(8): 2520-2529.
[30]	张荣祖, 1999. 中国动物地理[M]. 北京: 科学出版社: 201.
	ZHANG R Z, 1999. The zoogeography of China[M]. Science Press: 201.

编号 No.	生境 Habitat	面积 Area/hm²	样线长度 Length/km	起点坐标 Coordinates of the starting point	终点坐标 Coordinates of the end point
A	村庄和鱼塘区 Villages and fishponds	44.48	3.942	112°54′19.7″E, 23°14′21.5″N	112°53′29″E, 22°13′22.5″N
B	稻田区 Paddy fields	36.90	2.468	112°53′28.8″E, 22°13′22.3″N	112°53′11.9″E, 23°12′56.1″N
C	滩涂湿地和湖心岛区 Tidalflat wetlands and Lake island	47.39	3.990	112°52′54.4″E, 23°13′3.2″N	112°54′21″E, 23°13′27.1″N
D	芦苇丛区 Reeds	29.18	2.185	112°54′18″E, 23°13′27″N	112°54′19.7″E, 23°14′21.5″N

编号 No.	生境 Habitat	面积 Area/hm²	样线长度 Length/km	起点坐标 Coordinates of the starting point	终点坐标 Coordinates of the end point
A	村庄和鱼塘区 Villages and fishponds	44.48	3.942	112°54′19.7″E, 23°14′21.5″N	112°53′29″E, 22°13′22.5″N
B	稻田区 Paddy fields	36.90	2.468	112°53′28.8″E, 22°13′22.3″N	112°53′11.9″E, 23°12′56.1″N
C	滩涂湿地和湖心岛区 Tidalflat wetlands and Lake island	47.39	3.990	112°52′54.4″E, 23°13′3.2″N	112°54′21″E, 23°13′27.1″N
D	芦苇丛区 Reeds	29.18	2.185	112°54′18″E, 23°13′27″N	112°54′19.7″E, 23°14′21.5″N

目 Order	科 Family	属 Genus	种 Species	占种数比Percentage/%
䴙䴘目 Podicipediformes	1	2	2	2.78
鲣鸟目 Suliformes	1	1	1	1.39
鹳形目 Ciconiiformes	1	6	9	12.50
鹤形目 Gruiformes	1	2	2	2.78
鸻形目 Charadriiformes	3	3	4	5.56
鸽形目 Columbiformes	1	1	1	1.39
佛法僧目 Coraciformes	1	1	1	1.39
鸮形目 Strigiformes	1	1	1	1.39
雨燕目 Apodiformes	1	1	1	1.39
鹰形目 Accipitriformes	1	3	3	4.17
隼形目 Falconiformes	1	1	1	1.39
鹃形目 Cuculiformes	1	3	4	5.56
雀形目 Passeriformes	18	31	42	58.33

目 Order	科 Family	属 Genus	种 Species	占种数比Percentage/%
䴙䴘目 Podicipediformes	1	2	2	2.78
鲣鸟目 Suliformes	1	1	1	1.39
鹳形目 Ciconiiformes	1	6	9	12.50
鹤形目 Gruiformes	1	2	2	2.78
鸻形目 Charadriiformes	3	3	4	5.56
鸽形目 Columbiformes	1	1	1	1.39
佛法僧目 Coraciformes	1	1	1	1.39
鸮形目 Strigiformes	1	1	1	1.39
雨燕目 Apodiformes	1	1	1	1.39
鹰形目 Accipitriformes	1	3	3	4.17
隼形目 Falconiformes	1	1	1	1.39
鹃形目 Cuculiformes	1	3	4	5.56
雀形目 Passeriformes	18	31	42	58.33

指数 Index	总 Total	春 Spring	夏 Summer	秋 Fall	冬 Winter	A	B	C	D
H′	3.22	3.08	2.93	3.05	3.09	2.78	2.21	3.11	2.71
J′	0.52	0.58	0.57	0.54	0.52	0.53	0.41	0.53	0.52
D	0.94	0.94	0.93	0.93	0.92	0.90	0.81	0.94	0.91
M	7.72	4.35	3.81	5.44	6.53	4.13	4.46	6.09	3.81

广东三水云东海国家湿地公园鸟类多样性初步研究

Preliminary Study of Avian Diversity in Yundonghai National Wetland Park of Sanshui, Guangdong Province

RichHTML

PDF

可视化

摘要/Abstract

引用本文

使用本文

图/表 7

参考文献 30

相关文章 15

编辑推荐

Metrics

本文评价

湿地公园 Wetland Park	面积 Area/hm²	目 Order	科 Family	种 Species	调查时间 Survey time	G	来源 Source
云东海国家湿地公园 Yundonghai National Wetland Park	401.97	13	32	72	一年	12.01	本次调查
肇庆星湖国家湿地公园 ZhaoqingXinghu Wetland park	935.40	13	30	60	8个月	8.77	王伟恒等, 2019 (Wang et al., 2019)
海珠国家湿地公园 Haizhu National Wetland Park	869.00	13	31	77	一年以上	11.37	唐虹等, 2018 (Tang et al., 2018)
中山翠亨国家湿地公园 Cuiheng National Wetland Park	625.60	12	36	95	一年以上	14.76	刘钊等, 2020 (Liu et al., 2020)

[1]	李海鹏, 黄月华, 孙晓东, 曹启民, 符芳兴, 孙楚涵. 海南农田不同质地砖红壤及其细菌群落与番茄青枯病发生的关联分析[J]. 生态环境学报, 2023, 32(6): 1062-1069.
[2]	陈俊芳, 吴宪, 刘啸林, 刘娟, 杨佳绒, 刘宇. 不同土壤水分下元素化学计量对微生物多样性的塑造特征[J]. 生态环境学报, 2023, 32(5): 898-909.
[3]	姜永伟, 丁振军, 袁俊斌, 张峥, 李杨, 问青春, 王业耀, 金小伟. 辽宁省主要河流底栖动物群落结构及水质评价研究[J]. 生态环境学报, 2023, 32(5): 969-979.
[4]	李阳, 侯志勇, 陈薇, 于晓英, 谢永宏, 黄鑫, 谭佩阳, 李继承, 黎尚林, 杨辉. 大围山高山湿地植物多样性与区系组成研究[J]. 生态环境学报, 2023, 32(4): 643-650.
[5]	许静, 廖星凯, 甘崎旭, 周茅先. 基于MSPA与电路理论的黄河流域甘肃段生态安全格局构建[J]. 生态环境学报, 2023, 32(4): 805-813.
[6]	李善家, 王兴敏, 刘海锋, 孙梦格, 雷雨昕. 河西走廊荒漠植物多样性及其对环境因子的响应[J]. 生态环境学报, 2023, 32(3): 429-438.
[7]	张怀成, 韩红, 王在峰, 韩立钊, 刘克, 张桂芹, 范晶, 魏小锋. 济南市城市扬尘的微观形貌和化学组分特征分析[J]. 生态环境学报, 2023, 32(3): 545-555.
[8]	郝金虎, 韦玮, 李胜男, 马牧源, 李肖夏, 杨洪国, 姜琦宇, 柴沛东. 基于GEE平台的京津冀长时序水体时空格局及其影响因素[J]. 生态环境学报, 2023, 32(3): 556-566.
[9]	宋志斌, 周佳诚, 谭路, 唐涛. 高原河流着生藻类群落沿海拔梯度的变化特征--以西藏黑曲、雪曲为例[J]. 生态环境学报, 2023, 32(2): 274-282.
[10]	周世强, Vanessa HULL, 张晋东, 刘巅, 谢浩, 黄金燕, 张和民. 野生大熊猫与放牧家畜利用生境的特征比较[J]. 生态环境学报, 2023, 32(2): 309-319.
[11]	李少宁, 李婷婷, 陶雪莹, 赵娜, 徐晓天, 鲁绍伟. 4种落叶树种释放有益挥发性有机物的比较研究[J]. 生态环境学报, 2023, 32(1): 123-128.
[12]	张立进, 杜虎, 曾馥平, 黄国勤, 宋敏, 宋同清. 喀斯特峰丛洼地植被恢复过程中生产力与多样性关系探讨[J]. 生态环境学报, 2023, 32(1): 26-35.
[13]	李萍, 白小明, 陈鑫, 李娟霞, 冉福, 陈辉, 杨小妮, 康瑞卿. 白三叶入侵对禾本科草坪土壤特性和植物群落的影响[J]. 生态环境学报, 2023, 32(1): 70-79.
[14]	王洁, 单燕, 马兰, 宋延静, 王向誉. 秸秆/生物质炭协同还田措施对黄河三角洲盐碱土壤的改良效果研究[J]. 生态环境学报, 2023, 32(1): 90-98.
[15]	张林, 周飘, 齐实, 张岱, 伍冰晨, 崔冉冉. 侧柏人工林林分空间结构对林下草本多样性的差异性影响及其关联度[J]. 生态环境学报, 2022, 31(9): 1794-1801.

生境 Habitat	B	C	D
A	0.62	0.56	0.85
B		0.67	0.90
C			0.71

生境 Habitat	B	C	D
A	0.62	0.56	0.85
B		0.67	0.90
C			0.71