珠江河口区大型底栖动物群落结构

doi:10.17520/biods.2018321

生物多样性 ›› 2019, Vol. 27 ›› Issue (10): 1112-1121. DOI: 10.17520/biods.2018321

• 研究报告:动物多样性 • 上一篇下一篇

珠江河口区大型底栖动物群落结构

周细平^1,^2,^*(),李贞¹,吴培芳¹,吴茜¹,陈逸欣¹,刘康格¹,刘东艳³,王玉珏⁴,王跃启⁴

1 厦门大学嘉庚学院环境科学与工程学院, 福建漳州 363105
2 厦门大学嘉庚学院河口生态安全与环境健康福建省高校重点实验室, 福建漳州 363105
3 华东师范大学河口与海岸学国家重点实验室, 上海 200062
4 中国科学院海岸带环境过程与生态修复重点实验室, 山东烟台 264003

收稿日期:2019-09-20 接受日期:2019-10-13 出版日期:2019-10-20 发布日期:2019-10-20
通讯作者: 周细平
基金资助:
国家自然科学基金(41606119);福建省自然科学基金(2017J05068);福建省高等学校新世纪优秀人才支持计划(闽教科〔2017〕52号)

The structure of macrobenthic community in Pearl River Estuary

Zhou Xiping^1,^2,^*(),Li Zhen¹,Wu Peifang¹,Wu Xi¹,Chen Yixin¹,Liu Kangge¹,Liu Dongyan³,Wang Yujue⁴,Wang Yueqi⁴

1 School of Environmental Science and Engineering, Tan Kah Kee College, Xiamen University, Zhangzhou, Fujian 363105
2 Key Laboratory of Estuarine Ecological Security and Environmental Health, Tan Kah Kee College, Xiamen University, Zhangzhou, Fujian 363105
3 State Key Laboratory of Estuarine and Coastal Research, East China Normal University, Shanghai 200062
4 Key Laboratory of Coastal Environmental Processes and Ecological Remediation, Chinese Academy of Sciences, Yantai, Shandong 264003

Received:2019-09-20 Accepted:2019-10-13 Online:2019-10-20 Published:2019-10-20
Contact: Zhou Xiping

摘要/Abstract

摘要：

河口区大型底栖动物具有的重要群落特征往往可以反映群落所经历的环境污染。为更好地了解珠江河口区大型底栖动物群落结构, 作者于2014年11月至2015年8月进行了4个季度的大型底栖动物调查, 并利用PRIMER 6.0软件进行群落生物多样性指数计算、群落等级聚类(Cluster)和非度量多维标度排序(nMDS)分析。研究结果显示: 珠江河口区共获得大型底栖动物52种, 优势种包括光滑河篮蛤(Potamocorbula laevis)、中国绿螂(Glaucomya chinensis)、焦河篮蛤(Potamocorbula ustulata)和羽须鳃沙蚕(Dendroneris pinnaticirrus)。大型底栖动物年平均密度为269.3 ind./m ², 年平均生物量为129.61 g/m ²。12个站次的丰富度指数(D)、均匀度指数(J')和Shannon-Wiener多样性指数(H')平均值分别为1.81 ± 1.38、0.50 ± 0.27和1.60 ± 1.13。该结果显示除P01断面的秋季和冬季环境质量为优良外, 其他站位在不同季度都显示出轻度到重度的污染。Cluster聚类分析和nMDS标序结果表明, P01断面与P02和P03断面群落相似度较低, 与断面地理分布情况一致; P02断面和P03断面存在交叉聚集, 群落相似度较高。结合环境因子结果可知, 沉积物理化因子与群落分布特征相关性较大, 其中最能解释珠江河口区群落多样性分布特征的环境因子为盐度和pH值。

关键词: 珠江口, 大型底栖动物, 群落结构

Abstract

The macrobenthic communities of estuaries are often indicative of important community traits, such as the environmental pollution a community may experience. To better understand the structure of Pearl River Estuary’s macrobenthic community, macrobenthic species were identified based on investigations carried out from November 2014 to August 2015, and biodiversity analyses were performed. More specifically, biodiversity index calculations, cluster analysis, and nMDS (non-metric MDS) analysis were performed used PRIMER 6.0 software. While 52 macrobenthic species were identified in the Pearl River estuary, the dominant species in this study area were Potamocorbula laevis, Glaucomya chinensis, Potamocorbula ustulata and Dendroneris pinnaticirrus. The annual mean density of macrobenthos in the Pearl River Estuary was 269.3 ind./m ² and the annual mean biomass was 129.61 g/m ². The mean values of richness index (D), evenness index (J') and Shannon-Wiener diversity index (H') of 12 samplings were 1.81 ± 1.38、0.50 ± 0.27 and 1.60 ± 1.13, respectively. The results showed a range of environmental quality from clean to severe pollution, in which only P01 section indicated clean environmental quality in autumn and winter. Cluster and nMDS results revealed that low community similarity were observed among P01 section and P02 together with P03 sections, potentially due to the geographical distribution factors. Additionally, the P02 section and P03 section gathered crosswise with higher community similarity. Our results suggested the combination of environmental factors with physical and chemical sediment factors were significantly correlated with the distribution characteristics of communities. Also to note, water salinity and pH can help explain the biodiversity distribution pattern of the microbenthic community in the Pearl River Estuary.

Key words: Pearl River Estuary, macrobenthos, community structure

周细平,李贞,吴培芳,吴茜,陈逸欣,刘康格,刘东艳,王玉珏,王跃启 (2019) 珠江河口区大型底栖动物群落结构. 生物多样性, 27, 1112-1121. DOI: 10.17520/biods.2018321.

Zhou Xiping,Li Zhen,Wu Peifang,Wu Xi,Chen Yixin,Liu Kangge,Liu Dongyan,Wang Yujue,Wang Yueqi (2019) The structure of macrobenthic community in Pearl River Estuary. Biodiversity Science, 27, 1112-1121. DOI: 10.17520/biods.2018321.

导出引用管理器 EndNote|Ris|BibTeX

链接本文: https://www.biodiversity-science.net/CN/10.17520/biods.2018321

https://www.biodiversity-science.net/CN/Y2019/V27/I10/1112

图/表 10

参考文献 28

[1]	Cai LZ ( 2015) Zoobenthic Ecology in Shenzhen Bay. Xiamen University Press, Xiamen. (in Chinese)
	[ 蔡立哲 ( 2015) 深圳湾底栖动物生态学. 厦门大学出版社, 厦门.]
[2]	Gaston GR, Rakocinski CF, Brown SS, Cleveland CM ( 1998) Trophic function in estuaries: Response of macrobenthos to natural and contaminant gradients. Marine & Freshwater Research, 49, 833-846.
[3]	He GF, Yuan GM, Li FQ ( 2002) Effect of economic development on water quality in Zhujiang Estuary. Marine Environmental Science, 23(4), 50-52. (in Chinese with English abstract)
	[ 何桂芳, 袁国明, 李凤岐 ( 2002) 珠江口沿岸城市经济发展对珠江口水质的影响. 海洋环境科学, 23(4), 50-52.]
[4]	Huang HH, Lin YT, Li CH, Lin Q, Cai WG, Gao DY, Jia XP ( 2002) Ecology study on the benthic animals of Pearl River Estuary. Acta Ecologica Sinica, 22, 603-607. (in Chinese with English abstract)
	[ 黄洪辉, 林燕棠, 李纯厚, 林钦, 蔡文贵, 高东阳, 贾晓平 ( 2002) 珠江口底栖动物生态学研究. 生态学报, 22, 603-607.]
[5]	Huang SF, Liu Y, Li C, Huang JM ( 2011) Influence of reclamation on macrobenthic community in the Pearl River Estuary. Chinese Journal of Applied and Environmental Biology, 17, 499-503. (in Chinese with English abstract)
	[ 黄少峰, 刘玉, 李策, 黄晋沐 ( 2011) 珠江口滩涂围垦对大型底栖动物群落的影响. 应用与环境生物学报, 17, 499-503.]
[6]	Jiang WX, Lai ZN, Peng SY, Gao Y, Yang WL, Pang SX ( 2011) Primary study of macroinvertebrate community structure in the Pearl River Guangzhou portion. Environmental Monitoring in China, 27(5), 69-72. (in Chinese with English abstract)
	[ 蒋万祥, 赖子尼, 彭松耀, 高原, 杨婉玲, 庞世勋 ( 2011) 珠江广州段底栖动物群落结构初步研究. 中国环境监测, 27(5), 69-72.]
[7]	Lai TH, He BY, Huang ZJ, Tang Q, Qin LY, Zhu T, Mo ZN, Liu L, Zhong YX ( 2019) Study on the macrozoobenthic community structure in intertidal zone of Fangchenghe Estuary of Guangxi, China. Journal of Tropical Oceanography, 38(2), 70-80. (in Chinese with English abstract)
	[ 赖廷和, 何斌源, 黄中坚, 汤乔, 覃漉雁, 朱婷, 莫珍妮, 刘俐, 钟云旭 ( 2019) 防城河口湾潮间带大型底栖动物群落结构研究. 热带海洋学报, 38(2), 70-80.]
[8]	Li NC, Liu XS, Xu ZD, Zhao R, Shi HH ( 2015) Biodiversity of macrofauna in the southern waters of Miaodao Archipelago. Biodiversity Science, 23, 41-49. (in Chinese with English abstract)
	[ 李乃成, 刘晓收, 徐兆东, 赵瑞, 石洪华 ( 2015) 庙岛群岛南部海域大型底栖动物多样性. 生物多样性, 23, 41-49.]
[9]	Ma J, Fu RS ( 2010) Progress of ecology research on macrobenthos. Shandong Agricultural Sciences, ( 2), 78-81. (in Chinese with English abstract)
	[ 马骏, 付荣恕 ( 2010) 大型底栖动物生态学研究进展. 山东农业科学, ( 2), 78-81.]
[10]	Mao JX, Yan QL, Wang LJ ( 2011) Changes trend of species number, biomass and density of zoobenthos in typical estuaries of China. Marine Environmental Science, 30, 37-40. (in Chinese with English abstract)
	[ 毛婕昕, 闫启仑, 王立俊 ( 2011) 典型河口底栖动物种类数、生物量及种群密度变化趋势的研究. 海洋环境科学, 30, 37-40.]
[11]	Peng SY, Lai ZN, Mai YZ ( 2019) Distribution of quantity and diversity of macrobenthos in the Pearl River Estuary. Marine Fisheries, 41, 266-277. (in Chinese with English abstract)
	[ 彭松耀, 赖子尼, 麦永湛 ( 2019) 珠江口大型底栖动物数量与生物多样性的分布特征. 海洋渔业, 41, 266-277.]
[12]	Peng SY, Lai ZN, Jiang WX, Gao Y, Pang SX, Yang WL ( 2010) Study on community structure of macrozoobenthos and impact factors in Pearl River estuary. Acta Hydrobiologica Sinica, 34, 1179-1189. (in Chinese with English abstract)
	[ 彭松耀, 赖子尼, 蒋万祥, 高原, 庞世勋, 杨婉玲 ( 2010) 珠江口大型底栖动物的群落结构及影响因子研究. 水生生物学报, 34, 1179-1189.]
[13]	Qi S, Lin MX, Li KH ( 1982) Water pollution assessment of Pearl River, Guangzhou, by using benthic macroinvertebrates. Acta Scientiae Circumstantiae, 2, 181-189. (in Chinese with English abstract)
	[ 杞桑, 林美心, 黎康汉 ( 1982) 用大型底栖动物对珠江广州河段进行污染评价. 环境科学学报, 2, 181-189.]
[14]	Qi S, Lin MX ( 1985) Further assessment of pollution status of Pearl River, Guangzhou, by using benthic macroinvertebrates. Acta Scientiae Circumstantiae, 5, 354-359. (in Chinese with English abstract)
	[ 杞桑, 林美心 ( 1985) 用大型底栖动物再次对珠江广州河段污染的评价. 环境科学学报, 5, 354-359.]
[15]	Qi S, Huang WJ ( 1993) The benthic macroinvertebrate community relating to the water quality in lower Zhujiang (Pearl River). Acta Scientiae Circumstantiae, 13, 80-86. (in Chinese with English abstract)
	[ 杞桑, 黄伟建 ( 1993) 珠江三角洲底栖动物群落与水质关系. 环境科学学报, 13, 80-86.]
[16]	Smith CR, Austen MC, Boucher G, Heip C, Hutchings PA, King GM, Koike I, Lambshead PJD, Snelgrove P ( 2000) Global change and biodiversity of marine sediments: Impacts and linkages across the sediment-water interface. BioScience, 50, 1108-1120.
[17]	Soemodinoto A, Oey BL, Ibkar-Kramadibrata H ( 1995) Effect of salinity decline on macrozoobenthos community of Cibeureum River Estuary, Java, Indonesia. Oceanographic Literature Review, 42, 1116-1120.
[18]	Su BZ, Li WX, Lai ZX ( 1989) Investigation of benthic fauna in the Pearl River system (Guangdong river section). Chinese Journal of Zoology, 24(3), 15-19. (in Chinese)
	[ 苏炳之, 黎伟新, 赖泽兴 ( 1989) 珠江水系(广东江段)底栖动物调查. 动物学杂志, 24(3), 15-19.]
[19]	Taft OW, Haig SM ( 2005) The value of agricultural wetlands as invertebrate resources for wintering shorebirds. Agriculture, Ecosystems and Environment, 110, 249-256.
[20]	Wang D, Lin ZJ, Peng YC, Li TJ, Ma Y ( 2015) Macrobenthos community status of the Pearl River Delta coastal wetland in autumn 2007. Marine Science, 39, 70-78. (in Chinese with English abstract)
	[ 王迪, 林昭进, 彭艳超, 李团结, 马玉 ( 2015) 2007年秋季珠江三角洲典型滨海湿地大型底栖动物群落现状. 海洋科学, 39, 70-78.]
[21]	Wang LR, Zhao HT ( 2000) Common features of the estuarine wetland in China. Marine Science Bulletin, 19(5), 47-54. (in Chinese with English abstract)
	[ 王丽荣, 赵焕庭 ( 2000) 中国河口湿地的一般特点. 海洋通报, 19(5), 47-54.]
[22]	Wang XM, Zhong MJ, Liao WB, Lan CY ( 2003) The sustainable development strategy on resources and environment in Zhujiang Estuary and adjacent islands. Acta Scientiarum Naturalium University Sunyatsen, 42(6), 73-77. (in Chinese with English abstract)
	[ 王晓明, 仲铭锦, 廖文波, 蓝崇钰 ( 2003) 珠江口沿岸地区资源环境及其可持续发展措施. 中山大学学报(自然科学版), 42(6), 73-77.]
[23]	Wang XT, Xie Z, Liu W, Xu S ( 2016) Bioassessment of water quality using benthic macroinvertebrates in major rivers of Pearl River Basin. Water Resources Protection, 32(3), 94-98, 136. (in Chinese with English abstract)
	[ 王旭涛, 谢昭, 刘威, 徐盛 ( 2016) 珠江重要河流底栖动物水质生物学评价. 水资源保护, 32(3), 94-98, 136.]
[24]	Xu ZL, Chen YQ ( 1989) Aggregated intensity of dominant species of zooplankton in autumn in the East China Sea and Yellow Sea. Chinese Journal of Ecology, 8(4), 13-15. (in Chinese with English abstract)
	[ 徐兆礼, 陈亚瞿 ( 1989) 东黄海秋季浮游动物优势种聚集强度与鲐鳍渔场的关系. 生态学杂志, 8(4), 13-15.]
[25]	Yang J, Cai LZ, Liang JY, Zhou XP, Jin L, Chen ZH ( 2007) Quantitative analysis of two new dominant species of macrozoobenthos in Xiamen Harbour, China. Marine Sciences, 31(9), 44-49. (in Chinese with English abstract)
	[ 杨洁, 蔡立哲, 梁俊彦, 周细平, 金亮, 陈志鸿 ( 2007) 厦门海域大型底栖动物两个优势种的发现及其数量分析. 海洋科学, 31(9), 44-49.]
[26]	Ysebaert T, Herman PMJ, Meire P, Craeymeersch J, Verbeek H, Heip CHR ( 2003) Large-scale spatial patterns in estuaries: Estuarine macrobenthic communities in the Schelde Estuary, NW Europe. Estuarine, Coastal and Shelf Science, 57, 335-355.
[27]	Yuan XZ, Lu JJ ( 2002) Ecological characteristics of macrozoobenthic community of tidal flat wetland in the Changjiang Estuary. Resources and Environment in the Yangtze Basin, 11, 414-420. (in Chinese with English abstract)
	[ 袁兴中, 陆健健 ( 2002) 长江口潮滩湿地大型底栖动物群落的生态学特征. 长江流域资源与环境, 11, 414-420.]
[28]	Zhang JH ( 2014) The variation of biodiversity of macrobenthic fauna with salinity and water depth near the Pearl Estuary of the northern South China Sea. Biodiversity Science, 22, 302-310. (in Chinese with English abstract)
	[ 张敬怀 ( 2014) 珠江口及邻近海域大型底栖动物多样性随盐度、水深的变化趋势. 生物多样性, 22, 302-310.]

	P01			P02			P03
	高潮区 High tide	中潮区 Middle tide	低潮区 Low tide	高潮区 High tide	中潮区 Middle tide	低潮区 Low tide	高潮区 High tide	中潮区 Middle tide	低潮区 Low tide
粘土 Clay (%)	2.15	2.79	4.01	1.27	4.85	8.61	1.26	4.25	0.28
粉砂 Silt (%)	18.06	21.65	28.47	15.51	50.95	76.36	18.73	48.59	3.13
极细砂 Sand (%)	79.79	75.56	67.52	83.22	44.20	15.03	80.01	47.16	96.59
总氮 TN (%)	0.23	0.04	–	0.02	0.03	–	0.05	0.05	–
总有机碳 TOC (%)	1.83	0.37	–	0.22	0.21	–	0.60	0.70	–
温度 Temperature (℃)	24.23			24.50			23.87
盐度 Salinity (‰)	10.13			10.43			9.47
pH值	8.07			7.71			7.78

	P01			P02			P03
	高潮区 High tide	中潮区 Middle tide	低潮区 Low tide	高潮区 High tide	中潮区 Middle tide	低潮区 Low tide	高潮区 High tide	中潮区 Middle tide	低潮区 Low tide
粘土 Clay (%)	2.15	2.79	4.01	1.27	4.85	8.61	1.26	4.25	0.28
粉砂 Silt (%)	18.06	21.65	28.47	15.51	50.95	76.36	18.73	48.59	3.13
极细砂 Sand (%)	79.79	75.56	67.52	83.22	44.20	15.03	80.01	47.16	96.59
总氮 TN (%)	0.23	0.04	–	0.02	0.03	–	0.05	0.05	–
总有机碳 TOC (%)	1.83	0.37	–	0.22	0.21	–	0.60	0.70	–
温度 Temperature (℃)	24.23			24.50			23.87
盐度 Salinity (‰)	10.13			10.43			9.47
pH值	8.07			7.71			7.78

种类 Species	春季 Spring	夏季 Summer	秋季 Autumn	冬季 Winter
环节动物 Annelida
羽须鳃沙蚕 Dendroneris pinnaticirrus	-	-	-	0.022
软体动物 Mollusca
光滑河篮蛤 Potamocorbula laevis	0.512	0.143	0.326	0.603
中国绿螂 Glaucomya chinensis	0.067	0.128	0.020	0.031
焦河篮蛤 Potamocorbula ustulata	-	-	-	0.020

种类 Species	春季 Spring	夏季 Summer	秋季 Autumn	冬季 Winter
环节动物 Annelida
羽须鳃沙蚕 Dendroneris pinnaticirrus	-	-	-	0.022
软体动物 Mollusca
光滑河篮蛤 Potamocorbula laevis	0.512	0.143	0.326	0.603
中国绿螂 Glaucomya chinensis	0.067	0.128	0.020	0.031
焦河篮蛤 Potamocorbula ustulata	-	-	-	0.020

站次 Samplings	物种数 Species number	密度 Density (ind./m²)	生物量 Biomass (g/m²)	丰富度指数 Richness index (D)	均匀度指数 Evenness index (J')	Shannon-Wiener多样性指数 Shannon-Wiener diversity index (H')
P01
秋季 Autumn	19	183.1	89.47	3.92	0.80	3.39
冬季 Winter	14	113.8	45.69	3.18	0.81	3.09
春季 Spring	17	193.8	78.05	3.41	0.64	2.60
夏季 Summer	10	188.4	79.04	1.95	0.62	2.06
P02
秋季 Autumn	19	515.6	236.83	3.17	0.31	1.30
冬季 Winter	4	190.2	53.15	0.64	0.21	0.42
春季 Spring	4	391.1	100.12	0.56	0.54	1.08
夏季 Summer	4	236.4	63.18	0.61	0.51	1.02
P03
秋季 Autumn	7	446.2	222.87	0.92	0.40	1.03
冬季 Winter	4	469.3	323.93	0.54	0.22	0.45
春季 Spring	2	279.1	254.66	0.20	0.06	0.06
夏季 Summer	8	24.9	8.27	2.65	0.90	2.69
平均值 ± 标准差 Mean ± SD	9.3 ± 6.3	269.3 ± 153.1	129.61 ± 101.49	1.81 ± 1.38	0.50 ± 0.27	1.60 ± 1.13

珠江河口区大型底栖动物群落结构

The structure of macrobenthic community in Pearl River Estuary

RichHTML

PDF (PC)

可视化

被引次数

摘要/Abstract

引用本文

使用本文

图/表 10

参考文献 28

相关文章 15

编辑推荐

Metrics

本文评价

	物种数 Species number	密度 Density	生物量 Biomass	丰富度指数 Richness index (D)	均匀度指数 Evenness index (J')	Shannon-Wiener多样性指数 Shannon-Wiener index (H')
总有机碳 Total organic carbon (%)	0.703	0.233	0.486	0.716	0.447	0.682
总氮 Total nitrogen (%)	0.757	0.285	0.440	0.803	0.352	0.720
粘土 Clay (%)	-0.247	0.215	0.496	-0.053	-0.459	-0.104
粉砂 Silt (%)	-0.502	0.207	0.494	-0.317	-0.482	-0.369
极细砂 Sand (%)	0.483	-0.208	-0.496	0.296	0.482	0.347
温度 Temperature (℃)	0.080	0.504	-0.053	0.119	0.305	0.185
盐度 Salinity (‰)	0.623*	0.483	-0.051	0.577*	0.163	0.366
pH	0.958**	-0.179	0.015	0.272	0.023	0.144

调查年份 Investigation year	物种数 Species number	春季密度 Density in spring (ind./m²)	夏季密度 Density in summer (ind./m²)	春季生物量 Biomass in spring (g/m²)	夏季生物量 Biomass in summer (g/m²)	参考文献 Reference
1999-2000	32	591.7	-	26.70	-	Huang et al, 2002
2004	223	2,011.0	859.3	439.69	189.06	Mao et al, 2011
2005	240	183.0	138.5	127.17	25.36	Mao et al, 2011
2006	209	94.0	28.5	31.14	13.53	Mao et al, 2011
2008	293	251.7	215.0	27.15	38.91	Mao et al, 2011
2006	245	-	205.3	-	14.31	Zhang, 2014
2009	40	**	**	**	**	Huang et al, 2011
2015	67	215.0	212.0	11.79	3.32	Peng et al, 2019
2015	52	288.0	149.9	144.28	50.16	本研究 This study

[1]	杨润明, 中村彰宏. 巢居蚂蚁更倾向于在人造光源附近定居繁殖[J]. 生物多样性, 2022, 30(8): 22067-.
[2]	杨清, 张鹏, 安瑞志, 乔楠茜, 达珍, 巴桑. 拉萨河中下游纤毛虫群落时空分布模式及其驱动机制[J]. 生物多样性, 2022, 30(6): 22012-.
[3]	董建宇, 孙昕, 詹启鹏, 张宇洋, 张秀梅. 莱州湾东岸潮下带大型底栖动物群落beta多样性格局及其驱动因素[J]. 生物多样性, 2022, 30(3): 21388-.
[4]	陈燕南, 梁铖, 陈军. 亚热带不同树种组成森林中土壤甲螨群落结构特征：以江西新岗山为例[J]. 生物多样性, 2022, 30(12): 22334-.
[5]	易浪, 董亚坤, 苗白鸽, 彭艳琼. 云南高黎贡山地区蝴蝶群落多样性[J]. 生物多样性, 2021, 29(7): 950-959.
[6]	易祖盛, 黄元骏, 易晖, 张新旺, 李文俊. 广东车八岭国家级自然保护区大型底栖动物多样性[J]. 生物多样性, 2021, 29(5): 680-687.
[7]	王楠, 黄菁华, 霍娜, 杨盼盼, 张欣玥, 赵世伟. 宁南山区不同植被恢复方式下土壤线虫群落特征:形态学鉴定与高通量测序法比较[J]. 生物多样性, 2021, 29(11): 1513-1529.
[8]	吴二焕, 李东海, 杨小波, 左永令, 李龙, 张培春, 陈琳, 田路嘉, 李晨笛. 海南苏铁种群结构与森林群落郁闭度的关系[J]. 生物多样性, 2021, 29(11): 1461-1469.
[9]	余宏昌, 毕宝帅, 唐文乔, 张亚, 郭弘艺. 上海苏州河治理中鱼类多样性及群落结构变化[J]. 生物多样性, 2021, 29(1): 32-42.
[10]	向颖, 刘素群, 黄兴龙, 刘志霄, 张佑祥, 马方舟. 湖南高望界国家级自然保护区及其周边蝶类多样性与影响因素[J]. 生物多样性, 2020, 28(8): 940-949.
[11]	尚素琴, 吴兴波, 王召龙, 彭鹤年, 周惠丽, 张红勇, 白映禄. 兴隆山国家级自然保护区不同生境的蝴蝶群落结构与种-多度分布[J]. 生物多样性, 2020, 28(8): 983-992.
[12]	赵志霞, 赵常明, 邓舒雨, 申国珍, 谢宗强, 熊高明, 李俊清. 重度砍伐后极小种群野生植物崖柏群落结构动态[J]. 生物多样性, 2020, 28(3): 333-339.
[13]	胡芮, 王儒晓, 杜诗雨, 李萌, 邢雨辉, 潘达, 徐海根, 孙红英. 扬州宝应湖底栖大型无脊椎动物的生物多样性及其变化[J]. 生物多样性, 2020, 28(12): 1558-1569.
[14]	李宝泉, 姜少玉, 吕卷章, 陈琳琳, 闫朗, 刘春云, 李晓静, 宋博, 李新正. 黄河三角洲潮间带及近岸浅海大型底栖动物物种组成及长周期变化[J]. 生物多样性, 2020, 28(12): 1511-1522.
[15]	宋础良. 结构稳定性: 概念、方法和应用[J]. 生物多样性, 2020, 28(11): 1345-1361.