加拿大一枝黄花入侵对杭州湾地区土壤线虫群落的影响

doi:10.3724/SP.J.1003.2011.09048

生物多样性 ›› 2011, Vol. 19 ›› Issue (5): 519-527. DOI: 10.3724/SP.J.1003.2011.09048 cstr: 32101.14.SP.J.1003.2011.09048

所属专题：生物多样性与生态系统功能；土壤生物与土壤健康；生物入侵

加拿大一枝黄花入侵对杭州湾地区土壤线虫群落的影响

许湘琴¹, 王莹莹¹^,², 陆强¹, 林植华¹, 陈慧丽¹^,^*()

¹杭州师范大学动物适应与进化杭州市重点实验室, 杭州 310036
²中国湿地博物馆, 杭州 310036);

收稿日期:2011-04-19 接受日期:2011-07-01 出版日期:2011-09-20 发布日期:2011-10-08
通讯作者: 陈慧丽
基金资助:
浙江省教育厅项目(Y200907936);国家自然科学基金(31100301);陕西省科学技术研究发展计划项目(2010K01-086)

Effect of Solidago canadensis invasions on soil nematode communities in Hangzhou Bay

Xiangqin Xu¹, Yingying Wang¹^,², Qiang Lu¹, Zhihua Lin¹, Huili Chen¹^,^*()

¹Hangzhou Key Laboratory for Animal Adaptation and Evolution, Hangzhou Normal University, Hangzhou 310036
²National Wetland Museum of China, Hangzhou 310036

Received:2011-04-19 Accepted:2011-07-01 Online:2011-09-20 Published:2011-10-08
Contact: Huili Chen

1. 附录I 加拿大一枝黄花群落(S)和芦苇群落(P)中土壤线虫组成和营养类群.pdf(239KB)

摘要/Abstract

摘要：

近年来随着地下生态学的发展, 生态学家们逐渐重视生物入侵导致的地下生物多样性及其相关生态系统功能的改变。为探究加拿大一枝黄花(Solidago canadensis)入侵对土壤线虫的影响, 我们在杭州湾地区选取镇海、平湖、慈溪、奉贤、海盐和杭州6个研究地点, 比较外来种加拿大一枝黄花群落与土著种芦苇(Phragmites australis)群落土壤中的线虫群落结构和功能。结果显示: 两种植物群落土壤中的线虫属数和多样性没有显著差异, 而线虫营养多样性、大多数营养类群百分比以及线虫群落结构均存在显著差异, 表明加拿大一枝黄花的入侵在一定程度上改变了杭州湾地区土壤线虫的群落结构; 加拿大一枝黄花群落中土壤食真菌线虫比例趋于增加, 植食性线虫比例降低, 表明加拿大一枝黄花的入侵可能对土壤生态系统的能流途径产生影响, 在入侵地抗寄生线虫能力强于土著植物芦苇; 采样地点与植物的交互作用对线虫多样性和群落结构的影响显著, 表明入侵地点是决定加拿大一枝黄花对土壤生物影响的重要因素之一; 土壤颗粒组成、碳含量和氮含量是影响线虫群落结构的主要环境因子。

关键词: 植物入侵, Solidago canadensis, 线虫, 多样性, 群落结构

Abstract

Ecologists are increasingly focusing on the effects of biological invasions on soil biodiversity and ecosystem functioning. We compared soil nematodes under plant communities dominated by invasiveSolidago canadensis and native plant Phragmites australis at 6 sites (Zhenhai, Fengxian, Pinghu, Haiyan, Cixi and Hangzhou) in Hangzhou Bay to assess the effects of S. canadensis invasions on soil nematode communities. The total number of genera and diversity of soil nematode did not differ between S. canadensis and P. australis communities. Trophic diversity, most of the proportions of trophic groups and nematode community structure varied between the two plant communities. These results suggested that the invasion of S. canadensis changed soil community structure and functioning in Hangzhou Bay. Compared toP. australis communities, the proportion of fungivores tended to increase in soil underS. canadensis communities, suggesting that the invasion might modify soil nutrient cycling. The proportion of herbivores decreased in soil dominated by S. canadensis, suggesting that the exotic S. canadensisis less vulnerable to parasitic nematodes than the nativeP. australis. Interactions between plant community type and site were significant for nematode diversity and community structure, which indicated that site was an important factor in determining the impact of the invasive plant on soil fauna. Soil grain composition, soil carbon and soil nitrogen were identified as the most important factors in shaping nematode communities.

Key words: plant invasion, Solidago canadensis, nematodes, diversity, community structure

许湘琴, 王莹莹, 陆强, 林植华, 陈慧丽 (2011) 加拿大一枝黄花入侵对杭州湾地区土壤线虫群落的影响. 生物多样性, 19, 519-527. DOI: 10.3724/SP.J.1003.2011.09048.

Xiangqin Xu, Yingying Wang, Qiang Lu, Zhihua Lin, Huili Chen (2011) Effect of Solidago canadensis invasions on soil nematode communities in Hangzhou Bay. Biodiversity Science, 19, 519-527. DOI: 10.3724/SP.J.1003.2011.09048.

导出引用管理器 EndNote|Ris|BibTeX

链接本文: https://www.biodiversity-science.net/CN/10.3724/SP.J.1003.2011.09048

https://www.biodiversity-science.net/CN/Y2011/V19/I5/519

图/表 6

参考文献 39

[1]	Biederman LA, Boutton TW (2009) Biodiversity and trophic structure of soil nematode communities are altered following woody plant invasion of grassland. Soil Biology and Bio- chemistry, 41,1943-1950.
[2]	Callaway RM, Thelen GC, Rodriguez A, Holben WE (2004) Soil biota and exotic plant invasion. Nature, 427,731-733. URL PMID
[3]	Chen F (陈芳) (2006) Research progress of the invader— Solidago canadensis. Grassland and Turf (草原与草坪), (4),9-11. (in Chinese with English abstract)
[4]	Chen HL (陈慧丽), Li YJ (李玉娟), Li B (李博), Chen JK (陈家宽), Wu JH (吴纪华) (2005) Impacts of exotic plant invasions on soil biodiversity and ecosystem processes. Biodiversity Science (生物多样性), 13,555-565. (in Chinese with English abstract)
[5]	Chen HL, Li B, Hu JB, Chen JK, Wu JH (2007a) Benthic nematode communities in the Yangtze River estuary as influenced by Spartina alterniflora invasions . Marine Ecology Progress Series, 336,99-110.
[6]	Chen HL, Li B, Fang CM, Chen JK, Wu JH (2007b) Exotic plant influences soil nematode communities through litter input. Soil Biology and Biochemistry, 39,1782-1793.
[7]	Clarke KR, Warwick RM (1994) Change in marine communities: an approach to statistical analysis and interpretation. Plymouth Marine Laboratory, Plymouth,
[8]	Copley J (2000) Ecology goes underground. Nature, 406,452-454. URL PMID
[9]	Dong M (董梅), Lu JZ (陆建忠), Zhang WJ (张文驹), Chen JK (陈家宽), Li B (李博) (2006) Canada goldenrod ( Solidago canadensis): an invasive alien weed rapidly spreading in China . Acta Phytotaxonomica Sinica (植物分类学报), 44,72-85. (in Chinese with English abstract)
[10]	Ehrenfeld JG (2006) A potential novel source of information for screening and monitoring the impact of exotic plants on ecosystems. Biological Invasions, 8,1511-1521.
[11]	Ferris H, Bongers T,de Goede RGM (2001) A framework for soil food web diagnostics: extension of the nematode faunal analysis concept. Applied Soil Ecology, 18,13-29.
[12]	Grifﬁths BS, Boag B, Neilson R, Palmer L (1990) The use of colloidal silica to extract nematodes from small samples of soil and sediment. Nematologica, 36,465-473.
[13]	He JF (何锦峰) (2008) Advance in studies on invasion mechanisms of exotic plants. Chinese Journal of Applied and Environmental Biology (应用与环境生物学报), 14,863-870. (in Chinese with English abstract)
[14]	He JS (贺金生), Wang ZQ (王政权), Fang JY (方精云) (2004) Issues and prospects of belowground ecology with special reference to global climate change. Chinese Science Bulletin (科学通报), 49,1226-1233. (in Chinese)
[15]	Jin L (金樑) (2005) Ecology of Arbuscular Mycorrhizal Associations in Solidago canadensis, an Invasive Alien Plant (外来入侵种加拿大一枝黄花的菌根生态学研究). PhD dissertation, Fudan University, Shanghai. (in Chinese with English abstract)
[16]	Keane RM, Crawley MJ (2002) Exotic plant invasions and the enemy release hypothesis. Trends in Ecology and Evolution, 17,164-170.
[17]	Lei YB (类延宝), Xiao HF (肖海峰), Feng YL (冯玉龙) (2010) Impacts of alien plant invasions on biodiversity and evolutionary responses of native species. Biodiversity Science (生物多样性), 18,622-630. (in Chinese with English abstract)
[18]	Levine JM, Vilà M, D’Antonio CM, Dukes JS, Grigulis K, Lavorel S (2003) Mechanisms underlying the impacts of exotic plant invasions. Proceedings of the Royal Society of London Series B: Biological Sciences, 270,775-781. DOI URL PMID
[19]	Liang WJ (梁文举), Zhang WM (张万民), Li WG (李维光), Duan YX (段玉玺) (2001) Effect of chemical fertilizer on nematode community composition and diversity in the Black Soil Region. Biodiversity Science (生物多样性), 9,237-240. (in Chinese with English abstract)
[20]	Li B (李博), Ma KP (马克平) (2010) Biological invasions: opportunities and challenges facing Chinese ecologists in the era of translational ecology. Biodiversity Science (生物多样性), 18,529-532. (in Chinese)
[21]	Li Q (李琪), Liang WJ (梁文举), Jiang Y (姜勇) (2007) Present situation and prospect of soil nematode diversity in farmland ecosystems. Biodiversity Science (生物多样性), 15,134-141. (in Chinese with English abstract)
[22]	Li YJ (李玉娟), Wu JH (吴纪华), Chen HL (陈慧丽), Chen JK (陈家宽) (2005) Nematodes as bioindicator of soil health: methods and applications. Chinese Journal of Applied Ecology (应用生态学报), 16,1541-1546. (in Chinese with English abstract)
[23]	Lu JZ (陆建忠), Qiu W (裘伟), Chen JK (陈家宽), Li B (李博) (2005) Impact of invasive species on soil properties: Canadian goldenrod ( Solidago canadensis) as a case study . Biodiversity Science (生物多样性), 13,347-356. (in Chinese with English abstract)
[24]	Porazinska DL, Bardgett RD, Blaauw MB, Hunt HW, Parsons AN, Seastedt TR, Wall DH (2003) Relationships at the aboveground-belowground interface: plants, soil biota, and soil processes. Ecological Monographs, 73,377-395.
[25]	Porazinska DL, Pratt PD, Giblin-Davis RM (2007) Consequences of Melaleuca quinquenervia invasion on soil nematodes in the Florida Everglades . Journal of Nematology, 39,305-312. URL PMID
[26]	Posey MH, Alphin TD, Meyer DL, Johnson JM (2003) Benthic communities of common reed Phragmites australis and marsh cordgrass Spartina alterniflora marshes in Chesapeake Bay. Marine Ecology Progress Series, 261,51-61.
[27]	Shen LH (沈荔花), Guo QX (郭琼霞), Lin WX (林文雄), Chen Y (陈颖), Huang Z (黄振) (2007) Impacts of invasive alien weed Solidago canadensis L. on microbial population in the root soil . Chinese Agricultural Science Bulletin (中国农学通报), 23(4),323-327. (in Chinese with English abstract)
[28]	van der Putten WH, Yeates GW, Duyts H, Reis CS, Karssen G (2005) Invasive plants and their escape from root herbivory: a worldwide comparison of the root-feeding nematode communities of the dune grass Ammophila arenaria in natural and introduced ranges . Biological Invasions, 7,733-746.
[29]	Wang LC (王立成), Chu JJ (褚建君) (2007) Species association between Solidago canadensis and other plants . Journal of Shanghai Jiaotong University (Agricultural Science) (上海交通大学学报(农业科学版)), 25,115-119. (in Chinese with English abstract)
[30]	Wardle DA, Bardgett RD, Klironomos JN, Setälä H, van der Putten WH, Wall DH (2004) Ecological linkages between aboveground and belowground biota. Science, 304,1629-1633. URL PMID
[31]	Wolfe BE, Klironomos JN (2005) Breaking new ground: soil communities and exotic plant invasion. BioScience, 55,477-487.
[32]	Xing L (邢璐) (2009) Alien species invasion and some problems in the ecological security. Legal System and Society (法制与社会), (9),351-352. (in Chinese)
[33]	Yang RY (杨如意), Zan ST (昝树婷), Tang JJ (唐建军), Chen X (陈欣) (2011) Invasion mechanisms of Solidago canadensis L.: a review . Acta Ecologica Sinica (生态学报), 31,1185-1194. (in Chinese with English abstract)
[34]	Yeates GW, Bongers T, De Goede RGM, Freckman DW, Georgieva SS (1993) Feeding habitats in soil nematode families and genera—an outline for soil ecologists. Journal of Nematology, 25,315-331. URL PMID
[35]	Yeates GW, Bongers T (1999) Nematode diversity in agroecosystems. Agriculture, Ecosystems & Environment, 74,113-135.
[36]	Yeates GW, Williams PA (2001) Influence of three invasive weeds and site factors on soil microfauna in New Zealand. Pedobiologia, 45,367-383.
[37]	Yeates GW (2003) Nematodes as soil indicators: functional and biodiversity aspects. Biology and Fertility of Soils, 37,199-210.
[38]	Yin LP (印丽萍), Tan YB (谭永彬), Shen GH (沈国辉), Yao HM (姚红梅) (2004) Research advances of Solidago canadensis L. Weed Science (杂草科学), (4),8-11. (in Chinese)
[39]	Zhang GH (张桂花), Peng SL (彭少麟), Li GY (李光义), Li QF (李勤奋) (2009) Recent advances in the interaction between invasive plants and belowground ecosystem. Chinese Agricultural Science Bulletin (中国农学通报), 25,246-251. (in Chinese with English abstract)

		砂粒 Sand (%)	粉粒 Silt (%)	粘粒 Clay (%)	pH	总氮 Total nitrogen (mg/g)	总碳 Total carbon (mg/g)	株高 Height (cm)	植株密度 Shoot density (ind./m²)
镇海 Zhenhai	S	16.9 ± 1.4	45.0 ± 4.6	38.1 ± 5.5	8.7 ± 0.10	1.44 ± 0.24	65.23 ± 7.71	150 ± 18	116 ± 36
镇海 Zhenhai	P	13.5 ± 1.8	51.8 ± 3.0	34.7 ± 4.7	8.7 ± 0.07	0.61 ± 0.12	11.61 ± 0.58	156 ± 20	107 ± 44
奉贤 Fengxian	S	4.8 ± 0.8	23.9 ± 5.3	71.3 ± 6.0	8.7 ± 0.02	0.38 ± 0.10	11.89 ± 0.86	110 ± 4	98 ± 12
奉贤 Fengxian	P	5.4 ± 0.9	25.3 ± 1.6	69.3 ± 2.3	8.8 ± 0.03	0.46 ± 0.21	17.82 ± 1.43	161 ± 16	125 ± 23
平湖 Pinghu	S	6.5 ± 0.9	34.3 ± 1.8	59.1 ± 2.6	8.5 ± 0.17	0.49 ± 0.16	15.67 ± 1.58	143 ± 26	111 ± 24
平湖 Pinghu	P	8.7 ± 4.0	38.7 ± 14.4	52.6 ± 18.4	8.6 ± 0.02	1.21 ± 0.32	17.23 ± 0.87	220 ± 47	63 ± 6
海盐 Haiyan	S	9.4 ± 0.6	45.1 ± 1.4	45.6 ± 1.9	8.5 ± 0.15	1.04 ± 0.06	12.40 ± 0.32	114 ± 19	117 ± 63
海盐 Haiyan	P	12.5 ± 5.1	45.6 ± 14.4	41.9 ± 19.6	8.6 ± 0.04	0.61 ± 0.15	23.98 ± 2.55	190 ± 10	118 ± 26
慈溪 Cixi	S	6.7 ± 0.4	32.9 ± 1.6	60.4 ± 2.0	8.8 ± 0.05	0.91 ± 0.17	15.65 ± 3.52	177 ± 13	53 ± 15
慈溪 Cixi	P	2.0 ± 0.8	22.3 ± 2.6	75.7 ± 3.1	9.0 ± 0.41	0.33 ± 0.10	9.98 ± 0.31	156 ± 14	173 ± 28
杭州 Hangzhou	S	2.5 ± 0.9	16.9 ± 1.6	80.7 ± 2.5	8.7 ± 0.05	0.34 ± 0.09	9.36 ± 0.63	224 ± 25	92 ± 46
杭州 Hangzhou	P	2.0 ± 0.7	15.8 ± 0.4	82.2 ± 1.1	9.1 ± 0.08	0.31 ± 0.05	8.64 ± 0.87	173 ± 29	37 ± 10

		砂粒 Sand (%)	粉粒 Silt (%)	粘粒 Clay (%)	pH	总氮 Total nitrogen (mg/g)	总碳 Total carbon (mg/g)	株高 Height (cm)	植株密度 Shoot density (ind./m²)
镇海 Zhenhai	S	16.9 ± 1.4	45.0 ± 4.6	38.1 ± 5.5	8.7 ± 0.10	1.44 ± 0.24	65.23 ± 7.71	150 ± 18	116 ± 36
镇海 Zhenhai	P	13.5 ± 1.8	51.8 ± 3.0	34.7 ± 4.7	8.7 ± 0.07	0.61 ± 0.12	11.61 ± 0.58	156 ± 20	107 ± 44
奉贤 Fengxian	S	4.8 ± 0.8	23.9 ± 5.3	71.3 ± 6.0	8.7 ± 0.02	0.38 ± 0.10	11.89 ± 0.86	110 ± 4	98 ± 12
奉贤 Fengxian	P	5.4 ± 0.9	25.3 ± 1.6	69.3 ± 2.3	8.8 ± 0.03	0.46 ± 0.21	17.82 ± 1.43	161 ± 16	125 ± 23
平湖 Pinghu	S	6.5 ± 0.9	34.3 ± 1.8	59.1 ± 2.6	8.5 ± 0.17	0.49 ± 0.16	15.67 ± 1.58	143 ± 26	111 ± 24
平湖 Pinghu	P	8.7 ± 4.0	38.7 ± 14.4	52.6 ± 18.4	8.6 ± 0.02	1.21 ± 0.32	17.23 ± 0.87	220 ± 47	63 ± 6
海盐 Haiyan	S	9.4 ± 0.6	45.1 ± 1.4	45.6 ± 1.9	8.5 ± 0.15	1.04 ± 0.06	12.40 ± 0.32	114 ± 19	117 ± 63
海盐 Haiyan	P	12.5 ± 5.1	45.6 ± 14.4	41.9 ± 19.6	8.6 ± 0.04	0.61 ± 0.15	23.98 ± 2.55	190 ± 10	118 ± 26
慈溪 Cixi	S	6.7 ± 0.4	32.9 ± 1.6	60.4 ± 2.0	8.8 ± 0.05	0.91 ± 0.17	15.65 ± 3.52	177 ± 13	53 ± 15
慈溪 Cixi	P	2.0 ± 0.8	22.3 ± 2.6	75.7 ± 3.1	9.0 ± 0.41	0.33 ± 0.10	9.98 ± 0.31	156 ± 14	173 ± 28
杭州 Hangzhou	S	2.5 ± 0.9	16.9 ± 1.6	80.7 ± 2.5	8.7 ± 0.05	0.34 ± 0.09	9.36 ± 0.63	224 ± 25	92 ± 46
杭州 Hangzhou	P	2.0 ± 0.7	15.8 ± 0.4	82.2 ± 1.1	9.1 ± 0.08	0.31 ± 0.05	8.64 ± 0.87	173 ± 29	37 ± 10

变量 Variables	植物类型 Plant (df = 2)		地点 Site (df = 5)		植物类型×地点 Plant × Site (df = 5)
变量 Variables	F	P	F	P	F	P
砂粒 Sand (%)	0.59	0.449	41.75	< 0.001	4.31	0.004
粉粒 Silt (%)	0.02	0.897	30.31	< 0.001	1.76	0.145
粘粒 Clay (%)	0.01	0.928	33.33	< 0.001	1.75	0.149
pH	15.21	< 0.001	9.75	< 0.001	2.23	0.072
总氮 Total nitrogen	13.57	0.001	20.83	< 0.001	22.34	< 0.001
总碳 Total carbon	78.03	< 0.001	119.78	< 0.001	56.19	< 0.001
株高 Height	12.26	< 0.001	8.00	< 0.001	11.04	< 0.001
植株密度 Shoot density	0.42	0.52	3.34	0.014	7.84	< 0.001

变量 Variables	植物类型 Plant (df = 2)		地点 Site (df = 5)		植物类型×地点 Plant × Site (df = 5)
变量 Variables	F	P	F	P	F	P
砂粒 Sand (%)	0.59	0.449	41.75	< 0.001	4.31	0.004
粉粒 Silt (%)	0.02	0.897	30.31	< 0.001	1.76	0.145
粘粒 Clay (%)	0.01	0.928	33.33	< 0.001	1.75	0.149
pH	15.21	< 0.001	9.75	< 0.001	2.23	0.072
总氮 Total nitrogen	13.57	0.001	20.83	< 0.001	22.34	< 0.001
总碳 Total carbon	78.03	< 0.001	119.78	< 0.001	56.19	< 0.001
株高 Height	12.26	< 0.001	8.00	< 0.001	11.04	< 0.001
植株密度 Shoot density	0.42	0.52	3.34	0.014	7.84	< 0.001

变量 Variables	植物类型 Plant type (df = 1)		地点 Site (df = 5)		植物类型 × 地点 Plant type × Site (df = 5)
变量 Variables	F	P	F	P	F	P
属数 Genus number	2.56	0.118	24.18	< 0.001	6.90	< 0.001
密度 Density	3.59	0.006	5.76	< 0.001	5.28	< 0.001
Shannon-Wiener diversity index (H')	0.01	0.92	28.18	< 0.001	7.24	< 0.001
营养多样性指数 Trophic diversity index (TD)	17.05	< 0.001	17.50	< 0.001	3.76	0.008
富集指数 Enrichment index (EI)	11.52	0.002	20.62	< 0.001	13.15	< 0.001
结构指数 Structure index (SI)	9.07	0.005	4.08	0.005	3.39	0.013
线虫通路比值 Nematode channel ratio (NCR)	22.94	< 0.001	9.29	< 0.001	5.37	< 0.001
植食性线虫 Herbivores (%)	24.14	< 0.001	54.20	< 0.001	11.85	< 0.001
食藻类线虫 Algal feeders (%)	0.90	0.348	6.78	< 0.001	7.17	< 0.001
食细菌线虫 Bacterivores (%)	10.96	0.002	78.34	< 0.001	15.69	< 0.001
食真菌线虫 Fungivores (%)	34.65	< 0.001	8.98	< 0.001	5.42	< 0.001
杂食性线虫 Omnivores (%)	11.89	0.001	14.01	< 0.001	9.10	< 0.001
捕食性线虫 Carnivores (%)	14.65	< 0.001	5.98	< 0.001	8.70	< 0.001

加拿大一枝黄花入侵对杭州湾地区土壤线虫群落的影响

Effect of Solidago canadensis invasions on soil nematode communities in Hangzhou Bay

RichHTML

PDF (PC)

补充材料

可视化

被引次数

摘要/Abstract

引用本文

使用本文

图/表 6

参考文献 39

相关文章 15

编辑推荐

Metrics

本文评价

[1]	郝泽周, 申小莉, 斯幸峰, 赵岩岩, 魏晨韬, 吴飞, 许晓青, 阙品甲, 董路, 华方圆, 张立勋, 张承云, 刘阳. 中国鸟类被动声学监测规范与建议[J]. 生物多样性, 2026, 34(5): 25474-.
[2]	贾晓旭, 陈皖强, 唐修君, 樊艳凤, 张静, 王海威, 高玉时. 西南地区家鸡线粒体DNA控制区遗传多样性和基因渗入[J]. 生物多样性, 2026, 34(5): 26003-.
[3]	梁健超, 陈淑甜, 何文祥, 熊春妮, 许镇洲, 黄源欣, 刘源志弘, 张浪, 胡慧建. 广州市陆生野生脊椎动物资源——编目、分布与保护[J]. 生物多样性, 2026, 34(5): 25422-.
[4]	张海龙, 聂海燕, 刘萌萌, 魏美才, 李泽建. 浙江乌岩岭叶蜂多样性分布及影响因素[J]. 生物多样性, 2026, 34(5): 25459-.
[5]	梁竣策, 李开枝, 谭烨辉. 南海翼足类物种多样性与分布[J]. 生物多样性, 2026, 34(5): 25487-.
[6]	姚可侃, 余卉, 张巧玲, 陈琳. AI声纹监测与人工样线调查在鸟类多样性监测中的差异比较: 以西溪国家湿地公园为例[J]. 生物多样性, 2026, 34(4): 25239-.
[7]	周丽洁, 郝珉辉, 何怀江, 程艳霞, 张春雨, 赵秀海. 小兴安岭森林β多样性格局、组分及其影响因素[J]. 生物多样性, 2026, 34(4): 25443-.
[8]	蒋翠憶, 谢致敬, 田中平, 李玥莹, 郑明心, 房帅, 米尔卡米力∙麦麦提, 依里帆∙艾克拜尔江, 高梅香, 张健. 微地形生境异质性对新疆西天山森林土壤跳虫群落分异的塑造作用[J]. 生物多样性, 2026, 34(4): 25300-.
[9]	王露红, 李波, 杨攀艳, 黄嘉琴, 谢予婷, 杜鑫, 文毅, 王彬. 四川省繁殖鸟类群落的多维度多样性及其影响因子[J]. 生物多样性, 2026, 34(4): 25464-.
[10]	彭昀月, 彭奎, 刘昕然, 孙天怡, 张小全. 生物多样性信用的企业参与途径、市场发展障碍与建议[J]. 生物多样性, 2026, 34(4): 26031-.
[11]	李伯尧, 盛天成, 幸小云. 生物多样性风险对企业财务绩效的影响: 来自中国上市公司的证据[J]. 生物多样性, 2026, 34(4): 25330-.
[12]	张同, 梁力文, 王长剑, 舒服, 王璐, 郭泽光, 卓玛曲珍, 钱芊, 蒋安莉, 敖俊杰, 彭兴文, 伍小刚, 向左甫, 郭克疾, 廖梓延. 基于红外相机的西藏芒康滇金丝猴国家级自然保护区鸟兽多样性及代表性物种的季节性空间利用特征[J]. 生物多样性, 2026, 34(4): 25435-.
[13]	刘昊, 张玉霄, 刘冰, 李飞飞, 马洪峥, 覃海宁, 李德铢, 陈文俐. 中国禾本科植物多样性及其物种名录[J]. 生物多样性, 2026, 34(4): 25438-.
[14]	尹翔正, 姜海燕, 张俊, 罗春生, 张元明. 极端干旱区荒漠灌木叶际细菌群落多样性特征[J]. 生物多样性, 2026, 34(4): 25485-.
[15]	孔孜亦, 王德港, 王建涛, 裴志永, 孙晶, 张长春, 张军国. 基于SCD-HRNet模型的野生动物姿态估计及其在生物多样性监测中的应用: 以内蒙古赛罕乌拉地区为例[J]. 生物多样性, 2026, 34(4): 25287-.