大气CO2浓度和气温升高对麦田节肢动物群落的影响

doi:10.3724/SP.J.1003.2014.13219

生物多样性 ›› 2014, Vol. 22 ›› Issue (4): 502-507. DOI: 10.3724/SP.J.1003.2014.13219 cstr: 32101.14.SP.J.1003.2014.13219

所属专题：昆虫多样性与生态功能

大气CO₂浓度和气温升高对麦田节肢动物群落的影响

刘帅¹, 李保平¹, 孟玲^1,,A;^*(), 张旭辉², 潘根兴²

1 .南京农业大学植物保护学院/农作物生物灾害综合治理教育部重点实验室, 南京 210095
2 .南京农业大学资源与环境学院, 南京 210095

收稿日期:2013-10-11 接受日期:2014-01-14 出版日期:2014-07-20 发布日期:2014-07-24
通讯作者: 孟玲
基金资助:
国家科技支撑计划(2012BAC19B01)和国家公益性行业(农业)科研专项(200903003、201103002)

Effects of elevated CO₂ and increased temperature on wheat field arthropod community

Shuai Liu¹, Baoping Li¹, Ling Meng^1,^*(), Xuhui Zhang², Genxing Pan²

1. College of Plant Protection/Key Laboratory of Integrated Management of Crop Diseases and Pests, Ministry of Education, Nanjing Agricultural University, Nanjing 210095
2 .College of Natural Resources, Nanjing Agricultural University, Nanjing 210095

Received:2013-10-11 Accepted:2014-01-14 Online:2014-07-20 Published:2014-07-24
Contact: Meng Ling

1. 附表1 麦田节肢动物种类.pdf(156KB)

摘要/Abstract

摘要：

为了预测气候变化对麦田节肢动物群落多样性的影响, 本研究在麦田开放环境中设置4种处理, 分别是高温(高于当时气温2℃和当前CO₂浓度)、高CO₂浓度(500 μL/L和当时气温)、高温+高CO₂浓度和对照(当前CO₂浓度和气温)等, 采用定期随机抽样方法调查节肢动物群落的多样性, 用经典的多样性指数对整体节肢动物群落以及不同食性节肢动物群落多样性进行分析。共采到节肢动物3纲10目42科52种。仅“高温”和“高温+高CO₂”处理显著增大节肢动物群落的均匀度, 其余处理均无显著影响。“高温+高CO₂”处理的影响随小麦生长发育期不同而略有差异, 在苗期可增大Shannon-Wiener多样性指数, 而在后期使该指数减小; “高温+高CO₂”与“高温”处理的群落多样性较为相似。对不同食性节肢动物群落的分析表明, 与对照相比, 植食性昆虫群落在“高CO₂”下丰富度显著增大; 寄生性昆虫群落的多度在“高温”下显著增大; 腐食性等节肢动物群落的多度在“高CO₂+高温”和“高温”处理下有所增大、均匀度在“高温”下略降低, 但均未达统计上的显著水平; 捕食性节肢动物群落不受影响。本研究说明, CO₂浓度和气温升高不同程度地影响麦田节肢动物群落的物种多样性, 两类因素同时升高与各自单独升高的影响不完全一致。

关键词: 植食性昆虫多样性, 天敌昆虫多样性, FACE, 增温, 气候变化

Abstract

To project arthropod community response to climate change in wheat fields, a field survey of arthropods over the growing season was made in the plots under a factorial combination of two CO₂(ambient and 500 μL/L) and two temperature (ambient and +2℃) treatments. The survey collected 52 species, 42 families, 10 orders, and 3 classes. Analyses of overall arthropod community showed a significant increase in evenness due to “Elevated CO₂+ Increased temperature” treatment. Elevated CO₂ and increased temperature treatments had varying impacts on species diversity parameters within the wheat growing season. The “Elevated CO₂+ Increased temperature” treatment increased the Shannon-Wiener index slightly during the early growing season, but decreased it later in the season. Species diversity was most similar between the “Elevated CO₂ + Increased temperature” and the “Increased temperature” treatment. The analysis of arthropod communities by trophic level showed that the “Elevated CO₂” increased herbivorous insect richness and the “Increased temperature” increased parasitoid abundances, compared with the control. The treatments did not affect detritivorous and predaceous arthropod communities. The results of this study suggest that elevated CO₂and increased temperature can affect arthropod diversity in wheat fields, and the effects may vary between both elevated CO₂ and increased temperature and individual elevation of either CO₂ and temperature.

Key words: phytophagous insect diversity, carnivorous arthropod diversity, FACE, increased temperature, climate change

刘帅, 李保平, 孟玲, 张旭辉, 潘根兴 (2014) 大气CO₂浓度和气温升高对麦田节肢动物群落的影响. 生物多样性, 22, 502-507. DOI: 10.3724/SP.J.1003.2014.13219.

Shuai Liu, Baoping Li, Ling Meng, Xuhui Zhang, Genxing Pan (2014) Effects of elevated CO₂ and increased temperature on wheat field arthropod community. Biodiversity Science, 22, 502-507. DOI: 10.3724/SP.J.1003.2014.13219.

导出引用管理器 EndNote|Ris|BibTeX

链接本文: https://www.biodiversity-science.net/CN/10.3724/SP.J.1003.2014.13219

https://www.biodiversity-science.net/CN/Y2014/V22/I4/502

图/表 4

参考文献 23

[1]	Bale JS, Masters GJ, Hodkinson ID, Awmack C, Bezemer TM, Brown VK, Butterfield J, Buse A, Coulson JC, Farrar J, Good JEG, Harrington R, Hartley S, Jones TH, Lindroth RL, Press MC, Symrnioudis I, Watt AD, Whittaker JB (2002) Herbivory in global climate change research: direct effects of rising temperature on insect herbivores. Global Change Biology, 8, 1-16.
[2]	Feng ZQ (冯锺琪) (1990) Spiders of China in Colour (中国蜘蛛原色图鉴). Hunan Science and Technology Press, Changsha. (in Chinese)
[3]	Ge F (戈峰), Chen FJ (陈法军) (2006) Impacts of elevated CO2 on insects.Acta Ecologica Sinica(生态学报), 26, 935-940. (in Chinese with English abstract)
[4]	Hillstrom ML, Lindroth RL (2008) Elevated atmospheric carbon dioxide and ozone alter forest insect abundance and community composition.Insect Conservation and Diversity, 1, 233-241.
[5]	Huang QL (黄其林), Tian LX (田立新), Yang LF (杨莲芳) (1984) Identification Handbook of Agricultural Insects (农业昆虫鉴定). Shanghai Science and Technology Press, Shanghai. (in Chinese)
[6]	IPCC (WGII) (2001) Climate Change 2001: impacts, adaptation, and vulnerability. In: Contribution of Working Group II to the Third Assessment Report of the Intergovernmental Panel on Climate Change (eds McCarthy JJ, Canziani OF, Leary NA, Dokken DJ, White KS). Cambridge University Press, Cambridge.
[7]	Jeffs CT, Lewis OT (2013) Effects of climate warming on host-parasitoid interactions.Ecological Entomology, 38, 209-218.
[8]	Klironomos JN, Allen MF, Rilling MC, Allen MF, Rillig MC, Piotrowski J, Nejad SM, Wolfe BE, Powell JR (2005) Abrupt rise in atmospheric CO2 overestimates community response in a model plant-soil system. Nature, 433, 621-624.
[9]	Ma KP (马克平) (1994) The methods of biotic community diversity measurement. In: Principles and Methodologies of Biodiversity Studies (生物多样性研究的原理与方法) (ed. Biodiversity Committee of the Chinese Academy of Sciences (中国科学院生物多样性委员会), pp. 141-165. China Science and Technology Press, Beijing. (in Chinese)
[10]	Massad TJ, Dyer LA (2010) A meta-analysis of the effects of global environmental change on plant-herbivore interactions. Arthropod-Plant Interactions, 4, 181-188.
[11]	Meng L (孟玲), Li BP (李保平) (2005) Effects of elevated carbon dioxide on insect-plant interactions.Chinese Journal of Ecology(生态学杂志), 24, 200-205. (in Chinese with English abstract)
[12]	Mittelbach GG (2012)Community Ecology. Sinauer Associates, Inc., Massachusetts.
[13]	Nösberger J, Long SP, Norby RJ, Stitt M, Hendrey GR, Blum H (2006) Managed Ecosystems and CO2:Case Studies, Processes, and Perspectives. Springer Press, Berlin.
[14]	R Core Team (2014) R: A Language and Environment for Statistical Computing. R Foundation for Statistical Computing, Vienna, Austria..
[15]	Sanders NJ, Belote RT, Weltzin J (2004) Multitrophic effects of elevated atmospheric CO2 on understory plant and arthropod communities.Environmental Entomology, 33, 1609-1616.
[16]	Stacey DA, Fellows MDE (2002) Influence of elevated CO2 on interspecific interactions at higher trophic levels.Global Change Biology, 8, 668-678.
[17]	Stewart AJA, Wright AF (1995) A new inexpensive suction apparatus for sampling arthropods in grassland.Ecological Entomology, 20, 98-102.
[18]	Villalpando SN, Williams R, Norby RJ (2009) Elevated air temperature alters an old-field insect community in a multifactor climate change experiment.Global Change Biology, 15, 930-942.
[19]	Yamamura K, Kiritani K (1998) A simple method to estimate the potential increase in the number of generations under global warming in temperate zones.Applied Entomology and Zoology, 33, 289-298.
[20]	Zhang XX (张孝曦) (2001)Insect Ecology and Pest Prediction (昆虫生态及预测预报). China Agriculture Press, Beijing. (in Chinese)
[21]	Zhang Y, Chen XM, Zhang CC, Pan GX, Zhang XH (2014) Availability of soil nitrogen and phosphorus under elevated [CO2] and temperature in the Taihu Lake region, China.Journal of Plant Nutrition and Soil Science, 177, 343-348.
[22]	Zhu H (朱慧) (2012) The Relationships Between Plant Diversity and Insect Diversity in Response to Grazing and Climate Change on Grasslands (气候变化和放牧对草地植物与昆虫多样性关系的作用). PhD dissertation, Northeast Normal University, Changchun. (in Chinese with English abstract)
[23]	Zvereva EL, Kozlov MV (2006) Consequences of simultaneous elevation of carbon dioxide and temperature for plant- herbivore interactions: a meta-analysis.Global Change Biology, 12, 27-41.

处理 Treatment	多样性指数 Diversity index (H')	优势集中性指数 Dominant index (C)	均匀度指数 Evenness index (E)	丰富度Richness (S)	多度 Abundance
对照 (CK)	2.0209	0.2904	0.5831	32	857
高CO₂ Elevated CO₂	2.2452	0.2226	0.6421	33	773
高CO₂ + 高温 Elevated CO₂ + Increased temperature	2.3468	0.1531	0.6601	35	892
高温 Increased temperature	2.3938	0.1506	0.6788	34	902

处理 Treatment	多样性指数 Diversity index (H')	优势集中性指数 Dominant index (C)	均匀度指数 Evenness index (E)	丰富度Richness (S)	多度 Abundance
对照 (CK)	2.0209	0.2904	0.5831	32	857
高CO₂ Elevated CO₂	2.2452	0.2226	0.6421	33	773
高CO₂ + 高温 Elevated CO₂ + Increased temperature	2.3468	0.1531	0.6601	35	892
高温 Increased temperature	2.3938	0.1506	0.6788	34	902

节肢动物群落 Arthropod community	对照 CK	高CO₂ Elevated CO₂	高CO₂+高温 Elevated CO₂ + Increased temperature	高温 Increased temperature
植食性昆虫 Herbivorous insects
多度 Abundance	57.0 ± 2.4	51.0 ± 3.7	68.0 ± 7.0	71.0 ± 3.5
丰富度 Richness	9.0 ± 0.3	10.0 ± 0.7*	10.0 ± 1.2	8.0 ± 0.1
均匀度 Evenness	0.84 ± 0.1	0.9 ± 0.1	0.8 ± 0.1	0.7 ± 0.1
捕食性节肢动物 Predaceous arthropod
多度 Abundance	23.0 ± 1.6	21.0 ± 3.8	22.0 ± 1.1	32.0 ± 1.9
丰富度 Richness	7.0 ± 0.2	6.0 ± 0.8	6.0 ± 0.5	7.0 ± 0.5
均匀度 Evenness	0.8 ± 0.1	0.8 ± 0.1	0.8 ± 0.1	0.7 ± 0.1
寄生性昆虫 Parasitoids
多度 Abundance	15.0 ± 2.1	35.0 ± 5.3	53.0 ± 3.0	54.0 ± 11.6^*
丰富度 Richness	3.0 ± 0.2	3.0 ± 0.2	3.0 ± 0.4	4.0 ± 0.1
均匀度 Evenness	0.6 ± 0.1	0.6 ± 0.1	0.4 ± 0.1	0.5 ± 0.1
腐食性节肢动物 Detritivorous arthropod
多度 Abundance	191.0 ± 3.0	150.0 ± 4.5	154.0 ± 10.0	143.0 ± 3.9
丰富度 Richness	4.0 ± 0.2	4.0 ± 0.2	4.0 ± 0.2	4.0 ± 0.2
均匀度 Evenness	0.5 ± 0.1	0.5 ± 0.1	0.6 ± 0.1	0.7 ± 0.1

节肢动物群落 Arthropod community	对照 CK	高CO₂ Elevated CO₂	高CO₂+高温 Elevated CO₂ + Increased temperature	高温 Increased temperature
植食性昆虫 Herbivorous insects
多度 Abundance	57.0 ± 2.4	51.0 ± 3.7	68.0 ± 7.0	71.0 ± 3.5
丰富度 Richness	9.0 ± 0.3	10.0 ± 0.7*	10.0 ± 1.2	8.0 ± 0.1
均匀度 Evenness	0.84 ± 0.1	0.9 ± 0.1	0.8 ± 0.1	0.7 ± 0.1
捕食性节肢动物 Predaceous arthropod
多度 Abundance	23.0 ± 1.6	21.0 ± 3.8	22.0 ± 1.1	32.0 ± 1.9
丰富度 Richness	7.0 ± 0.2	6.0 ± 0.8	6.0 ± 0.5	7.0 ± 0.5
均匀度 Evenness	0.8 ± 0.1	0.8 ± 0.1	0.8 ± 0.1	0.7 ± 0.1
寄生性昆虫 Parasitoids
多度 Abundance	15.0 ± 2.1	35.0 ± 5.3	53.0 ± 3.0	54.0 ± 11.6^*
丰富度 Richness	3.0 ± 0.2	3.0 ± 0.2	3.0 ± 0.4	4.0 ± 0.1
均匀度 Evenness	0.6 ± 0.1	0.6 ± 0.1	0.4 ± 0.1	0.5 ± 0.1
腐食性节肢动物 Detritivorous arthropod
多度 Abundance	191.0 ± 3.0	150.0 ± 4.5	154.0 ± 10.0	143.0 ± 3.9
丰富度 Richness	4.0 ± 0.2	4.0 ± 0.2	4.0 ± 0.2	4.0 ± 0.2
均匀度 Evenness	0.5 ± 0.1	0.5 ± 0.1	0.6 ± 0.1	0.7 ± 0.1

	种 Species
蛛形纲 Arachnida
皿蛛科 Linyphiidae	隆背微蛛 Erigone prominens
	草间小黑蛛 Erigonidium graminicolum
蟹蛛科 Thomisidae	三突花蛛 Misumenops tricuspidatus
球腹蛛科 Theridiidae	八斑球腹蛛 Theridion octomaculatum
圆蛛科 Araneidae	灰斑新圆蛛 Neoscona griseomaculata
	大腹圆蛛 Araneus ventricosus
	黄褐新圆蛛 Neoscone doenitzi
肖蛸科 Tetragnathidae	卵腹肖蛸 Tetragnatha shkokiana
	鳞纹肖蛸 T. squamata
叶螨科 Tetranychidae	麦叶爪螨 Pentfaleus major
弹尾纲 Collembola
长角跳虫科 Entomobryidae	长角跳虫 Entomobrya sp.
昆虫纲 Insecta
剑角蝗科 Acrididae	中华剑角蝗 Acrida cinerea
宽蝽科 Veliidae	宽蝽 Microvelia donglasi
盲蝽科 Miridae	赤须盲蝽 Trigonotylus ruficornis
长蝽科 Lygaeidae	大眼长蝽 Geocoris pallidipennis
缘蝽科 Coreidae	平肩棘缘蝽 Cletus tenuis
叶蝉科 Cicadellidae	大青叶蝉 Cicadella viridis
	电光叶蝉 Inazuma dorsalis
	黑尾叶蝉 Nephotettix bipunctatus
	条沙叶蝉 Psammotettix striatus
飞虱科 Delphacidae	灰飞虱 Laodelphax striatellus
蚜科 Aphididae	麦长管蚜 Sitobion avenae
	禾谷缢管蚜 Rhopalosiphum padi
草蛉科 Chrysopidae	大草蛉 Chrysopa septempunctata
隐翅虫科 Staphylinidae	小黄立突眼隐翅虫 Stenus.dissimilis
蛛甲科 Ptinidae	蛛甲1种
花萤科 Cantharidae	花萤1种
瓢甲科 Coccinellidae	四星瓢虫 Hyperaspis repensis
	黑襟毛瓢虫 Scymnus hoffmanni
	龟纹瓢虫 Propylea japonica
	七星瓢虫 Coccinella septempunctata
叶甲科 Chrysomelinae	黄曲条跳甲 Phyllotreta striolata
螟蛾科 Pyralidae	印度谷螟 Plodia interpunctella
夜蛾科 Noctuidae	黏虫 Mythimna separata
瘿蚊科 Cecidomyiidae	麦红吸浆虫 Sitodiplosis mosellana
库蚊科Culicidae	库蚊1种
摇蚊科 Chironomidae	稻摇蚊 Chironomus oryzae
蛾蠓科 Psychodidae	蛾蠓1种
长足虻科 Dolichopodidae	长足虻1种
舞虻科 Empididae	舞虻1种
食蚜蝇科 Syrphidae	黑带食蚜蝇 Episyrphus balteata
鼓翅蝇科 Sepsidae	鼓翅蝇1种
秆蝇科 Chloropidae	麦黄秆蝇 Chlorops mugivora
蚤蝇科 Phoridae	蚤蝇1种
花蝇科 Anthomyiidae	灰地种蝇 Delia platura
姬蜂科 Ichneumonidae	食蚜蝇姬蜂 Diplozon laetatorius
茧蜂科 Braconidae	螟蛉绒茧蜂 Apanteles ruficrus
蚜茧蜂科 Aphidiidae	麦蚜茧蜂 Ephedrus plagialor
瘿蜂科 CyniPidae	瘿蜂1种
蚜小蜂科 Aphelinidae	蚜小蜂 Aphytis sp.
缨小蜂科 Mymaridae	叶蝉柄翅小蜂 Lymaenon longicrus
柄腹细蜂科 Heloridae	柄腹细蜂 1种

大气CO₂浓度和气温升高对麦田节肢动物群落的影响

Effects of elevated CO₂ and increased temperature on wheat field arthropod community

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 4

参考文献 23

相关文章 15

编辑推荐

Metrics

本文评价

[1]	顾婧婧, 刘宜卓, 苏杨. 基层地方政府在完成《昆蒙框架》中的作用和难点: 基于《联合国气候变化框架公约》任务的比较[J]. 生物多样性, 2025, 33(3): 24585-.
[2]	姚祝, 魏雪, 马金豪, 任晓, 王玉英, 胡雷, 吴鹏飞. 气候暖湿化对高寒草甸土壤线虫群落的短期影响[J]. 生物多样性, 2024, 32(5): 23483-.
[3]	吴琪, 张晓青, 杨雨婷, 周艺博, 马毅, 许大明, 斯幸峰, 王健. 浙江钱江源-百山祖国家公园庆元片区叶附生苔多样性及其时空变化[J]. 生物多样性, 2024, 32(4): 24010-.
[4]	曹可欣, 王敬雯, 郑国, 武鹏峰, 李英滨, 崔淑艳. 降水格局改变及氮沉降对北方典型草原土壤线虫多样性的影响[J]. 生物多样性, 2024, 32(3): 23491-.
[5]	冯莉. 国际法视野下生物多样性和气候变化的协同治理[J]. 生物多样性, 2023, 31(7): 23110-.
[6]	陈哲涵, 尹进, 叶吉, 刘冬伟, 毛子昆, 房帅, 蔺菲, 王绪高. 增温对东北温带次生林草本群落季节动态的影响[J]. 生物多样性, 2023, 31(5): 23059-.
[7]	姚雪, 陈星, 戴尊, 宋坤, 邢诗晨, 曹宏彧, 邹璐, 王健. 采集策略对叶附生苔类植物发现概率及物种多样性的重要性[J]. 生物多样性, 2023, 31(4): 22685-.
[8]	邵雯雯, 范国祯, 何知舟, 宋志平. 多地同质园实验揭示普通野生稻的表型可塑性与本地适应性[J]. 生物多样性, 2023, 31(3): 22311-.
[9]	桑佳文, 宋创业, 贾宁霞, 贾元, 刘长成, 乔鲜果, 张琳, 袁伟影, 吴冬秀, 李凌浩, 郭柯. 青藏高原植被调查与制图评估[J]. 生物多样性, 2023, 31(3): 22430-.
[10]	王金洲, 徐靖. “基于自然的解决方案”应对生物多样性丧失和气候变化: 进展、挑战和建议[J]. 生物多样性, 2023, 31(2): 22496-.
[11]	李季蔓, 靳楠, 胥毛刚, 霍举颂, 陈小云, 胡锋, 刘满强. 不同干旱水平下蚯蚓对番茄抗旱能力的影响[J]. 生物多样性, 2022, 30(7): 21488-.
[12]	朱瑞良, 马晓英, 曹畅, 曹子寅. 中国苔藓植物多样性研究进展[J]. 生物多样性, 2022, 30(7): 22378-.
[13]	祖奎玲, 王志恒. 山地物种海拔分布对气候变化响应的研究进展[J]. 生物多样性, 2022, 30(5): 21451-.
[14]	井新, 蒋胜竞, 刘慧颖, 李昱, 贺金生. 气候变化与生物多样性之间的复杂关系和反馈机制[J]. 生物多样性, 2022, 30(10): 22462-.
[15]	乔慧捷, 胡军华. 利用数值模拟重构物种多样性格局的形成过程[J]. 生物多样性, 2022, 30(10): 22456-.