生物多样性 ›› 2021, Vol. 29 ›› Issue (7): 980-994. DOI: 10.17520/biods.2020470
所属专题: 传粉生物学; 昆虫多样性与生态功能
谢正华1,*(), 王有琼1, 曹军2, 王健敏3, 安建东4
收稿日期:
2020-12-20
接受日期:
2021-04-14
出版日期:
2021-07-20
发布日期:
2021-05-28
通讯作者:
* 谢正华 E-mail: cnbees@gmail.com
基金资助:
Zhenghua Xie1,*(), Youqiong Wang1, Jun Cao2, Jianmin Wang3, Jiandong An4
Received:
2020-12-20
Accepted:
2021-04-14
Online:
2021-07-20
Published:
2021-05-28
Contact:
* Zhenghua Xie E-mail: cnbees@gmail.com
摘要:
全球传粉昆虫多样性正在下降, 如何保障农林生态系统传粉功能是当前研究的热点。理论上说, 传粉功能不仅与生态系统的传粉昆虫多样性相关, 还与生态系统的调节能力有关。近年来, 学者们逐渐认识到授粉生态弹性对传粉功能的影响。本文在回顾已有研究的基础之上, 总结传粉昆虫授粉生态弹性的内涵, 厘清授粉生态弹性与工程弹性、稳定性和抗性的异同。目前, 学者对授粉生态弹性形成机制开展广泛探讨, 提出功能冗余假说、密度补偿假说、响应多样性假说、连接周转假说和跨尺度弹性假说, 但这5个假说间的关系仍不清楚, 存在一词多义、词意混淆等现象。我们依次阐述功能冗余假说、密度补偿假说、响应多样性假说、连接周转假说和跨尺度弹性假说, 介绍不同假说中授粉生态弹性形成过程、研究热点和发展动态。通过解析授粉生态弹性的形成机制可知, 5个假说在内涵上存在紧密联系, 它们从不同空间尺度和研究对象下解释传粉昆虫授粉生态弹性的形成机制。未来授粉生态弹性研究将整合传粉昆虫群落动态和传粉功能动态的量化方法, 通过实验验证5个假说的合理性, 并揭示不同假说间的联系, 由此阐明授粉生态弹性的发生条件、形成阈值和动态规律。随着研究的深入, 授粉生态弹性理论有望用于指导农林生态系统传粉功能的经营管理。
谢正华, 王有琼, 曹军, 王健敏, 安建东 (2021) 传粉昆虫下降背景下的授粉生态弹性: 内涵、机制和展望. 生物多样性, 29, 980-994. DOI: 10.17520/biods.2020470.
Zhenghua Xie, Youqiong Wang, Jun Cao, Jianmin Wang, Jiandong An (2021) Ecological resilience of pollination in the face of pollinator decline: Content, mechanism and perspective. Biodiversity Science, 29, 980-994. DOI: 10.17520/biods.2020470.
生态现象/过程 Ecological phenomenon/process | 不同术语(参考文献) Glossary (references) |
---|---|
生态系统受到一定程度的外界干扰/压力时, 系统通过吸收干扰和重组系统内部结构或组分, 使生态系统功能保持不变或维持在可接受的水平。 Ecosystems under outer disturbances/pressures absorb the disturbances by reorganizing the inner structures or components to let the ecosystem functioning remain unchanged or at an acceptable level. | 主流术语: 生态弹性 其他术语: 抗性; 生态系统弹性; 补偿性 Main terms: ecological resilience ( Other terms: resistance ( |
生态系统在干扰和压力后恢复到平衡点的能力, 或生态系统恢复到平衡点所需要的时间。 The capability for ecosystems to return to an equilibrium point following a disturbance or pressure event, or the time for ecosystems to return to an equilibrium point after disturbance or pressure event. | 主流术语: 工程弹性 其他术语: 弹性; 系统性弹性; 稳定性; 伸缩性 Main terms: engineering resilience ( Other terms: resilience ( |
生态系统维持生态功能不变的现象, 对生态系统运行状态的一种表观性描述。通常不涉及生态系统功能的维持机制。 A description for the status of ecosystems which has a stable and invariable function. Generally, the underlying mechanisms for ecosystem functioning are not concerned. | 主流术语: 稳定性 其他术语: 持续性 Main terms: stability ( Other terms: persistence ( |
生态系统结构或组成在外界干扰和压力发生时未发生变化的现象 No change in ecosystem structures and components under outer disturbances /pressures | 主流术语: 抗性 其他术语: 补偿性 Main terms: resistance ( Other terms: compensation ( |
表1 生态弹性内涵及其与相似生态过程的异同
Table 1 The content of ecological resilience and its difference with other ecological processes
生态现象/过程 Ecological phenomenon/process | 不同术语(参考文献) Glossary (references) |
---|---|
生态系统受到一定程度的外界干扰/压力时, 系统通过吸收干扰和重组系统内部结构或组分, 使生态系统功能保持不变或维持在可接受的水平。 Ecosystems under outer disturbances/pressures absorb the disturbances by reorganizing the inner structures or components to let the ecosystem functioning remain unchanged or at an acceptable level. | 主流术语: 生态弹性 其他术语: 抗性; 生态系统弹性; 补偿性 Main terms: ecological resilience ( Other terms: resistance ( |
生态系统在干扰和压力后恢复到平衡点的能力, 或生态系统恢复到平衡点所需要的时间。 The capability for ecosystems to return to an equilibrium point following a disturbance or pressure event, or the time for ecosystems to return to an equilibrium point after disturbance or pressure event. | 主流术语: 工程弹性 其他术语: 弹性; 系统性弹性; 稳定性; 伸缩性 Main terms: engineering resilience ( Other terms: resilience ( |
生态系统维持生态功能不变的现象, 对生态系统运行状态的一种表观性描述。通常不涉及生态系统功能的维持机制。 A description for the status of ecosystems which has a stable and invariable function. Generally, the underlying mechanisms for ecosystem functioning are not concerned. | 主流术语: 稳定性 其他术语: 持续性 Main terms: stability ( Other terms: persistence ( |
生态系统结构或组成在外界干扰和压力发生时未发生变化的现象 No change in ecosystem structures and components under outer disturbances /pressures | 主流术语: 抗性 其他术语: 补偿性 Main terms: resistance ( Other terms: compensation ( |
图1 传粉昆虫下降背景下授粉生态弹性不同机制示意图。以土地类型变化为代表的全球变化引起传粉昆虫群落结构变化。在①功能冗余、②密度补偿、③响应多样性、④连接周转; ⑤跨尺度弹性机制作用下, 传粉功能团保障传粉功能(如植物柱头上沉降花粉数量)在可接受的水平, 形成授粉生态弹性。
Fig. 1 The framework showing the different mechanisms of ecological resilience of pollination in the face of pollinator decline. The global changes, such as land use change, invoke the variations in pollinator community. Under the mechanisms of ①functional redundancy, ②density compensation, ③response diversity, ④interaction turnover; ⑤cross-scale resilience, pollinator communities are able to deliver an acceptable level of pollination functioning (e.g. pollen grains on stigma surface), forming the ecological resilience of pollination.
图2 不同传粉功能团间功能冗余引起授粉生态弹性的机制示意图。假设生态系统中3个传粉功能团(a、b和c)均为开花植物授粉(A), 当传粉功能团a沉降的花粉(黄色)数量和传粉功能团c沉降的花粉(橙色)数量下降时, 传粉功能团b沉降的花粉(蓝色)数量增加(B)。柱头花粉数总量保持不变, 传粉昆虫群落形成授粉生态弹性。
Fig. 2 Conceptual diagram showing the mechanical effect of functional redundancy among functional groups of pollinators on ecological resilience of pollination. Three functional groups (a, b and c) are supposed to pollinate the flowering plants in the ecosystems (A). When the amount of pollens delivered by functional group a (yellow) and functional group c (orange) decreases, the amount of pollens delivered by functional group b (blue) increases (B). The number of pollens deposited on stigma surfaces does not change. The pollinator communities have the ecological resilience of pollination.
图3 密度补偿作用引起授粉生态弹性的机制示意图。假设生态系统存在传粉功能团a和传粉功能团b (A), 全球变化下生态系统由功能团a的4个体和功能团b的5个体的传粉昆虫群落(A)转变为功能团a的2个体和功能团b的9个体的传粉昆虫群落(B)。当生态系统内传粉功能团a访花频率下降时, 传粉功能团b访花频率上升, 反之亦然(B)。虽然不同传粉功能团传粉效率(如单次访花花粉沉降量)存在差异, 但沉降花粉数量保持不变, 形成授粉生态弹性。
Fig. 3 Conceptual diagram illustrating the mechanical effect of density compensation on ecological resilience of pollination. Two functional groups of pollinators (a and b) are supposed to deliver pollens on stigma surfaces (A). In the face of global changes, the pollinator communities with 4 individuals of functional group a and 5 individuals of functional group b (A) is transformed to a different pollinator communities with 2 individuals of functional group a and 9 individuals of functional group b (B). The visit density of functional group a decreases, but the visit density of functional group b increase, and vice versa (B). Due to the differences in pollination efficiency (e.g. pollen deposition per visit), the overall pollen numbers delivered by different pollinator communities are the same. The pollinator communities have the ecological resilience of pollination.
图4 响应多样性引起授粉生态弹性的机制示意图。假设传粉功能团在个体大小和巢穴位置等响应性状方面表现出多样性, 不同个体大小的传粉昆虫(A)对自然生境的空间响应尺度存在差异, 个体大的传粉昆虫响应尺度大于个体小的传粉昆虫(B)。同时, 不同巢穴位置的传粉昆虫(C)种群数量对自然生境呈现不同的响应规律, 部分传粉昆虫种群数量随自然生境百分率的下降而下降, 但其他传粉昆虫种群数量保持不变甚至增长(D)。传粉功能团的响应多样性可能通过效应多样性调节传粉功能, 使植物柱头花粉沉降数量保持不变, 形成授粉生态弹性(E)。
Fig. 4 Conceptual diagram showing the mechanical effect of response diversity on ecological resilience of pollination. Pollinators are supposed to be different in body size and nesting site. The pollinators with different body sizes (A) respond to natural habitats at different spatial scales, with a relatively large scale of effect for the large pollinators compared to a relatively small scale of effect for the smaller pollinators (B). Meanwhile, the pollinators with different nesting sites (C) respond differently to the natural habitats, with a decrease of populations for most pollinators along the loss of semi-natural habitats but an increase or stability of populations for other pollinators (D). Response diversity can affect ecosystem pollination functioning through effect diversity. The overall pollen numbers delivered by pollinators keep the same. The pollinator communities have the ecological resilience of pollination (E).
图5 连接周转引起授粉生态弹性的机制示意图。在生态系统中, 假设原传粉网络存在3种传粉昆虫(a1, a2, a3)和3种开花植物(p1, p2, p3) (A)。干扰作用下, 传粉昆虫和开花植物间部分连接消失但新的连接形成, 网络连接发生重连(B); 或者传粉昆虫下降, 对应的连接消失, 或新的传粉昆虫(a4)进入网络, 建立新连接, 传粉昆虫发生物种周转(C)。在传粉网络重连和物种周转的共同作用下, 传粉昆虫和开花植物形成传粉网络连接周转(D)。对开花植物来说, 连接周转前后传粉昆虫群落组成存在差异, 但原传粉网络中的传粉昆虫和连接周转后的传粉昆虫传播等量花粉, 形成授粉生态弹性(E)。黑线示意周转前传粉昆虫同开花植物间的联系, 红线示意形成的新连接。
Fig. 5 Conceptual diagram illustrating the mechanical effect of interaction turnover on ecological resilience of pollination. The ecosystem is hypothesized to have an original pollination network with three pollinators (a1, a2, a3) and three plants (p1, p2, p3) (A). Under disturbances, some interactions are lost but new interactions occur, forming interaction rewiring (B). Interactions are also lost as a result of pollinators decline, but new interactions is built as new pollinators (a4) enter the pollination network, resulting from species turnover of pollinators (C). The combined effect of interaction rewiring and species turnover explains an interaction turnover of the pollination network (D). For plants, their pollinator assemblages are different before and after interaction turnover, however, the amount of pollens delivered by the pollinator assemblages is the same. The pollinator communities have the ecological resilience of pollination (E). Black lines indicate the original interactions before interaction turnover and red lines indicate newly-built interactions after interaction turnover.
图6 跨尺度弹性引起授粉生态弹性的机制示意图。在生态系统中, 假设空间分布的开花植物a、b、c、d、e和f存在大、中、小3种传粉功能团, 传粉功能团空间传粉尺度(或空间搜索范围)分别约为300 m、1,000 m和1,500 m, 个体大的传粉昆虫空间跨尺度为开花植物传粉(A)。3种传粉功能团在个体大小(body size)轴上形成不连续性的分布(B)。开花植物a接收3个传粉功能团传粉, b、d和f接收2个传粉功能团传粉, c和e仅接收1个传粉功能团传粉, 因此开花植物a的传粉功能团跨尺度传粉功能冗余程度高于其他开花植物(C)。以开花植物a为对象, 当某搜索范围(如300 m)的传粉功能团访花密度下降时, 其他尺度(如1,500 m)的传粉功能团增加访花密度, 传播等量花粉, 形成授粉生态弹性(D)。在(C)和(D)中, 线条长度示意对应的传粉昆虫空间传粉范围, 线条宽度示意传粉昆虫空间传粉功能。
Fig. 6 Conceptual diagram showing the mechanical effect of cross-scale resilience on ecological resilience of pollination. The ecosystems are hypothesized to have three functional groups with large (1,500 m), medium (1,000 m) and small (300 m) spatial scales (i.e., foraging ranges), respectively, and they pollinate flowering plants a, b, c, d, e and f spatially distributed in ecosystems. The large-sized functional groups pollinate plants across scale (A). The three functional groups of pollinators are distributed discontinuously along the x-axis of body size (B). Flowering plant a is pollinated by three functional groups, flowering plant b, d and f are pollinated by two functional groups, and flowering plant c and e are pollinated by just one functional groups. Therefore, the level of cross-scale redundancy of pollinator assemblages for plant a is higher than that of other plants (C). If the visit density of a certain functional group of pollinators with a specific foraging range (e.g. 300 m) declines (e.g. plant a), other functional groups of pollinators with a large spatial foraging range (e.g. 1,500 m) increase their visit densities. The amount of pollens delivered by the pollinator assemblages on the stigma surface of plant a is similar. The pollinator communities have the ecological resilience of pollination (D). In (C) and (D), the lengths of lines corresponding to the pollinators indicate the foraging ranges of pollinators and the widths of lines quantify their pollination functioning.
[1] |
Aizen MA, Harder LD (2009) The global stock of domesticated honey bees is growing slower than agricultural demand for pollination. Current Biology, 19, 915-918.
DOI URL |
[2] |
Allen CR, Gunderson L, Johnson AR (2005) The use of discontinuities and functional groups to assess relative resilience in complex systems. Ecosystems, 8, 958-966.
DOI URL |
[3] |
Angeler DG, Allen CR (2016) Quantifying resilience. Journal of Applied Ecology, 53, 617-624.
DOI URL |
[4] | Astegiano J, Guimarães PR Jr, Cheptou PO, Vidal MM, Mandai CY, Ashworth L, Massol F (2015) Persistence of plants and pollinators in the face of habitat loss: Insights from trait-based metacommunity models. Advances in Ecological Research, 53, 201-257. |
[5] |
Baho DL, Allen CR, Garmestani A, Fried-Petersen H, Renes SE, Gunderson L, Angeler DG (2017) A quantitative framework for assessing ecological resilience. Ecology and Society, 22, 1-17.
DOI PMID |
[6] |
Bartomeus I, Cariveau DP, Harrison T, Winfree R (2018) On the inconsistency of pollinator species traits for predicting either response to land-use change or functional contribution. Oikos, 127, 306-315.
DOI URL |
[7] |
Bascompte J, Jordano P (2007) Plant-animal mutualistic networks: The architecture of biodiversity. Annual Review of Ecology, Evolution, and Systematics, 38, 567-593.
DOI URL |
[8] |
Biesmeijer JC (2006) Parallel declines in pollinators and insect-pollinated plants in Britain and the Netherlands. Science, 313, 351-354.
PMID |
[9] |
Biggs R, Schlüter M, Biggs D, Bohensky EL, BurnSilver S, Cundill G, Dakos V, Daw TM, Evans LS, Kotschy K, Leitch AM, Meek C, Quinlan A, Raudsepp-Hearne C, Robards MD, Schoon ML, Schultz L, West PC (2012) Toward principles for enhancing the resilience of ecosystem services. Annual Review of Environment and Resources, 37, 421-448.
DOI URL |
[10] |
Blüthgen N, Klein AM (2011) Functional complementarity and specialisation: The role of biodiversity in plant-pollinator interactions. Basic and Applied Ecology, 12, 282-291.
DOI URL |
[11] | Brand FS, Jax K (2007) Focusing the meaning(s) of resilience: Resilience as a descriptive concept and a boundary object. Ecology and Society, 12, 23. |
[12] | Brosi BJ, Briggs HM (2013) Single pollinator species losses reduce floral fidelity and plant reproductive function. Proceedings of the National Academy of Sciences, USA, 110, 13044-13048. |
[13] |
Burkle LA, Alarcón R (2011) The future of plant-pollinator diversity: Understanding interaction networks across time, space, and global change. American Journal of Botany, 98, 528-538.
DOI PMID |
[14] |
Burkle LA, Marlin JC, Knight TM (2013) Plant-pollinator interactions over 120 years: Loss of species, co-occurrence, and function. Science, 339, 1611-1615.
DOI PMID |
[15] |
CaraDonna PJ, Petry WK, Brennan RM, Cunningham JL, Bronstein JL, Waser NM, Sanders NJ (2017) Interaction rewiring and the rapid turnover of plant-pollinator networks. Ecology Letters, 20, 385-394.
DOI PMID |
[16] |
Cariveau DP, Williams NM, Benjamin FE, Winfree R (2013) Response diversity to land use occurs but does not consistently stabilise ecosystem services provided by native pollinators. Ecology Letters, 16, 903-911.
DOI PMID |
[17] | Chacoff NP, Aizen MA, Aschero V (2008) Proximity to forest edge does not affect crop production despite pollen limitation. Proceedings of the Royal Society B: Biological Sciences, 275, 907-913. |
[18] |
Connell SD, Ghedini G (2015) Resisting regime-shifts: The stabilising effect of compensatory processes. Trends in Ecology & Evolution, 30, 513-515.
DOI URL |
[19] |
Connell SD, Nimmo DG, Ghedini G, Mac Nally R, Bennett AF (2016) Ecological resistance—Why mechanisms matter: A reply to Sundstrom et al. Trends in Ecology & Evolution, 31, 413-414.
DOI URL |
[20] |
Dicks LV, Abrahams A, Atkinson J, Biesmeijer J, Bourn N, Brown C, Brown MJF, Carvell C, Connolly C, Cresswell JE, Croft P, Darvill B, De Zylva P, Effingham P, Fountain M, Goggin A, Harding D, Harding T, Hartfield C, Heard MS, Heathcote R, Heaver D, Holland J, Howe M, Hughes B, Huxley T, Kunin WE, Little J, Mason C, Memmott J, Osborne J, Pankhurst T, Paxton RJ, Pocock MJO, Potts SG, Power EF, Raine NE, Ranelagh E, Roberts S, Saunders R, Smith K, Smith RM, Sutton P, Tilley LAN, Tinsley A, Tonhasca A, Vanbergen AJ, Webster S, Wilson A, Sutherland WJ (2012) Identifying key knowledge needs for evidence-based conservation of wild insect pollinators: A collaborative cross-sectoral exercise. Insect Conservation and Diversity, 6, 435-446.
DOI URL |
[21] |
Dudney J, Hobbs RJ, Heilmayr R, Battles JJ, Suding KN (2018) Navigating novelty and risk in resilience management. Trends in Ecology & Evolution, 33, 863-873.
DOI URL |
[22] |
Elmqvist T, Folke C, Nyström M, Peterson G, Bengtsson J, Walker B, Norberg J (2003) Response diversity, ecosystem change, and resilience. Frontiers in Ecology and the Environment, 1, 488-494.
DOI URL |
[23] |
Fantinato E, Del Vecchio S, Gaetan C, Buffa G (2019) The resilience of pollination interactions: Importance of temporal phases. Journal of Plant Ecology, 12, 157-162.
DOI |
[24] |
Fischer J, Lindenmayer DB, Blomberg SP, Montague-Drake R, Felton A, Stein JA (2007) Functional richness and relative resilience of bird communities in regions with different land use intensities. Ecosystems, 10, 964-974.
DOI URL |
[25] |
Folke C, Carpenter S, Walker B, Scheffer M, Elmqvist T, Gunderson L, Holling CS (2004) Regime shifts, resilience, and biodiversity in ecosystem management. Annual Review of Ecology, Evolution, and Systematics, 35, 557-581.
DOI URL |
[26] |
Forys EA, Allen CR (2002) Functional group change within and across scales following invasions and extinctions in the everglades ecosystem. Ecosystems, 5, 339-347.
DOI URL |
[27] |
García Y, Clara Castellanos M, Pausas JG (2018) Differential pollinator response underlies plant reproductive resilience after fires. Annals of Botany, 122, 961-971.
DOI PMID |
[28] | Garibaldi LA, Aizen MA, Klein AM, Cunningham SA, Harder LD (2011) Global growth and stability of agricultural yield decrease with pollinator dependence. Proceedings of the National Academy of Sciences, USA, 108, 5909-5914. |
[29] | Garibaldi LA, Bartomeus I, Bommarco R, Klein AM, Cunningham SA, Aizen MA, Boreux V, Garratt MPD, Carvalheiro LG, Kremen C (2015) Trait matching of flower visitors and crops predicts fruit set better than trait diversity. Journal of Applied Ecology, 52, 1437-1444. |
[30] |
Gitay H, Wilson JB, Lee WG (1996) Species redundancy: A redundant concept? Journal of Ecology, 84, 121-124.
DOI URL |
[31] |
Gonzalez A, Loreau M (2009) The causes and consequences of compensatory dynamics in ecological communities. Annual Review of Ecology, Evolution, and Systematics, 40, 393-414.
DOI URL |
[32] |
Greenleaf SS, Williams NM, Winfree R, Kremen C (2007) Bee foraging ranges and their relationship to body size. Oecologia, 153, 589-596.
PMID |
[33] |
Grimm V, Wissel C (1997) Babel, or the ecological stability discussions: An inventory and analysis of terminology and a guide for avoiding confusion. Oecologia, 109, 323-334.
DOI PMID |
[34] | Gunderson LH (2000) Ecological resilience—In theory and application. Annual Review of Ecology, Evolution and Systematics, 31, 425-439. |
[35] |
Hagen M, Wikelski M, Kissling WD (2011) Space use of bumblebees (Bombus spp.) revealed by radio-tracking. PLoS ONE, 6, e19997.
DOI URL |
[36] | Hallett AC, Mitchell RJ, Chamberlain ER, Karron JD (2017) Pollination success following loss of a frequent pollinator: The role of compensatory visitation by other effective pollinators. AoB PLANTS, 9, plx020. |
[37] |
Holling CS (1973) Resilience and stability of ecological systems. Annual Review of Ecology and Systematics, 4, 1-23.
DOI URL |
[38] |
Holling CS (1992) Cross-scale morphology, geometry, and dynamics of ecosystems. Ecological Monographs, 62, 447-502.
DOI URL |
[39] | Houlahan JE, Currie DJ, Cottenie K, Cumming GS, Ernest SKM, Findlay CS, Fuhlendorf SD, Gaedke U, Legendre P, Magnuson JJ, McArdle BH, Muldavin EH, Noble D, Russell R, Stevens RD, Willis TJ, Woiwod IP, Wondzell SM (2007) Compensatory dynamics are rare in natural ecological communities. Proceedings of the National Academy of Sciences, USA, 104, 3273-3277. |
[40] |
Isbell F, Craven D, Connolly J, Loreau M, Schmid B, Beierkuhnlein C, Bezemer TM, Bonin C, Bruelheide H, de Luca E, Ebeling A, Griffin JN, Guo QF, Hautier Y, Hector A, Jentsch A, Kreyling J, Lanta V, Manning P, Meyer ST, Mori AS, Naeem S, Niklaus PA, Polley HW, Reich PB, Roscher C, Seabloom EW, Smith MD, Thakur MP, Tilman D, Tracy BF, van der Putten WH, van Ruijven J, Weigelt A, Weisser WW, Wilsey B, Eisenhauer N (2015) Biodiversity increases the resistance of ecosystem productivity to climate extremes. Nature, 526, 574-577.
DOI URL |
[41] |
Jiang L (2007) Density compensation can cause no effect of biodiversity on ecosystem functioning. Oikos, 116, 324-334.
DOI URL |
[42] |
Kaiser-Bunbury CN, Mougal J, Whittington AE, Valentin T, Gabriel R, Olesen JM, Blüthgen N (2017) Ecosystem restoration strengthens pollination network resilience and function. Nature, 542, 223-227.
DOI URL |
[43] |
Kaiser-Bunbury CN., Muff S, Memmott J, Müller CB, Caflisch A (2010) The robustness of pollination networks to the loss of species and interactions: A quantitative approach incorporating pollinator behaviour. Ecology Letters, 13, 442-452.
DOI PMID |
[44] | Karp DS, Ziv G, Zook J, Ehrlich PR, Daily GC (2011) Resilience and stability in bird guilds across tropical countryside. Proceedings of the National Academy of Sciences, USA, 108, 21134-21139. |
[45] |
Klaus F, Tscharntke T, Uhler J, Grass I (2021) Calcareous grassland fragments as sources of bee pollinators for the surrounding agricultural landscape. Global Ecology and Conservation, 26, e01474.
DOI URL |
[46] | Klein AM, Steffan-Dewenter I, Tscharntke T (2003) Fruit set of highland coffee increases with the diversity of pollinating bees. Proceedings of the Royal Society B: Biological Sciences, 270, 955-961. |
[47] |
Kremen C, Williams NM, Aizen MA, Gemmill-Herren B, LeBuhn G, Minckley R, Packer L, Potts SG, Roulston T, Steffan-Dewenter I, Vázquez DP, Winfree R, Adams L, Crone EE, Greenleaf SS, Keitt TH, Klein AM, Regetz J, Ricketts TH (2007) Pollination and other ecosystem services produced by mobile organisms: A conceptual framework for the effects of land-use change. Ecology Letters, 10, 299-314.
DOI URL |
[48] |
Kühsel S, Blüthgen N (2015) High diversity stabilizes the thermal resilience of pollinator communities in intensively managed grasslands. Nature Communications, 6, 7989.
DOI PMID |
[49] | Lake PS (2013) Resistance, resilience and restoration. Ecological Management & Restoration, 14, 20-24. |
[50] |
Lasky JR, Uriarte M, Muscarella R (2016) Synchrony, compensatory dynamics, and the functional trait basis of phenological diversity in a tropical dry forest tree community: Effects of rainfall seasonality. Environmental Research Letters, 11, 115003.
DOI URL |
[51] |
Martin EA, Feit B, Requier F, Friberg H, Jonsson M (2019) Assessing the resilience of biodiversity-driven functions in agroecosystems under environmental change. Advances in Ecological Research, 60, 59-123.
DOI |
[52] | Memmott J, Waser NM, Price MV (2004) Tolerance of pollination networks to species extinctions. Proceedings of the Royal Society of London Series B: Biological Sciences, 271, 2605-2611. |
[53] |
Miguet P, Jackson HB, Jackson ND, Martin AE, Fahrig L (2016) What determines the spatial extent of landscape effects on species? Landscape Ecology, 31, 1177-1194.
DOI URL |
[54] |
Mori AS (2016) Resilience in the studies of biodiversity-ecosystem functioning. Trends in Ecology & Evolution, 31, 87-89.
DOI URL |
[55] |
Mori AS, Furukawa T, Sasaki T (2013) Response diversity determines the resilience of ecosystems to environmental change. Biological Reviews, 88, 349-364.
DOI URL |
[56] |
Naeem S (1998) Species redundancy and ecosystem reliability. Conservation Biology, 12, 39-45.
DOI URL |
[57] |
Nash KL, Allen CR, Angeler DG, Barichievy C, Eason T, Garmestani AS, Graham NAJ, Granholm D, Knutson M, Nelson RJ, Nyström M, Stow CA, Sundstrom SM (2014) Discontinuities, cross-scale patterns, and the organization of ecosystems. Ecology, 95, 654-667.
DOI URL |
[58] |
Nash KL, Graham NAJ, Jennings S, Wilson SK, Bellwood DR (2016) Herbivore cross-scale redundancy supports response diversity and promotes coral reef resilience. Journal of Applied Ecology, 53, 646-655.
DOI URL |
[59] |
Nimmo DG, Mac Nally R, Cunningham SC, Haslem A, Bennett AF (2015) Vive la résistance: Reviving resistance for 21st century conservation. Trends in Ecology & Evolution, 30, 516-523.
DOI URL |
[60] | Öckinger E, Schweiger O, Crist TO, Debinski DM, Krauss J, Kuussaari M, Petersen JD, Pöyry J, Settele J, Summerville KS, Bommarco R (2010) Life-history traits predict species responses to habitat area and isolation: A cross-continental synthesis. Ecology Letters, 13, 969-979. |
[61] |
Oliver TH, Heard MS, Isaac NJB, Roy DB, Procter D, Eigenbrod F, Freckleton R, Hector A, Orme CDL, Petchey OL, Proença V, Raffaelli D, Suttle KB, Mace GM, Martín-López B, Woodcock BA, Bullock JM (2015) Biodiversity and resilience of ecosystem functions. Trends in Ecology & Evolution, 30, 673-684.
DOI URL |
[62] |
Peterson G, Allen CR, Holling CS (1998) Ecological resilience, biodiversity, and scale. Ecosystems, 1, 6-18.
DOI URL |
[63] |
Pimm SL (1984) The complexity and stability of ecosystems. Nature, 307, 321-326.
DOI URL |
[64] |
Poisot T, Canard E, Mouillot D, Mouquet N, Gravel D (2012) The dissimilarity of species interaction networks. Ecology Letters, 15, 1353-1361.
DOI URL |
[65] |
Potts SG, Imperatriz-Fonseca V, Ngo HT, Aizen MA, Biesmeijer JC, Breeze TD, Dicks LV, Garibaldi LA, Hill R, Settele J, Vanbergen AJ (2016) Safeguarding pollinators and their values to human well-being. Nature, 540, 220-229.
DOI URL |
[66] |
Robroek BJM, Martí M, Svensson BH, Dumont MG, Veraart AJ, Jassey VEJ (2021) Rewiring of peatland plant-microbe networks outpaces species turnover. Oikos, 130, 339-353.
DOI URL |
[67] |
Rogers SR, Cajamarca P, Tarpy DR, Burrack HJ (2013) Honey bees and bumble bees respond differently to inter- and intra-specific encounters. Apidologie, 44, 621-629.
DOI URL |
[68] |
Rosenfeld JS (2002) Functional redundancy in ecology and conservation. Oikos, 98, 156-162.
DOI URL |
[69] | Scheffer M, Bolhuis JE, Borsboom D, Buchman TG, Gijzel SMW, Goulson D, Kammenga JE, Kemp B, van de Leemput IA, Levin S, Martin CM, Melis RJF, van Nes EH, Romero LM, Olde Rikkert MGM (2018) Quantifying resilience of humans and other animals. Proceedings of the National Academy of Sciences, USA, 115, 11883-11890. |
[70] | Shade A, Peter H, Allison SD, Baho DL, Berga M, Bürgmann H, Huber DH, Langenheder S, Lennon JT, Martiny JBH, Matulich KL, Schmidt TM, Handelsman J (2012) Fundamentals of microbial community resistance and resilience. Frontiers in Microbiology, 3, 417. |
[71] | Simanonok MP, Burkle LA (2014) Partitioning interaction turnover among alpine pollination networks: Spatial, temporal, and environmental patterns. Ecosphere, 5, 1-17. |
[72] |
Stavert JR, Pattemore DE, Bartomeus I, Gaskett AC, Beggs JR (2018) Exotic flies maintain pollination services as native pollinators decline with agricultural expansion. Journal of Applied Ecology, 55, 1737-1746.
DOI URL |
[73] |
Suding KN, Lavorel S, Chapin FS, Cornelissen JHC, Díaz D, Garnier E, Goldberg D, Hooper DU, Jackson ST, Navas ML (2008) Scaling environmental change through the community-level: A trait-based response-and-effect framework for plants. Global Change Biology, 14, 1125-1140.
DOI URL |
[74] |
Sundstrom SM, Angeler DG, Barichievy C, Eason T, Garmestani A, Gunderson L, Knutson M, Nash KL, Spanbauer T, Stow C, Allen CR (2018) The distribution and role of functional abundance in cross-scale resilience. Ecology, 99, 2421-2432.
DOI PMID |
[75] |
Thomson DM (2016) Local bumble bee decline linked to recovery of honey bees, drought effects on floral resources. Ecology Letters, 19, 1247-1255.
DOI PMID |
[76] |
Tscharntke T, Tylianakis JM, Rand TA, Didham RK, Fahrig L, Batáry P, Bengtsson J, Clough Y, Crist TO, Dormann CF, Ewers RM, Fründ J, Holt RD, Holzschuh A, Klein AM, Kleijn D, Kremen C, Landis DA, Laurance W, Lindenmayer D, Scherber C, Sodhi N, Steffan-Dewenter I, Thies C, van der Putten WH, Westphal C (2012) Landscape moderation of biodiversity patterns and processes—Eight hypotheses. Biological Reviews, 87, 661-685.
DOI URL |
[77] |
Tylianakis JM, Morris RJ (2017) Ecological networks across environmental gradients. Annual Review of Ecology, Evolution, and Systematics, 48, 25-48.
DOI URL |
[78] |
Vanbergen AJ, The Insect Pollinators Initiative (2013) Threats to an ecosystem service: Pressures on pollinators. Frontiers in Ecology and the Environment, 11, 251-259.
DOI URL |
[79] |
Vizentin-Bugoni J, Debastiani VJ, Bastazini VAG, Maruyama PK, Sperry JH (2020) Including rewiring in the estimation of the robustness of mutualistic networks. Methods in Ecology and Evolution, 11, 106-116.
DOI URL |
[80] | Walker BH (2020) Resilience: What it is and is not. Ecology and Society, 25(2), 11. |
[81] |
Wardwell DA, Allen CR, Peterson GD, Tyre AJ (2008) A test of the cross-scale resilience model: Functional richness in Mediterranean-climate ecosystems. Ecological Complexity, 5, 165-182.
DOI URL |
[82] |
Weise HN, Auge H, Baessler C, Bärlund I, Bennett EM, Berger U, Bohn F, Bonn A, Borchardt D, Brand F, Chatzinotas A, Corstanje R, de Laender F, Dietrich P, Dunker S, Durka W, Fazey I, Groeneveld J, Guilbaud CSE, Harms H, Harpole S, Harris J, Jax K, Jeltsch F, Johst K, Joshi J, Klotz S, Kühn I, Kuhlicke C, Müller B, Radchuk V, Reuter H, Rinke K, Schmitt-Jansen M, Seppelt R, Singer A, Standish RJ, Thulke HH, Tietjen B, Weitere M, Wirth C, Wolf C, Grimm V (2020) Resilience trinity: Safeguarding ecosystem functioning and services across three different time horizons and decision contexts. Oikos, 129, 445-456.
DOI URL |
[83] |
Williams NM, Crone EE, Roulston TH, Minckley RL, Packer L, Potts SG (2010) Ecological and life-history traits predict bee species responses to environmental disturbances. Biological Conservation, 143, 2280-2291.
DOI URL |
[84] | Williams NM, Isaacs R, Lonsdorf E, Winfree R, Ricketts TH (2019) Building resilience into agricultural pollination using wild pollinators. In: Agricultural Resilience, Perspectives from Ecology and Economics. (eds Gardner SM, Ramsden SJ, Hails RS), pp.109-134. Cambridge University Press, Cambridge. |
[85] |
Winfree R (2013) Global change, biodiversity, and ecosystem services: What can we learn from studies of pollination? Basic and Applied Ecology, 14, 453-460.
DOI URL |
[86] | Winfree R, Kremen C (2009) Are ecosystem services stabilized by differences among species? A test using crop pollination. Proceedings of the Royal Society B: Biological Sciences, 276, 229-237. |
[87] |
Wong MKL, Guénard B, Lewis OT (2019) Trait-based ecology of terrestrial arthropods. Biological Reviews, 94, 999-1022.
DOI URL |
[88] |
Xie ZH, Shebl MA, Pan DD, Wang JM (2020) Synergistically positive effects of brick walls and farmlands on Anthophora waltoni populations. Agricultural and Forest Entomology, 22, 328-337.
DOI URL |
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