Interaction effects of different drivers of wild bee decline and their influence on host–pathogen dynamics

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Highlights

  • Wild bee decline is a multi-factorial problem.

  • Assessment of the effect of a single driver within the context of accompanying stressors is crucial.

  • Disturbance of natural host–pathogen dynamics can lead to host extinction in extreme cases.

  • Invasive species and bee domestication can disturb host–pathogen dynamics.

  • Habitat loss, climate change and insecticides can disturb host–pathogen dynamics.

Wild bee decline is a multi-factorial problem, yet it is crucial to understand the impact of a single driver. Hereto the interaction effects of wild bee decline with multiple natural and anthropogenic stressors need to be clear. This is also true for the driver ‘pathogens’, as stressor induced disturbances of natural host–pathogen dynamics can unbalance settled virulence equilibria. Invasive species, bee domestication, habitat loss, climate changes and insecticides are recognized drivers of wild bee decline, but all influence host–pathogen dynamics as well. Many wild bee pathogens have multiple hosts, which relaxes the host-density limitation of virulence evolution. In conclusion, disturbances of bee-pathogen dynamics can be compared to a game of Russian roulette.

Introduction

The treasure chest of life, Earth's biodiversity, is under pressure. Population declines and extirpations are of the magnitude to call it the sixth major extinction event [1]. This biological annihilation impairs ecosystem services. Insect pollination underpins plant-derived ecosystem services supporting the seed set in 85% of all flowering plants [2], but direct human benefits are also gained with pollination of 76% of the leading agricultural crops [3]. Insect pollination is performed by different families of insects; herein bees (the Apiformes within the superfamily Apoidea) are the most exemplary as the nutritional needs of all their life stages are fully dependent on nectar and pollen [4].

The decline of insect pollinators, especially wild bees, is acknowledged worldwide [5, 6]. A full overview of the population decline of wild bees, their status and of the drivers thereof fall outside the scope of this review. For this we refer to the report by the International Platform on Biodiversity and Ecosystem Services and the references therein [7, 8].

Wild bee decline is often described as a multi-factorial problem. While this is true, it is also an evasive answer. In order to further comprehend this complex puzzle, three things are essential: firstly, it is important to understand the impact of single drivers within an environmental context where multiple natural and anthropogenic stressors act on wild bee populations [9]; secondly, these drivers are expected to show interaction effects which can be antagonistic or synergistic [10]; thirdly, the impact of drivers can differ based on the target species. For bumble bees the interaction among pathogens, pesticides, and diet is identified as the most crucial stressor. Although bumble bees are the best monitored wild bee species, we still only have patchy and incomplete evidence of the specific role of different drivers of bumble bee decline, with challenges associated with the setup of environmentally realistic experiments to study interacting stressors [11].

Here we will address the interaction effects of drivers of wild bee decline with the stressor parasites and viruses (from here on referred to as pathogens). When talking about bee pathogens one must recognize the historical context and knowledge gathered from the domesticated western honey bee, Apis mellifera. For example, the term honey bee viruses is persistently used, while most of these viruses have a much larger host-range and for many of them the honey bee will most likely not even be the prime host [12]. Another consequence of honey bee diseases as a key information source is a biased view on host–pathogen dynamics. In domesticated animals a pathogen is sometimes considered as an aberrant factor, which needs to be eradicated. In a natural ecosystem, however, pathogens play an important role [13]. In an undisturbed natural ecosystem the population size of a species fluctuates around the environment's carrying capacity. The population size is driven by bottom-up forces such as food and nesting availability. Top-down forces such as predation and pathogens negatively affect the population size. The driver of wild bee decline called ‘pathogens or parasites’ should therefore be seen in the context of factors which disturb natural host–pathogen dynamics. Pathogens are often not the main player regulating the population size [14] and have often evolved a virulence equilibrium with their hosts [15]. However, disturbance of the natural ecosystem can unbalance this virulence equilibrium, increasing the role of pathogens as a top-down force on a population. In extreme cases pathogens can cause dramatic declines in host populations and eventually lead to host extinction [16].

Section snippets

The influence of drivers of wild bee decline on host–pathogen dynamics

In Figure 1 we give an overview of some widely reported drivers of wild bee decline. These drivers have a direct influence on wild bee populations, but also have the potential to cause interaction effects. Interactions can be synergistic, but shared occurrence of drivers can also be neutral or antagonistic [10]. It is important to make a distinction between two types of interaction effects: firstly, interaction modification effects and secondly, interaction chain effects. Interaction

Conflicts of interest statement

None.

Acknowledgements

We acknowledge the Foundation Research-Flanders (FWO), the Belgian Science Policy Office (Belspo) and the Special Research Fund of Ghent University (BOF-UGent).

References (64)

  • J. Shukla et al.

    Amazon deforestation and climate change

    Science

    (1990)
  • G. Ceballos et al.

    Biological annihilation via the ongoing sixth mass extinction signaled by vertebrate population losses and declines

    Proc Natl Acad Sci USA

    (2017)
  • J. Ollerton et al.

    How many flowering plants are pollinated by animals?

    Oikos

    (2011)
  • A.M. Klein et al.

    Importance of pollinators in changing landscapes for world crops

    Proc Biol Sci

    (2007)
  • C.D. Michener

    The Bees of the World

    (2007)
  • J.C. Biesmeijer et al.

    Parallel declines in pollinators and insect-pollinated plants in Britain and the Netherlands

    Science

    (2006)
  • I. Koh et al.

    Modeling the status, trends, and impacts of wild bee abundance in the United States

    Proc Natl Acad Sci USA

    (2016)
  • M. Aizen et al.

    The status and trends in pollinators and pollination

  • A. Kovács-Hostyánszki et al.

    Drivers of change of pollinators, pollination networks and pollination

  • D. Goulson et al.

    Bee declines driven by combined stress from parasites, pesticides, and lack of flowers

    Science

    (2015)
  • I. Steffan-Dewenter et al.

    Do resources or natural enemies drive bee population dynamics in fragmented habitats?

    Ecology

    (2008)
  • J.F. Rabajante et al.

    Red Queen dynamics in multi-host and multi-parasite interaction system

    Sci Rep-UK

    (2015)
  • M. Chytry et al.

    Habitat invasions by alien plants: a quantitative comparison among Mediterranean, subcontinental and oceanic regions of Europe

    J Appl Ecol

    (2008)
  • A. Strauss et al.

    Invading with biological weapons: the importance of disease-mediated invasions

    Funct Ecol

    (2012)
  • I. Meeus et al.

    Effects of invasive parasites on bumble bee declines

    Conserv Biol

    (2011)
  • A. Dobson et al.

    Patterns of invasions by pathogens and parasites

  • D.W. Kelly et al.

    Parasite spillback: a neglected concept in invasion ecology?

    Ecology

    (2009)
  • A.D. Gendron et al.

    Reduced survival of a native parasite in the invasive round goby: evidence for the dilution hypothesis?

    Aquat Invasions

    (2016)
  • T.M. Blackburn et al.

    Parasites as drivers and passengers of human-mediated biological invasions

    Ecohealth

    (2017)
  • J.C. Stout et al.

    Direct interactions between invasive plants and native pollinators: evidence, impacts and approaches

    Funct Ecol

    (2017)
  • F. de Castro et al.

    Mechanisms of disease-induced extinction

    Ecol Lett

    (2005)
  • M.A. Fürst et al.

    Disease associations between honeybees and bumblebees as a threat to wild pollinators

    Nature

    (2014)
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