Research Ideas and Outcomes :
Grant Proposal
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Corresponding author: Malte Jochum (malte.jochum@uni-wuerzburg.de)
Received: 10 Oct 2023 | Published: 13 Oct 2023
© 2023 Malte Jochum, Vera Zizka, Stefan Scheu, Nico Eisenhauer, Melanie Pollierer
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Jochum M, Zizka VMA, Scheu S, Eisenhauer N, Pollierer MM (2023) Global change in above-belowground multitrophic grassland communities. Research Ideas and Outcomes 9: e113960. https://doi.org/10.3897/rio.9.e113960
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Global change is transforming Earth’s ecological communities with severe consequences for the functions and services they provide. In temperate grasslands, home to a mesmerising diversity of invertebrates controlling multiple ecosystem processes and services, land-use intensification and climate change are two of the most important global-change drivers. While we know a lot about their independent effects on grassland biodiversity and ecosystem functioning, little is known about how these stressors interact. Moreover, most research on biodiversity change focuses on decreasing biomass or species richness, while a major aspect is commonly ignored – altered ecological interactions. This is problematic because these interactions represent and control many important ecosystem processes, such as predation, herbivory or decomposition. Networks of trophic interactions, so-called food webs, link the structure and functioning of ecological communities and unravel mechanistic relationships between environmental change, ecological communities and ecosystem multifunctionality – the ability of a system to simultaneously support multiple processes. Consequently, we need to study how ecological interactions and the food webs they comprise respond to environmental change and to multiple interacting global-change drivers. Fortunately, novel tools offer unprecedented opportunities in studying trophic interactions and their impact on ecosystem processes. In addition, we know far more about how global change impacts the aboveground world than its belowground counterpart. However, belowground communities are just as important for the overall functioning of terrestrial ecosystems. Thus, to comprehensively understand global-change impacts on temperate grasslands, we need to study above- and belowground multitrophic interactions and ecosystem processes together, also accounting for their interdependencies. Here, we propose to use the Global Change Experimental Facility (GCEF, Bad Lauchstädt, Germany) to study joint impacts of land-use intensity and climate change on above-belowground multitrophic interactions and ecosystem multifunctionality in a temperate grassland global-change experiment. We will combine novel approaches to assessing trophic interactions and basal-resource dependency with an innovative method to quantify energy flux through ecological interaction networks. We will disentangle separate and interactive effects of land use and climate change and unravel how global-change driven modifications in multitrophic interactions mechanistically translate into altered ecosystem processes and multifunctionality – above and below the ground. Combining a field-experimental approach with novel molecular and quantitative techniques will allow for a leap forward in our understanding of global-change impacts on temperate grasslands, which will be crucial to manage and conserve these important ecosystems.
multitrophic interactions, food webs, energy flux, climate change, land use, multiple stressors
Temperate grasslands, home to a mesmerising diversity of invertebrates controlling numerous ecosystem processes, are subject to global change. Two of the most pressing global-change drivers are land-use intensification and climate change. We know that these stressors introduce filters regarding species richness, community composition, body-size patterns and the overall biomass of arthropods. What we do not know is how they jointly modulate multitrophic interactions (i.e., interactions amongst trophic levels – the steps on the trophic ladder) and what consequences altered interaction networks have for ecosystem processes. The mechanisms of how global-change drivers impact grassland multitrophic biodiversity-ecosystem functioning relationships remain unresolved. In addition, most of our knowledge on grassland biodiversity and ecosystem functioning is focused on the aboveground world, while the belowground counterpart and its responses to global change are less-well understood. Here, we propose to use a field experimental approach, together with novel molecular techniques to study feeding relationships, and an innovative approach to calculating energy flux through ecological networks, to mechanistically unravel joint impacts of land-use intensity and climate change on multitrophic, above-belowground, temperate grassland arthropod interaction networks, ecosystem processes and multifunctionality.
More than 36% of Earth‘s land surface is agriculturally used (Worldbank, agricultural land %). With transforming these systems to meet our growing demands, human land use has severely altered their abiotic and biotic properties. We have modified their biodiversity, biogeochemical cycles and their productivity and have disrupted local to global biodiversity with consequences for ecosystem processes (
Moreover, temperate grassland ecological communities and interactions face an additional stressor, which, because of its crucial influence on central aspects, from individual physiology to community ecology, will likely modulate land-use effects: climate change. The impacts of climate change are proposed to surpass those of other threats to biodiversity and ecosystem functioning soon (
Interactions are the key to understanding how communities respond to global change (
When interested in linking interactions to processes, we need to advance the question of “who eats whom” to “… and how much”? We can do this by establishing quantitative food webs that contain information on interaction strengths. To quantify these and understand how interactions and basal-resource use affect ecosystem processes, we can use the concept of matter and energy flux through ecological communities (
As land use and climate change simultaneously affect temperate-grassland communities, we need to understand how these multiple stressors interactively influence the communities (
Despite all previous research on land-use and climate-change impacts on temperate grasslands, there are two main aspects that require substantial further investigation. First, while we know that multitrophic biodiversity and community composition change with land-use intensity and climate change, we know very little about the corresponding changes in ecological interactions and the interaction networks they comprise – as well as how these changes mechanistically impact ecosystem functioning and multifunctionality. This lack of knowledge is driven by previous technological constraints to an in-depth assessment of changing feeding interactions in complex communities. Fortunately, novel analytical techniques, such as gut content DNA metabarcoding (
Second, in comparison to the aboveground world, knowledge on biodiversity and ecosystem functioning below the ground is scarce (
The first author, Malte Jochum, has a broad background in global-change impacts on multitrophic communities and ecosystem functioning (
Overarching goal: Understand how land-use intensity and climate change jointly alter above-belowground multitrophic communities and ecosystem multifunctionality in temperate grasslands. Objective 1 (OB1): Explore how above- and belowground fauna communities (richness, density, biomass, average body mass, composition) differ in response to multiple stressors (i.e., under simultaneous climate change and land-use intensification). OB2: Assess climate- and land-use related changes in trophic interactions and basal-resource dependency of high-trophic level consumers above and below the ground. OB3: Quantify climate- and land-use impacts on above-belowground energy flux, ecosystem processes and grassland ecosystem multifunctionality.
Overarching hypotheses: HA: Detrimental effects of climate change on above-belowground communities will be more pronounced at high land-use intensity (
We propose to use an existing field experiment (see below) to mechanistically link two of the most prominent global-change drivers in temperate grasslands, land-use intensity and climate change, to changes in above-belowground multitrophic interaction networks and ecosystem multifunctionality. Instead of merely describing how communities change, we will obtain mechanistic insights on how these changes translate into altered ecosystem processes and multifunctionality – which is what society ultimately depends on.
We will investigate how land-use intensity and climate change jointly impact above-belowground communities and ecosystem processes. This is important because both stressors affect individual- to community-level aspects of biology and ecology and are likely to interact, i.e. to influence each other’s impact (
a The Global Change Experimental Facility (GCEF) Bad Lauchstädt, Germany, has 10 main plots, five in each climate level (ambient, blue; future, red). Each main plot is split into five plots (16 x 24 m) with different land-use types. We will use three of these (I-III, green shades), 30 plots overall. b On each plot, we will sample (WP1) vegetation- and ground-dwelling fauna (suction sampling, 45 cm diameter), soil macrofauna (20 cm diameter), mesofauna (5 cm diameter) and nematodes (2 cm diameter), each to 10 cm depth. We will extract earthworms (mustard extraction) in the 20-cm hole, below the 10-cm core. c Spiders and staphylinid beetles (top consumers) will be stored at -20°C, in molecular-grade ethanol. After extraction, sorting and identification, we will create multi-individual samples (WP2) for the five most common spider and staphylinid species (red and purple shades, respectively). These multi-individual samples will be used for gut content metabarcoding (f) and compound specific isotope analysis of amino acids (CSIA-AA, g). We will analyse how climate and land-use intensity (d) alter above- and belowground invertebrate communities (density, biomass, diversity, etc.) (e) and, using the molecular techniques, above- and belowground consumer trophic interactions (resource pool, f) and basal-resource dependency (g). Based on WP1 and WP2, we will build above-belowground food webs to calculate energy flux under different climates and land-use intensity (h, WP3).
The GCEF was set up to investigate how climate change and land-use intensity interactively impact ecosystem functioning via above-belowground biodiversity. GCEF research has shown that climate and land-use intensification independently and interactively modify aboveground arthropod species richness, abundance and community composition (
In WP1, our aim is to simultaneously assess the responses of above- and belowground invertebrate communities in temperate grasslands to the joint influence of land-use intensity and climate change (OB1). To achieve this goal, we (PhD & student helpers) will sample above- and belowground invertebrates in 30 GCEF plots (10 main plots, three land-use plots each: intensive and extensive meadow, extensive pasture) in two consecutive years (1 and 2, see Fig.
To quantitatively sample soil fauna at peak biomass, and in concert with the simultaneous aboveground-fauna assessment, we will take one large (20 cm diameter) and one small (5 cm diameter) soil core, both to a depth of 10 cm, to adequately assess soil macro- and mesofauna, respectively (
Macro- and mesofauna will will be pre-sorted to order or higher-level taxon by the PhD student and student helpers. All taxa, including nematodes and earthworms, will then be identified to species- or functional-group level by specialists to ascribe them to trophic species for food-web construction. We will measure body lengths of five individuals per species/highest identification level and plot to calculate body masses with allometric regressions (
To assess global-change impacts on multitrophic interactions and energy channels (OB2), we will use two state-of-the-art methods, gut-content metabarcoding for assessing short-term, direct trophic interactions (Who eats whom?) and compound-specific isotope analysis of amino acids (CSIA-AA) to quantify the relative dietary contribution of long-term basal resources, such as bacteria, fungi and plants, for consumers (... and how much?). The little information we have on global-change impacts on grassland-interaction networks is commonly constrained to plant-pollinator (
Gut-content metabarcoding (
Compound-specific isotope analysis of amino acids (
We know that global change impacts communities and ecosystem processes, but we lack the mechanistic understanding of how the two things are linked. In WP3, we aim to establish plot-level food webs to calculate above-belowground energy flux, ecosystem processes (e.g., predation, herbivory, decomposition), energy channels (plant-, bacteria-, fungi-based) and multifunctionality and unravel the mechanisms of global-change effects on grassland communities and ecosystems (OB3). We will combine the community data from WP1 (both years) with the trophic information from WP2 (based on sampling in year 1) to establish plot-specific food webs for both years. More specifically, we will use a combination of taxonomic and functional information together with novel, plot-specific data on predator-prey interactions from WP2 to build food webs (see
Based on the pre-sorting and expert identification of all invertebrates (WP1), we will group them into trophically-consistent feeding types, such as carnivores, herbivores, detritivores or omnivores, within taxonomic orders. Omnivores will be further specified into carnivore-herbivores, carnivore-detritivores, herbivore-detritivores or generalistic omnivores consuming animal, plant and detritus resources (
Based on this information, we will quantify ecosystem processes, such as primary and intraguild predation, herbivory and decomposition as all fluxes going out of the respective resource types, for example, out of autotroph nodes for herbivory. We will quantify energy channels by summing up all fluxes upstream of plants, bacteria and fungi, respectively. These assessments are based on established routines (
Generally, we expect higher land-use intensity and future climate to reduce total energy flux, but more severely above than below the ground (H3.1;
In summary, we will obtain fundamentally-novel information on how land-use intensity and climate change jointly alter above-belowground communities and trophic interactions and how this mechanistically modulates above-belowground ecosystem functions, energy channels and multifunctionality. Our results will offer unprecedented insights into how exactly multiple global-change drivers alter ecosystem performance, which is important to understand, manage and mitigate global-change impacts on temperate grasslands.
We would like to thank two anonymous reviewers for their positive assessment of this proposal. M.J. acknowledges funding by the Deutsche Forschungsgemeinschaft (DFG, German Research Foundation) – 527384685. Furthermore, we are grateful to UFZ GCEF scientific coordinator Martin Schädler, as well as iDiv (funded by the German Research Foundation, DFG–FZT 118, 202548816) and Leipzig University officials for their support and for constructive feedback on earlier versions of this proposal.
DFG Sachbeihilfe (Individual Research Grants) – 527384685
Global change in above-belowground multitrophic grassland communities