Abstract

To better predict the consequences of environmental change on aquatic microbial ecosystems it is important to understand what enables community resilience. The mechanisms by which a microbial community maintain its overall function, for example, the cycling of carbon, when exposed to a stressor, can be explored by considering three concepts: biotic interactions, functional adaptations, and community structure. Interactions between species are traditionally considered as, e.g., mutualistic, parasitic, or neutral but are here broadly defined as either coexistence or competition, while functions relate to their metabolism (e.g., autotrophy or heterotrophy) and roles in ecosystem functioning (e.g., oxygen production, organic matter degradation). The term structure here align with species richness and diversity, where a more diverse community is though to exhibit a broader functional capacity than a less diverse community. These concepts have here been combined with ecological theories commonly used in resilience studies, i.e., adaptive cycles, panarchy, and cross-scale resilience, that describe how the status and behavior at one trophic level impact that of surrounding levels. This allows us to explore the resilience of a marine microbial community, cultivated in an outdoor photobioreactor, when exposed to a naturally occurring seasonal stress. The culture was monitored for 6weeks during which it was exposed to two different temperature regimes (21 ± 2 and 11 ± 1°C). Samples were taken for metatranscriptomic analysis, in order to assess the regulation of carbon uptake and utilization, and for amplicon (18S and 16S rRNA gene) sequencing, to characterize the community structure of both autotrophs (dominated by the green microalgae Mychonastes) and heterotrophs (associated bacterioplankton). Differential gene expression analyses suggested that community function at warm temperatures was based on concomitant utilization of inorganic and organic carbon assigned to autotrophs and heterotrophs, while at colder temperatures, the uptake of organic carbon was performed primarily by autotrophs. Upon the shift from high to low temperature, community interactions shifted from coexistence to competition for organic carbon. Network analysis indicated that the community structure showed opposite trends for autotrophs and heterotrophs in having either high or low diversity. Despite an abrupt change of temperature, the microbial community as a whole responded in a way that maintained the overall level of diversity and function within and across autotrophic and heterotrophic levels. This is in line with cross-scale resilience theory describing how ecosystems may balance functional overlaps within and functional redundancy between levels in order to be resilient to environmental change (such as temperature).

Highlights

  • Microorganisms make up ≈70% of the aquatic biomass and their interactions in the microbial loop are vital for the recycling of energy and nutrients that ensure the ecosystem services provided by aquatic food webs (Azam et al, 1983; Bar-On et al, 2018)

  • The response of the PBR microbial community upon the two different temperature conditions may have been regulated at two interconnected levels, through function and population structure, which together affect microalgae-bacteria interactions, going from coexistence to competition (Figure 9). These results suggest that the PBR microbial community, with lower complexity than natural systems, but more complex than 2-3 species model systems, has the ability to respond in a manner to temperature stress, by structural and functional modulations that span across levels, which could be considered as resilient (Supplementary Figure S1)

  • The results from the present study suggest that interlevel interactions, in relation to functional and structural dynamics, are of importance for microbial community resilience

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Summary

Introduction

Microorganisms make up ≈70% of the aquatic biomass and their interactions in the microbial loop are vital for the recycling of energy and nutrients that ensure the ecosystem services provided by aquatic food webs (Azam et al, 1983; Bar-On et al, 2018). We focused on three interlinked mechanisms that together have the potential to influence microbial ecosystem resilience in response to changed environmental conditions: biotic interactions, functional adaptations, and community structure. The considered interactions may primarily be characterized by either coexistence, governed by resource partitioning (Sörenson et al, 2020), or by competition for energy and nutrients, which may lead to competitive exclusion (Schoener, 1974; Chesson, 2000) Both types of interactions influence biogeochemical cycles, e.g., that of carbon, through potential functional changes and variations in microbial community structure (Lindh and Pinhassi, 2018; Sörenson et al, 2020). Temporal dynamics in the structure of a community relate to its species richness or diversity, in which a more diverse community is characterized by a more efficient use of resources compared to a less diverse community that likely have a more narrow functional range (Cardinale et al, 2006; Ptacnik et al, 2008)

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