Abstract

Abstract Arctic freshwaters are facing multiple environmental pressures, including rapid climate change and increasing land___use activities. Freshwater plankton assemblages are expected to reflect the effects of these stressors through shifts in species distributions and changes to biodiversity. These changes may occur rapidly due to the short generation times and high dispersal capabilities of both phyto___ and zooplankton. Spatial patterns and contemporary trends in plankton diversity throughout the circumpolar region were assessed using data from more than 300 lakes in the U.S.A. (Alaska), Canada, Greenland, Iceland, the Faroe Islands, Norway, Sweden, Finland, and Russia. The main objectives of this study were: (1) to assess spatial patterns of plankton diversity focusing on pelagic communities; (2) to assess dominant component of __ diversity (turnover or nestedness); (3) to identify which environmental factors best explain diversity; and (4) to provide recommendations for future monitoring and assessment of freshwater plankton communities across the Arctic region. Phytoplankton and crustacean zooplankton diversity varied substantially across the Arctic and was positively related to summer air temperature. However, for zooplankton, the positive correlation between summer temperature and species numbers decreased with increasing latitude. Taxonomic richness was lower in the high Arctic compared to the sub___ and low Arctic for zooplankton but this pattern was less clear for phytoplankton. Fennoscandia and inland regions of Russia represented hotspots for, respectively, phytoplankton and zooplankton diversity, whereas isolated regions had lower taxonomic richness. Ecoregions with high __ diversity generally also had high __ diversity, and turnover was the most important component of __ diversity in all ecoregions. For both phytoplankton and zooplankton, climatic variables were the most important environmental factors influencing diversity patterns, consistent with previous studies that examined shorter temperature gradients. However, barriers to dispersal may have also played a role in limiting diversity on islands. A better understanding of how diversity patterns are determined by colonisation history, environmental variables, and biotic interactions requires more monitoring data with locations dispersed evenly across the circumpolar Arctic. Furthermore, the importance of turnover in regional diversity patterns indicates that more extensive sampling is required to fully characterise the species pool of Arctic lakes.

Highlights

  • The Arctic region is experiencing dramatic climate change, with both air temperature and precipitation expected to continue to increase more rapidly than in any other region of the world (Bintanja, 2018; IPCC, 2014; NOAA, 2018)

  • The main objectives of this study were: (1) to assess spatial patterns of plankton diversity focusing on pelagic communities; (2) to assess dominant component of β diversity; (3) to identify which environmental factors best explain diversity; and (4) to provide recommendations for future monitoring and assessment of freshwater plankton communities across the Arctic region

  • Our analysis focused on three aspects of freshwater biodiversity: taxonomic richness; α diversity, and β diversity

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Summary

Introduction

The Arctic region is experiencing dramatic climate change, with both air temperature and precipitation expected to continue to increase more rapidly than in any other region of the world (Bintanja, 2018; IPCC, 2014; NOAA, 2018) This will have direct and indirect effects on freshwater ecosystems and their biodiversity. Thermokarst or thaw ponds and lakes, which account for approximately 25% of the estimated total area covered by ponds and lakes in the Arctic (Grosse et al, 2013), encompass a variety of transparencies and trophic conditions, whereas most Arctic ponds and lakes are oligotrophic with low nutrient conditions (Rautio et al, 2011; Wauthy et al, 2018) Despite this great limnological diversity, the majority of Arctic lakes and ponds are characterised by low biodiversity and relatively simple food webs (Christoffersen et al, 2008; Rautio et al, 2011). These characteristics make them highly sensitive to environmental pressures that alter biodiversity and ecosystem properties (Hayden et al, 2017; Lizotte, 2008; Vadeboncoeur et al, 2003)

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