Abstract

We examined controls of benthic dinitrogen (N2) fixation and primary production in oligotrophic lakes in Arctic Alaska, Toolik Field Station (Arctic Long-Term Ecological Research Site). Primary production in many oligotrophic lakes is limited by nitrogen (N), and benthic processes are important for whole-lake function. Oligotrophic lakes are increasingly susceptible to low-level, non-point source nutrient inputs, yet the effects on benthic processes are not well understood. This study examines the results from a whole-lake fertilization experiment in which N and P were added at a relatively low level (4 times natural loading) in Redfield ratio to a shallow (3 m) and a deep (20 m) oligotrophic lake. The two lakes showed similar responses to fertilization: benthic primary production and respiration (each 50–150 mg C m−2 day−1) remained the same, and benthic N2 fixation declined by a factor of three- to fourfold by the second year of treatment (from ~0.35 to 0.1 mg N m−2 day−1). This showed that the response of benthic N2 fixation was de-coupled from the nutrient limitation status of benthic primary producers and raised questions about the mechanisms, which were examined in separate laboratory experiments. Bioassay experiments in intact cores also showed no response of benthic primary production to added N and P, but contrasted with the whole-lake experiment in that N2 fixation did not respond to added N, either alone or in conjunction with P. This inconsistency was likely a result of nitrogenase activity of existing N2 fixers during the relative short duration (9 days) of the bioassay experiment. N2 fixation showed a positive saturating response when light was increased in the laboratory, but was not statistically related to ambient light level in the field, leading us to conclude that light limitation of the benthos from increasing water-column production was not important. Thus, increased N availability in the sediments through direct uptake likely caused a reduction in N2 fixation. These results show the capacity of the benthos in oligotrophic systems to buffer the whole-system response to nutrient addition by the apparent ability for significant nutrient uptake and the rapid decline in N2 fixation in response to added nutrients. Reduced benthic N2 fixation may be an early indicator of a eutrophication response of lakes which precedes the transition from benthic to water-column-dominated systems.

Highlights

  • Dinitrogen (N2) fixation is one of the most important processes for understanding nutrient dynamics during the eutrophication of freshwater lakes

  • In both the deep (E-5) and shallow (E-6) fertilized lakes, no differences were detected in benthic Gross primary production (GPP) and Ecosystem respiration (ER)

  • Benthic N2 fixation was depressed in the fertilized lakes relative to reference lakes by about fourfold, leading to a significant treatment effect (Appendix 2 in Supplementary Material)

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Summary

Introduction

Dinitrogen (N2) fixation is one of the most important processes for understanding nutrient dynamics during the eutrophication of freshwater lakes. Our understanding has far focused on factors that control water-column N2 fixation and the role that it plays in compensating for N limitation of phytoplankton production in the presence of sufficient phosphorus supply (Schindler 1977; Smith 1983; Hendzel and others 1994). Oligotrophic lakes can exhibit a high buffering capacity to added nutrients as oxic bottom-waters sequester phosphorus in the formation of iron-P oxides (Wetzel 2001; O’Brien and others 2005), the dynamics that affect benthic processes during the early stages of eutrophication can be subtle and evident even before water-column changes are documented (Rosenberger and others 2008). Early changes in benthic production and benthic N2 fixation, especially in the context of low-level, non-point source nutrient inputs are not well understood

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