Abstract

A long‐standing debate in ecology deals with the role of nitrogen and phosphorus in management and restoration of aquatic ecosystems. It has been argued that nutrient reduction strategies to combat blooms of phytoplankton or floating plants should solely focus on phosphorus (P). The underlying argument is that reducing nitrogen (N) inputs is ineffective because N2‐fixing species will compensate for N deficits, thus perpetuating P limitation of primary production. A mechanistic understanding of this principle is, however, incomplete. Here, we use resource competition theory, a complex dynamic ecosystem model and a 32‐year field data set on eutrophic, floating‐plant dominated ecosystems to show that the growth of non‐N2‐fixing species can become N limited under high P and low N inputs, even in the presence of N2 fixing species. N2‐fixers typically require higher P concentrations than non‐N2‐fixers to persist. Hence, the N2 fixers cannot deplete the P concentration enough for the non‐N2‐fixing community to become P limited because they would be outcompeted. These findings provide a testable mechanistic basis for the need to consider the reduction of both N and P inputs to most effectively restore nutrient over‐enriched aquatic ecosystems.

Highlights

  • Eutrophication due to anthropogenic nutrient over-enrichment threatens the biodiversity, function and sustainability of freshwater ecosystems worldwide (Smith 2003), by promoting surface dwelling toxic cyanobacterial blooms (Paerl 1988, Huisman et al.2005) and through the invasion by dense mats of free-floating plants (Scheffer et al.2003)

  • We compared the model predictions with a 32-year field data set on eutrophic floating-plant dominated ecosystems to validate the results, and discussed the role of N2-fixation and its implication in developing nutrient management strategies for aquatic ecosystems undergoing cultural eutrophication

  • A key question we have addressed is whether N2-fixers are capable of perpetuating P limitation by compensating for ecosystem-scale N deficiencies, as this would make controlling N ineffective

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Summary

Introduction

Eutrophication due to anthropogenic nutrient over-enrichment threatens the biodiversity, function and sustainability of freshwater ecosystems worldwide (Smith 2003), by promoting surface dwelling toxic cyanobacterial blooms (Paerl 1988, Huisman et al.2005) and through the invasion by dense mats of free-floating plants (Scheffer et al.2003). Both lead to aphotic, anoxic sub-surface conditions that severely constrain aquatic life (Heisler et al 2008). A mechanistic understanding of how N2-fixation affects nutrient limitation and eutrophication in aquatic ecosystems remains incomplete

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