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Phytomining to re-establish phosphorus-poor soil conditions for nature restoration on former agricultural land

  • Schelfhout StephanieEmail author
  • De Schrijver An
  • Vanhellemont Margot
  • Vangansbeke Pieter
  • Wasof Safaa
  • Michael P Perring
  • Haesaert Geert
  • Verheyen Kris
  • Mertens Jan
Regular Article
  • 78 Downloads

Abstract

Aims

To restore species-rich grasslands on former agricultural land, typically phosphorus-poor soil conditions need to be re-established. Here we assess the potential of phosphorus extraction by biomass production, i.e. phytomining. We compare two techniques: (i) ‘mowing’, i.e. cutting and removing hay two or three times a year, and (ii) ‘P-mining’, i.e. mowing with yield maximization by adding growth-limiting nutrients other than phosphorus (i.e. nitrogen and potassium).

Methods

In a five-year field experiment at three fields situated along a soil phosphorus gradient, we studied phosphorus removal through both biomass assessment and changes in two soil phosphorus pools: bioavailable phosphorus (POlsen) and slowly cycling phosphorus (POxalate).

Results

Phosphorus-mining doubled the phosphorus removal with biomass compared to mowing, and phosphorus removal with biomass was lower at fields with an initially lower concentration of POlsen in the soil. The POlsen concentrations decreased significantly during the experiment with the largest decreases in phosphorus-rich plots. Changes in the POlsen and POxalate stocks were correlated with the amount of phosphorus removed with biomass.

Conclusions

Phosphorus-mining effectively increases phosphorus removal compared to mowing, but becomes less efficient with decreasing soil phosphorus concentrations. Restoring phosphorus-poor soil conditions on formerly fertilized land remains a challenge: phytomining most often needs a long-term commitment.

Keywords

Abiotic ecological restoration Phytoextraction Bioavailable phosphorus Mowing P-mining Species-rich grassland 

Abbreviations

P

Phosphorus

N

Nitrogen

K

Potassium

POlsen

Sodium bicarbonate-extractable soil P

POxalate

Ammonium-oxalate-extractable soil P

PAL

Ammonium-lactate-extractable soil P

PTotal

Total soil P

ΔPOlsen

Change in POlsen between 2011 and 2017

ΔPOxalate

Change in POxalate between 2011 and 2017

PNI

Phosphorus nutrition index

NNI

Nitrogen nutrition index

KNI

Potassium nutrition index

Notes

Acknowledgements

We are grateful for the admission to conduct our field experiment in Landschap De Liereman (Natuurpunt): the cooperation with the people of Natuurpunt and local farmers was greatly appreciated. Special thanks to Kris Van der Steen, Jan Van den Berghe and Dieter Dijckmans. Further, we thank our lab technicians Luc Willems and Greet de Bruyn for processing and analysing our samples. Kris Ceunen, Filip Ceunen, Luc Willems, Robbe De Beelde, Jelle Van den Berghe, Danny Vereecke and Tomohiro Nagata are thanked for helping with fieldwork. Lander Baeten and Haben Blondeel are thanked for helping out with the statistics. We thank Rob Marrs, Tobias Ceulemans, Frank Nevens, Lander Baeten and three anonymous reviewers for their helpful comments.

Supplementary material

11104_2019_4049_MOESM1_ESM.pdf (4 mb)
ESM 1 (PDF 4076 kb)

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Copyright information

© Springer Nature Switzerland AG 2019

Authors and Affiliations

  • Schelfhout Stephanie
    • 1
    Email author
  • De Schrijver An
    • 1
    • 2
  • Vanhellemont Margot
    • 2
  • Vangansbeke Pieter
    • 1
  • Wasof Safaa
    • 1
  • Michael P Perring
    • 1
    • 3
  • Haesaert Geert
    • 4
  • Verheyen Kris
    • 1
  • Mertens Jan
    • 1
  1. 1.Forest & Nature Lab, Department of Environment, Faculty of Bioscience EngineeringGhent UniversityGontrode (Melle)Belgium
  2. 2.Faculty of Science and TechnologyUniversity College GhentMelleBelgium
  3. 3.Ecosystem Restoration and Intervention Ecology (ERIE) Research Group, School of Plant BiologyThe University of Western AustraliaCrawleyAustralia
  4. 4.Department of Plants and Crops, Faculty of Bioscience EngineeringGhent UniversityGhentBelgium

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