• Aucun résultat trouvé

Restoring a worn-out pasture : What impact on greenhouse gas exchanges ?

N/A
N/A
Protected

Academic year: 2021

Partager "Restoring a worn-out pasture : What impact on greenhouse gas exchanges ?"

Copied!
1
0
0

Texte intégral

(1)

NPK Gly phosat e Lime Ha rro w Ha rro w Seedi ng Mo w ing

Restoring a worn-out pasture :

What impact on greenhouse gas exchanges ?

The restoration of permanent pastures is often required

in order to recover a productive state and the palatability

of the grass.

The restoration process consists of :

 Destruction of the former vegetation using herbicides

 Light tillage

 Reseeding

The short and long term impacts of such operations on

the carbon cycle and on N

2

O emissions are not well

understood for old permanent pastures.

CONTEXT

PRELIMINARY RESULTS – Dynamics from March to June 2018

Contact: margaux.lognoul@ulg.ac.be

Lognoul Margaux, Gourlez de la Motte Louis, Debacq Alain, Naiken Alwin, Lonneux Mélissa, Jan Segers, Arriga Nicolas, Roland

Marilyn, Yves Bekers, Bodson Bernard, Heinesch Bernard and Aubinet Marc.

Ecosystem :

• 40 y-o grazed pasture managed by a local farmer

• One parcel (red) fertilized in the spring and grazed as usual • The other one (blue) not fertilized and under restoration

EC instruments :

• Wind velocity (CSAT-3)

• N2O/CH4 : Quantum cascade laser (Aerodyne Research

Inc.) – CO2 : Closed-path Li-7000 (LI-COR®)

Additional data :

• 30-min monitoring of meteorological conditions • Regular soil sampling and grass height measuring

EXPERIMENTAL SET-UP

Paired flux tower experiment (BE)

Influence on CO

2

fluxes

Influence on N

2

O fluxes

A

B

C

A

B

C

After glyphosate application

A

After harrowing

B

After seeding

C

After glyphosate application

A

After harrowing

B

After seeding

C

• Cumulated GPPOld keeps increasing while GPPRestored reaches

a plateau ;

• RécoOld increases faster than RécoRestored

 Could come from a decrease of autotrophic/heterotrophic respiration in the restored parcel.

• The difference between RécoOld and RécoRestored increases :

 However, no direct effect of harrowing on the respiration is observed.

• The restored parcel becomes a net C source as the ecosystem

respiration exceeds the GPP.

• From day 140, RécoOld and RécoRestored evolve with a similar

slope and GPPRestored resumes :

 Growth of vegetation in the restored parcel.

D

After mowing

D

• GPPRestored is slightly slowed down.

• Despite identical precipitations and similar nitrate and ammonium soil content, FN2O,Old are higher than FN2O,Restored :

 Limiting organic C content on the restored parcel combined to cattle urine on the old parcel ?

Cumu

lated

• FN2O,Restored show an emission burst following harrowing,

while nothing is detected from the old parcel :

 Most likely a nitrification peak ( NH4+ and  NO3-)

 Role of harrowing on emission peak still to prove (burst also showing from NE winds)

 Organic C content has increased : no more limiting ?

• Fluxes are comparable in the two parcels and follow the same dynamics :

 Might be denitrification fluxes on both sides (heavy precipitations and decreasing nitrate content)

What’s next…

• Monitoring until March 2019 (one year experiment) ;

• Investigation of the footprint from NE in the restored

parcel ;

Références

Documents relatifs

CHAPTER 5: A SPECIFIC FRAMEWORK FOR S-LCA: FROM A PARTICIPATORY APPROACH TO THE INVESTIGATION OF RELATIONSHIPS BETWEEN CHAIN GOVERNANCE AND OTHER SOCIAL SUSTAINABILITY ASPECTS

(2004) reported that no differences in the soil organic carbon content were observed on soils with higher initial contents after 28 to 30 years of irrigation on plots in a

There is evidence that coastal sediments are very important in removal of riverborne nitrogen by denitrification (Voss.. Falk et al. Title Page Abstract Introduction

This automated assignment was based on a novel suite of through-bond APSY experiments that provided highly pre- cise and accurate peak lists, which were used as input to the

Keeping in mind the importance of liming acidic soils, we hypothesized that the application of lime materials can trigger N transformations following soil pH change and

Les simulations de pertes d’azote par lixiviation sur 20 ans (réalisée avec le modèle INRA LIXIM) semblent confirmer cette tendance à l’inversion du risque de lixiviation entre

Luiz Domeignoz Horta, Aymé Spor, David Bru, Marie-Christine Breuil, Florian Bizouard, Laurent Philippot. To cite

Ø The promotion of the N2O reduction function in soils is possible both by biological (introduction of Rhizobia able to reduce N2O) and chemical (soft liming of acid soils)