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HAL Id: hal-02813389

https://hal.inrae.fr/hal-02813389

Submitted on 6 Jun 2020

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Prairies, séquestration du carbone et effet de serre

Jean-François Soussana

To cite this version:

Jean-François Soussana. Prairies, séquestration du carbone et effet de serre. Séminaire Franco-

Britannique, MAP, Jun 2009, Paris, France. 6 p. �hal-02813389�

(2)

Séminaire Franco-Britannique 17 Juin 2009

A L I M E N T A T I O N A G R I C U L T U R E

E N V I R O N N E M E N T

Prairies, séquestration du carbone et effet de serre

Jean-François Soussana Unité de Recherche sur l’Ecosystème Prairial,

INRA, Clermont-Ferrand

Outline

1. Carbon sequestration in European grasslands

2. C sequestration in the context of greenhouse gas balance

3. Vulnerability of carbon stocks to climate change and biodiversity loss

Mt C year-1

-600 -400 -200 0 200 400 600

Peatlands Grasslands Croplands Woodlands Forests

Estimated carbon sink: 7-11 % of fossil fuel emissions

Geographic Europe

Uncertainties in the land carbon balance of Europe

(Janssens et al. Science, 2003) .

Source Sink

370 Mt CO

2

yr

-1

The eddy covariance method for measuring CO 2 fluxes

[CO 2 ] = C’

Vertical wind = w’ CO 2 flux = w’ c’

Flux towers : Spatial scale ≈ 1 km 2

(3)

C fluxes in a grassland ecosystem

NCS = (F

CO2

- F

CH4-C

- F

VOC

- F

fire

) + (F

manure

- F

harvest

- F

animal-products

) - (F

leach

+ F

erosion

) Simplified balance in a temperate managed system:

NCS = (F

CO2

- F

CH4-C

) + (F

manure

- F

harvest

– F

animal-products

) – F

leach

(Soussana and Tallec, 2009, Animal, in press) FCH4

FCO2

Fleach

Fanimal-products

Fmanure

Fharvest

Ferosion

Ffire

FVOC

Net carbon storage FCH4

FCO2

Fleach

Fanimal-products

Fmanure

Fharvest

Ferosion

Ffire

FVOC

Net carbon storage (NCS)

C sequestration (NCS) at grazed only European sites (g C m -2 yr -1 )

NCS = 129

Fleach 10

FCH4

4 145

Fanimal-products 2

Attributed NCS = 129 FCO2

Mean of 2 sites (Soussana et al., 2007, AGEE; Soussana & Tallec, 2009, Animal)

C sequestration (NCS) at cut European sites

(g C m -2 yr -1 )

?

H erbage utilisation b y grazing and cutting (gC m-2 an-1)

0 100 20 0 3 00 400 500 600 700 800

Carbon balance (gCCm-2 yr-1) -600

-400

-200

0

200

400 B G

B G B S

B S

C A

C A Lai

Lae Lai

Lae LE

M A

M A

O ei O e i

O ee O E e

- -

• The less carbon is used, the more is returned to the soil, which increases C sequestration

• Nitrogen supply also favours carbon sequestration

Carbon sequestration (NCS) at 10 European grassland sites

(Soussana et al. Agriculture, Ecosys. Environment, 2007)

Carbon gain

Carbon loss

(4)

Fate of harvested C at cut sites (g C m -2 yr -1 )

Mean of 3 sites (Soussana et al., 2007, AGEE; Soussana & Tallec, 2009, Animal)

Fleach 10 Fmanure

Fharvest 323 370

34 NCS =71

34 113

NCS@barn = 28

Attributed NCS = 99

At barn FCO2

Fmanure@barn FCO2@barn

FCH4@barn 13 132

Fanimal-products@barn

65 51

Flabile C losses

Att-NCS = NCS + NCS

@barn

= NCS + f

humif

Max[0, (1–f

diges

)F

harvest

- F

manure

]

Fate of harvested C at cut and grazed sites (g C m -2 yr -1 )

Att-NCS = NCS + NCS

@barn

= NCS + f

humif

Max[0, (1–f

diges

)F

harvest

- F

manure

]

Fleach 10 NCS = 50

Fharvest

At barn

237 Fmanure@barn

17 83

NCS@barn = 23

Attributed NCS = 73 5

FCH4 FCO2

290

17 Fmanure

FCO2@barn FCH4@barn

9 98 Fanimal-products

5

Fanimal-products@barn

47 43 Flabile C losses

Mean of 4 sites (Soussana et al., 2007, AGEE; Soussana & Tallec, 2009, Animal)

Land carbon sink distribution in Northern America

(Peters et al. 2007, PNAS)

Land carbon sink in Northern America

(Peters et al., 2007, PNAS)

(5)

Outline

• Carbon sequestration in European grasslands

• C sequestration in the context of GHG balance

• Vulnerability of carbon stocks to climate change and biodiversity loss

Herbivore

Vegetation

Soil

Atmosphere

CH

4

CO

2

CO

2

CH

4

CO

2

N

2

O

Greenhouse gas and organic carbon fluxes in a grassland

Manure / Slurry Organic carbon

Dissolved organic C Hay / Silage

Greenhouse

Greenhouse gas gas balance of balance of 10 10 European

European grassland grassland sites sites

Capsule SF6 SF6 CH4

CH

4

et SF

6

SF6

CH4 SF6 CH4 SF

6

CH4

CH

4

et SF

6

CH

4

and SF

6

H

4

CH

4

: in-situ dual tracer mehod - N

2

O: automated chambers On site emissions of N

2

O and CH

4

, converted in CO

2

equivalents using the GWP of each gas, offset 43 % of the ecosystem C sink

The net greenhouse gas balance, also including off-site emissions of N

2

O and CH

4

through digestion of cut herbage, is a small net sink by 85 ± 77 g C m

-2

yr

-1

(Flechard et al., 2007, Pinares-Pineiro et al., 2007, Soussana et al., 2007)

GHG balance in CO 2 equivalents at European sites

(g CO 2 -C equivalents m -2 yr -1 )

(Soussana et al., 2007, Soussana and Tallec, 2009) Management NCS Att-

NCS

Grazing 471 471

Grazing &

cutting

183 268

Cutting 259 359

NGHG Att- NGHG

320 320 -22 -272 230 -141

NGHG: grassland greenhouse gas balance

Att-NGH: attributed greenhouse gas balance (including off site emissions)

(6)

The GHG balance of the agriculture sector in Europe

Grassland C sequestration would play a significant role for the European agriculture sector

GHG balance of agriculture in EU25 including C sequestration

Tg C yr-1

-40 -20 0 20 40 60 80

Grassland Cropland Undisturbed peat Drained peat CH4 N2O

(Schulze et al., submitted to Nature Geosciences)

Outline

1. Carbon sequestration in European grasslands

2. C sequestration in the context of GHG balance

3. Vulnerability of carbon stocks to climate change and biodiversity loss

Impacts of climate variability and extremes on the C cycle in grasslands

Interannual variability

Agricultural

management Greenhouse gas emissions

Climate change impact on grassland soil carbon sequestration

(Smith et al., 2005, Global Change Biol.)

(7)

Biodiversity loss may impact C sequestration

Soil organic matter

CO 2

Energy

Chemical characteristics of litter

Plant Production/

Allocation

Micro- environmental

Temperature

Moisture

Plant species diversity Plant functional traits

Defoliation by cutting and grazing

Concluding remarks

• There is a clear potential for C sequestration in European grasslands

• An internationally agreed methodology is still missing to develop mitigation options in the livestock sector based on C sequestration

• Reducing CH 4 and N 2 O emissions from the livestock sector is strongly needed, given that soil carbon sequestration is reversible and vulnerable to climate change and biodiversity loss

• Mitigation strategies could be based on the net GHG balance of livestock farms

Thank you

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