14. Presentation Tixier 02.pptx - ART-Dijon

Sep 28, 2012 - Case of cover crops in banana ... Régulation ? How the cover crop alter the food web? Banana. A. B. C. D. Cover crop .... Biomass exportation.
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Which food web model in agriculture ? Bridging the gap between agronomists and food web ecologists Philippe TIXIER CIRAD, UPR26, Martinique, France Networks and interactions in agriculture Dijon, France, September 28th, 2012 [email protected]

Outline •  Which models to link food web mechanisms and agricultural performances? •  Integrate ecosystem functioning knowledge in predicting models to explore management options •  How to deal with complex webs and data issued from new empirical methods e.g. molecular tools?

Expected feedbacks of food webs on agroecosystem functioning

•  Pest regulation –  top-down –  Bottom-up

•  Biogeochemical cycles •  Indirect/non trophic effects –  Soil structure –  Pollination

Changes in agroecosystem view Intra-Guild predator Intra guild predation

Predator

Pests

Cultivated crop

Predator 3 Predation / parasitism: • Biological control Prédator 2 • Natural ennemies  Top-down effect Apparent competition

Alternative prey

Prey 2

Associated plants  Bottom-up effect

What should we expect by taking into account food webs in agroecosystems? •  Clarify and hierarchize the role of species or trophic groups in biological regulations •  Optimize beneficial feedbacks on ecosystem functioning •  Propose innovative management options •  Maximize ecosystem services

What type of food web model? •  Dynamic models –  Population models: Lotka-Volterra based … huge theoretical analysis of simple models –  Generalized population models –  Mass balance models (e.g. Ecopath-Ecosim)

•  Descriptive and structural models –  Cascade, niche models (Williams and Martinez, Nature 2000; Allesina et al Science 2008…)

–  Motif detection (Milo et al Science 2002…)

Application to a concrete management question •  How the addition of a cover crop (a new primary resource) alters –  food web structure –  functions, e.g. pest regulation –  ecosystem services ?

Case of cover crops in banana agroecosystem

How the cover crop alter the food web? D

?

 Régulation ?

C

C

?

? Cosmopolites sordidus

A

B

B

A

? Banana

Banana

Cover crop

Quantification of processes before designing a predictive model

Does the new primary resource is consumed ? araignées araignées carabes carabes scolopendres scolopendres forficules forficules fourmis fourmis litière banane litière banane litière Bracharia C. sordidus C. sordidus

10.00

8.00

δ15N

15 δδ15 N N (‰) (‰)

6.00

4.00

Banana

Cover crop

2.00

0.00 -28.00 -26.00 -24.00 -22.00 -20.00 -18.00 -16.00 -14.00 -12.00 -10.00

δ13C (‰)

δ13C Banana with bare soil

à Banana with cover crop

à Shift of the trophic niche of generalist predators: consumption of the cover crop primary resource Duyck et al. 2011 Basic & Applied Ecology

Does the addition of a new primary modify predators abundance? Solenopsis geminata Bare  soil    

Cover  crop  

5  3mes  more   ants  in  cover   crops    Site  1                                                      Site  2   Mollot  et  al.  2012.  Agricultural  &  Forest  Entomology  

Does the addition of a new primary modify the predation of the pest? Predation rate sordidus eggs Preda3on   rate  of by  C. ants  

Bare  soil    

Cover  crop  

2  to  7  3mes   more  preda3on   with  cover  crop  

                     Site  1                                              Site  2    

Mollot  et  al.  2012.  Agricultural  &  Forest  Entomology  

P1 Ants

H1 Weevils

H2 Alternative prey

Multi-cycle banana growth model

Cover crop growth model

Nitrogen balance model

CROP MODEL FOOD WEB MODEL

P2 Spiders

Linking a food web model (LotkaVolterra based)

with a cropping system model (Tixier et al 2008 Agr Syst)

Tixier et al Submitted

Effect of cultural practices on ecosystem services 25

Agricultural performances

Yield

§ Fertilization level + +/- § Cover crop management (mowing)

15 120

Mean weevil populations

Pest populations

100

5

20 0 0

5

-1

60 1400 10 15 20 25 1200 Mowing40interval (weeks)

5

1000

-1

0

800

tons ha y

0

80

600 10

Primary productivity Mowing interval vs cumul H1 1.0

Productivity

Mowing interval vs cumul H1 Mowing interval vs cumul H1 1.4

15

20

25

1,2

Mowing400 interval (weeks)

Arthropod diversity

1,0

200 0 0

5

10

Shanon index

10 Abundance

tons ha

-1

20

Biodiversity

0,8

15 20 0,6 Mowing interval (weeks) 0,4

25

0,2 0,0 0

5

10

15

20

Mowing interval (weeks)

25

Tixier et al Submitted

Generalize this framework to link agronomists and community ecologists models •  Use the best of agronomic models: crop models: –  which accurately describe the soil-plant relations regarding water and nutrients

•  Linked with food web models: –  which adequately describe interactions between communities associated with the crop

Top predator

Agricultural management

• Biological control

Parasitoids

Pests

• Pesticide application

• Biomass exportation • Pruning

Generalist predator

Herbivores

Cultivated plants

Associated plants

Photosynthesis

Photosynthesis

Detritivores

Bacteria & fungi

Food web model Crop model

• Planting

Soil • Fertilization

Mineral nutrients

Organic matter • Tillage

Physical properties

Tixier et al Submitted

How trophic groups may alter soil-plant processes?

Tixier et al Submitted

But in reality… webs are much more complex

Unraveling the quantitative banana food web by DNA barcoding •  Barcoding of plant DNA (trnL chloroplastic gene) and animal DNA (mini-CO1 mitochondrial gene) •  928 individuals sampled •  753 consumption links at the individual scale, corresponding to 33 taxa (mostly identified at species or genus level) •  98 trophic links identified

The complex quantitative banana food web unraveled by DNA barcoding

Mollot et al submitted

A generlized Lotka-Volterra food web model? s s dX i = ∑ q Xi a XiXi−1 X i X i −1 − ∑ a Xi+1 Xi X i +1 X i − u Xi X i dt j =1 j =1

S number of species per trophic level aXY per capita consumption rate qX conversion efficiency uX death rate KHiRi carrying capacity of Hi supported by resource Ri rHi growth rate of Hi

It becomes possible to establish real adjacency matrix

Mollot et al submitted

But the whole community modelling has limits… 800

weevil cover crop beatle myriapod earwig ant spider

700 600 500

Kg ha-1

•  Sensitivity of errors in adjacency matrix on final simulations •  Biological parameters not available (conversion efficiency…) •  Data demanding for validation

400 300 200 100 0 1

201

401

601

801

1001

Days after planting

1201

1401

1601

Simplify the web using functional trait/

trophic group approach Example of the arable ecosystem model (Caron-Lormier et al Ecol. Model. 2009)

Link structure to functions using motifs detection

From: Stouffer & Bascompte 2010. Eco. Lett.

Occurrence of motifs to assess whole web functions Analyze the position and the frequency of species of interest (pests) in motifs

Example of the position of the banana weevils in size 4 motifs 1

2

A) Bi-fan

B) Generalism

97

11

0

0

56 16

0

C) Vulnerability

76 36

0

2

16

à Higher occurrence of weevils inside the quantitative motifs was always associated with the higher interaction strength Mollot et al To be submitted

Key messages •  The perfect food web model for agricultural issues does not exist! •  A combination of different approaches is needed to address the range of agricultural issues –  Theoretical à general rules –  Simple dynamic models in link with soil-plant functioning à explore management options –  Structural models and motifs approaches à better description of complex webs

•  New methods to measure trophic links (molecular tools) offer great perspectives but taking account all these information in predictive models remain an issue

Thank you for your attention … and many thanks to my colleagues: Pierre-François Duyck, Grégory Mollot, Elsa Canard, Raphaël Achard…