Upload
others
View
3
Download
0
Embed Size (px)
Citation preview
0,33 ha
~ 460 trees/ha6 m
4 m
(A)
Bare ground
(B)
Tarpaulin mulching
(C)
High weed cover
© A. Ratnadass - Cirad
Assessment of mango blossom gall midge management solutions
from in-silico experiments : overview of an on-going modeling approach
Isabelle Grechi1,3,*, Laurie Saint-Criq1,2, Christian Soria1,3, Alain Ratnadass1,3, Frédéric Normand1,3,
Paul Amouroux5, Frédéric Boudon2,3
1 CIRAD, UPR HortSys, F-97455 Saint-Pierre, La Réunion, France2 CIRAD, UMR AGAP, F-34398 Montpellier, France 3 University of Montpellier, F-34090 Montpellier, France5 Departamento de Fruticultura y Enología, Pontificia Universidad Católica de Chile, Santiago, Chile
* Corresponding author: [email protected]
2. The modelling framework
Mango (Mangifera indica L.), a major fruit production in tropical and subtropical regions, is facing many production constraints: mango yield is irregular across
years, fruit quality is heterogeneous at harvest, and mango tree exhibits phenological asynchronisms within and between trees that result in long periods with
phenological stages susceptible to pests and diseases. Among them, the mango Blossom Gall Midge (BGM, Procontarinia mangiferae (Felt)) is a major pest
of mango. It can cause significant yield losses by damaging mango inflorescences. Management solutions to improve fruit yield and quality while reducing the
use of pesticides are considered. A crop-pest model applied to the mango-BGM system is currently developed from experimental data and will be used for in
silico assessment of BGM management levers (e.g. soil mulching and manipulation of mango phenology). The on-going modeling approach is presented.
1. Introduction
► Model description
A mango-BGM model simulates the dynamics of inflorescence and BGM populations of an
orchard at a daily time-step during the period of mango flowering (Fig.1). The orchard is
structured into three patches (A, B and C) according to soil mulching treatments (Fig.2).
In a first approach, the model is defined at the patch scale and considers:
Inflorescence age-structured population dynamics within each patch, accounting for
natural development and BGM-induced mortality of inflorescences: steps to
BGM stage-structured population dynamics within each patch, differentiating the effect of
soil mulching treatments on the BGM life cycle for each patch: steps to
Orchard colonization and movements of BGM adult individuals between patches, at
constant rates or driven by inflorescence abundance in each patch: steps to
© A. Franck - Cirad
Fig.2. The experimental orchard
Movements of
endogenous females
between patches
soil
3rd instar larvae
falling to the soil
𝐿𝑡+𝑑𝑙
Adult females
𝑁𝑡
New adult
females emerging
from the soil
𝑁𝑡+𝑑𝑙+𝑑𝑝
Fig.3. 3-D representation of simulated vegetative and reproductive
architectural development and phenology of a mango tree over a
growing cycle using a functional-structural plant model (FSPM) [1]
Female
egg-laying
Egg and larval
survival and
development
Resource abundance
within a patch
Inflorescence
mortality due
to larval
damages
1
2
1
2
Fig.1. Schematic representation of the mango-BGM model (bold text: estimated
parameters)
30th International Horticultural congress, 12-18 August 2018, Istanbul, Turkey
soil mulching
1
3
2
Orchard colonization by exogenous females (𝝀𝒕)
Local BGM dynamic
within a patch
Pupation rate and pupal survival and development
3 Larval & Adult
survival to soil mulching treatments
Pupae
females
leaving the
patch
4
5
Fig.4. Simulated (blue lines) vs observed (black points) BGM dynamics,
assessed by trapped larvae, in each of the three patches A, B and C
► Model parameterization and simulations
• Model parameterization from existing knowledge [2] and experimental data [3] collected in
Reunion Island on Cogshall cultivar (see experimental design; Fig.2)
Survival to soil mulching treatment, 𝜇𝑆𝑀 = 𝜇𝑆𝑀1 𝜇𝑆𝑀2 : 1 for bare ground (patch A), 0 for
tarpaulin mulching (patch B), and 0.11 for high weed cover (patch C).
• Qualitative validation based on experimental data and model simulations (Fig.4).
© A. Franck - Cirad
4. Conclusion
• This first modeling approach at the population scale gave promising results. However, further investigations are required to
assess the benefits of i) considering inflorescence phenological stages, and ii) changing from a population to an individual-
based and spatially explicit modelling approach, using a mango FSPM [1] for instance.
• Furthermore, relying on the mango FSPM can be useful to assess the effects of cultural practices on mango tree flowering
and their indirect effects on BGM dynamics. Eventually, the mango-BGM model should be used for the design of
management solutions for a sustainable mango production.
References: [1] Boudon et al. (2017). Acta Horticulturae, 1160: 83-
90; [2] Amouroux (2013). PhD Thesis dissertation. University of La
Réunion; [3] Brustel (2018). Master Thesis dissertation. Purpan.
Virtual experiments will be performed with the mango-BGM model to assess the effects of BGM
management levers on flowering level and fruit yield, according to exogenous pest pressure.
Tested environmental and management levers and their corresponding variables will be :
- Exogenous pest pressure: 𝜆𝑡- Soil mulching treatment: 𝜇𝑆𝑀- Manipulation of mango phenology: 𝐼𝑏𝑡- Pesticide applications: 𝜇𝑎 (adult survival rate to pesticides)
Acknowledgements. This work has been carried out as
part of the Cirad DPP COSAQ and ECOVERGER project
30th International Horticultural congress, 12-16 August 2018, Istanbul, Turkey
3. Future prospects: virtual experiments
Dynamic of inflorescence bud burst
(𝐼𝑏𝑡, input from experimental data)
Inflorescence development & aging
(constant lifespan T)
Inflorescence dynamic can also be simulated from a FSPM
model (Fig.3)
Inflorescences
born on day d,
𝐼𝑡𝑑 :
• 𝐼𝑏𝑑 if d≤t <d +T• 0 otherwise
𝐸0 𝑓 𝒌,𝑁𝑡 , 𝐼𝑡
0 ≤ 𝑓 ≤ 1
𝜇𝑙
0
500
1000
1500
2000
2500
3000
3500without BGM
with BGM
01-July 01-August 01-Sept. 01-Oct.
BGM-induced
mortality
Number of inflorescences, 𝐼𝑡 = 𝑑 𝐼𝑡𝑑
© L. Brustel - Cirad
𝝁𝑺𝑴𝟏 𝝁𝑺𝑴𝟐
𝑷𝒎𝒐𝒗
1 − 𝑃𝑚𝑜𝑣
𝜇𝑝𝑃𝑝
𝐼𝑡𝑑𝑔 𝜸,𝑁𝑡 , 𝐼𝑡 ,
0 ≤ 𝑔 ≤ 1
Nu
mb
er
of tr
ap
pe
dla
rva
e
(A) Bare ground (B) Tarpaulin mulching (C) High weed cover