Resumen
Context: The global shift toward sustainable agriculture has increased interest in using process-based models to design and optimize intercropping systems. However, these models differ fundamentally in how they represent trade-offs (competition for light, water, and nutrients) and synergies (facilitation, complementarity) in resource sharing between species. This conceptual variation creates uncertainty in model selection and application, particularly since most models were originally developed for monoculture and subsequently adapted for intercropping. Objective: In this study, we describe how current crop models represent interspecies resource-sharing mechanisms, analyse their structural differences, and synthesize findings from existing validation studies to understand how their structural differences affect model performance. The models examined include APSIM (APSIM-Canopy, APSIM-Micromet, APSIM-Strip, APSIM-Alternating, APSIM-APSwim, APSIM-SoilArbitrator), DayCent, DSSAT-Mixed, DSSAT-MPI, LandscapeDNDC, LUCIA, MONICA, SIMPLACE Lintul5-Intercrop, STICS-Big-Leaf, STICS-Multilayer, and WaNuLCAS. Methods: Through the Agricultural Model Intercomparison and Improvement Project (AgMIP) platform, we engaged with model developers and expert users to collect detailed information on how crop models represent intercropping systems using structured interviews and questionnaires. We then developed a framework that groups models by their core conceptual approaches to simulating resource sharing. Finally, we synthesize findings from existing quantitative validation studies to connect conceptual intercomparison to predictive performance across different intercrop characteristics and environments. Results and Conclusions: Our analysis identifies six distinct conceptual approaches for simulating light sharing and four for belowground resource (water and nutrient) competition. Intercrop models show greater structural divergence in canopy than in belowground representation. Furthermore, competitive trade-offs (light, water, and nutrients) are widely represented while facilitative and other complex processes like N₂-fixation, plasticity (shoot and root), microclimate effects or hydraulic lift are often simplified or omitted. Our analysis of model validation studies reveals a critical trade-off: structurally complex models often perform well in simulating intercropping when calibration is done on sole crops, whereas simpler models require extensive intercrop-specific calibration to achieve better prediction performance. This distinction is vital for model application in data-scarce environments, as more complex architectures can leverage existing sole-crop data to effectively simulate intercrop systems. The classification of the structural resource capture differences in combination with the evaluated model performance analysis allowed us to devise an evidence-based model selection criteria framework useful also for for non-specialist, while the unique detailed description provided are highly valuable for the model research community. Significance: This study establishes a conceptual framework that provides the necessary foundation for a meaningful quantitative intercomparison of intercrop models, as structural understanding enables the interpretation of numerical differences in model outputs. It also guides hypothesis testing, model choice, priorities in model development and improvements.
| Idioma original | English |
|---|---|
| Número de artículo | 110491 |
| Número de páginas | 18 |
| Publicación | Field Crops Research |
| Volumen | 343 |
| DOI | |
| Estado | Published - jun 1 2026 |
Nota bibliográfica
Publisher Copyright:© 2026 The Authors
Financiación
This study was funded by the European Union DESIRA program under the LEG4DEV project grant ( FOOD/2020/418–901 ), which supports the scaling of legume-based agroecological intensification in smallholder maize and cassava cropping systems across Sub-Saharan Africa. This initiative contributes to enhancing the sustainability of the water-food-energy nexus, improving food security, and strengthening livelihood resilience. We also acknowledge the invaluable support provided by the Agricultural Model Intercomparison and Improvement Project (AgMIP) and the European Union Horizon 2020 SustainSAHEL project (Grant No. 861974 ). Additionally, this study received co-funding from the Deutsche Forschungsgemeinschaft (DFG, German Research Foundation) under Germany’s Excellence Strategy ( EXC 2070–390732324 , PhenoRob), the European Union (EU Horizon project IntercropVALUES , grant agreement No. 101081973 ), BBSRC ( BB/S020969 ), the Leibniz Association under LL-SYSTAIN (Grant Labs- 2024-IÖR) , and the German National Science Foundation (DFG) under FAIRagro (Grant NFDI 51/1 ). AGRECO4CAST, Co-funded by the European Union (funding ID for Germany: 031B1610A ); PARAM-VC project (ID 01DQ25001A), funded by the Department of Science and Technology (DST), India, and the Federal Ministry of Research, Technology and Space of Germany ( BMFTR ). Chimonyo' s time was funded by the Consultative Group on International Agricultural Research ( CGIAR ) through the Multifunctional Landscape Science Program of the CGIAR
| Financiadores | Número del financiador |
|---|---|
| Consortium of International Agricultural Research Centers | |
| Department of Science and Technology, Ministry of Science and Technology, India | |
| Bundesministerium für Forschung, Technologie und Raumfahrt | |
| BMFTR | |
| Consultative Group on International Agricultural Research | |
| Biotechnology and Biological Sciences Research Council | BB/S020969 |
| German National Science Foundation | NFDI 51/1, 031B1610A, AGRECO4CAST, 01DQ25001A |
| Horizon 2020 Framework Programme | 861974 |
| Deutsche Forschungsgemeinschaft | EXC 2070–390732324 |
| European Commission | FOOD/2020/418–901 |
| EU Horizon Europe Program | 101081973 |
| Leibniz-Gemeinschaft | Labs- 2024-IÖR |
ASJC Scopus subject areas
- Agronomy and Crop Science
- Soil Science
Huella
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