Abstract

Pesticide transfers in agricultural catchments are responsible for diffuse but major risks to water quality. Spatialized pesticide transfer models are useful tools to assess the impact of the structure of the landscape on water quality. Before considering using these tools in operational contexts, quantifying their uncertainties is a preliminary necessary step. In this study, we explored how global sensitivity analysis can be applied to the recent PESHMELBA pesticide transfer model to quantify uncertainties on transfer simulations. We set up a virtual catchment based on a real one and we compared different approaches for sensitivity analysis that could handle the specificities of the model: high number of input parameters, limited size of sample due to computational cost and spatialized output. We compared Sobol' indices obtained from Polynomial Chaos Expansion, HSIC dependence measures and feature importance measures obtained from Random Forest surrogate model. Results showed the consistency of the different methods and they highlighted the relevance of Sobol' indices to capture interactions between parameters. Sensitivity indices were first computed for each landscape element (site sensitivity indices). Second, we proposed to aggregate them at the hillslope and the catchment scale in order to get a summary of the model sensitivity and a valuable insight into the model hydrodynamical behaviour. The methodology proposed in this paper may be extended to other modular and distributed hydrological models as there has been a growing interest in these methods in recent years.

Highlights

  • We explored how global sensitivity analysis can be applied to the recent PESHMELBA pesticide transfer model to quantify 5 uncertainties on transfer simulations

  • We set up a virtual catchment based on a real one and we compared different approaches for sensitivity analysis that could handle the specificities of the model: high number of input parameters, limited size of sample due to computational cost and spatialized output

  • It is commonly stated than only a few parameters explain most of the variability but such conclusion does not apply in this case as more than 40 parameters are identified as influential for each output variable considered

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Summary

Introduction

15 Pesticide transfers from fields to water bodies is a major and complex environmental concern. Significant efforts are required to assess risks for aquatic and human lives. This is made difficult due to the complexity of processes at stake, the diversity and the fragmentation of agriculture landscapes where pesticides are applied (Campbell et al, 2004). Pesticide transfer models are essential tools to support risk management as they make simulation of contamination and transfers possible. They make it possible to explore and compare alternative scenarios.

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