Uncertainty assessment of GlobalSoilMap soil available water capacity products: A French case study

Abstract Plant available water capacity (AWC) refers to the maximum amount of water that a soil can store and provide to plant roots. Spatial predictions of AWC through digital soil mapping at high resolution and national extent provide relevant information for upscaling ecological and hydrological models, and assessment of the provision of ecosystem services like water quantity and quality regulation, carbon sequestration, and provision of food and raw materials. However, the spatial predictions of AWC are prone to errors and uncertainties. Moreover, this digital soil mapping process requires using pedotransfer functions (PTFs) due to the lack of sufficient georeferenced measurements of the upper (i.e., soil moisture at field capacity, θFC) and lower (i.e., soil moisture at permanent wilting point, θPWP) limits of soil moisture contents defining AWC. This adds an additional source of uncertainty to the final estimates of AWC. The objectives of this study were: 1) to predict AWC for mainland France following the GlobalSoilMap (GSM) project specifications on depth intervals and uncertainty, and 2) to quantify the uncertainty of AWC accounting for uncertainty of the soil input variables and the PTFs' coefficients. We first predicted the soil input properties by GSM layer (0–5, 5–15, 15–30, 30–60, 60–100, 100–200 cm), and then applied PTFs for estimating θFC, θPWP, and volumetric AWC (cm3 cm−3). The volume of coarse elements by GSM layer was subtracted before aggregating AWC to estimated soil depth for a maximum of 2 m. The uncertainty of AWC was quantified by first-order Taylor analysis. Independent evaluation indicated that clay had the lowest R2 (clay R2 = 0.27, silt R2 = 0.43 and sand R2 = 0.46) and RMSE (clay RMSE = 128 g kg−1, silt RMSE = 139 g kg−1 and sand RMSE = 172 g kg−1) from the three particle size fractions. However, the model for coarse elements had the worst predictive performance (R2 = 0.14 and RMSE = 21%) among all AWC input variables. The performance of the GSM predictions for θFC and θPWP had a R2 of 0.21 and 0.29. When the PTFs were applied to the spatial predictions of sand and clay, the RMSE for θFC and θPWP had a relative increase of 25% and 36% respectively compared to when they were applied to measured horizon data. Across the majority of mainland France, the main sources of uncertainty of elementary AWC were coarse elements and soil texture, but the contribution of uncertainty of PTFs' coefficients increased in areas dominated by very sandy and clayey textures. An advantage of the produced maps of θFC, θPWP and AWC is that the end users can incorporate associated uncertainties into ecological and agricultural modelling, and decision-making processes involved in soil and water planning.

[1]  C. Piedallu,et al.  Mapping soil water holding capacity over large areas to predict potential production of forest stands , 2011 .

[2]  Philippe Lagacherie,et al.  Using quantile regression forest to estimate uncertainty of digital soil mapping products , 2017 .

[3]  H. Jenny Factors of Soil Formation: A System of Quantitative Pedology , 2011 .

[4]  Gerard B. M. Heuvelink,et al.  Sampling for validation of digital soil maps , 2011 .

[5]  Jean-Louis Roujean,et al.  ECOCLIMAP-II/Europe: a twofold database of ecosystems and surface parameters at 1 km resolution based on satellite information for use in land surface, meteorological and climate models , 2012 .

[6]  Durga L. Shrestha,et al.  Machine learning approaches for estimation of prediction interval for the model output , 2006, Neural Networks.

[7]  Gerard B.M. Heuvelink,et al.  Mapping rootable depth and root zone plant-available water holding capacity of the soil of sub-Saharan Africa , 2018, Geoderma.

[8]  Gerard B.M. Heuvelink,et al.  Including spatial correlation in structural equation modelling of soil properties , 2018, Spatial Statistics.

[9]  Christian Bernhofer,et al.  A novel approach in model-based mapping of soil water conditions at forest sites , 2009 .

[10]  John Aitchison,et al.  The Statistical Analysis of Compositional Data , 1986 .

[11]  H. Reuter,et al.  Functional Digital Soil Mapping for the Prediction of Available Water Capacity in Nigeria using Legacy Data , 2013 .

[12]  Gerard B. M. Heuvelink,et al.  Geostatistical prediction and simulation of European soil property maps , 2016 .

[13]  Jingyi Huang,et al.  Evaluating a Bayesian modelling approach (INLA-SPDE) for environmental mapping. , 2017, The Science of the total environment.

[14]  Dominique Arrouays,et al.  GlobalSoilMap France: High-resolution spatial modelling the soils of France up to two meter depth. , 2016, The Science of the total environment.

[15]  Jingyi Huang,et al.  Mapping Particle‐Size Fractions as a Composition Using Additive Log‐Ratio Transformation and Ancillary Data , 2014 .

[16]  I. Odeh,et al.  SPATIAL PREDICTION OF SOIL PARTICLE-SIZE FRACTIONS AS COMPOSITIONAL DATA , 2003 .

[17]  Johan Bouma,et al.  Using Soil Survey Data for Quantitative Land Evaluation , 1989 .

[18]  J. Gallant,et al.  A multiresolution index of valley bottom flatness for mapping depositional areas , 2003 .

[19]  Luca Montanarella,et al.  Digital soil assessments: Beyond DSM , 2007 .

[20]  T. Hengl,et al.  3D soil hydraulic database of Europe at 250 m resolution , 2017 .

[21]  G. Tóth,et al.  New generation of hydraulic pedotransfer functions for Europe , 2014, European journal of soil science.

[22]  Laura Poggio,et al.  3D mapping of soil texture in Scotland , 2017 .

[23]  B. Nicoullaud,et al.  The effect of soil stoniness on the estimation of water retention properties of soils: A case study from central France , 2015 .

[24]  Alfred E. Hartemink,et al.  Digital Mapping of Soil Particle-Size Fractions for Nigeria Pedology , 2022 .

[25]  W. Parton,et al.  Analysis of factors controlling soil organic matter levels in Great Plains grasslands , 1987 .

[26]  D. Liu,et al.  Modelling soil organic carbon 1. Performance of APSIM crop and pasture modules against long-term experimental data , 2016 .

[27]  P. Bertran,et al.  A map of Pleistocene aeolian deposits in Western Europe, with special emphasis on France , 2016 .

[28]  John Triantafilis,et al.  Digital soil mapping of compositional particle-size fractions using proximal and remotely sensed ancillary data , 2012 .

[29]  R Core Team,et al.  R: A language and environment for statistical computing. , 2014 .

[30]  Robert Tibshirani,et al.  An Introduction to the Bootstrap , 1994 .

[31]  Alex B. McBratney,et al.  Spatial prediction of soil properties from landform attributes derived from a digital elevation model , 1994 .

[32]  J. Giráldez,et al.  Soil Water‐Holding Capacity Assessment in Terms of the Average Annual Water Balance in Southern Spain , 2005 .

[33]  R. Lark,et al.  Cokriging particle size fractions of the soil , 2007 .

[34]  Soil texture GlobalSoilMap products for the French region 'Centre' , 2014 .

[35]  S. Recous,et al.  STICS : a generic model for the simulation of crops and their water and nitrogen balances. I. Theory, and parameterization applied to wheat and corn , 1998 .

[36]  Isabelle Cousin,et al.  Pedotransfer functions for predicting available water capacity in French soils, their applicability domain and associated uncertainty , 2019, Geoderma.

[37]  Budiman Minasny,et al.  Predicting and mapping the soil available water capacity of Australian wheatbelt , 2014 .

[38]  O. Duval,et al.  Use of class pedotransfer functions based on texture and bulk density of clods to generate water retention curves , 2003 .

[39]  O. Duval,et al.  Prediction of soil water retention properties after stratification by combining texture, bulk density and the type of horizon , 2008 .

[40]  Dominique Arrouays,et al.  Evaluating large-extent spatial modeling approaches: A case study for soil depth for France , 2016 .

[41]  L. Lin,et al.  A concordance correlation coefficient to evaluate reproducibility. , 1989, Biometrics.

[42]  M. Patterson,et al.  A framework for classifying and quantifying the natural capital and ecosystem services of soils , 2010 .

[43]  B. Nicoullaud,et al.  The contribution of rock fragments to the available water content of stony soils: Proposition of new pedotransfer functions , 2011 .

[44]  Gerard B. M. Heuvelink,et al.  About regression-kriging: From equations to case studies , 2007, Comput. Geosci..

[45]  C. Ballabio,et al.  Mapping topsoil physical properties at European scale using the LUCAS database , 2016 .

[46]  C. Folberth,et al.  Uncertainty in soil data can outweigh climate impact signals in global crop yield simulations , 2016, Nature Communications.

[47]  Marcel G. Schaap,et al.  Functional evaluation of pedotransfer functions derived from different scales of data collection , 2003 .

[48]  M. Donatelli,et al.  Testing Denitrification Functions of Dynamic Crop Models , 1997 .

[49]  B. Minasny,et al.  Digital Soil Map of the World , 2009, Science.

[50]  Laura Poggio,et al.  Soil available water capacity interpolation and spatial uncertainty modelling at multiple geographical extents , 2010 .

[51]  Andrea Vacca,et al.  Rates and spatial variations of soil erosion in Europe: A study based on erosion plot data , 2010 .

[52]  Geir-Arne Fuglstad,et al.  Predicting soil properties in the Canadian boreal forest with limited data: Comparison of spatial and non-spatial statistical approaches , 2017 .

[53]  Gerard B. M. Heuvelink,et al.  Propagation of errors in spatial modelling with GIS , 1989, Int. J. Geogr. Inf. Sci..

[54]  Jean Thioulouse,et al.  Large trends in French topsoil characteristics are revealed by spatially constrained multivariate analysis , 2011 .

[55]  Gerard B. M. Heuvelink,et al.  Multivariate mapping of soil with structural equation modelling , 2017 .

[56]  Richard Webster,et al.  Fluctuations in method‐of‐moments variograms caused by clustered sampling and their elimination by declustering and residual maximum likelihood estimation , 2013 .

[57]  Budiman Minasny,et al.  Predicting and mapping soil available water capacity in Korea , 2013, PeerJ.

[58]  B. J,et al.  Soil regionalisation by means of terrain analysis and process parameterisation , 2002 .

[59]  L. Poggio,et al.  Bayesian spatial modelling of soil properties and their uncertainty: The example of soil organic matter in Scotland using R-INLA , 2016 .

[60]  J. Arnold,et al.  SWAT2000: current capabilities and research opportunities in applied watershed modelling , 2005 .