Global SoilMappingin a Changing World

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Transcription:

Global SoilMappingin a Changing World Sabine Grunwald Acknowledgements: GIS-Pedometrics Team, UF

Soil Story My soil story. Your soil story

Digital Soil Mapping in a Changing World Global climate change, land use change, population growth Soil Gap Water Gap Food Gap Soil Carbon Resources Sustainability Rockström et al., 2009. Nature.

Digital Soil Mapping (DSM) High Low Abstraction level & complexity Sustainability Adaptation / mitigation potential Soil ecosystem services (natural capital) Risk / vulnerability Soil gaps Soil functions Soil ecosystem processes Soil change / evolution Soil properties Soil classes Statistical methods: e.g. multivariate regression Ensemble trees Machine learning Geostatistical methods: e.g. kriging Mixed/hybrid methods: e.g. regression kriging PTF & interpolation Process-based methods: e.g. simulation models and more.

What is the Purpose of Digital Soil Mapping? (1)Intrinsicknowledge: just for the sake of knowing (create maps) (2) Extrinsicknowledge: To address societal, complex, global issues; a changing world w/ uncertainty; we co-create soil ecosystems Global regional local scales

Multiple Soils Perspectives

Estimates of Carbon Stocks Globe 1 km Florida, U.S. 30 m WCA 2A, Florida UNEP-WCMC. http://www.carbon-biodiversity.net/globalscale/map Scharlemann et al. (2009): Harmonized World Soil Database (2009)-SOC values up to 1 m depth (1 km spatial resolution) & Ruesch and Gibbs (2008): Biomass carbon map using IPCC Tier 1 methodology and GLC 2000 land cover data. 10 m Grunwald, Myers, Harris, and Comerford. 2012. Kim and Grunwald, 2013

Grunwald et al. (2011). Soil Sci. Soc. Am. J. and Grunwald. 2006. Environmental Soil-Landscape Modeling. CRC Press.

Overview of Phenomena of Spaceand Time, Distribution of Soil Properties and Processes at Escalating Spatial Scale Grunwald et al. (2011). Soil Sci. Soc. Am. J.

Envisioned Future of Digital SoilMapping and Modeling Grunwald et al. (2011). Soil Sci. Soc. Am. J.

Conceptual Soil Formation Models Factorial soil models: The soil forming factors -climate (CL), organisms (O), relief (R), parent material (P), and time (T) -form soils Soils CL O T R P Jenny (1941)

SCORPAN Model Soil Properties/Classes Age & PositioN Parent material Soil Climate Quantitative framework suited for digital soil mapping (DSM) Empirical model Factors and soil predictions are spatially-explicit (x, y) and temporally-explicit (t) Relief Organisms McBratney et al. (2003) Geoderma

STEP-AWBH Model SoilProperties/Classes Biotic Water Human Atmosphere Soil Parent material Topography Ecology Grunwald et al. (2011) SSSAJ Thompson et al. (2012). DSM: Interactions w/ and applications for hydropedology. Spatially and temporally explicit Additional factors (W, H) Accounts for timedependent variation of STEP-AWBH variables Facilitates modeling of soil evolution and change Space-time model

STEP-AWBH Model Target soil property, rate, change, process, risk, etc. n Soil Topography Ecology Spatially-explicit, ~stable across time Parent material SA( z, p x, tc ) = f { S j ( z, px, tc ), Tj ( px, tc ), E j ( px, tc ), Pj ( px, tc )}; j Soil Depth Pixel w/ size x m { A i= 0 n j j ( p x, t i ), W j ( p x, t i ), B j ( p x, t i ), H j ( p Spatially-explicit + account for time-dependent variation of variables Atmosphere x, t i )} Current (c) time Water Biota Human

S Factor e.g. soil org. C SA( z, p x, tc ) = n f { S j ( z, px, tc )} j Examples -How to populate the S factor: Soil taxonomic data (e.g., soil order, great groups) Soil drainage class map Available water storage top 25 cm Soil texture map (clay, silt, sand content) Soil organic matter map

S Factor: Historic Soil Organic C (U.S.) Data source: Soil Survey Geographic Database (SSURGO) Soil Data Mart, NRCS

A Factor e.g. soil org. C SA( z, p x, tc ) = m { A i= 0 n j j ( p x, t i )} Examples -How to populate the A factor: Long-term mean precipitation Aggregated precipitation during summer months Max. temperature last year Max. temperature over the past 30 years Daily, weekly or monthly soil moisture Soil moisture yearly average

A Factor: Temperature Data source: Idaho Geospatial Spatial data extraction: R. Patarasuk (GIS-Pedometrics Team)

A Factor: Solar Radiation Solar radiation 30 yr averages for each month Data source: North American Regional Reanalysis (NARR) National Oceanic and Atmospheric Administration (NOAA) Spatial data extraction: X. Xiong (GIS-PedometricsTeam)

W Factor: Soil Moisture Spatial data extraction: X. Xiong (GIS-PedometricsTeam) Soil Moisture Data (SMOS) (European Space Agency, ESA)

B Factor: NDVI Spatial data extraction: X. Xiong (GIS-Pedometrics Team) and Y. Qiu (Geography, UF) Data source: MODIS (NASA) Moderate-resolution Imaging Spectroradiometer

SoilCarbon Assessment across the U.S. + STEP-AWBH (environmental covariates) Data source: NRCS Soil carbon map

Soil Carbon Assessment across Florida, U.S. (Xiong, Grunwald et al. 2013. Geoderma) Validation results R 2 =0.57 RMDS=2.85 R 2 =0.63 RMDS=2.64 R 2 =0.62 RMDS=2.65 [Grid res. = 30x30 m] STEP-AWBH variables = 210 Significant continuous predictor variables AWC (25 and 50 cm) SOM Soil albedo Sand % Slope Dist Stream Landsat (Bd5, Bd7, PC1, TC1) Dry Biomass Vegetation EVI (April) MODIS (small NDVI peak integral) MODIS (GPP) MODIS (NPP) (PrecipFeb and PrecipSept) (PrecipAvg) Significant categorical predictors: LULC VegType Soil Hydration

Bayesian GeostatisticalModeling of SOC with Uncertainty Assessment Xiong X., S. Grunwald, D.B. Myers, J. Kim, W.G. Harris, N. Bliznyuk and N.B. Comerford. 2013. Geophys. Res. Biogeosciences Posterior mean (a), standard deviation (b), 2.5 percentile (c) and 97.5 percentile (d) of soil organic carbon (SOC) prediction at 0-20 cm depth in Florida from Bayesian geostatistical model with both fixed and spatial random effects. (Markov Chain Monte Carlo (MCMC) simulation, after Diggle et al. 1998) Environmental covariates: AWC, SOC (SSURGO), dry surface albedo, Landsat PC1, CTI, LAI

Soil Carbon Change 1965 to 2010 (Florida) (Xiong, Grunwald et al. 2013.) N = 194

Remote Sensing Supported DSM (Kim, Grunwald et al. 2012) Water Conservation Area 2A, Florida, Everglades Spectral indices: EVI, MSI, NDVI, NDVI green, NDWI, RSR, SR, TVI SPOT (10 m) Landsat ETM+ (30 m) MODIS (250 m) Jan. 09, 2009 Feb. 16, 2010 Feb. 18, 2010

Remote Sensing Supported DSM (Kim, Grunwald and Rivero. 2013. IEEE Trans. Geosci& Remote Sensing J.) BK RF SPOT RF Landsat ETM+ RF MODIS TP (mg kg -1 ) R 2 : 0.60 RMSE: 213.7 R 2 : 0.92 RMSE: 102.1 R 2 : 0.92 RMSE: 102.2 R 2 : 0.89 RMSE: 120.3 TN (g kg -1 ) R 2 : 0.30 RMSE: 2.88 R 2 : 0.95 RMSE: 1.45 R 2 : 0.94 RMSE: 1.44 R 2 : 0.91 RMSE: 1.56

Observations (TP) BK RFSPOT 0 10 cm RFLandsat ETM+ RFMODIS TVI, SR, and NDVI green (biotic factor) ranked high.

Soil Gaps Soil Sci. Soc. Am.

Deep Soil Science Human activities triggering Global Soil Change (National Geographic, 2010)

Contact: sabgru@ufl.edu http://soils.ifas.ufl.edu/faculty/grunwald