TY - JOUR
T1 - Using aboveground vegetation attributes as proxies for mapping peatland belowground carbon stocks
AU - Lopatin, Javier
AU - Kattenborn, Teja
AU - Galleguillos, Mauricio
AU - Perez-Quezada, Jorge F.
AU - Schmidtlein, Sebastian
N1 - Funding Information:
This investigation was funded by the Graduate School for Climate and Environment of the Karlsruhe Institute of Technology [VH-GS-304], the Chilean National Commission for Science and Technology [FONDECYT 1130935] and CR2 [CONICYT/FONDAP/15110009]. We further thank Gamaya for their collaboration with the UAV hyperspectral sensor, Julián Cabezas, Ariel Valdés and Jose Ignacio Calderón for their crucial participation in the field survey and to Rocío Araya-Lopez for her valuable comments on the manuscript.
Funding Information:
This investigation was funded by the Graduate School for Climate and Environment of the Karlsruhe Institute of Technology [ VH-GS-304 ], the Chilean National Commission for Science and Technology [ FONDECYT 1130935 ] and CR 2 [ CONICYT/FONDAP/15110009 ]. We further thank Gamaya for their collaboration with the UAV hyperspectral sensor, Julián Cabezas, Ariel Valdés and Jose Ignacio Calderón for their crucial participation in the field survey and to Rocío Araya-Lopez for her valuable comments on the manuscript.
Publisher Copyright:
© 2019 Elsevier Inc.
PY - 2019/9/15
Y1 - 2019/9/15
N2 - Peatlands are key reservoirs of belowground carbon (C) and their monitoring is important to assess the rapid changes in the C cycle caused by climate change and direct anthropogenic impacts. Frequently, information of peatland area and vegetation type estimated by remote sensing has been used along with soil measurements and allometric functions to estimate belowground C stocks. Despite the accuracy of such approaches, there is still the need to find mappable proxies that enhance predictions with remote sensing data while reducing field and laboratory efforts. Therefore, we assessed the use of aboveground vegetation attributes as proxies to predict peatland belowground C stocks. First, the ecological relations between remotely detectable vegetation attributes (i.e. vegetation height, aboveground biomass, species richness and floristic composition of vascular plants) and belowground C stocks were obtained using structural equation modeling (SEM). SEM was formulated using expert knowledge and trained and validated using in-situ information. Second, the SEM latent vectors were spatially mapped using random forests regressions with UAV-based hyperspectral and structural information. Finally, this enabled us to map belowground C stocks using the SEM functions parameterized with the random forests derived maps. This SEM approach resulted in higher accuracies than a direct application of a purely data-driven random forests approach with UAV data, with improvements of r2 from 0.39 to 0.54, normalized RMSE from 31.33% to 20.24% and bias from −0.73 to 0.05. Our case study showed that: (1) vegetation height, species richness and aboveground biomass are good proxies to map peatland belowground C stocks, as they can be estimated using remote sensing data and hold strong relationships with the belowground C gradient; and (2) SEM is facilitates to incorporate theoretical knowledge in empirical modeling approaches.
AB - Peatlands are key reservoirs of belowground carbon (C) and their monitoring is important to assess the rapid changes in the C cycle caused by climate change and direct anthropogenic impacts. Frequently, information of peatland area and vegetation type estimated by remote sensing has been used along with soil measurements and allometric functions to estimate belowground C stocks. Despite the accuracy of such approaches, there is still the need to find mappable proxies that enhance predictions with remote sensing data while reducing field and laboratory efforts. Therefore, we assessed the use of aboveground vegetation attributes as proxies to predict peatland belowground C stocks. First, the ecological relations between remotely detectable vegetation attributes (i.e. vegetation height, aboveground biomass, species richness and floristic composition of vascular plants) and belowground C stocks were obtained using structural equation modeling (SEM). SEM was formulated using expert knowledge and trained and validated using in-situ information. Second, the SEM latent vectors were spatially mapped using random forests regressions with UAV-based hyperspectral and structural information. Finally, this enabled us to map belowground C stocks using the SEM functions parameterized with the random forests derived maps. This SEM approach resulted in higher accuracies than a direct application of a purely data-driven random forests approach with UAV data, with improvements of r2 from 0.39 to 0.54, normalized RMSE from 31.33% to 20.24% and bias from −0.73 to 0.05. Our case study showed that: (1) vegetation height, species richness and aboveground biomass are good proxies to map peatland belowground C stocks, as they can be estimated using remote sensing data and hold strong relationships with the belowground C gradient; and (2) SEM is facilitates to incorporate theoretical knowledge in empirical modeling approaches.
KW - Belowground carbon stocks
KW - Hyperspectral
KW - PLS path modeling
KW - Random forests
KW - SEM
KW - UAV
KW - Vegetation attributes
UR - http://www.scopus.com/inward/record.url?scp=85066758794&partnerID=8YFLogxK
U2 - 10.1016/j.rse.2019.111217
DO - 10.1016/j.rse.2019.111217
M3 - Article
AN - SCOPUS:85066758794
SN - 0034-4257
VL - 231
JO - Remote Sensing of Environment
JF - Remote Sensing of Environment
M1 - 111217
ER -