@article{fdi:010092540, title = {{E}stimating vegetation structure and aboveground carbon storage in {W}estern {A}ustralia using {GEDI} {L}i{DAR}, {L}andsat and {S}entinel data}, author = {{L}utz, {N}. and {R}odriguez-{V}eiga, {P}. and {O}liveras {M}enor, {I}mma}, editor = {}, language = {{ENG}}, abstract = {{W}orsening climate change impacts are amplifying the need for accurate estimates of vegetation structure and aboveground biomass density ({AGBD}) to assess changes in biodiversity and carbon storage. {I}n {A}ustralia, increasing wildfire frequency and interest in the role of forests in the carbon cycle necessitates biomass mapping across large geographic extents to monitor forest change. {T}he availability of spaceborne {L}ight {D}etection and {R}anging optimised for vegetation structure mapping through the {G}lobal {E}cosystem {D}ynamics {I}nvestigation ({GEDI}) provides an opportunity for large-scale forest {AGBD} estimates of higher accuracy. {T}his study assessed the use of the {GEDI} canopy height product to predict woody {AGBD} across five vegetation types in {W}estern {A}ustralia: tall eucalypt forests, eucalypt open woodlands, low-lying heathland, tropical eucalypt savannas, and tussock and hummock grasslands. {C}anopy height models were developed using random forest regressions trained on {GEDI} canopy height discrete point data. {P}redictor variables included spectral bands and vegetation indices derived from synthetic aperture radar {S}entinel-1 data, and multispectral {L}andsat and {S}entinel-2 data. {AGBD} was subsequently estimated using power-law models derived by relating the predicted canopy heights to field {AGBD} plots. {M}apping was conducted for 2020 and 2021. {T}he accuracy of canopy height predictions varied with height quantiles; models underestimated the height of taller trees and overestimated the height of smaller trees. {A} similar underestimation and overestimation trend was observed for the {AGBD} estimates. {T}he mean carbon stock was estimated at 69.0 ± 12.0 {M}g{C}ha-1 in the tall eucalypt forests of the {W}arren region; 33.8 ± 5.0 {M}g{C}ha-1 for the open eucalypt woodlands in the {S}outh {J}arrah region; 7.1 ± 1.4 {M}g{C}ha-1 for the heathland and shrublands in the {G}eraldton {S}andplains region; 43.9 ± 4.9 {M}g{C}ha-1 for the {K}imberley eucalypt savanna; and 3.9 ± 1.0 {M}g{C}ha-1 for the {K}imberley savanna grasslands. {T}his approach provides a useful framework for the future development of this process for fire management, and habitat health monitoring.}, keywords = {{AUSTRALIE}}, booktitle = {}, journal = {{E}nvironmental {R}esearch : {E}cology}, volume = {3}, numero = {4}, pages = {045004 [24 ]}, ISSN = {2752-664{X}}, year = {2024}, DOI = {10.1088/2752-664x/ad7f5a}, URL = {https://www.documentation.ird.fr/hor/fdi:010092540}, }