Mark Chopping (1), Darko Radakovic (1), Angela Erb (2), Rocio Duchesne-Onoro (3), Zhuosen Wang (4), Crystal Schaaf (2)
Montclair State University (1), University of Massachusetts Boston (2), University of Wisconsin - Whitewater (3), NASA GSFC/University of Maryland (4)
High resolution 2.5 m shrub abundance maps were created for 127sites of 2 km x 2 km in Alaskan Arctic tundra, with early / late QuickBird-2 (QB) / WorldView-2/3 (WV) panchromatic and NDVI image pairs over a 15- to 18-year period. The goal is to provide a dataset that can be used to assess the impact of changes in shrub abundance on summer surface albedo and to validate lower spatial resolution ABoVE remote sensing data products. The sequence of operations was: ortho-rectification of all imagery onto a 0.5 m grid using the Polar Geospatial Center code; raster-matching each WV panchromatic image to the corresponding QB image to account for differences in sun angle; conversion to 2.5 m shrub abundance maps by calculation of a roughness metric (st. dev.) in a 5 x 5 cell contiguous moving window, filtered by mean_NDVI >=0.35; validation against a very high resolution map; checks for limiting or anomalous conditions (polygonal ground, wet surface conditions, cloud contamination, poor illumination); comparisons with Landsat-derived aboveground biomass and cover maps; and comparisons to the MODIS albedo record from 2000-. Here, validation of the shrub maps was performed using the 'Toolik' map from the ABoVE 'High-Resolution Vegetation Community Maps for the Toolik Lake Area, 2013-2015' (Greaves et al. 2019; an ABoVE Sentinel site). The classes 0_No_Data, 5_Low dense shrub, 8_Shrubby tussock tundra, 10_Shrubby moist non-tussock tundra, 11_Low to tall moist shrub, and 12_Tall shrub were recoded 0_No_Data: 0; 5 & 8:1; 10 & 11: 2; and 12: 3. The 2009 QB and 2017 WV roughness maps were recoded to classes none, sparse, moderate, and tall, with <1.1, 1.1<1.5, 1.5<3, and >=3. All maps were masked for a small region of invalid imagery before calculation of confusion matrices and error metrics. The overall, user's, and producer's accuracies were 64%, 77%, and 82%, respectively, for the QB-derived map; and 61%, 78%, and 76%, respectively, for the WV-derived map. If classes are combined to none/sparse and moderate/tall, the respective accuracies are 82%, 87%, and 92% (QB); and 81%, 88%, and 89% (WV). Shrub cover was 11.4% and 14.5% in 2009 and 2017, respectively, though this may partly reflect the higher intrinsic resolution of the WV vs QB images rather than real change; if so, the rate of 0.39/year can be used to correct change estimates for the other 126 sites.
High resolution 2.5 m shrub abundance maps were created for 127sites of 2 km x 2 km in Alaskan Arctic tundra, with early / late QuickBird-2 (QB) / WorldView-2/3 (WV) panchromatic and NDVI image pairs over a 15- to 18-year period. The goal is to provide a dataset that can be used to assess the impact of changes in shrub abundance on summer surface albedo and to validate lower spatial resolution ABoVE remote sensing data products. The sequence of operations was: ortho-rectification of all imagery onto a 0.5 m grid using the Polar Geospatial Center code; raster-matching each WV panchromatic image to the corresponding QB image to account for differences in sun angle; conversion to 2.5 m shrub abundance maps by calculation of a roughness metric (st. dev.) in a 5 x 5 cell contiguous moving window, filtered by mean_NDVI >=0.35; validation against a very high resolution map; checks for limiting or anomalous conditions (polygonal ground, wet surface conditions, cloud contamination, poor illumination); comparisons with Landsat-derived aboveground biomass and cover maps; and comparisons to the MODIS albedo record from 2000-. Here, validation of the shrub maps was performed using the 'Toolik' map from the ABoVE 'High-Resolution Vegetation Community Maps for the Toolik Lake Area, 2013-2015' (Greaves et al. 2019; an ABoVE Sentinel site). The classes 0_No_Data, 5_Low dense shrub, 8_Shrubby tussock tundra, 10_Shrubby moist non-tussock tundra, 11_Low to tall moist shrub, and 12_Tall shrub were recoded 0_No_Data: 0; 5 & 8:1; 10 & 11: 2; and 12: 3. The 2009 QB and 2017 WV roughness maps were recoded to classes none, sparse, moderate, and tall, with <1.1, 1.1<1.5, 1.5<3, and >=3. All maps were masked for a small region of invalid imagery before calculation of confusion matrices and error metrics. The overall, user's, and producer's accuracies were 64%, 77%, and 82%, respectively, for the QB-derived map; and 61%, 78%, and 76%, respectively, for the WV-derived map. If classes are combined to none/sparse and moderate/tall, the respective accuracies are 82%, 87%, and 92% (QB); and 81%, 88%, and 89% (WV). Shrub cover was 11.4% and 14.5% in 2009 and 2017, respectively, though this may partly reflect the higher intrinsic resolution of the WV vs QB images rather than real change; if so, the rate of 0.39/year can be used to correct change estimates for the other 126 sites.