Characterizing sub-pixel Landsat ETM+ fire severity on experimental fires in the Kruger National Park, South Africa.

Burn severity was quantitatively mapped using a unique linear spectral mixture model to determine sub-pixel abundances of different ashes and combustion completeness measured on the corresponding fire-affected pixels in Landsat data. A new burn severity index was derived that is shown to map three categories of burn severity on three experimental burn plots in the southern Kruger National Park, South Africa. Those pixels which corresponded to a greater abundance of white ash were found to be significantly related to the pre-burn above-ground fuel biomass and an indicator of burn efficiency. Landsat ETM+ combustion completeness was most significantly related to the abundance of post-burn residual, non-photosynthetic fuel biomass. For the same reflectance change in pre- and post-fire imagery, a greater magnitude of fire severity was measured on corresponding ETM+ pixels. This implies that fire severity depends more on the colour of the ash than on the magnitude of change in reflectance. Burned area mapping methods that rely on reflectance change in multi-temporal imagery may not reliably characterize burn effects such as fire severity and efficiency in semi-arid savannas.

[1]  R. D. Johnson,et al.  Using Landsat TM data to estimate carbon release from burned biomass in an Alaskan spruce forest complex , 2000 .

[2]  Norm Campbell,et al.  On the errors of two estimators of sub-pixel fractional cover when mixing is linear , 1998, IEEE Trans. Geosci. Remote. Sens..

[3]  D. Roberts,et al.  Green vegetation, nonphotosynthetic vegetation, and soils in AVIRIS data , 1993 .

[4]  S. McNaughton,et al.  Grassland fire dynamics in the serengeti ecosystem, and a potential method of retrospectively estimating fire energy , 1989 .

[5]  S. Running,et al.  Remote Sensing of Forest Fire Severity and Vegetation Recovery , 1996 .

[6]  Fire management implications of fuel loads and vegetation structure in rehabilitated sand mines near Newcastle, Australia. , 2000 .

[7]  C. Justice,et al.  Effect of fuel composition on combustion efficiency and emission factors for African savanna ecosystems , 1996 .

[8]  N. M. Tainton,et al.  Effect of fire intensity on the grass and bush components of the Eastern Cape thornveld , 1986 .

[9]  Limin Yang,et al.  Derivation of a tasselled cap transformation based on Landsat 7 at-satellite reflectance , 2002 .

[10]  D. Lobell,et al.  Quantifying vegetation change in semiarid environments: precision and accuracy of spectral mixture analysis and the normalized difference vegetation index. , 2000 .

[11]  R. Swap,et al.  Southern African Regional Science Initiative (SAFARI 2000): Summary of science plan , 2002 .

[12]  A. Smirnov,et al.  AERONET-a federated instrument network and data archive for aerosol Characterization , 1998 .

[13]  M. Cochrane Linear mixture model classification of burned forests in the Eastern Amazon , 1998 .

[14]  W. Gertenbach,et al.  Landscapes of the Kruger National Park , 1983 .

[15]  Mário Caetano,et al.  Assessment of AVHRR data for characterizing burned areas and post-fire vegetation recovery , 1996 .

[16]  Cyrus Samimi,et al.  BIOMASS ESTIMATION FOR LAND USE MANAGEMENT AND FIRE MANAGEMENT USING LANDSAT-TM AND -ETM+ , 2002 .

[17]  C. Wessman,et al.  Fire scar mapping in a southern African savanna , 1998, IGARSS '98. Sensing and Managing the Environment. 1998 IEEE International Geoscience and Remote Sensing. Symposium Proceedings. (Cat. No.98CH36174).

[18]  Stephen R. Yool,et al.  Mapping Fire-Induced Vegetation Mortality Using Landsat Thematic Mapper Data: A Comparison of Linear Transformation Techniques , 1998 .