7th Workshop on Forest Fire Management - EARSeL, European ...
7th Workshop on Forest Fire Management - EARSeL, European ...
7th Workshop on Forest Fire Management - EARSeL, European ...
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2.2 - Active fire identificati<strong>on</strong><br />
Early warning system for fires in Mexico and Central America 183<br />
Immediately after each satellite overpass, Level-0 data is preprocessed to<br />
Level-1B, including geolocati<strong>on</strong>, calibrati<strong>on</strong>, and bowtie correcti<strong>on</strong>. In the<br />
case of MODIS, a suite of standard products is derived automatically including<br />
MOD14. The extracted fire informati<strong>on</strong> is projected to a Lambert<br />
C<strong>on</strong>formal C<strong>on</strong>ic projecti<strong>on</strong> and exported to a generic binary format for further<br />
processing. Then, the fires are attributed using additi<strong>on</strong>al GIS informati<strong>on</strong><br />
such as geographic coordinates, states and districts, type of vegetati<strong>on</strong>,<br />
slope, and informati<strong>on</strong> <strong>on</strong> the proximity to NPAs. C<strong>on</strong>tiguous fires<br />
are grouped and defined as a fire complex. Besides tabular informati<strong>on</strong>, the<br />
following suite of visual products is created: 1) a quick look to provide rapid<br />
clarificati<strong>on</strong> for satellite coverage and cloud cover; 2) informati<strong>on</strong> about<br />
cloud cover and invalid data percentages; 3) Enhanced Vegetati<strong>on</strong> Index<br />
(EVI) with superimposed fires; 4) 10-day FPI composite; 5) shaded relief of<br />
a DEM (200 m) with superimposed fires.<br />
2.3 - Burnt area identificati<strong>on</strong><br />
Many burnt area products use a set of thresholds together with a time series<br />
analysis to detect rapid and dramatic land cover changes.<br />
For instance, the <strong>on</strong>-going Global Burnt Areas 2000-2007 (L3JRC; Tansey et<br />
al., 2007) or the MODIS burnt area product (MCD45A1) (Roy et al., 2002,<br />
2005). All products are available <strong>on</strong> a m<strong>on</strong>thly or annual basis. In c<strong>on</strong>trast,<br />
this study uses two spectral indices for daily assessment, which have been<br />
deemed useful for burnt area detecti<strong>on</strong> (Walz et al., 2007). For this study,<br />
daily surface reflectance data of the MODIS-Aqua instrument with 500 m<br />
spatial resoluti<strong>on</strong> (MYD09GA) have been employed. In order to utilize <strong>on</strong>ly<br />
high quality data pixels, the quality assurance data set (QA) provided with<br />
the MODIS granules has been analyzed. Only pixels which fulfilled the<br />
str<strong>on</strong>g specificati<strong>on</strong>s of quality and with a sensor zenith angle lower than<br />
45° were preserved.<br />
Two indices have been used for burnt area detecti<strong>on</strong> in this study. The<br />
NDVI; Eq. (1) indicates vegetati<strong>on</strong> with higher photosynthetic activity and<br />
has been used for burnt area mapping in boreal forests and the Normalized<br />
Burn Ratio (NBR; Eq. (2)), indicates burnt areas by low values (Walz et al.,<br />
2007). While the reflectance in the near infrared and therefore also in the<br />
NDVI decreases due to the loss of biomass, the reflectance in the shortwave<br />
infrared increases because of the change in water c<strong>on</strong>tent and soil<br />
exposure.<br />
NDVI = ρNIR – ρRED / ρNIR + ρRED eq (1)<br />
NBR = ρNIR – ρSWIR / ρNIR + ρSWIR eq (2)