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1 Spatial Modelling of the Terrestrial Environment - Georeferencial

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178 <strong>Spatial</strong> <strong>Modelling</strong> <strong>of</strong> <strong>the</strong> <strong>Terrestrial</strong> <strong>Environment</strong><br />

complete, and <strong>the</strong>refore <strong>the</strong> actual heat produced during <strong>the</strong> combustion is but a fraction<br />

<strong>of</strong> <strong>the</strong> potential (<strong>the</strong>oretical) heat yield (Pyne, 1984) – an important point and one that we<br />

will return to. Combustion requires activation energy from an external source, which, as we<br />

have previously stated, is commonly provided as a result <strong>of</strong> human activity but may also<br />

be due to lightning, burning <strong>of</strong> underground coal deposits, volcanic activity, specific forms<br />

<strong>of</strong> vegetation decomposition or certain o<strong>the</strong>r phenomena (Chandler et al., 1983). The fuel<br />

is ignited when one <strong>of</strong> <strong>the</strong>se processes applies enough heat for pyrolysis to occur (Albini,<br />

1993; Whelan, 1995). Pyrolysis can be summarized as <strong>the</strong> chemical degradation <strong>of</strong> fuel<br />

through <strong>the</strong>rmal decomposition, and results in <strong>the</strong> release <strong>of</strong> water vapour, carbon dioxide<br />

and o<strong>the</strong>r gases such as methane, methanol and hydrogen (Lobert and Warnatz, 1993).<br />

During this process <strong>the</strong> combustion reaction shifts from being endo<strong>the</strong>rmic to exo<strong>the</strong>rmic.<br />

A spreading fire is a more complex combustion process than a simple campfire or candle<br />

flame; it is one in which <strong>the</strong> flaming front is heating and <strong>the</strong>n igniting unburnt fuels, allowing<br />

<strong>the</strong> fire to propagate through <strong>the</strong> fuel bed. During <strong>the</strong> heating process, fuel moisture is<br />

initially evaporated (fuel temperature > 100 ◦ C), <strong>the</strong>n <strong>the</strong> cellulose is <strong>the</strong>rmally degraded<br />

and at its breakdown temperature volatized (temperature > 200 ◦ C) and finally <strong>the</strong> volatiles<br />

are ignited to form a visible flame (300–400 ◦ C). The combustion process in a spreading<br />

fire also goes through three distinct stages (Pyne 1984; Albini, 1993): (i) preheating during<br />

which <strong>the</strong> fuel ahead <strong>of</strong> <strong>the</strong> fire front is heated, dried and partially pyrolyzed; (ii) flaming<br />

combustion, which is <strong>the</strong> result <strong>of</strong> <strong>the</strong> ignition <strong>of</strong> flammable carbohydrate gases; and (iii)<br />

glowing combustion where any remaining charcoal burns as a solid, with oxidation taking<br />

place on <strong>the</strong> surface, leaving a small amount <strong>of</strong> residual ash. A consideration <strong>of</strong> <strong>the</strong> processes<br />

<strong>of</strong> pyrolysis and ignition shows that a fire can to some extent be considered as self-sustaining.<br />

Hence, <strong>the</strong> fire is able to spread away from <strong>the</strong> originally ignited region and into <strong>the</strong><br />

surrounding landscape. In areas where conditions are optimum for this process, huge areas<br />

<strong>of</strong> hundreds <strong>of</strong> thousands <strong>of</strong> hectares maybe burnt in a single fire event.<br />

9.2.2 Heat Generation<br />

The spreading <strong>of</strong> fire through <strong>the</strong> heating <strong>of</strong> neighbouring unignited fuel, and <strong>the</strong> measurement<br />

<strong>of</strong> energy emitted from <strong>the</strong> fire via remote sensing, are both possible because<br />

combustion releases energy in large quantities, most obviously in <strong>the</strong> form <strong>of</strong> radiation<br />

(some <strong>of</strong> which is visible to <strong>the</strong> naked eye) but also via convective and o<strong>the</strong>r processes.<br />

The amount <strong>of</strong> energy liberated is <strong>of</strong> great significance because it is closely related to fire<br />

intensity, one <strong>of</strong> <strong>the</strong> most significant parameters in any wildfire. In order <strong>of</strong> importance, <strong>the</strong><br />

factors affecting <strong>the</strong> nature <strong>of</strong> <strong>the</strong> combustion and <strong>the</strong> amount <strong>of</strong> heat released are fuel moisture,<br />

fuel chemistry and <strong>the</strong> surface area to volume ratio <strong>of</strong> <strong>the</strong> fuel particle (Chander et al.,<br />

1983). The single most important element influencing <strong>the</strong> total amount <strong>of</strong> heat released is<br />

fuel moisture content (FMC), <strong>the</strong> most variable component <strong>of</strong> a fuel’s chemistry (Lobert<br />

and Warnatz, 1993; Whelan, 1995). FMC may vary from 2.5% (dead savanna grasslands) to<br />

200% (fresh needles and leaves) <strong>of</strong> <strong>the</strong> vegetation’s dry weight. High FMC has <strong>the</strong> capacity<br />

to stop a fire, or to slow down <strong>the</strong> process to a slow, intense smoldering where much <strong>of</strong> <strong>the</strong><br />

vegetation may remain only partly combusted. Since <strong>the</strong> heat released is used to (i) raise<br />

fuel temperature to 100 ◦ C; (ii) separate bound water from <strong>the</strong> fuel; (iii) vaporize <strong>the</strong> water<br />

in <strong>the</strong> fuel; and (iv) heat <strong>the</strong> water vapour to flame temperature, it is clearly a very important<br />

characteristic. The importance <strong>of</strong> FMC is illustrated by <strong>the</strong> fact that for eucalyptus fuels,

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