MFI1Fires (Hot Spots)in AmazoniaFIRES (HOT SPOTS)Fire forms part of the slash-burn model of agriculture practiced for millennia in Amazonia byindigenous peoples and more recently by other local populations that have settled there. Over thelast 50 years fire has been used on a larger scale, very often associated with deforestation, in order toconvert extensive areas of Amazonian forest into farm landscapes (MFI1). The use of fire as the “mostefficient and cheapest tool” for eliminating forest cover has transformed millions of hectares into newAmazonian ecosystems completely different from their original condition.With climate change generating extreme events in Amazonia, such as the 2005 drought, theconditions have been favorable for large-scale forest fires, such as those reported in Brasil and Bolivia(Marengo et al., 2008). Uncontrolled forest and ground fires may be responsible for a large proportionof greenhouse gas emissions in Amazonia.ContextFires, increasingly common and more intense in the region, are not limited just to the infamous‘arc of deforestation’ of Brasil and Bolivia. New fires have been occurring in more remote areas andwithin Protected Natural Areas (PNAs). Indigenous and traditional communities, including some whoinhabit regions far from the colonization frontiers, have denounced problems in controlling fires and illustratethe need to develop procedures for adapting to the climate changes under way. One exampleof this is the case of the Xingu Indigenous Park (MT, Brasil), an island of forest surrounded by the deforestationproduced over the last 20 years by farming activities, where 16 ethnic groups live in more than50 different communities. In 2009 an experimental process was begun to mobilize twelve communities,belonging to seven ethnic groups, to create new forms of managing and fighting fire (see BFI1: TheXingu Indigenous Park on the fire path).Scientists monitoring and studying the dynamic of deforestation and degradation in Amazoniaagree that a number of interrelated factors exists that increases the forest’s vulnerability to fire (Fearnside,2005). The main factors described include: 1) the advance of farming in Bolivian and BrazilianAmazonia close to areas of cerrado and dry transition forests, which are already naturally more proneto fire propagation (Laurance et al., 2001; Steininger et al., 2001); 2) the degradation of forest areasthrough selective logging, which increases sunlight and wind penetration, lowering the relative humidityof the forest (Nepstad et al., 2004), which explains the particular vulnerability to fire of illegal loggingzones (Veríssimo et al., 1992); 3) the severity and duration of the dry season, worsened by the firesthemselves, which curb cloud formation and delay the onset of the rainy season (Laurance et al., 2002);and 4) the fact that trees in Amazonia are not adapted to fire, which means that after the first fire hasburnt, the volume of material susceptible to burning and aridity increases, significantly augmenting theintensity of subsequent fires (Cochrane, 2003).The immediate and most evident consequences of the increase in fires are the loss of diversityin wildlife and plant life, air pollution and the consequent impact on human health, the increase in greenhousegas emissions and the reduction in local rainfall due to the smoke.Recent estimates indicate that the combination of deforestation and climate change may leadto a 50% increase in the occurrence of fires in Amazonia by 2050 (Silvestrini et al., 2011), intensifyingforest degradation and impoverishment.Burning to convert forest into cattle pasture. São Félix do Xingu, Pará, Brasil.© Daniel Beltra/Greenpeace, 2008 Fire, used in traditional agriculture, is no longer restrictedto marginal areas; it is advancing deep into Amazonia The highest number of forest fires were recordedduring the years 2002, 2004 and 2005 The southeastern portion of Amazonia, known as theArc of Deforestation (Brasil and Bolivia) is the regionwith the highest number of recorded forest fires The 10 indigenous territories most heavily affected by fireduring the period 2000-2010 are located in Bolivia and Brasil The traditional forms of managing fire used byindigenous peoples will have to adapt to climate change¾Ä¸Methodology<strong>RAISG</strong> 44Georeferenced information on ”hot spots” in Amazonia for the 2000-2010 period was obtainedfrom Brasil’s National Space Research Institute (<strong>Instituto</strong> Nacional de Pesquisas Espaciais do Brasil:INPE), taking into account: (i) the recorded date of hotspots, and (ii) the type of sensor used. Only datafrom the NOAA-12 (from 01/01/2000 to 09/08/2007) and NOAA-15 (from 10/08/2007 to 31/12/2010)satellites were used. For these satellites a hotspot appears as a 1 km² area of high temperature, whichmay represent the occurrence of a single small fire, several small fires or a larger fire. These satellitescannot detect fires that occur on the ground under the tree cover. To facilitate analysis, the data wasAmazonia under Pressure – FiresFiresYoung man from the Waurá indigenous peoples training to put out fires inside the Xingu Indigenous Park.Mato Grosso, Brasil. © Rogério Assis, 2011Cartographic sources for the theme Fires (Hot Spots): • <strong>Instituto</strong> Nacional de Pesquisas Espaciais de Brasil (INPE), 2011 (http://www.dpi.inpe.br/proarco/bdqueimadas/). Ocean and relieve: World Physical Map,U.S. National Park Service,in ArcGIS Online Services.Ä In 2010 the number of forest fires in theXingu Indigenous Park reached 884, almostfour times as high as 2007, the previousrecord-high year for fires.¾ Guyane Française was proportionallythe country with the highest number offorest fires in protected areas duringthe period 2000-2010 (44.7%).¸ In the arc of deforestation in Brasil,most of the forest fires are recordedin areas of Cerrado, dry forests ortransition zones.– Amazonia under Pressure 45 <strong>RAISG</strong>
epresented in 10 km 2 boxes and separated into two periods: 2000-2005 and 2006–2010. The informationwas analyzed for the following units: Amazonia, Amazonian countries, macro-basins and subbasins,Protected Natural Areas and Indigenous Territories.GFI1. Fires recorded annually in Amazonia over the period 2000-2010BFI1. Xingu Indigenous Park on the fire pathThe 16 indigenous peoples who live in the Xingu Indigenous Park (PIX) – one of the best known indigenous territories in the BrazilianAmazonia, spanning across 280,000 km 2 – have discovered a growing tendency for fire, which was always used in traditionalactivities, to go out of control: small fires that previously burnt themselves out now very easily become forest fires, while the burningof vegetation used to clear fields now invades the forest, and so on. In 2010, a very dry year, the number of forest fires inside the PIXreached 884, almost four times higher than in 2007, which was the year with the most forest fires in a decade. Fire fighting brigadesalready exist in many villages.Forest fires are, at the same time, cause and effect of the profound changes occurring in the Amazon basin (Davidson et al., 2012).Recent estimates indicate that the combination of deforestation and climate change may increase the occurrence of fires in Amazoniaby almost 50% by 2050, giving rise to a cycle of degradation and loss of biodiversity (Silvestrini et al., 2011). In the Xingu basin,situated in the transition zone between savannah and forest in the Brazilian Amazonia, fire has increasingly become a threat to socioenvironmentalsustainability.Fire, used to clear lands already deforested for agricultural practices or to open new lands for crops, may escape control and affectlarge tracts of forest. Forest fires, including those occurring deep in the forest, without destroying the forest cover immediately, increasethe mortality rate of trees and the opening of the forest canopy, reducing the forest’s humidity, increasing the quantity of dry materialwithin the forest and making it more susceptible to new blazes (Nepstad et al., 2001). Besides affecting the structure and compositionof the forest, the fires kill off wildlife, provoke the emission of greenhouse gases, worsening global warming, and produce smoke,which reduces local rainfall and causes respiratory andother health problems among humans (Cochrane 2003).The transition forests found in the region formed bythe Xingu’s headwaters are naturally more susceptible tofire compared to other types of forest, given that theyare smaller, have less dense plant cover and have lowerhumidity in the driest months (Ray et al., 2005; Alencaret al., 2006). This vulnerability is exacerbated by thehigh rates of deforestation affecting the region. Hencethese forests are considered one of the ecosystemsmost threatened within the Amazon basin. In extremelydry years, the surface affected by forest fires may beup to 14 times greater than in normal years (Alencar etal., 2006). With climate change and the increase in thedesertification of the forest, these events tend to be morefrequent and intense.Fire, used traditionally by indigenous peoples in theirsubsistence activities (for example, to clear fields, gatherhoney and to make small campfires during fishing andhunt trips), has become an ever bigger threat. As theforest has become more inflammable, traditional managementpractices already no longer seem sufficient tocontrol them. This fact shows the need for traditionalpractices to adapt to the climate changes taking placeon the planet. (Adapted from Observing the Xingu basin,ISA 2012)MFI3. Quantity of fires per country in Amazonia (2000-2010)Amazonia as a wholeA total of 1,320,866 fires were recorded for the period 2000-2010. The years with the highestnumber of fires were 2004, 2005 and 2002, in this order (GFI1). There were more fires during the2000-2005 period (approximately 685,000) than the 2006-2010 period (approximately 551,000).The largest number of fires occurred in the months of August, September and October, withthe highest figures recorded for September 2004 (59,698), August 2005 (51,627) and September2005 (59,455).These fires were detected in larger proportion in the southeast of Amazonia (MFI2), a zonecalled the ‘arc of deforestation’ of Brazilian Amazonia (Schor et al., 2008; Vieira et al., 2008) andBolivian Amazonia.MFI2. Fires in Amazonia in the period 2000-2010 (quantity per 10 km 2 squares)GFI2. Fires recorded monthly in Amazonia over the period 2000-2010By BasinGFI3. Annual quantity of fires recorded in Brazilian Amazonia overthe period 2000-2010The Middle-Lower Amazonas macro-basin presented the highest number of fires, followed byTocantins and Madeira. This trend was maintained over the eleven year time span, although more intenselyduring the 2000-2005 period (see TFI1 and MFI4).The sub-basins with the largest number of fires were the Western Northeast Atlantic S, TelesPires, Lower Araguaia, Arinos and Lower Tocantins. In all cases, the largest proportion of fires wasrecorded during the period 2000-2005 (TFI2 and MFI5).MFI4. Quantity of fires per macro-basin in Amazonia (2000-2010)Amazonia in each countryA total of 1,194,060 (90%) fires occurred in Brazilian Amazonia during the 2000-2010 period.The largest numbers occurred in the years 2004 (166,750), 2005 (161,589) and 2002 (157,299), andthe lowest in the years 2009 (39,627) and 2000 (66,175). The months with the largest number of fireswere August, September and October. It should be emphasized that there are large areas of savannahand drier transition forests within the limits of Brazilian Amazonia, which is where 25.7% of the detectedfires occured (GFI2).Bolivia had the second highest number of recorded fires, a total of 97,033, followed by Venezuelawith a total of 19,912. In Perú 4,364 fires were counted, while in Colombia a total of 2,962 wererecorded. In Guyana there were 1,619 fires. Finally the countries with fewer than 500 recorded fires wereSuriname (490), Guyane Française (369) and Ecuador (57). The annual distribution of fires, except forBrasil, is shown in GFI3.The largest proportion of fires in Bolivia, Brasil, Ecuador, Perú and Venezuela were detectedduring the 2000-2005 period, while in Colombia, Guyana, Guyane Française and Suriname the highestnumbers were in the 2006-2010 period. The intensity of fires per country in the period 2000-2010 isrepresented in MFI3.TFI1. Fires recorded in the macro-basins of Amazonia over the period 2000-2010Macro-basin 2000-2005 2006-2010 TotalMiddle-Lower Amazonas 295,971 130,164 426,135Tocantins 174,442 116,067 290,509Madeira 158,919 78,059 236,978Western Northeast Atlantic 102,024 58,356 160,380Mouth of the Amazonas/Estuary 47,356 27,186 74,542Paraná 27,221 16,619 43,840Upper Amazonas 17,655 7,247 24,902Orinoco 13,347 5,839 19,186Negro 12,570 5,478 18,048Parnaíba 10,325 6,588 16,913Guyanas/Amapá 5,570 3,565 9,135Middle Amazonas 156 33 189São Francisco 31 22 53<strong>RAISG</strong> 46Amazonia under Pressure – FiresFires– Amazonia under Pressure 47 <strong>RAISG</strong>