New roads have been proposed within the Maya Biosphere Reserve (MBR), some linkingGuatemala to Mexico. The MBR is a 2 million-hectare protected area in NorthernGuatemala that encompasses part of the Maya Forest, which extends into Belize andMexico and is the largest remaining forest in Mesoamerica. Parts of the MBR are strictlyprotected, while others allow logging, agriculture and other human activities. Past roadbuilding in and around the MBR has been strongly associated with <strong>de</strong>forestation, andthere is little reason to suppose that future roads will be different in this regard. Thatmakes the projected future routes through the MBR a critical matter of conservationand <strong>de</strong>velopment policy.This study explores the costs and benefits of new roads in the MBR. We analyze theimpacts related to the <strong>de</strong>forestation and fires likely to be caused by the constructionof several routes: Uaxatún-Arroyo Negro, Carmelita-Mirador, Lagunitas-El Ceibo,Circuito Yaxhá-Nakum-Naranjo, Melchor <strong>de</strong> Mencos-Tres Ban<strong>de</strong>ras. We perform in<strong>de</strong>ptheconomic analyses of Tikal-Caobas and San Andrés-Mirador, because theyappear most likely to be constructed over the medium term. These analyses consi<strong>de</strong>r thecosts of construction and maintenance, and of lost forest goods and services. Weighedagainst these expenses are the benefits of cheaper and quicker transportation betweenand within Guatemala and Mexico, as well as easier access to tourist <strong>de</strong>stinations inGuatemala.Building the Tikal-Caobas route (which inclu<strong>de</strong>s Uaxatún-Arroyo Negro stretch), fromTikal north across the MBR to the Mexican bor<strong>de</strong>r, would generate a total net loss onthe or<strong>de</strong>r of US$ 54 million. US$ 14 million of the losses would be suffered by Mexicoand US$ 40 million by Guatemala. That result does not inclu<strong>de</strong> environmental costs.Deforestation could increase Guatemalan losses to more than US$ 56 million, due tothe <strong>de</strong>struction of timber, non-timber forest products and carbon stores.The San Andrés-Carmelita project would consist of paving the road from San Andrés toCarmelita, and building a new paved route from there to the El Mirador archeologicalsite. These roads would incur economic losses of US$ 21 million. That figure climbs toat least US$ 26 million in net losses when environmental costs are consi<strong>de</strong>red.Building all five new roads would result in the <strong>de</strong>forestation of at least 37,530 hectares bythe year 2025. In addition, we estimate that roads would cause 41,170 additional hectaresto burn between 2010 and 2015, with another 104,600 hectares consumed by fire between2020 and 2025. The roads would also result in significant habitat fragmentation, with aprojected 47% reduction of forest free from ecological “edge effects.”These results suggest that at least the Tikal-Caobas and San Andres-Mirador roadsrepresent poor investment choices. Their <strong>de</strong>velopment value is negative, because their2 0 CONSERVATION STRATEGY FUND ConservaCIÓN Estratégica SERIE TÉCNICA 8 abril <strong>de</strong> 2007
construction and maintenance consume more resources than can possibly be offsetby savings in transportation expenditures and induced benefits from tourism. In theformer case, this finding can be explained by the fact that unmet local transportation<strong>de</strong>mand is low and international <strong>de</strong>mand is already served by a route – via Belize – thatis almost the same length as the proposed route through the MBR. Low local <strong>de</strong>mand isalso the driving force in the San Andres-Mirador results.Environmental sustainability would also be poorly served by building new roads inthe MBR. Deforestation, fire and habitat fragmentation would <strong>de</strong>prive the MBR of theenvironmental goods and services that led the Guatemalan Congress to establish it in1990. While better roads could eventually facilitate tourists’ access to more sites withinthe reserve, substantial and continuous control expenditures would be nee<strong>de</strong>d to avoid<strong>de</strong>struction of those very same sites. Tikal National Park, where a paved road has notled to <strong>de</strong>forestation, is a useful indicator of the scale of that control cost. CurrentlyTikal has 32 times as many conservation technicians (“técnicos”) and six times as manypark guards per unit area as the rest of the MBR.Other investments should be sought to improve international and local transportationin the bor<strong>de</strong>r region of Guatemala, Mexico and Belize. Likewise, alternativeinvestments should be studied to increase living standards in and around the MBR.Rigorous economic, environmental and equity criteria should be applied to ensure thatpublic spending leads to real, lasting <strong>de</strong>velopment and preserves Guatemala’s naturalheritage.Parallel to this study, a collaborating team (Amor et al. 2007) carried out a regionalanalysis of road impacts on the Selva Maya and the Mesoamerican Biological Corridor(MBC). In both studies the same internal analysis of transport economics of the SanAndrés-Mirador and the Tikal-Caobas projects was used, so the results are the same.The environmental externality valuation results are different because of differencesin the <strong>de</strong>forestation mo<strong>de</strong>ls used in the two studies. The regional mo<strong>de</strong>l used lessvariables, because obtaining comparable data for different countries was not practical.The local analysis projects changes that would occur in the Maya Biosphere Reserve in<strong>de</strong>tail, while the regional analysis explains the implications of roads over broad areason Northern Mesoamerica.<strong>Análisis</strong> Económico y Ambiental <strong>de</strong> Carreteras Propuestas <strong>de</strong>ntro <strong>de</strong> la Reserva <strong>de</strong> la Biosfera Maya 2 1
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asado en el modelo más reciente HD
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Tabla 16. Distancias de Subteniente
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ingresa es de origen externo y, por
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actualmente no existe un camino 23
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En la Zona de Uso Múltiple se esti
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Tabla 23. VAN y TIR del Proyecto Ca
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Tabla 24. Valor de las emisiones de
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Costos ambientales agregados de tod
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Los proyectos carreteros Tikal-Caob
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Es importante recalcar que las carr
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Alencar, A., Solórzano, L., Nepsta
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CONAP. 2003. Informe de estadístic
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Medellín, R. 1991. The Selva Lacan
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Secretaria de Comunicación y Trans
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Anexo 1 Valores de deforestación y
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807060Flores - BethelFlores - XanFl
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1.41.210.80.60.4Moran I0.20-0.2-0.4
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No Nombre corto Nombre largo Papel
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Anexo 3 Detalles de resultados del
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Tabla A5. Matriz de correlación de
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Anexo 4 Cálculos para la estimaci
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Anexo 5 Detalles de cálculos para
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Tabla A10. Pérdidas de carbono por
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Tabla A12. Especies por grupo comer
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Anexo 9 Desglose de costos del tram
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Anexo 10 Desglose de beneficios del
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Anexo 11 Costos totales, beneficios