Abstract
Establishing protected natural areas (PNA) has been one of the main policy mechanisms used for protecting flora and fauna species. However, in the last 18 years we have seen a sharp reduction in forest cover in Peru and this may have been exacerbated by the development of road infrastructure. Despite the accepted fact that roads can bring about socioeconomic benefits, it can also have negative environmental effects, such as deforestation. Using a difference in difference model with two treatments, we study the effectiveness of PNA to prevent deforestation in the presence of road infrastructure over panel data information. Our findings suggest that the expansion of the road network over the last decade has had an impact, increasing the rate of deforestation in the Peruvian Amazon. However, the increase in protected areas has partially neutralized this effect. On average, the approach of roads to within 10 km of the forests has been associated with reductions in forest coverage of around 7.1 km per 400 km2. In spite of this, the simultaneous creation of protected areas has led to a reduction in the deforestation rate of around 6.5 km2 per 400 km2. It seems that regardless of the “deforestation” effect of roads, PNA fulfill their protective role.
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Notes
Following to The Millennium Ecosystem Assessment (MA, 2003),the ecosystem services provided by the forest ecosystem services that contribute to a range of human outcomes can be: (i) provisioning services: providing food, timber, fiber, and others forest products contributing to poverty eradication and income generation, (ii) regulating services: sequestering and storing carbon from the atmosphere contributing to regulation of the global carbon cycle and climate change mitigation, (iii) cultural services: providing recreational opportunities, esthetic enjoyment and spiritual enrichment, and (iv) supporting services: producing and conserving soil, and stabilizing stream flows and water runoff -preventing land degradation and desertification and reducing the risks of natural disasters such as droughts, floods, and landslides.
The marine coverage is measured over national waters.
According to the Ministry of Transports and Communications (MTC) between 2000 and 2016 the road infrastructure in Peru was expanded from 78,213 to 165,905 km (that is, by 112%).
The construction of the Inter-Oceanic Highway in Madre de Dios (US$ 2.8 billion, 1600-mile paved road from the coast of Peru to Brazil) completed in 2011 had considerable impact on forest cover and structure-mainly, migration and (illegal) gold mining activities-although it has opened access to isolated forest regions (Oliveira et al. 2007; Smith and Schwartz 2015).
Our paper focuses its impact analysis on deforestation but not on socioeconomic outcomes, such as revenues, poverty, migration, etc. Notwithstanding the foregoing, the socioeconomic impacts of PNA are not clear at all. Díaz and Miranda (2012) find that the estimated effect on welfare at the level of income and expenses is largely negative (but higher in income than for expenses) for different types of PNA, including parks or reserves, and economic activities (direct-use, indirect-use, and tourism). In a subsequent study, Miranda et al. (2014) do not detect any improvements in welfare among households close to protected areas. Moreover, Robalino et al. (2012) found that PNAs had a largely negative impact on different socioeconomic indicators, including population growth, income inequality, and poverty. Conversely, other studies point to positive effects on welfare. For instance, Andam et al. (2010) showed that the implementation of protected areas reduces poverty in comparison to similar localities without PNA due to a greater tourist activity. Specifically, in Costa Rica, the income of populations situated close to park entrances was 13.5% higher than that corresponding to populations living farther from these locations. Additionally, in Thailand, the average monthly household consumption increased by 4.5% in places with protected areas. Along this line, Sims (2010) studied the Thailand case and found that the PNA reduced local poverty although it may have increased overall local inequality. Some other studies that point to positive effects of PNA on welfare are Robalino and Villalobos-Fiatt, (2010), and Canavire and Hanauer (2013).
“Protected Natural Areas are the continental and/or marine spaces of the national territory, expressly recognized and declared as such, including their categories and zoning, to conserve biological diversity and other associated values of culture, landscape and science, as well as for its contribution to the sustainable development of the country. The Natural Protected Areas constitute patrimony of the Nation. It´s natural condition must be maintained in perpetuity, allowing the regulated use of the area and the use of resources, or determine the restriction of direct uses.” (Article No. 1 of Law No. 26834 of the year 1997).
References cited by Khandker et al.(2009).
References cited by Khandker et al.(2009).
And also, Michalopoulus and Papaioannou (2014).
We constructed a variable to identify whether a district pertains primarily to the coast, highlands, or the jungle based on the average altitude of the settlements therein.
It could be possible that a road was destroyed between these two years or some PNA became deactivated, but in our dataset we do not have cases like these.
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Acknowledgements
We thank participants at the 9th Bolivian Conference on Development Economics in 2018 and at the 2019 annual congress of the Peruvian Economic Association for their useful comments and suggestions. We extend our gratitude to Pedro Rojas for his valuable research assistant support. Finally, the authors want to acknowledge the Economic and Social Research Consortium (CIES)—Grant Number PMA1AN60-969 for financing the research. The opinions contained herein represent those of the author only.
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Aguirre, J., Guerrero, E. & Campana, Y. How effective are protected natural areas when roads are present? An analysis of the Peruvian case. Environ Econ Policy Stud 23, 831–859 (2021). https://doi.org/10.1007/s10018-021-00304-y
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DOI: https://doi.org/10.1007/s10018-021-00304-y