Trade liberalization and forest transition

Date01 September 2017
AuthorFernando Pueyo,Rafael González‐Val
Published date01 September 2017
DOIhttp://doi.org/10.1111/ijet.12129
doi: 10.1111/ijet.12129
Trade liberalization and forest transition
Rafael Gonz´
alez-Valand Fernando Pueyo
Wede velopa theoretical model that provides an additional explanation for the forest transition
based on a trade liberalization scenario. Weintroduce a renewable natural resource (wood), used
as an input by manufacturing firms, in a framework with economic geography foundations:
transport costs affect the spatial distribution of firms. In a general equilibrium, the results
reproduce the forest transition at a global scale: a decrease in transport costs has an initial
negative effect on the worldwide stock of the natural resource, but this effect is offset over time
as a consequence of industrial reallocation and eventually disappears in the long run.
Key wor ds forest transition, natural resource, industrial location, trade liberalization
JEL classification F18, Q20, Q23, R12
Accepted 25 February 2016
1 Introduction
There is an extensive literature on the effects of trade liberalization on natural resources. A general
conclusion might be that an increasing openness to international trade (basically represented by
the fall in international transport costs, although changes in other trade policy measures are also
important) increases the specialization of different countries. Therefore, those with comparative
advantages in natural resources increase their natural condition as suppliers of these resources to
the rest, who specialize in industrial activities. This is the typical result of the theory of international
trade: liberalization leads to specialization – complete, as in Ricardo’s world, or incomplete, as in
Krugman (1980).
Among all natural resources, the effect on forest areas has received much attention in the lit-
erature; see the review by Robalino and Herrera (2009). In the context of growing environmental
concerns, the loss of forest area has emerged as a problem in many developedcountries. The g rowth
of economic activity requires increasing amounts of resources (land, timber, etc.). To the extent
that they are not renewable or that their regeneration is relatively slow, one might expect a gradual
depletion of these resources.
Department of Economic Analysis, Faculty of Economics and Business, University of Zaragoza, Zaragoza and Institut
d’Economia de Barcelona (IEB), Faculty of Economics and Business, University of Barcelona,Barcelona, Spain. Email:
rafaelg@unizar.es
Department of Economic Analysis, Faculty of Economics and Business, Universityof Zaragoza, Zaragoza, Spain.
Financial support was provided by the Spanish Ministerio de Econom´
ia y Competitividad (projects ECO2013-45969-P
and ECO2016-75941-R), the DGA (ADETRE research group) and FEDER. Earlier versions of this paper were presented
at the 19th Annual Conference of the EuropeanAssociation of Environmental and Resource Economists (Prague, 2012),
at the 66th European Meeting of the Econometric Society (M´
alaga, 2012), at the 59th Annual North American Meetings
of the Regional Science Association International (Ottawa, 2012), at the Fifth World Congress of Environmental and
Resource Economists (Istanbul, 2014), and at the XXXIX Simposio de An´
alisis Econ´
omico (Palma de Mallorca, 2014),
and all the comments made by participants are much appreciated. All remaininger rorsare ours.
International Journal of Economic Theory 13 (2017) 269–287 © IAET 269
International Journal of Economic Theory
Trade and forest transition Rafael Gonz´
alez-Valand Fernando Pueyo
Figure 1 Change in forest area (annual rates of change), 1990–2010
Source: FAOSTAT.The Global Forest Resource Assessment (FAO 2010) is the main sourceof forest area
data in FAOSTAT. Data were provided bycountr ies for the years1990, 2000, 2005 and 2010. Data on
intermediate years were estimated for FAO using linear interpolation and tabulation.
Note: Trend curves fitted by locally weighted scatter plot smoothing.
However, recent data offer partial good news. After several decades of continuous decrease in
forest areasall over the world, the rates of deforestation have diminished in many countries over recent
years. One of the key findings of the Global Forest Resources Assessment 2010 (Food and Agriculture
Organization (FAO) 2010) was that “ther ateof deforestation shows signs of decreasing”, although it
is still high. Figure 1 shows the annual rates of change in the forest areas of different regions based
on data from FAOSTAT. The left-hand graph displays the evolution in world rates and in the rates of
the Americas (North America, Central America, South America and the Caribbean). The Americas
represented 39% of the worldwide forest area in 2010. We can observe that, although growth rates
remain negative, there has been a remarkable decrease in deforestation rates both at world and at
American levels in recent years. The right-hand graph highlights the Brazilian case, where a growing
evolution in rates is also observed. Brazil represented 13% of the total forest area in the world in
2010, and the Brazilian Amazon is one of the most important cases of study. Obviously,this evidence
is weak as the data span considered is very short, only from 1990 to 2010. However, there are several
papers that document this forest change in different areas: Finland (Myllyntaus and Mattila 2002),
India (Foster and Rosenzweig 2003), southeastern Mexico (Brayand Klepeis 2005), the Ecuador ian
Andes (Farley 2010), the Ecuadorian Amazon (Rudel et al. 2002) and northeastern United States
(Pfaff and Walker2010).
This change in the trend from decreasing to expanding forestswas defined as the forest transition
by Mather (1992), which suggests the existence of a turning point. Therefore, the forest transition
theory (FTT) provides a framework for explaining scenarios of increasing forest cover after a de-
creasing phase. That is to say, although in the first stage economic activity needs a growing volume
of natural resources and this thus causes the depletion of forests, at some point the trend reverses,
allowing the recovery of the forest area. The argument can also be formulated in terms of the envi-
ronmental Kuznets curve (see Pfaff and Walker 2010). Empirically, evidence supporting the forest
transition is increasing. By using data from the Global Forest Resources Assessment 2015 (FAO2015),
Keenan et al. (2015) find that, between 1990 and 2015, 13 tropical countries may have either passed
through their forest transitions from net forest loss to net forest expansion, or continued along the
path of forest expansion that follows these transitions.
Many papers (Pfaff 2000; Andersen et al. 2002; Weinhold and Reis 2004; Pfaff and Walker
2010) point to increased transport easiness (through reductions in costs or liberalization of
270 International Journal of Economic Theory 13 (2017) 269–287 © IAET

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