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between the two groupsmay also bemuted because residentsmay have different
perceptions about their claims to land they occupy according to their length of
residence (see for exampleLanjouwandLevy (2002)).
8.7 OverallDiscussion
Anecdotal evidence in Thailand shows that North Thailand witnessed a large
increase in deforested area during the years 1986–1996. One ofmain reasons for
this is claimed to be agricultural expansion. ASB (2004) reports that during the
same period, area devoted to upland rice area grew rapidly aswell. To the extent
that both these occurred concomitantly, and that upland rice cannot be grown on
landdevotedtoothercrops, thestudysuggests that itmaybeimportant todoamore
detailedanalysisof thefactorsaffectinguplandricecultivationespeciallysince it is
seen as being detrimental to the environment. Upland rice is grown onmountain
slopeswith thin soil and low fertility, i.e. on land that is otherwise agriculturally
marginal and undisturbed. Upland rice also has a much larger effect on the
surrounding ecosystem compared to paddy rice and soybean. On the other hand,
paddyriceandsoybeancanbeintercroppedandareusuallygrownonagriculturally
important landwhile upland rice is usually not grownwith other crops (in these
contexts). Specifically speaking upland rice is grown on lands which is deserted
after twoor three crops havebeenplanted andharvested.
This study suggests that a reduction in travel time tomarket reduces the area
devoted to upland rice. It also suggests that while not affecting forest cover, a
reduction in travel time tomarket may also help to reduce the incentive to adopt
and cultivate upland rice. One policy implication from this study is to encourage
crops that allowmultiple rotation in the lowlands, and thus reduce pressures that
push the agricultural frontier tomountain slopes that are prone to erosion.Under-
standingthemagnitudesof impactsoncropadoptionandacreageofpopulationand
roads can also help understand certain trade-offs. If for example, road building is
beingconsideredas apolicyoption in a region, but there is evidence that it affects
crop adoption and acreage, thenunderstandingwhich crops are affectedmost, can
help tounderstandotherwise unintended repercussions of this policy.
References
Alix-Garcia, J., et al. (2011). The ecological footprint of poverty alleviation: Evidence from
Mexico’sOportunidadesProgram.
Alix-Garcia, J., Aronson,G., Radeloff, V., Ramirez-Reyes, C., Shapiro, E., Sims,K.,&Ya~nez-
Pagans, P. (2014). Environmental and socioeconomic Impacts of Mexico’s payments for
ecosystem services program.
Andam,K. S., Ferraro, P. J., Pfaff,A. S. P.,&Sanchez-Azofeifa,G.A. (2007).Protected areas
and avoided deforestation: A statistical evaluation (Final report). Washington, DC: Global
EnvironmentFacilityEvaluationOffice.
150 J. Puri
Evaluating Climate Change Action for Sustainable Development
- Title
- Evaluating Climate Change Action for Sustainable Development
- Authors
- Juha I. Uitto
- Jyotsna Puri
- Rob D. van den Berg
- Publisher
- Springer Open
- Date
- 2017
- Language
- German
- License
- CC BY-NC 3.0
- ISBN
- 978-3-319-43702-6
- Size
- 15.5 x 24.1 cm
- Pages
- 365
- Keywords
- Climate Change, Sustainable Development, Climate Change/ Climate Change Impacts, Environmental Management
- Categories
- Naturwissenschaften Umwelt und Klima