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overnight. This takes time; in fact the impact assessment done at the end of the
project asked for “adequate time” to pass and for a stable situation to be achieved
before impact is assessed (Ittyerah et al. 2005, p. xv). And if individual projects
need adequate time to have an impact, it follows thatmarket change can only be
observed andmeasuredover even longer stretches of time.Longer time lapses are
well known in environmental circles and on environmental impact, as Hilde´n
(2009)andRowe(2014,54–55)havepointedout,but theytendtobelessassociated
withmarket change.The slowpaceofmarket change ismore oftenobservedwith
impatience, raising the question why no change is happening, which ledW€orlen
(2014) inher studyof climatemitigation evaluations to reformulate the “theoryof
change” approach to a “theory of no change approach” that focuses on a better
understandingofmarket barriers andhow they canbeovercome.
In general environmental boundaries do not follow jurisdictional boundaries.
One ecosystem may spread over several countries, and one country may have
several ecosystems. Rowe (2012) asked attention for the fact that location may
differ conceptually and practically between a social and economic system that is
targeted forchangeandanecosystemthat is influenced through the same interven-
tionoraction.But this isnotonlyanissueofdifferent locationsofsystems,butalso
of scopeof an intervention: itmaybe focusedonadirect impact in thevillages in
which it is implemented,while other areas are still outside the scopeof theproject
or have not yet been approached by suppliers, or invited to participate byState or
Federal government.
It is an issueof scalewhen impactneeds tobeobservedat several levels: thatof
energy supply and demand, of greenhouse gas emissions related to energy, of
greenhousegasemissionsincludingdeforestationandalternativesourcesofenergy,
of livelihood and financial resources issues in the villages, of hilly rural areas in
general, andperhaps somewhatmore removed,whether greenhousegas emissions
in India are positively influenced bywhat happens in remote hilly areas. The last
doesnot seemlikely, and itmay lead toa feelingofdisenchantment– if it doesnot
help India, itdoesnothelp theworld, and itdoesnot stopclimatechange.3But that
was thereason theprojectwasco-fundedbytheGlobalEnvironmentFacility in the
first place!
Scale is not easily defined. It seems clear that while interventions or actions
move fromone actor tomultiple, fromone location tomany, from a “local” to a
“national” or even “global” level thatmovingup scales is involved, but scales can
also be understood in terms of different dimensions or sectors. Kennedy et al.
(2009) recognises jurisdictional andmanagement dimensions as different scales,
and Bruyninckx (2009) asks attention for overlap and discrepancies between
social, economic, environmental and spatial scales. Yet even though there is no
universal agreement onhowscales shouldbedefinedorwhat their boundaries are,
3Andagoodoverall conclusionontheprojectwasformulatedbyRatnaReddyetal. (2006,4078):
the overall impact of the project appears to be slightly positive or neutral in amajority of key
indicators.Certainly not amajor contribution to reducedgreenhousegas emissions as hoped for.
3 Mainstreaming ImpactEvidence inClimateChange andSustainableDevelopment 43
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