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Following the review of the impacts of climate

change on natural and human systems (Chapter 2)

and analysis of existing policies (Chapter 3), this

chapter identifies existing adaptation policy gaps,

but also opportunities, relating to country and

sectoral policies on water; ecosystem functions and

biodiversity; food; health, and energy. A selection of

regional cases illustrating adaptation measures and

policies are also presented.

The analysis of national and sector policies shows

that one potential gap is that policies are not designed

for easy integration with other instruments, which is

further complicated when policies are from another

sector. Because adaptation has just started to receive

more attention in policy circles over the last few

years, there is little experience on how to vertically

integrate adaptation instruments and measures from

national to local levels, and whether to do this across

and/or by sector (Hoffmann, 2015). This early stage

of adaptation policy development explains, in part,

why they are still absent in some sectors, and why

existing instruments have not included performance

indicators. Generally speaking, the policies analysed

have been found to be based on sectors’ needs,

whereby key climate risks identified under Chapter 2

have not guided policy design.

Analysis reveals that there is little specific mention

of mountains in the sectors’

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policies and few

specific policies for mountains. However, certain

instruments do have a mountain specific scope.

For example, in Ecuador the páramo are defined as

fragile ecosystems in Ecuador and included as such

in different policies. In addition to the perceived

Comparative analysis of available policies

remoteness of mountains, this neglect could be due

to several factors. These could include the perception

that mountains do not have unique problems or that

the problems are already being addressed by non-

mountain-specific approaches (Ariza et al., 2013).

The difficulty in defining mountain ecosystems

(including their boundaries) hinders using them as

units for policy design, even when there is political

interest in such ecosystems. Policies may also be

more focused on urban and/or lowland areas and

there might be greater interest in protecting an

ecosystem’s functions and services rather than the

ecosystem itself (i.e. mountains). Another possible

explanation is that mountains become objects for

policymakers only when impacts visibly affect urban

centres, lowlands or productive activities important

for the Gross National Product [including “damaging

extractive industries”]).

Though mountains in the region are not specifically

acknowledged as policy “objects/subjects of interest”,

more analyses are needed of the multiple impacts of

climate change on mountain ecosystems and sectors.

For instance, changing water availability within

mountains may have significant impacts on health,

energy, and several productive sectors, which in turn

will feed back on adaptive capacity and exposure of

mountain social-ecological systems. Further, these

impacts will hinder economic development from the

national to the local levels, and cause livelihood and

economic losses at the local levels.

Although extreme weather events and their direct

impacts (e.g. through floods and landslides)

on populations do grant them attention from

policymakers, this is mainly in the formof emergency

ad-hoc measures and disaster risk management/

reduction, while adaptation policies to prevent such

losses or increase resilience remain sectoral-based.

Finally, there is a clear disconnect between the

scientific community and the transfer and uptake of

scientific knowledge in policymaking. This gap is an

opportunity for collaborative work among scientists,

public and international agencies, civil society, and

mountain populations (who are among the most

vulnerable to social, political and climatic changes).

Farmers, Venezuela