madagascar research and conservation programme - annual report 2012
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INTRODUCTION
History
Goal and five-year objective
Our five-key principles
PROJECT SITES
ACTIVITIES AND ACHIEVEMENTS
Providing a legal framework for long term
conservation
Community based management of natural
resources and alternatives
Research and Monitoring
Restoration
Awareness-raising and Communication
Poverty reduction
FUNDING
IMPACT
PERSPECTIVES FOR 2013
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3
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History
At the start of the millennium, the staff of
Missouri Botanical Garden-Madagascar
prided ourselves on being the most acve
organizaon in the world researching and
sharing knowledge about the Malagasy
flora and developing in-country compe-tence in field botany and taxonomic re-
search. Today, we are sll the most
effecve organizaon in these respects,
but we are also one of Madagascars most
successful and innovave in achieving
community-based conservaon. This new
development originated from the desire
of MBGs young Malagasy staff not only to
discover and understand their highly
threatened flora, but also to play an acverole in halng its loss. To address this cri-
cal need, we first conducted research to
idenfy 79 priority areas for plant conser-
vaon (PAPCs); then, in 2002, we laun-
ched a pilot project to conserve, through a
sustainable community-based iniave,
one of these areas the Agnalazaha Fo-
rest, a rare and precious fragment of lio-
ral forest in southeast Madagascar.
Success at this site encouraged us to ex-pand our conservaon program, and
today we support conservaon projects at
eleven PAPCs, distributed throughout the
country, with a total area of nearly 60,000
ha. All but one of these sites (the ny An-
kafobe Forest, which is managed as a com-
munity reserve) have now formally been
given Temporary Protecon by the Mala-
gasy government, the first of two stages in
the process leading to permanent des-
ignaons as a New Protected Area.
Goal and five-year objecve
In April 2009 a strategic planning meeng
was held in Antananarivo aended by
staff members of MBGs Conservaon
Unit. The parcipants formulated our pro-
grams goal and developed a five year ob-
jecve, as follows:
Our goal is To conserve Madagascars na-
ve flora in its natural ecosystems in order
to support and enrich life.
Our five year objecve (2009 to 2014) is
To achieve the effecve management of
eleven priority sites for plant conservaon
according to the specific objecves of
each site and with progressive increase inparcipaon of the local communies.
Our five key principles
MBGs conservaon program is basedon five underlying principles that guideall aspects of the development and im-plementaon of our work.
Analycal, informaon-based decision-
makingWe believe that good management strate-
gies can be developed only when based
on thorough understanding of each sites
specific human, physical and biological en-
vironment and the parcular opportuni-
es and threats that flow from this
context. We reject both the unthinking
implementaon of acvies at a succes-
sion of sites irrespecve of need and deci-
sion-making based on unsupported
preconcepons. Rather, we develop work
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I NTRODUCTION
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plans based on the collecon and analysis
of informaon. When methods are un-
proven, they are monitored and tested
using an experimental approach.
Conservaon by the people for the people
Although Madagascars flora and faunaare highly valued by sciensts and much
appreciated by tourists, we believe that
the primary beneficiaries of conservaon
should be local people. Never would we
want to exclude locals from their natural
heritage and create reserves that serve
only researchers, tourists and other outsi-
ders. Such an approach would be both
unfair and ulmately unlikely to result in
long-term biodiversity conservaon. To
avoid such exclusion while sll achieving
conservaon is a major challenge that re-
quires valorizing each area for local stake-
holders, developing in them a sense of
ownership and responsibility for the site,
and empowering them to oversee the sus-
tainable management of the natural re-
sources in their area, thereby creang a
stewardship paradigm in which it makes
more sense for them to use natural wealth
sustainably than to squander it.
Inclusiveness
We believe that durable conservaon pro-
jects must be inclusive and involve those
from all groups in society, including the
young, elderly, women, economically less
advantaged, and new immigrants. Oen it
is the young and new immigrants to an
area who lacking their own land and are
forced to seek their livelihoods from the
non-sustainable exploitaon of natural re-
sources. Although quick results can be ob-
tained by focusing efforts on winning the
support of the powerful, there is oen a
rapid turnover among these people, and
todays powerful ally can be quickly repla-
ced by his/her competor, with disastrous
results for the project. To understand fully
the threats to a site and to develop effec-
tive methods to diminish these threats
requires the full engagement of the enre
community.
Respect for tradions
Most rural Malagasy are conservave and
somemes slow to adopt innovaons.
Therefore, community-based conserva-on must find ways of working with tradi-
ons and, where possible, valorize local
cultures to achieve the projects objec-
ves. Oen, conservaon approaches are
perfectly consistent with local cultures
and their acceptability much enhanced if
framed in this context. In addion, we be-
lieve that unwrien societal rules are
much more powerful in controlling abu-
sive exploitaon of natural resources than
is naonal legislaon, and certainly more
resilient to the whims of naonal policians.
Grassroots project concepon and imple-
mentaon
In many conservaon organizaons, the
best people are based at headquarters,
managing projects from far away through
locally recruited intermediates, using sim-
ple one size fits all soluons that regu-
larly yield disappoinng results. There is
lile opportunity or movaon to develop
the personal commitment and understan-
ding needed to fight for the kind of
change that is urgently required or to
grasp and deal with the complex and site-
specific causes of environmental degrada-
on. To avoid this scenario, at MBG -
Madagascar we place our best people clo-
sest to the problem, challenge them to
understand the complex reasons for the
environmental degradaon in their com-
munies, and trust and empower them to
work with local stakeholders to develop
and implement an effecve program of
acvies to achieve for their project goal.
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Agnalazaha Forest
(Conservaon Facilitator : Ludovic Reza)With an area of 2250 ha, this forest is one
of the largest fragments of lioral forest
(low-elevaon humid evergreen forest on
sand) remaining in Madagascar. It is loca-
ted in SE Madagascar, about 50 km south
of the town of Farafangana, within Ma-
habo-Mananivo Commune. Our invento-
ries show that the forest and its adjacent
marshes, rivers and lakes support a rich
flora and fauna including several speciesthat are locally endemic and endangered,
such as the newly discovered Diospyros
mahaboensis and Ivodea mahaboensis,
and the very rare and threatened lemur
Eulemur cinereiceps. The forest also makes
an important contribuon to local liveli-
hoods through the diverse goods and ser-
vices that it provides. Our major
achievement at this site is to reduce anar-
chic exploitaon and thereby ensureAgnalazahas resources are available to
both present and future generaons.
Anadabolava-Betsimalaho Thicket
constutes an important means of liveli-
hood for the local populaon, and by wild-
fires, started by local cale rustlers to hide
their tracks. Our main acvity at this site
is to help local farmers culvate crops in
permanent fields adjacent to the Man-
drare River.
(Conservaon Facilitator : Angelos Josso
Tianarifidy)
The 18,000 ha Anadabolava-Betsimalaho
Thicket in southern Madagascar is impor-
tant for several reasons: it is an almost
prisne example of thicket vegetaon,
which in places is tall and almost forest
like in aspect; it supports a rich biodiver-
sity that includes several locally endemic
plant and animal species including the
ring-tailed lemur (Lemur caa) and the ra-
diated tortoise (Geochelone radiata); and
it has a major role in protecng the water-
shed of the Mandrare River, the principal
source of water for 350,000 people. Ho-
wever, the site is threatened both by shif-
ng culvaon, which currently
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Figure 1 : Locaon of project sites
PROJECT SITES
Analalava Forest
(Conservaon Facilitator: Anselme Tilahimena)
This 200 ha parally degraded, low-eleva-
on, humid forest is located in eastern
Madagascar close to the popular coastal
tourist resort town of Foulpointe. The site
is important for conservaon because of
its rich flora, which includes 26 palm spe-
cies and ten plant species endemic to the
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CONSERVATION UNIT ANNUAL REPORT 20124
(Conservaon Facilitator : Tefiharison
Andriamihajarivo)This 15,000 ha sub-humid forest is located
in the dry southwest and exists only be-
cause of a special local climate. This
pocket of humidity in an otherwise very
dry part of Madagascar provides a refuge
for many species normally associated with
the weer eastern part of the country,
and its isolaon has also led to the evolu-
on of a number of locally endemic plants
and animals. The forest is nearlyprisnebecause the local Bara people consider it
to being habited by the spirits of their an-
cestors, and therefore they strictly limit
access and exploitaon within this spiri-
tual refuge. Recently these restricons
have begun to weaken due to the en-
croachment of outside cultures. The fo-
rest also seems to be increasingly
threatened by wild fires that now fre-
quently burn the surrounding grasslandand somemes penetrate into the forest.
Our major acvies at Analavelona are to
support tradional beliefs concerning the
forest and to enable local people to pro-
tect the forest from fires by the installa-
on of firebreaks.
Analavelona Sacred Forest
site. It is important socially because it is
the only remaining fragment of natural ve-
getaon in the area and has a high poten-
al for generang wealth and contribung
to local livelihoods as a tourist aracon.
The site was previously threatened by
shiing culvaon, mber extracon andwildfires, but only the laer threat persists
today. Without our intervenon at this
site, which began in 2005, the Analalava
forest, now regenerang strongly, would
have disappeared.
Ankafobe Forest
(Coach : Jean-Jacques Rasolofonirina)
This ny (33 ha) forest fragment is located
on the Tampoketsa of Ankazobe, on the
Malagasy Central Highlands, a two hours
drive from the capital city of Antanana-
rivo. It consists of three sub-humid ever-
green forest patches located within
adjacent valleys and surrounded by spe-
cies-poor and low-producvity anthropo-
genic grassland. It is primarily importantbecause it contains most of the worlds
total populaon of one of Madagascars
rarest and most threatened trees, Schizo-
laena tampoketsana (Sarcolaenaceae).
The main threat to the Ankafobe Forest is
burning from wild fires, and one of our
main annual acvies at this site is encir-
cling the forest with double firebreaks.
Without this acon, the forest, with its
precious flora, would already have been
reduced to cinders. Among the eleven
sites where we work, the community ad-
jacent to the Ankafobe forest is the most
advanced in accepng full management
responsibility for their natural resources.
Ankarabolava-Agnakatrika Forest
(Conservaon Facilitator : Hubert
Andriamaharoa)
This is a 2400 ha, highly fragmented, low-
elevaon, humid forest on basalt is the
only significant area of natural vegetaon
remaining in Vangindrano District, in
south-eastern Madagascar. It is being
conserved to protect its exceponally di-
verse flora, which includes a large number
of local endemics, and also for its
fauna,which includes the endangered
lemur Eulemur cinereiceps. The forest is
also the source of several streams that ir-
rigate adjacent rice fields. In the last two
decades, two-thirds of this forest has been
destroyed by shiing culvaon and m-
ber extracon, and these threats, al-
though diminished, persist at the site.
Also, fires started to control weeds infes-
ng fields within the forest are oen
poorly controlled and burn several hec-
tares of trees each year. Shiing culva-
on is pracced mainly by young men
who lack other land to farm.
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Makirovana-Tsihomanaomby Forest
source for the many thousands of hectares
of irrigated riceculvaon on the surroun-
ding plains.The forest is threatened byshif-
ng culvaon, vanilla culvaon and the
selecve exploitaon of trees for mbe-
rand precious woods (most notably rose-
wood). While indigenous villagers areanxious to conserve the forest (as a source
of water), recent immigrants to the area
areforced into abusive exploitaon due to
the lack of good farming land on the
plains. The successful conservaon of the
Makirovana-Tsihomanaomby Forest will
require providing these immigrants with
new sources of livelihood that do not de-
pend on the destrucon of the forest.
Oronjia Forest
CONSERVATION UNIT ANNUAL REPORT 2012 5
(Conservaon Facilitator : Jeremie Razafitsalama)
Oronjia is a fragment of dry deciduous fo-
rest located on a sand-covered limestone
peninsula overlooking the huge natural
harbor of Antsiranana in far northern Ma-
dagascar. Following decades of unsustai-
nable exploitaon of the forest to provide
mber and charcoal, as well as clearancefor manioc culvaon, the forest is now
very degraded and would surely have now
disappeared without our intervenon,
which began in 2007. Despite its condi-
on, the forest sll retains most of its ori-
ginal flora and, if exploitaon can be
controlled for a decade or two, will rege-
nerate. The major part of the proposed
New Protected Area, which covers 1648
ha, lies within a military base. Our majorwork at this site is to facilitate the sustai-
nable use of natural resources by the local
community and to valorize the site for
ecotourism.
Ibity Massif
(Conservaon Facilitator : Mamisoa Andrianjafy)
The 6136 ha Ibity Massif is a spectacular
quartz mountain (whose summit reaches
2050m) located on Madagascars Central
Highlands, 25 km south of Antsirabe. Itsnatural vegetaon includes gallery forest,
sclerophyllous woodland, shrubby grass-
land, and vegetaon specially adapted to
growing in rocky sites.
Three hundred and fiy plant species have
been recorded from Ibity, at least eight of
which occur nowhere else. Most of the
flora is not included in any other protec-
ted area. The site is less important than
others for animals, but our inventorieshave shown the presence of threatened
species of amphibians and reples and a
rare Highland colony of fruit bats. Ibitys
biodiversity is threatened by wildfires and
arsanal gold-mining. Although fires are a
natural part of the ecology of the site,
their high frequency is prevenng the
regeneraon of the sclerophyllous wood-
land. Currently there are ca. 250 gold mi-
ners seeking this precious metal justoutside the south-western limits of the
protected area and there is a risk that they
could invade the reserve. To reduce this
threat we have invested heavily in develo-
ping a posive relaonship with them by
helping them create an associaon and fa-
cilitang their endeavors to legalize their
acvies.
Pointe Larre
(Conservaon Facilitator: Adolphe Lehavana)
This sandy peninsula juts out into the In-
dian Ocean opposite to le Ste Marie, on
Madagascars east coast. The proposed
protected area encompasses a complex
(Conservaon Facilitator: Jeremie Raza-fitsalama)
This 5200 ha of fragmented, low-eleva-
on, humid forest is situated on a range of
smallmountains in north-eastern Mada-
gascar, within the communes of Anjango-
veratra,Antsirabe Nord and Marogaona.
Preliminary biological inventories revealed
a rich floraand fauna that includes several
locally endemic and threatened species.
The forest is also an important water
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mosaic of vegetaon types including lio-
ral forest, low-elevaon humid forest,
swamp and marshes, all of which are ina-
dequately represented in Madagascars
exisng network of of parks and reserves.
The swamp forest is parcularly remarka-
ble, with an aspect that resembles the Flo-rida Everglades. The woody vegetaon of
Pointe Larre has been transformed
over the past two decades because of
anarchic exploitaon of mber, shiing
culvaon and wildfires.
Vohibe Forest
(Conservaon Facilitator: Fortunat Rakotoarivony)
This 3117 ha block of mid- and low-eleva-
on forest is located on the lower slopes
of Madagascars great eastern escarp-
ment, 72 km west of the coastal town of
Vatomandry. It is part of the Ankeniheny-
Zahamena Forest Corridor, thought to be
of key importance in enabling the flora of
eastern Madagascar to adapt to climate
change. Vohibe includes a rare example
of almost prisne low-elevaon forest, the
vegetaon type with the highest biologicaldiversity of any ecosystem in Madagascar,
yet under-represented in the countrys
network of protected areas. To date, 11
species of lemurs (including the largest ex-
tant species, Indri indri), 80 species of
birds, 23 species of reples, and 47 spe-
cies of amphibians have been recorded
here. Our intervenon at this site began
in 2007 and ancipated the invasion of
the area by shiing culvators originangfrom Madagascars growing rural popula-
on.
ACTIVITIES AND ACHIEVEMENTSSituatedat the interface of human society
and natural ecosystems, community-
based conservaon requires the imple-
mentaon of a perplexingly diverse range
of acvies that vary in importance across
time and space. These activities can be
usefully classifed into six strategic axes,
and it is this framework that is used
below to describe our acvies and
achievements during 2012.
As in the two previous years, during 2012
funding was inadequate to implement a
full program at several sites, making itnecessary to priorize our acvies. In
parcular, we focused on supporng the
community management of natural re-
sources, yet even within this crically im-
portant strategic axis, our ability to
provide real alternaves for local stake-
holders to the non-sustainable exploita-
on of natural resources remains
inadequate.
Providing a legal framework for long
term conservaon
The successful long-term community-
based conservaon of a site requires a
compable and naonally recognized
legal framework. Fortuitously, the deci-
sion of MBG-Madagascar to intervene in
the conservaon of a set of priority areas
for plant conservaon coincided with the
Malagasy Governments declaraon, at
the World Parks Congress in Durban in
2003, that the country would triple the
area managed primarily for conservaon.
Furthermore, the Governments iniave
allowed for the establishment of new
types of protected area that could be ma-
naged jointly with local stakeholders to
achieve the dual objecves of conserva-
on and sustainable use. These iniaves
provided MBG with an ideal context in
which to designate and manage new pro-
tected areas.
As required by the Malagasy government,
the process for establishing new protec-
ted areas (PAs) places emphasis on
consultaon with local stakeholders and
their acceptance of the proposal in all of
its details. This process has two stages:
preparaon and acceptance by local sta-
keholders and naonal authories of a
dossier for Temporary Protection, and
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then the subsequent establishment and
acceptance of the dossier for Permanent
Creaon of the PA. The first dossier in-
cludes a descripon of the site, a provisio-
nal delimitaon that shows the various
management zones, a proposal for mana-
gement, informaon concerning land ow-nership and exploitaon rights, and
evidence that the proposal has been dis-
cussed with stakeholders and has their ap-
proval. The dossier for Permanent
Creaon of a PA includes all of the ele-
ments listed above, but requires greater
detail along with a study, validated by the
Naonal Office for the Environment
(ONE), describing the potenal negave
environmental and social impacts of the
establishment and management of a new
PA, along with a plan to avoid, migate
and/or compensate for these impacts. By
2010, ten of the eleven conservaon sites
in which MBG is involved had obtained
Temporary Protecon through inter-minis-
terial decrees. The eleventh site, the
ny Ankafobe Forest, will not be designa-
ted as a protected area but rather is being
managed as a community reserve under
the provisions of a formal agreement bet-
ween the Forest Service and a legally re-
cognized local associaon. This situaon
remained unchanged during 2011, but in
2012, further progress was made for one
site, the Ibity Massif, where ONE validated
the management plan and the plan for en-
vironmental and social safeguard, and is-
sued MBG with a cahier des charges for
the management of the site. This docu-
ment includes a list of condions that
must be fulfilled by the site managers in
their future work. The proposed manage-
ment plan for Ibity Massif, integrang the
condions specified in the cahier des
charges, will be presented to local stake-
holders in 31st January 2013, then on
confirmaon of their approval, the dossier
can be sent to the Malagasy government,
thereby compleng the administrave
process that will result in for designation
of this site as a new PA. In 2012 we were
unable to complete this process for other
sites because inadequate funds were avai-
lable to pay for the services of ONE, which
cost more than $3000 per site.
Community-based management ofnatural resources and provision of
alternaves
While we are convinced that PAs and
other types of nature reserves will be es-
senal for the conservaon of Madagas-
car's biodiversity, we are also aware that
these areas oen disenfranchise Malagasy
people from their natural heritage, reduce
their access to natural goods and services,
and consequently contribute to poverty.Moreover, experience elsewhere in Mada-
gascar has shown that if local stakeholders
do not value their natural ecosystems,
they will be inclined, should the opportu-
nity arise, to degrade and destroy them
for quick profit. Seemingly, then, efforts
to provide long-term protecon of Mada-
gascar's PAs would require the connuing
repression of rural poor, an approach we
do not wish to use.There is, however, an alternave. We seek
to establish and manage reserves in which
the aim is to conserve biodiversity by
maintaining and increasing the value of
natural ecosystems to local people, inclu-
ding efforts to support the sustainable
exploitaon of natural goods and ensure
that the value of goods and services is
fully appreciated by the beneficiaries. This
"use it or lose it" approach to conserva-
on became popular in Madagascar du-
ring the 1990s, but the results of inial
efforts have fallen far farshort of the
hopes of its advocates, an outcome mirro-
ring that elsewhere in the world.
For the reasons indicated above, commu-
nity-based conservaon through sustaina-
ble exploitaon of natural resources is not
an opon at our eleven sites but rather an
imperave, and ways must be found to
make it work. While it would be foolish
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not to take careful note of the all-too-
frequent failure of community-led pro-
jects in Madagascar and elsewhere,
successes can be found, including at some
of our own sites, and we are confident
that the risk of failure can be minimized by
idenfying the condions associated withsuccess and then replicang them. Our
own experience and that of others repor-
ted in the literature (e.g. Newton 2008,
Freudenberger 2011) suggest that suc-
cessful community-led projects aimed at
achieving the sustainable management of
natural resources share the following cha-
racteriscs :
Stakeholders feel ownership of the pro-
ject and have real power to control access
to their natural resources.
Project benefits are shared by a majo-
rity of the stakeholders rather than a res-
tricted subset.
Project goals are designed to provide
significant, tangible benefits for local
stakeholders in both the short and
medium term.
Management plans are simple, flexible,
and realisc and are conceived to provide
alternaves to over-exploited resources
and add value to exploited resources,
while also taking into account the role of
natural resources as an economic safety-
net during mes of environmental or so-
cial perturbaon.
Decision-making is based on the princi-
ples of good governance and informed by
sound informaon rather than assump-
ons, preconcepons, and prejudices.
Community managers understand and
accept the responsibilies associated with
their post and are compensated for their
investment in the project.
Community managers receive close
coaching from outside agencies in the
short term and can access support and
advice in the longer term.
Periodic, objecve evaluaon is done to
assess project success in aaining goals,
with rewards allocated to those responsi-
ble for the success.
Previously at each of the eleven conserva-
on sites our Conservaon Facilitators
have worked with the local community to
adapt and reanimate local, tradional
rules (known as dina) concerning themanagement and use of the areas natural
resources. The dina is implemented and
policed by the community itself through a
local Management Commiee composed
of stakeholders who meet every month to
issue permits, to consider infracons and
to apply sancons. Policing is effected by
a small team of local people who have
been trained by us to patrol the site, note
infracons, and report them to the
Commiee. MBG also works with the
Commiee to provide both alternave
resources to community members who
are subject to raoning, and alternave
methods of generang income for those
who are potenally impoverished due to
loss of livelihoods that were based on the
non-sustainable exploitaon of natural re-
sources.
In 2012 we connued to assist commu-
nity- based management by: compensa-
ng the members of the management
commiee for their me, paying salaries
for those policing the dina, providing
equipment, and supporng the provision
of alternaves to over-exploited natural
resources.
Training was also provided to several
management commiees and teams of
forest police in the principles of good
governance and how these principles can
be applied to their daily work. Details of
the work completed in 2012 at each site
within this theme are given in Table 1.
A major concern for many of the Conser-
vaon Facilitators is that our capacity to
provide alternaves to over-exploited
natural resources is inadequate. In reality
several of the sites constute small
pockets rich in natural goods located in a
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landscape where such resources are rare
and people are to one degree or another
dependent on them for their livelihoods.
In 2012, in total, 62,000 seedlings of fast
growing alien trees were planted as an
alternave for wood unsustainably
harvested from nave forests. However,this achievement falls far short of what is
required: hundreds of thousands of tree
seedlings need to be propagated, planted
and nurtured; and hundreds of new
employment opportunies are required
for those who are destroying the forest
through shiing culvaon, not just the
few jobs we are currently able to offer.
This represents a huge challenge, but it is
not impossible, and one way it can be
achieved is through collaboraon with
development organizaons whose mission
includes the restoraon of producve
capacity to degraded landscapes. One
such relaonship that is just beginning to
yield results is between MBGs projects at
Agnalazaha and Ankarabolava-Agnakatrika
in south-eastern Madagascar and the
development organizaon Hungar Hilfe
Welt, which offers the potenal to reforest
hundreds of hectares of the impoverished
land that surrounds these two protected
areas.
The extent to which we are sasfied with
the applicaon of the dina is summarized
in Table 2. At three sites, exploitaon of
natural resources by the local community
is now minimal or absent and therefore
easy to control (indeed at Ankafobe the
creaon and implementaon of a dina
was not judged to be necessary because
there is no history of the local people ex-
ploing the natural resources within the
site); at three sites exploitaon of one or
more natural goods is significant but sus-
tainable; but at the five remaining sites,
some natural goods are exploited unsus-
tainably. Thus, we are sasfied with the
applicaon of the dina at five of the sites,
but, it should be noted that the successful
implementaon of these local rules does
not by itself indicate that natural goods
are being used sustainably. For example,
at Agnalazaha most mber extracon
from the forest is done legally with a per-
mit issued by the management commiee
and the wood is desned for local use, butin 2012, 396 permits were issued for per-
sonal use, resulng in a level of exploita-
on that is probably not sustainable.
Currently it is not feasible to reduce these
excessive levels of exploitaon because no
alternave sources of mber are yet avai-
lable and, this being the case, restricons
could prevent vulnerable people from
meeng their legimate housing needs.
In contrast to the situaon at Agnalazaha,
much of the mber exploited at Pointe
Larre is sold rather than used by the local
community. This reckless and greedy
exploitaon seems to have flourished
during Madagascars on-going polical
stability. Unfortunately, under present
condions, those who should be responsi-
ble for nurturing respect for the rule of
law and for policing and implemenng
rules and regulaons are themselves im-
plicated in this illegal and unsustainable
exploitaon, and there is lile that we can
do about it. The forests at Pointe Larre
are managed by seven local associaons
(called COBA) that, previous to our inter-
venon at the site, had each obtained a
contract from the Forest Service for the
sustainable exploitaon of mber in
designated parts of the forest. Although in
the past we have endeavored to support
all these COBA in developing and imple-
menng sustainable management of their
mber resources, as required by their
contracts, a review of our impact has
shown that our intervenons were suc-
cessful in only four of the COBA.
Consequently, this project is now under
review and it is likely that in 2013 we will
concentrate our limited resources on the
creang a more modest protected area in
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collaboraon with the more responsible
COBA. Tourism is a very popular approa-
chused by protected area managers to va-
lorize their sites because it is directly
linked to biodiversity and because foreign
tourists are comparavely wealthy and
provide addional revenue beyond whatnormally circulates within the local eco-
nomy.
However, while a few protected areas in
Madagascar aract comparavely large
numbers of tourists and generate a signi-
ficant revenue stream for local people and
for reserve management, many other
sites, despite appropriate investment,
have failed to aain even modest success.
Understandably, most tourist agencies are
risk-averse and are loyal to a few inera-
ries familiar to them that reliably and relia-
bly provide sasfacon to their clients.
Five of our eleven sites have clear poten-
al for tourism :
Analalava, located just 7 km from the
major coastal resort of Foulpointe, boasts
a rainforest experience with habituated
lemurs and a large fruit bat colony
Ankafobe lies immediately adjacent to
a naonal highway and provides a scenic
picnic spot less than 2 hours drive from
Tana
Ibity offers dramac rock landscapes,
cultural importance and proximity to the
island's main north-south road
Oronjia is easily accessible from Diego
Suarez and offers fine marine views and
beauful, un-spoiled beaches
Pointe Larre, a quick speedboat ride
from Madagascars second most impor-
tant tourism desnaon on le Ste Marie,
offers forest, beaches, lemurs and crocodiles.
In 2012 progress was made on developing
the ecotourism potenal at three of these
sites. At Analalava we conceived and im-
plemented a five-month course that suc-
cessfully trained five local people who are
now able to offer their services as char-
ming, aenve and knowledgeable guides.
In 2012, Analalava welcomed 124 tourists
who not only generated income for these
guides but also for an associaon of
women who provide them with meals. At
Ankafobe, we recruited and trained one
local person to act as site guardian and
guide, and since his installaon in Novem-ber he has hosted visits by 17 tourists. At
Oronjia, we collaborated with a consultant
provided by the Dpartement du Finistre
in France to research and publish a tou-
rism plan for the site. This plan is now
being used to solicit funds for implementaon.
R ESEARCH AND ONITORINGThe resources required to implement ac-
vies are always limited so it is important
that they be used in a manner that maxi-
mizes posive impact and the aainment
of our long-term goals. Work plans must
be developed that are based on a tho-
rough understanding of problems and the
strengths and weaknesses of possible so-
luons. Deep understanding can be built
through the daily experiences of a percep-
ve site-based staff, but this needs to be
accompanied by focused research on key
issues and indicators, many of which are
oen poorly-understood. Monitoring can
be considered as a special type of research
in which the implementaon of acvies
and the resulng impacts are tracked
through me to verify whether expected
results are being achieved as effecvely as
possible. More generally, we also encou-
rage researchers from diverse domains to
conduct studies at the conservaon sites.
In addion to improving our own know-
ledge, the presence of researchers can ge-
nerate employment for local people as
assistants of various types, and their pre-
sence further helps to convince local sta-
keholders of the sites importance.
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Moreover, the presence of research at a
site helps to jusfy its conservaon.
Table 3 summarizes the research conduc-
ted at each of MBGs sites during 2012. In
general, the level of research conducted in
2012 increased from the previous year.
Three sites in parcular boasted a highlevel of research acvity: Agnalazaha, Ana-
lalava, and Vohibe, the first and last of
which are not easily accessible, suggesng
that the abundance of research acvies
there reflects the highly collaborave na-
ture of these projects and the willingness
of their staff to supervise postgraduate
students.
Three research endeavors deserve special
menon. First, at three of our sites
(Pointe Larre, Analalava and Vohibe)
MBG botanists are collaborang with mi-
crobiologists from Madagascars Naonal
Center for Ecological Research (CNRE) and
the University of Maryland in a study to
explore the relaonship between flora
and vegetaon structure and the diversity
of soil micro-organisms. In parcular, the
project aims to invesgate the effect of
disturbance to forests (e.g. by selecve
exploitaon of mber or shiing culva-
on) on the soil microbial community.
The fieldwork for this innovave project
has now been completed and the data are
being analyzed. Second, at Analalava, two
restoraon ecologists, Cyprien Miandri-
manana and Simon Dunster,have establi-
shed a series of seven experiments that
aim to inform protocols for forest restora-
on by propagang and planng nave
tree seedlings. They are considering a
range of variables in this approach inclu-
ding, for example, the effect on seedlings
survival and growth of factors such as dis-
tance from the forest edge, shade, size of
planng hole, addion of compost, and
inoculaon of growing media with mycor-
rhizae. These experiments are now being
carefully monitored and the final set of
data will collected in March 2013, 12 months
CONSERVATION UNIT ANNUAL REPORT 2012 11
aer the start of the invesgaon. Also at
Analalava, five students from the Univer-
sity of Toamasina are working with Cy-
prien to develop cost-effecve protocols
for the control of two parcularly proble-
macal invasive alien plant species. In
total, during 2012, we enabled 19 Mala-gasy students to conduct research at our
sites and facilitated their work.
We are also parcularly proud that in
2012 three of our sites (Agnalazaha, Ana-
dabolava-Betsimalaho,and Oronjia) were
selected by the Royal Botanic Gardens,
Kew, as focal areas for seed collecon ac-
vies as part of their Millennium Seed
Bank (MSB) Project. This project aims to
preserve threatened species by placing
samples of their seeds into long term sto-
rage, both within Madagascar and at the
MSB in England. During 2012 our bota-
nists were able to contribute over 50 seed
samples to this important project.
In December 2012, a major new research
iniave was launched at Makirovana-Tsi-
homanaomby with the recruitment and
inial training of two local plant collectors.
During 2013 experienced MBG botanists
will train and coach these young recruits
so that they can complete an ongoing bo-
tanical inventory of this poorly known site.
Finally, a major achievement during the
year was to insgate the scienfic moni-
toring of conservaon impact at several
sites where such tracking was hitherto ab-
sent. At least one indicator of conserva-
on impact is now being monitored all of
the sites where we are promong conser-
vaon, and at three sites an array of indi-
cators are being carefully and consistently
monitored.
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CONSERVATION UNIT ANNUAL REPORT 201212
Table1Acvies20112012:communitybasedmanage
mentofnaturalresourcesandprovisiono
falternaves
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Table 2.Exploitaon of natural resources at the conservaon sites and status of dina applicaon
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Table
3.Acvies20
12:research
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The forest, woodland or thicket ecosys-
tems at all but one of the eleven conserva-
on sites are, at least in part, degraded,
the sole excepon being the AnalavelonaSacred Forest. This impacts the conserva-
on value of the sites and increases the
risk of further ecosystem deterioraon
due to wildfires, catastrophic winds asso-
ciated with cyclones, and invasive species.
In order to address this situaon, ecologi-
cal restoraon has been incorporated into
the program of acvies at each site.
Our restoraon acvies include: a)control of parcularly harmful, alien inva-
sive plants; b) reducon of anthropogenic
pressures, including burning and the un-
sustainable harvesng of trees, which
constrain natural regeneraon and reduce
forest cover and integrity; and c) reforesta-
on of degraded areas using nave spe-
cies with the aim to increase the total
forested area. The nature and scale of
these acons vary from year to year and
between sites according to need and the
resources available. In total, during 2012,
for all sites combined, 28.5 km of firebreak
were maintained and 39,672 seedlings of
122 different species of nave trees and
shrubs were propagated and planted.
The team at the Analalava Forest includes
a restoraon ecologist (Cyprien Miandri-
manana) and during 2012 a major
research project was implemented at this
site, including an array of experiments to
idenfy the most effecve protocols for
propagang and planng seedling of
nave plants. At Analalava, and likewise
at Oronjia, major experiments were also
launched to define the least expensive,
most effecve,and least environmentally
damaging protocols for controlling three
parcularly invasive alien plant species:
the tea tree (Melaleuca quinquenervia)
CONSERVATION UNIT ANNUAL REPORT 201216
and guava (Psidium caleyanum) at Anala-
lava, and the white leadtree (Leuceana-
leuco cephala) at Oronjia. Perhaps the
most important acvity in enabling eco-
system restoraon, however, involves em-
powering the local community in the
sustainable management of their naturalresources by supporng the establish-
ment and applicaon ofdina and provi-
ding alternaves to over-exploited natural
goods, as discussed above.
Our restoraon acvies bring much
sasfacon: there is nothing more inspi-
ring and movang than seeing the reco-
very of a degraded forest. This is
parcularly true in difficult mes when
there is the tendency to lose opmism
and fall into the trap of believing that the
very best one can hope is to maintain the
status quo. Nevertheless, our restoraon
acvies remain modest and inadequate
compared to the need. For example, du-
ring 2012, at Ankaraboalava-Agnakatrika,
five village nurseries propagated 11,432
seedlings of nave trees and planted them
in two forest gaps created by shiing
culvaon. An excellent result one might
think, yet at least one hundred such gaps
exist, all of which require acon. Similar
stories can be told from other sites, and
we connue our search for addional
funds to enable the required up-scaling of
our restoraon work.
WARENESS-RAISING ANDOMMUNICATION
A
The long term conservaon of our sites
will require that local stakeholders unders-
tand several key points: 1) their natural
ecosystems are important (as habitat for
rare species and as sustainable sources of
natural goods and services on which their
livelihoods depend); 2) these ecosystems
can be destroyed and indeed are being
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destroyed (it is a common yet false human
be lief that natural resources are infinitely
available and cannot be exhausted);
3) tools are available to achieve lasng
conservaon and sustainable use; and
4) ulmately responsibility for the wise
use of local resources rests with the localpeople. Our Facilitators, usually working
with the local Management Commiee
and somemes with associaons or other
staff members, employ a wide range of
approaches to promote and share this
paradigm, including :
Financing and facilitang annual biodi-
versity fesvals that provide an enjoyable
and educaonal forum to promote local
pride in and awareness of natural and cul-
tural heritage while sharing informaon
such as reminders of the dina and a res-
tuon of the years acvies and achieve-
ments
Establishing and supporng green
clubs in schools that host environmental
educaon acvies such as nature ram-
bles, tree planng, vegetable growing,
and film shows
Creang, stocking and managing com-
munity libraries rich in environmental in-
formaon
Building and erecng educaonal
panels in public places on themes such as
the dina, the appropriate use of fire as an
agricultural tool, local natural heritage,
and project milestone achievements
Designing, producing and distribung
t-shirts, baseball caps and posters themed
to support specific campaigns (e.g. lemur
conservaon or responsible use of fire);
and
Ensuring that ALL members of our site-
based team can speak authoritavely
about the raonale for the project and its
aims, approaches and acvies, and that
they also set a good example in their eve-
ryday relaonships with the environment.
A prerequisite for successful community-
based conservaon is a trusng relaonship
between the conservaon organizaon
and the local stakeholders. People eve-
rywhere are less suspicious and more
trusng if and when they know what is
going on. Thus, in addion to carrying out
specific, focused environmental aware-
ness-raising acvies, we invest daily
inensuring effecve two-way communica-
on between the site-based team and the
full range of local stakeholders. This com-
municaon takes place by means of
doorstep interest group and village
meengs, and also throughbroadcasts
from local radio staons.
Table 4 summarizes the awareness-raising
and communicaon acvies implemen-
ted at each of our conservaon sites du-
ring 2012. Differences in the importance
and nature of these acvies between
sites reflect available funding as well as
cultural parcularies of the stakeholders,
In general, the quanty of awareness rai-
sing acvies remained stable between
2011 and 2012. Biodiversity fesvals were
held at three sites and each was judged to
be an enormous success in promong
conservaon paradigms to local commu-
nies and increasing awareness of and
support for our iniaves. Also highly suc-
cessful was a program of school nature
camps at the Analalava Forest organized
in collaboraon with the local US Peace
Corps volunteer and animated by our
newly trained guides. The objecve of
these regular forest sleepovers is to re-
connect local school children with theirnatural heritage using a lively mix of ac-
vies that include film shows, games,
songs, quizzes and nature rambles.
POVERTY EDUCTIONIn Madagascar extreme rural poverty re-
sults primarily from a profound, systemic
lack of access to information, services
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Table4.Acvies2012:awareness-raising
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(educaon, health, and communicaons),
markets, venture capital, and natural ca-
pital. Overcoming these deficiencies will
be essenal for the success of MBGs ef-
fort to facilitate conservaon at the eleven
sites where we are engaged. Part of the
work of our site-based teams, each led bya Conservaon Facilitator, is to achieve
conservaon by reducing local poverty
and improving human well-being. Cur-
rently we seek to accomplish this goal by
providing training in improved agricultural
techniques, promong new income-gene-
rang iniaves, and making the materials
available to support the exploitaon of
this knowledge, as well as by aracng
development organizaons to assist with
launching projects around the conserva-
on sites and then facilitang their work
to ensure maximum benefits to the com-
munity.
Table 5 summarizes poverty reducon ac-
vies at each of our sites during 2012.
Although many of the income genera-
ng/food producing iniaves can be jud-
ged successful in the short term at least, in
general, these development projects, in-
dividually and in combinaon, have been
neither sufficiently extensive nor dura-
bleto bring about a significant reducon
in poverty among those living around the
sites. Indeed, a brutally objecve review
of these projects shows that they have, at
best, had a modest, short-term posive
impact on the livelihoods of a limited
number of people, barely compensang
for populaon increase around most of
the sites. For example, while we are de-
lighted with the success of projects at
Ibity, Makirovana and Oronjia that enable
some local people propagate and sell
seedlings of nave plants of horcultural
interest, and also project to train charcoal
producers living adjacent to Oronjia to use
the wood of invasive alien trees to makeanimal models for sale to passing tourists,
these projects transformed the lives of
few people. The producon of 63,000
seedlings of clove plants for distribuon
to local farmers at Pointe Larre is one of
the few agricultural iniaves at our sites
that is likely to touch the lives of a signifi-
cant poron of the local populaon.
By contrast, infrastructure projects have
the potenal to impact the lives of many
people, and in 2012, funds were obtained
to provide the Commune of Ambalabe,
which includes the Vohibe Forest, with six
market pavilions, six piped communal
water sources, and electricity from solar
power for the Mayors office and the clinic.
In addion, in the three communes adja-
cent to the Ankaraboalava-Agnakatrika
Forest, we were able to provide 600 bench
and table sets (each accommodang two
or three students) that were distributed
among 40 schools: over one thousand
children who previously studied squang
on parasite-infested earthen floors can
now learn in comparave comfort.
We are convinced that, in collaboraon
with development organizaons, conser-
vaon projects such as ours have the
potenal to make a significant contribu-
on to development with posive bene-
fits for Madagascar's rural poor. Our
projects are oen located in remote areas
where development organizaons have
historically been reluctant to venture, and
our site-based personnel, who have gai-
ned the trust of the local people, possess
a deep knowledge of local issues and have
made a long-term commitment to their
host communies. These strengths now
need to be more widely appreciated by
those working to nurture development in
Madagascar. These persons and organiza-
ons must also revise the widely held but
unfounded and counter-producve belief
that conservaon organizaons are not
interested in people but only lemurs. All
serious conservaonists understand that
nature reserves will never be secure so
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Table5:Acvies2012:povertyreducon
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long as they are surrounded by impoveri-
shed and resource-starved people. In
2012, we were thus delighted to see the
launch of a collaborave iniave with the
development organizaon Welt Hunger
Hilfe to promote reforestaon and impro-
ved agricultural techniques in the land-scapes adjacent to Agnalazaha and
Ankarabolava-Agnakatrika. Also at Agna-
lazaha, 1300 specially designed, high qua-
lity, woven baskets made by local weavers
were purchased at beer than fair-trade
prices by the Blessing Basket Project and
are now being sold in the USA. However,
perhaps the most impressive collabora-
on was with USAID (though the Ra-
nonala project), which led to the
installaon of 36 pumps and 360 family la-
trines in the commune that includes the
Pointe Larre Peninsula. In 2013 we will
do our best to develop addional collabo-
rave efforts of this kind.
FUNDINGIn 2012, MBGs total, in-country expendi-
tures on site-based conservaon were ap-
proximately $427,955, as summarized in
Table 6, up from the previous year
($379,000), but nevertheless sll much
less than required to ensure the long-term
conservaon of our eleven sites. The fi-
nancial constraints we have faced have
made any expansion of our program un-
realisc.
Table 6.Expenditure on conservaon acvies in
Madagascar in 2012, classified according to type
I MPACTOur Conservaon Facilitators have worked
hard to implement the diverse array of ac-
vies described in this report, but the
quesons remains: are these acon sac-
tually leading to the conservaon of the
eleven sites where we work? To provide
an objecve answer to this queson we
have idenfied a small number of quan-
fiable aributes for each site that accura-
tely and reliably reflect conservaon
success. These are periodically monitored
through the consistent applicaon of ca-
refully defined protocols, and the results
are shown in Table 7. The number of sites
where indicators are being monitored and
the number of indicators we use both in-
creased in 2012, and in parcular the
team at Oronjia began for the first me to
monitor an impressive suite of conserva-
on-related aributes.
CONSERVATION UNIT ANNUAL REPORT 201222
In addion to core funding provided by
the Missouri Botanical Garden, which co-
vers a poron of staff salaries and office
expenses, among others, support was ob-
tained from a diverse group of donors in-
cluding: the Beneficia Foundaon, the Liz
Claiborne and Art Ortenberg Foundaon,the Internaonal Cooperave Biodiversity
Group, the Fondaon pour les Aires Prot-
ges et la Biodiversit de Madagascar
(FAPBM), Fonds Franais pour lEnvironne-
ment Mondial (FFEM), Global Colors, the
Helmsley Charitable Trust, Idea Wild, the
Marisla Foundaon, the Mohamed bin
Zayed Fund for Nature Conservaon, the
Naonal Geographic Society, Programme
de Petes Iniaves du FFEM, RanonAla
(funded by USAID), Seacology, Rio Tinto,
and the Small Grant Program of the Global
Environment Facility. Support was also
provided by two private benefactors.
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Table 7.Indicators of impact 2006-2012
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Table 8. Evaluaon of the extent to which community-based conservaon was being achieved at the
eleven sites in December 2012
The indicators we are using suggest that
the value for biodiversity conservaon of
most sites is stable or increasing. The only
apparently alarmingly result came from
the Ibity Massif, where during the year
2,808 hectares of the Massif burnt. Wild-
fires are a natural part of the Ibitys grass-land and shrub-land ecosystems, and they
are both inevitable and desirable, provi-
ded that they occur infrequently and at
the appropriate mes of year. However,
recent research suggests that the ideal
fire regime for the massif would be one in
which around 500 hectares (i.e.,10%) of
the sites area is burned annually. The bur-
ning of 50% of the reserve is clearly not
acceptable, but given that the wildfires
which impacted the Massif in 2012 were
started by cale rustlers to hide their
tracks, it is difficult to know what more we
can do! Firebreaks would certainly help,
but they are expensive to establish, can
cause erosion, and their presence could
spoil Ibitys wild landscapes. A long term
soluon we are now considering would be
to restore the strips of gallery forest that
once lined each of Ibitys many streams
but have been degraded over the de-
cades. If these protecve gallery forests
could be restored then they would act as
a natural barrier to the spread of wildfires,
although such an effort would clearly take
many years to implement.
Three other sites gave us cause for
concern in 2012 due to non-sustainable
exploitaon of natural resources: Ankara-
boalava-Agnakatrika (where shiing cul-
vaon and mber extracons were judged
to be non-sustainable); Makirovana-Tsiho-
manaomby (unsustainable shiing culva-
on); and Pointe Larre (anarchic
exploitaon of mber for sale). The mana-gement of these sites has proved challen-
ging for several years,and in 2013 they will
be focus of new remedial iniaves (see
below).
Our objecve is not just to achieve conser-
vaon, but to achieve community-based
conservaon, and therefore it is important
to consider our achievements in this
context. A classificaon of the eleven sites
according to trends of biodiversity impor-
tance as well as the extent to which the
local community parcipates in the
conservaon acvies is given in Table 8.
At all sites there is moderate to high level
of community parcipaon in the project.
At the end of the year the dina for Oronjia
was fully validated by the local authories
and therefore in 2013 we expect that the
community at this site will be empowered
for the first me ever in the management
of their natural resources. The dina for
Makirovana-Tsihomanaomby should also
have been validated by the end of 2012
but the final signature was delayed due to
a strike within the courts, although it has
recently come to an end and we therefore
expect this dina to be applicable very
shortly.
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forestideally these would include paid
work to restore their exhausted fields to
forest;
At Ibity, a plan will be developed and
then implemented to reduce the extent of
annual burns; and
At Pointe Larre, our project will beredefined so that it focuses on collabora-
ng with those communies willing and
able to invest in the sustainable use of
their natural resources.
Achieving these objecves will, as in
previous years, be extremely challenging.
The current financial, social and polical
climates within the country are not
conducive for achieving much of what we
hope to accomplish. More than ever be-
fore, we will need to rely on the iniave,
adaptability, passion, competence and
commitment of our remarkable conserva-
on team. Whatever the constraints, we
will move forward as we have in the past,
strengthened by our strong belief that
only way to manage Madagascar's extra-
ordinary natural heritage is honestly and
humbly to seek approaches that achieve
success because of, not in spite of, the
desires and efforts of local stakeholders.
CONSERVATION UNIT ANNUAL REPORT 2012 25
ERSPECTIVES FOR 0132The strengths and weaknesses, opportu-
nies and threats idenfied in this report
lead naturally to our perspecves for
2013. Our three major objecves for thisyear are :
1) to strengthen the community-based
implementaon of the dina at the sites
where its applicaon is currently unsas-
factory;
2) complete the dossier for definive PA
establishment at four sites (Analalava,
Ibity, Oronjia, Pointe Larre) and submit
the dossier to the Malagasy government;
and
3) at the four sites where we believe
conservaon importance is currently de-
clining,seek funds to implement major
remedial acons to reverse this trend.
With respect to the third objecve, we
specifically propose the following acons:
At Ankarabolava-Agnakatrika and Maki-
rovana-Tsihomanaomby, those praccing
shiing culvaon within the forest need
to be helped to access alternave and im-
proved livelihoods that dont destroy the
-
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Photographs by conservaon facilitators
MISSOURI BOTANICAL GARDEN
Madagascar Research and Conservaon ProgramAddress: P.O. Box 3391, Antananarivo 101, MadagascarPhone: (261) 20 22 324 82Facsimile: (261) 20 22 353 44
Chrisan CamaraPermanent Representavee-mail: [email protected]
Jeannie Raharimampionona
Coordinator Conservaon Unite-mail : [email protected]