Prioritising areas for biodiversity conservation to inform the Mahavavy- Kinkony Wetland Complex management plan, Madagascar Principal author: Rado H.

Slides:



Advertisements
Similar presentations
Towards More Sustainable and Market-based Payment for Ecosystem Services A Pilot Project in Lijiang, China Lu Zhi.
Advertisements

Landscape Level Conservation Planning for prioritizing conservation action in Mozambique Bruno Nhancale, PhD Conservation Science workshop, 21 st April.
Step 1: Valley Segment Classification Our first step will be to assign environmental parameters to stream valley segments using a series of GIS tools developed.
Intact Forest Landscapes and Conservation Planning in Canada Prepared by: Ryan Cheng Global Forest Watch Canada.
OVERVIEW PRESENTATION TO PLENARY CBC Madagascar Corridors workshop, Santarem, 6 December 2004.
Lake-scale planning for management, conservation and restoration Objective: Bring together researchers, managers, NGO representatives and other interested.
Development of a Comprehensive Wildlife Conservation Strategy for Georgia Georgia Department of Natural Resources Wildlife Resources Division.
Biodiversity in Vietnam
Simon linke robert. l. pressey robert c. bailey richard h. norris the ecology centre university of queensland australia
Use of Remote Sensing and GIS in Agriculture and Related Disciplines
FNU Seminar 15 November 2006 Land-use option conservation: Habitat requirements for wetland species in Europe Kerstin Jantke Research Unit Sustainability.
Future Research NeedsWorld Heritage and Climate Change World Heritage and Climate Change - Future Research Needs Bastian Bomhard World Heritage Officer.
© James Byrne/TNC The Nature Conservancy envisions a world where forests, grasslands, deserts, rivers and oceans are healthy and vibrant; where their.
THE POTENTIAL FOR CONSERVATION CONTRACTS TO CONTRIBUTE TO BIODIVERSITY CONSERVATION IN MADAGASCAR Joanna Durbin, Aristide Andrianarimisa, Philip Decosse,
Understanding REDD+ Actions United Nations Framework Convention on Climate Change to address greenhouse gas emissions from deforestation and degradation.
Center for Watershed Protection USDA Forest Service, Northeastern Area, State and Private Forestry How to estimate future forest cover in a watershed.
Review of the KBA process in Indo-Burma First iteration of KBAs identified by BirdLife International in collaboration with the Bird Society of Thailand,
11-4 How Should We Protect and Sustain Wetlands?
Measuring Habitat and Biodiversity Outcomes Sara Vickerman and Frank Casey September 26, 2013 Defenders of Wildlife.
An Introduction to the NC Natural Heritage Data Explorer (NHDE) Allison Schwarz Weakley, Conservation Planner NC Natural Heritage Program North Carolina.
Prioritizing Agricultural Lands for Riparian Buffer Placement in the Raritan Basin: A Geographic Information System (GIS) Model Project Partners: North.
Rio de Janeiro Earth Summit Signatories pledged to establish a system of protected areas Reserves should be Comprehensive Representative Adequate Flexible.
Planning and Zoning Reform – Energy and the Environment.
Dr. Florian Siegert, RSS - Remote Sensing Solutions GmbH, München The role of Remote sensing in monitoring land cover and impacts on peatlands.
Center for Watershed Protection USDA Forest Service, Northeastern Area, State and Private Forestry How to estimate future forest cover in a watershed.
Prepared for the 3rd SBB telecon 20 Mar 2012 Michele Walters, BI-01 task coordinator.
Benjamin Blandford, PhD University of Kentucky Kentucky Transportation Center Michael Shouse, PhD University of Southern Illinois.
Presented by James Atherton (Conservation Outcomes Manager) KBA Review and Lessons Learned Workshop Washington DC July 25-28, 2006 Presented by James Atherton.
Presented by James Atherton (Conservation Outcomes Manager, CI Pacific Islands Program) KBA Review and Lessons Learned Workshop Washington DC July 25-28,
Desktop Analysis Used To: Identify areas that meet certain criteria (e.g. contig forest 50 acres+, id gaps as well, or set lower value in urban area) Identify.
Survey Priorities Discussion Group Participants: Wang Hao, Cristiano, Megan, Wiggy, Curtis, Simon, Henni, Kristen, Naamal, Matt, Lisa, Leeanne, Tom L.
Green Infrastructure Network Design Analysis Beaufort County, North Carolina.
The State of the World’s Wetlands Building a knowledge-base on wetland information and resources Taej Mundkur and Jaime Garcia-Moreno Wetlands International.
Characterization, Inventory and Monitoring of trends in indigenous livestock Dr. E. D. Ilatsia D. N. Kamiti 23-Oct-15Animal Breeding and Genomics Group1.
ISSUES ARISING IN KBA DELINEATION Centre for Biodiversity Conservation Conservation International Madagascar 26 th July 2006.
WORLD BANK / WWF ALLIANCE FOR FOREST CONSERVATION AND SUSTAINABLE USE Reporting Progress in Protected Areas - a Tracking Tool Leonardo Lacerda, WWF International.
Role of Spatial Database in Biodiversity Conservation Planning Sham Davande, GIS Expert Arid Communities Technologies, Bhuj 11 September, 2015.
Engaging partners for KBAs Harison Randrianasolo.
Monitoring for Conservation Planning and Management Elizabeth Kennedy Conservation International 5-8 June 2007 Intervention Monitoring Exchange, Wang Lang.
OECD World Forum on Statistics, Knowledge and Policy Measuring and Fostering the Progress of Societies Istanbul, 29 June 2007 BIODIVERSITY.
Belize National Protected Areas Policy and System Plan.
Using EoH tools to identify values and threats to those values (tools 1 and 2)
SUMATRA KBA DELINEATION Species point localities Prioritization works (e.g. Protected areas Important bird areas) Key Biodiversity Areas Habitat maps (e.g.
ENGAGING STAKEHOLDERS AND SELECTING CONSERVATION RESPONSES CBC Madagascar.
Helping Communities Protect Wildlife Habitat Emily Brunkhurst Wildlife Biologist NH Fish and Game Taking Action for Wildlife.
Gap analysis presentation: November 2008 Use the information to identify gaps Northern Madagascar.
Monitoring Programme. What is monitoring? Environmental monitoring is the systematic observation, measurement and calculation of the condition of the.
Biodiversity Health Index Main Streams for Life John MacKinnon UNDP consultant June 2012.
Map of remaining significant woodlands in Southern Ontario. Used to be all woodlands before settlers arrived.
CEPF Strategic Funding Direction 3 Meeting: 28 th June, 2006 Outcomes Monitoring: Status & trends in biodiversity Establishing standard regional monitoring.
Issues arising in KBA delineation 1) How do we delineate KBAs in a vast area of contiguous habitat when the area teems with threatened and irreplaceable.
Short overview of the legal framework of protected sites and status of existing ecological networks in Serbia.
Biomass Biodiversity is greatest in the tropics Biodiversity is generally greatest in the southern hemisphere Seventy per cent of the world's species.
"INTER-AMERICAN BIODIVERSITY INFORMATION NETWORK (IABIN)"
IUCN and Biodiversity Assessment
The use of Article 17 assessments in SE (national biodiversity strategies, measuring progress, target setting etc.) ArtDatabanken.
Watershed Literacy & Engagement
IsMAEEl Chafekar Cambodia Analysis
Systematic conservation plan for cambodia
Student Number: ESS 333 practical Faculty: Arts November 2018
CAMBODIA BCB/ESS Kingdom of Cambodia Student Number:
Title BCB/ESS Kingdom of Cambodia Student Number :
Student Number: BDC332 practical faculty November 2018
Prioritizing Watershed Protection in King County
Student Number: BDC332 practical Faculty: ARTS November 2018
Thailand conservation analysis
HELCOM Baltic Sea Protected Areas
Student Number: BDC332 practical faculty November 2018
Ecological analysis of Thailand
Presentation transcript:

Prioritising areas for biodiversity conservation to inform the Mahavavy- Kinkony Wetland Complex management plan, Madagascar Principal author: Rado H. Andriamasimanana Co-authors: Hedley S. Grantham, Eddy Rasolomanana, Voninavoko Raminoarisoa

2 Supporting organizations

3 Objective Prioritizing potential areas for threatened species in order to design the management plan of the protected area, Mahavavy-Kinkony Wetland Complex (MKWC) Why this study is different from the prioritization already done in Madagascar?

4 Context Madagascar is a globally important biodiversity hotspot In 2003, during the World Parks Congress in Durban: Malagasy Government committed to triple the protected area coverage (from 2 million hectares to 6 million hectares) Existing prioritizations at the national scale in Madagascar (Kremen et al and Razafimpahanana, 2010) for identifying potential sites for protected area

5 Context Result: this map was edited in 2008 and serves as tools for national planification MKWC is one of these priority sites for protected area establishment MKWC

6 Context The prioritization of this study is at site level Why? MKWC is classified as Category V (UICN), people can use sustainably some parts of the natural resources The aim is to inform decision makers where are the importantes places for threatened species, and merit to be protected and where are places that pepople can use sustainably

Methodology: area Study area: o Located in north-west of Madagascar o Total area of about 300,000ha o Mixture of habitats : fresh water lakes, rivers, marshes, mangrove forest, and deciduous forest

6/7/2016 Methodology: Data Sources of Data: o Identification project of Important Bird Areas (ZICOMA, ) o Inventory and Monitoring done by Conservation program of Birdlife in Madagascar ( )

Methodology: Data Data used: o 19 threatened species : 9 birds, 3 primates, 3 fishes, 3 bats and 1 aquatic reptile o Species distributions of these19 species needed for the analysis o For modeling distributions, we used as sources : 1) land cover types from Remote sensing using Landsat ) expert knowledge: species records inside the site were used to guide experts at Asity Madagascar

10 Methodology: Tool Software-based Analysis using as tool: conservation planning software Marxan Following files were created to run Marxan : o Planning Unit File (pu.dat) o Conservation Feature File (spec.dat) o Planning Unit versus Conservation Feature File (puvspr2.dat) o Input Parameter File (input.dat)

Methodology Approach for having management plan used two steps: software-based analysis community consultation process Finality : to delineate three zones those for conservation, those sustainable uses and those for human occupancy. This reseach contibuted mainly to the first step

Methodology: process Conservation goal : keep at least 25% of the species habitat Planning unit: o Using GIS, study area was devided into planning units of 625m ² (corresponding to planning unit of mining permits) o Conservation cost: Planning Unit belonged to the natural habitat such as forest, lakes, rivers and mangroves had lower cost. Planning Unit located in a degraded habitat like degraded forest and wooded savannah land had higher cost All planning units available for prioritization

Methodology: analysis Conservation Feature File created using WWF Gap 1.5 tool o Maximum value of the area of occupation set at 250,000,000m ², minimum value at 100,000,000 m ² with asymptote at 25 for species with occupation area more or equal to maximum value, 25% of its occupation area only will be kept for species with less or equal to the minimum value, 100% per cent of its occupation area will be prioritized. Between these two extremes, the priority will vary progressively from 25 to 100%

Methodology: analysis Boundary length file value set at 1 Default setting of Simulated annealing algorithm with iterations for each run Ran Marxan 100 times For detail of Marxan parameters please refer to: ml or Manual_2008.pdf

Results 7 classes were extracted from Landsat 2005:

6/7/2016 Forest, mangrove and terrestrial wetland are important for the biodiversity o Forests are important for lemurs o Mangrove for water birds o Terrestrial wetlant for fishes, waterbirds and aquatic reptile Results

Site divided into 7354 planning units, costs rank from 10 to 3979 Summed solution of Marxan with the irreplaceability more than 25 % was kept as solution

Results: Gap analysis Majority of the species had more than 25% of their distribution protected, except crowned sifaka (Propithecus coronatus) and Decken's sifaka (P. deckenii) with respectively 9.19% and 22% They didn’t meet the 25% target of conservation Manual adjustment

Results: Manual adjustment Why manual adjustment instead of systematic adjustment? Systematic adjustment will increase considerably the amount of habitat kept for other taxa and may offend local community o Some resources have to be retained for sunstainable uses by local community The goal of manual adjustment was to detect the area where these two species of lemurs occur but had not been captured in the solution

Results: Manual adjustment Part of forest where these two species occur was not captured in the solution Manual incorporation of this part of forest increased the conservation of these species to 91.66% for Crowned Sifaka and 96.56% for Decken’s Sifaka

6/7/

Results : After public consultations

Discussion/lesson learnt Gap analysis is a compulsory to ensure that all target species are enough protected even if the overall percentage of the species habitat kept in the solution was arleady high (63.06%) Difference was very enormous at species level (Crowned Sifaka : 9.19% # 91.66%) even if the difference between global percentages of the natural habitat of all species included in the solution without manual adjustment and with manual adjustment were very little (63.06% # 69.89%)

Discussion/lesson learnt Program was very good for restricted distribution species : o Madagascar grebe (Tachybaptus pelzelnii) o a fish Paratilapia polleni only at Tsiambarabe Lake o Sakalava rail (Amaurornis olivieri) and Paretroplus dambabe occurred Lac Kinkony o Madagascan rousette (Roussetus madagascariensis) at Anjohibe forest.

Discussion/lesson learnt Very high percentage of the conservation values were kept as goal during the systematic planning process for two reasons: o Threatened species only are considered so the solution should ensure others species o After public consultations some areas have to be released for sustainable uses of the local people.

6/7/2016 Discussion/lesson learnt Extent of the prioritized natural habitat should always be considered for the prioritization because it will be divided into different zones (core area, the sustainable utilization area and the controlled human-occupied area)

Thank you for your attention