ANNEX 1: LOGICAL FRAMEWORK MATRIX · Web viewDespite environmentally unfriendly practices, such as slash and burning, cattle overgrazing and felling (by Ecuadorian Word traders),

ANNEX 11.1: LOGICAL FRAMEWORK MATRIX

Objectives Indicator Means of Verification AssumptionsDevelopment GOAL:Globally important biodiversity of the Andean Paramo maintained.

Conservation status of a selected group of biodiverse landscapes (Polylepis scrub, mires, cushion bogs) in Paramo improved over baseline.

Assessment of Polylepis scrub, mires and cushion bogs in a selected series of sites at start and end of project

IMMEDIATE OBJECTIVES (Objective to Goal)Environmental goods and services in a network of critical Paramo sites conserved.

Replication of project objectives and best lessons in other (not covered by this project) Paramo sites at Andean level

At the end of the project, the area without direct human impact has stabilized or is larger as compared to baseline, in all of the project intervention sites. At the end of the project, activities of low negative or positive impact on biodiversity are in execution in human intervened areas in at least two-thirds of the project intervention sites.

At the end of the project, lessons from the project on Paramo management, policy development, capacity building or information management, with help of external stakeholders and financial resources have been adopted in at least one other site per country.

Conservation status maps (land use & biodiversity) of Paramo sites at start and end of project. GEF & UNEP commissioned reviews Progress reports of implementation of management plans at project sites and others.

Local social and economic conditions do not change dramatically. Local political conditions do not change dramatically. Sustained stakeholder interest and organization Financial resources are made available for Paramo conservation on mid and long term

OUTCOMES (Outcome to obj.)

Outcome 1

1. Adequate conservation friendly practices for productive activities, zoning and conservation strategies implemented at nine Paramo sites

Outputs

1.1 Participative Management plans defined and under implementation

1.2 Formal conservation agreements initiated in all countries

1.3 Sustainable management practices in use by local stakeholders

1. A participative management plan agreed by local stakeholders in all project intervention sites, three years after the start of the project.

2. At the end of the project, formal conservation agreements have initiated in at least half of the project intervention sites and in at least one site per country.

3. At the end of the project, at least 20% of all production units (farms) of all project intervention sites are applying novel sustainable management practices.

4. At the end of the project, at least 85% of all production units (farms) that apply novel sustainable management practices, have received a positive contribution (monetary and in-kind income, time savings; increased food security)

Report on implementation of PMP Land use maps (year one, year three and end of project) of each site. Statements of conservation agreements Surveys among local stakeholders directed to their productive activities in year one, year three and end of project. Monitoring of direct and indirect contributions to household income in each project site by means of a participatory early warning systemhousehold surveys..

Sustained support from farmer communities for the execution of management plan. Governments support enabling environment.

Objectives Indicator Means of Verification AssumptionsOutcome 2

2. Key conservation and sustainable use supporting policies are accepted at different governmental levels and by non governmental groups

Outputs2.1 Local policy

instruments agreed and implemented

2.2 Policy implementation initiatives conducted at national level

2.3 International plan of action accepted

2.4 Codes of conduct functioning in two productive sectors

1. At each of the project intervention sites, policy instruments (economic, legislative, regulative) that assure the implementation of management plans have been agreed upon and implemented by local and regional stakeholders, three years after the start of the project.

2. At the end of the project, in each of the four countries, at least two initiatives to implement participatory identified key policies to support conservation and sustainable use of Paramo are being conducted.

3. At the end of the project, an international plan of action for Paramo has been accepted by the Andean Community and by the four countries´ environmental authorities.

4. Codes of conduct for relevant sectors established and functioning in at least two sectors (agriculture plus one more).

Documentation on policy instruments at different levels (government decisions, external evaluation, etc.). Description of initiatives at national level to implement key policies Decision of CAN on plan of action for Paramo Survey of use of reference text with codes of conduct for relevant sectors.

Political commitment of participating countries and of CAN is assured. Sustained intersectoral coordination

Outcome 3

3. Increased technical capacity of Paramo inhabitants, field technicians and local governmental and non-governmental organizations for Paramo conservation

Outputs3.1 Management

capacities for three target groups of key Paramo stakeholders improved

3.2 Exchange of experiences between local stakeholder groups implemented

3.3 Stakeholders apply taught management practices in productive activities

1. A representative set of members of the three main target groups of the training program have increased their capacity to sustainably manage Paramo by at least 50% (scorecard value) after participation in basic training program.

2. During the execution of the project, at least half of the participants in basic capacity programs have visited other Paramo areas and farmer communities to interchange experiences at Andean level.

3. Identified experiences in Paramo management with positive environmental impact have been included or strengthened in daily practice of at least half of the participants in basic capacity programs during the project.

Pre and post evaluation of participants in capacity building programs with a tailor made scorecard. Reports on visits to other areas by participants in training program Target groups survey (start, mid term and end of project) about the application of evaluated experiences.

Target groups of training program continue to be related to Paramo management at the sites.

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Objectives Indicator Means of Verification AssumptionsOutcome 4

4. Increased awareness and information about the importance of the Paramo ecosystem among key decision makers and the rural and urban population related to Paramo

Outputs4.1 Paramo ecosystem

related subjects included in curricula of relevant education centers

4.2 Improved knowledge of Paramo ecology and management in key stakeholders

4.3 Key decision makers adequately informed on Paramo issues

4.4 Paramo Information Mechanism is fully connected to Clearing House Mechanisms in the Andean countries

1. At the end of the project, at least 27 education centers, related to the project intervention sites have included formal and non-formal education projects and activities on the Paramo ecosystem.

2. At the end of the project, a representative set of rural and urban population related to Paramo has increased their knowledge of Paramo ecology and management by at least 50% (scorecard value).

3. Selected groups of key decision makers have been provided with information responding to their identified demands during the project.

4. At the end of the project, the Paramo Information Mechanism is fully connected to Clearing House Mechanisms in the Andean countries.

Pre and post evaluation of participants in environmental education programs (scorecard) Target groups survey (start, mid term and end of project) about use of information. Survey of use of Paramo Information Mechanism at mid term and end of project. Monthly count of hits on website Collaboration protocol between PIM and CHM in each country

Government and NGO’s support for and participation in environmental education projects. Increased awareness results in better decisions taken.

Outcome 5

5. A replication strategy of the project agreed, including its mechanism for implementation

Outputs5.1 Best lessons, sites

and stakeholders identified and implementation timetable for replication finalized

1. An institutional alliance consisting of executing agencies and local stakeholders of the project and external stakeholders, have adopted a commonly designed strategy consisting of (1) lessons identified, (2) a list of potential sites and stakeholders, and (3) an execution timetable for replication.

Minutes of meetings of institutional alliances. Interinstitutional agreements on replication strategy.

External stakeholders are successful in generating financial support for their activities. Agencies and institutions whose actions can potentially affect Paramo biodiversity assimilate lessons from project.

Activities Means Costs (PRELIMINARY) (from Activities to Outcome)

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1.1. Inter-Sectoral Implementation Units, including local stakeholders, develop participatory management plans.1.2. Fill knowledge gaps to support the decision making of land use activities in management plans.1.3. Execute projects for the protection of well-conserved areas and the recuperation of degraded areas 1.4. Execute projects that guarantee and enhance income to the local inhabitants of project sites by sustainable production.

2,30 mln $

1,41 mln $

3,32 mln $

2,15 mln $

Land owners (farmer communities) collaborate with implementation of PMP during project execution.

2.1. Develop and implement a policy, legislative and regulatory framework at different governmental levels, to support the implementation of management plans at all project intervention sites.2.2. Develop and promote policy instruments (economical, legislative, regulative) that assure the implementation of management plans.2.3. Develop and negotiate an Action Plan for the conservation of Paramo at Andean level, within the framework of Decision 523.2.4. Within national institutional platforms, identify key policies to support conservation and sustainable use of Paramo and conduct initiatives for their implementation.2.5. Develop and promote codes of conduct for relevant sectors (agriculture, tourism, mining, public works, etc.).

0,68 mln $

0,59 mln $

0,29 mln $

0,68 mln $

0,24 mln $

Political will at local level Effectiveness of inter-sectoral coordination Countries accept CAN decisions. Effectiveness of inter-sectoral coordination.

3.1. With participation of key actors, develop and execute a training program directed towards the main and complementary target groups of the project, in fundamental aspects of Paramo management, which includes ancestral, traditional and local knowledge, and participatory action research techniques.3.2. Execute a program for identification, compilation and interchange of experiences at local, national and Andean level.

1,254 mln $

0,49 mln $

Participants of main target groups comply with minimum education level Local groups are willing to share traditional knowledge.

4.1. Develop and execute a formal environmental education program directed at students and teachers of the educational institutions of Paramo areas.4.2. Develop and execute a non-formal environmental education program dedicated to local stakeholders in Paramo areas.

4.3. Execute a public awareness campaign about the conservation and sustainable use of Paramo.

4.4. Collect and analyze adequate information to support decision making in Paramo.

4.5. Create and administrate a Paramo Information Mechanism at Andean level

1,08 mln $

0,28 mln $

0,40 mln $

0,87 mln $

0,57 mln $

Collaboration of communication media. Institutions that possess information on Paramo are willing to share. CHM are operational in each country

5.1. Create and operate an institutional alliance consisting of executing agencies, local stakeholders of the project and external stakeholders (governmental and non governmental).5.2. Identify lessons, potential sites, stakeholders and a timetable for execution of replication.5.3. Support the implementation of replication activities in other sites with other stakeholders

1,69 mln $

1,07 mln $

2,37 mln $

Agencies and institutions whose actions can potentially affect Paramo are willing to participate in alliance.

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ANNEX 11.2: INCREMENTAL COST ANALYSIS

1. National Development ObjectivesAll four participating countries (Colombia, Ecuador, Perú and Venezuela) have ratified the CBD. They are also members of the Andean Community (CAN) which has set forth Decision 523 (D523) “Regional Biodiversity Strategy for the Tropical Andean Countries” as an officially binding resolution. D523 draws from the national strategy documents of all Andean Countries thus identifying Paramo as a priority trans-boundary ecosystem requiring regional cooperation on biodiversity conservation and sustainable use initiatives. For further information on respective national agendas on biodiversity please refer to section 1.2. Country Ownership.

2. Scope of análisisThe scope of analysis of the baseline scenario and the GEF alternative covers the timeframe of the full-scale project (6 years). Geographically, the scope of the analysis comprises the boundaries of the Andean Paramo ecosystem covering parts of (N to S) Venezuela’s, Colombia’s, Ecuador’s and Northern Peru’s mountain systems, as described in section 1.3 Biodiversity Significance.

3. BaselineParamo development issues occupy an important place in all four country’s baseline agendas, receiving funding from local, national and even sub-regional budgets as well as NGO’s and international organizations. These activities will continue irrespective of GEF financing. A summary of the initiatives that are complementary to the project’s objectives and activities follows:

3.1 Sustainable management of the Paramo and its areas of influenceA vast number of initiatives including regional action plans, research activities, and poverty alleviation programs, among others, contribute to the improvement of local livelihoods and natural resource management in the Paramo areas of the four participating countries. Venezuela has the largest number of initiatives, while Colombia ranks the highest in terms of actual resource allocation. Each of the project countries invest significant resources in activities related to agricultural development, gender issues, and livelihood enhancement programs for local stakeholders, among other related issues. The total estimated baseline investment in Paramo areas in the four participating countries amounts to US$ 4,949,822. While constituting a notable contribution to the project’s objectives, these plans will, however, generally work in an isolated manner and often have narrow sectoral approaches. Furthermore, even though some address environmental issues, these are primarily geared towards poverty alleviation and food security, thereby lacking the necessary integration and approach to render globally significant benefits.

3.2 Policy development and advocacyThe baseline investment in issues contributing to the project’s objectives in this area is comprised of national initiatives that include water laws, legislation to establish a Paramo biosphere reserve, financial and tax incentive schemes to promote Paramo conservation, promotion of inter-sectoral coordination for biodiversity conservation, national policies and instruments for Paramo biodiversity management, biodiversity related laws for fragile ecosystems, decentralization and local government strengthening programs, environmental law projects for indigenous groups, ecologic/economic zoning studies as well as sub-regional initiatives dealing with agrobiodiversity and bio-commerce, to name but a few. The baseline expenditure estimated for policy and legislation related issues in Paramo, amounts to US$ 2,826,425. Even though this represents a considerable investment, these efforts are not sufficient to overcome weak inter-sectoral policy coordination, disarticulation of local, regional and national planning and the lack of policies and policy instruments as well as the lack of an effective conservation strategy and international

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cooperation for border crossing ecosystems and international watersheds. Thus these issues still constitute legislative barriers impeding proper Paramo management with an integral ecosystem approach.

3.3 Training and capacity buildingThe estimated baseline expenditures for capacity building related activities in the Paramo areas of the four participating countries amount to US$ 2,776,230. These include principally community strengthening programs and issues dealing with productive activities and natural resources management at a local level. They do not however sufficiently address aspects of ecosystem management with a comprehensive view for Paramo resources management, or capacity building to support decision-making at national or institutional level.

3.4 Information and communicationBaseline activities considered under this subject include education programs in broad environmental issues, vegetation, water and wildlife conservation, as well as applied principles to promote improved livelihoods for Paramo inhabitants. A number of research activities related to natural resources in general, biodiversity and water quality also contribute to project objectives. The total estimated expenditures for these baseline activities amount to US$ 3,041,043. Even though they address very specific issues and contribute to natural resource as well as biodiversity conservation, they lack the necessary inputs to adequately promote education of key stakeholders including local, national and regional players in Paramo conservation issues with an integrated ecosystem perspective. Furthermore, there is insufficient adequate information to support decision making in Paramo and the existing information is not properly disseminated to reach key decision makers. In combination with low public awareness about the importance of conserving this marginalized ecosystem, this precludes commensurate action for proper conservation of Paramo resources including biodiversity.

3.5 ReplicationEstimated baseline expenditures amounting to US$ 1,890,000 have been identified under this subject, including isolated efforts in water resources management, environmental research and specific evaluation studies. However an initiative to systematically identify and record lessons learned and best practices and a replication strategy as such to achieve a multiplication effect of the impact of successful Paramo conservation initiatives is lacking.

4. GEF Alternative: The proposed GEF Alternative will complement ongoing baseline activities and will leverage co-financing to achieve project objectives. Project outcomes under the GEF Alternative comprise the following:

4.1 Adequate conservation friendly practices for productive activities, zoning and conservation strategies implemented at nine Paramo sitesThe project will design and implement Participatory Management Plans (PMP) for Paramo conservation and sustainable land use in nine PIS, to include zoning, protection, managing and restoration of key Paramo sites and contamination control mechanisms. Within these plans, strengthened local stakolders’ alliances will implement and oversee sustainable production projects drawing from a catalogue of approved low impact income generating activities such as conservation and natural sustainable resource management projects, projects for improving living conditions and social organization strengthening projects. The project will contribute to protecting natural resources in key areas and restoring ecosystem functions and biodiversity in degraded areas of the Paramo ecosystem, thereby also strengthening the natural base of income generation for Paramo inhabitants. These activities complement the existing baseline activities and are required to achieve global benefits.

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The cost of the increment for Component 1 amounts to US$ 7,928,828US$ 7,954,385 of which US$ 3,334,233 is GEF and US$ 4,594,594 is co-financingout of which the GEF contribution amounts to US$ 3,334,233 and a co-financing of US$ 4,620,152.

4.2 Key conservation and sustainable use supporting policies are accepted at different governmental levels and by non governmental groupsThe project will help to identify and promote formal and informal policy options, alternatives and instruments at local, regional, national and ecoregional level, to support an ecoregional policy strategy for Paramo conservation and sustainable use. Therefore the project will support local stakeholders' alliances and environmental authorities in all four countries to identify, develop and implement an appropriate policy, legislative and regulatory framework at different governmental levels (local, subnational, national). In support of inter-sectoral coordination in the political framework, codes of conduct for sectors such as agriculture, mining, forestry, tourism and infrastructure will be developed. The project will support a Paramo expert within the environmental authority at national level and together with the Secretary General of the Andean Community (CAN) it will develop and implement a Plan of Action for the conservation of Paramo at Andean level. These activities are necessary to create a supporting policy environment for adequate Paramo management. They are complementary to the ongoing baseline and required to achieve global benefits.

The cost of the increment for Component 2 amounts to US$ 2,177,879 of which US$ 1,542,950 is GEF and US$ 634,930 is co-financingUS$ 2,178,241, of which US$ 1,542,950 will be financed by a GEF contribution and US$ 635,291 by co-financing.

4.3 Increased technical capacity of Paramo inhabitants, field technicians and local governmental and non-governmental organizations for Paramo conservationFollowing a previous requirement assessment, the project will implement an Andean regional training program consisting of a series of short courses for three target stakeholder groups to improve technical capacities in biodiversity conservation and sustainable use of the Paramo among farmers, field practitioners and local decision makers. The project will also execute an experience exchange plan between stakeholders of different areas to strengthen the farmer-to-farmer approach. The project will furthermore identify and compile experiences in Paramo management, including the analysis, application and publication of ancestral and traditional knowledge, as well as the identification and diffusion of demonstration experiences in the field. These initiatives will complement ongoing capacity building baseline activities and are necessary to achieve globally significant biodiversity conservation goals.

The cost of the increment for Component 3 amounts to US$ 2,014,247 of which US$ 1,159,751 is GEF and US$ 854,496 is co-financingUS$ 2,014,733 to be financed by a GEF contribution of US$ 1,159,751 and co-financing of US$ 854,982.

4.4 Increased awareness and information about the importance of the Paramo ecosystem among key decision makers and the rural and urban population related to ParamoThe project will inform key decision makers and the general public about the biodiversity and economic value of the Paramo using three complementary education strategies tailored to their respective target groups. Thereby it will assure that Paramo ecosystem related subjects are included in curricula of relevant education centers, key stakeholders improve their knowledge of Paramo ecology and management and key decision makers are adequately informed on Paramo issues. These initiatives will be further supported by the implementation of a Paramo Information Mechanism, which will be connected to Clearing House Mechanisms in the Andean countries. These activities are complementary to the existing baseline initiatives and all necessary for the conservation of globally significant biodiversity.

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The total cost of the increment for Component 4 amounts to US$ 3,715,241 of which US$ 1,545,048 is GEF and US$ 2,170,193 is co-financingUS$ 3,716,476 financed by a GEF contribution of US$ 1,545,048 and co-financing in the amount of US$ 2,171,428.

4.5 A replication strategy of the project agreed, including its mechanism for implementationThe project will develop and implement a replication strategy to multiply the impact of its most effective interventions and lessons. Paramo working groups will be strengthened and new ones created, rendering a replication platform to support this objective. Thus best lessons in Paramo management and biodiversity conservation will be exported to other Paramo sites. These activities are complementary to the existing baseline initiatives and required to achieve benefits of global significance.

The total cost of the increment for Component 5 is US$ 2,859,109 of which US$ 609,868 is GEF and US$ 2,249,241 is co-financingUS$ 2,860,389 of which there is a GEF contribution in the amount of US$ 609,868 and co-financing in the amount of US$ 2,250,521.

5. Incremental Costs of the AlternativeThe total estimated value of the baseline amounts to US$ 15,483,520. The sum of all contributions to the GEF alternative (baseline + GEF + co-financing) totals US$ 34,178,823. The difference between the alternative and the baseline amounts to US$ 18,695,304, which represents the total incremental cost of assuring globally significant environmental benefits. This will be funded by a GEF contribution of US$ 8,191,850 and by non-GEF sources in the form of co-financing in the amount of US$ 10,503,454.The total estimated value of the baseline amounts to US$ 15,483,520. The sum of all contributions to the GEF alternative (baseline + GEF + co-financing) totals US$ 34,207,743. The difference between the alternative and the baseline amounts to US$ 18,724,224, which represents the total incremental cost of assuring globally significant environmental benefits. This will be funded by a GEF contribution of US$ 8,191,850 and by non-GEF sources in the form of co-financing in the amount of US$ 10,532,374.

Incremental Cost MatrixOutcome Cost Category US$ million Domestic Benefit Global Benefit1. Adequate conservation friendly practices for productive activities, zoning and conservation strategies implemented at nine Paramo sites

Baseline 4,949,822

Present scenario of individual projects with local focus contributes to improve livelihoods of stakeholders, yet is not sufficient to avoid encroachment in pristine Paramo, including protected areas

Present land use scenario and economic activities of local stakeholders still compromises globally significant biodiversity in Paramo

Alternative 12,878,650

Improved Paramo management integrates socio economic activities with natural resource conservation, rendering more sustainable livelihoods whilst protecting natural resources

Improved Paramo management allows for sustainable conservation of globally significant Biodiversity

IncrementOf which:

7,928,828

8

Non GEF For details refer to co-financing table

4,594,594

GEF 3,334,233


Baseline 2,826,425

Segregated sectoral policy approach resolves individual development aspects but is inadequate for an integrated conservation of mountain ecosystems

Present policy framework does not constitute an adequate scenario for the conservation of globally significant biodiversity


Integrated, cross-sectoral policy and regulatory framework at local, regional, national and ecoregional level supports the implementation of PMP, considering social and cultural aspects of the Paramo inhabitants

Integral ecosystem approach for conservation policy development allows for improved conservation of globally significant biodiversity of Paramo

IncrementOf which:

2,177,879

Non GEFFor details refer to co-financing table

634,930

GEF 1,542,950

3. Increased technical capacity of Paramo inhabitants, field technicians and local governmental and non-governmental organizations for Paramo conservation

Baseline 2,776,230

Limited baseline programs to foster expertise and capacity at the individual, community and institutional level to conserve and manage Paramo contribute to sustain local livelihoods

Limited baseline programs to foster expertise and capacity at the individual, community and institutional level to conserve and manage Paramo are insufficient to render environmental benefits


Strengthened capacities in Paramo management contribute to improve natural resource conservation as a basis for more sustainable local livelihoods

Strengthened capacities in Paramo management contribute to the preservation of globally significant Paramo biodiversity

IncrementOf which:

2,014,247


854,496

9

GEF 1,159,751

4. Increased awareness and information about the importance of the Paramo ecosystem among key decision makers and the rural and urban population related to Paramo

Baseline 3,041,043

Baseline provides limited education and information programs addressing Paramo ecosystem conservation

Present baseline scenario in terms of education and information programs provides only limited global benefits.


Environmental education and awareness raising programs, supported by a Paramo Information System, fosters better stewardship of the ecosystem leading to improved livelihoods

Environmental education and awareness raising programs, supported by a Paramo Information System, contribute to globally significant biodiversity conservation

IncrementOf which:

3,715,241


2,170,193

GEF 1,545,048


Baseline 1,890,000

The current baseline in terms of information exchange mostly from studies and research projects provides limited national benefits

The present baseline in terms of replication of best practices in critical Paramo sites does not provide significant global benefits.


An adequate replication strategy multiplies the national benefits arising from the improvement of the natural resource base to other areas.

Conservation of globally significant biodiversity is systematically extended to Paramo areas beyond the PIS

IncrementOf which:

2,859,109


2,249,241

GEF 609,868

TOTAL Baseline 15,483,520


IncrementOf which

18,695,304

Non GEF 10,503,454

10

GEF 8,191,850

Outcome Cost Category US$ million Domestic Benefit Global Benefit1. Adequate conservation friendly practices for productive activities, zoning and conservation strategies implemented at nine Paramo sites

Baseline 4,949,822

Present scenario of individual projects with local focus contributes to improve livelihoods of stakeholders, yet is not sufficient to avoid encroachment in pristine Paramo, including protected areas

Present land use scenario and economic activities of local stakeholders still compromises globally significant biodiversity in Paramo


Improved Paramo management integrates socio economic activities with natural resource conservation, rendering more sustainable livelihoods whilst protecting natural resources

Improved Paramo management allows for sustainable conservation of globally significant Biodiversity

IncrementOf which:

7,954,385

Non GEF For details refer to co-financing table

4,620,152

GEF 3,334,233


Baseline 2,826,425

Segregated sectoral policy approach resolves individual development aspects but is inadequate for an integrated conservation of mountain ecosystems

Present policy framework does not constitute an adequate scenario for the conservation of globally significant biodiversity


Integrated, cross-sectoral policy and regulatory framework at local, regional, national and ecoregional level supports the implementation of PMP, considering social and cultural aspects of the Paramo inhabitants

Integral ecosystem approach for conservation policy development allows for improved conservation of globally significant biodiversity of Paramo

IncrementOf which:

2,178,241


6,35,291

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GEF 1,542,9503. Increased technical capacity of Paramo inhabitants, field technicians and local governmental and non-governmental organizations for Paramo conservation

Baseline 2,776,230

Limited baseline programs to foster expertise and capacity at the individual, community and institutional level to conserve and manage Paramo contribute to sustain local livelihoods

Limited baseline programs to foster expertise and capacity at the individual, community and institutional level to conserve and manage Paramo are insufficient to render environmental benefits


Strengthened capacities in Paramo management contribute to improve natural resource conservation as a basis for more sustainable local livelihoods

Strengthened capacities in Paramo management contribute to the preservation of globally significant Paramo biodiversity

IncrementOf which:

2,014,733


854,982

GEF 1,159,7514. Increased awareness and information about the importance of the Paramo ecosystem among key decision makers and the rural and urban population related to Paramo

Baseline 3,041,043

Baseline provides limited education and information programs addressing Paramo ecosystem conservation

Present baseline scenario in terms of education and information programs provides only limited global benefits.


Environmental education and awareness raising programs, supported by a Paramo Information System, fosters better stewardship of the ecosystem leading to improved livelihoods

Environmental education and awareness raising programs, supported by a Paramo Information System, contribute to globally significant biodiversity conservation

IncrementOf which:

3,716,476


2,171,428GEF 1,545,048

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Baseline 1,890,000

The current baseline in terms of information exchange mostly from studies and research projects provides limited national benefits

The present baseline in terms of replication of best practices in critical Paramo sites does not provide significant global benefits.


An adequate replication strategy multiplies the national benefits arising from the improvement of the natural resource base to other areas.

Conservation of globally significant biodiversity is systematically extended to Paramo areas beyond the PIS

IncrementOf which:

2,860,389


2,250,521

GEF 609,868

TOTAL Baseline 15,483,520

Alternative 34,207,743IncrementOf which 18,724,224

Non GEF 10,532,774

GEF 8,191,850

Co-financing detail by Component and Contributing Institution (US$ 1000)

Components1 2 3 4 5

Adefor 300,000 Altropico 14,000 Altropico 12,000 Altropico 18,000 Altropico 4,000Altropico 24,000 EcoCiencia 65,000 CAMAREN 150,000 CIP 420,000 CESA 100,000Aspaderuc 9,000 CGIAB 100,000 Cedepas 41,000 GTZ 50,000 Cotopaxi 30,000Cedepas 50,000 TNC 300,000 Cepeser 12,000 TNC 200,000 Corpei 60,000Cepdif 160,000 WWF 82,000 EcoCiencia 50,000 U. A’dam 1,124,500 Eco-Ciencia 309,000CIP 786,255 EcoPar 350,000 WWF 105,000 FAO 24,390CI 400,000 GTZ 100,000 FAN 500,000Corantioquia 298,380 Probona 40,000 FONAG 135,000Corpoboyacá 63,939 GTPL 5,000Corpochivor 76,726 GTZ 100,000CVC 34,101 Probona 25,000EcoCiencia 65,000 TNC 500,000Gob Cajamarca 20,800 ULA-CINVIV 50,000Grupo Randi Randi 125,000

U. Amster-dam 6,500

GTPL12,000

Vision Mundial 18,454

GTZ 150,000 WWF 120,000ICGH 133,200MARN 14,309Moore Foundation 0Probona 20,000TNC 505,900UICN 50,000ULA-CINVIV 180,000U. A’rdam 156,000U. Wisconsin 225,000WWF

200,000Total 4,059,610 Total 561,000 Total 755,000 Total 1,917,500 Total 1,987,344Operative/administrative

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Altropico 38,494 5,320 7,159 18,182 18,845Condesan 81,363 11,244 15,132 38,431 39,831EcoCiencia 218,718 30,225 40,677 103,309 107,071GTPL 5,249 725 976 2,479 2,570ICAE 91,862 12,694 17,084 43,390 44,970TMI 39,369 5,440 7,322 18,596 19,273UICN 20,997 2,902 3,905 9,918 10,279U. Amsterdam 17,060 2,358 3,173 8,058 8,352U. Wisconsin 21,872 3,022 4,068 10,331 10,707Sub-Total 513,113 70,907 95,428 242,362 251,190Total 4,594,595 634,930 854,496 2,170,193 2,249,241

Components1 2 3 4 5

Adefor 300.0 Altropico 14.0 Altropico 12.0 Altropico 18.0 Altropico 4.0Altropico 24.0 EcoCiencia 65.0 CAMAREN 150.0 CIP 420.0 CESA 100.0Aspaderuc 9.0 CGIAB 100.0 Cedepas 41.0 GTZ 50.0 Cotopaxi 30.0Cedepas 50.0 TNC 300.0 Cepeser 12.0 TNC 200.0 Corpei 60.0Cepdif 160.0 WWF 82.0 EcoCiencia 50.0 U.

A’dam1124.5 Eco-

Ciencia309.0

CIP 786.3 EcoPar 350.0 WWF 105.0 FAO 24.4CI 400.0 GTZ 100.0 FAN 500.0Corantioquia 298.4 Probona 40.0 FONAG 135.0Corpoboyacá 63.9 GTPL 5.0Corpochivor 76.7 GTZ 100.0CVC 34.1 Probona 25.0EcoCiencia 65.0 TNC 500.0Gob Cajamarca

20.8 ULA-CINVIV

50.0

Grupo Randi Randi

125.0 U. Amster-dam

6.5

GTPL 32.3 Vision Mundial

18.5

GTZ 150.0 WWF 120.0ICGH 133.2MARN 14.3Moore Foundation

0

Probona 20.0TNC 505.9UICN 50.0ULA-CINVIV

180.0

U. A’rdam 156.0U. Wisconsin 225.0WWF 200.0

Sub-Total 4,079.9 561.0 755.0 1917.5 1987.3Operative/administrativeAltropico 38.6 5.3 7.1 18.1 18.8Condesan 81.6 11.2 15.1 38.3 39.7EcoCiencia 219.3 30.2 40.6 103.1 106.8GTPL 9.1 1.2 1.7 4.3 4.4ICAE 92.1 12.7 17.0 43.3 44.9TMI 39.5 5.4 7.3 18.6 19.2UICN 21.1 2.9 3.9 9.9 10.3U. Amsterdam 17.1 2.4 3.2 8.0 8.3U. Wisconsin 21.9 3.0 4.1 10.3 10.7Sub-Total 540.3 74.3 100.0 253.9 263.2

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Total4620.2

635.3 855.0

2171.4

2250.5

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ANNEX 11.3: ENDORSEMENTS

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18

19

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ANNEX 11.4: SITE SELECTION, DESCRIPTION AND ACTION PLAN DEVELOPMENT

Site selection process

This project concentrates its activities in a series of critical but representative Paramo sites, in four countries and includes two trans-boundary sites. These Project Intervention Sites (PIS) were selected during the PDF-B phase in a process with international, national and local stakeholders, including the focal points.

The selection process was carried out in by local (farmer) organizations and NGOs as well as with national and regional institutions, coordinated by the National Executing Agency. First, at national level a short list of critical Paramo areas was selected by the national executing agency in coordination with the GEF focal point and with the other country members of the coordination committee of the PDF-B to assure an international adjustment among sites. The project developed a short list of approximately 20 sites that were visited and local organizations contacted. Together with international, national and local stakeholders, a final selection was undertaken in order to maintain a maximum of ten sites. To assure the selection of an illustrative set of sites that represent the biological and cultural diversity and the diversity in conservation status of the Paramos in the Andes and for assuring the opportunity of replication of the results to other Paramo areas, the following criteria were used and weighted:

Biological diversity (richness, uniqueness) General geographical and biological importance Conservation status Socioeconomic y cultural diversity Extension of Paramo area within site Cultural significance Land tenure situation Threats on biodiversity and ecosystem integrity Source of important water resources (drinking water, irrigation, major watersheds) Relationship with protected areas

To assure an effective implementation of the project, the following additional criteria were applied

Availability of information Accessibility Organizational basis for project implementation Institutional basis for project implementation Presence of strategic projects for collaboration General feasibility (political situation, social instability, safety)

The selection process resulted in nine PIS, two of which were deliberately selected in trans-boundary areas within the designated Frontier Integration Zones (Zonas de Integración Fronteriza, ZIF): Loja-Piura (Peru-Ecuador) and Chiles (Ecuador-Colombia)1. Other sites are: Tuñame and Gavidia (Venezuela), Rabanal and Belmira (Colombia), Zuleta-Mojanda and LLangahua (Ecuador) and Cajamarca (Perú). A pristine area in Colombia (El Duende) will be included as a reference site for research and comparison.

1 No trans-boundary site between Venezuela and Colombia was selected, due to the difficult public order situation here.

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Normally, the sites included or limited to a protected area of different category (national park, ecological reserve, forest reserve, indigenous reserve, etc.)

All the PIS together contain most major ecological formations, cultural diversity and threats to Paramo integrity. A second immediate objective of the project is the replication of the lessons from these sites to other sites (outscaling) and levels (upscaling). Herewith, the replication approach is transversally and vertically included in the project. Outscaling and upscaling will be governed by formal and informal replication mechanisms. First, stakeholders from other Paramo sites (farmers, local NGOs) and from other levels (provincial governments, national NGOs) will be directly involved with the training and environmental education program at the PIS to allow for major participation and interchange of experiences. With these stakeholders, an informal relationship will be established, to support them to implement lessons from this project at their sites and levels. Formal replication mechanisms exist of collaboration agreements with other projects, other sectors and, especially, national and international governmental agencies to support the inclusion of lessons at the PIS in international and national multi sectoral policies. Finally, the Paramo Information Mechanism (PIM) that the project will develop allows for broad involvement of different stakeholders and informal exchange of best lessons.

Stakeholder participation and action plan development.

Upon site selection, local stekeholders were invited to work in a local alliance to elaborate a Plan of Action for on-site activities in a participatory way. First, an NGO and/or a local governmental agency with local activities in environmental themes was invited to coordinate the process (site coordinators). One or two farmer communities that possess larger amounts of Paramo within the areas (typically between 100 and 1000 has; including farming area and relatively conserved area) were selected and invited to act as main beneficiaries of the on-site process. Finally other NGOs and GOs at local and regional level and (in some cases) production groups or private companies were included in the alliance to support the Plan of Action development.

During the site intervention process in PDF-B, a fully participatory approach was followed, through which an Action Plan was developed based on the present knowledge and necessities of local farmer communities, NGOs, local governments and other stakeholders. Herewith, the local institutional basis for Paramo conservation was reaffirmed.

This local process first provided a joint characterization of stakeholders and the formation of strategic alliances. Together with them, a common vision was developed. This common vision responded to questions such as: What is our goal? What do we want to do? How will we do this? and, What is our general philosophy? After this, a general description of the area was made by inhabitants supported by the site coordination and NEA. This description serves as baseline assessment at site level. The information collected during this characterization was:

Geographical information on the site and/or community (name, formal status, geographic position, area)

Population information (history, ethnics, important facts and dates, # population, distribution of population, work, income, housing, schooling, roads)

Paramo Resources (flora, fauna, crops, pastures, water, soils, climate surface area, conflicts) General land use and land tenure (present activities, potential activities, land tenure, access rights,

problems, conflicts, possible solutions) Use of water (type -consumption, irrigation, electricity-, participants, organization, distribution,

rights/conflicts) Crops and Livestock (type, intensity, trends, profit) Use of biodiversity ((type, intensity, trends, profit) Other uses (forestry, mining, tourism)

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Social organization (internal organization, political organization) External organizations and projects present in area (including investments)

After this, an Action Plan was developed in a series of meetings with all stakeholders. The Action Plan contains:

Main problems, and their associated threats and opportunities General objectives of the action plan Project goals (outcomes or specific objectives) Strategies to obtain goals Activities pertaining to strategies Responsible organization(s) Estimated time of execution Estimated budget

Short Site description:

Tuñame (Venezuela)

The Paramo of Pajarito-Arenales (2526 ha) is located in Sierra de Trujillo, in the Parish of Tuñame of the Municipality of Urdaneta (State Trujillo). The area borders the “Teta of Niquitao” and “Guirigay” National Monuments and “Sierra de la Culata” National Park. The Paramo occupies the higher part of the watershed of Quebrada de Tuñame. The elevations are between 2900 and 3820 m. It is a relatively dry area (approx. 760 mm). Water drains partly through Pueblo Llano and the Boconó River towards the Orinoco Plains and through the Tuñame and the Motatán River towards the Lake Maracaibo watershed. Most of the soils in the area are inceptisols with an organic horizon with depths between 20 and 60 cm. There are diverse vegetation formations, including some of the most characteristic of the Andean Paramo in Venezuela (3000-4000 m) such as the open rosette vegetation, rosettes and shrubs and tall shrubs in the lower areas. The total number of species of vascular plants identified in the area so far is 124, which represents 5% of the flora of the Paramos of Venezuela. In the area there are numerous wetland areas, strategic environments for the storage and regulation of hydrologic dynamics, with characteristic plant diversity and important as forage for livestock in most of these areas. The agriculture in the area presents different grades of intensity and goes from an intensive system with irrigation to a system with 3 year-old fallow periods or more. The area can be divided into three areas according to their height and the accessibility to water sources: the low area (approximately 2900-3300 m) with irrigation and intensive agriculture with 2-3 harvest per year; the middle area (3150-3300 m) with little irrigation and a single crop per year, and the high areas (3300-3600 m) where estates are larger and the agriculture is practiced with fallow periods. The main crop is potato, rotated with carrot in irrigated places. The cultivation of garlic was introduced about 5 years ago by external producers, but nowadays it is not sown in large extensions due to fungal problems. Cattle raising seems to have been a very important activity in the area until recent times. Due to the change in land use in the high areas and the drainage of swamps, the number of animals seems to have diminished recently. Cop marketing presents a problem for small producers since middlepersons do not arrive to their property and they have to take it to urban centers (e.g. Valera) paying the freight.

The community in the area has a low population density and is dispersed. The total population is 975 inhabitants, 53% are 20 or younger, only 5% are senior citizens. Fifty seven percent of the population has basic education; the index of literacy is 81%. Forty percent is devoted to the main economic activity, i.e. agriculture. In the area there are 209 housings and only 48% of these are in good physical condition. The main road for the population of Tuñame is the Trasandina Highway.

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Gavidia (Venezuela)

The Paramo of Gavidia (6030 ha) is located in the Sierra Nevada de Mérida, in the Municipality of Rangel of the State of Mérida. The area lies within the Sierra Nevada National Park and has been classified as “area of autochthonous population use.” The community of Gavidia is a rural establishment in which three main sectors are located: Gavidia, Micarache and Las Piñuelas. It is made up of two large glacier valleys and several lateral hanging valleys between 3200 m and 4300 m. The mean annual rainfall is moderate (approx. 1320 mm). The water courses originate in numerous marshy and swampy areas. In the high areas there are more than 12 lakes that cover a total surface of 57 ha. The area drains through the Quebrada de Gavidia towards the Chamá River, part of the Maracaibo lake watershed. The soils studied are inceptisols (Ustic Humiptropet) with an organic horizon that reaches 50 cm of depth. The Paramo of Gavidia presents a great diversity of vegetation formations, including some of the most characteristic of the Andean Paramo in Venezuela (3000-4000 m; rosettes-tussocks, rosettes-shrubs and tall shrubs). The total number of vascular plants identified so far is about 210 species, which represent 10% of the flora of the Paramos of Venezuela. As for fauna, local people recognize 11 species of mammals, several of them in a vulnerable state or in danger, such as cougar and limpet (Agouti taczanowskii).

The agricultural system of the area is a system of long fallow periods for the cultivation of commercial potato, closely tied to a system of extensive cattle raising. The agricultural area covers 18% of the total surface (6030 ha). The parcels after potato cultivation are also used for shepherding and for firewood extraction. Recently, the system has been suffering a series of transformation tendencies towards intensification, with a reduction or elimination of fallow times, the installation of an n irrigation system that serves the lower areas of the valley of Piñuelas and the introduction of crops such as carrots and garlic. In the extensive cattle raising system in the area, most of the animals are left in the Paramos out of the cultivation area and the breeding cows are brought down to the housing area for milking. The bovine load in the agricultural belt is approximately 0.13 heads for hectare. The system with long fallow periods allows the maintenance of a high space diversity at a landscape scale, but a reduction of the times of fallow and an expansion of the agricultural frontier could have negative effects on the maintenance of the diversity of the vegetation of the Paramos.

The community in study is characterized by a low population density. The total population is 360 inhabitants most of them of school age (40% < 14 years). Fifty five percent of the population has primary education and the index of literacy is 84%. In the study area, there are 69 housings, 70% in regular to bad condition. The index of accumulation is high (63%). The main access road to the town of Gavidia is an asphalted road asphalted in good condition that connects to the Trasandina highway.

Rabanal (Colombia)

The Rabanal Massif has an approximate area of 17.567 ha and is located in areas surrounding the cundiboyacense highlands in the municipalities of Guachetá, Lenguazaque and Villa Pinzón in the department of Cundinamarca, and Ventaquemada, Samacá and Ráquira in the department of Boyacá. The waters generated are part of the basins of the Magdalena and Orinoco rivers through the Garagoa river, which provides water to La Esmeralda reservoir of the Chivor Hydroelectric Power station (one of the main producers of local electric power), and the basins that feed the Fúquene lake. This Paramo also supplies water to the Teatinos reservoir that provides water to the aqueduct of Tunja (a city of 130.000 inhabitants) and 50.000 people in other municipalities. Rabanal produces water for the Gachaneca I and II reservoirs, which irrigate more than 1'000.000 ha of this region, as well as for 92 local aqueducts. In the Paramo of Rabanal, natural high Andean ecosystems still persist: frailejonales (Espeletia Paramo), peat

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wetlands and high grasslands. The compositional changes can be evidenced by the presence of numerous fragments of secondary formations, with the presence of islands or fragments of more mature formations. Most of their current biodiversity (Paramo and subParamo vegetation), lingers in a few areas surrounded by grasses, with a landscape made up of vegetation formations with a prevalence of secondary dynamics, with multiple patches of different ages and different transformation types (burning, slash, cultivation, grasses, shepherding, among others). Forty seven wetlands have been identified in the area of influence (ca. 1.400 ha) including peat-bogs, swamps and lakes, and reservoirs. There is also a significant quantity of desiccated wetlands (7% of the total). They were dried up mostly for agricultural and intensive potato cultivation. The present forests show a prevalence of secondary formations (stubbles) with encenillales (Weinmaniatum), gacales (Clusietum) and oak groves (Quercetum). The fauna is scarce apparently due to intense and frequent hunting in the whole region, although there are evidences of curíes (Cavia porcellus), possibly armadillos (Dasypus novemcintus), Guaches (Nassuella olivacea) or Faras (Didelphus albiventris), rabbits (Silvilagus brasiliensis), squirrels (Sciurus granatensis), some mice, shrews and hawks (Falconiformes) and eagles (Geranoaetus melanoleucus meridensis) as the most remarkable fauna.

The population of the region of Paramo de Rabanal is mainly rural, and inhabits primarily lower altitude areas but possesses also Paramo lands, dedicating these estates to agriculture and the almost exclusive cultivation of potato, rotating this crop with grasses. In the region, made up by five municipalities, there are 61.397 people and the population inhabiting the veredas that are directly inside the area of environmental management is 10.304 people, of which less than 500 live directly in the Paramo. In the massif, there are activities related to coal mining, mainly extraction and coking, activities that link this area to an increasingly growing population nucleus. The main problem identified by the inhabitants of the region is the water-related conflicts, mainly in the northern and western sub-humid slopes of the massif. As a result of the conflicting conditions of water management that comes from the massif, an inadequate use of the water has developed in its entire periphery. The coke production in the Paramo of Rabanal is one of the highest-impact activities on natural resources, mainly on water. There are no environmental plans at mining level. 3.500 to 5.000 ha of the Paramo de Rabanal have been intervened with potato cultivations, and 6000 to 9000 ha have cattle-related activities including bovines for meat and milk) and sheep in a smaller proportion. One of the main impacts on the area is fire. There are 4000 ha of reforestation with Pinus patula in different areas of Paramo, such as the Gachaneca I and II reservoirs. In the forest remnants of Paramo de Rabanal, there are also human activities that generate an impact on the natural environment, among them livestock shepherding inside the forests, expansion to the forest of potato cultivation, elaboration of coal from oak wood and the extraction of posts for fences. The Paramo de Rabanal is altered by the construction of roads and other infrastructural development, promoted by Municipal Governments and private owners.

Within Rabanal lies the Robledal Forest Preserve with 400 hectares between the municipalities of Ráquira and Guachetá, close to the Lake of Fúquene. On the southwest side of the Rabanal massif lies the forest preserve Paramo of Rabanal (2.681 have).

Belmira (Colombia)

The System of High Andean Paramos and Forests of Middle Northwestern Antioquia is located on a high plateau of the Colombian central mountain range, with a maximum height of 3.350 and a minimum one of 2.400 m, 70 km. north of Medellín, capital of the Department of Antioquia. The area of Belmira (19.630 ha) mainly occupies part of the municipalities of Belmira and San José de la Montaña, and also part of Entrerríos, San Pedro de los Milagros and San Andrés de Cuerquia, mainly in the area of the northern Antioquia Highland, and small areas of the municipalities of Sabanalarga, Liborina, Olaya, San Jerónimo and Sopetrán, the latter in the Cauca river canyon, in the western area of the System. It conserves plant

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populations and representative animals of high mountain ecosystems, important from an environmental-offer point of view, for the area contains a dense hydrological net born in the local Paramos and forests, which functions regulating rain water and receiving the humid fronts, common in the Andean ecosystems, and providing water for basic necessities of approximately 64.000 inhabitants of the urban and rural areas of 11 municipalities, located in the north highland and in the area of West on the canyon of the river Cauca, and a population of 980.000 of the Metropolitan Area of the Valley of Aburrá, connected to the multiple-use system of Río Grande ll, that also uses water for hydropower in Tasajeras and Niquía, generating 3% of the local energy. From a productive point of view, the area supplies water to large extensions dedicated to milk cattle raising in the area of the north highland of Antioquia and to the coffee and agricultural system of the oriental hillside of the Cauca canyon.

In general, the economy in the area is based on dairy production in the highland and interior valleys of the system and, in a smaller scale, on pork and trout. In the western flank, on the river Cauca basin’s nearby areas, the economy is based on dairy production in the high parts and coffee in the middle area. There are also small staple cultivations and extensive marginal cattle raising. According to 2002 annual statistics, the percentage of unsatisfied basic necessities for the area that covers ten municipalities is 32%, which denotes low habitation quality, low coverage of sanitary services, especially sewer systems, and little access to road infrastructure and services. The education level is low, with high-school levels with agricultural and teaching emphasis in the urban nuclei of the ten municipalities, in three corregimientos of six and one in a vereda of 42, which are inside the area of influence of the system. The residents of the area of the northern highland come mainly from the West and the Southwest of Antioquia, and the Valley of Aburrá, who, attracted by the current gold rush in the region, settled in the area, establishing a conjugation of different cultures, including Afro-American communities, characterized by the conformation of a nuclear rooted family, typical of the Andean area.

In 1998, the Regional Autonomous Corporation of the Center of Antioquia, CORANTIOQUIA, defined and zoned an area of 34.358,74 hectares in the Systems of Paramos and High Andean Forests of the Middle Northwest of Antioquia, aiming at declaring it a Protected Area, but to date the administrative act of declaration has not been signed declaring it a District of Integrated Management (DMI), and Management Plan has been formulated to plan and regulate the use and management of natural resources and the economic, educational, scientific and recreational activities that are developed as a conservation strategy.

Chiles (Colombia-Ecuador)

The Paramos around the Chiles volcano on the Colombia-Ecuador border (ca. 15500 ha) connect the Chiles indigenous territory (Colombia) and the El Angel Ecological Reserve (Ecuador). It is the southernmost extension of Paramos where giant rosettes of the genus Espeletia dominate the vegetation structure. The area is relatively wet (1000 mm) and has deep soils of volcanic origin (organic layer up to 150 cm). This Paramo area supplies water to one of the most intensive potato growing areas in the Northern Andes (Carchi-Nariño) and to watersheds that drain towards the Amazon Basin (via the Putumayo river and the Carchi and Guaitara rivers). The area is currently suffering from the side effects of the armed conflict in Colombia (migrations, illicit crops, large military presence). The project developed two Action Plans in this area, one at the Colombian side (Chiles territory) and one at the Ecuadorian side (Comuna La Esperanza).

The Colombian portion of the Paramo de Chiles is located in the South of the Department of Nariño, Municipality of Cumbal, Indigenous Territory of Chiles. It covers an extension of 5.626 ha, between 3200 and 4748 m. There are different vegetation types such as Polylepis forests with trees up to 15 meters, Miconia, Hedyosmum etc., scrub with shrubby vegetation of up to 5 m, mainly of Asteraceae; grasslands

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with herbaceous vegetation of macollas of Poaceae; Frailejonales with Espeletia pycnophylla, Puya clava-hercules and Blechnum loxense; Grasslands and peat-bogs with herbaceous strata and crawlers, and cushions and pads. In total 176 vascular plants have been registered, distributed in 56 families and 110 gerera. Five Subfamilies of butterflies were identified, 115 species of birds contained in 42 families and 81 genera; Lizards of the genus Stenocercus; Frogs of the genera Eleutherodactylus and Osornophryne; and two species of bats, Anora goeffroyi and Histiotus montanus. The soils in the Paramo of Chiles are of volcanic origin, formed by pyroclastic material of the volcanoes Chiles, Cumbal and Azufral. In the Paramo of Chiles three watersheds are born: Chiles or Germagan, Capot and Játiva. There are several lakes and thermal waters. The natural water currents have suffered deep human alterations due to the construction of channels and drainage systems for irrigation and water troughs. The domestic use for laundry, motorcycle, cars washing and fumigation pumps is contaminating the water sources with detergents, oils, and agrochemicals. The agrochemical abuse has generated water pollution processes especially in the lands close to ravines.

Human activities threatening the integrity of this ecosystem are deforestation of 8 ha/year, burning (10 ha/year) and others impossible to quantify such as livestock shepherding, grass extraction and wetland drainages, and the road construction that can produce in the future a larger occupation of these areas. It is important to highlight that small patches and forest remnants were observed amid the Paramo and bordering running water bodies, from 3.600 to 3.900 m, which make up a habitat net that makes possible the establishment of a great variety of plant and animal species that contribute to maintain the ecological balance of the area. The forest areas and Paramos of the Chiles volcano have been classified as places of critical priority for the conservation of the Southeast of Nariño. This priority is based on biological importance, vulnerability and integrity criteria, with the purpose of maintaining the multiple interrelations that allow this ecosystem to maintain its dynamic equilibrium.

The indigenous community of Chiles is formed by 888 families. The town council is the highest authority in the community. In the Territory of Chiles there are five Communal Action Boards in each vereda. The Territory has four educational nuclei. There is also the Nuestro Senior del Río High School in Chiles, which offers all the levels of pre-school, primary and secondary education. The vereda schools and the high school are directed by teachers belonging to the Territory who are knowledgeable about their traditions; therefore the education children receive theoretical/practical. It is important to mention that in relation to School Environmental Projects (PRAES), CORPONARIÑO implemented workshops related especially to environmental education guidelines. The housing in the area has evolved from the bahareque adobe type and today the brick type is dominant. Equally, roofs have been modified and in some cases concrete has been used. There are two types of land property: private (40%) and community (60%). Fifty percent of the families possess properties smaller than one hectare and only 3% have 32 properties larger than five hectares. The economy of the Indigenous Territory is based on agricultural activities and, in a smaller scale, commercial, handcrafts and tourism activities. According to the Agricultural Census of Chiles 2004, the area fit for agricultural activity is of 1232 ha, 1024 ha dedicated to grasses for the production of milk and 208 ha dedicated to agriculture, of which 80% correspond to potato cultivation and 20% to other crops such as beans, onions and ulloco (an Andean tuber).

The Ecuadorian portion of the Paramo of Chiles (9900 ha) limits with the Colombian border in the north, the El Angel Ecological Reserve in the south and with Golondrina Protected Forest in the West, between 3.000 to 4.723 meters. The waters in the area drain to the Pacific (through the San Juan and Mira Rivers) and to the Amazonía (Carchi River). The mean annual rainfall varies considerably in this area from approximately 1.000 mm in the sector of Tufiño to more than 1.750 mm in the surroundings of the volcano Chiles. The soils have developed on volcanic deposits of the Quaternary, formed by acid lavas of the andesite type, basalts and mainly of ashes, product of the activity of the Chiles volcano. In the area big there are large extensions of wetlands (lakes and peat-bogs besides typical vegetation of Paramo (rosettes -grasslands) and superParamo.

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Comuna La Esperanza is a community of approximately 1.300 people, belonging to the Quillasingas and Pastos cultures that have lost their identity via transculturization processes. This human group is made up of around 260 families. They occupy individual houses built with adobe in association with fibrous wooden natural materials. These groups are distributed forming small towns located along the road, coordinated by a central head that in Tufiño, where all the planning is made for the Community and where the Central Board is located. The comuna settled here some three hundred years ago, in the beginning as a town council of the Gran Colombia, where lands were managed in combination by people from Ecuador and Colombia. After the national boundary was established, the Comuna was founded in the Ecuadorian side. The literacy rates are moderate; approximately 80% of the population has basic notions of reading and writing. Most of the revenues come from the sales of agricultural and forest products. People obtain economic revenues outside of the commune for manpower, consequently migration is very high, being woman the ones that emigrate most. Most of the communities that belong to the Comuna lack sanitary services and waste-elimination facilities. The water for human consumption is not treated. Transport inside of and toward the area is done through a third-order road that unites the province-capital city of Tulcán with the parishes of Tufiño and Maldonado, of approximately 92 km. This road crosses from East to West to the Center of the communal area, dividing it in two parts. One of the communities, Chilmá Bajo, is connected with the main road through a branch; the other ones do it through paths or horse roads.

There are six main types of land uses: cultivation, grasses, Paramo, natural forest, areas without vegetation cover and town centers. Traditional crops are potatoes, beans, ocas and mellocos (Andean tubers), in the mountain; banana, manioc, corn and a variety of tropical fruits and grasses in the subtropical slopes. 9.891 hectares that represent 21.9% of the total area are dedicated at the moment to agriculture.

Zuleta-Mojanda (Ecuador)

This site comprises two independent but closely located Paramos: Zuleta and Mojanda. Although their biophysical and socioeconomic realities are partly shared and partly independent, it is possible to treat them as one site for the purposes of this project.

This area comprises approximately 29000 ha. between the Pichincha and Imbabura provinces in Ecuador. It limits with the Cayambe Coca Ecological Reserve in the East. The Mojanda lakes area was declared as a bi-municipal conservation area but does not have a legal status as such, thus the two municipalities involved have “twin” legislations. It is an area representative for the majority of Paramos in North and Central Ecuador, where tussock grasses dominate the landscape, intermingled with small peat lands, lakes and forest remnants. Indeed, some scattered Polylepis and mixed high Andean forest can be found in this landscape. The dominance of the relatively homogeneous tussock grass Paramo is probably associated with repeated burning and extensive livestock grazing all over the area. The population in this region is mixed between Quichua speaking indigenous people and mestizos. In general, they are well organized in communities and higher-level organizations. The project developed two Action Plans in this area in different social conditions: one around the Lake of Mojanda and one the Paramos of the Zuleta hacienda and community.

The place called Cerro de Mojanda (25000 ha) is located in the provinces of Pichincha and Imbabura, shared by the municipalities of Pedro Moncayo, Otavalo and Quito. In 2001, the Municipalities of Otavalo and Pedro Moncayo subscribed an agreement for the management of Mojanda that creates a protected area starting at 3000 m to the highest point located to 4260 m in mount Fuyafuya. The protected area has an extension of 25.000 approximately. Mojanda was formed by the eruptions of the old volcano

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Mojanda, the crater of which has a diameter of approximately 4.5 kilometers. In the crater there are three main lakes and a fourth smaller one. The humid montane forest is between 3000 and 3400 m, with temperatures averaging annually between 8 and 12°C, and rainfall averaging annually between 500 and 1000 mm. The soils are Mollisoles. The native vegetation is characterized by arboreal vegetation, including species such as Yagual, Pumamaqui, Quishuar, Colca, Chachacomo and Piquil. Most of the forest has been transformed into cultivation fields of potatoes, beans, barley, quinua and ocas. Pine plantations also exist (Pinus radiata). This belt is the propriety of communities and large landowners. The Very humid montane forest registers annual mean precipitations of 1000 mm, where, besides the aforementioned species, there are Sachacapulí, Matache, Pigüe an Arrayán. In this ecosystem the soil type is Duripan. The Andean forest remnants border the agricultural and cattle-raising areas and the Paramo. The Paramo ecosystem begins at 3.500 m. The mean annual temperature of the Paramo in Mojanda goes from 3 to 6°C, with a mean annual rainfall of 1.000 mm. The soils of the Paramo are Dystrandepts. This ecosystem is dominated by gramineous vegetation of the genera Festuca, Calamagrostis and Stipa, and shrubs, and in the forest remnants there are species like pumamaqui, piquil, quisuar, and yagual. The highest areas of the Mojanda have been used for livestock shepherding and cultivation. The lake system of Mojanda and other slopes are the only source of water for human consumption for the whole municipality of Pedro Moncayo and three parishes of Otavalo. The population that benefits from this water reaches a total of 36000 inhabitants.

In relation to the conservation status of the lake system, there has been a decrease of the water mirror of the big lake due to direct use through the installation of a valve that captures a larger flow than the one feeding the lake; there is also contamination of the lakes and the slopes due to livestock shepherding. This area is affected by agricultural, coal miming and unchecked tourist activities. If appropriate measures are not taken, the destruction of this ecosystem will get worsened in the short term, affecting directly a considerable population in the two municipalities and the country’s natural heritage.

The Area of Mojanda is inhabited by diverse peoples: Otavalos, Cayambis and Cochasquis, and a mestizo population. In total, there are 26 communities with a total population of 11.000. The traditional productive activities are agriculture and cattle raising. Even though flower production in Pedro Moncayo is done below 3000 m, its influence is enormous in the area. In Otavalo community property is predominant under traditional agricultural practices, but crops such as have intensified lately. In the high part of the Paramos, both in Pedro Moncayo and Otavalo, bull-fighting cattle are maintained. For their landscape qualities and the easy access, this is a place visited by many tourists, a fact associated to the characteristics of Otavalo. Several educational centers are located in diverse communities of the two municipalities. Health centers are located in the municipal and parochial heads. The road infrastructure is: a paved road that goes from Otavalo to the big lake (21 km); a third-order road that goes from Tabacundo to the Black lake (14 km); and a fourth-order road that goes from Malchinguí to the Chiriacu lake.

The total surface of the area of Paramo of Zuleta is 4770 ha. It lies in the Ecuadorian Oriental mountain range, in the Angochagua parish of the municipality of Ibarra, in the province of Imbabura. The Paramos of Zuleta limit to the East with the Cayambe Coca Ecological Reserve. The area was declared as Protected Forest and Vegetation “Zuleta y Anexos Co. Ltda. and community of Zuleta” in 1995. The landscape is highly undulated with slopes over 50%. The soils are of young to very young volcanic origin, of the dystrandepts type. The area is located in the Santiago-Mira Hydrographic System, the Río Mira basin, the Chota watershed, and the micro-watershed Tahuando, ravines San Pedro, San Leonidas; Santa Isabel, Santa Martha and Yanajaca. The mean annual rainfall is 1.500 mm. The area presents the typical type of vegetation of Paramo grassland, with a dominance of Calamagrostis effusa, grasses and shrubs. There are a few forest fragments in the area. The community has identified 19 species of useful trees and 26 species of frequently-used medicinal herbs. In a participatory diagnosis workshop, the community also identified 24 birds and 25 mammals, 3 fish, 4 amphibians, 3 reptiles and 14 invertebrates.

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After the Spanish conquest, the lands that at the moment correspond to Hacienda Zuleta (now a private company) and the community of Zuleta were given to the Jesuits by the Spanish crown. They introduced Spanish agricultural and livestock techniques, and later they established looms and sawmills. At the moment, the lands in the lower area and the hillsides are property of the company Zuleta and Annexes and the community of Zuleta, and the vast majority of Paramos is communal property. Inside the aforementioned area, there are 329 families with a total of 1037 inhabitants. Until the 80’s the local economy was stable, until, little by little, it became a “survival” one due to the impressive and uncontrollable monetary devaluation and monstrous speculation that had an accelerated growth from 1981 up to the 2000’s. At the moment most of the population lives below the poverty limit. Currently, there is medical attention at the Health Sub-center regulated by the Imbabura Health Headquarters. At the moment, in the community there is education at the three levels: Pre-primary, primary and secondary (Agricultural Technical High School).

Among the main problems that have been determined is the scarcity of water due to low flows, thus it is urgent to develop prevention and control measures of Paramo burning and tree slashing, improve agricultural technification, curve the environmental impact of the electric interconnected system Pasto-Quito that crosses the Paramo, control the introduction of cow and horses to prevent the erosion and laterization of the Paramo vegetation layer, and promote fulfillment of agreements by water management authorities and institutions.

Llangahua (Ecuador)

The highlands of Llangahua in the province of Tungurahua, to the west of the city of Ambato, contain almost 5000 ha of Paramo located between 3800 and 4400 m. The precipitation is low; around about 600 mm yearly. There a great number of water sources originate, that have bee used to provide drinking and irrigation water to the communities of the area, as well as to feed the flow of the main rivers that allow the irrigation of the lower areas through small canals and, at the same time, to supply drinking water to the city of Ambato (ca. 250,000 inhabitants). The Ambato river is a tributary of the Pastaza river (Amazon basin). The mean annual temperature averages yearly around 6°C with frequent frosts (nights with temperature blow 0°C) during the months of October to December and April. The low part of the Paramos of Llangahua possesses deep black Andean soils in the category inceptisoles. The Paramo suffers from a great impact due to overgrazing, and many areas are degraded and desertified. However, there remains the typical Paramo (pajonal) with useful species such as the sunfíllo (Satureja nubigena), cunucchaqui (Lachemilla orbiculata) and taruga cacho and fragments of small yagual (Polylepis spp.) and piquil (Gynoxys sp.) forests that harbor líchens, fungi and climbers. Within the degraded landscape, the Paramo possesses wetlands at the bottom of its extensive glacial valleys in which large cushion-forming plants dominate, especially of Azorella pedunculata and Plantago rigida, which form a layer of humid and spongy matter that turns into peat, thus assuring the storage and generation of water. In some sectors the Paramo is more humid as in Escaleras and Verdepungo, with higher plant diversity and a continuous vegetation cover; therefore, one can find there more water sources. The humid part of the Paramo covers 2000 ha. The Paramos of Llangahua, jointly with those of Calamaca, are important areas of special protection since in them there are the last relicts of native forest in the Ambato area, and they have a large number of high Andean wetlands which are the source of water that feeds the river.

Of all the places of the project, this seems to be the most degraded. It has a long history of use with much human presence and good accessibility (the access roads cross the area with 45 asphalted and ballasted kilometers). The infantile population is served by 3 primary schools located in the three sectors: Loma Gorda, Escaleras and El Salado, with a total of 17 teachers. Also, the Pastaza river area has one school with 43 students and 2 teachers. Unfortunately, there is no health service according to the population

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number; For the Salado sector there is one health center of Peasant Social Security in agreement with the Indigenous Department of Health.

The communities have a permanent service of irrigation due to their location and environmental conditions, an aspect that can foster a better cultivation planning, including its diversification. The development of agricultural activities generates the main income for the population. However, subsistence agriculture is not very productive due to faulty technical support and to a very low production diversification. In some communities, Paramo land is still used communally, a fact that has fostered conservation of these sites, although there is currently a lot of pressure to divide it into plots for each family.

At the moment, the five localities with which the Project will work belong to the Llangahua Central Agricultural Cooperative, which in turn belongs to Cristóbal Pajuña Corporation of Organizations (a second-grade organization). The history of occupation of these lands goes back to the Spanish conquest and the colonial tines, starting in 1534. This process forced the native inhabitants to flee to the Paramos. When the peasants established a cooperative, they could buy properties at a preferential price according to the politics of distribution of Paramo lands for the benefit of all; nowadays the Paramo is used as natural grassland for bull-fighting cattle (mainly), sheep and horses. The families of the communities cultivate grasses, potatoes, beans, garlic and maintain natural grassland. In spite of some technical support, skilled labor and resources from the external institutions, deficiencies exist still in the planning of management activities. Therefore, the different predominant productive systems should be analyzed in this area in terms of the strategy farmers use to maximize their utilities using the available resources. It is also necessary to analyze and to generate alternatives for elimination of elements of Paramo degradation such as burning, presence of pigs in wetlands, indiscriminate forest slashing and indiscriminate extraction of native vegetation.

Loja-Piura (Ecuador-Perú)

The Paramos of the Sabanilla Cordillera on the Ecuador-Peru border (25000 ha) connect the Southernmost tip of the Podocarpus National Park in Ecuador with the Colambo-Yacuri forest reserve on the border, and the Tabaconas Namballe Sanctuary in Peru. It is a relatively well conserved Paramo area dominated by grassland-scrubland and dwarf bamboo Paramo with many important wetlands. The area is very wet (up to 5000 mm) and has shallow fragile soils (organic layer up to 20 cm). This Paramo area supplies water to the dry, banana-growing area in the Pacific coast (Catamayo-Chira watershed) and to watersheds that drain towards the Amazon Basin. The project developed three Action Plans in this area, one at the Ecuadorian side (Jimbura) and two at the Peruvian side (Espíndola and Pacaipamba).

Jimbura in Ecuador is located in the south of the province of Loja, under the jurisdiction of the Municipality of Espíndola, which, together with other parishes, adds to an approximate area of 10.000 ha of Paramo. The intervention area is characterized by a glacier panorama located up to 3200 m, with a rocky landscape with a rough geography in most of the area. The area is cold and it is subjected to intense precipitations, with the presence of a very dense fog and permanent winds. The mean daily temperatures in the Paramo are around 8.5ºC, with a mean annual rainfall of 1101mm, with a period of heavy rains from November to April. The Jimbura Paramos are part of a complex ecological panorama with cloud forests, spiny dry forests and scrub, and two main types of Paramos (shrubby and grassland). The conservation status of the Paramo areas is relatively good due to a low intervention. Nevertheless, cattle raising and concomitant burning are present. Some wood and medicinal plants are used.The municipality of Espíndola (ca. 18.000 inhabitants) is one of the poorest in Ecuador, with a poverty (non satisfied basic needs) of 94.3% and an extreme poverty of 77.1%. Scholarity (study years) is 4,4 and the deficit of basic residential services is 94,5. The population recognizes the importance of incorporating

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appropriate and complementary technologies in the use of the different ecological altitudinal levels that exist in this area.

In Perú, Espíndola (in Ayavaca, Piura, Peru, not to be mistaken with the Ecuadorian Espíndola municipality) is made up of three settlements: Espíndola, El Toldo, and El Huilco. The three are sections of the Samanga Peasant Community that are closer to the cloud forests and Paramos. The Samanga Community has an approximate area of 12,700 ha, of which 1,200 are cloud forests with Podocarpus and Alnus species, and 2,000 Paramo. The Paramo zone lies between 2,600 and 3,000 m in the western slopes of the Andes. In the Espíndola and El Toldo settlements families directly use Paramo services, mainly through grasslands for extensive cattle raising. This community is located on the left margin of the Espíndola river in the heights of the Catamayo-Chira watershed, between two landmarks: río Quingo headwaters in the higher part and the and Calvas in the lower part. Territorially there are three zones: lower, middle and upper, each one characterized by soils, vegetation, main crops, climate and water availability. The town centers have ca. 96 families and 382 inhabitants. The topography allows a good availability of water resources; although the flow fluctuates, there is water throughout the year, with a mean of 350 l/s in the wet months and of 150-200 l/s in the dry months. Espíndola, on the border with Ecuador, has grown more rapidly that the surrounding settlements . Nowadays it has a police station, migration office, modern educational and health infrastructure, and domestic drinking water service. Here the mean annual rainfall is 1,800 mm.

The vast majority of Paramos is communal. There are no management plans although the conscience about the importance of these ecosystems is growing. These areas are free for cattle and there is certain permissibility for families to do agriculture. In the lower zones people cultivate coffee, corn and small animals (chicken, pigs). The mean surface owned is 30 ha. The Paramo zone is mainly used for cattle shepherding throughout the year. This use is not done by Samanga families but by Huamba families, who have less Paramo extensions and use Samanga’s Paramos to cover their demands.

Another activity carried out in a lesser scale is slash and burning of the cloud forest bordering the Paramo. Some 10 families occupy the Paramos without previous petition., to cultivate after slash-and-burning. The Paramo consists of a grassland-scrubland dominated by Calamagrostis with a notable presence of Asteraceae and Ericaceae shrubs. There is a high diversity within genera such as Neurolepis, Puya and Paepalanthus. In the forests there are woody genera (Juglans, Podocarpus, Myrcianthes and Alnus). The Piura Paramos are considered by people as “strong” places where one can get cured and energized. The cloud forest harbors fauna with Odocoileus virginianus and Mazama, Penelope barbata, Andigena, Dasypus novemcinctus, toucans, Pseudalopex culpaeus, Tapirus pinchaque, anteater, woodpecker, birds, butterflies, reptiles, insects, and in the Paramo zone the Andean bear can be seen.

Despite environmentally unfriendly practices, such as slash and burning, cattle overgrazing and felling (by Ecuadorian Word traders), ca. 60-70% of the forests and Paramos can be said to be in a virgin state due to a low-density population. In the zone the cultural value of the lakes is Paramount. There are seven important lake systems from where many small ravines start.

The Pacaipamba Paramos are a possession of the San Juan de Cachiaco peasant community in the upper part of the Bellavista de Cachiaco watershed (Ayavaca,

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Piura, Peru). It is formed by three settlements: Totora, San Juan and El Palmo, close to the Paramo zone and whose inhabitants (approx. 835) use it directly and indirectly.

The population has a secondary educational level. The housing is rustic, with adobe, wood planks and straw thatching. In San Juan de Cachiaco only the Paramo portion has not been divided (1,500 ha). The agricultural activities are done below the Paramo where they cultivate Andean tubers and Fava beans. In the lower parts they cultivate coffee, sugar cane, and pastures. The use if pesticides is low and done mainly in the Lagunas de San Pablo sector. Each family has a mean number of cattle of three. Cows are the main income followed by pigs and sheep. Horses and mules are bred for burden and people transportation. Both agricultural and animal husbandry activities are not technically aided. Some 15 years ago people used the Paramos fir shepherding but nowadays it has become too dangerous supposedly due to raids and Andean bear attacks. There are two irrigation boards in El Palmo for the Chinchín and Chirimoyo canals. There are other canals such as Paramo, La Huaca, and Tierra Amarilla. Nine important lakes are in the Paramo, where the Chirimoyo, Mushcapam and Tamillo rivers originate.

Cajamarca (Perú)

The southernmost intervention area of the project is a complex of Paramo (locally called Jalca) areas around the Peruvian city of Cajamarca. In general, the Jalca area is heavily transformed by human occupation, mainly through overgrazing and side effects of the gold mining industry. The relatively small well conserved areas form the only examples of Jalca in this region and are the source of important watersheds that drain to the coastal desert (Jequetepeque) and to the Amazon basin (San Lucas). In the area, Action Plans were developed for two Jalca sites: Chetilla-Magdalena and Cajamarca.

Las Jalcas of Chetilla-Magdalena are a slope area of grasslands (3,200-3,770 m) that go down towards the Chetilla river. These places until 10 years ago were pastures but lately they have been divided and are the living quarters of families that come up from Cajamarca and Jequetepeque. The extension is ca. 4,000 ha and ca. 850 inhabitants. It was formerly part of the Sexemayo hacienda, which was dedicated to sheep and cows. In the upper part there are a few natural Paramo areas. Some pine plantations have been developed and are waiting to be used by the local population but nowadays serve as firewood from the pruning. In the middle altitude people cultivate exotic pastures there are some Paramo-jalca shrubby species used for firewood. Between the Paramo middle and upper parts people cultivate mainly potatoes, fava beans, Andean tubers, oats, wheat and barley. Most is used for self-consumption and some surplus is transported to local markets, such as in the case of aromatic herbs. An important activity is cattle, sheep, and horse raising as well as of small animals. Milk production is one of the main income-producing activities.

Jalcas are important water sources for the Jequetepeque basin and for local settlements and the district capital. The upper parts have been severely impacted and only a few sectors conserve a grass cover. Several NGOs have used pine tree for reforestation. There are also small shrubby areas and some untouched grassland areas. With the diminishing vegetation also animal populations have decreased.

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Deer, foxes, rabbits, cuy, vizcachas, several birds, are increasingly scarce. One of the main threats is local hunting.

Local people perceive the lack of water as a weighty problem. For about three years there has been drought. Frosts have increased consequently. It is not rare that all crops be lost. Many people have changed vegetables for grasses since they are deemed less risky (from 70% self-consumption agriculture has gone down to 30%). Nowadays the middle areas are for milk cattle and agriculture is done increasingly in the jalca belt. They usually plant oats initially.

The Cajamarca District jalcas cover an area of ca. 3,000 ha (3,200-3,900 m) comprising the upper basins of Chamis and Cushunga, both feeding the San Lucas river that crosses the city of Cajamarca towards de Amazon basin. The area topography is rather rough although it presents some rounded profiles, which, before the Agrarian Reform 40 years ago, were covered by extensive native grasslands with small depressions or wetlands (the larger one being the Chamis lake, with ca. 16 ha). This lake used to be the habitat for many migrant bird species but currently it is deeply threatened due to the drought.These areas were formerly large haciendas dedicated to cattle raising. Nowadays the tendency is towards very small agricultural estates and strong erosion. The changing climate has favours the cultivation of crops in higher zones where currently the major threats are agricultural and mining practices. The tree local settlements (Chamis, Cushunga and Carhuaquero) have 2,666 inhabitants, 40% of them Quechua speakers. The main agricultural activity is the cultivation of potato, wheat, rye, Andean tubers, quinoa and barley. There are medicinal and other plants used such as straw, andacushma, chicoria, escorzonera, diego lopez, pushgay, valeriana, trenza, chulcolindo, paja blanca, pacha chamca, chulco, papilla, cushco, ishguin, ortiga negra – blanca, cola de caballo, estrella, pie de perro. The destination of these plants is mainly for self-consumption and some for sale. Cattle raising is not a main activity due to the lack of pastures. In some vases raygrass, clover and foraging barley are planted. However, there is not enough water and there is also a lack of technification in seeds and installations. Fauna-wise there are still deer, vizcachas, foxes, several birds, among others. The principal problems are soil poverty, winds and hailstorms, drought, plagues, etc.

El Duende (Colombia)

This pristine area in the Colombian western Cordillera will be used for comparison studies only, although a strong collaboration with the local environmental authority (CVC) and a conservation NGO (FUNDENA) has started to support the creation of a regional protected area and the development of its conservation plan.

The area is located in the Departments of Cauca and Chocó, with a total extension of 1,900 he. The zone belongs both to the Cauca and the Pacific basins. Metasedimentary and metamorphic rocks of the Dagua group make up the geology of the area. The geomorphology presents strong slopes above 80% that increase towards the ravines. This and the high rainfall (2500 to 4000 mm) cause a de-saturation of the soils due to washing. An optimal development of the soils is prevented by the torrentiality and deep slopes, which cause laminar erosion. The organic layer is thin. The Western cordillera Paramos are usually well-conserved small areas in the summit of a not very high but very irregular sierra with not

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much glaciation. The lack of human intervention renders this area particularly biologically important. A brief vegetation analysis showed that there are 155 Paramo plant species. The Paramos and surrounding forests register more than 140 bird species of which 22 fulfil AICA criteria The lower zone is inhabited by peasants of several origins, mainly from the municipality of Calima, an indigenous territory at ca. 2,000 m in the buffer zone. The total of veredas is 21, located in 8 corregimientos.

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1 2 3 3 4 5 6 7 8 9 10 11 12 13 14 15

Proj

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Tuñame 2 3 2 2526 Poor pheasants and mestizos

1 Private /communal

Potatoes/unplanned animal husbandry, fire

4 Buffer area of a National Monument

2 5 1 1 1 3

Gavidia 4 4 3 6030 Poor pheasants and mestizos

4 Private in a National Park

Potatos/livestock/turism/garlic conflict

3 Part of Sierra Nevada National Park

5 5 3 2.5 3 4

Rabanal 5 4 3 17567 Poor pheasants and mestizos

3 Private Potato, fire, livestock, mining

4 No 5 4.5 5 5 4 5

Belmira 4 4 3.5 19630 Mestizo and settlers. Not very poor

1 Private Potato, intensive livestock, pigs, fire

4.5 Under construction 4.5 4.5 4 4.5 4 4

El Duende 5 3 5 2500 No 2 Wasteland In the future 4 Several private reserves 3 2 3.5 3.5 4 3.5Chiles 4 4 3 15500 Poor pheasants

and indigenous (Col) and wealthy mestizos (Ecu)

4 Communal /Private

Potatoes, intensive livestock, fire, conflicts

4 Indigenous territory (Col) and Buffer zone of the El Angel Ecological

Reserve (Ecu)

2 4 4 3 2 2

Zuleta - Mojanda 2 3 2 29770 Indigenous community and mestizo and hacienda

3 Communal/Private/in conflict

Burns, livestock, pine, uncontrolled tourism

4 Protected Forest (Mojanda) and Buffer Zone of the Cayambe

Coca Ecological Reserve

2 4.4 4 2 2 3

LLangahua 2 2 1 5000 Poor Indigenous 4 Private Fire /Livestock 5 Buffer Zone of the Chimborazo Faunistic

Reserve

4 3 4 3 4 4

Loja-Piura 4 4 4 25000 Poor mestizo, traders and “absents”

5 Private/communal

Fire, agriculture and mining

4 Colambo Protected Forest, Buffer Zone of

the Tabaconas Namballe reserve

3 2 3 3 5 2.5

Cajamarca 2 3 1 7000 Poor pheasants and mestizos

1 Private Mining, agriculture forestry

3 No 1 4 3 3 1 3

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Tuñame

Chiles

Mojanda-Zuleta

Llangahua

Cajamarca

Loja-Piura

Gavidia

El Duende

RabanalBelmira

Legend

Paramo areaPrincipal citiesProject Intervention Sites

Distribution of Paramo in the Northern Andes; Project Intervention Sites of Proyecto Paramo Andino

ANNEX 11.5: LOW-IMPACT LAND-USE PRACTICES IN PARAMOS

During the design phase of the project, a group of experts identified and analyzed a series of productive activities with low impact (environmental and social) on the Paramo. This task was carried out through an Infoandina electronic conference as well as field visits to different Paramo areas in the four participating countries. An initial diagnosis of the effects of such practices in the visited localities has already been developed. However, due to the large number of variables considered, most of the practices still require further analysis to define more clearly their impact on Paramos.

Particularly in the area of Ecotourism, PDF-B analysis shows that even though this activity may constitute a possible source of additional income for Paramo inhabitants, only very few areas would have real possibilities for substantial benefits and, it does not appear to be a major potential source of income for the population in general as an alternative to traditional income generating activities, at least in the medium term. Some of the analyzed areas that exploit this option differ in their characteristics from Paramo and lie outside of the project intervention area. Paramo sites in Colombia, Ecuador and Peru are not easily accessible and not likely to attract a critical mass of tourists with sufficient spending capacity. This being said, the option for ecotourism development is open and the list includes several potential sites.

The analyzed practices constitute a catalog that will be an important input for the development of sustainable development plans for different Paramo areas. The complete catalog can be perused at http://www.condesan.org/ppa/doc_dis.htm. A description of each practice and the site where it was identified and analyzed follows:

Biodiversity and Tourism:

1. Use of Paramo straw by the artisans of Guacamayas. Department of Boyacá, municipality of Guacamayas, Colombia.

2. Sale of wild Paramo flowers. Department of Cundinamarca, municipalities of Bogotá D.C and La Calera, Colombia.

3. Propagation of endemic threatened Paramo flora. Department of Boyacá, municipality El Cocuy, Natural National Park El Cocuy, Colombia.

4. Ecotourism in the a-zonal Paramos bordering the lake of La Cocha. Department of Nariño, municipality of Pasto, Colombia.

5. Ecotourism in the Paramo bordering the lake of Telpis, Sanctuary of Flora and Fauna Galeras. Department of Nariño, municipalities of Pasto, Tangua, Yacuanquer, Consacá, Sandoná and La Florida, Colombia.

6. Ecotourism in Natural National Park El Cocuy. Departments of Boyacá, Arauca and Casanare, municipalities of Güicán and Cocuy, Colombia.

7. Plan of ecotourism development for the Mamapacha and Bijagual Massifs. Department of Boyacá, Colombia.

8. Management of natural resources in the Paramo of Atapo Quichalán. Province of Chimborazo, municipality Guamote, parish of Palmira, communities of Guantug, Guasán, Santa Elena and Santa Cruz, Ecuador.

9. Straw management for handcrafts in the Community of Cruz del Arenal. Provinces of Chimborazo, Tungurahua and Bolívar, Fauna Production Reserve of Chimborazo, Ecuador.

10. Ecotourism in the Yanahurco Hacienda, Cotopaxi and Antisana Ecological Reserves, Ecuador. 11. Community Ecotourism in Chimborazo (Federation of Indigenous Rural Organizations of the

Slopes of Chimborazo), FOCIFCH, Ecuador.

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12. Programs of community ecotourism in Chimborazo. Provinces of Chimborazo, Tungurahua and Bolívar, Ecuador.

13. Ecotourism project of the indigenous community of Oyacachi. Province of Napo, municipality Chaco, parish Oyacachi, Cayambe-Coca Ecological Reserve, Ecuador.

14. Introduction, management and use of vicuña in the Fauna Production Reserve of Chimborazo. Provinces of Chimborazo, Tungurahua and Bolívar, Ecuador.

15. Rural tourism in the Natural Parks Sierra Nevada and Sierra de la Culata and buffer areas. State of Merida, municipality of Rangel, Venezuela.

16. Tourism in the cable-car of Merida. State of Merida, municipality of Merida, Venezuela. 17. Trout cultivation in Valle Encantado. State of Merida, municipality of Rangel, town of Gaviria,

Venezuela 18. Use of natural wool dyes, Textile School “La Chamarra.” State of Merida, municipality of Rangel,

Venezuela. 19. Recovery of water sources with native plants. State of Merida, municipality of Rangel, Venezuela. 20. Initiative to use medicinal plants, (National Committee for the use of the medicinal plants)

CONAPLAMER. State of Merida, municipality of Rangel, Venezuela. 21. “The Honey House” and “Mayan Honey”, production of honey and by-products starting from bees

fed in the Paramo. State of Merida, municipality of Rangel, town of Gavidia, Venezuela. 22. Education and popularization for Paramo populations, Ecoazul. State of Merida, municipality of

Merida, Venezuela.

Other possible current or future cases (not analyzed in detail):

1. Use of Paramo straw for the elaboration of hats in the municipality of Sandoná and elaboration of medicines, creams and shampoos from resources of the Paramo, department of Nariño, slopes of the Galeras volcano, Colombia.

2. Ecotourism in the Paramo of Belmira. Department of Antioquia, municipality of Belmira, Colombia.

3. Ecotourism in Cajamarca. Department of Cajamarca, Peru. 4. Ecotourism in Huaraz. Department of Ancash, Peru. 5. Ecotourism in the Natural National Park Los Nevados. Departments of Caldas, Quindío, Risaralda

and Tolima, Colombia. 6. Use of frailejón leaves for the transport of ice in the Paramo of Cumbal. Department of Nariño,

Colombia. 7. Extraction of wild flowers packed in frailejón for sale in Bogotá. Department of Cundinamarca,

municipality of la Calera, Colombia. 8. Use of curí skin. Departments of Nariño and Cauca, Colombia. 9. Food security projects with the use and management of Armadillo in Chiquita. Department of

Boyacá, adjacent to the Fauna and Flora Sanctuary of Iguaque, Colombia. 10. Food security projects with the use and management of Agouti in the PNN Munchique.

Department of Cauca, Colombia. 11. Breeding of Agouti taczanowsky for self-consumption, investigations already in place for prompt

application in Paramos of Cruz Verde, Choachí and adjacent. Department of Cundinamarca, Colombia.

Mining:

1. Geo-environmental studies for the feasibility phase of the Project Río Blanco. Province of Azuay, municipality Cuenca, parish Molleturo, Ecuador.

2. Soil use in the exploratory phase of the Mozo mining area. Province of Azuay, municipality Nabón, parish Cochapata, sector Cerro El Mozo, Ecuador.

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3. Project Yanacocha, challenges for the Regional Sustainable Development of Cajamarca, Peru. (not classified as low-impact but evaluated due to its incidence on the area)

4. Defense of the agriculture and community organization to face mining in the district of Tambogrande. Department of Piura, Peru.

Forestation:

1. Massive plantation in Carboncillo. Province of Loja, municipality Saraguro, parish Urdaneta (Paquishapa), Ecuador.

2. Pine plantations for mushroom production in Salinas de Bolívar. Province of Bolívar, parish Salinas, Ecuador.

3. Block Plantation. Province of Tungurahua, parish Pilahuín, community Yatzaputzán, Ecuador. 4. Agro-forestry system with native and exotic species. Community Cochabamba, Ecuador. 5. Agro-forestry Plantation. Province of Imbabura, parish Angochagua, association Gallo Rumi,

Ecuador. 6. Community forestry development in the watersheds of Ayash and Carash. Department of Ancash,

province of Huari, district of San Marcos, Peru. 7. Management of forest seed nurseries in Callejón de Huaylás. Department of Ancash, provinces of

Huaraz and Yungay, Peru. 8. Community forestry development in the Encañada watershed. Department of Cajamarca, district

La Encañada, Peru. 9. Forestation with pine in Granja Porcón. Department of Cajamarca, district of Porcón, Peru. 10. Reforestation in the Río Blanco basin. Department of Nariño, municipality of Cumbal, Indigenous

Territory of Chiles, Colombia.

Agriculture and cattle rearing:

1. Breeding and management of alpacas in high Andean areas and Paramos for the production of fiber as an economic alternative to cattle (bovine and sheep) and agricultural (potato) production. Province of Cañar, municipality Azogues, parish Rivera, Ecuador.

2. Proposal for integral land management in the Paramo of Letras. Departments of Tolima and Caldas, municipality of Herveo, vereda El Doce, Colombia.

3. Huacho rozado, a reduced potato plough system that allows the obtention of a better-quality product reducing erosion and chemical pollution. Province of the Carchi, municipality San Gabriel, Ecuador.

4. Rotational shepherding in native pastures. Department of Ancash, province Recuay, Village of Acocancha, sector Canrey Chico, Huaylas, National Park Huascarán buffer zone, Peru.

5. Lupinus plantation with Polylepis living fences. Department of Cajamarca, Municipality of La Encañada, Village Quinuamayo, Peru.

6. Stone terraces for erosion control and improvement of production areas. State of Merida, municipality of Gavidia, Venezuela.

7. Use of coverings with rice shell in strawberry cultivation. Asociación de Proyectores Integrales del Paramo (PROINPA) Angostura y El Rincón, municipality of Rangel, State of Merida, Venezuela.

8. Association of medicinal plants. PROINPA, Rangel, Merida, Venezuela. 9. Production of vegetables with organic fertilizer PROINPA, Merida, Venezuela. 10. Sheep management. PROINPA, Rangel, Merida, Venezuela.

Water management:

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11. Improvement of the soil hydraulic dynamics by means of the introduction of alpacas, sustainable use of straw and intensification of agricultural activities in the lower area, Sangay National Park. Province of Chimborazo, communities Guarguallá and Alao, Ecuador.

12. Declaration as Ecological Reserve of Paramos de El Ángel and management of the buffer area via a basin integral management approach. Province of Carchi, municipalities of Mira, Bolívar and Espejo, Ecuador.

13. Improvement of the soil hydraulic dynamic by means of the substitution of sheep by vicuñas in the Fauna Production Reserve of Chimborazo. Province of Chimborazo, Ecuador.

14. Water regulation in the high basin of the Machángara river by means of hydropower, drinking water and irrigation reservoirs. Provinces of Azuay and Cañar, basin of the Paute river, watershed of the Machángara river, Ecuador.

15. Dialogue and agreement as tools for a sustainable administration of natural resources. Province of Tungurahua, Ecuador.

Some practices suggested as possibly low-impact but not yet analyzed:

1. Protection of water sources by means of the acquisition of Paramo lands. Departments of Cundinamarca and Meta, Chingaza Natural National Park, Colombia.

2. Protection of water sources by means of the acquisition of Paramo lands. Province of Azuay, municipality of Cuenca, Cajas National Park, Mazán, Ecuador.

3. Protection of water sources by means of the acquisition of Paramo lands. Department of Boyacá, Paramo El Rabanal, Colombia.

4. Low-impact regulation of natural water bodies. Departments of Cundinamarca, Meta and Huila, Paramo of Sumapáz, Colombia.

5. Low-impact regulation of natural water bodies. Province of Azuay, municipality of Cuenca, Cajas National Park, Ecuador.

6. Regulation in reservoirs. Departments of Cundinamarca and Meta, Chingaza Natural National Park, Colombia.

7. Protection of water sources by means of the declaration of Protected Areas. Province of Azuay, municipality of Cuenca, Cajas National Park, Ecuador.

8. Protection of water sources by means of the declaration of Protected Areas. State of Merida, National Park Sierra de la Culata, Venezuela.

9. Consensual management of Paramo for conservation and water regulation. Province of Tungurahua, high basin of the Pastaza river, Ecuador.

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ANNEX 11.6: PARTICIPANTS IN THE PROJECT (PDF-B)

LOCAL PARTNERSCommunities NGO's GO´s Others Colombia PPA Site Coordinators Acueductos veredales Rabanal (water users)

FEDENA CORPOCHIVOR/CORPOBOYACÁ

Indigenous Council of Chiles

CORPONARIÑO

Community of Fenicia CORANTIOQUIA Other site partners

Rabanal Association CVC University of Nariño Cabildo verde Belmira/Entreríos (environmental groups)

UAESPNN Gestores Ambientales Noroccidente de Antioquia

WWF Colombia CVC Foundación Trópico UAESPNN

Ecuador PPA Site CoordinatorsComuna La Esperanza (Carchi)

Fundación Altrópico Provincial Government of Carchi, parish of Tufiño

Zuleta Company and Annexes

Community of Zuleta Fundación Galo Plaza Lasso

Angochagua parish board

Mushuk Yuyay Project

Paramo communities of Pedro Moncayo-Mojanda (Pichincha)

Fundación Brethren & Unida

Municipality of Pedro Moncayo, parish boards

Community of Llangahua and nearby communities (Tungurahua)

GTZ-PROMACH Provincial Government of Tungurahua

Community El Salado de Jimbura (Loja)

Loja Paramo Working Group (ArcoIris, FundaTierra Loja Herbarium)

El Salado parish board

Other site partners WWF Colombia Municipality of

Tulcán Alliance of NGO of North Ecuador (Grupo Randi Randi, Jatun Sacha, EcoPar, TNC, Macrena, CI)

Provincial Government of Loja

Peru PPA Site Coordinators Community of San Juan of Cachiaco (Pacaipampa), Community of Samanga (Ayabaca)

Piura Paramo Working Group, IGCH

University of Piura

Communities of Shinshilpampa, Quinuapampa, Alto Chetilla, Jamcate, Cushunga, Carhuaquero, Chamis.

CIPDER, CEDEPAS ASPADERUC

Ayabaca Superior Technological Institute

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Other site partners CEPESER Municipality of

Pacaipampa (ODER),

Museum of Leymebamba

MIRHAS Provincial Municipality of Ayabaca

Wilder Jaramillo Hualpa

Pro Aves Regional Government of Piura

Research and Promotion for Development Institute

CARE Provincial Municipality of Cajamarca

Coordination of Jequetepeque watershed

ProNaturaleza Regional Government of Cajamarca

CIPCA IDEAS UGEL (Ministry of Education)

IRAGER

Venezuela PPA Site Coordinators Community of Gavidia, Community of Los Arenales, Community of El Pajarito

CEPDIF - Cooperative Valle Encantado, Centro de Capacitación e Investigación Participativa del Paramo (Paramo Center of Training and Participative Research), Caja rural (rural fund) of Pajarito (Tuñame)

Provincial and parish board - Tuñame

CINVIV-University of the Andes, Medicine Social-ULA, Institute of Environmental and Ecological Sciences -ULA

Other site partners PROINPA, ACAR, Association of Neighbors of Gavidia,

National Parks Institute –Mérida

Baqueanos Association, BRACOMLA Environmental Brigade, TATUY

Ministry of the Environment and Natural Resources -Mérida

Andes Program, Boconó Center of Ecology

National Institute of Agrarian Research -Mérida

PRODECOP Ministry of Agriculture and Land - Mérida

CONAPLAMED COORPOANDES, CORMETUR HIDROANDES TRUJILLO, AGUAS DE MÉRIDA Municipality of Rangel (Merida), Governorship of the Municipality Urdaneta (Trujillo)

NATIONAL PARTNERS NGO's GO´s Others

COLOMBIA Red de Reservas de la Sociedad Civil (private nature reserve network)

Ministry of Environment, Housing and Territorial Development

Andes Project - IAvH National University Javeriana University

ECUADOR CEDA Ministry of

Environment University of Cuenca - PROMAS

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Fundación Natura CAMAREN Catholic University - Herbarium QCA

FONAG FAN CBP Project-EcoCiencia

PERU UNIGECC Catamayo Chira Binational Project

CONAM (National Environment Council)

National Agrarian University of La MolinaSan Marcos National University

Adefor INRENA (Ministry of Agriculture)

Institute of Common Property

PRONAMACHS (Ministry of Agriculture)

WWF Perú Ministry of Education Conservation International

Ministry of Energy and Mining

Moore foundation CONACS (Ministry Agriculture)

VENEZUELA Fundación Tierraviva MARN (Vice-

ministry of Conservation, National Office of Biological Diversity)

CAM-Venezuela

Foundation BIOPARQUES

Ministry of Agriculture and Lands

Andean Development Corporation

Ministry of Science and Technology

GISGA. Economy Faculty, ULA.

Parks National Institute Focal point of RAMSAR´s high Andean wetland Strategy (MARN).

Laboratory of Rural Studies, IVIC.

INTERNATIONAL PARTNERS NGOs GOs Others

WWF CAN Researchers Team CI OTCA CIP Moore Foundation GTZ Basins SDC RAMSAR IUCN IADBWCS TNC

EXECUTION OF THE PROJECT NGO's Others

CONDESAN IAvH TMI ICAE EcoCiencia University of

Amsterdam University of Wisconsin

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PDF-B INTERNATIONAL CONSULTANTS NGO's OthersEcoPar Eloísa Trellez Ecodes Eugenia Ponce de

León Fundación Semillas de Agua

Esteban Suárez

Fundación Humedales PROMAS – University of Cuenca

Fundación Ambiente y Sociedad.

Participation of the IADB in PDF-B activities and Full Size Project

The joint interest of IADB and UNEP in Paramo conservation was reflected in the collaboration of both institutions during PDF-B. Following a memorandum of understanding signed on July 9 th

2003, both institutions jointly pursued the preparation of this full size project. IADB was active in providing technical support to CONDESAN in component 1 (Sustainable Management of Paramo and its areas of influence) and component 4 (Policy Development and Advocacy) of the PDF-B. UNEP complemented this work with technical support to CONDESAN in components 2 (Quantification of environmental goods and services), component 3 (research, training and capacity building) and component 5 (regional education and awareness raising). The result of this collaboration among CONDESAN, IADB and UNEP is the full size project presented to this DROC.

The participation of the IADB in PDF-B and project was originally viewed as important because the initial assumption was that field sites would need significantly baseline investments to support conservation activities. These baseline investments, it was assumed, could be financed through the credit arm of the IADB. In addition, the in-house expertise of the IADB on issues of rural development stood as a value added to project design and implementation.

The collaborative work performed by CONSESAN, IADB and UNEP found that the most promising field sites were not in need of baseline investments required for project success and of a magnitude that could justify official requests from government to the IADB for new rural development or rural infrastructure credits. Rather, the need for baseline investments can be met from the co-financing that accompanies this project.

For this reason, the IADB considered that co-executing the project with UNEP was not a necessary condition for the success of the project. However, the IADB indicated its interests in being kept up to date on overall advance of the project in general, and on lessons learned in sustainable use of Paramo resources in particular. The latter are of special interest because they could be applied to other sites as part of the replication component of the project, for example, in sites in which the participation of the IADB could facilitate baseline investments of a magnitude that require requests from governments for rural development credit. The project welcomed this suggestion and will include the IADB in the coordination and information sharing mechanisms supported by the FSP. In particular, the project will maintain close communication during the execution of the replication component (#5). At the same time, local implementing agencies in

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participating countries will regularly update IADB local offices on the main findings and results of the project.

In addition, the project has established partnerships with organizations with strong in-house technical expertise on rural development issues. This include NEA, CEDEPAS, Aspaderuc and the Mountain Institute (Peru), the latter a globally renown organization for rural development in mountain areas, the regional corporations (Colombia), Grupo Randi Randi and CAMAREN (Ecuador), and IVIC (Venezuela). At regional level, GTZ and CGIAB bring in expertise with rural development issues as do Condesan consortium members.

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ANNEX 11.7: INSTITUTIONAL RÉSUMÉS OF EXECUTING AGENCIES

CONDESAN -ANDESThe Consortium for the Sustainable Development of the Andean Ecoregion(CONDESAN) is an association of public and private sector partners working together on research, training and development, and policy initiatives promoting the protection of natural resources and improvements in the welfare and equity for the people of the Andes. Today, CONDESAN is a consortium of nearly 75 organizations actively working in the Andes of Venezuela, Colombia, Ecuador, Peru, Bolivia and Argentina. The membership is primarily made up of Latin American research and development organizations (NGOs), government agencies, producer groups, Andean Universities and National Research Institutes, but also includes European and North American Universities as well as several international centers (CIP, CIAT, ILRI, IWMI). CONDESAN’s research agenda covers the intersecting themes of sustainable natural resource management, improved rural incomes and social equity. To meet these objectives, the Consortium facilitates both research programs and benchmark integrated research/development programs. The former are developing much needed tools for improved natural resource management, participatory methodologies and productive technologies, while the latter are working at the frontier of increasing agricultural productivity, resource use, and community control. In almost all cases, the activities are multi-disciplinary, multi-institutional, and strive to develop a participatory agenda.Consortium members make alliances to define and undertake research and development projects. The hallmark of the benchmark teams is that they join good science and development expertise with community organizations. Other, more thematic teams draw together the best organizations regionally to address common issues. The major trans-Andean research activities fall into four categories:

Soil and water management and conservation; Conservation and use of agrobiodiversity in Andean roots and tubers and pasture species; Improved farming systems, covering all aspects of the system from producer to consumer; Policy research to promote sustainable development and conservation in the Andes.

Two companion themes that are part of the cross-Andean portfolio are developing human resources, and communications (INFOANDINA). In addition to conducting workshops, in the case of the former, CONDESAN is working to improve postgraduate in agricultural production and natural resource management. INFOANDINA is the Consortium’s information network with nearly 500 participants. It is focusing on improving communications between Consortium members, access to “gray literature”, and conducting forums on key development issues. INFOANDINA has organized three electronic conferences on the Paramo ecosystem, with over 300 participants (1997, 2000 and 2004).

INSTITUTO ALEXANDER VON HUMBOLDT - COLOMBIA The Institute of Biological Resources Research “Alexander von Humboldt” was created through Law 99 of 1993 and is part of the Colombian National Environmental System (SINA). The Institute is a non-profit civil corporation, subject to the rules of private law and linked to the Ministry of Environment, Housing and Territorial Development, with administrative autonomy, legal status and patrimony, organized according to law 29 of 1990 and Ordinance 393 of 1991. The Institute is in charge of carrying out basic and applied research on genetic resources of national flora and fauna, and of to develop the scientific inventory on biodiversity in the whole national territory. Law 99 of 1993 establishes that the Institute is responsible for the scientific and applied investigation of the biotic and hydrobiological resources continental territory of the nation. The Institute will support, through technical consultancies and technology transfer, the Regional Autonomous Corporations of Sustainable Development, the Departments, the Districts, the Municipalities and other territorial entities in charge of the administration of the environment and renewable natural resources. The investigations lead by the Institute and the associated data bank, will be the base for the development of the national

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biodiversity inventory. The Institute has the mission of promoting, coordinating and executing research that contributes to the conservation and sustainable use of the Colombian biodiversity. Given the Colombian biophysical complexity, the Institute has approached the execution of its mission concentrating on certain fields of knowledge and certain regions. The institute’s research lines comprise four programs: Conservation Biology, Use and Valuation of the Biodiversity, Inventories of Biodiversity, and Politics and Legislation. In their first years of existence, research concentrated on the dry ecosystems; then, the oriental mountain ecosystems were studied, and from 2001 on, the investigation of the Institute has concentrated on the Andes and the Orinoquia. This recent experience has allowed Institute researchers to come closer to the problem of biodiversity knowledge and of the conservation of the high mountain ecosystems through biodiversity characterizations and the study of the factors of its transformation, such as agriculture and mining.

ECOCIENCIA - ECUADORThe Ecuadorian Foundation of Ecological Studies, EcoCiencia, was founded in 1989 by a group of Catholic University biologists fresh from graduate studies in the US. Its aim was to contribute to the conservation of biodiversity from an ecological and research-oriented perspective. This perspective, albeit still much present, has been complemented by political, economic and social points of view and thus nowadays EcoCiencia can claim a holistic perspective towards the conservation of Ecuador's remarkable biological diversity.EcoCiencia, in its 15 years of existence, has worked in several main themes that include ecological and biological research, natural resources management, environmental policies, economic valuation of biodiversity, environmental education, training and interpretation, and biodiversity information managing. Funding generally comes from international sources and has included donors such as the Dutch Government, USAID, the British Government, the MacArthur Foundation and GEF.The foundation has its headquarters in Quito but works in the whole territory of Ecuador, including the Galapagos. Its involvement with the Paramo ecosystem dates to the first years of its existence but became consolidated in 1996 with the one-year Dutch Government funded project "Perspectives for the Conservation of Paramos in Ecuador"; in collaboration with the Mountain Institute's Andean office. From this experience, among other things a close link with the University of Amsterdam began that resulted in another Dutch Government funded "Proyecto Paramo" (also with the Mountain Institute), which lasted from 1998 to 2001 and produced several participatory management plans in thirteen Paramo pilot sites along the Andean region, an Action Plan for the Ministry of the Environment, an ecological zoning of the ecosystem, a complete data- base and several publications. This project can be seen as the Ecuadorian seed for the Andean Paramo Project that united similar efforts from Venezuela, Colombia and Peru and is currently finishing a PDF-B phase funded by GEF. EcoCiencia also coordinates the National Paramo Working Group in Ecuador, which brings together approx. 120 institutions from governmental, non-governmental, private and community sectors in an information-exchange and discussion platform that gathers tri-monthly around a selected issue (gender, infrastructure, ecological services and products, policies, forestation, biodiversity, community projects, culture, etc.). These meetings are published through a quarterly publication currently in its 16th installment. Currently its funding comes from the Dutch Government and formerly included resources from the Netherlands Committee for IUCN.

THE MOUNTAIN INSTITUTE - ANDEAN PROGRAM, PERÚThe Mountain Institute (TMI) is an organization founded on 1972 and executes conservation and development projects in Nepal, Tibet, India, the Andes and the United States. The Andean Program was established in Peru in 1995. With the purpose of obtaining a sustainable future for mountains of the world and their communities, the mission of the Andean Program is to preserve mountain environments, to improve mountain livelihoods and to support mountain cultures. TMI´s vision is to contribute to a world in

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which the mountains and their towns are valued and understood like vital and integral elements of the ecosystems of the world and their populations, to contribute to a world in which the mountain communities prosper ecologically in healthy atmospheres. The basis of TMI's Andean Program in Perú is the city of Huaraz, with a small connection office in Lima. From Huaráz, TMI developes cooperative links with experiences and mountain organizations of the country, the Andean region and the world. The Andean Program executed projects to support communities, in coordination with the National Institute of Natural Resources (INRENA) and a set of other governmental and non governmental partners. The Andean Program has three major components (1) Huascarán and Huayhuash Biosphere Reserve (2) Natural High Altitude Grassland Ecosystem (Paramo, Punas, Jallqas) and (3) Private Company, Community and Conservation.Among the specific technical capacities of the Andean Program we can mention:

Development, validation and publication of participatory methodologies for the planning and design of development integrated conservation projects for the zoning of protected areas, the design of site plans, the participatory elaboration of maps, the territorial code and the design of routes. Use of conflict management methodologies in areas with mining influence.

Strengthening environmental education in local elementary schools in protected areas. Manuals for community based tourism and for range management. Guides for the identification of wild plants and wild forage species Development of cooperative alliances at regional scales (coordination of groups) and access to

diverse international support networks in conservation and sustainable mountain development matters.

GIS and mountain data bases. Landscape change studies with repeated photography. Low cost range management technologies. Staff Languages: Spanish, Quechua, English.

The Andean program has, among others, coordinated the implementation of the management plan for the Huascarán National Park - World Heritage Area, has successfully implemented a conservation project associated with high country gold mines and has been a co-executor of the Dutch funded Proyecto Paramo in Ecuador.

INSTITUTO DE CIENCIAS AMBIENTALES Y ECOLOGICAS - UNIVERSIDAD DE LOS ANDES, VENEZUELA

In 1969, ULA formalized vegetation ecology research by founding of the "Vegetation ecology research group” within the School of Sciences. This was the base for the establishment of the Center for Tropical Andes Ecological Research in 1985. In 1997, the National Council of Universities endorsed the transformation of this center into the “Institute of Environmental and Ecological Sciences” (ICAE). Throughout three decades, it has developed an intense and fruitful scientific activity on different aspects of Neotropical ecology, including the development of qualified human resources. This last activity was consolidated in the Tropical Ecology Graduate Program (Master 1981 and Doctorate 1987), in which 75 professionals from different countries including Spain and Latin America have graduated, presently dedicated to scientific research and university level teaching in Ecology. During its entire trajectory, the ICAE has been characterized by three essential aspects: 1. The execution of basic ecology projects, oriented towards the resolution of regionally important problems with environmental and social repercussions, integrated in several research lines, with emphasis on Andean environmental problems, tropical and subtropical ecosystems’ functioning, biodiversity conservation and the effect of global changes on these ecosystems. 2. An important scientific production materialized in 175 articles in specialized magazines and 10 books as well as 79 chapters in books, besides the active participation of researchers in congresses, simposia and other scientific meetings of national and international character (more than 460 presentations). 3. Development of programs of international cooperation with institutions of several countries. At the moment, ICAE maintains cooperation projects with the Biodiversity Nets CYTED (Grasslands and

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Mountains), IAI and the European Union, besides projects financed by CDCHT-ULA, FONACIT, which are developed by 15 ICAE researchers, 4 associate investigators, 5 technicians and two secretaries. Including thesis students and visiting researchers, some 40 people work at the institute. As results of its 35-year research, the ICAE has become one of the worldwide references on the knowledge about the Paramo ecosystem, with special emphasis on aspects related to biodiversity and functioning, adaptations that allow plants to be successful in the conditions of the cold tropic, restoration dynamics and regeneration of the Paramo, and analysis of the ecological bases for the most important strategies of human management (agriculture and cattle raising).

THE INSTITUTE FOR BIODIVERSITY AND ECOSYSTEM DYNAMICS - UNIVERSITY OF AMSTERDAM THE NETHERLANDS

The University of Amsterdam (UvA) has a relatively long academic history in the Andean countries. It is a non-Andean academic institution with a long trajectory in investigation on biodiversity and ecology. Through the Schools of Biology and Geography (now united in the Institute of Biodiversity and Ecosystem Dynamics, IBED), UvA researchers have executed investigations in Paramos in Colombia since the 1950s. One of the larger programs in this country is EcoAndes, for the Andean region. In this program the emphasis was on fundamental and applied investigation, with the collaboration of national institutions and university students. From the experience in Colombia, the University widened its investigation activities and institutional collaboration with national institutions of other Andean and Central American countries. In the 1980s there was a lot of collaboration with Venezuela (Universidad de Los Andes) and then with Mexico (UNAM, EcoSur) and Costa Rica (National University, InBio). From 1996 on, investigators of the already formed IBED began investigation projects in Ecuador. In the last years, IBED-UvA has been an important actor in conservation efforts of Ecuador since it was the administrator of the Paramo Project, executed with EcoCiencia and the Mountain Institute, and financed by the Royal Dutch Embassy. Besides the volume of knowledge generated on the diversity, operation and management of ecosystems, a large number of secondary results were achieved in relation to professional education and institutional strengthening. In total, more than a hundred students from Colombia, Mexico, Venezuela, Ecuador, Costa Rica and Brazil have been trained. Recently, in the field of research IBED is developing a long term program (a proposal to the Netherlands Science Organization; NWO) on the dynamics of Andean forests that includes natural processes (diversity, evolutionary history) as well as anthropic processes (deforestation, climatic change, use). In the field of institutional collaboration and the education, IBED is executing a Master Degree program in tropical ecology in Ecuador, Colombia and The Netherlands that will mainly benefit students of Andean countries.

UNIVERSITY OF WISCONSIN - UNITES STATES OF AMERICATwo of the University of Wisconsin’s 22 colleges, the Faculty of Letters and Sciences and the Faculty of Agriculture and Life Sciences are particularly engaged in research and teaching relevant to the Proyecto Paramo Andino. The former is focused on issues of biodiversity conservation and plant botany as well as the economic and political issues that surround good governance while the latter is working on improved agricultural systems based on small grains, potatoes, vegetables and forages as well as dairy production. In addition both faculties conduct a great deal of watershed management work . Also the University is the home of several specialized institutes that are engaged with the project. These include the Institute for Environmental Studies, the Land Tenure Center and the Center for Sustainability and the Global Environment.

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ANNEX 11.8: MAP OF PARAMO AREAS

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Tuñame

Chiles

Mojanda-Zuleta

Llangahua

Cajamarca

Loja-Piura

Gavidia

El Duende

RabanalBelmira

Legend

Paramo areaPrincipal citiesProject Intervention Sites

Distribution of Paramo in the Northern Andes; Project Intervention Sites of Proyecto Paramo Andino

ANNEX 11.9: MAIN OUTCOMES OF PDF-B

During the PDF-B phase of the project, studies were undertaken to identify the present situation of the different themes related to Paramo in which the project will intervene. The project executing agencies, in collaboration with local and national organizations and independent consultants analyzed the state of knowledge, the present offer and demand for policies, training, communication and investigation. An inventory and analysis was undertaken to productive activities with low impact. In all project intervention sites, participatory plans of action were designed by the executing agencies in collaboration with local NGOs. All these documents form the basis for the design of the full size project proposal and the activities to be executed during its life span.

Policy development and advocacy International and Andean policies that impact the Paramo ecosystem (Eugenia Ponce de León). Integration of national and international policies on Paramo and a proposal for the execution phase

of the project (Eugenia Ponce de León). Analysis of policy and legal instruments that impact the Paramo ecosystem in Colombia (Henry

Salazar, IAvH). Document on the analysis of policies on Paramo in Ecuador (Carla Cárdenas, CEDA). Strategy for the policy component in Perú (Ludgerio Abanto, Cedepas). Policies for the conservation and sustainable development of the Venezuelan Paramo (Eliézer

Arias, Freddy Matos,Luis Llambi; IVIC).

Training and Capacity Building Proposal for capacity building, Proyecto Paramo Andino (Eloisa Trellez). Bases for an interdisciplinary training program directed to people that work in the Paramos of

Colombia (María José Durán). Analysis of demand and offer of training in Paramos of Venezuela (GISAGA, ULA). Analysis of demand and offer of training in Paramos of Ecuador (Rodrigo Chontasi, Eloy Alfaro;

CAMAREN). Evaluation of the training demand in Peruvian Paramos (Ricardo Pineda, CEPESER).

Education y comunication Regional strategy for environmental education and communication on the biodiversity of the

Andean Paramo (Eloisa Trellez). Strategy for education and environmental communication for the conservation of the Colombian

Paramos (Pedro Quijano). Proposal of Ecuador for the program of environmental education and awareness rising (Patricio

Crespo). Strategy for environmental education and consciousness building at the level of Peruvian Paramos

(Baudilio Valladolid Catpo, Oscar Infante Reque, CEPESER) Proposal for environmental education and public dissemination for the conservation of the

Paramos of Venezuela (Bioparques-Tierra Viva). Investigation

Proposal for investigation of the Proyecto Paramo Andino (Esteban Suarez). Memories of the workshop on gaps and necessities for investigation in Andean Paramo (Cali-

Colombia; Esteban Suarez).

Low-impact land-use practices in Paramos

Evaluation of best practices in water management in the Paramos of the Andes (PROMAS).

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Catalogue of practices in mining with low impact for the conservation of Paramo (Fundación Ambiente y Sociedad).

Catalogue of forestry experiences with less impact on Andean Paramos (Ecopar-ECODES). Evaluation of best practices in biodiversity use in the Paramos of the Andes (Fundación

Humedales). Practices in agriculture and animal husbandry of low impact with low impact for the conservation

of Paramo (Fundación Semillas de Agua).

Sustainable Management of the Paramo and its Areas of Influence.Participatory plans of action for Gavidia, Tuñame (Venezuela); Rabanal, Belmira, El Duende (Colombia), Chiles (Colombia-Ecuador border), Zuleta-Mojanda, Llangahua (Ecuador) Loja-Piura (Ecuador-Perú border); Cajamarca, Perú. (local communities, site coordination organizations and national executing agencies)

Full Size Project Brief for presentation to GEFSEC and UNEP/DGEF.

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Documents

ANNEX 1: LOGICAL FRAMEWORK MATRIX · Web viewDespite environmentally unfriendly practices, such as slash and burning, cattle overgrazing and felling (by Ecuadorian Word traders),