PROJECT IDENTIFICATION FORM (PIF) PROJECT TYPE: FULL SIZED PROJECT THE GEF TRUST FUND Submission Date: 7 April 2009 Resubmission date: 16 April 2009 PART I: PROJECT IDENTIFICATION INDICATIVE CALENDAR* GEF PROJECT ID1: PROJECT DURATION: 60 months Milestones Expected Dates GEF AGENCY PROJECT ID: 3253 mm/dd/yyyy COUNTRY: Tanzania Work Program (for FSP) TBD PROJECT TITLE: Strengthening the Protected Area Network in CEO Endorsement/Approval Dec 2010 Southern Tanzania: Improving the Effectiveness of National Parks in Agency Approval Date Feb 2011 Addressing Threats to Biodiversity Implementation Start Mar 2011 GEF AGENCY: UNDP Mid-term Evaluation (if Sep 2013 OTHER EXECUTING PARTNER: Tanzania National Parks planned) (TANAPA), Ministry of Natural Resources and Tourism, Tanzania Project Closing Date Mar 2016 GEF FOCAL AREA: Biodiversity GEF-4 STRATEGIC PROGRAM(s): BD-SP3-Strengthening Terrestrial PA Systems PARENT PROGRAM/UMBRELLA PROJECT (if applicable): NA A. PROJECT FRAMEWORK Project Objective: The biodiversity of Southern Tanzania is better represented and buffered from threat within National Parks. Project Expected Outcomes Components Integrating TA A working model for management integrating management of of NPs and NPs and wider production broader landscapes is piloted and landscapes in adapted in 7 Districts in Southern Southern Tanzania and Tanzania secures wildlife corridors and dispersal areas covering over 30,000 km2 in the Ruaha–Usangu-Kipengere and Kitulo– Livingstone ecological landscapes PAs expanded to encompass ecologically sensitive areas adjacent to Kitulo NP (Mt Rungwe) and Ruaha NP (Usangu Game Reserve), totalling over 10,000 km 2 over baseline of 10,712 km2. No net loss of natural habitat in major habitat blocks identified as critical for wildlife dispersal and at least 40% reduction in hunting pressures in these blocks (baseline to be determined during project preparation). Integrated landscape management approach is replicated by TANAPA in at least one additional ecological landscape in southern Tanzania. 1 Expected Outputs Inter-sectoral District land management coordination mechanism is emplaced in the Ruaha–Usangu-Kipengere- Kitulo– Livingstone landscapes of Southern Tanzania, to ensure that biodiversity management in National Parks, and wildlife migration corridors and dispersal areas is factored into decisionmaking governing land use management. GEF Co-financing ($) % ($) % 775,000 16 4,150,000 84 Total 4,925,000 Tanzanian National Parks Authority (TANAPA) and 7 pilot District Authorities plan, implement, and monitor biodiversity management measures (systematic conservation plan defines wildlife corridors and dispersal areas, EIA and impact management stipulations in place to avoid and/ or mitigate development impacts in sensitive areas, monitoring and reporting systems are in place, and enforcement measures are operational). Kitulo NP is finally gazetted, with Parliamentary approval secured. For both Kitulo and Ruaha NPs, boundaries for PA extensions are demarcated, public consultations are completed and management plans are prepared, taking into account the outcomes for both. TANAPA has a staffed community extension services to ensure effective engagement between communities and park authorities and dispute resolution. TANAPA has the competence and staff skills to lead land use planning, management and monitoring in landscapes; to assess hydrological Project ID number will be assigned by GEFSEC . PIF PAF Tanzania National Parks 1 Project Objective: The biodiversity of Southern Tanzania is better represented and buffered from threat within National Parks. Project Components Expected Outcomes Expected Outputs GEF ($) % Co-financing ($) % Total dynamics, make predictions of climate change trends and gauge long term impacts on biodiversity conservation. Operations TA Core NP operations Support for INV strengthened in Southern NP Tanzania covering over Management 33,000 km2 leading to the in Southern effective detection and Tanzania deterrence of poaching and fire risks. This is evidenced in a reduction in poaching activity, retaliatory wildfires set by poachers, and grazing of cattle where proscribed. Systematic staff training programme 4,000,000 39 6,200,000 61 covering all aspects of PA operations ensures 300 rangers and other field staff meet necessary competencies for planning, administration, conflict resolution, policing and enforcement). 10,200,000 Funds, human resources and equipment (surveillance equipment, ranger uniforms and provisions, firefighting equipment) are provided and deployed to address threats to NPs in a cost effective manner. [Business plans set cost co efficients for all prescribed PA functions and rolling operations plans define site management priorities.] Management Effectiveness Score for NPs in Southern Tanzania increased over the baseline score by at least 40%. (baseline to be determined during project preparation). Stable populations of indicator species including predators (lion, wild dog) and ungulates (Elephant, Buffalo and Sable antelope). A joint (TANAPA-Community-DistrictPrivate Sector) stakeholder group formed to address overall management issues in NPs and adjacent Village Wildlife Management Areas is established (committee formed, joint management plan developed, and joint enforcement systems emplaced using the Management Orientated Management System(MOMS) in Ruaha NP (covering a total area of 25,000 km2). A sustainable finance plan is developed approved and implemented for the NP system. Business Planning is mandated for all NPs, along approved best practice guidelines Together, these define management costs for different NP sites, provides accurate revenue forecasts (from gate fees, concessions, film rights and other permissible uses to private sector investments), and matches revenue to priority management needs. Project management Total 529,550 31 1,150,000 69 1,679,550 5,304,550 31 11,500,000 69 16,804,550 B. INDICATIVE CO-FINANCING FOR THE PROJECT BY SOURCE if available, ($) Sources of Co-financing Project Government Contribution GEF Agency(ies) Bilateral Aid Agencies Multilateral Agencies NGOs Total Co-financing PIF PAF Tanzania National Parks Type of Co-financing Cash from TANAPA In Kind Support from District Administrations and Forestry and Beekeeping Division Cash from UNDP Amount 11, 000,000 500,000 11,500,000 2 C. INDICATIVE FINANCING PLAN SUMMARY FOR THE PROJECT ($) Project Preparation Amount GEF financing Co-financing 0 0 0 Total Project (b) 5,304,550 11,500,000 16,804,550 Total * c=a+b 5,304,550 11,500,000 16,804,550 Agency Fee 530,455 530,455 *The GoT will request a GEF PPG amount of US$ 149,995 for Project preparation. D. GEF RESOURCES REQUESTED BY AGENCY (IES), FOCAL AREA(S) AND COUNTRY(IES) NA PART II: PROJECT JUSTIFICATION A. STATE THE ISSUE, HOW THE PROJECT SEEKS TO ADDRESS IT, AND THE EXPECTED GLOBAL ENVIRONMENTAL BENEFITS TO BE DELIVERED: 1) Tanzania is a major repository of globally significant biodiversity, ranking amongst the top countries in tropical Africa in terms of the distinct eco-regions represented, and in species richness / species endemism. Tanzania lies at the meeting point of six major bio-geographic zones (the dry Somali-Masai, the Soudanian savannas, the Zambezian woodlands, the Guinea-Congolian forest, the coastal forest mosaic and the scattered afro-montane / afroalpine areas). Well over thirty major vegetation communities are recognized – housing more than 11,000 plant species, with >15% endemism. The species inventory includes 300+ mammal species, over 1100 species of birds, one of the largest avi-faunas in Africa, with 56 species of global conservation concern, and over 360 species of herpetofauna, of which 99 species are endemic. Tanzania contains three areas designated by Conservation International as Global Biodiversity Hotpots (Eastern Afro-montane forests, the Coastal Forests, and the southern reaches of the Albertine Rift Forests to the far west), as well as eight WWF Critical Eco-Regions. These are the Albertine Rift Montane Forest; Kenya-Tanzania Montane Forest; Eastern Arc Forest; Southern Rift Forest / Grassland mosaic; Coastal Forest Mosaic; Guinea-Congolian Forest Mosaic; Acacia Savanna and Miombo Woodland. The Miombo woodlands and Acacia Savanna of Tanzania constitute huge wilderness areas that support some of the largest assemblages of large mammals in the World, including large herbivores (e.g. elephant, hippo, giraffe, buffalo); migratory plains game (e.g. zebra, wildebeest, gazelle); and large predators (African wild dog, lions, leopards, cheetahs and two species of hyena).The country is also a major staging post and destination for avifauna migrating south during the boreal winter. 2) The high turnover of biodiversity across the landscape presents a challenge to conservation managers, as it means large areas need to be managed so as to conserve a bio-geographically representative sample of biodiversity. Protected Areas (PAs) provide the principal means for protecting the country’s biodiversity values. The PA network is amongst the largest in Africa, covering 27% of the land area (almost 250,000 km2), and consists of 651 sites. There are several categories of PA, which operate under different institutional arrangements. These are (in declining order of conservation standing): National Parks, Forest Nature Reserves, Game Reserves, Forest Reserves, the Ngorongoro Conservation Area and Wildlife Management Areas. The national PA system includes 15 National Parks, 33 Game Reserves, the NgoroNgoro Conservation Area, and over 600 Forest Reserves. These totals exclude Wildlife Management Areas, Village Land Forest Reserves and Game Controlled Areas, most of which are on village land and serve to regulate sustainable natural resource use, but also can act as corridors and dispersal areas for wildlife. 3) The Tanzania National Parks Authority (TANAPA) is responsible for managing the network of National Parks. National Parks2 provide the highest conservation standing of all the protected area categories. They are created through an Act of Parliament, and require an act of parliament to be degazetted, which is difficult to secure. Other PA categories allow the Minister to degazette areas via simple notification of parliament. Moreover, National Parks permit no extractive use, unlike other PA categories. As National Parks have higher inherent opportunity costs than other PA categories, they are likely only ever to cover a small part of the PA estate (currently NPs cover 19% of the PA estate or 46,523 km2). However, the security they afford means that they provide an important safety net for biodiversity. Table 1 below provides an overview of the NPs. These are sub divided into categories: the Northern Circuit in northern Tanzania, and the less known Southern Circuit (22,069 km2) in the Country’s South, which consists of 7 sites, several of which have been established within the last decade, and is important in terms of its bio-geographic representation. 2 Registered on the WDPA as IUCN Category II PAs. PIF PAF Tanzania National Parks 3 NP Northern Circuit Arusha Kilimanjaro Lake Manyara Mkomazi Saadani Rubondo Island Serengeti Saanane Tarangire Southern Circuit Gombe Katavi Kitulo Mountains Mahale Mountains Mikumi Ruaha Udzungwa Established Area Ecoregion 1960 1973 1960 2008 2005 1977 1951 Proposed 1970 552 sq km 1668 sq km 330 sq km 3,245 sq km 1,100 sq km 457 sq km 14,763 sq km 500m2 2850 sq km Afro Montane Forest Afro Montane Forest Acacia Commiphora Woodlands / Lakes Acacia Commiphora Woodlands Coastal Woodlands Equatorial Rainforest / Lake Victoria Savannah Grassland and Acacia Commiphora Woodlands Savannah Woodland Mosaic Acacia Commiphora Woodlands 1968 1974 2005 1980 1964 1964 1992 52 sq km 4,471 sq km 465 sq km 1,613 sq km 3,230 sq km 20,300 sq km 1,990 sq km Albertine Rift Forests and Grasslands Western Miombo Woodlands Southern Rift Forests and Grasslands Albertine Rift Forests and Grasslands Eastern Miombo Woodlands Miombo Woodland/ Acacia Commiphora Woodlands ecotone Eastern Arc Mountain Forests and grasslands 4) The National Parks System is underpinned by strong policy and legislation, codified in the National Parks Ordinance. This was enacted in 1951, but underwent a major revision in 1959. TANAPA operates as an independent parastatal, and is allowed to retain funds earned from Park fees although it is required to pay income taxes to the Treasury. National Parks in the northern circuit, including the Serengeti, Arusha and Mt Kilimanjaro NPs tend to be effectively managed. Finally, the Northern Circuit is a source of considerable tourism income to the country. The resulting national economic benefits have meant that NPs have consistently had a high place on the national policy agenda. 5) Despite these many positive fundamentals, the National Park estate still suffers from some shortcomings: NPs are not wholly representative of the characteristically complex biodiversity patterns in Tanzania. The Government is seeking to expand (gazette new areas) NPs and upgrade (to higher categories) other PA categories to NPs, so as to improve bio-geographic coverage and conservation impact. In furtherance of this policy, the Government has recently gazetted three new national parks covering inadequately represented ecosystems, and is in the process of expanding three more. Expansion of the NP system is required in order to improve bio-geographic coverage (gaps include swamp systems, montane grasslands, lakes, and some forest types). Although National Parks are relatively more effective than other PA categories at buffering biodiversity from threats, they are not immune from threats such as poaching. Tanzanian national parks are not fenced, unlike parks in Southern Africa, which is one reason why they support large wildlife numbers; wildlife tends to disperse during the wet season. However, migration corridors and dispersal areas are being settled and farmed. This is leading to increasing human wildlife conflict, to the detriment of wildlife; in some cases numbers have declined drastically. Unplanned conversion of forest, woodland and wetland to both temporary (shifting cultivation) and permanent agriculture is a major problem in some areas. Such conversion cuts movement corridors, reduces dispersal areas, annexes dry-season water points, and reduces viable animal population sizes. With annual rural population growth of 2.5%, and substantial rural poverty, these pressures are likely to intensify. Climate change and economic depression will exacerbate such pressures. Moreover, new economic opportunities, such as the development of a biofuels industry could lead to mass future land use conversion of natural habitat in certain sensitive landscapes to tree plantations, particularly in wetter parts of Southern Tanzania. Some Parks are long established, Serengeti NP is over 50 years old; many others are new, and lack effective management. A number of recent assessments have shown that the pressures facing NPs can be countered through effective management. This is a need to improve management in several NPs in the Southern Circuit. There is an almost total dependence on external tourist arrivals for NP financing; and the dependence on two older, well established NPs on the northern Tourist circuit for some 75% of all revenues, the newer emerging parks have very limited tourist inputs, and their revenues do not cover costs (see details in tables below). This proposal aims to increase the effectiveness of the National Parks in protecting biodiversity and provide for the long-term ecological, social and financial sustainability of that system. The focus will be on the new and developing southern Tanzania National Parks. The long term solution underpinning the application is to build the management PIF PAF Tanzania National Parks 4 effectiveness of these PAs, to reduce anthropogenic pressures on the sites and secure biodiversity status within them. The project will develop capacity to apply, sustain and replicate innovative management practices across this estate. 6) Two major barriers are currently impeding the attainment of the long term solution: Integration of PA and Landscape Level Management: With the exception of the Greater Serengeti Ecosystem, National Parks are currently being managed in isolation to the landscapes in which they are located. There is a need to nest NP management in broader landscape level planning and management, encompassing “buffer zone” Game / Forest Reserves and village based conservation areas as well as production areas used for agriculture or forestry. The management system needs to be geared to maintaining vital corridors and wildlife dispersal areas. While the Government recognizes the need for this, action has been hampered by the fact that the country has a complex administrative system. The Central Government is responsible for establishing policy and ensuring its effective implementation. Responsibilities for land use planning and management lie with District administrations. However, these authorities have very limited capacity to integrate biodiversity management into their work, and lack the scientific and socio-economic data needed to establish tradeoffs between conservation and economic imperatives. Thus contra-conservation investments in agriculture or other land uses may be sanctioned, even where wildlife has significant economic potential. Moreover, the capacity of Districts to regulate unplanned land conversion is weak. This problem is compounded by inefficient integration of policing activities undertaken by different enforcement units, for example TANAPA and the Police. A capacity deficit for integrated landscape management is also evident within TANAPA itself. The complex institutional base, with several different agencies involved, requires careful definition of roles and mandates within functional partnerships. Effective landscape planning will require negotiation and conflict resolution, along with solid data sets for decision making and further development of institutional competencies. Many National Parks have adjacent Protected Areas, such as forest reserves, or wildlife management areas, which are not, however, managed by TANAPA. Nature Reserves and critical national Forest Reserves are managed by the Forestry and Beekeeping Division of the Ministry of Natural Resources and Tourism, many other Forest Reserves fall under District Administrations, while Wildlife Management Areas are managed by the Wildlife Division. In practice coordination of management between these entities tends to be weak at the site level. Nevertheless, such coordination will be critical to ensure the long term sustainability of National Parks, as uncoordinated management in these areas simply serves to undermine biodiversity status within the National parks – particularly in some of the smaller sites. One option is to reconfigure NP boundaries, in order to encompass ecologically sensitive areas. This is complicated by the fact that there has been no comprehensive overview of PA representation gaps within the past two decades3. The savanna and woodland ecosystems are relatively well represented in the PA network, in part because they harbour large wildlife assemblages that are a draw-card for the economically important tourism industry. The northern mountains and mountain forests are included in the Park network, but the forests, grasslands and wetlands of southern Tanzania have a less complete coverage. Although many Forest Reserves were established, most were created to provide forest products and, unlike National Parks, do not serve an overarching biodiversity conservation purpose. Protected Area Operations: TANAPA maintains a staff presence in all its National Parks, with a total staff complement of about 1700. Although staff are trained, there are a limited number of specialists. The Northern Circuit has seen significant investment in PA infrastructure and equipment, with funds ploughed back from tourism receipts. However, with the exception of Katavi NP, which has received funding from the Government of Germany, Mahale Mountains, which has received funding from the EU and several NGOs, including the Frankfurt Zoological Society, the Southern circuit has received limited funding and operational support. There is a need to expand operations to cover new areas that the Government plans to incorporate into the NP estate, and to provide for boundary notification, patrol equipment and other essentials, needed for effective policing and enforcement. Although all National Parks, except Mkomazi and Ruaha, have Management Plans, there is a need to complement these with Business Plans, which define the cost coefficients for different PA functions, defines revenue options, and ensure that scarce funds are utilized optimally and are integrated into TANAPA’s overall business model. There is a need to establish partnerships with tourism operators and other private sector actors, to support certain aspects of PA management. Finally, community interests are still not adequately catered for in NP management, although TANAPA’s experience with community conservation and the new land-use categories of wildlife management areas and village forest reserves provide modalities for community inputs to conservation. Where communities have been excluded from PA management, and as a consequence, where their livelihood needs have been ignored, majority perceptions remain that PAs generate few benefits but impose high costs. While policies to work with communities are codified in national legislation, improved mechanisms to operationalize and test these policies are still needed, as are experiences by which to inform its wider constituency. At the national level there is still some lack of commitment towards conservation approaches involving local communities. Existing legislation is not sufficiently understood by 3 Past detailed analyses include H Lamprey in 1975, TFAP in the 1980s, PAWM in 1994/5. PIF PAF Tanzania National Parks 5 government officials on-the-ground and by local communities, leading to inconsistent implementation. Trust between communities, powerful local resource users and government-authorities is often limited and needs to be improved. Until late 2008, Tanzania’s National Parks Authority had undergone over ten year’s growth in revenues, of which 98% came from tourism activities. The 2006/2007 annual financial report showed an income of 69 billion T Shs, (57.5million $ at 2008 rates). This was 69% over 2005/6 figures, and three times that of 2002/03. However, there is a huge revenue earning differential between parks. From the 14 parks documented in the 2006/7annual financial statement, two parks (Kilimanjaro 42 % and Serengeti 33 %) raised over 75% of all revenue. The 7 southern parks between them raised <1.5 % of all revenue. Whilst southern Park revenues increased from /06 to 07, this was minor, and in ratios was less than the pattern of increase in the north. Currently, TANAPA covers its costs through the cross subsidization of operations in PAs with limited income from PAs such as the Serengeti and Kilimanjaro NP, which run at a surplus. However, the income received covers direct costs estimated at 50 billion shillings; it not sufficient to fully cover the costs of managing the Southern Circuit. There is a need to increase the income earning potential of the Southern Circuit, through promotion of tourism or other means, while also ensuring that operations are moulded to ensure cost effectiveness and are prioritised to maximise threat abatement, per dollar invested. This will improve the efficacy of the existing budgetary cross subsidisation scheme between the Northern NPs and the Southern Circuit. 7) The project has been designed to address the afore-mentioned barriers through two complementary components. Interventions will focus on the Southern Tanzanian Circuit, reflecting the fact that with some exceptions, the management effectiveness of NPs in this region remains sub-optimal, relative to the Government’s desired levels. Integrating Management of NPs and Broader Landscapes: The project will develop a working model for integrating management of NPs with surrounding PAs or production lands in wildlife corridors and dispersal areas. Activities will focus on two landscapes straddling 7 districts, namely the Greater Ruaha landscape and the Kitulo- Livingstone Landscape (see map in Annex 1). These areas have been selected based on the following criteria: (1) Biodiversity Significance; (2) Management Need; (3) Management Opportunity; and (4) Government Priority—both areas form part of the economically important Rufiji River Catchment. The project will set up inter-sectoral district land administration mechanisms and develop land use plans; to ensure that land in ecologically sensitive areas is allocated to conservation compatible land uses. Development impact assessments will be undertaken, to define acceptable land uses and management practices. Support will be rendered to strengthen the enforcement framework, to ensure compliance and guard against chaotic, un planned economic development, which is leading to habitat degradation and loss elsewhere in Tanzania. This effort will also seek to ensure that conservation activities within National parks that lead to avoided GHG emissions or carbon sequestration are accounted for in the National Framework for REDD (Reduced Emissions from Deforestation and Degradation). The most critically sensitive areas from an ecological perspective will be gazetted as extensions to the two NPs in the target landscapes: Ruaha NP and Kitulo NP. This will bring in the region of 10,000 km2 into the NP estate, and in the case of Ruaha, ensure that a vital wet season wildlife dispersal area in the Usangu Game Management Area receives effective protection, and in the case of Kitulo, will expand NP coverage in the under-represented montane grassland biome. Results will be evaluated against control areas, where there is no such intervention and good practices distilled for replication elsewhere in Tanzania. Strengthening NP Operations: Component 1 will reduce the externalities imposed on National Parks from threats outside NP boundaries. Component 2 will address threats within the NP boundaries by engineering the delivery of an integrated package of PA management functions. Based on a needs assessment to be undertaken during further preparation, the project will provide funding for basic infrastructure and field equipment across the Southern Circuit Sites. An emphasis will be placed on building operations capacity at PA sites that have not previously benefitted from such investment (i.e. Ruaha/ Kitulo NPs). This support will be accompanied by the development of business plans for the sites, to define the optimum operations support needed to address threats in a cost effective and sustainable manner. A systematic staff training program will be supported, geared to meeting staff competency needs. Finally, at the national Systems level, the Project will assist TANAPA to develop a sustainable financing plan. This will provide guidelines and norms for site based business planning, provide accurate revenue forecasts, expand income opportunities (by developing new tourism products in NPs, particularly in the Southern Circuit, letting tourism concessions in the Southern Circuit, promoting domestic tourism, and seeking investment funds from energy utilities that benefit from PA management4), with a view to tapping the potential financial returns from the Southern Circuit. 8) The two landscapes that will be the subject of intervention under the project are both important storehouses of biodiversity, the status of which will be secured through Component 1. The Kitulo-Livingstone area comprises Tanzania’s largest montane grassland community. This area is a repository of floristic diversity, with high diversity found in the orchids, but also harbors red-hot poker, aloes, proteas, geraniums, giant lobelias, lilies and aster daisies. Southern Tanzania is the country’s major watershed; the Rufiji River has its headwaters in the Livingstone Mountains, and passes through Ruaha NP; both the Livingstone and Ruaha Landscapes provide important hydrological services, managing water quality and quantity into downstream hydroelectric plants. There is an incentive for this industry to maintain these services. 4 PIF PAF Tanzania National Parks 6 Some 30 species are endemic to the area. The site is an Important Bird Area, harboring populations of endangered blue swallow, Tanzania’s only population of Denham’s bustard, and range-restricted species such as mountain marsh widow, and Kipengere seedeater. The Greater Ruaha landscape harbours huge wildlife assemblages, in particular of African elephant (the area supports East Africa’s largest elephant population), has a high diversity of antelopes, reflecting its location in an ecotone between the Acacia Savannas and Miombo Woodland, large numbers of predators, including Lion, Leopard and Wild Dog and some 450 species of birds (the site is also an Important Bird Area). Component 2 will ensure that all NPs in Southern Tanzania have the necessary operational capacities (human capital, equipment and funding) to address threats to biodiversity within their borders. This will ensure that important samples of six eco-regions are safeguarded within National Parks, and thus afforded the maximum security possible. B. DESCRIBE THE CONSISTENCY OF THE PROJECT WITH NATIONAL/REGIONAL PRIORITIES/PLANS: 9) The project is aligned with the National Parks Policy, National Forest Policy, the Wildlife Policy and Environmental Policy of Tanzania. The National Biodiversity Strategy and Action Plan stress the importance of Southern Tanzania’s National Parks and highlight the fact that they have received relatively less management attention than the Northern Circuit. Tanzania’s Tourism Development Policy and Master Plan stresses the importance of wildlife management as buttress for the tourism sector. While an economic analysis of the costs/benefits of National Parks to tourism has not been undertaken, broad data sets from the Tourism Division of Government suggest that: 1) Tourism receipts increased from US$ 259.44 million in 1995 to US$ 746.02 million in 2004, and that 90% of tourism was based on wildlife (cf Kenya where >70% is coast based); 2) Tourism currently accounts for 16% of national GDP (and is rising), and this wider economic impact of tourism is estimated at (2006) US$ 1,858 million and is anticipated to reach US$ 3,699 million by 2015. 3). While the returns from the tourism industry have provided Tanzania with an incentive to set aside large swathes of land as protected areas, most of the tourism is concentrated in Northern Tanzania, and that region receives a disproportionate share of the benefit. Government policy aims at developing tourism products in the Southern Circuit, both to develop conservation- compatible livelihoods that will provide a utilitarian incentive for biodiversity management, but also to reduce the stresses placed on some Northern PAs from visitors. Finally, Tanzania’s Vision 2025 and guiding development paper PRSP 2 or “Mkukuta” stresses the importance of developing a fully representative system of Protected Areas including National Parks and highlights the imperative of ensuring concordance between PA management and local governance systems for land use management. C. DESCRIBE THE CONSISTENCY OF THE PROJECT WITH GEF STRATEGIES AND STRATEGIC PROGRAMS: 10) This project satisfies the requirements for GEF financing under Strategic Objective one in the Biodiversity Focal Area SP3 – “Strengthening Terrestrial Protected Area Networks”. The project takes a comprehensive approach towards strengthening the management effectiveness of PAs in conserving biodiversity. The project will directly bring an additional 10,000 KM2 of land into the NP estate, including under-protected wildlife dispersal areas and poorly represented montane grasslands and wetlands. The accompanying operations support will improve the status of the entire Southern NP estate. This will be achieved by improving accountability for decision making, monitoring and adaptive management, through staff training, and the development of protocols for business planning and annual operations planning. In order to ensure that existing management capacities and finances are not stretched unduly in the process, the project addresses capacity needs at the systemic level--- particularly the need to improve institutional coordination of PA management within landscapes, and integration of NPs into local area development framework. The project also proposes steps to increase revenue earned by the Southern Tanzania NP system, including from tourism, and potential investments from hydroelectricity and tourism industries in PA infrastructure and equipment. D. JUSTIFY THE TYPE OF FINANCING SUPPORT PROVIDED WITH THE GEF RESOURCES: 11) GEF support will be provided entirely as grants for technical assistance and investment in management demonstrations. The project is designed to lift barriers that are currently preventing the effective and sustainable management of Tanzanian National Parks—in particular those Parks that do not currently generate major economic returns. This will allow TANAPA to underwrite future NP management costs from its own financial resources. E. OUTLINE THE COORDINATION WITH OTHER RELATED INITIATIVES: 12) This initiative forms part of a suite of GEF supported initiatives that aim at strengthening Tanzania’s complex PA system (across different PA categories). A World Bank-GEF project is strengthening management of MPAs, while a UNDP/WB-GEF Project has strengthened management of PAs in the Eastern Arc Mountains, an initiative managed by the Forestry and Beekeeping Division. A new UNDP-GEF initiative will strengthen the PA sub system in the Coastal Forests, while a UNDP-GEF supported MSP has created a corridor between the Selous Game Reserve and Niassa Game Reserve in Mozambique. None of these initiatives work in National Parks, and only the latter works with the wildlife sector--- the other projects focus on strengthening forest sector institutions. The Selous- Niassa Corridor Project, the GEF funded component of which is scheduled to close in 2009, has provided valuable lessons pertaining to the management of wildlife on village lands. This initiative also builds on past support rendered by GTZ / KFW to PIF PAF Tanzania National Parks 7 the management of Katavi National Park, and past EU funding to the Northern Circuit NPs and to the Mahale Mountains National Park as well as USAID support through NGOs to management of certain Northern Circuit NPs, such as Tarangire NP. The proposed project aims at building on these interventions by supporting management in NPs such as Ruaha and Kitulo National Parks, that have not received comparable support, and where PA management effectiveness remains sub optimal. The project will be linked into a community of practice between UNDP-GEF supported PA initiatives in Ethiopia, Rwanda, Zambia, Namibia and elsewhere, allowing for the cross fertilization of lessons. F. DISCUSS THE VALUE-ADDED OF GEF INVOLVEMENT IN THE PROJECT, DEMONSTRATED THROUGH INCREMENTAL REASONING : 13) Without this GEF intervention, there will be a continuing loss of globally significant biodiversity values in the southern area of the Country, despite considerable intervention by the Government. This will happen in three ways. Firstly, areas of biodiversity significance will remain excluded from the NP system. Secondly, there will be increased isolation within core PAs, unless landscape planning provides for effective conservation management of dispersal areas and corridors. Thirdly there will be increased pressures on core NPs, from resource dependent communities, and reduced capacities / finance to provide adequate protection. Project interventions under the GEF Alternative will add to, and support, government’s commitment to addressing these complex pressures and problems. Two important ecological landscapes will be brought under higher management control. Two globally important NPs within them will be expanded by 10,000 Km2 (doubling the baseline area) to encompass under protected but important ecosystems. The integrity of these NPs will be secured by integrating their management with that of surrounding landscapes and corridors on production lands, so safeguarding them from external pressures. This will address a major threat to biodiversity in Tanzanian National Parks; there is considerable demand to develop a working model for such integrated management. Moreover, the project will strengthen the management effectiveness of NPs with an expanded area of 33,000 Km2, by strengthening institutional capacities within TANAPA and staff competencies and skills for PA management. This will address a past deficit in investment for PA operations in the Southern Circuit. G. INDICATE RISKS, INCLUDING CLIMATE CHANGE RISKS, THAT MIGHT PREVENT THE PROJECT OBJECTIVE(S) FROM BEING ACHIEVED, AND THE RISK MITIGATION MEASURES THAT WILL BE TAKEN: Risk Landscape planning and subsequent implementation of plans will be affected by institutional intransigence, reducing collaborative efforts between NPs, District Councils and Villages. Rating L/M The tourism down-turn continues for longer and at deeper levels than expected, thus even further reducing financial viability of the Southern Circuit. L Land pressure from local communities and short term gain seekers reduce attempts for rational landscape level conservation. Med Climate change could lead to changed distributions of BD components, and changes in community and private sector demands on wildlife and forest resources. Low PIF PAF Tanzania National Parks Risk Mitigation Measure TANAPA has selected to work in landscapes where this risk will be muted, and builds on strong Government will to strengthen management of the NP Southern Circuit. The project will invest in building conflict avoidance and resolution skills, and build on existing institutional mechanisms such as district environmental committees, and seek to cost economic tradeoffs between wildlife, tourism, agriculture and other land uses and to reduce opportunity costs thus reducing the prospects that institutions will not find common ground. The NP system is heavily dependent on the tourism industry. Bookings for 2009 are down year on year by 10%. While tourism numbers are expected to decrease further, the situation is not as serious as in some other destinations and tourism numbers are expected to increase again in two years [The country has a number of iconic attractions, such as Mt Kilimanjaro, Africa’s highest mountain, which reduces the potential for destination switching.]. The project strategy aims at building Tanzania’s capability to weather the economic crisis, including by improving the cost effectiveness of operations, expanding the tourism product in the Southern Circuit, tapping into the under-serviced domestic tourism market and assisting TANAPA to build its Operating Reserve during high tourism years. Feasibility studies will be undertaken as part of the Systematic Conservation Plans that will be prepared under component 1. The project will seek to manage trade-offs between real development needs and conservation actions within the PA system. Improved enforcement will serve as a deterrent against rent seeking; the project will therefore strengthen the enforcement capabilities of Government. A focus on landscapes (as opposed to small patches), with sufficient buffer zone protection militates against short-term change. The maintenance of forest cover is a good adaptation policy in the face of uncertainty (because rainfall in this region is expected to increase; the maintenance of watershed integrity is critical to avoid major floods). 8 H. DESCRIBE, IF POSSIBLE, THE EXPECTED COST-EFFECTIVENESS OF THE PROJECT: 14) The project might have focused solely on strengthening management of NPs without addressing landscape level management in parallel. Instead, it seeks to avoid externalities from development outside PAs, that might foreclose future opportunities for wildlife to access corridors between PAs and wet season refugia outside them. This is already happening in Tanzania, where some landscapes have already been so altered that wildlife numbers have fallen drastically (the problem being that the core NPs are not large enough to sustain large wildlife populations). The project will provide an opportunity for managing NPs as part of a matrix of conservation compatible land uses, through careful zoning of development and consideration of conservation-development tradeoffs in vetting applications for development licenses. The important economic contribution made by wildlife tourism to the Tanzanian economy makes this a workable strategy, as the tradeoffs may be substantial and provide an incentive for damage avoidance. Another alternative would be to begin fencing PAs, as in Southern Africa, but this would stymie vital ecosystem processes such as migrations, and as in Southern Africa, lead to a reduction in wildlife numbers. Active management of meta-populations of threatened species would be needed, which is a costly undertaking. The proposed approach is considered to be more cost effective in comparison, but is time sensitive in that a delay in the intervention will reduce the opportunity to take preventive action, and would result in future costs being incurred in ecosystem restoration, managing wildlife-human conflict, or more active management of wildlife meta populations. I JUSTIFY THE COMPARATIVE ADVANTAGE OF GEF AGENCY: 15) UNDP is one of the lead GEF agencies working on PA management in Africa; the UNDP-GEF PA portfolio is strengthening management of 208 existing PAs with a total area of 47,161,194 hectares, and has helped to expand the PA estate in Africa by gazetting 65 new PAs in the past four years, with a combined total area of 1,185,845 hectares. 35 PAs are in the process of being gazetted. UNDP has particular strengths, aligned to this initiative, in creating effective PA governance systems and opening new financing options, so as to improve PA management effectiveness. Component 1 is aligned with UNDP’s work on mainstreaming biodiversity management into economic sector activities on production lands, including by strengthening institutional arrangements for land use planning and management. PART III: APPROVAL/ENDORSEMENT BY GEF OPERATIONAL FOCAL POINT(S) AND GEF AGENCY(IES) A. RECORD OF ENDORSEMENT OF GEF OPERATIONAL FOCAL POINT (S) ON BEHALF OF THE GOVERNMENT(S): Ruth Mollel: Permanent Secretary Ministry of Environment and Tourism, Government of Tanzania Date:23 March, 2009 B. GEF AGENCY(IES) CERTIFICATION This request has been prepared in accordance with GEF policies and procedures and meets the GEF criteria for project identification and preparation. This request has been prepared in accordance with GEF policies and procedures and meets the GEF criteria for project identification and preparation. Yannick Glemarec UNDP/GEF Executive Coordinator Date: April 16, 2009 PIF PAF Tanzania National Parks Nik Sekhran, Project Contact Person: Tel: 27-829642384 nik.sekhran@undp.org 9 Annex 1: Map of Tanzania Showing the Location of National Parks Source: WWF/UNEP-WCMC, 2009 PIF PAF Tanzania National Parks 10