The Minziro-Sango Bay Forest Reserves (MSBF) across the Tanzania-Uganda border are used as the first case study example in this volume describing and analyzing Transboundary Natural Resource Management (TBNRM) in Eastern Africa. These area-based case studies support the account of TBNRM Processes described in the Eastern Africa Regional Overview (“Beyond Boundaries: Regional Overview of Transboundary Natural Resource Management in Eastern Africa”) in this volume. This case study uses the experiences of a Global Environment Facility (GEF)1 Biodiversity Project that has addressed cross-border conservation in the MSBF area since 1997.
While Minziro is little known compared with the classic wildlife TBNRM Areas (TBNRMAs) of Eastern Africa, such as Serengeti-Mara (often referred to as Peace Parks); the MSBF does offer a great deal of insight into the evolution of TBNRM. There is a growing set of analysis of local and national policy issues, descriptions of resource-based and people-centered collaboration, and a complex history of war and peace.
Most of the international boundary between Uganda and Tanzania (originally German East Africa) follows an artificially created line along the 1st degree south line of latitude from a point in Lake Victoria westward to a point on the River Kagera (see Map 1). A description of the origins of this line is given by McEwan (1971), and is summarized in Box 1. The border bisects a continuous closed forest, and cuts through an overlap area between the southern extent of the Ugandan Buganda and Ankole Kingdoms and the northern extremity of the former Karagwe Kingdom and Haya Chiefdoms of Tanzania. Clearly people and resources were of no concern to the boundary commissions.
This once extensive forest is now known as Minziro Forest Reserve in the Bukoba District of the Kagera Region of northwest Tanzania and the Sango Bay Forest Reserve in the Rakai District of southern Uganda. The complex is a swamp forest with adjacent wetlands in the Kagera River floodplain. The reserve covers an area of 249 km2 in Tanzania and 600 km2 in Uganda (of which 151 km2 is closed forest) giving a total of 405 km2 of forest, and a total system area of 849 km2 (forest, swamp, and grassland (see Map 2).
|
Box 1. The Origins of the One Degree South Uganda-Tanzania Boundary The boundaries between Uganda and Tanzania and between Uganda and Rwanda show different approaches to boundary setting. The Uganda-Rwanda border is defined by physical features, and therefore is a “natural” boundary. The boundary between Uganda and Tanzania, by contrast, originated with Britain and Germany delimiting their sphere of influence in Eastern Africa by a line extending from the western to the eastern shore of Lake Victoria. On the Uganda border, in the absence of any local agreements, and with no detailed local knowledge, the “hinterland boundary” (on the far side of Lake Victoria) was agreed to in 1890. The agreed border was described as follows:
The benefit to be had by drawing this artificial boundary was clear—there was a need for physical demarcation as German influence was trying to extend to Kakuto in Uganda—in claiming that this was in Deutsch Ost-Afrika (German East Africa, or DOA). So from 1902 to 1904 a boundary commission erected 42 pillars and surveyed a 15 km.-wide strip on both sides of the boundary. Two areas of difficulty were found: in the west around what was Mt Mufumbiro, and on land north and south of the Kagera River, which crossed the 1 degree parallel three times. After the First World War, in 1919, Germany renounced its rights over overseas possessions. In 1922 the League of Nations divided DOA into two parts—Ruanda-Urundi went to the Belgians and the Tanganyika Territory (TT) to the British. There was debate about the Ruanda-Urundi border with Tanganyika, but eventually the Kagera River was used. If one argues that a sensible decision was made to use a major river in that case, the question arises as to why the latitude parallel instead of the same Kagera River to demarcate the Uganda-TT border all the way to Lake Victoria. Germany in 1890 agreed that Uganda was under British influence, but that the British had no claim or role closer to the Congo. The Germans would not allow this British influence to go more than 1 degree south. Explorer Stanley argued that the Kagera made a more normal boundary and separated the TT Kingdoms of Karagwe and Buziba from those of Uganda. Some observers believe that Germany would have accepted this suggestion but the British Government did not pursue it. After the 1902–04 boundary commission completed its work, the British Commissioner, Lt. Col. Delme-Radcliffe argued that the parallel be replaced by a natural boundary. He suggested the Kagera River, from its entry into Lake Victoria upstream to its confluence with the Kakitumba River, as the border. Then it would follow a natural and agreed border to Rwanda. This suggestion would affect two pieces of land:
Delme-Radcliffe proposed that Britain should give the triangle to Germany, and Germany would give the salient to Britain. A port in the triangle area would compensate the difference in size. It was stated that administration would be much easier as neither side would have to cross the difficult Kagera River. It is interesting that by 1914 district administrators in both German Bukoba and British Masaka had asked for the boundary to be changed to follow the river. The substance of these arguments is an easily administered boundary. People were not considered in these arguments, although Delme-Radcliffe stated the people of the Salient were “of no particular value to either administration, but they belong by rights to the Ugandan Ankole (pastoralist) and Buddu (Buganda) groups.” The Delme-Radcliffe recommendations were not accepted, however. The boundary still follows the 1st degree south parallel and the Minziro-Sango Bay Forest is still bisected. The salient issue returned to haunt later governments with Idi Amin’s invasion of Tanzania in the 1970s—see Box 6. Box 1 is based on the book by McEwan (1971). |
The GEF project is not the first attempt to develop broad-based TBNRM in the Kagera area. Two decades ago there was an attempt to develop major cross-borders development in the whole Kagera region via the four-country (Tanzania, Uganda, Rwanda, and Burundi) “Kagera Basin Organisation” or KBO. The KBO was to seek development through the exploitation of hydro-power, minerals (e.g., nickel), and natural resources (fish, forest, wildlife, and agricultural yield) in the whole Kagera area. But political events derailed the process, with Uganda the first to break away. As conflict and tension grew, donors withdrew, and the KBO slowly faded away.3
The conservation of the forest biodiversity within the cross-border MSBF site has been supported by the UNDP GEF project, “Reducing Biodiversity Loss at Selected Cross-Border Sites in East Africa.” The GEF provides incremental funding to countries to meet their responsibilities for conserving global biodiversity values, as stipulated by country ratification of the global Convention on Biological Diversity (see the Regional Overview in this volume). This is a regional project, with inputs to Kenya, Tanzania, and Uganda. The Minziro-Sango Bay site demonstrates national resource management and regional and transboundary issues. The authors of this case study all work within the project and the project has helped generate many of the ideas and discussions presented here. Box 2 describes the objectives and expected outputs of the project.
|
Box 2. The GEF Cross-Borders Biodiversity Project (CBBP) The MSBF site is one of four pairs of cross-border sites in this five-year Global Environment Facility project. The project has activities from the village level, to district (e.g., Bukoba, Rakai), national, and regional levels. CBBP has two immediate objectives under the broad goal of “reducing the rate of loss of forest and wetland biodiversity in specific cross-border sites of national and global significance.” (a) “To establish an environment around the cross-border sites where local agencies and communities can promote sustainable use of biodiversity”; and (b) “To bring into balance the demand and supply of natural resource products including biodiversity at the cross-border sites.” These objectives are outlined in greater detail in the Annex. The first objective is largely aimed at building capacity within the whole environment in which biodiversity conservation takes place (including capacity to address TBNRM). Four outputs address this capacity. Two are resource management agencies within government and within local communities. A third is aimed at the small institutions of policy and law within the overall-enabling environment that is “created with compatible and effective policy and legislative frameworks.” The fourth output deals with developing transboundary processes at both national and local levels. The second objective deals with managing supply and demand within three outputs. The first creates management plan processes for the target forest reserves in a participatory and holistic manner, which would include cross-border issues. The second and third outputs develop alternative resource use technologies and alternative income strategies, respectively. CBBP is thus an Integrated Conservation and Development Project (ICDP) working with both conservation issues within the forest reserves and the development of sustainable livelihood issues with adjacent communities. Both components have a transboundary approach. CBBP has separate national components, funded through government environmental institutions, which follow national execution modalities. In addition there is a regional component that supports regional studies and fosters regional linkages. The project works through partnerships with agencies (e.g., Uganda Forest Department), districts, nongovernmental organizations (NGOs), and regional partners such as the Africa Centre for Technology Studies (ACTS) and the World Conservation Union (IUCN). In 1999, CBBP initiated detailed site planning processes, with considerable levels of community participation. Steps included situation analyses, stakeholder analysis, threat/opportunity analyses, setting strategic interventions, and Monitoring and Evaluation frameworks. The site planning process raised a great deal of awareness and ownership of conservation issues at both local community and district levels. This basis for participation is being used in the preparation of forest management plans at both project sites. CBBP pioneered a dialogue between Rakai and Mbarara districts from Uganda and Bukoba from Tanzania on cross-border biodiversity management. The regional component of CBBP initiated a series of studies into the broader policy and economic policy environment that affects the conservation and sustainable use of biodiversity values in the cross-border sites. This analysis is at local, national, and regional levels. The initial reports (by ACTS on policy, and by IUCN on economics, both in 1999) have fed into this case study—see Chapter V. |
Regionalism in CBBP Project Design
Regionalism was a key concept in the initial design of the CBBP; with governments wanting to see increased synergies of working together to secure conservation and sustainable utilization of biodiversity at a variety of institutional levels. This wish for regionalism was articulated in the evaluation report of an earlier GEF project, “Institutional Support for the Conservation of East African Biodiversity,” carried out from 1992 to 1996.
Such cooperation in East Africa in the area of environmental management and biodiversity conservation is particularly effective because the countries form a mega-biodiversity region and either share, or have in common, a variety of ecosystems. The countries should continue to work together on issues of mutual concern, and share and learn from each other’s experience. There will still be major advantages in a regional approach in the future as project emphasis switches to field activities. Wherever there are common ecosystems, common threats, and/or common training needs among the three countries, there will be advantages in regional exchanges of experiences and expertise and sharing of training resources.
The MSBF site has the three factors that GEF believes are necessary for developing a regional approach, shown below with examples:
A regional approach was needed at many levels:
That these issues were built into the developing project is confirmed by a December 1997 comment from a Swiss member of the GEF Council: “From the conceptual point of view we fully agree with the objectives of regional projects. Arising from clear ecological necessities (transboundary ecosystems or biological corridors) or from institutional opportunities (regional institutional networks), in most cases the regional projects seem scientifically and technically justified, and conceptually advantageous.”
However, experience in this and other regions suggests that strong regional4 approaches can only be built on the basis of strong national foundations. It is not possible to superimpose a strong regional mechanism on weak national structures in natural resource management as much as in other sectors.
The GEF project supports cross-border interaction at site and district levels, and requires this interaction to be linked to real cross-border issues of biodiversity management; and not just a set of generalized discussions—such as security and pastoralism. In the past year the project has identified what these specific cross-border issues are, and is bringing them to the discussion table. There is synergy and linkage between the newly recreated EAC5 and the project. The EAC provides political support for regional activity. The project provides support to regional interaction; and provides examples of the advantages of cross-border technical activity. The project is represented on the EAC Environment Committee, and provides technical advice as needed; in turn, the EAC is represented on the project steering committee.
The Cross-Borders Project addresses the situation in the Minziro Sango Bay forests, but the Uganda-Tanzania border has several other sites of TBNRM interest. These sites are described in Box 3 below.
|
Box 3. TBNRM Sites across the Tanzania-Uganda Border Kagera River. The Kagera River rises in Rwanda and Burundi and forms the boundary between Tanzania and Rwanda before turning eastward to flow into Lake Victoria within the MSBF complex. The Kagera River is the principal river-flow into the Lake, and has implications for Nile River waters (see Box 11 on the Nile River basin initiative in the Regional Overview in this volume). Much of the Kagera is slow-flowing, extensive papyrus-filled lagoons with broad floodplain grasslands. The meandering river is in some cases a “no man’s land” where it forms the border, and allowing unchecked cultivation along the banks in those areas is causing rapid siltation, and consequently pollution for Lake Victoria. The Kagera River floods frequently and the flat terrain near Lake Victoria and MSBF can be under 50 cm. of water for several months. This flooding allows the continuation of the swamp-forest as local rainfall (c. 750 mm. pa) is too low for wet forest. The Kagera River is not yet used for irrigation. Fishing is at a subsistence level. The river achieved notoriety in the 1990s as the source of water hyacinth into Lake Victoria (see the Regional Overview in this volume) and for carrying several hundred human bodies following the 1994–95 genocide in Rwanda. The Dry Grasslands of Karagwe-Mbarara (and Northeast Rwanda). These areas accommodate the Bahima pastoralists who move seasonally from the drier grasslands to the swamps around MSBF in the dry season. Water and fires are key aspects of their ecology. The area is a potential UNEP-UNDP GEF project site, focusing on maintaining landscape and community biodiversity. In the process of searching for pasture and water the pastoralists are blamed for starting fires, charcoal production, banditry, and so on. Conflicts abound between pastoralists and cultivators, although there also is synergy through cultivators’ use of pastoralists’ dung manure and pastoralists’ cows grazing on fallow fields. Wildlife Protected Areas. The Ibanda Arena Game Reserve (of 500 sq. km.) is the apex of the borders among Uganda, Rwanda, and Tanzania. Home to beautiful scenery, the area was used for hunting professionally in the 1960s and 1970s (by Uganda Wildlife Safaris—interestingly in an early case of TBNRM utilization.). Lack of protection and massive poaching has greatly reduced populations. The Rumanyika Game Reserve (named after a past Haya paramount chief) is a more hilly forested area. Renowned at one time for extraordinarily high rhinoceros densities (now hunted to the brink of completely being wiped out), the area has more recently gained attention for bird populations (Marc Baker, pers. comm.). Both game reserves are managed as a national wildlife project, with some funding via the European Union (EU). Lake Mburo National Park (gazetted in 1983 as 200 sq. km.) in the Mbarara District is some 40 km. from the Tanzanian border. The scale of land and grazing pressure makes the future of this little-visited park uncertain. Recurrent droughts in the area (rainfall averaging 600–700 mm. pa) lead to enormous pastoralist pressures. While these protected areas (Pas) are close to (e.g., Mburo) or on (e.g., Ibanda) national boundaries, none of the PAs have strong potential as full TBNRMAs, although sympathetic land use in boundary areas could enhance conservation efforts. As border areas are largely pastoralist, this is feasible. |
Uganda and Tanzania have extensive protected area networks as indicated by Table 1.
|
Table 1. Country Parameters |
||
|
Parameter |
Tanzania |
Uganda |
|
Country area land only |
883,590 sq. km. |
199,650 sq. km. |
|
Human population |
32 million |
21 million |
|
Density |
36 people per sq. km. |
105 people per sq. km. |
|
No. of protected areas (national parks and game reserves) |
39 |
37 |
|
Area (sq. km.) |
138,170 sq. km. |
19,130 sq. km. |
|
Percentage of country as PA |
14.6 |
7.9 |
|
No. of PAs over 10,000 sq. km. |
3 |
0 |
|
Percentage of country as forest |
22.4 |
32.9 |
|
Percentage of country as protected forest |
9.1 |
7.0 |
|
Tropical forest area |
143,560 sq. km. |
37,720 sq. km. |
|
Percentage of tropical forest protected |
15.8 |
17.0 |
1. The GEF supports several regional/transboundary biodiversity projects in the region—see the Regional Overview in this volume.
2. See a detailed history by H. B. Thomas in the Uganda Journal, 1959, 23.
3. The KBO is starting to be revived as Rwanda politics open up again.
4. “Regional” and “transboundary” approaches to NRM are described in some detail in the Regional Overview in this volume.
5. The role of the East African Community in supporting both “regional” and “cross-border” issues is spelled out in the Regional Overview in this volume.