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Zimbabwe - Main Details

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Status and Trends of Biodiversity

Overview

Zimbabwe is characterised by three phytogeographic regions, the Zambesian, the Afromontane and the East African coastal. The Zambesian region covers over 95% of the country. The Eastern Highlands form part of the Afromontane region and have the highest level of endemism, notably in the Chimanimani Mountains. The Zambesian phytogeographic region comprises five woodland types – miombo, mopane, teak, acacia and Terminalia/Combretum. Many tree species in these woodlands are economically important and are used for timber, poles, firewood, fruit and medicines. The total flora of Zimbabwe comprises 5930 taxa.

During the national Red Data listing for Zimbabwe, 504 taxa were formally assessed, of which 211 were regarded as threatened. There are 232 species or subspecies that are believed to be endemic or near-endemic to Zimbabwe. A number of these rare and threatened species lie outside formally protected areas. The major areas of endemism in the country are the Chimanimani Mountains, the Great Dyke and the dambos of the central watershed area. Table 1 shows the habitats of the plant species on the Red Data List. Seven species are listed as extinct, while 54 are listed as critically endangered (Table 2). Those reported as extinct are Triceratella drummondii, Agraecopsis trifurca, Angraecum stella-africae, Oeceoclades decaryana, Polystachya pubescens, Platycerium alcicorne and Encephalartos chimanimaniensis.

Moist forest: 138 listed taxa; 94 threatened taxa; 44.3% of total threatened taxa. Dry forest: 12 listed taxal 6 threatened taxa; 2.8% of total threatened taxa. Moist woodland: 41 listed taxa; 25 threatened taxa; 11.8% of total threatened taxa. Dry woodland: 64 threatened taxa; 22 threatened taxa; 10.4% of total threatened taxa. Rock and outcrops: 31 listed taxa; 14 threatened taxa; 6.6% of total threatened taxa. Grasslands: 130 listed taxa; 37 threatened taxa; 17.5% of total threatened taxa. Dambos: 24 listed taxa; 2 threatened taxa; 0.9% of total threatened taxa. Wetlands: 13 listed taxa; 3 threatened taxa; 1.4% of total threatened taxa. Disturbed: 1 listed taxa; 1 threatened taxa; 0.5% of total threatened taxa. Unknown: 63 listed taxa; 12 threatened taxa; 5.7% of total threatened taxa.

Total number of RDL: 504 taxa. Genera: 257 taxa. Families: 84 taxa. Endemic/near endemic taxa: 224 taxa. Strict endemic taxa: 178 taxa. Threatened taxa (extinct, critically endangered, endangered, vulnerable): 211 taxa. Lower risk taxa: 162 taxa. Extinct: 7 taxa. Critically endangered: 54 taxa. Endangered: 29 taxa. Vulnerable: 121 taxa. Lower risk near threatened: 91 taxa. Lower risk least concern: 71 taxa. Data Deficient: 131 taxa.

The major threat to forest species is collectors, afforestation and land conversion to agriculture. Other threats to species survival in Zimbabwe are habitat loss due to human activities such as deforestation, mining, dams and urban expansion.

There are no systems for the protection of these species and chances of degradation are high especially with the land reform programme. Innovative systems for their protection also need to be developed and enforced. There is thus an urgent need to re-examine the representativeness of protected areas and the appropriateness of current management regimes with a view to extending the protected areas to comprehensively address pressing issues of biodiversity loss and habitat fragmentation outside protected areas. Fig 1 shows 27 sites that are being recommended for protection as special areas of endemism or representatives of certain vegetation/species types on former privately owned land.

The status and conservation of many plant species in Zimbabwe remains poorly documented. It is therefore prudent that such an exercise be carried out so that the status of almost 90% of the plant species is documented.

Animal diversity is very high in Zimbabwe and consists of 175 mammal species, 600 bird species and 264 reptile and amphibian species. Total bird species number fluctuates within and across years due to migration, but there is a general decline in bird populations associated with the disappearance of their specialized habitats. The most common wild animals found in Zimbabwe include elephant, lion, giraffe, hippopotamus, buffalo, zebra, impala, cheetah, leopard, kudu, ostrich, bushbuck, duiker, eland, reedbuck, sable, steenbok, tsessebe, warthog, waterbuck, wild beast, hyena, pangolin, wild dogs, crocodile, tortoise, crab, snails, earth worms, frogs, ants, monkeys, baboons, birds, owls, snakes, lizards and butterflies. The most widely monitored wildlife species are those of economic importance as well as ecological key indicator species.

The crocodile (Crocodylus niloticus) is the only reptile that has been extensively studied due to its economic importance, while the python (Python sebae) is the only protected reptile in the country. Some causes of biodiversity loss include population pressure and land tenure systems, fire, drought and frost, and the negative impact of high density of elephants. The diversity of Zimbabwe’s aquatic flora and fauna is directly related to the type and distribution of its wetlands. These wetlands include floodplains, riparian wetlands, dambos, pans, swamps and artificial impoundments. Of the 123 fish species occurring in the country, only a few economically and biologically important ones have been monitored. Causes of aquatic biodiversity change include interbasin transfer, reservoir formation, pollution, hybridization, and anthropogenic activities.

Wildlife Population on Parks Estates:According to the Parks and Wildlife Authority the population of elephants stands at more than twice the ecological carrying capacity in the core range within the protected areas. Having exceeded the carrying capacity of the areas, the elephants are threatening the habitats of many other species and biodiversity in general. Although populations of many other wildlife species have been doing well outside protected areas, they still face uncertainty in the former game farms, as some new farmers may prefer land use forms other than game farming. A Wildlife Based Land Use Policy was developed by Ministry of Environment and Tourism to facilitate the continuation of wildlife production as a land use in former conservancies and game farms.

Both the black and white rhinoceros continue to increase although they face serious risk from reduced protection and habitat loss in the interim period during change of ownership and land use associated with resettlement in conservancies. However several "safe" areas are still available in secure conservancies and the proposed Gonarezhou Intensive Protection Zone (IPZ) in the Gonarezhou National Park.

Number and Extent of Protected Areas

15% of the country is protected as National Parks, Forest Reserves and Botanic Gardens. Conservancies (private farmland and combined holdings managed for wildlife) make up approximately 17% of the country.

Percentage of Forest Cover

Zimbabwe’s land area is classified in the following categories: 0.03% is moist forest (tropical rainforest), 0.4% is Forest Plantation, 65.92% is indigenous woodland (including bushland), 4.85% is grassland, 27.47% is cultivated land, 0.36% is settlement and 0.97% is rock outcrop and water body.

National Biodiversity Strategy Action Plan

Major features of National Biodiversity Strategy and Action Plan

Zimbabwe produced its NBSAP in 1998 and identified several key unmet needs to be addressed in terms of biodiversity conservation and management. These are: 1) the absence of comprehensive and elaborate biodiversity inventory and monitoring programmes; 2) Inadequate incentives for some local communities to undertake biodiversity conservation and sustainable use initiatives in both protected and non-protected areas; 3) Inadequate environmental awareness, education and training; 4) Limited appreciation of the importance of biodiversity to national economy and to local communities and policy makers; 5) Inadequate, conflicting and poorly enforced pieces of legislation that tend to adversely affect biodiversity conservation and sustainable use; 6) A limited financial base and institutional capacity to facilitate the formulation, implementation and monitoring of biodiversity projects at the local level; 7) Inadequate affordable alternatives to reduce the reliance on natural resources at the local level; 8) Inappropriate research and extension approached in biodiversity conservation and sustainable use. Zimbabwe’s biodiversity strategy and action plan aims at addressing the priority unmet needs listed above. Several specific strategies along with broad actions were formulated to achieve this goal.

The revision of the NBSAP is long overdue. There is need to revise the NBSAP in line with emerging issues and to determine whether it remains adequate for reducing rates of biodiversity loss, promoting sustainable use, and contributing to the fair and equitable sharing of benefits arising out of the utilization of genetic resources. This will facilitate the implementation of the Strategic Plan and CBD programmes of work as well as follow-up on progress towards the 2010 Biodiversity Target and relevant Millennium Development Goals. The NBSAP should ensure that biodiversity concerns are being integrated into relevant sectoral or cross-sectoral plans, programmes and policies in the country.

The revision could include: (i) status and trends in biodiversity, current and projected major threats to biodiversity, obstacles to sustainable use and to the fair and equitable sharing of benefits arising out of the utilization of genetic resources, and the experience of the previous and existing strategies; and (ii) a gap analysis taking into account all relevant activities including those being undertaken within the framework of other conventions, and by organizations and initiatives that contribute to the objectives of the convention. The gap analysis would also help to identify opportunities for collaboration, as well as areas where additional activities would add the most value.

The NBSAP does not explicitly look at the issues of taxonomy, access and benefit sharing, degradation, international waters and risks posed by organisms modified by biotechnology in detail. Proposals to address these issues are required.
 

Implementation of the Convention

Measures Taken to Achieve the 2010 Target

Zimbabwe has implemented sectoral strategies in the agriculture, water and environment sectors. Protected areas are in fact increasing through the formation of private conservancies and the extension of wildlife ranges into rural areas through incentive use programmes such as CAMPFIRE, which promotes the conservation and sustainable use of wildlife and other natural resources outside protected areas. This has led to the extension of the range of wildlife species beyond protected areas into rural areas/communal areas by as much as 17%. In agriculture, there is an increased use of underutilized crops/genetic materials through the use of open pollinated varieties. Indicators for these programmes include: hectares under protected area, level of genetic diversity of crops or livestock and the number of dams and protected catchment areas. There is no national target set for the conservation of species diversity, but ongoing activities include species restoration programmes (e.g. black rhino, wild orchids and cycads), and species recovery programmes. One very clear national target is that no single species of flora and fauna will be endangered by international trade. Legislation, regulations and controls, as well as the institutions to control international trade in endangered species, are in place and being enforced. Conservation legislation is in place and regulates the utilization of forests and other natural resources and encourages restoration of degraded systems. The Government of Zimbabwe enacted the Environmental Management Act in 2003. This was part of the law reform process to deal with problems associated with the administration of up to 21 pieces of legislation on the environment that were housed in nine different ministries and departments. The Act contains measures the Minister may take in to ensure conservation of and access to biological diversity. The Environmental Management Act gives the major responsibility for promoting conservation and sustainable use in rural areas to Rural District Councils (RDC). This move provided an opportunity to protect threatened species in rural areas through RDC by-laws. Efforts are being made to protect threatened and endemic species found outside protected areas under botanical reserves.

Initiatives in Protected Areas

Protected areas were set aside prior to the CBD and largely on the basis that the areas were marginal to agricultural and industrial development and because of their value for hunting of big game. Fortunately the areas also cover large biomes such as teak and mopane, but threatened species were not targeted.

Initiatives for Article 8(j)

The Environmental Management Act (EMA) of 2003 provides the building blocks for a more comprehensive national access and benefit-sharing framework. Under the EMA, regulations entitled Access to Genetic Resources and Traditional Knowledge Regulations, 2006 have been developed and are awaiting approval by Parliament. The Statutory Instrument advocates the need for an equitable access regime and benefit sharing mechanism for traditional medicinal plants, as well as intellectual property rights that recognise the contribution of indigenous knowledge to primary health care and to the development of modern medicines. There is a need to broaden the regulations to cover aspects of agro-biodiversity (crops and livestock), wildlife and fisheries. Alternatively sector-specific regulations may be required. A number of community-based programmes which relate to the provisions of Article 8j are already in place such as the Communal Areas Management Programme for Indigenous Resources (CAMPFIRE) and the MASAU Project to mention only a few. However, these programmes and projects need to be harmonised and better coordinated.

Concerning agro-biodiversity, the country is promoting the conservation and sustainable utilisation of plant genetic resources for food and agriculture. The ‘Zunde RaMambo’ (The Chief’s Silo) concept or the chief’s seed and food security programme recognizes the role of traditional leaders in grain storage schemes. The leaders have the role to make sure that the goals are achieved. Establishing of in situ gene banks is being encouraged to ensure availablity of seed at field level. This concept is also being extended to tree planting programmes to recognize traditional leaders in tree planting and hence conservation of biodiversity. Through the traditional leaders, the local communities are encouraged to leave seed trees or seed stands in their natural habitats. In addition communities are being empowered to produce and market open pollinated seed varieties.

Documentation in order to create awareness on the CBD amongst various stakeholders including traditional leaders, NGOs and CBOs is very good. However documentation on traditional knowledge, innovations and practices is poor. The next step is to develop guidelines that will constitute an agreed system for (i) inventory of traditional systems and practices and (ii) legally protecting traditional knowledge systems and practices and (iii) promote benefit sharing.

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  • United Nations
  • United Nations Environment Programme