WETLAND STATUS IN UGANDA

WETLAND STATUS IN UGANDA

Table 3.8: Wetland status of districts in the Albertine Graben (Source: WMD/MWE, 2020)

Table 3.9: Number of animal species in MFNP and Bugungu Wildlife reserve (Source: UWA, 2018)

WETLAND STATUS IN UGANDA

Table 3.39: Land Cover Statistics for the Albertine Graben (NFA, 2019)

Table 3:65: Trends in the Number of Landing Sites on Lake Albert and Lake Edward and George for the period 2015 -2018 (NAFIRRI, 2018)

Uganda, a country located in East Africa, has a diverse range of wetland ecosystems that are crucial for both ecological balance and human livelihoods. These wetlands include swamps, marshes, floodplains, and lakes, and they provide important services such as water purification, flood control, and habitat for wildlife. Here’s a detailed overview of the wetland status in Uganda:

Wetland Types in Uganda

1. Lakes:
   • Lake Victoria: The largest lake in Africa, shared with Kenya and Tanzania. It is vital for fisheries and transportation.
   • Lake Albert, Lake Edward, and Lake George: Smaller lakes that support a range of aquatic species and are crucial for local communities.
2. Swamps and Marshes:
   • These include extensive areas like the Murchison Falls-Albert Delta and Sio-Siteko Wetlands, which are critical for biodiversity and flood control.
3. Floodplains:
   • Found in regions like the West Nile Region and Kibale National Park, these areas play a key role in agricultural productivity and wildlife habitats.

Current Status and Challenges

1. Ecological Importance:
   • Wetlands in Uganda are home to diverse flora and fauna, including endangered species like the shoebill stork and the Nile crocodile.
   • They act as natural water filters, removing pollutants and maintaining water quality.
2. Threats:
   • Urbanization and Agricultural Expansion: Rapid population growth and the expansion of agriculture have led to significant wetland drainage and conversion.
   • Pollution: Industrial activities, improper waste disposal, and agricultural runoff contribute to the degradation of wetland ecosystems.
   • Climate Change: Changes in precipitation patterns and increased temperatures affect the hydrology and health of wetlands.
   • Overexploitation: Excessive harvesting of resources such as fish and reeds can lead to the depletion of wetland resources.
3. Conservation Efforts:
   • Legislation: Uganda has implemented various laws and policies to protect wetlands, including the National Environment Act and the Wetlands Management Department within the Ministry of Water and Environment.
   • Protected Areas: Some wetlands are designated as protected areas or are included within national parks and reserves, such as Queen Elizabeth National Park and Bwindi Impenetrable National Park.
   • Community Involvement: Local communities are increasingly involved in conservation efforts, through initiatives that promote sustainable use of wetland resources and raise awareness about the importance of wetlands.
4. International Collaboration:
   • Uganda is a signatory to the Ramsar Convention, an international treaty focused on the conservation and sustainable use of wetlands. This involvement helps in the implementation of best practices and access to global support for wetland conservation.

Future Outlook

• The future of wetlands in Uganda depends on balancing development needs with conservation efforts. Effective management strategies that integrate scientific research, community engagement, and sustainable practices are crucial for preserving these vital ecosystems.
• Ongoing monitoring and adaptive management approaches are needed to address the dynamic challenges facing Uganda’s wetlands, ensuring they continue to provide ecological and socio-economic benefits for future generations.
• WETLAND STATUS IN UGANDA

POLLUTER PAY PRINCIPAL

Polluter Pays Principle
The polluter pays principle (PPP) was developed in the 1970s as an economic principle
within the frameworks of the Organisation for Economic Co-operation and Development
(OECD) and the then European Economic Community (EEC). Its aim was to internalize
external costs in order to avoid distortions of trade and competition. It was initially
recognized in regional soft law instrument of these two organizations. In 1972, the OECD
Guiding Principles Concerning the International Economic Aspects of Environmental
Policies9
first articulated PPP as a principle ‘to be used for allocating costs of pollution
prevention and control measures to encourage rational use of scarce environmental
resources and to avoid distortions in international trade and investment’. The principle
implies that ‘the polluter should bear the expenses of carrying out the measures decided
by public authorities to ensure that the environment is in an acceptable state and that ‘the
cost of these measures ,should be reflected in the cost of goods and services which cause
pollution in production and/or consumption.’10 The EEC also advocated PPP in its 1st
Environmental Action Programme of 1973, which included in its statement of the general
principles of EEC environmental policy, inter alia, that ‘the cost of preventing and
eliminating nuisances must in principle be borne by the polluter.’11 This principle was
‘further elaborated in a Recommendation of 3 March 1975 regarding cost allocation and
action by public authorities on environmental matters, which stated that ‘the European
Communities at Community level and the, Member States in their national legislation on
environmental protection must apply the “polluter pays” principle.”12
After being developed in soft law instruments, PPP was subsequently recognized in
regional hard law in 1986 with the Single European Act which amended the EEC Treaty
and inserted in it specific provisions on environmental policy. One of those provisions,
Article 130R (2) of the Treaty, listed the general principles of the Community’s
environmental policy, including PPP. In 1992 PPP was eventually recognized in a
universal soft law instrument. Principle 16 of the Rio Declaration provides: ‘National
authorities should endeavor to promote the internalisation of environmental costs and the
use of economic instruments, taking into account the approach that the polluter should,