Lake Rweru is located in central Africa, close to the northernmost point of Burundi, with its northern shore forming part of the Burundi-Rwanda border. The lake is surrounded by marshes and papyrus, and contains floating islands. It is considered by many to be the most distant starting point of the Nile River, in that the Kagera River, which rises at the northern part of the lake, is considered to be the starting point of the Nile. The lake hosts limited fishing activities, and is being increasingly invaded by water hyacinth. Lake Rweru could be a subject for GEF-catalyzed management interventions, along with Lakes Cohoha and Ihema, with all three lakes located in the same general proximity in the upper catchment wetland region of the riparian countries, and sharing similar economic (fishery management) and environmental (progressing eutrophicatio) challenges. Effectively considering these lakes for such management interventions may require a new strategic approach that considers them as a lake cluster comprising both transboundary and national (non-transboundary) lake basins.

TWAP Regional Designation Eastern & Southern Africa   Lake Basin Population (2010) 359,565
River Basin Nile Lake Basin Population Density
(2010; # km-2)
Riparian Countries Burundi, Rwanda Average Basin Precipitation
(mm yr-1)
Basin Area (km2) 941.6 Shoreline Length (km) 96.7
Lake Area (km2) 125.5 Human Development Index (HDI) 0.38
Lake Area:Lake Basin Ratio 0.109 International Treaties/Agreements Identifying Lake No

Lake Rweru/Moereo Basin Characteristics

(a)Lake Rweru/Moereo basin and associated  transboundary water systems

(a)Lake Rweru/Moereo basin and associated transboundary water systems

(a)Lake Rweru/Moereo basin and associated  transboundary water systems

(b)Lake Rweru/Moereo basin land use

Lake Rweru/Moereo Threat Ranking

A serious lack of global-scale uniform data on the TWAP transboundary in-lake conditions required their potential threat risks be estimated on the basis of the characteristics of their drainage basins, rather than in-lake conditions. Using basin characteristics to rank transboundary lake threats precludes consideration of the unique features that can buffer their in-lake responses to basin-derived disturbances, including an integrating nature for all inputs, long water retention times, and complex, non-linear response dynamics.

The lake threat ranks were calculated with a spreadsheet-based interactive scenario analysis program, incorporating data and information about the nature and magnitude of their basin-derived stresses, and their possible impacts on the sustainability of their ecosystem services. These descriptive data for Lake Rweru/Moero and the other transboundary lakes included lake and basin areas, population numbers and densities, areal extent of basin stressors on the lake, data grid size, and other components considered important from the perspective of the user of the data results. The scenario analysis program also provides a means to define the appropriate context and preconditions for interpreting the ranking results.

The Lake Rweru/Moero threat ranks are expressed in terms of the Adjusted Human Water Security (Adj-HWS) threats, Reverse Biodiversity (RvBD) threats, and the Human Development Index (HDI) score, as well as combinations of these indices. However, it is emphasized that, being based on specific characteristics and assumptions regarding Lake Rweru/Moero and its basin characteristics, the calculated threat scores represent only one possible set of lake threat rankings. Defining the appropriate context and preconditions for interpreting the lake rankings remains an important responsibility of those using the threat ranking results, including lake managers and decision-makers.

Table 1. Lake Rweru/Moereo Relative Threat Ranks, Based on Adjusted Human Water Security (Adj-HWS) and Reverse Biodiversity Threats,
and Human Development Index (HDI) Score

(Estimated risks: red – highest; orange – moderately high; yellow – medium;
green – moderately low; blue – low)

Adjusted Human Water Security
(Adj-HWS) ThreatScore
Relative Adj-HWS Threat Rank   Reverse Biodiversity (RvBD) Threat Score Relative RvBD Threat Rank   Human Development Index (HDI) Score Relative HDI Rank
0.96 4 0.58 30 0.36 3

It is emphasized that the Lake Rweru/Moero rankings above are discussed here within the context of the management and decision-making process, rather than as strict numerical ranks. Based on its geographic, population and socioeconomic assumptions used in the scenario analysis program, the calculated Adj-HWS score for Lake Rweru/Moero indicates a high threat rank compared to other priority transboundary lakes, a common situation for transboundary lakes in many developing countries.

The Reverse Biodiversity (RvBD) for Lake Rweru/Moero, which is meant to describe its biodiversity sensitivity to basin-derived degradation, places the lake in a medium threat rank, compared to the other transboundary lakes. Management interventions directed to improving the biodiversity status must be viewed with caution, however, since we lack sufficient knowledge and experience to accurately predict the ultimate impacts of biodiversity manipulations and preservation efforts. Further, the RvBD scores indicate the relative sensitivity of a lake basin to human activities, and high threat scores per se do not necessarily justify management interventions. Such interventions may actually increase biodiversity degradation, noting that many developed countries have already fundamentally degraded their biodiversity because of economic development activities. Thus, activities undertaken to address the Adj-HWS threats may actually degrade the biodiversity status and resources, even if the health and socioeconomic conditions of the lake basin stakeholders are improved as a result of better conditions, thereby increasing stakeholder resource consumption.

The relative Human Development Index (HDI) places the Lake Rweru/Moero basin in the highest quarter of the priority transboundary lake basins in regard to its health, educational and economic status.

Table 2. Lake Rweru/Moereo Threat Ranks, Based on Multiple Ranking Criteria

(Scores for Adj-HWS, RvBD and HDI ranks are presented in Table 1; the ranks may differ in some cases because of rounding of figures; Estimated risks: red – highest; orange – moderately high; yellow – medium;
green – moderately low; blue – low)

Adj-HWS Rank HDI Rank RvBD Rank   Sum Adj-HWS + RvBD Relative
Threat Rank
  Sum Adj-HWS + HDI Relative Threat Rank   Sum Adj-HWS + RvBD + HDI Overall Threat Rank
4 3 30 34 16 7 2 37 8

When multiple ranking criteria are considered together in the threat rank calculations, the Adj-HWS and HDI scores considered together place Lake Rweru/Moero in the highest quarter of the threat ranks. The relative threat is somewhat reduced when the Adj-HWS and RvBD threats are considered together. Considering all three ranking criteria together, Lake Rweru/Moero exhibits an overall high threat ranking.

Further, a series of parametric sensitivity analyses of the ranking results also was performed to determine the effects of changing the importance of specific criteria on the relative transboundary lake rankings. This analysis involved increasing or decreasing the weights applied to the threat ranks derived from multiple ranking criteria to reassess the relative impacts of the weight combinations on the threat ranks. For example, in determining the sensitivity of the Adjusted Human Water Security (Adj-HWS) and Biodiversity (BD) ranking criteria, the threat rank associated with the first was assumed to be of complete (100%) importance (i.e., rank weight of 1.0), while the other was assumed to be of no (0%) importance (i.e., rank weight of 0.0). The relative importance of the two ranking criteria was then successively changed, with weight combinations of 0.9 and 0.1, 0.8 and 0.2, etc., until the first ranking criteria (Adj-HWS) was assumed to be of no importance (rank weight of 0.0) and the second (BD) was of complete importance (rank weight of 1.0). In the case of Lake Rweru/Moero, the 0.5 and 0.5 weight combinations for three cases of parametric analysis for Lake Rweru/Moero resulted in respective threat rankings of 3rd, 2nd and 12th, respectively, among the total of 23 African transboundary lakes in the TWAP study (see Technical Report, Section 4.3.3, pp44-49).

In essence, therefore, identifying potential management intervention needs for Lake Rweru/Moero must be considered on the basis of both educated judgement and accurate representations of its situation. A fundamental question to be addressed, therefore, is how can one decide that a given management intervention will produce the greatest benefit(s) for the greatest number of people in the Lake Rweru/Moero basin? Accurate answers to such questions for Lake Rweru/Moero, and other transboundary lakes, will require a case-by-case assessment approach that considers the specific lake situation and context, the anticipated improvements from specific management interventions, and its interactions with water systems to which the lake is linked. To this end, it is noted that the African transboundary lakes as a group merit special attention in regard to management interventions, with some lakes requiring more immediate attention than others.