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Newsletter and Technical Publications
<Planning and Management of Lakes and Reservoirs:
An Integrated Approach to Eutrophication
Abridged Version- A Student's Guide>
Lake Chivero, Zimbabwe (Africa)
Perhaps one of the most studied lakes in Africa is Lake Chivero, formerly
Lake McIllwaine. The lake was built to supply water to the City of Harare, as
well as to serve the irrigation needs of downstream farmers. This case study is
chosen to illustrate management failure due to institutional problems. The
technological, manpower, legislative, and financial resources for the proper
management of Lake Chivero could be marshaled, but in recent years working
institutions have been lacking. The failure arose from a lack of clear linkages
between stakeholders and administrative structures, as well as failure to forge
working partnerships with other institutions, and a lack of public awareness,
education and stakeholder participation in the ecological management of the
reservoir.
Historical background
Beginning in the mid 1980s, the lake became progressively eutrophic, after a
recovery period from a previous eutrophication phase in the mid 1960s. When the
lake was constructed, the population of Harare was about 400,000 inhabitants.
The urban population of the Lake Chivero watershed now stands at about 1.6
million. As the population grew, the wastewater discharge also increased. Human
and livestock populations in the rural part of the catchment also grew. A new
urban settlement, now the second largest city in Zimbabwe, mushroomed upstream
of the lake to a population of over half a million inhabitants in less than two
decades. More recently, with an increase in urban drift, the city has expanded
as new residential areas have been established. Due to the highly seasonal
nature of the river flow, the dry season flow into the lake consists largely of
processed wastewater.
| Table 6. Historical trends in phosphorus loading to Lake Chivero |
| Parameter |
1967 |
1978 |
1996 |
| P- load, tons yr-1. |
288 |
39.6 |
350 |
| Mean P concentration in inflow mg l-1 |
2.25 |
0.13 |
1840 |
| Conductivity mS cm-1 |
160 |
120 |
800 |
In the late 1960s, the lake became hypereutrophic (Table 6). Before the
construction of Lake Chivero, Harare took its water from reservoirs that were
upstream of the sewage effluent outflow. When the lake was created, the need to
protect the watershed was recognized, and took the form of a recreational
wildlife park around the lake. While this measure guarded against siltation from
the immediate surroundings of the lake, it did not include the impact of an
increasing volume of treated sewage flowing into the lake. In 1974, the City of
Harare took further measures to protect the lake by installing a biological
nutrient removal sewage treatment plant for its municipal wastewater. Tertiary
treatment was effected by use of pastureland where the final effluent was used
for irrigation.
For a period of nearly ten years, the lake showed recovery from eutrophic
conditions. In the late 1970s, satellite settlements around Harare, particularly
Chitungwiza, grew. These settlements did not have the funds to install
sophisticated wastewater treatment works, so their wastewater was discharged
into the Lake Chivero watershed streams after only primary treatment. By the mid
1980s, the lake had reverted to hypereutrophy. It remains hypereutrophic today,
and is beset with a chronic water hyacinth problem and repeated fish kills.
Management issues with respect to Lake Chivero are as follows:
Lack of institutional harmonization
Though Harare is the principal user of the lake water, the management of the
lake falls under the jurisdiction of the Department of National Parks and
Wildlife Management, which is not represented in the municipal water supply and
wastewater management decision-making system. Furthermore, the Department has no
facilities for water quality management, as its main interest in the lake is the
fishery. The responsibility for water quality monitoring and pollution control
was invested in the Ministry of Health. While the city invested heavily in
managing wastewaters from its own sewers, it failed to recognize the
contribution of satellite settlements as well as rural runoff in the watershed.
The regulatory authority for use and management of the lake is invested in a
separate department.
Lack of stakeholder participation
There are no established consultative arrangements among the land users of the
Lake Chivero watershed for the management of the watershed. Land users in the
watershed include commercial farmers, subsistence farmers and urban and local
authorities.
Inadequate funding
A problem, perhaps peculiar to developing countries, is the growth of human
settlements of limited revenue base, such that the administrative authorities
have a limited financial capacity to provide civic works and to maintain
services. Consequently, waste management works tend to be under-funded.
Failure to appreciate watershed dimensions of the problem.
Though there were possibilities of use of wetlands and other impoundments within
the catchment to manage overland runoff, the lack of a holistic watershed
approach led to a failure to maximize opportunities for the restoration of the
lake's water quality.
Lack of public awareness
While the concept of public awareness and participation is increasingly
recognized in natural resource management, in the case of Lake Chivero public
awareness and participation were viewed as threats to the workings of the
municipal authority. Information on water quality of the lake and that of the
water delivered to consumers is not readily available. Members of the public
thus remained ignorant of their role in the eutrophication of the lake and how
they could assist in the remedy. The various authorities thus missed an
opportunity for public support in their disparate attempts to arrest the
eutrophication trend in the reservoir.
Legal framework failure
The political institutions did not appear to be concerned about the
deteriorating water quality of the lake. Elected councilors seemed to be
ignoring breaches of municipal environmental by-laws, and in some cases
encouraged such breaches to retain popularity with an ill-informed electorate.
The civic authority’s strategy was limited to passing the rising operational
costs of potable water production to middle class ratepayers, an electoral
minority. Environmental advocacy by the public was poorly developed and
politically ineffective. Thus, while a legal framework existed both at national
and local levels in the form of various acts and bylaws, the political
leadership was unwilling to enforce the legislation.
Failure to forge partnerships
In the 1970s, the Municipality had a collaborative research program with the
University in which the Municipality funded research programs aimed at solving
water quality management problems. In the post independence period, these links
were discontinued, and so was the research into possible technical innovations
in eutrophication management. The Municipality also failed to take advantage of
developments in industry, which, over the years had developed an environmental
program of its own, as evidenced at the CemZim 99 Environmental Management
Conference, organized by the Environmental Forum of Zimbabwe. Most significant,
however, was the failure of the various urban and local authorities to cooperate
in the lake's environmental management.
The management status of Lake Chivero, as a case study of institutional
failure, can perhaps be defined by comparing its management to guidelines
outlined in “Environment and development in Africa: Tools for implementing
environmentally sustainable developmentEin Table 7.
| Table 7. Comparison of guidelines for environmental management as
recommended in “Environment and Development for AfricaE(Scandinavian Seminar
College, 28-30 August 1995, Telemark College, Norway), with the state management
regime for Lake Chivero, Harare |
| Guideline Principle |
Observation for Lake Chivero |
| Environment should be integrated in decision- making at all
levels and be given equal priority with economic and social concerns. Planning
programs and processes should be proactive and take into account the
environmental impacts of activities. |
Environmental issues often considered secondary to economic and
political agenda. |
| Residents must own the idea environment and interpret it in
relation to their daily needs. |
No consultative facility for ratepayers and residents to
participate in environmental issues. Ratepayers expected to accept and pay what
council delivers. |
| Human resources development, institution building and strong
legal and policy framework related to natural resources are therefore keystones. |
Human and financial resources and legal framework are often in
place, but low priority rating of environmental issues results in underfunding
and suboptimal performance. |
| Natural resources management by communities at the local level
must be strongly supported through participatory methods, information systems
and appropriate financial mechanisms. |
Local authorities in some of the emerging democracies are often
wary of stakeholder participation; decision-making highly centralised; with
limited information dissemination facility. |
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