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LIMCOM's current ongoing interventions being undertaken include:
The aquatic environment should always be considered as a legitimate consumer of water, whose requirements must be met alongside basic human requirements, and ahead of any other demand. In the case of water projects involving impoundment, this translates to maintenance of flow in the reaches of the river downstream of the impounding structure, dam, or diversion. Environmental flows are required to:
THE OLIFANTS RIVER, SOUTH AFRICA.
SOURCE: ASHTON 2008
Environmental Flow Requirements (EFR) are accounted for in the legislation of all of the basin states.
Source: LBPTC 2010
The map below shows a preliminary assessment of ecological status of the sub-basins of the Limpopo River basin. The classes are Environmental Management Classes (EMC) - ranging from A (close to natural conditions) to D (highly modified).
PRELIMINARY ASSESSMENT OF ENVIRONMENTAL WATER REQUIREMENTS FOR THE LIMPOPO RIVER BASIN.
SOURCE: LPBTC 2010
As can be seen from this map, most of the northern sub-basins (including the Changane in Mozambique) of the Limpopo River basin are classified as A to B (close to natural, relatively un-impacted status). However, with the exception of the Sand, Shingwedze and Letaba, most of the South African sub-basins are moderately to severely impacted.
Specific areas for concern are the Upper Olifants, Lephalala and Nzhelele sub-basins in terms of negative status. One area of specific concern is the Waterberg, which is located in the Lephalala sub-basin. This sub-basin is already under stress in terms of ecological flow requirements and plans for development in this area include a coal-fired power station and a coal mine.
This environmental status is elaborated in the table below, with the Environmental Management Classes defined as above and estimated Environmental Flow Requirements (EFR) calculated as a percentage of mean annual runoff (MAR). The comments column of the table provides specific reference to issues that may or do affect the EFR.
Sub-catchment | EMC or estimated EMC | Estimated EFR (% of MAR) | Comments |
---|---|---|---|
Marico | C | 20 | Large dams and irrigation activities |
Crocodile | C | 20 | Urbanised and large irrigation areas with dams |
Mokolo | C | 20 | Many farm dams and irrigation |
Matlabas | C | 20 | Many farm dams and irrigation |
Lephalala | D | 13 | Undeveloped but low Ecological Water Requirement |
Mogalakwena | C | 20 | Mining, dams and irrigation |
Sand | B | 28 | Largely natural |
Nzhelele | D | 13 | Irrigation and dam |
Levuvhu | B | 28 | Kruger National Park (KNP) |
Shingwedzi | A | 40 | Originates in KNP |
Letaba | B | 28 | Very developed but flowing through KNP |
Upper Olifants | D | 13 | Highly modified with mines, dams and irrigation |
Lower Olifants | C | 20 | Developed but releases for KNP |
Shashe | B | 28 | Development only Upper Shashe |
Mzingwani | B/C | 24 | Development (Bulawayo) in upper reaches of Mzingwane |
Bubi | B | 28 | Largely natural |
Mwenezi | B | 28 | Largely natural |
Notwane | B/C | 24 | Notwane Dam for water supply in Gaborone |
Bonwapitse | B | 28 | Largely natural |
Mahalapswe | B | 28 | Largely natural |
Lotsane | B | 28 | Largely natural |
Motloutse | B | 28 | Largely natural |
Lower Middle Limpopo | C | 16 | Massingir Dam |
Lower Limpopo | C | 15 | Irrigation from Macarrentane |
Changane | A/B | 35 | Natural |
Source: LBPTC 2010
For a detailed discussion of environmental flow requirements in the Limpopo River basin and the relevant legislation see Environmental Flows in Resource Management.
LIMCOM's current ongoing interventions being undertaken