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− | [[Africa Groundwater Atlas | + | [[Overview of Africa Groundwater Atlas | Africa Groundwater Atlas]] >> [[Hydrogeology by country | Hydrogeology by country]] >> Hydrogeology of Namibia |
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==Authors== | ==Authors== | ||
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'''Arnold Bittner''', SLR Environmental Consultants, Namibia | '''Arnold Bittner''', SLR Environmental Consultants, Namibia | ||
− | + | '''Brighid Ó Dochartaigh''', '''Kirsty Upton''', British Geological Survey, UK | |
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− | ''' | ||
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==Geographical Setting== | ==Geographical Setting== | ||
− | [[File:Namibia_Political.png | right | frame | | + | [[File:Namibia_Political.png | right | frame | Map of Namibia (For more information on the datasets used in the map see the [[Geography | geography resources section]])]] |
===General=== | ===General=== | ||
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{| class = "wikitable" | {| class = "wikitable" | ||
|- | |- | ||
− | |Capital | + | |Estimated Population in 2013* || 14,538,640 |
+ | |- | ||
+ | |Rural Population (% of total)* || 60.0% | ||
+ | |- | ||
+ | |Total Surface Area* || 743,390 sq km | ||
+ | |- | ||
+ | |Agricultural Land (% of total area)* || 32.1% | ||
+ | |- | ||
+ | |Capital City || Lusaka | ||
|- | |- | ||
− | |Region || | + | |Region || Eastern Africa |
|- | |- | ||
− | |Border | + | |Border Countries || Angola, Democratic Republic of the Congo, Malawi, Mozambique, Namibia, Tanzania, Zimbabwe, Botswana |
|- | |- | ||
− | | | + | |Annual Freshwater Withdrawal (2013)* || 1572 Million cubic metres |
|- | |- | ||
− | | | + | |Annual Freshwater Withdrawal for Agriculture (2013)* || 73.3% |
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− | | | + | |Annual Freshwater Withdrawal for Domestic Use (2013)* || 18.5% |
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− | | | + | |Annual Freshwater Withdrawal for Industry (2013)* || 8.3% |
|- | |- | ||
− | | | + | |Rural Population with Access to Improved Water Source (2012)* || 49.2% |
+ | |- | ||
+ | |Urban Population with Access to Improved Water Source (2012)* || 84.8% | ||
|} | |} | ||
− | <nowiki>*</nowiki> Source: | + | <nowiki>*</nowiki> Source: World Bank |
===Climate=== | ===Climate=== | ||
− | + | <gallery widths="375px" heights=365px mode=nolines> | |
+ | File:Namibia_ClimateZones.png |Koppen Geiger Climate Zones | ||
+ | File:Namibia_ClimatePrecip.png |Average Annual Precipitation | ||
+ | File:Namibia_ClimateTemp.png |Average Temperature | ||
+ | </gallery> | ||
− | [[ | + | For further details on these climate datasets, see the [[Climate | climate resources section]]. |
− | + | A summary of the climate of Namibia is also available in the report [http://www.namhydro.com/downloads.html Groundwater in Namibia] (ed. Christelis & Struckmeier 2011). | |
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===Surface water=== | ===Surface water=== | ||
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− | [[File:Namibia_Hydrology.png | frame | | + | | [[File:Namibia_Hydrology.png | frame | Surface Water Map of Namibia. For more information on the datasets used in the map see the [[Surface water | surface water resources section]]]] |
+ | |} | ||
− | + | Information on the hydrology of Namibia is also available in the report [http://www.namhydro.com/downloads.html Groundwater in Namibia] (ed. Christelis & Struckmeier 2011). | |
===Soil=== | ===Soil=== | ||
+ | |||
{| | {| | ||
|- | |- | ||
− | | | + | | [[File:Namibia_soil.png | frame | Soil Map of Namibia. For more information on the datasets used in the map see the [[Soil | soil resources section]]]] |
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− | [[File:Namibia_soil.png | frame | ||
− | + | Information on soils in Namibia is also available in the report [http://www.namhydro.com/downloads.html Groundwater in Namibia] (ed. Christelis & Struckmeier 2011). | |
===Land cover=== | ===Land cover=== | ||
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− | + | There are three main land cover types in Namibia: desert, savanna and woodland. The Namib Desert comprises most of the desert land cover class. Various types of savanna vegetation cover much of the country. Woodland, largely forest savanna, occurs across much of the more humid northeast and in perennial river valleys, and some ephemeral river valleys. | |
− | + | [[File:Namibia LandCover.png]] | |
==Geology== | ==Geology== | ||
− | + | The following summary of the geology of Namibia is based around 12 geological units that were defined according to their hydrogeological characteristics as part of the development of the Hydrogeological Map of Namibia (2011). This map, at 1 000 000 scale, was prepared as a Namibian – German technical cooperation project of the Department of Water Affairs, Ministry of Agriculture, Water and Rural Development; the Geological Survey of Namibia, Ministry of Mines and Energy; the Namibia Water Corporation and the Federal Institute for Geoscience and Natural Resources. The map is accompanied by a report [http://www.namhydro.com/downloads.html Groundwater in Namibia] (ed. Christelis & Struckmeier 2011). More details on Namibia's hydrogeology can be found in the section below. | |
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+ | Different geological maps are produced by the Geological Survey of Namibia. These include a simplified geological map of Namibia at 1:2 000 000 scale, a geological map of Namibia at 1:1 000 000 scale in 4 sheets, and a series of geological map sheets at 1:250 000 scale covering parts of the country. More details are available from the [http://www.gsn.gov.na/mapping.htm Geological Survey of Namibia]. Other more detailed information on the geology of Namibia can be found in the references that are given below: many of these are available through the [http://www.bgs.ac.uk/africagroundwateratlas/index.cfm Africa Groundwater Literature Archive]. | ||
− | + | The following section provides a summary of the geology of Namibia from a hydrogeological perspective. In defining the 12 geological units below, the main emphasis was on the groundwater potential of the rocks. Although stratigraphic relationships and spatial distribution were taken into consideration, some of the units include geological formations of more than one age or lithology. | |
+ | [[File:Namibia_Geology.png]] | ||
===General Summary=== | ===General Summary=== | ||
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{| class = "wikitable" | {| class = "wikitable" | ||
− | |+ | + | |+ Hydrogeological Units |
− | |'''Unit Number'''||''' | + | |'''Unit Number'''||'''Hydrogeological Unit'''||'''Key Formations'''||'''Period'''||'''General lithology and structure''' |
|- | |- | ||
|1||Sand and gravel valley deposits||Alluvium ||Recent||Recent sedimentary infill of valleys, including the courses of some ephemeral rivers. Occasionally extensive. | |1||Sand and gravel valley deposits||Alluvium ||Recent||Recent sedimentary infill of valleys, including the courses of some ephemeral rivers. Occasionally extensive. | ||
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|11||Metamorphic rocks, including quartize and marble bands, with granitic intrusions||||Neoproterozoic to Cambrian||Including many of the same formations as Unit 10, but also including granites which were intruded into Damaran metasedimentary rocks in a broad zone between Otjiwarongo and Okahandja and the coast, during mountain building processes between 650 and 450 Ma. Individual granite bodies that are too small to be shown separately on the hydrogeological map (as Unit 12) are included here with the surrounding metamorphic rocks. | |11||Metamorphic rocks, including quartize and marble bands, with granitic intrusions||||Neoproterozoic to Cambrian||Including many of the same formations as Unit 10, but also including granites which were intruded into Damaran metasedimentary rocks in a broad zone between Otjiwarongo and Okahandja and the coast, during mountain building processes between 650 and 450 Ma. Individual granite bodies that are too small to be shown separately on the hydrogeological map (as Unit 12) are included here with the surrounding metamorphic rocks. | ||
|- | |- | ||
− | |12||Granite, gneiss and old volcanic rocks||Epupa and Kunene complexes; Orange River Group; Vioolsdrif Suite; Elim Formation; Khoabendus Group; | + | |12||Granite, gneiss and old volcanic rocks||Epupa and Kunene complexes; Orange River Group; Vioolsdrif Suite; Elim Formation; Khoabendus Group; Reheboth Sequence; Namaqualand Metamorphic Complex; Sinclair Sequence; Fransfontein Suite and Gamsberg Granite||Archaean to Jurassic||This unit includes a multitude of lithologies that almost covers the entire geological history of Namibia. Vaalian rocks comprise the gneisses of the Epupa Complex and the intrusives of the Kunene Complex. Early Mokolian rocks include gneisses and meta-volcanics of the old metamorphic complexes, metavolcanics of the Orange River Group, granites of the Vioolsdrif Suite, gneisses of the Elim Formation and meta-volcanics and gneisses of the Khoabendus Group. Middle to late Mokolian rocks of this unit are the meta-volcanics of the Rehoboth Sequence, the gneisses of the Namaqualand Metamorphic Complex, the meta-volcanics of the Sinclair Sequence, the granites of the Fransfontein Suite, as well as the younger granites, for example the Gamsberg Granite. The unit also comprises a range of syn- to post- tectonic granites which intruded Damaran sedimentary rocks during the Damaran Orogeny. Complex igneous intrusions with ages of about 135 Ma occur in a zone extending northeast from the coast north of Swakopmund. Some of them are extremely complex layered intrusions and contain rhyolite, grano phyre, granite, syenite, foyaite, gabbro, dunite, pyroxenite and carbonatite. They are not related to any orogeny and interpreted as a result of a hot mantle plume. |
|} | |} | ||
==Hydrogeology== | ==Hydrogeology== | ||
− | + | The hydrogeology of Namibia is described in detail in the report [http://www.namhydro.com/downloads.html Groundwater in Namibia] (ed. Christelis & Struckmeier 2011), which accompanies the Hydrogeological Map of Namibia. The following section provides a summary. Readers wishing more detailed information should consult the detailed report (ed. Christelis & Struckmeier 2011) and/or the references given below, many of which are available through the [http://www.bgs.ac.uk/africagroundwateratlas/index.cfm Africa Groundwater Literature Archive]. | |
The aquifers of Namibia have been classed according to whether they are consolidated (hard rock) or unconsolidated; according to the type of porosity and permeability they show (porous/intergranular or fractured, fissured or karstified); and according to how much groundwater resource potential they have. They have also been qualified according to the presence of saline or otherwise poor quality groundwater. The hydrogeological map, shown below, shows the distribution of these aquifer types across the country. General properties of each of the main aquifer types are given in the table below. | The aquifers of Namibia have been classed according to whether they are consolidated (hard rock) or unconsolidated; according to the type of porosity and permeability they show (porous/intergranular or fractured, fissured or karstified); and according to how much groundwater resource potential they have. They have also been qualified according to the presence of saline or otherwise poor quality groundwater. The hydrogeological map, shown below, shows the distribution of these aquifer types across the country. General properties of each of the main aquifer types are given in the table below. | ||
− | + | [[File:simple-hgcl-map.png]] | 500x195px]] | |
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||Recharged by river leakage when ephemeral Kuiseb River flows | ||Recharged by river leakage when ephemeral Kuiseb River flows | ||
|- | |- | ||
− | | | + | |Ohangwena Aquifer System (Unit 1) |
+ | || | ||
+ | || | ||
+ | || | ||
+ | |- | ||
+ | |Cuvelei-Ethosa Basin (Unit 1 and ?) | ||
||This is a three layered system dominated by unconsolidated sand with some sandstones, with an average aquifer thickness of 220 m. It has a high primary porosity with no secondary porosity, and high horizontal connectivity. The average transmissivity value is 220 m²/day. The average piezometric level is 30 m below ground level, and the aquifer is mostly confined, but in some parts is unconfined. Typical borehole depth is 100 to 250 m. | ||This is a three layered system dominated by unconsolidated sand with some sandstones, with an average aquifer thickness of 220 m. It has a high primary porosity with no secondary porosity, and high horizontal connectivity. The average transmissivity value is 220 m²/day. The average piezometric level is 30 m below ground level, and the aquifer is mostly confined, but in some parts is unconfined. Typical borehole depth is 100 to 250 m. | ||
||About 35% of the deep aquifer has groundwater that is unsuitable for drinking water. | ||About 35% of the deep aquifer has groundwater that is unsuitable for drinking water. | ||
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|- | |- | ||
|} | |} | ||
+ | |||
+ | Key sources of more information on some these aquifers are: | ||
+ | |||
+ | ''Cuvelai-Ethosa Basin:'' | ||
+ | |||
+ | Falk L and Christelis G. 2012. Groundwater for the North of Namibia (Cuvelai-Etosha Basin)- Exploration of Ohangwena two Aquifer and Preliminary Isotope study. Department of Water Affair and Forestry/BGR | ||
====Fractured, Fissured or Karstified Aquifers==== | ====Fractured, Fissured or Karstified Aquifers==== | ||
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||The aquifer is recharged mainly by direct infiltration of rainfall over areas of quartzite outcrop. A new system of artificially recharging the Windhoek aquifer has recently been tested. Treated water from Von Bach Dam is pumped into the Windhoek production boreholes and stored underground to reduce water losses from evaporation. Many years of abstraction have lowered the water table, creating enough open pore space to allow infiltration of up to 50 Mm³ of water when the dams are sufficiently full. | ||The aquifer is recharged mainly by direct infiltration of rainfall over areas of quartzite outcrop. A new system of artificially recharging the Windhoek aquifer has recently been tested. Treated water from Von Bach Dam is pumped into the Windhoek production boreholes and stored underground to reduce water losses from evaporation. Many years of abstraction have lowered the water table, creating enough open pore space to allow infiltration of up to 50 Mm³ of water when the dams are sufficiently full. | ||
|- | |- | ||
− | |Caprivi Aquifer (Nata Karoo Sub-basin) (Units 5 and | + | |Caprivi Aquifer (Nata Karoo Sub-basin) (Units 5 and 6?) |
||The Caprivi aquifer underlies the unconsolidated Kalahari Sequence (see above)and has an average thickness of 82 m. The formation has high primary porosity, and high vertical and horizontal connectivity. The average transmissivity is 193 m²/day. | ||The Caprivi aquifer underlies the unconsolidated Kalahari Sequence (see above)and has an average thickness of 82 m. The formation has high primary porosity, and high vertical and horizontal connectivity. The average transmissivity is 193 m²/day. | ||
− | Groundwater levels are generally shallow. The aquifer is confined. Variable borehole yields from | + | Groundwater levels are generally shallow. The aquifer is confined. Variable borehole yields from zero to more than 20 m³/hour are seen. Borehole depths vary from 50 to 150 m. |
||About 60% of the shallow aquifer is unsuitable for drinking water. | ||About 60% of the shallow aquifer is unsuitable for drinking water. | ||
||Total mean annual recharge is 15 Mm³ | ||Total mean annual recharge is 15 Mm³ | ||
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!colspan="4"|Fractured, Fissured or Karstified Aquifers with Moderate Potential | !colspan="4"|Fractured, Fissured or Karstified Aquifers with Moderate Potential | ||
|- | |- | ||
− | |Eiseb Aquifer (Northern Kalahari / Karoo Basin) ( | + | |Eiseb Aquifer (Northern Kalahari / Karoo Basin) (Units 5 and 6?) |
||This aquifer is a 2 layer system with both shallow Kalahari unconsolidated sedimentary sands (see above), and deeper Karoo consolidated sedimentary rocks, which may hold some potential for increased amounts of water, although this is still uncertain. The presence of a palaeo channel that contains abundant groundwater within a largely surrounding water scarce area is an example of the groundwater potential. The average aquifer thickness is around 130 m. The aquifer is mainly confined, although parts are unconfined. The average transmissivity values are 150 m²/day. Typical borehole depths are between 120 and 180 m. | ||This aquifer is a 2 layer system with both shallow Kalahari unconsolidated sedimentary sands (see above), and deeper Karoo consolidated sedimentary rocks, which may hold some potential for increased amounts of water, although this is still uncertain. The presence of a palaeo channel that contains abundant groundwater within a largely surrounding water scarce area is an example of the groundwater potential. The average aquifer thickness is around 130 m. The aquifer is mainly confined, although parts are unconfined. The average transmissivity values are 150 m²/day. Typical borehole depths are between 120 and 180 m. | ||
||About 20% of the aquifer contains groundwater that is unsuitable for drinking water. | ||About 20% of the aquifer contains groundwater that is unsuitable for drinking water. | ||
||Mean annual recharge is 10 Mm³/annum | ||Mean annual recharge is 10 Mm³/annum | ||
|- | |- | ||
− | |SE Kalahari Karoo Basin (Units 5 and | + | |SE Kalahari Karoo Basin (Units 5 and 6?) |
||The aquifer is dominated by sandstones and shales, overlain by unconsolidated Kalahari sediments. Dolerite sills and dykes occur, more frequently towards the central parts of the basin, and sometimes enhance the level of fracturing within the sedimentary rock. The sandstones are characterized by a high primary porosity, and by secondary porosity fractures. There is a high horizontal connectivity while the vertical connectivity is generally low. The average transmissivity values are relatively low although the variation is relatively large within the system. The average transmissivity is 20 m²/day. | ||The aquifer is dominated by sandstones and shales, overlain by unconsolidated Kalahari sediments. Dolerite sills and dykes occur, more frequently towards the central parts of the basin, and sometimes enhance the level of fracturing within the sedimentary rock. The sandstones are characterized by a high primary porosity, and by secondary porosity fractures. There is a high horizontal connectivity while the vertical connectivity is generally low. The average transmissivity values are relatively low although the variation is relatively large within the system. The average transmissivity is 20 m²/day. | ||
|| | || | ||
− | || | + | || |
|- | |- | ||
+ | |} | ||
+ | |||
+ | Key sources of more information on these aquifers are: | ||
+ | |||
+ | ''Windhoek Aquifer:'' | ||
+ | |||
+ | Environmental Engineering Services. 2009. Artificial Recharge of the Windhoek Aquifer as best option for supply augmentation to the Central Area of Namibia. Draft Report, Department of Water Affairs and Forestry (unpublished). | ||
+ | |||
+ | ''Caprivi Aquifer (Nata Karoo Sub-basin):'' | ||
+ | |||
+ | Margane A, Roland B, Schildknecht F and Wierenga A. 2005. Groundwater investigation in the Eastern Caprivi Region - Main Hydrogeological report. Technical report, Department of Water Affairs and Foresty/BGR | ||
+ | |||
+ | |||
+ | ''The Eiseb Aquifer (Northern Kalahari / Karoo Basin):'' | ||
+ | |||
+ | Margane A. 2004. Investigation of Groundwater Resources and Airborne-Geophysical Investigation of Selected Mineral Targets in Namibia-Groundwater investigation in the Eiseb Graben, Evaluation of Pumping Test. Department of Water Affairs (DWA), Namibia/Federal Institute for Geosciences and Natural Resources (BGR) | ||
+ | |||
+ | |||
+ | ''SE Kalahari Karoo Basin:'' | ||
+ | |||
+ | Pacific Consultants International. 2002. The Study on the groundwater potential evaluation and management plan in the Southeast Kalahari (Stampriet) artesian basin in the Republic of Namibia. Japan International Cooperation Agency (JICA) and Department of Water Affairs and Forestly (DWAF) | ||
+ | |||
+ | Margane A, Roland B, Schildknecht F and Wierenga A. 2005. Groundwater investigation in the Eastern Caprivi Region - Main Hydrogeological report. Technical report, Department of Water Affairs and Foresty/BGR | ||
+ | |||
+ | ====Rock Bodies With Little Groundwater Potential==== | ||
+ | {| class = "wikitable" | ||
+ | |Named Aquifers||General Description||Water quantity issues||Water quality issues||Recharge | ||
+ | |- | ||
+ | |Aquitards / Rock Bodies with Generally Low but Locally Moderate Potential||G |||||| | ||
+ | |- | ||
+ | |Aquicludes / Rock Bodies with Very Low and Limited Potential|| || || || | ||
|} | |} | ||
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==Groundwater-Surface Water Interaction== | ==Groundwater-Surface Water Interaction== | ||
− | Groundwater-surface water interaction is strong along the perennial rivers at the northern and southern borders (Kunene and | + | Groundwater-surface water interaction is strong along the perennial rivers at the northern and southern borders (Kunene and Kavango in the north, Orange in the south), but this is not widely accounted for by the basin management bodies. |
Recharge of alluvial aquifers, especially in the coastal basins, depends on high run-off events in ephemeral rivers, which tend to occur at 4 to 8 year intervals. | Recharge of alluvial aquifers, especially in the coastal basins, depends on high run-off events in ephemeral rivers, which tend to occur at 4 to 8 year intervals. | ||
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Many farm or earth dams exist in the country - estimates are up to 1000 - which are partly used to recharge groundwater to improve yields of water supply boreholes. | Many farm or earth dams exist in the country - estimates are up to 1000 - which are partly used to recharge groundwater to improve yields of water supply boreholes. | ||
− | The potential for storing surface water in, for example, the Windhoek Aquifer, is not currently | + | The potential for storing surface water in, for example, the Windhoek Aquifer, is not currently utilised. Managed Aquifer Recharge (MAR) could be key to dealing with increasing future demand. This will particularly be true in the case of an increase of extreme climatic events, as predicted in numerous climatic models. |
In the Caprivi aquifer (Nata Karoo Sub-basin), although recharge occurs predominantly through direct precipitation, some recharge from rivers also occurs along the major drainage channels within the northern parts of the aquifer. | In the Caprivi aquifer (Nata Karoo Sub-basin), although recharge occurs predominantly through direct precipitation, some recharge from rivers also occurs along the major drainage channels within the northern parts of the aquifer. | ||
− | In the Cuvelai- | + | In the Cuvelai-Ethosa Basin, some recharge from the Okavango River system in Angola is probably occurring. |
In the Eiseb Aquifer (Northern Kalahari / Karoo Basin) the majority of recharge occurs through surface runoff. | In the Eiseb Aquifer (Northern Kalahari / Karoo Basin) the majority of recharge occurs through surface runoff. | ||
− | In the southeast Kalahari Karoo Basin, although the main recharge mechanism is through direct precipitation | + | In the southeast Kalahari Karoo Basin, although the main recharge mechanism is through direct precipitation, a certain amount of recharge also occurs through major rainfall event runoff in the ephemeral rivers that flow across the aquifer system. |
===Groundwater dependent ecosystems=== | ===Groundwater dependent ecosystems=== | ||
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Groundwater dependent ecosystems occur in west-flowing rivers and at river mouths. Riverine vegetation is dependent on shallow, fresh to brackish groundwater from alluvial aquifers, in an otherwise arid environment with saline groundwater. Animals such as the world renown ‘desert elephant’ also depend on that groundwater resource. | Groundwater dependent ecosystems occur in west-flowing rivers and at river mouths. Riverine vegetation is dependent on shallow, fresh to brackish groundwater from alluvial aquifers, in an otherwise arid environment with saline groundwater. Animals such as the world renown ‘desert elephant’ also depend on that groundwater resource. | ||
− | In the Cuvelai- | + | In the Cuvelai-Ethosa Basin, shallow groundwater and groundwater dependent ecosystems cover around 5% of the area. |
Groundwater in Coastal Basins often feeds estuaries along the coastline, forming prominent ecosystems, such as at Sandwich Harbour south of Walvis Bay, and the Orange River estuary on the border with South Africa. | Groundwater in Coastal Basins often feeds estuaries along the coastline, forming prominent ecosystems, such as at Sandwich Harbour south of Walvis Bay, and the Orange River estuary on the border with South Africa. | ||
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• Borehole hand pump | • Borehole hand pump | ||
− | • Improved spring | + | • Improved spring |
===Groundwater Management and Monitoring=== | ===Groundwater Management and Monitoring=== | ||
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The main institutions involved in groundwater management are: | The main institutions involved in groundwater management are: | ||
− | - the Department of Water | + | - the Department of Water affairs and Forestry, Directorate Resource Management. General observation/management |
− | + | - the Department of Water affairs and Forestry, Directorate Rural Water Supply and Sanitation. Coordination for rural usage | |
− | - the Department of Water | ||
− | |||
- NamWater. For bulk supply | - NamWater. For bulk supply | ||
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• The Namibia Water Corporation Act, Act No 12 of 1997 | • The Namibia Water Corporation Act, Act No 12 of 1997 | ||
− | • The Namibia Water Resources Management Act No 24 of 2004 – which was never commenced | + | • The Namibia Water Resources Management Act No 24 of 2004 – which was never commenced |
− | • The Revised Namibia Water Resources Management Act, | + | • The Revised Namibia Water Resources Management Act, whcih was gazetted in December 2013 |
New institutions with a role in groundwater management are: | New institutions with a role in groundwater management are: | ||
− | • The Water Regulator | + | • The Water Regulator |
− | • The Water Advisory Council | + | • The Water Advisory Council |
• The Basin Management Committees | • The Basin Management Committees | ||
− | • The Water Tribunal | + | • The Water Tribunal |
• Water Point Committees | • Water Point Committees | ||
− | A | + | A particular practical groundwater management activity is the delineation of groundwater control areas, which include the most highly productive aquifers, to promote the use of groundwater resources on a long-term sustainable basis. |
====Groundwater Monitoring==== | ====Groundwater Monitoring==== | ||
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Monitoring data have in the past been stored in the Geohydrology Division filing system, but a National Groundwater Database (GROWAS) has been designed to be the main storage facility for groundwater monitoring data, and is under improvement. | Monitoring data have in the past been stored in the Geohydrology Division filing system, but a National Groundwater Database (GROWAS) has been designed to be the main storage facility for groundwater monitoring data, and is under improvement. | ||
− | ==Transboundary aquifers== | + | === Transboundary aquifers=== |
A number of transboundary aquifers occur in Namibia, the main ones of which are: | A number of transboundary aquifers occur in Namibia, the main ones of which are: | ||
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• The Caprivi Aquifer (Nata Karoo Sub-basin) | • The Caprivi Aquifer (Nata Karoo Sub-basin) | ||
− | • The Cuvelai- | + | • The Cuvelai-Ethosa Basin |
• The Eiseb Aquifer (Northern Kalahari / Karoo Basin | • The Eiseb Aquifer (Northern Kalahari / Karoo Basin | ||
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All were included in the Transboundary Waters Assessment Programme (TWAP) carried out by GEF/UNESCO. More information about TWAP can be found on the [[Transboundary aquifers | Transboundary aquifers resources page]]. | All were included in the Transboundary Waters Assessment Programme (TWAP) carried out by GEF/UNESCO. More information about TWAP can be found on the [[Transboundary aquifers | Transboundary aquifers resources page]]. | ||
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==References== | ==References== | ||
− | Many of the references listed on this page, and others relating to the hydrogeology of | + | Many of the references listed on this page, and others relating to the hydrogeology of Zambia, can be accessed through the [http://www.bgs.ac.uk/africagroundwateratlas/searchResults.cfm?title_search=&author_search=&category_search=&country_search=ZM&placeboolean=AND&singlecountry=1 Africa Groundwater Literature Archive]. |
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<!-- PLEASE DO NOT DELETE BELOW THIS LINE --> | <!-- PLEASE DO NOT DELETE BELOW THIS LINE --> | ||
[[Category:Hydrogeology by country|n]] | [[Category:Hydrogeology by country|n]] | ||
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