ISP: LOWER ORANGE WMA Appendix B Groundwater Overview for Lower Orange Water Management Area 03 - APPENDIX B GROUNDWATER.DOC JULY 2004 B1 DEVELOPMENT OF INTERNAL STRATEGIC PERSPECTIVES GROUNDWATER OVERVIEW FOR LOWER ORANGE CATCHMENT MANAGEMENT AREA Prepared by: JA Pretorius and I Dennis Darcy Groundwater Scientists and Consultants Bloemfontein Prepared for: Directorate Water Resource Planning DWAF Private Bag X313 Pretoria SEPTEMBER 2003 TABLE OF CONTENTS 1 OVERARCHING ISSUES ........................................................................................................ 3 1.1 AVAILABILITY OF GROUNDWATER INFORMATION IN THE CATCHMENT AREA............................... 3 1.2 OVERVIEW OF GROUNDWATER RESOURCES AND USE THROUGHOUT THE CATCHMENT AREA .... 3 1.2.1 Industrial and mining.................................................................................................. 3 1.2.2 Agriculture.................................................................................................................. 3 1.2.3 Domestic .................................................................................................................... 3 1.3 GROUNDWATER QUALITY IN THE CATCHMENT AREA ............................................................... 4 1.3.1 Natural ....................................................................................................................... 4 1.3.2 Point and diffusive pollution ....................................................................................... 7 1.4 GROUNDWATER MANAGEMENT AND MONITORING REQUIREMENTS IN THE CATCHMENT AREA .... 9 1.4.1 Current groundwater monitoring and management................................................... 9 1.4.2 Current (quality and quantity) requirements ............................................................ 10 1.5 POVERTY ERADICATION AND THE ROLE GROUNDWATER CAN PLAY IN THE CATCHMENT........... 10 2 GROUNDWATER ACCORDING TO GEOLITHOLOGICAL UNITS AND CATCHMENTS ASSOCIATED OR ENCLOSED WITH THE UNITS (1: 1000 000 GEOLOGY). .......................... 10 3 RIVER BED SAND AQUIFERS............................................................................................. 12 4 GROUNDWATER-SURFACE WATER LINKAGE................................................................ 13 5 REFERENCES....................................................................................................................... 13 2 1 Overarching Issues The following is a brief description of the major groundwater issues in the Lower Orange Water Management Area (WMA). For more detailed information please refer to the references and the sources of data referred to in Section 1. 1.1 Availability of groundwater information in the catchment area The following data sources with regard to groundwater are available: • NGDB database • WARMS data base • DWAF Geohydrology Northern Cape • GH Reports • 1: 5000 000 Geohydrological maps and brochures • Consultants reports and other academic reports The NGDB is heavily populated with groundwater data for the WMA. There are over 400 points currently being monitored throughout the Northern Cape (including the Lower Vaal WMA). Most of the data are related to water supply schemes and ambient water quality monitoring. The WARMS database also contains valuable information with regard to large-scale abstraction for water supply schemes and irrigation. Verification of the data still has to be performed. The Geohydrology offices in the Northern Cape also has good data on groundwater utilization and the natural quality of groundwater due to the close relationship with ongoing water supply projects and other groundwater investigations. Another vast source of information is from GH reports (> 500) and the 1: 500 000 geohydrological maps completed for the region by the Geohydrology Directorate. Several consultant reports and academic reports are also available. PD Toens and Associates have been involved in ongoing monitoring of groundwater resources in the Northern Cape for a number of years. 1.2 Overview of groundwater resources and use throughout the catchment area 1.2.1 Industrial and mining Mining plays an important role in the WMA’s economic development. Several diamond mines are located in the WMA including the Kleinzee, Alexcor and Hondeklipbaai mines. Diamonds are recovered at these mines from alluvial deposits. A number of small-scale diamond diggings are also found in the area. Some impacts do exist with regard to localized dewatering of aquifers. These impacts are however localized and very little data exist in this regard. Black Mountain base metal mine utilizes surface water from the Orange River for processes and no data is available on the water resource utilized by the Okiep Copper Mines. 1.2.2 Agriculture Most farming settlements are dependent on groundwater for domestic and stock watering use. The groundwater resource is of such a nature that it cannot be utilized for large-scale irrigation throughout the WMA, except in the areas underlain by dolomitic aquifers. Volumes of total abstraction are available for this use. 1.2.3 Domestic As discussed above, groundwater is utilized for individual domestic use in most rural and farming areas. Groundwater is the most important resource for bulk water supply in areas located far from the surface water bulk supply network. The naturally poor quality (See Section 1.3.1) and 3 poor yields of some aquifers are a constraining factor in the utilization of this resource. This is overcome in some areas by good water management practices and treatment of the groundwater. Data received from DWAF (see Table 1) estimate the total abstraction for groundwater at 10 mil m3 per year for domestic supply for approximately 100 000 inhabitants dependant on the source (DWAF, 2003). The majority of the water (43%) is abstracted from the granite and gneiss aquifers (See Section 2), 25% is from the Dwyka and Ecca Karoo sediments, 17 % from the Beaufort Karoo sediments and the remainder is abstracted from the dolomites (6%) and other primary aquifers (2%). 1.3 Groundwater quality in the catchment area 1.3.1 Natural Groundwater quality is one of the main factors affecting the development of available groundwater resources. Although there are numerous problems associated with water quality, some of which are easily corrected, total dissolved solids (TDS), nitrates (NO3 as N) and flourides (F) are thought to represent the majority of serious water quality problems. The water quality was evaluated in terms of TDS and potability. The information was obtained from DWAF Geohydrology. The potability evaluation done was based on the evaluation of chloride, fluoride, magnesium, nitrate, potassium, sodium, sulfate and calcium using the Quality of Domestic Water Supplies, Volume 1 (DWAF, 1998). The portion of the groundwater resources considered to be potable has been calculated as the portion classified as ideal, good and marginal (Class 0 -blue, 1- green and 2 - yellow) according to the classification system given in Section 6.4.1. Water classified as poor and unacceptable (Class 3 - red and 4 - purple) is considered not to be potable (See Point and diffusive pollution Agricultural activities are a source of diffuse water contamination. The contribution of each farm on a local scale is often fairly small but the contribution on a catchment scale needs to be included in assessing any pollution situation. Most findings regarding this issue can only be assessed in a generic way due to the lack of data in the WMA. Nitrates are the contaminant of most concern, since they are very soluble and do not bind to soils, nitrates have a high potential to migrate to groundwater. Because they do not evaporate, nitrates/nitrites are likely to remain in water until consumed by plants or other organisms. Generally on a local scale the areas of intense cultivation are the major contributors in terms of inorganic nitrates. The primary inorganic nitrates, which may contaminate drinking water, are potassium nitrate and ammonium nitrate both of which are widely used as fertilizers. Where feedlots are operated the contribution of organic nitrates to groundwater contamination can be far more problematic. For most farming activities organic nitrate is not a severe problem in South Africa. High-density cultivation at surface water irrigation schemes along the Orange River contributes to the nitrate load of localized aquifers in the WMA. Other contaminants of concern are pesticides and herbicides. The contribution of these to groundwater contamination is very difficult to quantify on catchment scale. Site-specific data relating to likely loading/application volumes and history, soil profile and local geohydrology are required. Table 2). The mineralogical groundwater quality in the Lower Orange Water Management Area is not particularly good in terms of its TDS rating. In general the groundwater quality is rated as class 2 to class 4, marginal to completely unacceptable. The southern portion of the inland region, De Aar, Victoria West and Sutherland has a class 2 rating, together with the areas surrounding Prieska, Griekwastad, Upington and Springbok. The rest of the WMA, particularly north of Brandvlei and Carnarvon and the coastal strip are rated as class 3 and 4. The Sutherland, De Aar, Upington belt has a varying range of potable groundwater from a moderate 50% to approximately 90%. The balance of the WMA, has a predominant potable usage of less than 4 30%, with the occasional improvement to 50% (V3, 2002). See Figure 1 for