western cape intra-governmental shale gas task team
Transcription
western cape intra-governmental shale gas task team
WESTERN CAPE INTRA-GOVERNMENTAL SHALE GAS TASK TEAM: YOUR BASIC GUIDE TO SHALE GAS EXTRACTION AND RELATED SUBJECTS CONTENT PAGE 1. The Situation at Present ....................................................................... 3 2. Introduction and Context Specific Information ................................ 5 3. Shale Gas and the Extraction Process ................................................ 6 4. The Way Forward ..................................................................................15 5. Uncertainties ........................................................................................ 16 6. Opportunities ........................................................................................18 7. Risk Consideration ............................................................................... 18 8. More Facts ............................................................................................19 9. Official Communication ...................................................................... 20 2 THE SITUATION AT PRESENT The National Department of Mineral Resources recently released an executive summary on the Investigation of Hydraulic Fracturing in the Karoo Basin of South Africa which contains key recommendations. The report was released after the announcement on Friday 07 September 2012 that the moratorium on the consideration of shale gas exploration, which was declared in February 2011, had been lifted. The report that supported this decision contained the following key recommendations: • Allow normal exploration (excluding the actual hydraulic fracturing), such as geological field mapping and other date gathering activities (e.g.) hydrological studies) to proceed under the existing regulatory framework. • Constitute a monitoring committee to ensure comprehensive and co-ordinated augmentation of the regulatory framework and supervision of operations. • Augment the current regulatory framework. The establishment of the appropriate regulations, controls and co-ordination systems is expected to take 6-12 months. • Department of Science & Technology and Mineral Resources to collaborate in developing mechanisms for the co-existence of the Astronomy Research Projects and development of shale gas in the Karoo. • Once all the preceding actions have been completed, authorise hydraulic fracturing under strict supervision of the monitoring committee. In the event of any unacceptable outcomes, the process may be halted. • Ongoing research to be conducted and facilitated by relevant institutions to develop and enhance science knowledge in respect of the development of Karoo shale gas. This includes, albeit to limited to, geo-hydrology of the prospective areas, methodologies for hydraulic fracturing in RSA and environmental impacts. • The actions required to give effect to the proposed conditional approval must be properly resourced, incorporated into the programmes of the relevant departments and agencies and capacity developed. 3 THE SITUATION AT PRESENT contd. The lifting of the moratorium now makes it possible for the Department of Mineral Resources to consider and decide on applications for exploration for shale gas in the Karoo Basin. The merits of each application will have to be considered with due regard to the associated impacts of the exploration processes. While the exploration must obtain the necessary approval in terms of the Mineral and Petroleum Resources Development Act (Act No. 28 of 2002), approvals will also have to be obtained in terms of the Land Use Planning Ordinance (Ordinance 15 of 1985), and if listed activities are involved, environmental authorisation will also have to be obtained in terms of the National Environmental Management Act (Act No. 107 of 1998). Even if all the approvals were to be granted, careful monitoring will be required to ensure compliance and continued good environmental management. With a focus on responsible governance, the Western Cape Provincial Minister of Local Government, Environmental Affairs and Development Planning requested the Department of Environmental Affairs and Development Planning to report on the implications of shale gas extraction in the Western Cape and specifically the Central Karoo District municipality. The terms of reference to the Department were: • to establish an intra-governmental task team to investigate the opportunities and risks associated with shale gas extraction; and • to convey the task team’s findings in a report to be submitted to the Western Cape Cabinet to inform policy debates. With a focus on responsible governance, the Western Cape Government wants to encourage on-going and informed debate on the issue of shale gas exploration and extraction. 4 INTRODUCTION AND CONTEXT SPECIFIC INFORMATION The recovery of shale gas by hydraulic fracturing has sparked considerable debate and reaction from various stakeholders globally, including South Africa. At the heart of this debate is the tension between the anticipated economic benefit and the potential environmental and social impacts which accompany shale gas extraction. South Africa’s economy is energy intensive. The energy mix is dominated by coal-derived electricity for industry and domestic use, direct coal use in minerals refining and petroleum-based products for transport. South Africa has made an international commitment to reduce its 2020 carbon footprint by an amount equal to 34% below a business-asusual scenario. Currently, about 50% of the country’s greenhouse gas emissions (GHG) are from electricity production, a further 20% from the metallurgical industry, and 10% from transport (Devarajan et al, 2009). The national Integrated Resource Plan (IRP, 2010) for electricity generation proposes to effectively double the country’s current electricity generating capacity by 2030. About 40% of this additional installed capacity will come from renewable energy (principally wind and PV solar, with a smaller contribution from hydro), with the total proposed contribution of gas only about 7%. Natural gas represents a significant opportunity for further economic development in the Western Cape (and South Africa). It strengthens energy security and will support regional development through its use for power generation, minerals beneficiation, synthetic fuels and chemicals production. These investment opportunities can be realised in the short to medium term separately from the production of shale gas by utilising available known gas sources, such as off-shore gas fields in Mozambique and Tanzania or off the West Coast between Cape Town and Namibia. Therefore, investment in imported liquid natural gas (LNG) at this time will help to establish downstream markets that can become available for (potential) shale gas production in the future. 5 SHALE GAS AND THE EXTRACTION PROCESS Shale gas occurs in compact rock formations with low permeability, compared to conventional gas resources that occur in porous rock formations trapped below layers of impermeable rock formations. Due to its low permeability that do not allow for easy circulation of the gas in the rock, the flow and recovery of gas are achieved through the process of hydraulic fracturing at depths of between 4000 m and 5000 m along vertical and horizontal wellbores. Hydraulic fracturing is the process where a mixture of water sand and chemicals tailored to suit the target rock formation, is forced into the well at extremely high pressure to fracture the formation and to stimulate the flow of gas to the surface (Steyl et al 2012). The Karoo is a water-stressed environment, and there are no surface water sources with sufficient water for hydraulic fracturing, even at the prospecting phase. Each stage in a multi-stage fracturing operation requires around 1 100 – 2 200 m3 of water; the entire multi-stage fracturing for a single well requires about 9 000 – 29 000 m3 of water, with chemical additives of up to 2% by volumes, that is, about 180 – 580 m3. For all fracturing operations carried out on a six well pad, a total of 54 000 – 174 000 m3 of water would be required for the first hydraulic fracturing procedure and, with chemical additives of up to 2% by volume, that is, about 1 000 – 3 500m3 of chemicals (Minnesota Department of Natural Resources, 2012). Figure 1 below illustrates the typical activities associated with shale gas extraction. This is schematic only, and different options exist for delivering water to site, injecting the hydraulic fracturing cocktail, and removing waste water. 2 It must be noted that amounts of water used, as well as the volumes of flowback water, differs significantly in the international literature quoted in this report. This is to be expected based on differences between geological formations, technologies used, drilling depth, etc. 6 SHALE GAS AND THE EXTRACTION PROCESS contd. Figure 1: Typical activities associated with shale gas extraction (source: US EPA, 2011) At the conclusion of the fracturing procedure, fluid returns to the surface as ‘flowback’. Fracturing fluid components of significant concern are gelling agents, surfactants and chlorides; others are dissolved solids, metals, biocides, lubricants and organics. Shale formations may contain acid-producing minerals (e.g. sulphides), naturally occurring radioactive materials (NORMs) and other toxic metals (e.g. copper, aluminium, cadmium, arsenic, lead and mercury). The mobility of NORMs and metals and their potential to impact on groundwater are increased when they are dissolved or suspended in fracturing fluids that are brought to the surface. Fluids that are recovered range from 10 - 75% of the volume injected depending on the site (US EPA 2011). Accordingly, each well on a multiwell pad will generate between 1 300 – 23 000 m3 of flowback waste fluid containing water, fracturing chemicals and subsurface contaminants mobilised during the process, which includes toxic organic compounds heavy metals and NORMs. Similarly, any flowback fluid that is not recovered remains underground where there is concern that it is, or may become, a source of contamination to other formations including aquifers. 7 Figure 1: Extent of Shale Gas formations in South Africa 8 The figure below reflects a limited number of exploration areas that are distributed across three precincts. The exploration will last approximately one year. The map below also identifies the areas that have been identified for these explorations. Step 1: Create access roads (if needed) & prepare drilling pad. 9 Steps in the Exploration (including hydraulic fracturing) & Shale Gas Production Process Step 2: Bring in drilling rig & drill a vertical well, & then drill horizontally outward into the layer of shale (~30 days). Steps in the Exploration (including hydraulic fracturing) & Shale Gas Production Process 10 Step 3: Bring in the water & pump trucks, undertake hydraulic fracturing, & manage flow-back (~20 days). 11 Steps in the Exploration (including hydraulic fracturing) & Shale Gas Production Process Step 4: Remove fracturing equipment, secure well & site. Steps in the Exploration (including hydraulic fracturing) & Shale Gas Production Process 12 Step 5: Install pipeline to a storage facility and ultimately to the market. Steps in the Exploration (including hydraulic fracturing) & Shale Gas Production Process 13 • Rehabilitate the site • Plug the well • Decommission the well pad (remove equipment) Step 6: At the end of production life of a well: Steps in the Exploration (including hydraulic fracturing) & Shale Gas Production Process 14 THE WAY FORWARD Now that the moratorium has been lifted, the commencement of any exploration operations will be subject to various statutory approval processes. Adherence to the statutory requirements of the relevant environmental legislation constitutes part thereof. In general, the National Environmental Management Act, 1998 provides the framework for environmental management in South Africa that gives effect to the environmental right as contained in the Constitution. In particular, the environmental management principles contained in the National Environmental Management Act provides guiding principles for informed decision making. Applicants are now able to submit applications for exploration rights to the competent authority for consideration. The table below lists: • the type of decision to be concluded; • the competent authority who concludes the associated decision; and • the legislation guiding competent authority during decision making. DECISION COMPETENT AUTHORITY LEGISLATION Environmental Authorisation DEA&DP / National Department of Environmental Affairs NEMA Atmospheric Emission Licence Land use zoning departures Provincial Department on behalf of District Municipality Relevant local authority NEMA: AQA Land use zoning departures appeals Provincial competent authority LUPO Rezoning applications Provincial competent authority LUPO Water licence National Water Affairs Water Act LUPO 15 UNCERTAINTIES There are a number of uncertainties and information gaps that makes it difficult and in certain instances not possible to accurately determine the profile of certain opportunities and risks. The lack of information on the receiving environment (especially the subsurface environment), as well as the nature and extent of development, makes it difficult to clarify the consequences (extent) of opportunities/risks and the likelihood that these opportunities/risks will occur. The potential contribution of shale gas to South Africa’s energy mix needs to be examined in light of the risks and present uncertainties associated with development of this resource. Apart from the obvious one (is there any gas in the Karoo; and if so, is it an attractive development proposition?) there is a need to clarify those uncertainties which preclude a definitive assessment of the attendant socio-economic benefits, as well as the environmental and social risks. Beyond that, there is a need to understand the extent to which these underlying risks can be mitigated. The key uncertainties and information gaps include: • The size and nature of the shale gas reserve. This in turn will influence well density and roll-out during the production phase, that is, how many and their areal extent and the rate of production. Many of the potential positive and negative impacts associated with shale gas extraction can only be quantified once this information is known; • A better understanding of the impact associated with the use of available and changing (best practice) technologies; • Improving our understanding of the receiving environment, especially the geohydrological environment. The chemical and physical properties of the subsurface environment will influence the chemical properties of the flowback and production fluid, and the potential environmental impacts associated with their management; • Determining the institutional context that will be needed to support the implementation of a shale gas industry. South Africa does not have adequate capacity (knowledge/skills, human resources, technical equipment and financial resources) at any of the institutional levels in government (i.e. municipal, provincial; and national spheres) to deal with the anticipated general servicing, regulation and compliance monitoring and enforcement that will be associated with shale gas extraction; 16 UNCERTAINTIES contd. • Understanding the socio-ecological implications (now and in future) related to shale gas operations and considering the nature of the receiving environment; • A significant investment will have to be made to establish the necessary infrastructure and create the institutional capacity to maintain this expanded infrastructure; • Determining the sources of water and sand that will be used during the hydraulic fracturing process, both during the exploration and production phases are not known; • Understanding the chemical properties of the hydraulic fracturing fluid that will be used and the implications thereof; • The method of waste water treatment and final discharge during the prospecting and the production phases.; and • The legacy of managing well integrity in perpetuity to prevent well failure is poorly understood. These challenges are interrelated, and the short and medium term focus should be on information gathering - an expanded knowledge-base is a prerequisite for any future decision regarding shale gas in South Africa. 17 RISK CONSIDERATIONS The risks and uncertainties involved are listed below: Hazards Benefits Financial and Human Resources Country does not have the capacity at any institutional level to manage the anticipated general servicing of the industrial processes. Ground water impacts Sound baseline information must be gathered regarding the volume and quality of water sources that are currently utilised for domestic and agricultural purposes before any exploration is undertaken. A strategic assessment of the use of deeper aquifers for alternative long term beneficial use in the area should be done. Water treatment and disposal Standards for treatment need to be put in place for the contaminants not already considered under legislation. The re-use and flowback and production water must be implemented. Dedicated treatment facilities need to be put in place before exploration and production takes place. Greenhouse Gas Emissions Technologies need to be investigated and implemented in order to reduce the GHG emissions from these activities. A life-cycle assessment of emissions from energy sources needs to be developed in order to determine the impact of shale gas on South Africa’s energy picture and as a transitional fuel to a low carbon economy. Air Pollution Impacts A proactive approach must be taken that is focused on the avoidance of environmental impacts (air quality and noise). This can be achieved through the development of site selection criteria. Heritage Resources A strategic planning approach should be followed to ensure that sensitive landscapes and specific sites are avoided. Impact on Biodiversity The general recommendation is to exclude protected areas from shale gas exploration and production activities and related infrastructure development in general. Socio-economic impacts Pursue active community engagement to ensure that communities are capacitated to participate meaningfully in public debates and regulatory processes. 18 MORE FACTS The emergence of natural gas as an economically viable resource and recent developments in technology for recovery of fossil fuels from reservoirs with low permeability, such as hydraulic fracturing, has turned the spotlight on the exploration potential of Karoo sediments (Steyl et al 2012). Though available geoscientific data is limited, current estimates suggest that the Karoo Basin has a commercially viable recoverable resource, that is, about 30 trillion cubic feet (Tcf) to about 500 Tcf. Figure 1 below shows the geographical extent shale rock formations which could potentially be targeted the shale gas exploration and extraction. It also depicts the areas for which the Department of Mineral Resources (“DMR”) has recently allocated operating permits for exploration to 5 companies. Operator Permits (TCPs) Shell 185,000km2 Sasol / 88,000km2 Chesapeake / Statoil Anglo Coal 50,000km2 Falcon 30,000km2 Sunset 4,600km2 Total 357,600km2 Figure 2: Extent of the shale formations in South Africa, as well as the coverage of the Operating Permits (USEIA, 2011) 19 OFFICIAL COMMUNICATION It is important to note that only authorised officials may divulge any information on this matter. The subject of shale gas extraction will be managed in terms of the Media Policy of the Department of Environmental Affairs and Development Planning. Contact: Media & External Relations: Aziel Gangerdine +27 (0)21 483 4643 +27 (0)71 866 9887 Aziel.Gangerdine@westerncape.gov.za Technical: Paul Hardcastle +27 (0)21 483 5687 +27 (0)82 889 9065 Paul.Hardcastle@westerncape.gov.za Gerhard Gerber +27 (0)21 483 2787 +27 (0)83 226 9127 Gerhard.Gerber@westerncape.gov.za Disclaimer: This document is intended for informational purposes only and does not constitute legal, technical, business or other advice and should not be relied on as such. Please consult a professional advisor if you have any questions related to the topics discussed in the report. The Western Cape Government does not make any express or implied warranties, or assumes any legal liability for the accuracy, completeness, timeliness or usefulness of any information contained in this document. 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............................................................................................................................. ............................................................................................................................. 23 PRODUCED BY : Western Cape Department of Environmental Affairs and Development Planning Utilitas Building, 01 Dorp Street, Cape Town, 8001 Private Bag X9086, Cape Town, 8000 Website: www.westerncape.gov.za/eadp