BRICS: Balancing Economic Growth and Environmental Sustainability
Throughout this growth period, BRICS countries have largely upheld policies to ensure affordability of energy to drive competitiveness in industry. Industry growth has been the primary driver of energy demand in countries like China, where industry accounted for nearly 50% of final energy consumption in 2012.84 These policies have, to some extent, been to the detriment of the environmental sustainability of the energy systems that developed as a consequence.
In response to growing environmental concerns, both China and India have set a range of targets to reduce the energy intensity of their economies and improve their climate metrics. China’s current Five-Year Plan has among its targets the reduction of energy intensity of its industry by 16% by 2015 from 2010 levels – this is further complemented by the 10-Point Plan adopted by the Chinese government in 2013 to tackle urban pollution. Similarly, India has plans to reduce carbon-intensity by 20-25% by 2020. To achieve these targets without hindering growth, BRICS countries need to realize opportunities to balance the imperatives of the energy triangle.
To achieve a 2°C increase scenario – to limit global warming to a 2°C increase to 2035 – the IEA suggests four key GDP-neutral emissions abatement measures: adopting energy efficiency measures; limiting use and further deployment of low-efficiency coal-based power plants; phasing out fossil fuel subsidies; and minimizing methane emissions from upstream oil and gas.
Given the diversity of energy systems within the BRICS countries, each measure is likely to have a varying degree of impact by country.
Adopting Energy Efficiency Measures
Energy efficiency measures in the industrial, residential and transportation sectors can make a strong contribution to reducing GHG emission globally.85 Potential efficiency measures in these sectors include the implementation of minimum energy performance standards (MEPS) in cooling/heating products, residential appliances and industrial equipment.
Addressing energy consumption of industry in economies such as China and India is key to achieving efficiency improvements. Aside from the roll-out of MEPS for industrial motors, China is increasing standards and regulation for its largest industrial energy consumers through a range of measures including the Top 10,000 Programme, which sets energy savings targets to 2015 for the largest industrial consumers accounting for 85% of energy demand in industry.86 According to the Chinese State Council, the programme could save an estimated 250 million tonnes of coal equivalent and 610 million tonnes of CO2 from 2011 to 2015. Similarly, in India, the “Perform, Achieve and Trade” initiative was set up as a mandatory trading system for energy efficiency obligations in some of the most energy-intensive industry industries.
In the Russian Federation, improvements in the residential and heating sector could be instrumental in addressing energy efficiency – 26% of total final energy consumption of the country in 2012 came from the residential sector, compared to less than 10% in Brazil. A recent study on the potential of energy efficiency in Russia estimates that efficiency measures in insulation, heating and appliances could account for over 60% of efficiency-related savings in a 2030 scenario.87
Limiting Use of Low-Efficiency Coal-Based Power Plants and Finding Alternative Lower-Carbon Sources
Coal-powered generation is predominantly a concern in China, India and South Africa. China accounted for 46% and India 9% of global coal consumption in 2011, while coal contributed to 70% of total primary energy supply in South Africa the same year. Most forecasts believe coal will continue to play a key role in meeting the increased energy demand in these countries. However, environmental pressures are driving these countries to identify measures to limit the use of low-efficiency coal power generation, in favour of more efficient fossil fuel technologies, or through investment in renewable energy capacity.
China is exploring a range of fiscal and financial disincentives and is currently piloting emission trading in its most emission-intensive districts – however, carbon trading schemes such as the EU ETS have had limited success to date. In addition, China has indicated the potential roll-out of a resource tax on coal, and the country’s 10-Point Plan to tackle pollution aims to reduce the proportion of coal in total energy consumption to 65% by 2017.88 A perspective from Lin Boqiang, Director at the China Centre for Energy Economics Research of Xiamen University, further expands on the transition pathway of China towards improving its energy-environmental performance. India and South Africa are also exploring a range of measures to reduce coal consumption and replace it with alternative, lower-carbon options.
Disincentives for coal consumption can contribute to creating an enabling environment for the deployment of low-carbon power generation. BRICS countries all have in place targets to increase their share of energy from renewable and low-carbon energy sources. Aside from having targets for renewable energy, India is continuing its long-term drive to increase the share of nuclear capacity from 4% in 2011 to 25%.89 Although installed renewable capacity has grown significantly over the past decade, cost competitiveness with fossil fuels, reliance on subsidies and incentives remain a challenge, underlining that more needs to be done to address cost and market structures for renewables.
Renewable energy is, however, unlikely to fill the base-load gap if coal capacity in these coal-dependent countries is significantly scaled back; instead, natural gas has a key role to play in filling the gap. Beyond the strategies to secure gas supplies from international markets, South Africa and China, which hold some of the largest recoverable shale gas reserves90 globally, can aspire to replicate the shale gas revolution in the US, which is seeing coal displaced by the cheaper and widely available natural gas. However, IEA estimates suggest that resource, technical and infrastructure requirements of shale recovery and the gas/coal price differential will mean development to scale will not occur before 2020.91
Phasing out Fossil-Fuel Subsidies
Phasing out fossil-fuel subsidies has a key role in improving the environmental performance in those BRICS countries where energy subsidies persist. Subsidies promote the inefficient use of energy, weigh on the economy and create market distortions which, among other things, impact the competitiveness of investing in renewable energy sources. In the BRICS cluster, Russia, India and South Africa have the highest fossil fuel subsidies, with an average 18% subsidization rate in India and Russia, and a 4% rate in South Africa.92
Subsidy reform globally has been challenging and a politically sensitive topic in a number of countries. Best practice in addressing subsidy reform emphasizes the importance of clearly communicating the objectives with stakeholders and consumers, planning a long-term, gradual phase-out, and monitoring the progress and impact of the policies.93 In Nigeria (2012) and Bolivia (2010), overnight significant reductions on subsidies were met with public protests and civil unrest – drawing attention to the need for long-term planning and information campaigns to support any such measures.
Minimizing Methane Emissions
The energy sector is responsible for 40% of global methane emissions, a greenhouse gas with a global warming potential 21 times higher than CO2. 94 In the energy sector, the vast majority of methane emissions occur when natural gas is released in oil production operations (“associated petroleum gas”), as part of safety venting operations or due to leaks during transmission and distribution.
With extensive oil and gas production and pipeline infrastructure, methane emissions are a key challenge for Russia – the country was responsible for 40%95 of global energy-related methane emissions in 2012. In 2009, Russia aimed to reach a 95% utilization rate of “associated gas” by 2012; however, estimates from 2012 point at a 76% utilization rate achieved96 to date. Although a number of measures are being implemented, the cost of retrofitting extensive infrastructure and limited success in enforcing standards is impacting progress. In the absence of stringent regulation and incentive mechanisms, it is unclear to what extent capture and reuse technologies will be implemented.
As evidenced above and in the performance of the BRICS cluster in the EAPI, these economies face a number of challenges in balancing the energy requirements of their growing economies with the concerns over the long-term environmental sustainability of their energy systems. The IEA recommendations for GDP-neutral carbon abatement solutions identify the key opportunities for developing long-term strategies to address the environmental challenge.
External Perspective: Balancing Economic Growth and Development with the Challenge of Environmental Sustainability – China’s Perspective
China Centre for Energy Economics Research,
People’s Republic of China
China Centre for Energy Economics Research,
People’s Republic of China
There are many factors contributing to air pollution in China. However, controlling energy consumption, changing the energy structure and increasing the supply of clean energy are likely to be the main factors in reducing air pollution in these regions.
The plan focuses on reducing coal consumption in Eastern China, which is still in a development stage of relatively high economic growth and represents a major portion of projected increases in energy demand. If renewable or cleaner-burning energy sources cannot meet the growing energy demand in the eastern regions, energy resources, especially coal from the western regions, will be required to supplement electricity – compounding the pollution problems in the western regions.
Coal currently provides 69% of primary energy and close to 80% of electricity in China. Hydropower development is restricted by its potential, and other renewable energy, such as wind and solar, are too small to make a meaningful contribution at this point. Nuclear energy could substitute coal substantially, but it requires a long-term development plan. Natural gas with less emission could possibly substitute not more than 5% of coal in the primary energy mix in next few years.
Air pollution control in the eastern regions will result in more pollution in the western regions in two ways: one is the migration of high energy-intensive industries from the eastern to the western regions, and the other is more coal-fired power generation in the western regions that could be transmitted to the eastern regions. Therefore, the trend of accelerated pollution in the western regions seems inevitable.
What happened in the eastern regions should be an important lesson for China. How to balance economic growth and development with the challenge of environmental sustainability is critically important today, as China has been forced to clean up the eastern regions that could lead to high possibilities of polluting the western regions.
The government needs to establish two mechanisms to avoid the pollution pattern in the eastern regions. First, the terms of trade for energy transfer should be in favour of the western regions so that an effective ecological compensation mechanism could be established to minimize the environmental impact. The central government needs to coordinate and ensure reasonable energy prices, which can support economic development in the western regions and curb energy consumption in the eastern regions. Secondly, the government should ensure ordinary people in the western regions benefit from the energy resource transfer. With higher incomes, the people in the western regions could gain access to commercial energy, change their energy consumption patterns, afford cleaner energy and reduce coal consumption.
Over the past decade, BRICS countries have experienced rapid industrialization, economic growth and increases in GDP per capita. On average, the GDP of Brazil, China, India, Russia and South Africa grew by 7% annually between 2002 and 2012.[fn 81]GDP per capita, PPP (current international $). World Bank, http://data.worldbank.org/indicator/NY.GDP.PCAP.PP.CD.