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Market Based Instrument in
Developing Economies
(comparison)
By Prince Gupta (544)
Under the guidance of Mrs. Rashmi Agarwal
Problems
1. Rising Environmental problems.
2. Pressure from developed economies to cope up with rising Environmental problems taking immediate
action.
3. Fear of losing competitiveness due to implementation of effective but costly instruments.
4. Sectorial conflicts.
5. Rising awareness of general public about the environmental problems and thus pressurising the
respective Governments for concrete actions against the problem.
Objective
1. To understand the status of implementing MBIs for developing
economies from two different continents.
2. To determine factors causing adoption of MBIs.
Developing Economies
Rapid economic growth in the Asia and Latin America region in recent years has been accompanied by
changes such as increased demographic pressure, greater intensification of agricultural production,
industrialization, and urbanization. These changes have brought about further stress on the region’s
natural resource base that underpins development
Asia and South America being the host of major growing economies and being the most dynamic region
in the world in terms of economic expansion, have vital responsibility in solving both global and regional
environmental problems.
In both the continents, expenditure on environmental programs rarely exceeded 1–2% of GDP
compared to defence budgets, which range from about 0.8–6% of GDP. To meet the environmental
program needs of the region, expenditures of at least 7% of GDP will be required.
China
Rapid industrialization in addition with lax environmental oversight, are main contributors to
environmental problems. According to eco-city designer Thomas V. Harwood,16 of the world's 20 most
polluted cities are in China.
China is the world’s largest emitter of greenhouse gases, having overtaken the United States in 2007, and
was responsible for 27 percent of global emissions in 2014.
World’s highest sulphur dioxide (SO2) emissions, due mostly to its reliance on coal for energy
generation.
The carbon emission is rising @10% and by 2030 it can account for half of the world emission if it
continues at this rate.
The Chinese government has acknowledged the problems and made various responses, resulting in
some improvements.
Brazil
The proposition of a river basin approach in Brazil started in 1978 with the creation of the Special
Committee of Joint Studies on River Basins and later on of the Brazilian Association of Water
Resources comprising all agencies related to water services in Brazil.
Other developments, since then, were the organization of executive commissions of several river
basins.
What is MBI?
In order to achieve environmental objective of reducing negative
environmental externalities the policy makers have evolved two types of
measures.
One is “command and control” approach – instruments which provide businesses
with relatively little flexibility in achieving goals.
And the other is “Market based instrument” - those that provide businesses with
greater flexibility to consider more.
Why MBIs are preferred?
While the key interest in MBI application is achieving policy targets at reduced cost. MBIs have two
potential cost advantages over more traditional instruments.
First, MBIs allow different firms to make different adjustments in response to their unique business
structures and opportunities.
Second, incentives to discover cheaper ways to achieve outcomes provide dynamic ways of reducing
the future costs of achieving targets.
Under a command and control instrument two neighbouring firms producing similar amounts of
pollution may face widely differing costs to reduce their pollution (due to processes employed, input
mixes, type of goods produced or other reasons).
Types of MBIs
Fuel consumption Forecast (China)
2020 Estimated Production Estimated Consumption
Coal 2.5 – 2.8 Bn. Tn. 2.5 – 3.5 Bn. Tn.
Oil 210 Mn. Tn. 600 Mn. Tn.
Natural Gas 133 – 150 Bn. m^3 170 Bn. m^3
MBIs used in China: SUBSIDY
Government subsidies have been offered to manufacturers of more efficient products and wind
turbines. These subsidies aim to encourage: vehicles with low-fuel consumption, hybrid and electric
vehicles; energy-efficient appliances14; solar photovoltaic (PV) power projects and the production of
wind turbines.
A large-scale efficient light bulb subsidy program was launched in 2008; 50 million subsidized low-
energy bulbs were placed on the market, increasing to 100 million in
2009. The bulbs are sold at a discount and companies are reimbursed by the government for the
shortfall.
A subsidy for the purchase of plug-in hybrid, fuel-cell and all-electric vehicles has been in place since
2008.
Restricted and Encouraged Lending
In May 2010, the People’s Bank of China and the China Banking Regulatory Commission issued a joint
circular, requiring that commercial banks restrict lending to companies with high levels of energy
consumption and emissions, and industries with “backward” production facilities and over-capacity
problems.
At the same time banks were instructed to encourage loans to new and high technology industries;
including strategic growth industries, nuclear, solar, wind and biomass, clean energy vehicles, as well as
new materials and high-end manufacturing (such as aeronautics and high-speed rail).
Tax Incentives
Beginning in 2003, foreign investment in both biogas and wind energy production benefits from a
reduced income tax rate of 15 percent, as opposed to 33 percent. This preferential 15 percent income
tax rate also applies to “high and new technology enterprises” as of 2007, which include most renewable
energy enterprises.
In addition, wind turbines and their main components, as well as photovoltaic modules, benefit from
preferential customs duty rates. Starting in 2001 and expanding in 2003, reduced VAT rates have also
been applied to wind power.
While increasing excise tax rates for larger vehicles, China reduced the excise rate for cars with engines
under one litre from 3 percent to 1 percent. Starting in 2012 domestically manufactured electric and fuel
cell vehicles are exempt from sales tax.
TAXES
Starting in September 2006, the Ministry of Finance increased export taxes on energy intensive
industries by reducing the export tax rebate. One of the main goals was to encourage economic
restructuring away from polluting and energy-intensive industries by discouraging the production and
export of energy-intensive products.
The export tax rebate was reduced by between 2 and 6 percent on steel, cement, glass and certain
nonferrous metal products. In April 2007, the rebate on exports of most steel products was lowered to 5
percent. In early 2011 the government announced further export tax rebate reductions and cancellations
for heavy energy-using and polluting manufacturing processes.
Since 2006, China also used excise tax rate adjustments to discourage purchase of larger cars that
consume more fuel. In September 2008, the excise tax rate on cars with engines above four litres
doubled from 20 percent to 40 percent, and increased from 15 percent to 25 percent for those with
engines between three and four litres.
Differential Electricity Pricing
Starting in June 2004 and strengthened in 2006, differential electricity pricing policy (DEPP) was Market-
Based Climate Mitigation Policies in Emerging Economies implemented for certain high energy
consuming industries, requiring them to pay a surcharge on their electricity price.
Facilities are placed in four categories based on their level of capacity, energy and resource efficiency,
and environmental standards: those in the “encouraged” and “permitted” category pay the standard price
in their area, while those in the “restricted” or “eliminated” categories pay a surcharge of CNY 0.10/kWh
and CNY 0.30/kWh respectively.
Between 2004 and 2006, approximately 900 firms in the “eliminated” category and 380 firms in the
“restricted” category had closed, invested in energy efficiency measures, or changed production
processes
China respondents reflected the following policies and/or frameworks that have either been
implemented or subject of public policy- making processes and discussions:
• China Low Carbon Strategy. The strategy aims to increase the renewable energy capacity in China and
explore growth in clean technologies
• China low carbon economy strategy. Started work towards a china climate change legislation
MBIs used in Brazil: Credit and Tax Incentives
Offer subsidized credit and taxation relief for environment-related investments. They cover abatement
investments or clean technology adoption in the industrial sector.
Subsidies for abatement investments have, however, been of limited impact since environmental
enforcement has not been effective enough to increase firms’ demand for these expenditures.
Moreover, it is reported that firms are using these incentives inadequately because of the lack of proper
fiscal and environmental follow-up procedures to monitor their investments.
Cost-Recovery Tariffs
Pricing of water supply, sanitation, solid waste collection, and energy plays an important role in
pollution control and resource use. Moreover, a full cost-recovery approach is essential for service
expansion and it allows for cross-subsidies to low-income groups.
• Sewage
• Sanitation
• Energy
Deposit-Refund Systems
Voluntary deposit-refund systems for returnable glass bottles are traditionally adopted in most
countries due to the predominance of the beverage and beer packaging system.
Refund payments for aluminium cans, due to the high value-added from recycling and the expanding
use of such containers, are now increasing considerably in Brazil.
Car batteries are now under a compulsory deposit-refund scheme through which a new battery can only
be sold with the return of an old one.
Resource Use Charges
In Brazil, a forestry tax is charged for wood consumption when the harvesting is not compensated by
equivalent reforestation activity.
These taxes are usually set at very low levels and with very weak enforcement, particularly in frontier
regions where monitoring is very difficult.
Other such charge is levied on water usage.
Brazil respondents reflected the following policies and/or frameworks that have either been
implemented or subject of public policy- making processes and discussions:
• National policy on climate change
• Renewable energy feed in tariff, mechanism to encourage CDM projects through the designated
national entity
Brazil was the first country to propose the Clean Development Mechanism (CDM) to benefit the
developing countries.
It is responsible for 7% all CDM worldwide.
Comparison: Carbon emission per capita
Comparison of two economies on various
aspects
Comparison of two economies: Implementation
of MBIs
Comparison of two economies: Priority Sectors
Conclusion
Market-based instruments have now moved centre stage, and policy debates look very different from
the time when these ideas were characterized as "licenses to pollute" or dismissed as completely
impractical. Market-based instruments are considered seriously for each and every environmental
problem that is tackled, ranging from endangered species preservation to what may be the greatest of
environmental problems.
China is way far behind in terms of coping with the environmental challenges when compared to other
economies like U.S., Japan and European countries.
Being the Second largest economy of the world, the country have not done much than what they
should have done.
THANK YOU

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MBI in china and brazil

  • 1. Market Based Instrument in Developing Economies (comparison) By Prince Gupta (544) Under the guidance of Mrs. Rashmi Agarwal
  • 2. Problems 1. Rising Environmental problems. 2. Pressure from developed economies to cope up with rising Environmental problems taking immediate action. 3. Fear of losing competitiveness due to implementation of effective but costly instruments. 4. Sectorial conflicts. 5. Rising awareness of general public about the environmental problems and thus pressurising the respective Governments for concrete actions against the problem.
  • 3. Objective 1. To understand the status of implementing MBIs for developing economies from two different continents. 2. To determine factors causing adoption of MBIs.
  • 4. Developing Economies Rapid economic growth in the Asia and Latin America region in recent years has been accompanied by changes such as increased demographic pressure, greater intensification of agricultural production, industrialization, and urbanization. These changes have brought about further stress on the region’s natural resource base that underpins development Asia and South America being the host of major growing economies and being the most dynamic region in the world in terms of economic expansion, have vital responsibility in solving both global and regional environmental problems. In both the continents, expenditure on environmental programs rarely exceeded 1–2% of GDP compared to defence budgets, which range from about 0.8–6% of GDP. To meet the environmental program needs of the region, expenditures of at least 7% of GDP will be required.
  • 5. China Rapid industrialization in addition with lax environmental oversight, are main contributors to environmental problems. According to eco-city designer Thomas V. Harwood,16 of the world's 20 most polluted cities are in China. China is the world’s largest emitter of greenhouse gases, having overtaken the United States in 2007, and was responsible for 27 percent of global emissions in 2014. World’s highest sulphur dioxide (SO2) emissions, due mostly to its reliance on coal for energy generation. The carbon emission is rising @10% and by 2030 it can account for half of the world emission if it continues at this rate. The Chinese government has acknowledged the problems and made various responses, resulting in some improvements.
  • 6. Brazil The proposition of a river basin approach in Brazil started in 1978 with the creation of the Special Committee of Joint Studies on River Basins and later on of the Brazilian Association of Water Resources comprising all agencies related to water services in Brazil. Other developments, since then, were the organization of executive commissions of several river basins.
  • 7. What is MBI? In order to achieve environmental objective of reducing negative environmental externalities the policy makers have evolved two types of measures. One is “command and control” approach – instruments which provide businesses with relatively little flexibility in achieving goals. And the other is “Market based instrument” - those that provide businesses with greater flexibility to consider more.
  • 8. Why MBIs are preferred? While the key interest in MBI application is achieving policy targets at reduced cost. MBIs have two potential cost advantages over more traditional instruments. First, MBIs allow different firms to make different adjustments in response to their unique business structures and opportunities. Second, incentives to discover cheaper ways to achieve outcomes provide dynamic ways of reducing the future costs of achieving targets. Under a command and control instrument two neighbouring firms producing similar amounts of pollution may face widely differing costs to reduce their pollution (due to processes employed, input mixes, type of goods produced or other reasons).
  • 10. Fuel consumption Forecast (China) 2020 Estimated Production Estimated Consumption Coal 2.5 – 2.8 Bn. Tn. 2.5 – 3.5 Bn. Tn. Oil 210 Mn. Tn. 600 Mn. Tn. Natural Gas 133 – 150 Bn. m^3 170 Bn. m^3
  • 11. MBIs used in China: SUBSIDY Government subsidies have been offered to manufacturers of more efficient products and wind turbines. These subsidies aim to encourage: vehicles with low-fuel consumption, hybrid and electric vehicles; energy-efficient appliances14; solar photovoltaic (PV) power projects and the production of wind turbines. A large-scale efficient light bulb subsidy program was launched in 2008; 50 million subsidized low- energy bulbs were placed on the market, increasing to 100 million in 2009. The bulbs are sold at a discount and companies are reimbursed by the government for the shortfall. A subsidy for the purchase of plug-in hybrid, fuel-cell and all-electric vehicles has been in place since 2008.
  • 12. Restricted and Encouraged Lending In May 2010, the People’s Bank of China and the China Banking Regulatory Commission issued a joint circular, requiring that commercial banks restrict lending to companies with high levels of energy consumption and emissions, and industries with “backward” production facilities and over-capacity problems. At the same time banks were instructed to encourage loans to new and high technology industries; including strategic growth industries, nuclear, solar, wind and biomass, clean energy vehicles, as well as new materials and high-end manufacturing (such as aeronautics and high-speed rail).
  • 13. Tax Incentives Beginning in 2003, foreign investment in both biogas and wind energy production benefits from a reduced income tax rate of 15 percent, as opposed to 33 percent. This preferential 15 percent income tax rate also applies to “high and new technology enterprises” as of 2007, which include most renewable energy enterprises. In addition, wind turbines and their main components, as well as photovoltaic modules, benefit from preferential customs duty rates. Starting in 2001 and expanding in 2003, reduced VAT rates have also been applied to wind power. While increasing excise tax rates for larger vehicles, China reduced the excise rate for cars with engines under one litre from 3 percent to 1 percent. Starting in 2012 domestically manufactured electric and fuel cell vehicles are exempt from sales tax.
  • 14. TAXES Starting in September 2006, the Ministry of Finance increased export taxes on energy intensive industries by reducing the export tax rebate. One of the main goals was to encourage economic restructuring away from polluting and energy-intensive industries by discouraging the production and export of energy-intensive products. The export tax rebate was reduced by between 2 and 6 percent on steel, cement, glass and certain nonferrous metal products. In April 2007, the rebate on exports of most steel products was lowered to 5 percent. In early 2011 the government announced further export tax rebate reductions and cancellations for heavy energy-using and polluting manufacturing processes. Since 2006, China also used excise tax rate adjustments to discourage purchase of larger cars that consume more fuel. In September 2008, the excise tax rate on cars with engines above four litres doubled from 20 percent to 40 percent, and increased from 15 percent to 25 percent for those with engines between three and four litres.
  • 15. Differential Electricity Pricing Starting in June 2004 and strengthened in 2006, differential electricity pricing policy (DEPP) was Market- Based Climate Mitigation Policies in Emerging Economies implemented for certain high energy consuming industries, requiring them to pay a surcharge on their electricity price. Facilities are placed in four categories based on their level of capacity, energy and resource efficiency, and environmental standards: those in the “encouraged” and “permitted” category pay the standard price in their area, while those in the “restricted” or “eliminated” categories pay a surcharge of CNY 0.10/kWh and CNY 0.30/kWh respectively. Between 2004 and 2006, approximately 900 firms in the “eliminated” category and 380 firms in the “restricted” category had closed, invested in energy efficiency measures, or changed production processes
  • 16. China respondents reflected the following policies and/or frameworks that have either been implemented or subject of public policy- making processes and discussions: • China Low Carbon Strategy. The strategy aims to increase the renewable energy capacity in China and explore growth in clean technologies • China low carbon economy strategy. Started work towards a china climate change legislation
  • 17. MBIs used in Brazil: Credit and Tax Incentives Offer subsidized credit and taxation relief for environment-related investments. They cover abatement investments or clean technology adoption in the industrial sector. Subsidies for abatement investments have, however, been of limited impact since environmental enforcement has not been effective enough to increase firms’ demand for these expenditures. Moreover, it is reported that firms are using these incentives inadequately because of the lack of proper fiscal and environmental follow-up procedures to monitor their investments.
  • 18. Cost-Recovery Tariffs Pricing of water supply, sanitation, solid waste collection, and energy plays an important role in pollution control and resource use. Moreover, a full cost-recovery approach is essential for service expansion and it allows for cross-subsidies to low-income groups. • Sewage • Sanitation • Energy
  • 19. Deposit-Refund Systems Voluntary deposit-refund systems for returnable glass bottles are traditionally adopted in most countries due to the predominance of the beverage and beer packaging system. Refund payments for aluminium cans, due to the high value-added from recycling and the expanding use of such containers, are now increasing considerably in Brazil. Car batteries are now under a compulsory deposit-refund scheme through which a new battery can only be sold with the return of an old one.
  • 20. Resource Use Charges In Brazil, a forestry tax is charged for wood consumption when the harvesting is not compensated by equivalent reforestation activity. These taxes are usually set at very low levels and with very weak enforcement, particularly in frontier regions where monitoring is very difficult. Other such charge is levied on water usage.
  • 21. Brazil respondents reflected the following policies and/or frameworks that have either been implemented or subject of public policy- making processes and discussions: • National policy on climate change • Renewable energy feed in tariff, mechanism to encourage CDM projects through the designated national entity Brazil was the first country to propose the Clean Development Mechanism (CDM) to benefit the developing countries. It is responsible for 7% all CDM worldwide.
  • 23. Comparison of two economies on various aspects
  • 24. Comparison of two economies: Implementation of MBIs
  • 25. Comparison of two economies: Priority Sectors
  • 26. Conclusion Market-based instruments have now moved centre stage, and policy debates look very different from the time when these ideas were characterized as "licenses to pollute" or dismissed as completely impractical. Market-based instruments are considered seriously for each and every environmental problem that is tackled, ranging from endangered species preservation to what may be the greatest of environmental problems. China is way far behind in terms of coping with the environmental challenges when compared to other economies like U.S., Japan and European countries. Being the Second largest economy of the world, the country have not done much than what they should have done.