![]() | The Global Greenhouse Regime. Who Pays? (UNU, 1993, 382 p.) |
![]() | ![]() | List of contributors |
![]() | ![]() | Preface |
![]() | ![]() | Acknowledgements |
![]() | ![]() | Part I Measuring responsibility |
![]() | ![]() | 1 Introduction |
![]() | ![]() | (introduction...) |
![]() | ![]() | The greenhouse effect |
![]() | ![]() | What was decided at Rio? |
![]() | ![]() | Protocol negotiating difficulties |
![]() | ![]() | Key issues for climate change negotiations |
![]() | ![]() | References |
![]() | ![]() | 2 The basics of greenhouse gas indices |
![]() | ![]() | (introduction...) |
![]() | ![]() | Apples and oranges |
![]() | ![]() | Implications |
![]() | ![]() | Conclusion: indices do matter |
![]() | ![]() | References |
![]() | ![]() | 3 Assessing emissions: five approaches compared |
![]() | ![]() | (introduction...) |
![]() | ![]() | Introduction |
![]() | ![]() | Comprehensiveness compared |
![]() | ![]() | Accuracy by category |
![]() | ![]() | Regional and national emissions by source |
![]() | ![]() | Conclusions |
![]() | ![]() | References |
![]() | ![]() | Appendix A: Estimates of greenhouse gas emissions |
![]() | ![]() | Appendix B: Calculating cumulative and current emissions |
![]() | ![]() | 4 Who pays (to solve the problem and how much)? |
![]() | ![]() | (introduction...) |
![]() | ![]() | Indices of allocation: a brief review |
![]() | ![]() | Accountability |
![]() | ![]() | Equity and efficiency |
![]() | ![]() | Conclusion |
![]() | ![]() | References |
![]() | ![]() | Part II Resource transfers |
![]() | ![]() | 5 North-South carbon abatement costs |
![]() | ![]() | (introduction...) |
![]() | ![]() | Climate change convention |
![]() | ![]() | Method overview |
![]() | ![]() | Implications for the South |
![]() | ![]() | Notes and references |
![]() | ![]() | 6 North-South transfer |
![]() | ![]() | (introduction...) |
![]() | ![]() | Obligation to pay indices |
![]() | ![]() | Redistribution of incremental cost |
![]() | ![]() | Benchmarks |
![]() | ![]() | UN scale of payments |
![]() | ![]() | Financing mechanisms |
![]() | ![]() | Conclusion |
![]() | ![]() | Notes and references |
![]() | ![]() | 7 Insuring against sea level rise |
![]() | ![]() | (introduction...) |
![]() | ![]() | Insurability of losses |
![]() | ![]() | Oil pollution |
![]() | ![]() | Nuclear damage |
![]() | ![]() | Implications |
![]() | ![]() | The insurance scheme proposed by AOSIS |
![]() | ![]() | The Climate Change Convention |
![]() | ![]() | Notes and references |
![]() | ![]() | Appendix: Scheme proposed by AOSIS for inclusion in the Climate Change Convention |
![]() | ![]() | Part III National greenhouse gas reduction cost curves |
![]() | ![]() | 8 Integrating ecology and economy in India |
![]() | ![]() | (introduction...) |
![]() | ![]() | Introduction |
![]() | ![]() | Emissions inventory |
![]() | ![]() | Energy efficiency and fuel substitution |
![]() | ![]() | Emissions and sequestration from forest biomass |
![]() | ![]() | Conclusions |
![]() | ![]() | References |
![]() | ![]() | 9 Carbon abatement potential in West Africa |
![]() | ![]() | (introduction...) |
![]() | ![]() | Introduction |
![]() | ![]() | Long-term energy and carbon emissions scenarios |
![]() | ![]() | Options for rational energy use and carbon conservation |
![]() | ![]() | Economic opportunities for implementation |
![]() | ![]() | Policy issues for the region |
![]() | ![]() | Conclusions |
![]() | ![]() | References |
![]() | ![]() | 10 Abatement of carbon dioxide emissions in Brazil |
![]() | ![]() | (introduction...) |
![]() | ![]() | Brazil energy economy |
![]() | ![]() | Energy subsector analyses |
![]() | ![]() | Changing land-use trends |
![]() | ![]() | Conclusion |
![]() | ![]() | References |
![]() | ![]() | 11 Thailand's demand side management initiative: a practical response to global warming |
![]() | ![]() | (introduction...) |
![]() | ![]() | Introduction |
![]() | ![]() | End-use energy efficiency policies |
![]() | ![]() | Costs and benefits of the DSM master plan |
![]() | ![]() | CO2 reductions from the DSM Plan |
![]() | ![]() | Why should other developing countries adopt DSM? |
![]() | ![]() | The role of the multilateral development banks |
![]() | ![]() | Conclusions |
![]() | ![]() | References |
![]() | ![]() | 12 Carbon abatement in Central and Eastern Europe and the Commonwealth of Independent States |
![]() | ![]() | (introduction...) |
![]() | ![]() | Energy-environment nexus |
![]() | ![]() | Scenarios for the future |
![]() | ![]() | Country results |
![]() | ![]() | Policy implications |
![]() | ![]() | Conclusion |
![]() | ![]() | References |
![]() | ![]() | 13 Greenhouse gas emission abatement in Australia |
![]() | ![]() | (introduction...) |
![]() | ![]() | Abatement of energy sector emissions |
![]() | ![]() | Economic impact of abatement strategies |
![]() | ![]() | Non-energy emission abatement |
![]() | ![]() | Australia's international role |
![]() | ![]() | Carbon taxes, externalities and other policy instruments |
![]() | ![]() | References |
![]() | ![]() | Part IV Conclusion |
![]() | ![]() | 14 Constructing a global greenhouse regime |
![]() | ![]() | (introduction...) |
![]() | ![]() | Conditionality and additionality |
![]() | ![]() | Technology transfer |
![]() | ![]() | Multi-pronged approach |
![]() | ![]() | Implementation procedures |
![]() | ![]() | Regional building blocks |
![]() | ![]() | North-'South' conflicts |
![]() | ![]() | Conclusion |
![]() | ![]() | Notes and references |
![]() | ![]() | Appendix: The Climate change convention |
![]() | ![]() | Introduction |
![]() | ![]() | Background |
![]() | ![]() | Climate change convention |
![]() | ![]() | Article 1. Definitions |
![]() | ![]() | Article 2. Objective |
![]() | ![]() | Article 3. Principles |
![]() | ![]() | Article 4 Commitments |
![]() | ![]() | Article 5. Research and systematic observation |
![]() | ![]() | Article 6. Education, training and public awareness |
![]() | ![]() | Article 7. Conference of the Parties |
![]() | ![]() | Article 8. Secretariat |
![]() | ![]() | Article 9. Subsidiary body for scientific and technological advice |
![]() | ![]() | Article 10. Subsidiary Body for implementation |
![]() | ![]() | Article 11. Financial mechanism |
![]() | ![]() | Article 12. Communication of information related to implementation |
![]() | ![]() | Article 13. Resolution of questions regarding implementation |
![]() | ![]() | Article 14. Settlement of disputes |
![]() | ![]() | Article 15. Amendments to the Convention |
![]() | ![]() | Article 16. Adoption and amendment of annexes to the Convention |
![]() | ![]() | Article 17. Protocols |
![]() | ![]() | Article 18. Right to vote |
![]() | ![]() | Article 19. Depositary |
![]() | ![]() | Article 20. Signature |
![]() | ![]() | Article 21. Interim arrangements |
![]() | ![]() | Article 22. Ratification, acceptance, approval or accession |
![]() | ![]() | Article 23. Entry into force |
![]() | ![]() | Article 24. Reservations |
![]() | ![]() | Article 25. Withdrawal |
![]() | ![]() | Article 26. Authentic texts |
Several investigators have attempted to allocate the global carbon budget based on exogenous considerations of the maximum acceptable warming or its rate of increase (for example, Krause et al. 1992), world averages (Mukherjee 1992), economic optimization models (Michaelis 1992), or other factors (Gurney 1991)
Dividing emissions rights equally among countries, coupled with the ability to sell or lease those rights, is the simplest scheme, yet fraught with inequities because it does not link emissions to human beings or activities. Thus it has few, if any, proponents. Another straightforward basis for allocating rights is land area (Welting 1989). Since 1950, national boundaries have not changed much (leaving aside the national break-ups of the early 1990s). Its stability as a measure, the ease of measurement, the avoidance of monitoring and verification difficulties are what recommend it. (Cheating is difficult.) There was a time, according to Grubb (1989), when the United States was arguing informally in international fore that its continental land mass necessitated enormous energy expenditures in having to move goods and people. Ultimately, with the possible exceptions of those countries with large wastelands (for example, Mongolia), land area is a measure of natural resources. Using it as an index to allocate emissions rights, however, favours large but sparsely populated nations (for example, Australia) and discriminates against small densely populated nations (for example, Japan).
If it is accepted that every person has an equal right to atmospheric resources - the ultimate global commons - then the most obvious and equitable basis is to distribute emissions permits in proportion to national populations (Feiveson et al. 1988; Agarwal and Narain 1991). If rights in subsequent years continue to be proportional to contemporaneous populations, however, a perverse incentive for population growth may be created. For this reason, and to make his scheme more palatable to industrialized countries, Grubb (1989) has suggested that allocations be based on adult populations. This would have the effect of reducing net transfers from countries with rectangular age distributions to developing countries with pyramidal age structures, but could be seen as discrimination against children. Depending on the definition of 'adult,' it would provide a 15-21 year delay between births and receiving the allotment, and thus reduce the pro-natalist incentive.
An alternate incentive for population stabilization could be built into the scheme by pegging the allotment to the entire population in a recent year and not increase future allotments. Compared to an index based on adult population, this would seem to represent less discrimination against children in the first years of an international protocol and no more discrimination in later years.
Arguing that any index based on per capita emissions alone would require unacceptably huge reductions in industrial countries (up to 75 per cent) or entail massive transfer payments to developing countries, Wirth and Lashof (1990) have proposed apportionment based half on per capita and half on per GDP, all the quantities being for the current or a recent year.
Similarly a multiplicative index could be structured that is directly proportional to emissions and inversely proportional to both GDP and population, the ratio being integrated over time. It is not clear, however, if GDP should find a place in an index for allocation, since countries would have already benefited from that economic activity.