![]() | 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 |
The other important anthropogenic greenhouse gases emitted in Australia are methane and nitrous oxide. Compared with carbon dioxide, little is known about either sources of, or possible abatement measures for these gases, particularly nitrous oxide. The most important source of methane, thought to account for about two-thirds of total emissions, is domestic livestock, principally cattle, sheep and pigs. Landfill (municipal garbage) is also an important source. Small quantities of methane are released as a result of coal mining and from the natural gas distribution system. Agricultural activities, in this case soil denitrification associated with both the application of nitrogenous fertilizers and the use of legumes in improved pastures, is thought to be the main source of nitrous oxide (Ecologically Sustainable Development Working Groups 1992). Measures which it is thought could contribute to reducing these emissions include: the use of rumen modifiers (anti-bloat capsules) with intensively reared cattle; a modest decrease in stocking rates on some pasture types used for extensively reared cattle; aerobic, rather than predominantly anaerobic treatment of piggery waste; and the optimization of application rates of nitrogen fertilizers. The ESD did not estimate the scope, let alone the cost of these measures if applied on a large scale.
Abatement of atmospheric carbon dioxide levels by increased tree growth in Australia has been analysed superficially. Over the last few years growing concern about deforestation and soil erosion stimulated a variety of government and privately supported programmes to reverse the trends of two centuries of European colonization. These programmes could perhaps stop and perhaps reverse the continuing emission of carbon dioxide previously sequestered in biomass in trees and in the soil. As such they can legitimately be seen as an important part of national activities to curb greenhouse gas emissions, although that is not the reason they were initiated. From a greenhouse perspective, therefore, they are costless measures. However, much more far-reaching tree plantation programmes would be required to make a significant contribution to offsetting carbon dioxide from energy related activities. No estimates are available yet of the possible cost and scale of such programmes in Australia.