
| Eco-restructuring: Implications for sustainable development (UNU, 1998, 417 pages) |
| (introductory text...) |
| 1. Eco-restructuring: The transition to an ecologically sustainable economy |
![]() | (introductory text...) |
![]() | Introduction: On sustainability |
![]() | The need for holistic systems analysis |
![]() | Environmental threats and (un)sustainability indicators |
![]() | Sharpening the debate |
![]() | Non-controversial issues: Population, resources, and technology |
![]() | Controversial issues: Pollution, productivity, and biospheric stability |
![]() | (introductory text...) |
![]() | On toxicity |
![]() | The stability of the biosphere: The impossibility of computing the odds |
![]() | Technical preconditions for sustainability |
![]() | Finding the least-cost (least-pain) path |
![]() | Concluding comments |
![]() | Notes |
![]() | References |
| Part I: Restructuring resource use |
![]() | 2. The biophysical basis of eco-restructuring: An overview of current relations between human economic activities and the global system |
![]() | (introductory text...) |
![]() | Introduction |
![]() | The earth system |
![]() | The climate system and climatic change |
![]() | Climatic change and vulnerability |
![]() | Biological diversity |
![]() | Fresh water |
![]() | Soils |
![]() | The solid earth (lithosphere) |
![]() | Land-cover and land-use changes |
![]() | Human impacts and industrial metabolism |
![]() | The case of West Africa |
![]() | Outlook |
![]() | 3. Ecological process engineering: The potential of bio-processing |
![]() | (introductory text...) |
![]() | Editor's note |
![]() | Introduction |
![]() | The current situation: The status of biotechnologies |
![]() | Potential and promises |
![]() | Market penetration by biotechnology |
![]() | Barriers to penetration |
![]() | Final remarks |
![]() | Notes |
![]() | References |
![]() | 4. Materials futures: Pollution prevention, recycling, and improved functionality |
![]() | (introductory text...) |
![]() | Editor's introduction |
![]() | Background |
![]() | Strategies to increase materials productivity |
![]() | Materials technology |
![]() | Material attributes |
![]() | Material performance trends |
![]() | Conclusions |
![]() | Notes |
![]() | References |
![]() | 5. Global energy futures: The long-term perspective for eco-restructuring |
![]() | (introductory text...) |
![]() | Introduction |
![]() | What is the energy system? |
![]() | Energy system inefficiencies |
![]() | The deep future energy system |
![]() | Transition and the rate of change of the energy system |
![]() | North-South disparity and sustainable energy systems |
![]() | Concluding remarks |
![]() | Notes |
![]() | References |
![]() | 6. Fuel decarbonization for fuel cell applications and sequestration of the separated CO2 |
![]() | (introductory text...) |
![]() | The challenge of stabilizing the atmosphere |
![]() | Flue gas decarbonization vs. fuel gas decarbonization |
![]() | Lifecycle CO2 emissions - without and with CO2 sequestration |
![]() | Options for sequestering CO2 |
![]() | Framing the cost analysis for CO2 sequestration |
![]() | Major findings of the sequestration cost analysis |
![]() | Appendix A: The importance of the water-gas shift reaction in fuel decarbonization |
![]() | Appendix B: Biomass CO2 emission offset potential in a world where some coal-rich regions cannot or will not reduce emissions |
![]() | Appendix C: Pipeline transport of hydrogen |
![]() | Acknowledgements |
![]() | Notes |
![]() | References |
![]() | 7. Photovoltaics |
![]() | (introductory text...) |
![]() | Introduction |
![]() | The technological potential of PV |
![]() | PV costs |
![]() | A PV market diffusion strategy |
![]() | Possible PV adoption and diffusion scenarios |
![]() | Concluding remarks: PV and eco-restructuring |
![]() | Notes |
![]() | Bibliography |
| Part II: Restructuring sectors and the sectoral balance of the economy |
![]() | 8. Global eco-restructuring and technological change in the twenty-first century |
![]() | (introductory text...) |
![]() | Globalization |
![]() | Population growth and economic growth |
![]() | Environmental pressures for global change |
![]() | Scenario analysis and the use of materials |
![]() | The challenge for eco-restructuring |
![]() | Concluding remarks |
![]() | Notes |
![]() | References |
![]() | 9. Agro-eco-restructuring: Potential for sustainability |
![]() | (introductory text...) |
![]() | Editor's note |
![]() | The broad situation |
![]() | Identifying the limiting factors |
![]() | The technological feasibility of sustainable agriculture |
![]() | The possible course towards sustainable change |
![]() | Final remarks |
![]() | Notes |
![]() | References |
![]() | 10. The restructuring of tropical land-use systems |
![]() | (introductory text...) |
![]() | Introduction |
![]() | Models of rural development |
![]() | The need for integrated solutions in tropical land use |
![]() | Strategic issues |
![]() | Concluding remarks |
![]() | Notes |
![]() | References |
![]() | 11. The restructuring of transport, logistics, trade, and industrial space use |
![]() | (introductory text...) |
![]() | Introduction |
![]() | The significance of freight transport |
![]() | Past growth and patterns of freight transport development |
![]() | Spatial and transport outcomes |
![]() | Future developments affecting freight volumes and patterns |
![]() | The scope for reducing freight volumes |
![]() | Taking up the potential |
![]() | Conclusion |
![]() | Notes |
![]() | References |
![]() | 12 National and international policy instruments and institutions for eco-restructuring |
![]() | (introductory text...) |
![]() | Introduction |
![]() | Building on small agreements |
![]() | Economic policy instruments and mechanisms |
![]() | International distributional implications |
![]() | A precondition for social breakthroughs in the context of developing societies |
![]() | Issues of science and technology for development |
![]() | A future united nations system |
![]() | References |
![]() | Contributors |
![]() | Other titles of interest |
Human economic activities have now reached an order of magnitude where their influence on the natural earth systems is quite significant. If we accept the analogy between biological and industrial metabolism, the latter can be defined as "the whole integrated collection of physical processes that convert raw materials and energy, plus labor, into finished products and wastes... with the economic system as the metabolic regulatory mechanism" (Ayres 1994). The firm (factory/plant) as a basic unit of the economic system can be compared to living organisms in biology. This analogy, taken a step further, leads into the notion of "industrial ecology."
Similarly, the "cycle" concept of the geo-scientists (e.g. the hydrological, carbon/oxygen, nitrogen, or sulphur cycles) can be adopted as "materials cycles" of the industrial system, starting with raw materials from the earth and returning them to nature as wastes (Ayres 1994). Industry converts primary resources into products useful for humans. In the course of these transformations, large amounts of waste are generated. It is important to measure these fluxes and processes. A number of measures of industrial metabolism have been proposed, which also require a sound knowledge of the biophysical basis. They include measurements of dissipative losses, of recycled materials, and also of the economic output per unit of material input, which can be called material productivity. Clearly, more exact measurements based on geophysical and geochemical data are desirable. This is because, collected at a sectoral level, they would allow improved analyses of the entire process of industrial metabolism. The establishment of an information system on industrial metabolism has been proposed (Fischer-Kowalski et al. 1993).
One attempt to introduce a universal measure for ecological disturbances is "materials intensity per unit of service" (Schmidt-Bleak 1992). The underlying idea is that the potential for disturbance is closely related to the mass of materials moved or processed in the whole chain of processes beginning with extraction and ending with disposal or recycling. The difference between the mass of the product itself and the total mass moved indirectly in the chain has been given the evocative term "rucksack." The size of the rucksack of a material product is a rough measure of the potential for disturbance resulting from its production and use.