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Harnessing Ingenuity for Sustainable Outcomes
Author:Deanna Richards
Source:The Bridge, National Academy of Engineering
Improving Ecoefficiency Strategies for improving product-related ecoefficiency include:
More ambitiously, ecoefficiency improvements from an EPR perspective suggest designing products and engineering systems to optimize "functionality" or "service" (Allenby and Richards, 1994; Richards, 1997). This means, for example, offering pest control instead of pesticides, refrigeration instead of refrigerators, document reproduction or printing instead of copiers or printers. For this approach to work, the design has to take into account upgradability and, for diverse product lines, interchangeability. In the latter case, managing the complex logistics of juggling different products, parts, and their recovery and remanufacture, as Xerox does (Committee on Industrial Environmental Performance Metrics, forthcoming), is key. The hurdle for ecoefficient products and services is the customer. In many instances, the customer base for these products is small. However, it may be growing. Electrolux's new line of ecoefficient products now accounts for as much as 8 percent of its revenues. In addition, companies that are aggressive in pursuing ecoefficiency improvements in their industrial practices and products see potential markets looming simply from the demands placed on physical and natural resources by a growing population. Most of the innovations discussed so far have resulted from incremental change. Incremental change is driven by pressures to reduce costs or meet quality, design, performance, manufacturability, or environmental goals. Change of this sort seldom results directly from any deliberate R&D, although it frequently is influenced indirectly by R&D conducted for other purposes. Three Types of Innovation There are at least three other types of innovation that have to be harnessed for sustainability to be realizable: radical innovations, technology-system innovations, and techno-economic revolutions (Freeman, 1992). Radical innovations are discontinuous events that result from deliberate R&D. (For example, incremental improvements in canoes did not lead to steamships and the developments of glass and paper did not lead to the creation of plastics). The underlying science and engineering are often incremental, but the deployment of the technologies leads to radical departures from past production practices. These innovations are unevenly distributed over industry sectors and over time. However, when they occur, they can spawn new markets or significantly improve the use of inputs (by lowering cost and improving the quality of existing products), as occurred with the shift to the oxygen steelmaking process. Technology-system innovations affect many branches of the economy through far-reaching technological change. New sectors of economic activity are created. The development of the semiconductor industry can be attributed to technology-systems innovation, as can synthetic materials and petrochemicals introduced during the 1930s, 1940s, and 1950s. Adjunct developments in machinery for injection molding and extrusion and later innovations in packaging, construction, electrical equipment, agriculture, textiles, clothing, toys, and other applications resulted in a range of interrelated innovations that were not contemplated when the materials and chemicals were first developed. Even more far-reaching change results from new technology that has a ubiquitous effect on the economy, creating a techno-economic revolution. These innovations transform production and management throughout the economy, in essence changing the ecology of industry (Richards and Pearson, 1998). The introduction of electric power is an example of one such dramatic transition. The computer, microelectronics, and biotechnology are more recent cases in point. Computers and microelectronics have radically improved the monitoring and control of emissions, and of energy and materials use, and they have facilitated more effective quality and inventory control. They have changed the social and management fabric of commerce and communications (e.g., through the Internet and workplace practices such as telecommuting) and raised the importance of knowledge management for environmental and other purposes (Richards, forthcoming). Biotechnology tools are transforming chemical companies into biotechnology companies. Monsanto, for example, is focusing on health services and food production as part of its sustainable-development vision (Magretta, 1997). Indeed, it is insufficient to think in terms of strictly green or sustainable technologies, if sustainability concerns are to be effectively addressed. Technology is dynamic. Change is inevitable. History and projections of technological advance show that we have been replacing resources that are limited (or found to be wanting in other ways) with substitutes of similar or superior performance. For example, there has been a decarbonization of energy systems over the centuries. Studies of technological trajectories of energy systems indicate a shift to a hydrogen economy (which will require solar and nuclear power) (Ausubel and Langford, 1997). Data also show that the economy is dematerializing (not literally, but in the sense of using less material by weight and per unit product). For example, newer materials (plastics and composites) have led to the lightweighting of cars. Lightweighting and more sophisticated electronics for monitoring and controlling on-board systems have led to greater fuel efficiency. Other areas have also benefited from efficiency improvements. Water conservation is relieving pressures on fresh-water supplies, and further improvements are possible through technology and policy change (e.g., eliminating subsidies for certain consumptive uses, such as agriculture in arid areas like California). Improvements in agricultural practices and yields, combined with the potential that biotechnology promises, offers brighter prospects for meeting the food needs of the planet. However, new technologies often create new problems. Newer materials such as plastics and composites that have environmental advantages are used dissipatedly. This makes their management (to prevent leaks and accumulations in the environment) an important design consideration. Similarly, improvements in agricultural yields may improve the availability of food but are not sustainable if they also damage ecosystems (e.g., as a result of pesticide use) or result in other unintended environmental impacts. Unlike the environmental concerns of the 1970s, which were often local and recognized at their points of origin (e.g., smokestacks, effluent pipes, unregulated dumps), today's environmental threats are cumulative and interactive, often arising from multiple causes that are not sector specific. In addition, many more-recent environmental concerns, such as the potential of toxins to bioaccumulate or to disrupt basic human and animal endocrine systems, are subtle, often difficult to identify, and complex to manage. The complexities associated with the interactions between human and natural systems make quantification and management in the sustainable-development context daunting. These tasks must be approached at many levels: national policy; interfirm decisions that change production and consumption patterns; process and product decisions made by firms; and choices made by consumers. In the short term, the move toward sustainable business practices presents an opportunity to disseminate "best practices" in environmental management as well as environmentally friendly products and services. The longer-term challenge is to manage the uncertainties inherent in resolving complex, coupled interactions between human and natural systems (Schulze, forthcoming; Schulze, 1996). Addressing Indirect, Delayed Effects We also need to improve our ability to predict and deal with systems effects. While any action has direct effects, interconnection within a system produces indirect and delayed effects. Chlorofluorocarbons were invented in the 1930s as a safe alternative to ammonia and sulfur dioxide, then used in home refrigeration. The intent was to eliminate the toxicity, flammability, and corrosion concerns of the other chemicals used at the time. The indirect and delayed effect was stratospheric ozone depletion (Ausubel and Sladovich, 1989) due to CFCs leaking from refrigerators, air conditioners, and electronics-cleaning operations. Policies intended to address social and environmental concerns similarly have often had indirect and delayed effects. For example, solid-waste management policies enacted a decade ago led local jurisdictions to develop waste management plans. These included the siting and financing of landfills and the encouragement of curbside recycling. The intent was to have municipalities take responsibility for the waste they generated. The indirect and delayed effect has been the creation of an overcapacity of heavily financed landfills in search of trash. In this case, system interactions were interactive, not additive. Local trash volumes were lower than anticipated because of the success of recycling. The trash example also shows that when there are more than two actors in a system, the relationship between any two is determined not by the actions of the two players, but by the interactions among all those in the system. Landfill owners, including municipalities, struck deals with cities like New York to take their trash. As these deals have become public, they are being questioned by communities and environmental groups, who are concerned about what is in the trash and if it will cause problems locally. System effects such as these are everywhere. Hence, even the greatest steps toward sustainable development will bring future problems. Accepting this fact frees us from the futility of searching for magic bullets or having groundless faith in the perfectibility of human societies (which underlies much of the sustainable-development rhetoric). It allows us to embrace progress and take steps to improve the quality of life of humans and the environment. As noted by Robert Frosch (Sustainability Engineering (editorial), The Bridge, Vol. 29, No. 1), over the next 50 years, assuming current trends continue, roughly 80 million people per year will be added to the world's urban population. That is equivalent to building an average of 8 cities of 10 million people each year for 50 years. How can the needs of those new urbanites be met without further affecting the sustainability of the planet? The Need for Social Innovation Large parts of Russia, China, and Africa are already unlivable by any reasonable standard and face serious trade-offs in their national investment decisions. For example, China burns coal as its primary source of power. Cleaner coal-burning technologies exist but are more expensive than traditional coal-powered plants. China is also a cold country, and a significant share of its population still lacks electricity, heat, or adequate nutrition. So, given the choice between building several dirty power plants or fewer cleaner ones that would deprive many of power, the economic and social choice is simple: Build the cheaper, dirtier plants. In many instances, technologies exist to dramatically improve the world's worst environmental and social problems. What is missing are social innovations that can transcend or alter current political and economic realities. The situation of the Dinka tribe in southern Sudan illustrates one extreme of the need for sustainable development. The Dinkas are on the brink of starvation, after having been uprooted from their homeland. They live on international handouts. One in six people in the world live like the Dinka (Hertsgaard, 1999). That is a huge number. The more telling point is that for much of history, that proportion has been closer to 9 out of 10. That means we've made tremendous progress. The challenge posed by sustainable development is one of spreading and speeding this progress through technological ingenuity and economic growth that successfully integrate ecological constraints and social needs. This requires harnessing technological innovations already in the pipeline and developing new systems of sustainable production and consumption -- essentially reengineering industrial systems within emerging ecological constraints and social demands. This challenge can be met by taking an integrated approach that taps the human capacity to learn and improve efficiency; harnesses the spirit of innovation; anticipates and acts on unintended consequences of systems of technology and public policies; and leverages new knowledge about ecological and social needs to improve the quality of human life and the environment. References Allenby, B. R., and D. J. Richards. 1994. The Greening of Industrial Ecosystems . Washington, D.C.: National Academy Press. Ausubel, J. H., and H. D. Langford. 1997. Technological Trajectories and the Human Environment. Washington, D.C.: National Academy Press. Ausubel, J. H., and H. E. Sladovich. 1989. Technology and Environment. Washington, D.C.: National Academy Press. Committee on Industrial Environmental Performance Metrics. Forthcoming. Environmental Performance Metrics: Challenges and Opportunities. Washington, D.C.: National Academy Press. Freeman, C. 1992. The Economics of Hope -- Essays on Technical Change, Economic Growth, and the Environment. London: Pinter Publications, Ltd. Hertsgaard, M. 1999. Earth Odyssey: Around the World in Search of Our Environmental Future. New York: Broadway Books. Magretta, J. 1997. Growth through global sustainability: An interview with Monsanto CEO Robert B. Shapiro. Harvard Business Review 75(1):79-88. Richards, D. J. 1997. The Industrial Green Game: Implications for Environmental Design and Management. Washington, D.C.: National Academy Press. Richards, D. J. Forthcoming. Green Tech-Knowledge-y: Information and Knowledge Systems for Improving Environmental Performance. Washington, D.C.: National Academy Press. Richards, D. J., and G. Pearson. 1998. The Ecology of Industry: Sectors and Linkages. Washington, D.C.: National Academy Press. Schulze, P. C. 1996. Engineering Within Ecological Constraints. Washington, D.C.: National Academy Press. Schulze, P. C. Forthcoming. Measures of Environmental Performance and Ecosystem Condition. Washington, D.C.: National Academy Press. World Bank. 1992. World Development Report 1992: Development and the Environment. Washington, D.C.: World Bank. World Business Council for Sustainable Development (WBCSD). 1996. Eco-efficient Leadership for Improved Economic and Environmental Performance. Conches-Geneva, Switzerland: WBCSD. Notes 1. The World Business Council for Sustainable Development (1996) has suggested that ecoefficiency is the delivery of competitively priced goods and services that satisfy human needs and bring quality of life and the progressive reduction of ecological impacts and resource intensity throughout the life cycle to a level commensurate with the Earth's estimated carrying capacity. 2. AES (previously known as Applied Energy Services) was founded by Roger Sant and Dennis Bakke, who headed up the energy conservation programs at the old Federal Energy Administration. Their experience showed them that Americans were not about to give up the comforts of industrial civilization, nor were those in developing countries going to accept poverty. They started AES with the goal not of producing energy-conserving products, but of providing services -- heat, light, and power -- at the lowest possible cost. About the Author Deanna J. Richards is associate director of the National Academy of Engineering's Program Office and directs the Academy's program on Technology and Sustainable Development, formerly known as Technology and Environment. |
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