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close this bookIndustrial Metabolism: Restructuring for Sustainable Development (UNU; 1994; 376 pages)
View the documentNote to the reader from the UNU
View the documentAcknowledgements
View the documentIntroduction
Open this folder and view contentsPart 1: General implications
close this folderPart 2: Case-studies
close this folder6. Industrial metabolism at the national level: A case-study on chromium and lead pollution in Sweden, 1880-1980
View the documentIntroduction
View the documentThe use of chromium and lead in Sweden
View the documentCalculation of emissions
View the documentThe development of emissions over time
View the documentThe emerging immission landscape
View the documentConclusions
View the documentReferences
Open this folder and view contents7. Industrial metabolism at the regional level: The Rhine Basin
Open this folder and view contents8. Industrial metabolism at the regional and local level: A case-study on a Swiss region
Open this folder and view contents9. A historical reconstruction of carbon monoxide and methane emissions in the United States, 1880-1980
Open this folder and view contents10. Sulphur and nitrogen emission trends for the United States: An application of the materials flow approach
Open this folder and view contents11. Consumptive uses and losses of toxic heavy metals in the United States, 1880-1980
View the documentAppendix
Open this folder and view contentsPart 3: Further implications
View the documentBibliography
View the documentContributors


In many countries, estimations of annual emissions of chemicals from point sources are now being regularly presented for the nation as a whole. For Sweden, the figures show that the emissions have been decreasing since the mid-1970s. This is, of course, encouraging with regard to environmental protection objectives. Unfortunately, however, these figures do not present a complete picture. Nor do they provide sufficient information to evaluate human impact on the environment systematically, especially in a long-term perspective. There are two major shortcomings of the standard estimates:

1. Lack of a spatial dimension; a nationwide scale is hardly satisfactory to assess impacts (or the value) of reduced industrial emissions.
2. Lack of a temporal dimension; to evaluate present pollution loadings, knowledge about the dimension and localization of past emissions is needed.

The development of industry in Sweden has led to an increased use of chemicals and other materials. In this study we want to approach the environmental problems of tomorrow that will arise from the use of various materials, from a historical standpoint. This type of study could be used as an argument for what has recently been called the precautionary principle of environmental management (see O'Riordan, chapter 12 of this volume). The purpose is to develop methods to reconstruct the flows of materials and estimate the emissions over time. This is done through studies of the development of production, technology, trade, and the longevity of products in society. This last part in the chain will form the "consumption emissions."

The concept of industrial metabolism suggests that we should seek to estimate the total load of toxic substances in soils and sediments, i.e. to describe and assess the development of a new "immission landscape." In this chapter industrial metabolism is illustrated in terms of the total flow and accumulation of chromium (1920-1980) and lead (18801980) in Sweden (Anderberg et al., 1989, 1990; Bergbäck et al., 1989, 1992).

The method of analysis is based on a simplified flow scheme: Various substances enter the economy either through imports or domestic production. Production of goods and extraction of primary materials result in "production emissions." The main part of these emissions is found in the products themselves, and is accumulating in the "anthroposphere." Depending on the type of product, large amounts may remain for a long time. Some parts are recycled after use. However, a significant quantity is sooner or later spread to the environment through consumption emissions, dissipative losses (see Ayres, chapter 1 of this volume), consumer-related emissions, or emissions from diffuse sources.

This materials' balance approach method (inspired by Ayres and Kneese, 1969; Ayres, 1978; Ayres and Rod, 1986; Tarr and Ayres, 1990) consists, in somewhat simplified form, of the following steps:
1. Construction of flow schemes for various substances.
2. Collection of data concerning production, trade, and technology with the aim of filling the boxes in the flow schemes and creating a base for assumptions concerning emissions.
3. Estimating the emissions over time, using the net surplus and the flow scheme of the substance; emission coefficients concerning consumption are based on "life-expectancy" of the product in the technosphere.
4. Calculation of the anthropogenic amounts of stable substances in the soil and sediments per region and decade, i.e. the immission landscape.

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