The Swedish footprint: A multi-model comparison
Introduction
Current levels and patterns of consumption in developed countries are unsustainable, using too many raw materials and producing too much waste and pollution (Lorek and Vergragt, 2015). This is reflected in developed countries' high carbon, land and material footprints – estimates of the global pressures on ecosystems and natural resources that are linked to a country's consumption. For most developed countries, including Sweden, much of that footprint pressure falls outside of the territory, in the countries supplying Sweden's imported goods (Schmidt et al., 2018 (this issue); Steen-Olsen et al., 2012). This paper compares the global geographic “hotspots” of environmental pressures in Sweden's consumption footprints that are identified in different models. It explores the possible underlying causes of differences between the model results. The research is motivated by the objective to support policy and decision-makers in monitoring Sweden's footprint and provide recommendations for future research to improve the accuracy of national footprint estimates.
Sweden is now one among a number of countries that have produced and analysed their environmental impacts of consumption. The Swedish national statistics agency (Statistics Sweden, or SCB) has published national consumption-based carbon dioxide (CO2) emissions accounts (carbon footprints) since the end of the 1990s, with current estimates of GHG emissions per product group for 2008–2014 publicly available. In addition, a consistent time series from 1995 to 2009 of data on the CO2 emissions from Swedish consumption was published by Statistics Sweden in 2015 (Statistics Sweden, 2015) including a comparison of calculation methods using two different models. Earlier pilot studies by Swedish government agencies and research organizations had reported comparable footprint findings (Finnveden et al., 2001; Palm et al., 2006; Naturvårdsverket, 2008).
Work to develop similar consumption-based accounts for numerous countries has also been ongoing over a number of years, examining a wide range of environmental pressures such as the carbon footprint (Hertwich and Peters, 2009; Wiedmann et al., 2010); the water footprint (Hoekstra and Mekonnen, 2012) the land footprint (Weinzettel et al., 2013); and the material footprint (Wiedmann et al., 2015). Footprint results are now publicly available for many countries (Wood et al., 2018).
While the varying results that different models produce for the same footprint indicator may be confusing for communication purposes. There are benefits in examining the outputs of models with varying designs or data sets employed; this variability can be seen as repeated analyses concerned with the same basic set of questions, demonstrating plausibility of a consumption-based accounting approach and raising new policy questions.
This is particularly relevant in Sweden, where a number of national policies and strategies aim to tackle unsustainable consumption. A central component is the Generational Goal, the overarching goal of the national system of environmental objectives. This calls for solving the major environmental problems in Sweden within a generation, without exacerbating health or environmental pressures in the rest of the world (Swedish Environmental Protection Agency, 2012). In addition, Sweden is a signatory to Agenda 2030 and Sustainable Development Goals, with sustainable consumption and production as Goal 12 (United Nations, 2015), and recently launched a national Sustainable Consumption Strategy in December 2016 (Government Offices of Sweden Ministry of Finance, 2016). Regular monitoring of the global impacts of Swedish consumption will be essential to these efforts.
Section snippets
Consumption-based environmental impact accounting
For this study, the Swedish footprint results were compiled from five MRIO databases: EXIOBASE, WIOD, Eora, OECD and GTAP. These results were also compared with Statistics Sweden's calculations, based on an import-adjusted single-region input-output model. All of these models employ standard input-output analysis to calculate environmental pressures associated with final consumption. For the specific method behind each of the MRIOs, refer to the references listed in the short model descriptions
Carbon dioxide from fossil fuel combustion emissions – multi-model results
All of the models include an estimate of the Swedish consumption-based emissions from fossil fuel combustion, so this is a suitable indicator to compare between models and also selected by other model comparison studies (for example Owen et al. (2014)). Ideally, the emissions inventory should also include emissions from processes such as cement production and steel production, but in practice these process emissions are not handled consistently across the MRIO models. MRIO models are therefore
The global hotspots of Swedish environmental footprints
All consumption requires resources, and the various stages of production often cause adverse impacts on the local and global environment, particularly when the energy system is driven by fossil fuels. With the development of global supply chains these adverse impacts can happen in locations very distant from the consumer and from the reach of environmental legislation in the country where the products are consumed. The results of this study demonstrate that MRIO analysis can provide insight
Conclusion
The Swedish footprint results from five MRIO databases were compiled – EXIOBASE, WIOD, Eora, OECD and GTAP – along with the Statistics Sweden calculations that employ an import-adjusted single-region input-output model. As could be expected, given the complexity of the models, the analyses show different results, but they are similar enough to allow important general conclusions to be drawn. For example, they show that the distribution of environmental pressures due to Swedish consumption
Acknowledgements
This research was carried out as part of the PRINCE project (www.prince-project.se), supported by the Swedish Environmental Protection Agency and the Swedish Agency for Marine and Water Management under a Swedish Environmental Protection Agency research grant (Environmental Research Appropriation 1:5). We would also like to thank Caspar Trimmer at the Stockholm Environment Institute for improving the language and presentation of this article.
References (60)
- et al.
Effect of aggregation and disaggregation on embodied material use of products in input–output analysis
Ecol. Econ.
(2015) From production-based to consumption-based national emission inventories
Ecol. Econ.
(2008)- et al.
Towards a global multi-regional environmentally extended input-output database
Ecol. Econ.
(2009) - et al.
Affluence drives the global displacement of land use
Global Environ. Change
(2013) A review of recent multi-region input-output models used for consumption-based emission and resource accounting
Ecol. Econ.
(2009)- et al.
An overview of the GTAP 9 data base
J. Glob. Econ. Anal.
(2016) - et al.
Carbon Dioxide Emissions Embodied in International Trade of Goods
(2003) - et al.
Comparing the gtap-mrio and wiod databases for carbon footprint analysis
Econ. Syst. Res.
(2014) - et al.
Consumption-based accounting of CO2 emissions
Proc. Natl. Acad. Sci.
(2010) - et al.
The construction of world input–output tables in the WIOD project
Econ. Syst. Res.
(2013)
Structural Economics: Measuring Change in Technology, Lifestyles, and the Environment
A method to create carbon footprint estimates consistent with national accounts
Econ. Syst. Res.
Miljöpåverkan fån olika varugrupper
Stockh. Forskningsgruppen För Miljöstrategiska Stud. Total. Forskningsinstitutfms Rep.
Strategy for Sustainable Consumption (No. Fi 2016:7)
Does consistency with detailed national data matter for calculating carbon footprints with global multi-regional input–output tables? A comparative analysis for Belgium based on a structural decomposition
J. Econ. Struct.
Multiregional Input-output Database: OPEN:EU Technical Document. One Planet Economy Network, 7th Framework Programme for Research and Technological Development
Carbon footprint of nations: a global, trade-linked analysis
Environ. Sci. Technol.
The water footprint of humanity
Proc. Natl. Acad. Sci.
Environmental Footprints: an Methodological and Empirical Overview from the Perspective of Official Statistics
Comparative evaluation of mrio databases
Econ. Syst. Res.
Climate Change 2007–IPCC Fourth Assessment Report
Hållbara Konsumtionsmönster: Analyser Av Maten, Flyget Och Den Totala Konsumtionens Klimatpåverkan Idag Och 2050
Building eora: a global multi-region input–output database at high country and sector resolution
Econ. Syst. Res.
Environmental repercussions and economic structure - input-output approach
Rev. Econ. Stat.
Sustainable consumption as a systemic challenge: inter- and transdisciplinary research and research questions
National Water Footprint Accounts: the Green, Blue and Grey Water Footprint of Production and Consumption
The blue water footprint of electricity from hydropower
Hydrol. Earth Syst. Sci.
The green, blue and grey water footprint of crops and derived crop products
Hydrol. Earth Syst. Sci.
The Green, Blue and Grey Water Footprint of Farm Animals and Animal Products
Input-output Analysis: Foundations and Extensions
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2021, Cleaner and Responsible ConsumptionCitation Excerpt :Based on previous findings, researchers should try to further integrate the contributions from the fields of economics and industrial ecology; scholars should combine econometrically sound estimations of household spending with a broad perspective on the environmental impacts of consumption. This task may be facilitated by the increase in available environmentally extended multi-regional input-output databases in recent years (for an overview, see Dawkins et al., 2019). Furthermore, given the scarce and ambiguous evidence on the sign and magnitude of substitution effects discussed in the preceding section, more studies taking account of both income and substitution effects are required.