Hostname: page-component-7c8c6479df-27gpq Total loading time: 0 Render date: 2024-03-17T10:55:45.645Z Has data issue: false hasContentIssue false

Social Policy Without Growth: Moving Towards Sustainable Welfare States

Published online by Cambridge University Press:  04 October 2021

Max Koch*
Affiliation:
Socialhögskolan, Lund University, Lund, Sweden E-mail: max.koch@soch.lu.se
Rights & Permissions [Opens in a new window]

Abstract

Growth-dependent welfare states contribute to climate emergency. The ecological economics, degrowth, and sustainable welfare literatures demonstrate that to re-embed Western production and consumption patterns in environmental limits, an encompassing social-ecological transformation would need to be initiated very soon. This article focuses on the potential roles of the welfare state and social policy in this transformation, applying the concepts of ‘sustainable welfare’ and ‘safe-operating space’. Based on two Swedish studies, it also provides an empirical analysis of the popularity of selected eco-social policies designed to steer the economy and society towards this space: maximum and basic incomes, taxes on wealth and meat, as well as working time reductions. In analogy to the historical role of the state in reconstituting the welfare-work nexus in the post-WWII era and its present engagement in the context of the Covid-19 crisis, it is argued that a more interventionist state is required to grapple with climate emergency.

Type
Themed Section on Towards a Sustainable Welfare State
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution, and reproduction in any medium, provided the original work is properly cited.
Copyright
© The Author(s), 2021. Published by Cambridge University Press

Introduction: Climate emergency, economic growth and social policy

Thresholds for biophysical processes such as climate, biodiversity and the nitrogen cycle are being approached or crossed (Steffen et al., Reference Steffen, Rockström, Richardson, Lenton, Folke, Liverman, Summerhayes, Barnosky, Cornell, Crucifix, Donges, Fetzer, Lade, Scheffer, Winkelmann and Schellnhuber2018). In relation to climate change, the Intergovernmental Panel on Climate Change (IPCC, 2018) highlights that concentrations of CO2 and other greenhouse gases in the atmosphere have risen to levels unprecedented in 800,000 years. By 2100, the IPCC projects the global surface temperature increase to exceed 1.5°C relative to the period 1850–1900 in all but the most optimistic scenario considered. Other, increasingly more likely scenarios predict global temperatures to rise by as much as 3-4°C. While the 2015 Paris Agreement established an international covenant to reduce emissions on track with holding the temperature increase to ‘well below 2°C… and to pursue … 1.5°C’, Anderson et al. (Reference Anderson, Broderick and Stoddard2020) demonstrate that global modelling studies to achieve these targets came to increasingly rely on negative emissions technologies that are yet to become available. In the absence of such negative emissions technologies on a planetary scale, the time period to deliver fully decarbonised energy systems would be as early as 2035-2040 based on a calculation of remaining carbon budgets for the UK and Sweden – countries often associated with ‘progressive’ climate legislations (Anderson et al., Reference Anderson, Broderick and Stoddard2020). This calculation also considers the historical responsibility of the rich countries for the climate crisis, which translates into greater emission targets in the future.

Given the devastating effects on human and non-human livelihoods triggered by rapid temperature rise, over 11,000 scientists issued a warning of ‘climate emergency’ (Ripple et al., Reference Ripple, Wolf, Newsome, Barnard and Moomaw2020; Gills and Morgan, Reference Gills and Morgan2020). This ‘Alliance of World Scientists’ calls for ‘bold and drastic transformations’ in a range of policy areas. In unprecedentedly clear-cut terms it states that ‘economic growth must be quickly curtailed’ to ‘maintain long-term sustainability of the biosphere’ and that the goals of economic and other policy making ‘need to shift from GDP growth … toward sustaining ecosystems and improving human well-being by prioritising basic needs and reducing inequality’ (Ripple et al., Reference Ripple, Wolf, Newsome, Barnard and Moomaw2020: 11). This echoes recent comparative empirical studies (Parrique et al., Reference Parrique, Barth, Briens, Kerschner, Kraus-Polk, Kuokkanen and Spangenberg2019; Haberl et al., Reference Haberl, Wiedenhofer, Virág, Kalt, Plank, Brockway, Fishman, Hausknost, Krausmann, Leon-Gruchalski, Mayer, Pichler, Schaffartzik, Sousa, Streeck and Creutzig2020), indicating that attempts to absolutely decouple GDP growth from material resource use and greenhouse gas emissions either failed totally or did not reach the extent necessary for the large and rapid reduction of these parameters to meet the Paris climate targets. The corollary is that ‘decoupling needs to be complemented by sufficiency-oriented strategies and strict enforcement of absolute reduction targets’ (Haberl et al., Reference Haberl, Wiedenhofer, Virág, Kalt, Plank, Brockway, Fishman, Hausknost, Krausmann, Leon-Gruchalski, Mayer, Pichler, Schaffartzik, Sousa, Streeck and Creutzig2020: 1) as well as a de-prioritisation of GDP growth as an overall target in policy making (Parrique et al., Reference Parrique, Barth, Briens, Kerschner, Kraus-Polk, Kuokkanen and Spangenberg2019).

The objective of the present article is to further understand the roles of social policy and the welfare state within broader social-ecological transformations in a postgrowth context. Though still a fringe topic within social policy scholarship, the intersection of welfare/social policy and the environment/environmental policies has been increasingly addressed in the last two decades (Stamm et al., Reference Stamm, Matthies, Hirvilammi and Närhi2020: 43-44); particularly in publications by Michael Cahill (e.g. Reference Cahill2002), Tony Fitzpatrick (e.g. Reference Fitzpatrick2014) and Ian Gough (e.g. Reference Gough2017). According to these authors, welfare systems should be conceptualised as embedded in ecosystems and in need of respecting the regeneration capacity of the biosphere. Subsequent research included various sorts of eco-social policies (Hirvilammi and Helne, Reference Hirvilammi and Helne2014), the limits of the ‘environmental state’ and potentials of the ‘eco-social state’ (Koch and Fritz, Reference Koch and Fritz2014; Gough, Reference Gough2016; Hausknost, Reference Hausknost2020; Koch, Reference Koch2020a). Relevant theoretical concepts have been developed under the headings of ‘sustainable welfare’ (Koch and Mont, Reference Koch and Mont2016; Koch et al., Reference Koch, Gullberg, Koch, Schoyen and Hvinden2016; Büchs and Koch, Reference Büchs and Koch2017) and a ‘good life for all within planetary boundaries’ (O’Neill et al., Reference O’Neill, Fanning, Lamb and Steinberger2018). In what follows I will use ‘sustainable welfare’ as an umbrella term to conceptualise the intersection of social and environmental goals and policies.

For a better understanding of social policy and welfare states within wider social-ecological transformations, the article methodologically triangulates literature review, theory application as well as qualitative and quantitative data analyses.Footnote 1 Since historical analogies can help understand possible features of future patterns of change, it starts from the political and economic conjuncture of the post-WWII period, rehearsing how social policy and the state came to regulate capitalist growth. This is followed by a theoretical outline of the roles of the welfare state and social policy within a ‘sustainable welfare’ strategy aimed at ensuring economic and social practices proceed within a ‘safe operating space’ (Raworth, Reference Raworth2017). The subsequent section complements this by examining concrete eco-social policies, which previous research suggested to respect the upper and lower boundaries of this space, and a presentation and discussion of qualitative and quantitative data on the popularity of some of these proposals for Sweden, considering specificities of the social-democratic welfare context. The conclusion summarises and reflects on the main findings and identifies some future research avenues.

Socio-economic regulation in the postwar growth strategy

In Western Europe, the entire welfare-work nexus came on the agenda after World War II. The new Fordist welfare-work nexus rested on the recognition of trade unionism and more or less centralised collective bargaining (Aglietta, Reference Aglietta1987). As a result, wages were indexed to productivity growth, while fiscal and credit policies were orientated towards the creation of effective demand in national economies. The trade unions respected the management’s power to control (often Taylorized) work processes. The state supported this ‘class compromise’ by means of policies designed to integrate the circuits of the capital and consumer goods industries, and by mediating conflicts between capital and labour, especially over individual and social wages. It also helped achieve growth and productivity through public infrastructure spending and permissive credit and monetary policies. As a corollary, production and consumption norms increased in parallel – particularly in the case of mass-produced consumer goods of longevity such as refrigerators, televisions, cars and standardised housing – resulting in unprecedented growth rates in GDP and real wages, especially in the 1950s and 1960s. The state could use the growing tax take from the primary incomes of the labour market parties to create and/or expand welfare systems to cover risks such as old age, sickness and unemployment.

It is well known in social policy circles that the post-war regulation of economic growth assumed different national shapes. Welfare ‘regimes’ (e.g. Esping-Andersen, Reference Esping-Andersen1990; Arts and Gelissen, Reference Arts and Gelissen2002) vary, above all, in terms of the division of social labour between market and public spheres to which different forms and levels of taxation correspond, and are associated with different patterns of stratification. Esping-Andersen characterised the ‘social-democratic’ countries (e.g. Sweden) as having the highest degree of universalism in welfare programmes with a correspondingly weak role for the market, especially concerning care for children and the elderly. This welfare cluster offered the greatest extent of redistribution of the primary incomes from capital and labour, and the lowest degree of stratification. Conversely, ‘liberal’ welfare regimes (e.g. UK) represented the lowest decommodification and highest stratification potential and a corresponding emphasis on individual responsibility in combination with a greater welfare role of private and civil sector agencies. This overall orientation does not exclude that the UK real type nevertheless featured some ‘universal’ elements – particularly in the health sector. The third originalFootnote 2 welfare regime was the ‘conservative’ one (e.g. Germany) with medium decommodification and stratification, where state welfare, unemployment and pension policies were not designed to redistribute market inequalities but tended to reproduce original social positions.

The welfare regime approach has subsequently been taken up in ecological modernisation discourses. According to Dryzek (in Gough et al., Reference Gough, Meadowcroft, Dryzek, Gerhards, Lengfeld, Markandya and Ortiz2008), social-democratic countries are better positioned than liberal countries to manage the intersection of social and environmental policies. This is due to the greater support within social-democratic countries for the idea that environmental policies could be good for business, and their more developed state apparatuses and functioning governance regimes, which are seen as preconditions for ‘green growth’ trajectories. The result would be a ‘mainstreaming of both environmental and equality concerns’ (Gough et al., Reference Gough, Meadowcroft, Dryzek, Gerhards, Lengfeld, Markandya and Ortiz2008: 330). Yet, in relation to key environmental indicators such as CO2 emissions per capita and the ecological footprints of production and consumption, comparative research (Koch and Fritz, Reference Koch and Fritz2014; Duit, Reference Duit2016; Zimmermann and Graziano, Reference Zimmermann and Graziano2020) could not verify the ‘synergy hypothesis’ that social democratic countries as a whole perform better than liberal or conservative countries. What in fact most affects countries’ objective environmental performances is not so much welfare regime affiliation but the level of their GDP per capita (Fritz and Koch, Reference Fritz and Koch2016): in general, the richer a country the worse is its performance in environmental indicators. However, there is also comparative research on attitudes towards providing climate and welfare (‘eco-social’) policies simultaneously (Fritz and Koch, Reference Fritz and Koch2019; Otto and Gugushvili, Reference Otto and Gugushvili2020), which supports the synergy hypothesis to some extent. Citizens of the Nordic countries are most prepared to back a combined eco-social policy strategy, even though this has hitherto not had any implications on the objective ecological performance of these countries. The attitudes of Swedish citizens on selected eco-social policies will be explored below.

The most recent period did not bring a loosening of the close link between economic growth and welfare state activity, but a transition in emphasis from Keynesian demand towards ‘Schumpeterian’ supply management (Jessop, Reference Jessop1999) in the context of the transnationalisation and financialisation of production and investment. Welfare institutions became modified and received new functions within the general structure of the ‘competition state’ (Cerny, Reference Cerny2010). Designed to support competing national and/or local actors in the global economy, social policy came itself to be regarded as ‘investment’ (Hemerijck, Reference Hemerijck2018). However, demand and supply strategies of socio-economic regulation have hitherto had in common that they largely ignore the environmental aspects of welfare capitalist development. In relation to ecological and carbon footprints, at no point in time after WWII were Western material welfare standards generalisable to the rest of the planet (Fritz and Koch, Reference Fritz and Koch2016; O’Neill et al., Reference O’Neill, Fanning, Lamb and Steinberger2018) – despite the fact that these were culturally celebrated, ideologically reinforced and exported to many other parts of the world. In fact, had citizens of all nations led similar lifestyles as Westerners, the planet would have ended up in acute climate emergency significantly earlier.

Safe operating space and sustainable welfare

The framework of a ‘safe and just operating space’ (Raworth, Reference Raworth2017) may serve as a point of departure for conceptualising welfare state activity and eco-social policymaking in a postgrowth context, since it considers both planetary and social boundaries. Economy and society develop within a doughnut-shaped space, where resource use is below the level of critical planetary limits (the outer boundary or the safe and ecologically sustainable space), but above the sufficiency level required to meet people’s basic needs (the inner boundary or the socially just space).Footnote 3 Not only is the economy here conceptualised as a subsystem of the biophysical and social systems (Fig. 1), but welfare systems would then likewise be regarded as ‘embedded in the ecological context’ (Hirvilammi, Reference Hirvilammi2020: 6) and grasped as ‘provisioning systems’ (Fanning et al., Reference Fanning, O’Neill and Büchs2020) for sustainable need satisfiers. Considering the upper boundary, welfare state activity and social policies would no longer assume the simplistic form of redistributing growing tax takes (as in the post-war period) but involve controversial decisions targeted at the power resources of affluent and influential groups.

Figure 1. Inner and outer boundaries for economic and societal development.

The concept of ‘sustainable welfare’ (Koch and Mont, 2016) in general and theories of human need in particular may serve as theoretical context for a new generation of state engagement and social policies (Koch, Reference Koch2020a). Starting from the ‘double injustice’ (Walker, Reference Walker2012) – that responsibilities and impacts of climate change often work in opposing ways, since the groups likely to be affected most are the ones least responsible for causing it – sustainable welfare considers the fact that social policies will need to counter the inequalities and conflicts that are likely to emerge as a result of the decarbonisation of production and consumption patterns, and that it will be increasingly necessary to formulate them in ways that create synergies with environmental goals, yet are also acceptable to the electorate. This includes the recognition of critical thresholds and limitations for material welfare, a correspondingly critical review of existing welfare systems and the notion that in a constrained world not all ‘wants’ for often ‘positional’ goods can be politically supported in the name of consumer sovereignty. Some would indeed need to be restrained. Further debates in sustainable welfare and degrowth/postgrowth circles (Büchs and Koch, Reference Büchs and Koch2017) have resulted in the adoption of needs-based accounts (Max-Neef, Reference Max-Neef1991; Gough, Reference Gough2017) over hedonic, utilitarian and subjective accounts of wellbeing.

Max-Neef’s Human Scale Development methodology introduced the term ‘satisfier’ to highlight the culturally specific – and more or less ecologically sustainable – ways in which needs are being met in practice (Guillén-Royo, Reference Guillén-Royo2015). Also in Gough’s ‘dual strategy’ the practical knowledge of citizens complements the various sorts of expert knowledge on sustainable needs satisfaction. From the perspective of a wider social-ecological transformation, policy ideas serving as what Max-Neef called ‘synergetic’ needs satisfiers are particularly relevant as they have the potential of fulfilling more than just one need in different contexts and may hence serve as entry points for initiating a ‘virtuous policy circle of sustainable welfare’ (Hirvilammi, Reference Hirvilammi2020). Academic and policy deliberations circling around welfare provisioning systems within the ‘safe and just operating space’ have further attempted to identify maximum and minimum levels for needs satisfaction as well as eco-social policy instruments with the potential of steering the economy and society towards respecting these ‘floors and ceilings’ (Gough, Reference Gough2020; see below).

There are overlaps between the debates about satisfying needs at sufficiency or minimum levels and vindicating social rights. Themes often addressed in social rights discourses such as housing, education, health and minimum income would be treated as basic needs currently in jeopardy in sustainable welfare approaches. In relation to housing and the sufficiency level of needs satisfaction, the latter would promote provisions to guarantee everyone a certain quantity of square meters to live: that is, independent of ability to pay. Hence, housing at sufficiency level would be treated as a social right and not as an area of financial investment. Yet on top of this and concerning the maximum level of needs satisfaction, the sustainable welfare perspective would call for limitations to living beyond a certain threshold of square meters: for example, by taxation. Targeting inheritance, high incomes and wealth through taxation (Buch-Hansen and Koch, Reference Buch-Hansen and Koch2019) – again the higher end of needs satisfaction or luxuries – would not only simultaneously serve ecological targets (since the rich emit over proportional amounts of greenhouse gases) and social equality but also constitute an important means to decouple the financialisation of welfare state activity from economic growth.Footnote 4

Selected eco-social policies and their popularity in a Nordic welfare context

This section reviews a selection of concrete eco-social policy proposals that previous research identified as capable of steering economy and society towards the ‘safe operating space’ outlined above, highlighting both upper and lower boundaries: maximum income, wealth tax, basic income, reduction in working hours and meat tax. It presents and discusses corresponding qualitative and quantitative data from two ongoing projects at Lund University for Sweden and the social-democratic welfare context: ‘Sustainable Welfare for a New Generation of Social Policy’Footnote 5 and ‘The New Urban Challenge: Models of Sustainable Welfare in Swedish Metropolitan Cities’.Footnote 6 The former project gathered data on needs satisfaction and eco-social policies from eighty-four participants in eleven deliberative citizen forums. The latter conducted a representative survey with new quantitative data on some of these policies. Both data sets were collected in 2020, with the aim of rectifying the current knowledge gap concerning public support for eco-social policy measures within specific welfare contexts. In some cases, such as maximum incomes, there is no data concerning their popularity at all. Which eco-social policies regarding upper and lower levels of needs satisfaction were frequently mentioned in the forums? How popular are the selected policy ideas in the Swedish population as a whole? To what extent can the study findings be generalised to other welfare-state contexts, with weaker emphasis on universalism and state redistribution?

In the debate on the role of the welfare state in safeguarding needs satisfaction at a sufficiency level – the inner boundary of the ‘safe operating space’ – proponents for an eco-social or sustainable welfare state argue for the introduction of a universal and unconditional basic income (UBI, e.g. Van Parijs and Vanderborght, Reference Van Parijs and Vanderborght2017), the expansion/introduction of universal basic services (UBS, e.g. Coote and Percy, Reference Coote and Percy2020), a voucher system (Bohnenberger, Reference Bohnenberger2020) or a combination of the three. Forum participants mentioned UBI particularly often and in various contexts, highlighting the potentially high degree of sustainable satisfaction of needs (in Max-Neef’s terminology) as different as subsistence, participation, leisure, creation and freedom. Yet many also argued for an expansion of UBS: that is, in the Swedish context, beyond health and care and especially in the areas of transport, digitalisation and food provision. Complementing previous contributions expressing the tensions and contradictions between UBI and UBS (see, for the different perspectives, Lombardozzi, Reference Lombardozzi2020, and Coote and Percy, Reference Coote and Percy2020), this points towards a demand for exploring the institutional and financial conditions that would allow combinations of UBI and UBS to function as provisioning systems of sustainable needs satisfiers and how such mixes may look.

Such research could begin from the hypothesis that welfare regimes and institutional path dependency may be important factors in determining concrete national mixes of UBS, UBI and possibly vouchers. Where there is already a strong universal tradition in welfare delivery such as in the Nordic countries, it may be easiest to expand these systems, while there would be a minor role for UBI. This hypothesis is supported by the fact that just over 17 per cent are in favour and 71 per cent against the introduction of UBI in Sweden (Table 1). Hence, here UBS would be a more appropriate institutional basis for a social-ecological transformation, possibly extended and selectively complemented with (more or less means-tested) minimum income schemes. Yet where UBS exists in merely rudimentary forms and liberal welfare traditions predominate, UBI may be the easiest and quickest option for proceeding. This is because the build-up of universal welfare systems takes considerable time and could in all likelihood proceed in the mid- to long-term perspective only.

Table 1 Support for eco-social policies in Sweden 2020 (percentages)

Source. Representative survey conducted within the Project ‘The New Urban Challenge: Models of Sustainable Welfare in Swedish Metropolitan Cities’. Respondents were asked to evaluate the above policy suggestions and answered on five-point Likert scales that contained the following categories: very good and fairly good (‘in favour’), quite bad and very bad (‘against’), neither good nor bad (‘undecided’).

Concerning the upper boundary, much fewer proposals have been tabled. However, there are now philosophical approaches defending ‘limitarianism’ in an ecologically constrained world (Robeyns, Reference Robeyns2019), to which social policy scholars may turn, and more concrete economic proposals (Concialdi, Reference Concialdi2018; Pizzigatti, Reference Pizzigatti2018), suggesting the definition of maximum incomes as some quantitative proportion from minimum incomes (10:1, 20:1 etc.). There is, however, no agreement about where exactly the cap level (beyond which taxation would be 100 per cent) should be set and whether all forms of wealth should be targeted (Buch-Hansen and Koch, Reference Buch-Hansen and Koch2019). Given the newness of a policy proposal, for the introduction of which no major political party currently campaigns, it does not strike one as particularly surprising that no more than a quarter of the Swedish population supports a maximum income set at approximately 145,000 Euro a year (Table 1). However, it is not inconceivable that the backing for such a policy would increase, if it were promoted more actively and made the object of bottom-up policy deliberations.Footnote 7 Not surprisingly, support for the comparatively moderate but better-known tax on wealth, which currently doesn’t exist either in Sweden, is significantly higher (42.5 per cent). Forum participants mentioned the latter proposal more frequently as many were unaware of the recent academic debate about caps on wealth and/or income.

Two further eco-social reform suggestions, often highlighted in the forums as synergetic satisfiers for universal needs as different as protection, participation, leisure, creation and freedom (following Max-Neef’s terminology), are a reduction of working hours (especially to defuse the work-spend-consume circle) and a tax on meat consumption (to support ecological agriculture, a more vegetarian nutrition and a general transition to a post-fossil lifestyle). A reduction of working hours is by far the most popular policy instrument selected here: Almost 52 per cent of respondents would like to see a regular working week of thirty hours in Sweden (as opposed to forty now). Despite this, only the Swedish Left party (Vänster) campaigns for this policy. The support for a meat tax stood at 30 per cent with almost 53 per cent opposing this policy suggestion. However, 17 per cent of ‘undecided’ respondents indicates a greater structural potential for popularity.

The relatively high support scores for a wealth tax and working hour reduction seem to suggest that governments, particularly in social-democratic welfare contexts such as Sweden, could be bolder than currently in implementing eco-social policies. But also the attractiveness of increasingly far-reaching Green New Deal models (Galvin and Healy, Reference Galvin and Healy2020; Mastini et al., Reference Mastini, Kallis and Hickel2021) in the USA and beyond indicates that civil society mobilisation, political parties and government agencies may in fact reinforce each other to create the momentum necessary for social-ecological transformations. That governments continue to be capable of initiating far-reaching change is highlighted by Eckersley (Reference Eckersley2020) at the example of the current Covid-19 crisis: After several decades of welfare state retreat, the immediate reaction of Western governments was an expansion of the state’s activity – from restrictions on mobility via new types of welfare payments to stimulus packages for businesses. Concerning a possible exit from the Covid-19 and climate crises in combination, Eckersley (Reference Eckersley2020: 18) suggests a ‘stimulus spending on green infrastructure with a sequenced phase-out of the most emissions-intensive and ecologically harmful industries’ to enable an ecological restructuring of the economy after the Covid-19 crisis.

Yet, in general, the empirical results point to a considerable gap between the far-reaching measures that scientists consider necessary to meaningfully address climate emergency (see Introduction) and the measures that citizens of an advanced welfare state such as Sweden are presently prepared to support.Footnote 8 Explanations for this gap include the thorough inculcation of the growth imperative in people’s minds, bodies and day-to-day social practices, often appearing as the ‘natural’ way of doing things (Koch, Reference Koch2018). Since it is part of the collective consciousness that a range of institutions – such as the legal, educational and welfare systems, which have proven to be crucial for the relatively high subjective wellbeing scores measured in Western societies – historically co-developed with the provision of economic growth and are presently coupled to it, any political move beyond the capitalist growth economy would need to reckon with concerns about wellbeing loss, anomy and social exclusion (Büchs and Koch, Reference Büchs and Koch2019). One way to defuse these concerns is to expand already existing spaces, where alternative, sustainable and cooperative forms of working and living together are tested. For this purpose, it would be necessary to carry out participatory exercises (such as workshops, consultations or deliberative forums) much more often and on greater scales than in our forums (Guillén-Royo, Reference Guillén-Royo2020; Koch, Reference Koch2020b). As the Irish example suggests (Harris, Reference Harris, Hogan and Murphy2021), governments could support this by enhancing the status of citizen forums and giving them advisory character. This would be in line with recent arguments from political theorists that an adequate response to the ecological crisis requires augmenting the institutions of representative democracy with mechanisms of direct and deliberate democracy that carry the potential of ‘disruptive deliberation’ (Hammond, Reference Hammond2020).

Conclusion

Against the background of climate emergency, overshoot of other planetary boundaries and the failure of ‘green growth’ policy responses, this paper addressed the potential role of social policy in broader social-ecological transformations in a postgrowth context. It reviewed previous relevant literature, the theoretical concepts of ‘sustainable welfare’ and ‘safe operating space’ as well as eco-social policy ideas designed to steer the economy and society to operate within this space, and presented and discussed qualitative and quantitative data for Sweden and a Nordic welfare context.

The literature and theory reviews suggest that a move from existing towards sustainable welfare states would, irrespective of institutional point of departure and welfare regime affiliation, require a fundamental transformation from the expansionary logic that characterised Western welfare provision since the post-war period to one that seriously considers environmental and social limits (here considered as ‘safe operating space’). However, the empirical results indicate that welfare regime affiliation may be an important factor when it comes to the identification of concrete national trajectories within this general line of change. While previous comparative research demonstrated that citizens of the Nordic countries are most prone to support welfare and climate policies in combination, the present study added knowledge on the support for particular policies designed to steer the economy and society towards a safe operating space. In relation to the lower boundary, much speaks for Sweden and the social-democratic welfare tradition to immediately expand UBS, while UBI may be more relevant for liberal countries. Concerning the upper boundary, support is much greater for a wealth tax than for a cap on income/wealth. However, this result may be co-determined by a lack of awareness of the latter policy proposal.

Future conceptual development of the sustainable welfare approach should incentivise the dialogue between degrowth, philosophical limitarianism and social policy to further improve our understanding of welfare and wellbeing within planetary limits. Politically, it will be crucial to not only discuss and study single policy suggestions but also develop models of how these may reinforce each other in a new virtuous policy circle. The support for such a policy strategy as well as for single policies is likely to increase when co-developed by researchers, activists and citizens in various kinds of deliberative forums, including at greater scales than in the present study. Concerning empirical research of eco-social policies, future studies should consider more and different types of policies than in the present article and explore the social composition of their supporters and rejecters along the lines of class, gender, ethnicity and age. This knowledge would be crucial for the formation of political alliances to bring about the calibre of societal change that an effective and socially inclusive response to climate emergency requires.

Acknowledgements

I wish to thank the editors of this themed section and two anonymous reviewers for their constructive feedback on earlier drafts. This research benefited from funding from the Swedish Energy Agency (Energimyndigheten) [grant no. 48510-1], the Swedish Research Council FORMAS (grant no. 2016-00340) and Lund University’s research programme for excellence, focusing on Agenda 2030 and sustainable development (project “Postgrowth Welfare Systems”).

Footnotes

1 The kinds of data employed are introduced at the beginning of the section ’Selected eco-social policies and their popularity in a Nordic welfare context’ below.

2 For further developments of the welfare regime debate including additional types see Arts and Gelissen (Reference Arts and Gelissen2002) and Emmenegger et al. (Reference Emmenegger, Kvist, Marx and Petersen2015).

3 Spash (Reference Spash2020) and Koch and Buch-Hansen (Reference Koch and Buch-Hansen2020) suggest to further theorise this space in relation to institutional features, power asymmetries and material interests.

4 On the ‘repolitization’ of the fiscal capacity of the state in the absence of economic growth, see Bailey (Reference Bailey2020).

7 Several of the forum participants suggested the introduction of citizen assemblies for Sweden. Concerning caps on income and/or wealth these could identify concrete thresholds and deliberate how the generated tax surplus may be used.

8 The representative survey was conducted between January and March 2020: that is, before the magnitude of the Covid-19 crisis became fully discernible. It is conceivable that the support rates for policies such as UBI or income caps would be somewhat higher now that the crisis has enfolded.

References

Aglietta, M. (1987) A Theory of Capitalist Regulation: The US Experience, London: Verso.Google Scholar
Anderson, K., Broderick, J.F. and Stoddard, I. (2020) ‘A factor of two: how the mitigation plans to “climate progressive” nations fall short of Paris-compliant pathways’, Climate Policy, 20, 10, 12901304.CrossRefGoogle Scholar
Arts, W. and Gelissen, J. (2002) ‘Three worlds of welfare capitalism or more? A state-of-the-art report’, Journal of European Social Policy, 6, 2, 87100.Google Scholar
Bailey, D. (2020) ‘Re-thinking the fiscal and monetary political economy of the green state’, New Political Economy, 25, 1, 517.CrossRefGoogle Scholar
Bohnenberger, K. (2020) ‘Money, vouchers, public infrastructures? A framework for sustainable welfare benefits’, Sustainability, 12, 2, 596.CrossRefGoogle Scholar
Buch-Hansen, H. and Koch, M. (2019) ‘Degrowth through income and wealth caps?Ecological Economics, 160, 264–71.CrossRefGoogle Scholar
Büchs, M. and Koch, M. (2017) Postgrowth and Wellbeing: Challenges to Sustainable Welfare, Basingstoke: Palgrave Macmillan.CrossRefGoogle Scholar
Büchs, M. and Koch, M. (2019) ‘Challenges to the degrowth transition: the debate about wellbeing’, Futures, 105, 155–65.CrossRefGoogle Scholar
Cahill, M. (2002) The Environment and Social Policy, London: Routledge.Google Scholar
Cerny, P.G. (2010) ‘The competition state today: from raison d’etat to raison du monde’, Policy Studies, 31, 1, 521.CrossRefGoogle Scholar
Concialdi, P. (2018) ‘What does it mean to be rich? Some conceptual and empirical issues’, European Journal of Social Security, 20, 1, 320.CrossRefGoogle Scholar
Coote, A. and Percy, A. (2020) The Case for Universal Basic Services, Cambridge: Polity.Google Scholar
Duit, A. (2016) ‘The four faces of the environmental state: environmental governance regimes in 28 countries’, Environmental Politics, 25, 1, 6991.CrossRefGoogle Scholar
Eckersley, R. (2020) ‘Greening states and societies: from transitions to great transformations’, Environmental Politics, doi: 10.1080/09644016.2020.1810890.CrossRefGoogle Scholar
Emmenegger, P., Kvist, J., Marx, P. and Petersen, K. (2015) ’Three world of welfare capitalism: the making of a classic’, European Journal of Social Policy, 25, 1, 310.CrossRefGoogle Scholar
Esping-Andersen, G. (1990) The Three Worlds of Welfare Capitalism, Cambridge: Polity.Google Scholar
Fanning, A.L., O’Neill, D.W. and Büchs, M. (2020) Provisioning systems for a good life within planetary boundaries’, Global Environmental Change, 64, 102135.CrossRefGoogle Scholar
Fitzpatrick, T. (ed.) (2014) International Handbook on Social Policy and the Environment, Cheltenham: Edward Elgar.CrossRefGoogle Scholar
Fritz, M. and Koch, M. (2016) ‘Economic development and prosperity patterns around the world: structural challenges for a global steady-state economy’, Global Environmental Change, 38, 41–8.CrossRefGoogle Scholar
Fritz, M. and Koch, M. (2019) ‘Public support for sustainable welfare compared: links between attitudes towards climate and welfare policies’, Sustainability, 11, 15, 4146.CrossRefGoogle Scholar
Galvin, R. and Healy, N. (2020) ‘The Green New Deal in the United States. What it is and how to pay for it’, Energy Research and Social Science, 67, 101529.CrossRefGoogle Scholar
Gills, B. and Morgan, J. (2020) ‘Global climate emergency: after COP24, climate science, urgency, and the threat to humanity’, Globalizations, 17, 6, 885902.CrossRefGoogle Scholar
Gough, I. (2016) ‘Welfare states and environmental states: a comparative analysis’, Environmental Politics, 25, 2447.CrossRefGoogle Scholar
Gough, I. (2017) Heat, Greed and Human Need: Climate Change, Capitalism and Sustainable Wellbeing, Cheltenham: Edward Elgar.CrossRefGoogle Scholar
Gough, I. (2020) ‘Defining floors and ceilings: the contribution of human needs theory’, Sustainability: Science, Practice and Policy, 16, 1, 208–19.Google Scholar
Gough, I., Meadowcroft, J., Dryzek, J., Gerhards, J., Lengfeld, H., Markandya, A. and Ortiz, R. (2008) ‘JESP symposium: climate change and social policy’, Journal of European Social Policy, 18, 4, 2544.CrossRefGoogle Scholar
Guillén-Royo, M. (2015) Sustainability and Wellbeing: Human-Scale Development in Practice, London: Routledge.Google Scholar
Guillén-Royo, M. (2020) ‘Applying the fundamental human needs approach to sustainable consumption corridors: participatory workshops involving information and communication technologies’, Sustainability: Science, Practice and Policy, 16, 1, 114–27.Google Scholar
Haberl, H., Wiedenhofer, D., Virág, D., Kalt, G., Plank, B., Brockway, P., Fishman, T., Hausknost, D., Krausmann, F., Leon-Gruchalski, B., Mayer, A., Pichler, M., Schaffartzik, A., Sousa, T., Streeck, J. and Creutzig, F. (2020) ’A systematic review of the evidence on decoupling of GDP, resource use and GHG emissions, part II: synthesizing the insights’, Environmental Research Letters, 15, 6, 065003.CrossRefGoogle Scholar
Hammond, M. (2020) ‘Democratic deliberation for sustainability transformations: between constructiveness and disruption’, Sustainability: Science, Practice and Policy, 16, 1, 220–30.Google Scholar
Harris, C. (2021) ‘Democratic innovations and policy analysis: climate policy and Ireland’s citizens’ assembly’, in Hogan, J. and Murphy, M. P. (eds.), Policy analysis in Ireland, Bristol: Policy Press, 221-35.Google Scholar
Hausknost, D. (2020) ‘The environmental state and the glass ceiling of transformation’, Environmental Politics, 29, 1, 1737.CrossRefGoogle Scholar
Hemerijck, A. (2018) ‘Social investment as a policy paradigm’, Journal of European Social Policy, 25, 6, 810–27.Google Scholar
Hirvilammi, T. (2020) ‘The virtuous circle of sustainable welfare as a transformative policy idea’, Sustainability, 12, 1, 391.CrossRefGoogle Scholar
Hirvilammi, T. and Helne, T. (2014) ‘Changing paradigms: a sketch for sustainable wellbeing and ecosocial policy’, Sustainability, 6, 2160–75.CrossRefGoogle Scholar
IPCC (International Panel on Climate Change) (2018) Global Warming of 1.5°C: An IPCC Special Report, https://www.ipcc.ch/sr15/.Google Scholar
Jessop, B. (1999) ‘The changing governance of welfare. Recent trends in its primary functions, scale, and modes of coordination’, Social Policy and Administration, 33, 4, 348–59.CrossRefGoogle Scholar
Koch, M. (2018) ‘The naturalisation of growth: Marx, the regulation approach and Bourdieu’, Environmental Values, 27, 1, 927.CrossRefGoogle Scholar
Koch, M. (2020a) ‘The state in the transformation to a sustainable postgrowth economy’, Environmental Politics, 29, 1, 115–33.CrossRefGoogle Scholar
Koch, M. (2020b) ‘Structure, action and change: a Bourdieusian perspective on the preconditions for a degrowth transition’, Sustainability: Science, Practice and Policy, 16, 1, 414.Google Scholar
Koch, M. and Buch-Hansen, H. (2020) ‘In search of a political economy of the postgrowth era’, Globalizations, doi: 10.1080/14747731.2020.1807837.CrossRefGoogle Scholar
Koch, M. and Fritz, M. (2014) ‘Building the eco-social state: do welfare regimes matter?Journal of Social Policy, 43, 4, 679703.CrossRefGoogle Scholar
Koch, M., Gullberg, A.-T., Koch, M., Schoyen, M.A. and Hvinden, B. (2016) ‘Sustainable welfare in the EU: promoting synergies between climate and social policies’, Critical Social Policy, 36, 4, 704–15.CrossRefGoogle Scholar
Koch, M. and Mont, O. (eds.) (2016) Sustainability and the Political Economy of Welfare, London: Routledge.CrossRefGoogle Scholar
Lindellee, J., Alkan-Olsson, J. and Koch, M. (2021) ‘Operationalizing sustainable welfare and co-developing eco-social policies by prioritising human needs’, Global Social Policy, doi: 10.1177/14680181211019164.CrossRefGoogle Scholar
Lombardozzi, L. (2020) ‘Gender inequality, social reproduction and the universal basic income.The Political Quarterly, 91, 2, 317–23.CrossRefGoogle Scholar
Mastini, R., Kallis, G. and Hickel, J. (2021) ‘A Green New Deal without growth?Ecological Economics, 179, 106832.CrossRefGoogle Scholar
Max-Neef, M. (1991) Human Scale Development: Conception, Application and Further Reflections, New York: Zed Books Ltd.Google Scholar
O’Neill, D.W., Fanning, A.L., Lamb, W.F. and Steinberger, J. K. (2018) ‘A good life for all within planetary boundaries’, Nature Sustainability, 1, 8895.CrossRefGoogle Scholar
Otto, A. and Gugushvili, D. (2020) ‘Eco-Social divides in Europe: public attitudes towards welfare and climate change policies’, Sustainability, 12, 404.CrossRefGoogle Scholar
Parrique, T., Barth, J., Briens, F., Kerschner, C., Kraus-Polk, A., Kuokkanen, A. and Spangenberg, J. H. (2019) Decoupling debunked. Evidence and arguments against green growth as a sole strategy for sustainability, Brussels: European Environment Bureau.Google Scholar
Pizzigatti, S. (2018) The Case for a Maximum Wage, Cambridge: Polity.Google Scholar
Raworth, K. (2017) Doughnut Economics: Seven Ways to Think Like a 21st-Century Economist, London: Random House Business.Google Scholar
Ripple, W. J., Wolf, C., Newsome, T. M., Barnard, P. and Moomaw, W. R. (2020) ‘World scientists’ warning of a climate emergency’, BioScience, 70, 1, 812.CrossRefGoogle Scholar
Robeyns, I. (2019) ‘What, if anything, is wrong with extreme wealth?’, Journal of Human Development and Capabilities, 20, 3, 251–66.CrossRefGoogle Scholar
Spash, C. L. (2020) ‘The economy as if people mattered: revisiting critiques of economic growth in a time of crisis’, Globalizations, doi: 10.1080/14747731.2020.1761612.CrossRefGoogle Scholar
Stamm, I., Matthies, A.-L., Hirvilammi, T. and Närhi, K. (2020) ‘Combining labour market and unemployment policies with environmental sustainability? A cross-national study on ecosocial innovations’, Journal of International and Comparative Social Policy, 36, 1, 4256.CrossRefGoogle Scholar
Steffen, W., Rockström, J., Richardson, K., Lenton, T. M., Folke, C., Liverman, D., Summerhayes, C. P., Barnosky, A. D., Cornell, S. E., Crucifix, M., Donges, J. F., Fetzer, I., Lade, S. J., Scheffer, M., Winkelmann, R. and Schellnhuber, H. J. (2018) ‘Trajectories of the earth system in the Anthropocene’, Proceedings of the National Academy of Science of the United States of America, 115, 33, 8252–59.CrossRefGoogle ScholarPubMed
Van Parijs, P. and Vanderborght, Y. (2017) Basic Income: A Radical Proposal for a Free Society and a Sane Economy, Cambridge: Harvard University Press.CrossRefGoogle Scholar
Walker, G. (2012) Environmental Justice: Concepts, Evidence and Politics, London: Routledge.CrossRefGoogle Scholar
Zimmermann, K. and Graziano, P. (2020) ‘Mapping different worlds of eco-welfare states’, Sustainability, 12, 5, 1819.CrossRefGoogle Scholar
Figure 0

Figure 1. Inner and outer boundaries for economic and societal development.

Figure 1

Table 1 Support for eco-social policies in Sweden 2020 (percentages)