Eight Tons of Material Footprint—Suggestion for a Resource Cap for Household Consumption in Finland

Lettenmeier, Michael; Liedtke, Christa; Rohn, Holger

doi:10.3390/resources3030488

Open AccessArticle

Eight Tons of Material Footprint—Suggestion for a Resource Cap for Household Consumption in Finland

by

Michael Lettenmeier^1,2,6,*,

Christa Liedtke^1,3 and

Holger Rohn^1,4,5

¹

Wuppertal Institute for Climate, Environment and Energy, Döppersberg 19, Wuppertal 42103, Germany

²

Ltd., Purokatu 34, Lahti 15200, Finland

³

Folkwang University of the Arts, Industrial Design, Klemensborn 39, Essen 45239, Germany

⁴

Faktor 10—Institut für nachhaltiges Wirtschaften gemeinnützige GmbH, Alte Bahnhofstraße 13, Friedberg 61169, Germany

⁵

Institute of Refrigerating and Biotechnology Lomonosov, ITMO University, Ulitsa 9, St. Petersburg 191002, Russia

⁶

Department of Design, Aalto University, Hämeentie 135 C, Helsinki 00760, Finland

^*

Author to whom correspondence should be addressed.

Resources 2014, 3(3), 488-515; https://doi.org/10.3390/resources3030488

Received: 10 August 2013 / Revised: 3 February 2014 / Accepted: 23 June 2014 / Published: 9 July 2014

(This article belongs to the Special Issue How Much Environment Do Humans Need?+20 - Reviewing Progress in Material Intensity Analysis for Transition towards Sustainable Resource Management)

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Abstract

The paper suggests a sustainable material footprint of eight tons, per person, in a year as a resource cap target for household consumption in Finland. This means an 80% (factor 5) reduction from the present Finnish average. The material footprint is used as a synonym to the Total Material Requirement (TMR) calculated for products and activities. The paper suggests how to allocate the sustainable material footprint to different consumption components on the basis of earlier household studies, as well as other studies, on the material intensity of products, services, and infrastructures. It analyzes requirements, opportunities, and challenges for future developments in technology and lifestyle, also taking into account that future lifestyles are supposed to show a high degree of diversity. The targets and approaches are discussed for the consumption components of nutrition, housing, household goods, mobility, leisure activities, and other purposes. The paper states that a sustainable level of natural resource use by households is achievable and it can be roughly allocated to different consumption components in order to illustrate the need for a change in lifestyles. While the absolute material footprint of all the consumption components will have to decrease, the relative share of nutrition, the most basic human need, in the total material footprint is expected to rise, whereas much smaller shares than at present are proposed for housing and especially mobility. For reducing material resource use to the sustainable level suggested, both social innovations, and technological developments are required.

Keywords: consumption; lifestyle; household; natural resources; resource cap; sustainability; transition; material footprint; MIPS; ecological backpack

1. Introduction

An increasing number of consumers, especially in Western societies, can be characterized by a medium or high resource consumption profile. Since these lifestyles are becoming more popular in growing cities worldwide, resource efficiency is an issue of increasing importance on different levels.

The use of natural resources by human activities has been constantly growing during the recent decades. From 1980 to 2008, for example, the extraction and use of many raw materials on a global scale has grown by tens or hundreds of percent. Since 2000, the global resource extraction has risen further and with a stronger growth rate than in the previous decade [1]. The Total Material Consumption (TMC) of between 40 and 50 tons per capita in a year [2] for most industrialized countries is factor four to five higher than the sustainable level suggested by Bringezu [3]. In addition, the “ecological footprint”, i.e., the land area required for human activites either directly or for absorbing the carbon dioxide emitted, has doubled since 1966. It has exceeded the productive land area available already during the 1970s, from 2008 on by more than 50 percent [4]. Other studies focus on the limited environmental space and the effect of exceeding limits on, e.g., biodiversity, climate change, clean water, erosion, soil degradation, migration, social conflicts due to limited acces to resources, etc. [5,6,7,8,9].

The welfare and the consumption of households are the ultimate purpose of basically any economic activities [10]. The amount of household consumption is still growing on a global level [11]. Thus, the way households are living and consuming is a major basic driver of the overconsumption of natural resources by the human technosystem [12,13]. However, this does not mean that households were the only actors that can affect sustainable resource use. In order to decrease the resource use from household consumption, both production and consumption patterns have to be changed, as well as infrastructures and politics that are provided by governments.

The purpose of this paper is to explore the general possibilities of, and the basic prerequisites for, “sustainable lifestyles” [14] in terms of natural resource use. The hypothesis of this paper is that a sustainable level of natural resource use by households is achievable and it can be roughly allocated to different consumption components in order to illustrate the need for change in our lifestyles. The paper is mostly based on data from Finland. Therefore, the assumptions, comparisons, and conclusions especially relate to Finnish households, although they might be similar when studying other Western countries.

On the basis of results from macroeconomic calculations [2,3] we propose an amount of eight tons per person in a year for household consumption and two tons per person in a year for public consumption (e.g., education, health care, public administration). The indicator for describing the resource use by household consumption is the material footprint (see Section 2.3). On the basis of existing research on Finnish households and other research results, promising practices and examples, possible future material footprint levels are reasoned (Section 4). They can, on a more holistic basis than earlier benchmarking approaches (e.g., [15]), provide a benchmarking framework to which the material footprint of products and activities can be compared. However, it is noteworthy to mention that these are only suggestions because user behavior and social practices of households greatlyvary (e.g., [16,17,18]) and technological development in the coming decades can hardly be anticipated [19,20]. Therefore, Section 4 shows only one possible profile of sustainable household consumption. Conclusions concerning the results and the ways to achieve them are given in Section 5.

2. Methodology

This paper is based on several methodological approaches and decisions choosen for developing a reference framework to assess household consumption. It integrates an interdisciplinary and transdisciplinary, transition research oriented view for an action research approach that helps to reflect present resource use. Thus, it is intended to support the creation of new ways of low resources individual lifestyles. It, thus, refers to a variety of approaches of transition and action orientated research, such as [21,22,23,24,25,26]. The material footprint as a method for calculating the natural resource use of households is briefly described in Section 2.1. Section 2.2 describes in which way the system boundaries for households were set. Section 2.3 shows central assumptions for the study and its calculations, as well as how and which kind of existing research results, promising practice examples, and other aspects were utilized for suggesting a framework for sustainable resource use in household consumption.

2.1. Material Footprint and Resource Efficiency Potential Calculations

The term material footprint was established by Lettenmeier et al. [27] as a parallel term for the ecological backpack created by Schmidt-Bleek [28]. The intention was to apply the increasingly popular footprint metaphor for comprehensively illustrating and communicating resource use and material flows. The term material footprint has mostly been used to describe the life-cycle-wide resource use of products, services, activities, and households on micro level (e.g., [27,29]).

The material footprint as used in this paper is calculated by using the MIPS methodology (Material Input Per unit of Service). MIPS values are calculated by summing up the amount of natural material resources required throughout the life cycle in order to provide a specific benefit [27,28,30,31]. The material footprint, as used in this paper, sums up the MIPS categories abiotic and biotic recources, as well as the erosion out of the category soil movement in agriculture and forestry. The resource categories of water and air are not part of the material footprint and are, thus, left out of this study.

The material input contains both the resources used in human economy and the unused extraction (see [32]). This means that any material flows, regardless of their economic utility, are considered.

MIPS values are expressed in mass units per unit of the service provided, for instance in kilograms per kilometer traveled. The concept of service (S) in MIPS is based on the notion that any product is not an end in itself, but it is only produced to fulfill a specific service or need [28]. Thus, even very different products and services can be compared to each other on the basis of the service they provide (e.g., a video conference service and an aeroplane as means for meeting people located far away).

The calculation data used for this paper is mostly the same as in two Finnish research projects on the material footprint of households, “FIN-MIPS Household” [33] and “Basic income MIPS” [29].

The calculation and presentation of the results in Section 4 can be seen as a rough variation of the Resource Efficiency Potential Analysis (REPA) described by Rohn et al. [34]. The REPA analyses the resource efficiency potential of specific or new technologies, products and strategies in comparison to previous or average ones. In this paper, the comparison of the sustainable material footprint level to the existing level for both household consumption as a whole and the different consumption components can be interpreted as REPA on system and subsystem level.

In addition to defining the household as a system, system boundaries are also strongly influenced by the way of calculating the resource use of households. The material footprint, as a micro level approach, is calculated on the basis of the life-cycle material input of all goods and services used by the household (see [27,30]). In terms of natural resource categories, it is equivalent to the term Total Material Requirement (TMR), including abiotic and biotic material resources (including their unused extraction) and erosion in agriculture and forestry, which is the cumulative primary material requirement for the products and services consumed. However, the calculation procedures used here are different from the application of TMR (Total Material Requirement) and TMC (Total, Material Consumption, see [34]) on a macro level. Macro level calculations are usually based on data such as physical input-output tables and consumption expenditure, whereas the TMR (i.e., material footprint), used here, is based on life-cycle material flow calculations of products and activities.

One major difference between applying TMR as micro level material footprint in this paper and its application on most macro level studies concerns the allocation of the material flows of infrastructure like houses, roads, railways, etc. In the material footprint, as used here, the material inputs for the existing infrastructure stock, newly built infrastructure and infrastructure maintenance are allocated to the user of the infrastructure by dividing the life-cycle-wide material input required by the expected useful lifetime of the infrastructure (see [31,35,36]). In macroeconomic material flow accounting (MFA), inputs for constructing the infrastructure are usually allocated to the year they are used. Only the maintenance, use, and renewal of the infrastructure are allocated to the material flows of the years the infrastructure is in use. Thus, in countries with most of their transport infrastructure already built, this leads to considerably smaller values for mobility and transportation in macroeconomic TMR and TMC calculations. In addition, in these maroeconomic calculations, transport infrastructure is often allocated to public consumption so that its material inputs are not allocated to the households. Thus, macroeconomic material flow calculations for consumption (e.g., [2,37,38]) may provide significantly lower mobility-related values than results from micro level calculations like [29,39] or this paper.

2.2. The System Boundaries of Household Consumption

The material resource use by households includes, in principle, any natural material resources required for, first, producing and using materials, products, and services private households consume, for, second, any other activities performed by or covering the needs of households, and for, third, disposing of the related materials and products.

When taking a life-cycle perspective, nearly any human activity can be defined as serving private households at a certain point of time. Thus, basically most of the production and consumption system of an economy can be attributed to private households. However, in this paper we attribute to households only consumption components that households are able to influence and exclude mainly public activities. For example, the resource use caused by public administration, like ministries and authorities or the defense budget, cannot be directly influenced by household consumption despite contributing in fulfilling the human needs of security and participation in society. We also exclude public services, such as health care and education, of which the resource intensity is known only to a small extent and which are also mainly part of public consumption and out of households’ direct influence in Finland. In addition, water supply and waste-water treatment are excluded from the calculations because households influence the material footprint of these public services only to a limited extent. However, the energy required for heating the water is part of the calculations. On the basis of earlier results [39], the consumption components of packaging and waste management were left out because of their low relevance in comparison to the total material footprint of the households.

The household system as studied in this paper is divided into the following consumption components pragmatically defined on the basis of people’s everyday life:

(1): Nutrition, including all the foodstuffs and drinks consumed;
(2): Housing, including the housing infrastructure, as well as the use of energy (electricity and heating) for household purposes;
(3): Household goods, including the 12 product groups used by Kotakorpi et al. [39]: clothes, home textiles, furniture, electric appliances, electronic appliances, paper products, jewellery, dishes, tools, toys and leisure equipment, daily consumer goods, other goods;
(4): Mobility, including the use of cars, bicycles and public transport for both everyday mobility and tourism;
(5): Leisure activities including sport and cultural activities either actively or as a spectator;
(6): Other purposes, including goods or services consumed, e.g., accommodation during holiday trips, but excluding services provided by public systems like health care and education.

2.3. Basic Methodological Procedures and Assumptions

The level of a sustainable material footprint for household consumption in 2050 is reasoned in Section 4.1 on the basis of the sustainable level for the total material consumption (TMC) for European countries proposed by Bringezu [3]. Macroeconomic calculations divide the TMC into private consumption, public consumption, and capital formation (e.g., [2,40]). From the micro level perspective that deals with the whole life cycle or value chain of products, capital formation is part of the life cycle of products and services because infrastructure, for instance, has to be taken into account in MIPS calculations [31]. Therefore, the TMC needs to be distributed only between public and private consumption. On the basis of their relation in present TMC results [2,37,40,41], we roughly break up the sustainable level of TMC into 80 percent for household consumption and 20 percent for public consumption.

While the sustainable level of material footprint for household consumption suggested is based on existing literature, the target level for the different consumption components can differ and allow trade-offs according to individual needs and preferences. For example, someone who is not travelling at all could have a higher material footprint for housing and, thus, “afford” more living space. This serves the establishment of a diversity of possible development paths, as well as strategic acceptance, awareness and responsibility for the desired change with the actors involved (see [17]).

For the basic allocation of the sustainable material footprint level to the different consumption components, the four following aspects have been considered: First, basic needs (nutrition, housing, household equipment) were considered before allocating material footprints to other activities (mobility, leisure activities, other purposes). The basic needs identified are in line with the observations of Lettenmeier et al. [29] on the material footprint of households living on low social standards.

Second, we used results, experiences and conclusions from household level studies [29,39,42] to define a potential future level of material footprint in each consumption component.

Third, results from resource efficiency potential analyses (e.g., [43,44]) and other examples of promising practices were utilized for exploring future possibilities of sustainable consumption patterns. This includes examples of developments or niche solutions already accepted or promoted although still far from mainstream. This part of the research contains also websites and grey literature because only a part of the examples has been described in peer-reviewed scientific literature.

Fourth, as household consumption is an extremely broad topic, it would not have been possible to cover all research done and examples available in this paper. Therefore, the examples used are mainly based on projects, contexts and publications the authors have been involved in. Even with this relatively restrictive approach, plenty of examples became available showing the huge opportunities for developing future sustainable lifestyles and technologies.

For the consideration and calculation of the material footprints of the different consumption components in 2050, the assumption was made that future resource intensities of materials, products and activities will be lower than today. For example travelling 3000 km by bike, bus, tram, metro, or ferry requires approximately 1 ton of material footprint today. For the future, we assumed that improvements in materials, production processes, and capacity use of both infrastructure and vehicles should allow 5000 km of travelling out of 1 ton of material footprint. These material intensity assumptions are basically artificial. Their plausibility was based on a range of studies on existing material intensities and resource efficiency potentials already identified (Appendix). The assumptions used are given in a structured table for each of the consumption components (Table 2, Table 3, Table 4, Table 5, Table 6 and Table 7).

3. Literature Review on the Present and Sustainable Resource Use by Households

3.1. Present Level, Composition and Diversity of Resource Use

The total material footprint of an average Finn is 40 tons per capita in a year [45,46]. This average material footprint was calculated from a micro level approach though utilizing a mixture of statistical and survey data published by different sources from 2005 to 2007. This makes it comparable to the material footprints calculated for specific households described below. Mobility, housing, and nutrition make up 84% of the average Finn’s material footprint (recalculated on the basis of [45,46]). Compared to other studies on the environmental impact of consumption [47,48,49], this is a similar, though even slightly bigger, share of these central consumption components.

Kotakorpi et al. [39] calculated the material footprints of 27 Finnish households from questionnaires and diaries of the actual consumption of these households. With an average material footprint of 39 tons per person in a year, the results show a huge diversity both in level (maximum difference of factor 9, from 13 to 118 tons) and composition of the material footprints. The diversity in both terms continues when disaggregating the different consumption components into subcomponents. Nutrition shows a factor 3 difference in the material footprint levels while the differences in the other consumption components range from factor 11 for household goods to factor 85 for mobility [39] (pp. 44–60).

Lettenmeier et al. [29] report the material footprints of 18 Finnish low-income single households ranging between 7 and 35 tons per person in a year with an average of 18 tons. In general terms, both the absolute levels of and the diversity among the material footprints of the participants were lower than in [39]. With a range from 7.4 to 35.4 tons per person the maximum difference in the footprint level is slightly below factor 5 and all households are below the average Finn’s level. Housing has the greatest share in the material footprints and nutrition is second with most of the households. Housing, nutrition and household goods are the only consumption components with a material footprint higher than zero for each of the 18 participants.

Lettenmeier et al. [50] calculated the material footprint for different decent minimum reference budgets developed by the Finnish National Consumer Research Centre [51]. The material footprints for these reference budgets, i.e., for the minimum living standard Finnish inhabitants should be able to achieve, ranged from 20 to 24 tons per person in a year, depending on the household type [50].

The average annual material footprint of Europeans today is estimated as being between 27 and 40 tons per capita by Groezinger et al. [52]. An average European’s material footprint from 22 to 26 tons per person in a year was reported by Kuittinen et al. [16]. That study calculated the material footprint of 69 individual consumers from mostly European countries on the basis of a web questionnaire (see [16]). The material footprints of the participating individuals ranged from 8.5 to 69 tons per person in a year [16] but exclude some aspects included in the other studies described (e.g., leisure activities and water consumption). Kuittinen et al. [16] stress the importance of the diversity in the households’ lifestyles and their material footprints now and in the future. They show the examples of seven participants in terms of material footprint level and diversity, explaining factors behind them (e.g., “compact home and the life nearby” or “big home and moving around”), as well as potential future development and preferences.

Finnish macroeconomic calculations give values from 14 to 31 tons per person in a year [45,53]. German macro-based values for household consumption are reported from 22 tons per person in a year [2] to 29 tons, respectively [38]. Macroeconomic data tend to show lower values for the resource use of household consumption because of differing system boundaries and allocation procedures, for instance by allocating the material input for building infrastructure in a different way (see Section 2.1).

3.2. Sustainable Future Level of Resource Use

The need for a general dematerialisation in order to decrease global environmental problems has been stated already for several decades [28,54,55,56]. However, unlike the ecological footprint the sustainable boundaries of which are set by the productive land area our planet is providing, the determination of a sustainable material footprint level is complex and not unambigous.

By suggesting, in 1993, that global resource consumption should be halved by the middle of the 21st century and an equal per capita use should be achieved, Schmidt-Bleek [28] claimed a factor of 10 as a necessary, but not sufficient, transformation goal for industrialized countries. Bringezu [3] applied this to the global extraction of abiotic resources, which amounted to about 100–110 billion tons in 2000 (16 to 18 tons per capita). If that amount is reduced by half and then shared equally by nine billion people in 2050, the acceptable level of abiotic resource use would be approximately 5.6–6.1 tons per capita. With the EU per capita consumption of 33.4 tons this requires a reduction by at least 80% or a factor of 5. This is in line with the suggestion of Ekins et al. [57] of six tons of abiotic resources per person in a year. It also includes the aspect of a fair share of resource use within the environmental space provided by the planet as proposed by Spangenberg [5].

For European countries, Bringezu [3] proposes a sustainable level of biotic material use and top soil erosion in agriculture and forestry of four and 0.2–0.3 tons, respectively. Including abiotic resources this means a sustainable TMC of approximately 10 tons per capita in a year.

Since 2000, global resource extraction has risen further and with a stronger growth rate than in the previous decade [1]. The used extraction increased from 2000 to 2008 by 27 percent to 68 billion tons (abiotic and biotic). Business as usual would cause a further increase globally [58,59]. Thus, from the perspective of recent development, a return to the global resource use in 2000 would be progress already [60]. Bringezu therefore revised his original proposal [3] and proposed a global abiotic TMC of 11–12 tons per capita per year in order to not exceed the resource use level of the year 2000 while, for the EU, with most of its housing and mobility infrastructure already built, he considers plausible a level of 10 tons, respectively [60]. However, the considerations behind this are rather related to political target-setting than to new scientific findings on the planetary boundaries. Therefore, we still use Bringezu’s [3] original target of 10 tons of TMC in total as the starting point for this paper. The distribution of these 10 tons into household consumption and public consumption for this study is explained in Section 2.3.

4. Results and Discussion

This section first gives a suggestion on the sustainable level of material footprint for household consumption and one example on how to allocate it to the different consumption components. In Section 4.2, Section 4.3, Section 4.4, Section 4.5, Section 4.6 and Section 4.7 the values suggested for each consumption component are explained and reasoned on the basis of already existing technologies, solutions, concepts, and other developments.

4.1. A Sustainable Lifestyle of Eight Tons Material Footprint

On the basis of Section 2.3, we propose a share of eight tons per person in a year for household consumption and two tons for public consumption, respectively. In order to make this amount of resource use operationable, it has to be allocated to the different consumption components. In the case of real households this aggregation depends on the specific needs, wants, lifestyles, situation, location, etc. of a household. Table 1 gives a summary on the material footprint recently reported for Finnish households (on the basis of [45] and [46] which used statistical data published from 2005 to 2007), the suggestion for a future material footprint, and the reduction required in the different consumption components. The order of the different consumption components proceeds from most basic needs to less basic needs, as explained in Section 2.3.

Table 1. Summary of status quo material footprints and proposal for sustainable material footprint requirements in the different consumption components.

**Table 1.** Summary of status quo material footprints and proposal for sustainable material footprint requirements in the different consumption components.
Consumption component	Status quo material footprint		Sustainable material footprint		Change required
Consumption component	kg/(person·a)	Share	kg/(person·a)	Share	%	Factor
Nutrition	5,900	15%	3,000	38%	–49%	2.0
Housing	10,800	27%	1,600	20%	–85%	6.8
Household goods	3,000	7%	500	6%	–83%	6.0
Mobility	17,300	43%	2,000	25%	–88%	8.7
Leisure activities	2,000	5%	500	6%	–75%	4.0
Other purposes	1,400	3%	400	5%	–71%	3.5
Total	40,400	100%	8,000	100%	–80%	5.1

Section 4.2, Section 4.3, Section 4.4, Section 4.5, Section 4.6 and Section 4.7 provide the central facts, assumptions and features on the material footprint level for each consumption component in a structured table and in text. Central assumptions and other relevant information are given in the text before each table. The tables contain the following issues. The resource use reduction required is given in absolute (tons) and relative (factor X) terms. The amount of direct consumption, the material intensity and the share in households’ total material footprint is listed for the recently reported consumption of an average Finn and the proposed future average. Multiplying the present direct consumption amount with the present or future material intensity factor results in the present or future material footprint level for each consumption component. This is followed by a core statement on ways and strategies for achieving the future material footprint.

More detailed examples, arguments and promising practices for the different consumption component is given in Tables A1–A6. These are provided from both a consumption and a production point of view as results reasoning that the material intensity and the amount of service proposed can be seen plausible.

We have to emphasize that the material footprint reduction requirements presented are suggestions on an average basis. However, different households and individuals have very diverse needs, wants, locations, and other circumstances affecting their present material footprints. Therefore, their future material footprint distribution can also vary considerably [16]. As long as the average future material footprints of households do not exceed eight tons per person in a year, the individual footprints can highly differ from each other.

4.2. Nutrition

The average material footprint for nutrition requires a reduction by half from present (see Table 2). The level suggested here is based on a highly but not totally vegetarian nutrition, a slightly smaller amount of foodstuffs (600 kg/(person·a)) consumed compared to today, and efficiency gains in the food chain, e.g., by reducing waste. Table A1 shows arguments for determining a sustainable material footprint for nutrition at three tons per person in a year. This value includes both food and drinks.

A reduction by a factor of 2 is a smaller reduction than with the other consumption components. Thus, the share of nutrition in the total material footprint will considerably increase in the future while the shares of the other consumption components either decrease or just slightly increase (see Table 1). This is because nutrition can be considered the most basic need represented in the consumption components.

Table 2. Sustainable material footprint proposal for nutrition.

**Table 2.** Sustainable material footprint proposal for nutrition.
Nutrition—from 5.9 to 3 tons/(person·a)
Reduction required by	Factor 2		Direct consumption amount	Present	840 kg (including drinks) [45]
Reduction required by	Factor 2		Direct consumption amount	Future	600 kg (including drinks)
Share in household’s material footprint	Present	15%	Material intensity	Present	7 kg/kg (including drinks) [45]
Share in household’s material footprint	Future	38%	Material intensity	Future	5 kg/kg (including drinks)
Core statement	The material footprint for nutrition can be reduced from 5.9 to 3 tons/(person·a): - by reducing the amount of food and drinks consumed to a healthy and still enjoyable level; - by developing acceptable and delicious diets e.g., towards notably less meat and dairy products; - and by increasing the resource efficiency in the food chain e.g., through waste prevention.

4.3. Housing

Housing is another very basic need. The suggested 85 percent reduction in the material footprint of housing is based on a decrease in living space per person by nearly half to an average of 20 m² per person while the energy and resource efficiency of houses would increase drastically. In addition a decrease in electricity use to 1000 kWh per person in a year and a notable increase in the resource efficiency of the electricity produced will be necessary and can be expected.

Table 3 shows the consequences of and Table A2 arguments for suggesting a sustainable material footprint for housing at 1.6 tons per person in a year. This value includes both the building and the energy used in the building.

Table 3. Sustainable material footprint proposal for housing.

**Table 3.** Sustainable material footprint proposal for housing.
Housing—from 10.8 to 1.6 tons/(person·a)
Reduction required by	Factor 6.8		Direct consumption amount	Present	38 m²/capital (house) [45] 11500 kWh (heat and electricity) [45]
Reduction required by	Factor 6.8		Direct consumption amount	Future	20 m²/capital (zero energy house) 1000 kWh (electricity)
Share in household’s material footprint	Present	27%	Material intensity	Present	65 kg/ m²/a (house, unheated/uncooled) [39] 0.6 kg/kWh (Finnish heat and electricity) [39]
Share in household’s material footprint	Future	20%	Material intensity	Future	65 kg/ m²/a (house, heated/cooled) 0.3 kg/kWh (European electricity)
Core statement	The material footprint for housing can be reduced from 10.8 to 1.6 tons/(person·a): - by developing zero-energy houses not exceeding present houses’ material intensity (i.e., strongly combining energy and resource efficiency); - by drastically shifting electricity production from fossils to renewables, especially wind an solar energy; and - by decreasing individual living space. The impacts of the latter on the individual wellbeing can be reduced by increasing shared living space and improving public space more liveable and attractive.

The material footprint proposed requires a huge change in building infrastructure as most houses are far from a zero energy standard at present. Presently existing buildings that will still be in use by 2050 cannot necessarily be assumed to be zero energy houses then. This means that the additional material inputs required for heating those houses in the future have to be compensated, e.g., by increasing the benefit provided by them or decreasing their material input in a way or another. For example, longevity and renewable energy can open additional options for reducing the material intensity of existing buildings. On the other hand, increasing urbanization is still going in Finland. This provides opportunities for establishing a much more energy and resource efficient stock than previously if resource efficiency is developed and taken into account in new buildings and quarters. In addition, increasing urbanization can help to achieve the mobility proposals given in Section 4.5.

4.4. Household Goods

A part of the household goods we are using can be considered as basic need. However, as the amount of household goods used on average today certainly exceeds the most basic needs, a reduction of 83 percent is suggested for the material footprint of producing the goods households use (Table 4). This should be achieved by a decrease in ownership as well as an increase in longevity, reuse, second-hand use, sharing, and other options. Table A3 shows arguments for this proposal.

Table 4. Sustainable material footprint proposal for household goods production.

**Table 4.** Sustainable material footprint proposal for household goods production.
Household goods production (cradle to retail)—from 3 to 0.5 tons/(person·a)
Reduction required by	Factor 6	Direct consumption amount	Present	1943 items/household (avg), out of which 568 second hand or similar [39]
Reduction required by	Factor 6	Direct consumption amount	Future	less own items
Share in household’s material footprint	Present 7%	Material intensity	Present	200 kg/(person·a) as an average for the 12 product groups, with a range from 15 to 420 kg/(person·a) per one product group and with only 3 product groups below 170 kg/(person·a) [39]
Share in household’s material footprint	Future 6%	Material intensity	Future	42 kg/(person·a) on average for each of the 12 product groups
Core statement	The material footprint for household goods can be reduced from 3 to 0.5 tons/(person·a) by increasing longevity, decreasing ownership of equipment, increasing sharing options, improving reuse and second hand schemes, etc.

Recycling and reuse (e.g., second hand products or reuse of components in appliances) usually cause particularily low material footprints because in the MIPS concept the material input is allocated to the original material or product produced. For additional using times afterwards only the material input for reintegrating the material or product into the market (e.g., sorting plants, washing, transportation) is calculated [31].

This section covers the material footprint for the production of the 12 product groups used by Kotakorpi et al. [39] with a life cycle “from cradle to retail”. The resource use during the use phase of the products is covered by Section 4.3. Because all electricity and energy used at homes is allocated to the consumption component of housing, and households usually receive only one electricity bill for all the power consumed at home (see also [59]). Furthermore, the transportation of goods from retail to home is included in the mobility figures.

4.5. Mobility

Mobility has a strong influence on the present average material footprint (Table 1). The diversity of different activity profiles concerning mobility is huge [16] (pp. 24–41), [29] (pp. 1436–1438) and [39] (pp. 48–49).

The greatest average reduction (88%, i.e., close to a factor of 9) we suggest is for this consumption component. It can be achieved by reducing private car traffic to a fraction of present levels. In addition a reduction of overall mobility performance to 10,000 km per person in a year is required while simultaneously increasing the resource efficiency of public transport from present.

Table 5 shows the central consequences and Table A4 the arguments for determining a sustainable material footprint for mobility at 2 tons per person in a year. This value includes both everyday mobility (e.g., trips to work, shopping and leisure activities) and tourism-related transportation (but excludes trips that are done on behalf of the employer). This means that also the composition of a sustainable material footprint for mobility can differ according to a person’s individual needs and interests. Table 5 shows a range of values for present mobility in the case of aeroplanes, trains, and other transport subsystems because the huge differences in both material intensity and function between, for instance, local and long-distance trains or domestic and intercontinental flights are too big to be covered by one single average value.

Table 5. Sustainable material footprint proposal for mobility.

**Table 5.** Sustainable material footprint proposal for mobility.
Mobility—from 17.3 to 2 tons/(person·a)
Reduction required by	Factor 8.7		Direct consumption amount	Present	17,500 km
Reduction required by	Factor 8.7		Direct consumption amount	Future	10,000 km
Share in household’s material footprint	Present	43%	Material intensity	Present [61]	1.44 kg/person-km* (private car) 0.53–1.2 kg/person-km (train) 0.06–0.56 kg/person-km (plane) 0.26–0.38 kg/person-km (bus, coach, tram, metro, ferry, bike)
Share in household’s material footprint	Future	25%	Material intensity	Future	0.2 kg/person-km
Core statement	The material footprint for mobility can be reduced from 17.3 to 2 tons/(person·a): - by making public transport and biking still more resource-efficient; - by reducing the role of private cars dramatically; - by limiting the amount of kilometres travelled to 10,000 km/(person·a); - by changing travel requirements for work and leisure, e.g., by a higher attractiveness of the living environment as well as the change of production and communication structures that allow a reduction in mobility and transports; - by the integrative management of mobility and ICT options.

Note: * kg/person-km: material input in kg per person transported one kilometre.

4.6. Leisure Activities

Leisure activities are important because they provide recreation and health to people who are often doing one-sided work. The material footprint for leisure activities is suggested to be reduced from present by 75 percent. This should be possible by reducing especially resource-intensive activities and products, by keeping the amount of activities and products on a sufficient level and by increasing the resource efficiency of the activities or products.

Table 6 shows the central consequences and Table A5 the arguments for determining a sustainable material footprint for leisure activities at 0.5 tons per person in a year. This value focuses basically on activities out of the home because activities within homes are covered by the consumption components of household goods and housing. The material footprints reported for basic leisure activities at home have been relatively low, for example 1 kg/h for watching TV or 2 kg per shelf centimeter of books [39]. However, if leisure activities at home could also be allocated to this consumption component if they require a huge amount of additional resources, e.g., for equipment.

Table 6 shows a range of values for common leisure activities. They appear to follow a rough pattern according to which they can be divided into

(1): low-infrastructure activities with low material footprints, such as jogging;
(2): group or mass activities with an apparent need for infrastructure, such as using a swimming hall or fitness club, thus requiring a higher amount of resources; and
(3): highly individual and/or infrastructure-intensive activities showing also the highest material footprints, such as golf or sailing.

Table 6. Sustainable material footprint proposal for leisure activities.

**Table 6.** Sustainable material footprint proposal for leisure activities.
Leisure Activities—from 2 to 0.5 tons/(person·a)
Reduction required by	Factor 4		Direct consumption amount	Present	3.5 h of physical exercise or other leisure activities outside the home [45]
Reduction required by	Factor 4		Direct consumption amount	Future	3 h but strongly dependent on the material intensity of the activity
Share in household’s material footprint	Present	5%	Material intensity	Present [39]	1 kg/h for low-infrastructure outdoor activities; 5–15 kg/h for activities requiring infra-structure like buildings, harbours, slopes; ≥30 kg/h for resource-intensive individu-al activities like sailing, golf, motor sport
Share in household’s material footprint	Future	6%	Material intensity	Future	1–6 kg/h (e.g., 2 × 50 h/a × 1 kg/h + 1 × 50 h/a × 6 kg/h)
Core statement	The material footprint for leisure can be reduced from 2 to 0.5 tons/(person·a): - by rather decreasing than increasing leisure activities that are highly material intensive and/or require built and heated infrastructure; - by utilizing outdoor options requiring few resources (walking, jogging, canoeing, gardening, …); - by using infrastructure more efficiently (e.g., schools in the evening); and - by making leisure activities more resource efficient (e.g., longevity of venues, resource efficient use of energy).

The latter of these will have the greatest needs for decreases in material intensity, improved resource management, and/or trade-offs with other consumption components in the future, depending on the needs and interests of individuals and households.

4.7. Resource Use for Other Purposes

As this concumption component, in principle, covers anything not covered by the previous ones no direct consumption amount nor material intensity has been specified in Table 7. In addition the reduction required in reality is probably higher than proposed because, for example, the consumption of many services is not yet included in the calculations so far (see Section 2.1 for details). Other purposes could include, e.g., services or accommodation during holiday trips (see also Table A6).

Table 7. Sustainable material footprint proposal for other purposes.

**Table 7.** Sustainable material footprint proposal for other purposes.
Other purposes—from 1.4 to 0.4 tons/(person·a)
Reduction required by	Factor 3.5		Direct consumption amount	not specified
Share in household’s material footprint	Present	3%	Material intensity	not specified
Share in household’s material footprint	Future	5%	Material intensity	not specified
Core statement	The material footprint for other purposes should be reduced from 1.4 to 0.4 tons/(person·a) in order to keep the material footprint of household consumption within the limits of 8 tons/(person·a).

5. Conclusions

This paper provides a basic reference framework for achieving sustainable household consumption by 2050. In general, a sustainable household consumption in 2050 seems achievable on the basis of the mostly Finland-related proposals of the paper (Section 4). However, the targets proposed (see Table 1, Table 2, Table 3, Table 4, Table 5, Table 6 and Table 7) show that there is a long way to go and a lot of efforts required (see also Appendix, Table A1–A6). The findings of this study can help to show the way towards sustainable household consumption and are intended to contribute to a positive vision for the enormous transformation task we are facing.

For the suggested average factor 5 of reduction in material footprint (see Table 1), a factor 2 to 3 improvement appears necessary in terms of both production-based and consumption-based solutions (see Appendix, Table A1–A6 for examples). By developing four different scenarios for achieving sustainable lifestyles by 2050, Leppänen et al. [62] have shown that the transition to sustainable lifestyles can have very different faces. They defined some common features of the different scenarios that can be confirmed by the results in Section 4. These aspects are:

-: A reduced consumption of meat and other animal-based foodstuffs;
-: A radical reduction of the heating and cooling energy demand of houses;
-: A strongly dematerialized, fossile-free electricity production, and a lower level of mobility including a drastically decreased use of private cars.

The more technology and infrastructure can be integrated into this change, the more space will be left for individual diversity in achieving sustainable household consumption. However, even with advanced developments in technology and infrastructure the role of basic needs, especially nutrition, and their satisfaction is likely to increase strongly in the future (see Table 1).

Households have space for even immediate decisions decreasing the material footprint. In the fields of nutrition, electricity procurement and tourism, for instance, sustainable decisions can be made any time so that even fast changes could be envisaged in these areas. Although households are, in principle, free to make decisions on their consumption, some decisions are highly complex and can be locked into existing infrastructures (see [16,39,63,64]). For instance, housing-related decisions are done rarely compared to e.g., nutrition choices and the location of housing affects many further decisions, e.g., the mobility options available. Therefore, incentives should be set to facilitate change in public planning and decisions, for example on infrastructure.

Infrastructure affects resource use in the long run and determines lifestyles in many respects. Therefore, including the aspect of facilitating sustainable, low-resource lifestyles in public decision-making provides an opportunity for avoiding misinvestments and creating synergies from options simultaneously decreasing the resource use of several consumption components. For example, promoting car-free lifestyles in city planning can reduce car use and the need for public and private infrastructure like streets and parking space. Thus, it can decrease the material intensity of both mobility and housing. Attractive car-free quarters can reduce the highly relevant (see [65,66]) need for leisure time trips and could possibly also reduce the need for private living space. Without a car, closely situated shops and other facilities are more attractive than distant ones [67]. In addition, the health effects of decreasing car use are evident [68]. Increasing walking and cycling could, thus, also decrease the resource use required for leisure activities and for health care.

The framework given by this paper could also help preventing rebound effects of changing consumption patterns. For example, information and communication technology (ICT) has a considerable potential for decreasing mobility needs. Therefore, trade-offs between mobility, household goods and housing (electric power) should be considered. ICT can, for instance, facilitate car-sharing and public transport and monitor, control and reduce the need for lighting and heating at home. However, a challenge of ICT use is the increased need for copper and other resource-intensive materials and equipment (e.g., [69]). The material footprint of digital banking, for instance, has been reported to be still 40% in comparison to traditional banking (approximately 1.1 and 2.8 kg/happening, repsectively) because also digital banking requires bank infrastructure, electric power, computers, etc. [70]. In addition, Rohn et al. [71] have pointed out the need for a careful resource management in the ICT sector in order to avoid rebound effects.

Another example that can either increase or decrease resource use is collaborative consumption. Collaborative consumption is a rising trend with dematerialisation potentials in different consumption components [72]. However, if sharing consumer goods largely increases, rebound effects should actively be avoided in terms of both the overall amount of different products in use and their potential overall energy consumption and especially the potentially increasing car use for providing and acquiring products and services. This is one area further research should focus on.

Additionally, the following suggestions for further research could help to facilitate the transition challenge we are facing.

Investments in production and infrastructures highly influence what and how people consume. Therefore, it would be highly relevant to study how to use both public and private financial resources in the best way for decreasing material footprints while maintaining a high quality of life. To which extent affluent households could facilitate dematerialisation by using or allocating their financial resources in an optimal way and how can public earning (e.g., taxes) and spending (e.g., research and development funding) best facilitate dematerialisation instead of increasing resource use? For example, investments in energy and resource efficient buildings are urgent in order to achieve the targets proposed in Section 4.3.

There is a high demand for further research in order to make concrete and to mainstream the dematerialisation options sketched in Section 4 and Appendix. For example, resource-efficient zero-energy construction and low-energy retrofitting still require lots of questions to be solved. Both urban structures and mobility systems that reduce car dependency have been developed only to a small extent, so far.

An enlargement of the database to other countries than Finland and to other continents would help to address and compare household consumption on a broader basis. We also excluded public services the resource intensity of which is known only to a small extent although their contribution to resource use is highly relevant. Examples for this kind of services are health care and education.

This paper provides a first framework for developing household consumption towards a sustainable material footprint. Hopefully it can inspire also other researchers and practitioners to make sustainable lifestyles more attractive and concrete and to develop political and business solutions facilitating sustainable lifestyles.

Acknowledgments

The authors would like to thank Jana Meier, Lena Brüch, Sini Veuro and Satu Lähteenoja for their valuable assistance during the preparation and editing of the paper. We thank Tuuli Hirvilammi, Senja Laakso, Satu Lähteenoja, Aleksi Neuvonen, Michael Ritthoff, Fritz Hinterberger, Christine Ax and Stefan Giljum for the fruitful discussions during the development of the idea of this “8 tonnes framework”. Special thanks also to the SPREAD team of Politecnico di Milano for organizing a workshop inspring to develop the “8 tonnes concept” for sustainable lifestyles.

This paper was prepared with financial support of the project “Socio-economic practices of sustainable development in the new industrialization”. The project is founded by the Government of the Russian Federation, Grant 074-U01 and conducted within the ITMO University.

Appendix

Table A1. Promising examples and practices supporting the sustainable material footprint proposal for nutrition in detail.

**Table A1.** Promising examples and practices supporting the sustainable material footprint proposal for nutrition in detail.
Nutrition—from 5.9 to 3 tons/(person·a)
Central consumption-related arguments, examples, promising practices	- 6 out of 27 Finnish households studied already achieve 3200 kg or less [39]; - 4 out of 18 low-income single households already achieve 3200 kg or less, with one vegan participant at 2200 kg [29]; - Indian average diet (2007) at 2500 kg, “Livewell UK 2020” at 3700 kg [73]; - Present differences in the direct consumption of selected foodstuffs (including most relevant foodstuffs, excluding drinks) in European countries [42]: amount from below 500 and over 700 kg/(person·a), For Finland the present amount consumed according is 540 kg/(person·a) and the present material intensity 8.2 kg/kg (both excluding drinks) [42]; - Vegan and vegetarian lifestyles presently becoming trendy in Western countries, which opens people options for less resource-intensive diets; - Catering establisments have huge opportunities for developing and spreading low resource diets, and thus for initiating behavioral change. So far, these opportunities are used rarely. Their potentials have not been sufficiently analyzed so far but single examples show that relevant new practices can be developed on the basis of user- and actor-integrated experiments (e.g., [74] (pp. 6–9)).
Central production-related arguments, examples, promising practices	- Huge differences presently in the material intensity of selected (most relevant ones included, drinks excluded) foodstuffs in selected European countries: from 8.4 to 11.4 kg/kg, several European countries already below 9 kg/kg [42]; - Cereals and bread, milk, eggs, domestic fruits, outdoor vegetables, soya, wild fish can already today be below 6 kg/kg [27,39,42]; - Material footprints of typical lunch meals, for instance, vary between 1.7 and 6.8 kg/meal [75] and material intensities by factors of 5 and more [39]; - The reduction of the high amount of food waste in Western countries at present offers opportunities for decreasing food consumption and material intensities. German food waste amount (value chain, incl. production, distribution and consumption) estimated at 146 kg/(person·a) and its material footprint at 1185 kg/(person·a) [76]; - Also food production technologies can still be developed less resource-intensive (e.g., [44] (pp.52–53)). - Agricultural production and practices can be developed more resource efficient (e.g., [44] (pp. 30–31,109–111)). So far, factors like animal welfare, erosion, soil quality, irrigation, soil movement, etc. have usually rather been optimized in terms of cost efficiency than resource efficiency. Niche solutions and concepts like permaculture show that huge potential from different production practices exists (e.g., [77,78]). - Legal requirements and industrial standards concerning the appearance and shape of the products cause unnecessary resource use in the production chain of food [79].

Table A2. Promising examples and practices supporting the sustainable material footprint proposal for housing in detail.

**Table A2.** Promising examples and practices supporting the sustainable material footprint proposal for housing in detail.
Housing—from 10.8 to 1.6 tons/(person·a)
Central consumption-related arguments, examples, promising practices	- 8 of 27 households already achieve 1500 kg or less for the building (excluding heating). 14 of 27 households already achieve 300 kg or less for electricity consumption [39]; - 20 m² of living space is 55% of present European average but also today reality for students and other groups; - Shared space use is an option for increasing individual living space. Co-housing is seen as a promosing practice emerging in the context of sustainable living [80]; - A study on residents’ heating behavior using data loggers in different apartments of multifamily residences found out that the heating energy consumption of flats with the same floor plan differed by 110% [81]. Thus, the user behavior has a notable effect on heating energy consumption.
Central production-related arguments, examples, promising practices	- European law requires that all new buildings shall be nearly zero-energy consumption buildings by the end of 2020 [82]. To provide this energy efficiency level with present material intensities will require innovations in construction materials but some interesting solutions are on the market already; - In Austria several innovative house concepts have been developed [44] (pp. 56–57) and [83,84]. These houses reduce the life-cycle impacts of houses by up to 90% (factor 10). Innovative building materials can be used, e.g., wood, straw and clay; - An insulation material innovation with a material intensity cut by half shows that additional insulation can be done resource-efficient [43] (pp. 54–60). - The production of heavy bulk materials like gravel and cement has huge resource efficiency potentials. Innovaitons are currently developed, see e.g., [44] (pp. 38–39, 66–67). - 0.3 kg/kWh of electricity is appr. 50% of the present Finnish but only 10% of German power’s material intensity [85,86]. However, power production technologies with low material intensity are already in use or under development: wind power (0.09–0.16 kg/kWh [86]), Desertec power (0.12–0.22 kg/kWh [87]) and photovoltaic (0.2 kg/kWh, [43] (pp. 84–90)). New developments in wind power, for instance, may still be even more productive than present solutions (e.g., [44] (pp. 26–27)). The resource use of wave power has not been assessed yet but this could provide another low resource technology for power production (e.g., [44] (pp. 40–41)). - The energy efficiency of many household goods has increased considerably in the recent years so that reducing power consumption by half by 2050 appears achievable. E.g., washing and lighting are expected to develop considerably towards low resource use (e.g., [43] (pp. 44–45, 58–59) and [88] (pp. 162–166). There is a potential rebound effect of using more devices more often thus jeopardizing energy efficiency gains. With a need for decreasing living space and decreasing material footprints for household goods (see Section 4.4) an actual reduction in power consumption still appears achievable.

Table A3. Promising examples and practices supporting sustainable material footprint proposal for household goods production.

**Table A3.** Promising examples and practices supporting sustainable material footprint proposal for household goods production.
Household goods production (cradle to retail)—from 3 to 0.5 tons/(person·a)
Central consumption-related arguments, examples, promising practices	- 500 kg/(person·a) of material footprint is close to the very lowest end of the 27 Finnish households ranging between 560 and 5.900 kg/(person·a) [39]. Thus, 500 kg means a considerable decrease compared to today; - 3 out of 18 Finnish low-income single households already achieve below 750 kg [29]. Generally, the low-income households in this study tend to have smaller material footprints than the households studied by [39]. This is at least partly due to second hand purchases and an intensive use of public sharing services like libraries; - A reduced living space per person (see Section 4.3) decreases the space and the need for household goods to a certain extent (e.g., [39] (p. 68)); - Among consumers swapping and sharing schemes as well as collaborative co nsumption are rising trends (e.g., [80]) with clear advantages in terms of resource use (e.g., [89]). They thus can decrease the need for the production of new goods notably if rebound effects are avoided.
Central production-related arguments, examples, promising practices	- Longevity and modularity for repair/reuse of products can decrease the material input per year of product use notably (e.g., [88,90] for furniture, shoes and jewelry). The availablility of repair and reuse services is a central factor in order to facilitate a long life of products. Mobile repair services can help to make repair services accessible while preventing consumers from having to drive long distances (e.g., [44] (pp. 60–61)). - If a product requires energy during its use face, a long lifetime might increase total resource use. However, with low material footprints for energy (as proposed in Section 4.3), longevity remains a resource-efficient option (e.g., [88,91]). - Increasing the share of recycled materials and/or reused components in products is another option decreasing the material footprint. Especially recycled metals have considerably lower material intensities (see [88] (pp. 58–61) and [92]). This can be an increasingly important option for electronic products as the availability of several raw-materials of theses products is predicted to decrease during the coming decades (e.g., [93,94]). Also durable jewelry has a huge reuse and recycling potential [88] (pp. 58–91). - Numerous examples show that product design, standardization and other measures can decrease both the amount of products in use and their material intensity (e.g., [44] (pp. 44–45, 50–51)).

Table A4. Promising examples and practices supporting sustainable material footprint proposal for mobility.

**Table A4.** Promising examples and practices supporting sustainable material footprint proposal for mobility.
Mobility—from 17.3 to 2 tons/(person·a)
Central consumption-related arguments, examples, promising practices	- 2 out of 27 Finnish households achieve 2500 kg or less [39]; - 13 of 18 participants already achieve 2000 kg or less for daily mobility and 14 participants 1500 kg or less for tourism (most of which relates to mobility) [29]; - The distance of 10,000 km can mean 40 km on 250 days of the year, for instance. However, with lower daily mobility also longer trips are still possible. A holiday trip of 10,000 km one-way for example would be possible if daily mobility didn’t exceed 10,000 km in 3 years. - Car-free households studied in Vienna use public transport while reference households use a car as basic means of transport. Yet, the total distances travelled and the flights made by car-free households are only slightly higher than in the reference group [95]; - Car-sharing can reduce the need of owning and using private cars by providing a possibility of car use when it’s especially necessary.
Central production-related arguments, examples, promising practices	- Bus transport in finnish cities already achieves an average material intensity of only 0.1 kg/person-km *, bike traffic in Helsinki 0.2 kg, respectively [96]; - Private cars in their present use and amount can hardly be seen as a broad solution to achieve a sustainable material footprint for mobility. Even wind-power-based electric drive decreases the material footprint only slightly when infrastructure is not even considered [43]. - Longhaul flights are presently well below, long European flights and ferry trips close to 0.2 kg/person-km in material intensity (0.06, 0.11 and 0.26 kg/person-km, respectively [61]). Thus, this kind of travelling would basically be possible in the future also but probably to a much smaller extent than flight-intensive lifestyles are presently consuming. Compared to the material footprint and other means of transport, the air consumption and carbon footprints of flights are relatively high. Thus, there may occur further future needs to restrict flights because of their climate impacts although peak oil is expected to reduce flying dramatically long before 2050 [97]; - Development of low resource services concerning the social interaction needs of individuals and social groups as well as basic procurement like shopping. These services should be developed on the basis of low resource infrastructure because presently infrastructure requires a huge share of mobility material footprints [61].

Note: * kg/person-km: material input in kg per person transported one kilometre.

Table A5. Promising examples and practices supporting sustainable material footprint proposal for leisure activities.

**Table A5.** Promising examples and practices supporting sustainable material footprint proposal for leisure activities.
Leisure activities—from 2 to 0.5 tons/(person·a)
Central consumption-related arguments, examples, promising practices	- 2 out of 27 Finnish households achieve less than 800 kg [39]; - 13 out of 18 low-income single households already achieve 500 kg or less but this is often due to financial constraints [29]; - 6 kg/h is already achieved by activites in e.g., music schools, fitness centres or sports halls, 1 kg/kg with e.g., jogging or rowing [39]; - Presently resource-intensive activities like golf or going to a theatre (see [39]) could be done only sometimes per year; - Activities at home can be excluded from here if they fit into the consumption components of housing (e.g., electricity use, see Section 4.3) and household goods (see Section 4.4).
Central production-related arguments, examples, promising practices	- Increase in resource efficiency of activities expectable by 2050 e.g., by more efficient use of infrastructure and by more resource-efficient energy use (electricity and heat, similar to the requirements and achievements in housing, see Section 4.3). Sensitivity analyses of leisure-related MIPS studies show that the longevity, the energy use and the capacity use of leisure infrastructure are important factors affecting and being able to decrease material footprints [65,66]. - The location and accessibility of venues greatly affects mobility needs. Presently often half or more of the material footprint of events or training sessions is affected by transporting participants and/or spectators to the venue [39] (pp. 65–66, 69); [88] (pp. 99–107) and [90]. Although mobility is covered by Section 4.5, this is an important aspect when planning leisure facilities. - The other parameter greatly influencing the material footprint of leasure activities is the venue [65,66] and [88] (pp. 99–107). Therefore, in order to achieve lower material footprints, the capacity of venues should be used as efficiently as possible, also for other purposes than the original one (see e.g., [66] for additional events in theatres). Also the use of schools etc. for evening or weekend events can decrease material footprints especially when it decreases the need for building additional facilities.

Table A6. Promising examples and practices supporting sustainable material footprint proposal for other purposes.

**Table A6.** Promising examples and practices supporting sustainable material footprint proposal for other purposes.
Other purposes—from 1.4 to 0.4 tons/(person·a)
Central consumption-related arguments, examples, promising practices	- The content of this consumption component can be highly different depending on the specific household. In the calculations for the average Finn the 1400 kg used here is related to accommodation on holiday trips, e.g., in hotels or cottages. However, it could contain something totally different, like going to events, purchasing medicine, having pets, or just consuming more in other consumption components (Section 4.2, Section 4.3, Section 4.4, Section 4.5 and Section 4.6). Therefore, consumption-related ways for reducing material footprints can be based on similar strategies as before, e.g., using less, sharing goods with other consumers, using instead of owning, using infrastructure already existing, using less material-intensive materials, products or energy modes, etc.
Central production-related arguments, examples, promising practices	- Accommodation in hotels or cottages can be developed less resource-intensive e.g., by decreasing the amount of space required, by reducing the level of equipment, or by increasing capacity use [98]. New collaborative consumption schemes like airbnb can even reduce the need for additional hotels and second homes by making the use of existing homes and second homes more efficient; - As “other purposes” can contain any products or activities, production-related ways for reducing material footprints can be based on similar strategies as in the examples mentioned before, e.g., applying less resource-intensitve materials, products or energy modes, designing goods and infrastructures for multi-purpose use and longevity, utilizing reused components and recycled materials in production, etc.

Conflicts of Interest

The authors declare no conflict of interest.

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Eight Tons of Material Footprint—Suggestion for a Resource Cap for Household Consumption in Finland

Abstract

1. Introduction

2. Methodology

2.1. Material Footprint and Resource Efficiency Potential Calculations

2.2. The System Boundaries of Household Consumption

2.3. Basic Methodological Procedures and Assumptions

3. Literature Review on the Present and Sustainable Resource Use by Households

3.1. Present Level, Composition and Diversity of Resource Use

3.2. Sustainable Future Level of Resource Use

4. Results and Discussion

4.1. A Sustainable Lifestyle of Eight Tons Material Footprint

4.2. Nutrition

4.3. Housing

4.4. Household Goods

4.5. Mobility

4.6. Leisure Activities

4.7. Resource Use for Other Purposes

5. Conclusions

Acknowledgments

Appendix

Conflicts of Interest

References

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