Absolute & Relative Scarcity
Absolute & Relative Scarcity
Absolute & Relative Scarcity
Abstract
Thomas Robert Malthus (1766 – 1834) introduced the notion of absolute scarcity of nature into classic economic thought. He maintained that a population grows faster than the food required to sustain the population, and that will eventually lead to a decline in the population.
In contrast, Mainstream Economics focuses on relative scarcity which defines a good as scarce in relation to other scarce goods. A scarce good carries opportunity costs, which in turn results in a positive price. Goods with no price are not scarce. However, many pollutants have no price, therefore they are not dealt with. In contrast, Ecological Economics focuses its analysis on the damage caused by these pollutants.
We show why the concept of relative scarcity is too narrow to secure the natural basis of life. For example, ground water is irreversibly lost, and climate change causes draught and flooding. In contrast, Ecological Economics is very much aware of the absolute scarcity of natural goods: A good which cannot be substituted with another is absolutely scarce Ecological Economics focuses its analysis on non-priced goods.
This concept is necessary to recognise that many services provided by the environment become absolutely scarce in the long run, therefore we must take precautionary measures now.
To illustrate our critique, we examine the concept of relative scarcity in the context of the present loss of biodiversity.
Key Contributers: Stefan Baumgärtner – Christian Becker – Kirsten Hertel – Reiner Manstetten
Related concepts: HOMO OECONOMICUS & HOMO POLITICUS – RESPONSIBILITY – BASICS OF LIFE – BASICS OF TIME – IRREVERSIBILITY
1. History
The philosopher Aristotle (384/3 – 324/1 B.C.) postulated that the freedom of mankind was necessarily connected to the ability of human beings to understand their natural mean, the right proportion of necessities and desires that allowed them to live together peacefully with other people and nature.
In contrast to this anthropological concept, Mainstream Economics perceives the human being as homo oeconomicus, a concept whose roots go back to the political philosopher Thomas Hobbes (1588 – 1779) [HOMO OECONOMICUS & HOMO POLITICUS – Faber et al. 1997, Manstetten 2000, Faber and Manstetten 2007: Chapter 4]. The homo oeconomicus does not have any understanding of a natural proportion of necessities and desires. Instead, the necessities and desires of a homo oeconomicus are postulated as infinite, and his nature is to try to fulfill as many of them as possible. This natural ambition leads to the experience of limits: Whatever the homo oeconomicus acquires or achieves, it will be less than he wishes to acquire or achieve. Nevertheless, the homo oeconomicus feels challenged by these limits. Thanks to technological progress and innovation, modern economies develop an intrinsic dynamic that allows them to go beyond some limits that were formerly known as ‘natural’ ones.
“For the discussion within Ecological Economics, the scarcity concepts of classical political economy have been of importance in particular. Thomas Robert Malthus (1766 – 1834) introduced the notion of a general scarcity of nature into classical economic thought. According to Malthus, natural laws specify that population growth is always substantially faster than the growth in agricultural output, which ‘implies a strong and constantly operating check on population from the difficulty of subsistence’ (Malthus [1798] 1976: 20; see also Becker et al. 2005). More generally, Malthusian scarcity denotes the idea that essential natural resources have a finite physical limit. This implies that, ultimately, there are limits to economic growth. [HISTORY OF THOUGHT] David Ricardo (1817 [1951]) gave a different economic interpretation of the scarcity of nature which refers to the decreasing quality of land: Land as a natural resource is readily available, but only in ever more declining quality.
With the renewed interest in economy-environment interactions in the second half of the 20th century, there have been several attempts to revitalize the discussion about the economic scarcity concept by referring to classical economic considerations as well as to the natural sciences such as THERMODYNAMICS and ecology (Barbier 1989). Pioneering contributions have been made e.g. by Barnett and Morse (1963), Boulding (1966), Georgescu-Roegen (1971), Meadows et al. (1972) and Daly (1977). All of them refer in some sense to the Malthusian concept of a general inescapable scarcity of nature. Following Georgescu-Roegen (1971), the laws of thermodynamics in particular have been regarded as imposing such inescapable scarcity of nature. In this regard Daly (1977: 39) introduces the notion of ‘absolute scarcity’ which he distinguishes from ‘relative scarcity’. The distinction between ‘relative’ and ‘absolute’ scarcity has been taken up by a number of authors (e.g. Faber et al 1983/1990, Barbier 1989, Underwood and King 1989, Barbier et al. 1994, Sahu and Nayak 1994) and has been identified as one feature that distinguishes Mainstream Economics from Ecological Economics (e.g. Underwood and King 1989, Sahu and Nayak 1994): While Mainstream Economics is said to focus on issues of relative scarcity, Ecological Economics is primarily interested in issues of absolute scarcities” (Baumgärtner et al: 2006: 488-489).
Despite the appearance of many limits concerning the satisfaction of needs and wants as temporary ones, whoever deals with economic issues will have to admit the existence of limits that cannot be surpassed. These natural limits are studied by Ecological Economists – BASICS OF LIFE – THERMODYNAMICS – JOINT PRODUCTION – SUSTAINABILITY & JUSTICE. In this context, a further neglected concept experiencing a renaissance is the notion of moderation [see Section 3.4 Biocoenosis and Faber and Manstetten 2007: Chapter 12].
2. Theory
The Concept of Scarcity
The objective of this chapter is to represent the roles of the concept of scarcity in Mainstream Economics on the hand and Ecological Economics and Ecology on the other (Section 2.1). To illustrate these concepts we will show, how it can be applied in order understand the role of biodiversity for ecosystem functioning and human well-being (Section 2.2). Due to the absolute dependence of human beings on the functioning of nature and the lack of manmade substitutes to the services of nature we discuss the concept of absolute scarcity in Mainstream Economics and in Ecological Economics as well as in Ecology (Section 2.3.) The issue of biodiversity will be presented not only as one of relative scarcity (which would mean to postulate substitutability of natural services), but as one of absolute scarcity (Section 2.4). The relationship between relative and absolute scarcity is discussed in Section 2.5.
2.1 Relative scarcity in Mainstream Economics
Intuitive definition of scarcity
To understand scarcity, it is expedient to begin with a first definition of scarcity in economics: “Whenever goods and services are not available in a quantity that allows fulfilling completely the desires of all consumers, goods and services are, in economic terms, scarce.
Scarce means of life
“The means acquired as the basis of life for an individual are scarce in relation to the needs and desires that distinguish this life. Hence, a person without needs would not experience scarcity, similarly to persons living their life in a world with an infinite amount of the means of life available” (Faber and Manstetten 2007: 285f; our translation).
In a similar vein Robbins (1932:15) writes: “We have been turned out of Paradise. We have neither eternal life nor unlimited means of gratification. Everywhere we turn, if we choose one thing we must relinquish others which, in different circumstances, we would wish not to have relinquished. Scarcity of means to satisfy given ends is an almost ubiquitous condition of human behaviour” (Faber and Manstetten 2007: 286; our translation).
“Economic scarcity on a market requires the ability to choose. Only people who are able to choose, thus, free people, can experience the scarcity described by Robbins. Freedom therefore is understood as the possibility to choose between different alternatives. Scarcity shows us, that choosing is always an act of abstinence – HOMO OECONOMICUS & HOMO POLITICUS. Since our means are scarce and the days of our lifetime are finite, a choice can imply that that which is not chosen might be something never to be chosen again. Hence, every factual satisfaction of one’s needs leads to not satisfying another, also urgent need. Such situations of choice and their analysis are, according to Robbins, the field of economic sciences – HOMO OECONOMICUS & HOMO POLITICUS. In his definition, Robbins defines economics as a theory of choice under the conditions of (relative) scarcity” (Faber and Manstetten 2007: 286f, our translation).
Economics as the study of relative scarcity: choice and substitution
Such a relative notion of scarcity relies on one particular assumption about (a) the objective possibilities of consumption and (b) peoples’ subjective preferences over these options, namely substitutability – SUSTAINABILITY & JUSTICE. First of all, the idea of relative scarcity presupposes the existence of alternative consumption bundles. Usually, there exists a wide spectrum of consumption possibilities which can all be produced from a number of elementary resources. Giving up one particular consumption bundle allows the production of a substitute consumption bundle from these resources if the resources can be used in alternative ways to produce different consumption bundles. Furthermore, the concept of relative scarcity presupposes that peoples’ preferences are characterized by substitutability. Saying that people are willing to give up something else in order to obtain one additional unit of a scarce good rests on the implicit assumption that people consider these two goods to be substitutes. Giving up one unit of good A and receiving in exchange a certain amount of good B will leave them equally well off in terms of utility. Only then does it make sense to say that one is willing to pay for one good by giving up another.
An illustration: scarcity of bread
2.2 The study of biodiversity in Mainstream Economics
Mainstream Economics has also addressed the issue of biodiversity loss and conservation. This includes, inter alia, the analysis of
– the measurement of biodiversity (e.g. Weitzman 1992, 1998, Solow et al. 1993, Nehring and Puppe 2002, 2004, see Baumgärtner 2005 for an overview),
– the valuation of biodiversity or individual components thereof (e.g. Randall 1988, Pearce and Moran 1994, Watson et al. 1995, Costanza et al. 1997, Goulder and Kennedy 1997),
– the optimal selection of specific plant genetic traits for the development of pharmaceutical substances (e.g. Polasky and Solow 1995, Simpson et al. 1996, Rausser and Small 2000),
– the use of biodiversity as an insurance of the provision with certain ecosystem services, for instance in agriculture or medicine (e.g. Perrings 1995, Weitzman 2000, Schläpfer et al. 2002, Swanson and Goeschl 2003 – IGNORANCE,
– different use and ownership regimes of biodiversity (e.g. Sedjo and Simpson 1995, Lerch 1998, Swanson and Goeschl 2000b),
– the relationship between biodiversity loss and poverty or, more generally, the distribution of wealth and income (e.g. Munasinghe 1992, Dasgupta 1995, Myers 1995, Swanson and Goeschl 2000a), and
– the design of cost-effective and efficient measures of nature conservation (e.g. Polasky et al. 1993, Solow et al. 1993, Weitzman 1993, Swanson 1994, Metrick and Weitzman 1996, 1998, Wu and Boggess 1999).
All these economic contributions are based on the idea of relative scarcity of biodiversity.
The Mainstream Economic view of the relationship between humans and nature
“Looking at biodiversity from the point of view of relative scarcity, economics features a specific, implicit understanding of humans, nature, and the relationship between them. In the view of economics, both human preferences and real production possibilities, including production by nature, are characterized by substitutability (Turner 1999). The human actor is seen as a rational decision-maker who makes choices based on his own preferences over goods – HOMO OECONOMICUS & HOMO POLITICUS. Besides consumption goods, this also includes environmental goods and services. Thus, nature is seen as consisting of substitutable and reproducible environmental goods which serve the purpose of satisfying human preferences. The relationship between humans and nature in economics, therefore, appears as a relationship between homo oeconomicus and nature as a collection of goods and services which are, in principle, like any other economic goods and services. Other aspects of the relationship between humans and nature are outside the scope of economics (Becker 2005a)” (Baumgärtner et al. 2006: 490).
2.3 Absolute scarcity in Ecological Economics and ecology
Having dealt with relative scarcity, we now turn to absolute scarcity. “If a certain good is neither substitutable against others on the production side nor on the preference side, a relative notion of scarcity will not capture the scarce nature of this good. As an illustration, consider again the example of bread. As argued above, at the margin and at sufficiently high income levels bread is scarce only in a relative sense.
An illustration of absolute scarcity: a besieged town
Three relations of scarcity: desires and needs, other goods, time and location
Up to now we have given rather broad definitions of scarcity. Now we want to go into more detail. To this end we note that “the economic term of scarcity describes the scarcity of a good within three relationships:
(i) In relation to the choosing human being, his desires and needs.
(iii) In relation to a certain point in time and a certain location.
The example of bread in a besieged town may seem far-fetched and absolute scarcity hardly relevant for standard economic problems, but the idea of absolute scarcity is very relevant for the issue of nature conservation. From ecology it is well known that the extinction of one species can lead to the extinction of another species if the former is an essential resource for the latter and cannot be replaced (Begon et al. 1998, Ricklefs and Miller 1999). Thus, absolute scarcity is an essential characteristic of biological life – BASICS OF LIFE. The questions are to what extent can humans be reduced to being a purely biological species and how relevant, as a result, is absolute scarcity for humans? In the following, we will discuss the meaning of absolute scarcity for the human being. We will first address non-substitutability on the preference side and then on the production side before we turn to a discussion of absolute scarcity of biodiversity.
Non-substitutability on the preference side: elementary and imaginary goods
In the HISTORY OF THOUGHT, a distinction has been made between two classes of human needs which may be called elementary needs and imaginary needs following Schlosser (1784; cf. Binswanger 1991; see for an extensive analysis Faber and Manstetten: 2010: 135-138). This distinction goes back to the ancient Aristotelian distinction between the natural economy and the artificial economy (Roscher 1874: 529). This Aristotelian perspective shows up in various forms over time among various scholars; for example, Thoreau ([1854]1998) employs a similar distinction based on whether the satisfaction of needs is ‘necessary for life’ or not, when discussing man’s relation to nature. And even today, the United Nations make a distinction between basic needs and non-basic needs when assessing progress in worldwide poverty alleviation (ILO 1976, Boltvinik 2001).
There are other aspects of human being beyond elementary needs which might also be regarded as essential to human life and thus as absolutely scarce. Human life is not fulfilled by mere survival but by striving for aims beyond mere survival. In this regard some fundamental values might be regarded as absolutely scarce. For example, ethical laws in a Kantian sense can be regarded as universally and absolutely valid – RESPONSIBILITY.
The same holds for human rights, freedom or and justice – SUSTAINABILITY & JUSTICE. Such values can be seen as absolutely scarce with regard to a fulfilled human existence. No substitution is conceivable without degrading a human being. In this perspective, ethical categories are not within the scope of economics, but they constitute a form of absolute scarcity which is not within the scope of ecology either.
Non-substitutability on the production side
When we want to know whether a certain bundle of goods and services can be replaced by another bundle, by reallocating resources from one production process to another, we have to make recourse to the objective natural and engineering sciences – JOINT PRODUCTION. Resource availability and transformation (by production) has to obey the laws of nature – THERMODYNAMICS – IRREVERSIBILITY. For that reason, geology, ecology, physics, chemistry, mechanical and chemical engineering, etc. tell us about the potential and limits of producing goods and services from primary resources – BASICS OF LIFE.
– The laws of thermodynamics – THERMODYNAMICS – specify the minimal energy and material input required to produce a certain product (Kondepudi and Prigogine 1998, Bejan 1997).
– Both thermodynamics and ecology stress the importance of IRREVERSIBILITY in a system’s dynamics and EVOLUTION. This means, it is not always possible to substitute one production result with another one by just undoing the former and starting anew. An extreme example is species extinction, which cannot be reversed.
From these arguments it becomes obvious that, in as far as production is governed by the laws of nature, the possibilities for substitution between producing alternative consumption bundles are generally limited. In particular, non-substitutability on the production side holds for the goods and services produced directly by nature, as the laws of ecology play a key role here. There are more or less restrictive limits to producing more or less natural goods and services in exchange for the production of manufactured goods and services. Nature provides a lot of factors for agricultural and industrial production, e.g. water, nutrients, sunlight, pollination and mineral as well as fossil resources – BASICS OF LIFE. While some of these factors may be replaced by manufactured substitutes, this is not possible for all of them in their entire amount. As a consequence, these services of nature are indispensable – at least to a certain extent. Overall, nature has a number of characteristics which are systematically neglected when nature’s goods and services are treated as ordinary economic goods, services or production factors” (Baumgärtner et al. 2006: 490-492).
2.4 Absolute scarcity in ecology and Ecological Economics: the study of biodiversity
“Ecologists and ecological economists have stressed that biodiversity has an important value in so far as it is instrumental for ecosystem functioning and ecosystems’ capability of providing essential life-supporting ecosystem services for humankind. In making this claim, the ‘division of labor’ between ecologists and Ecological Economists is the following. Ecology studies biodiversity and its role for ecosystem functioning and evolution in a descriptive way, independent of subjective human valuations. One result of this research is that biodiversity is essential for ecosystem functioning (e.g. Schulze and Mooney 1993, Holling et al. 1995, Kinzig et al. 2001, Loreau et al. 2001, 2002, Hooper et al. 2005) and for the provision of a number of ecosystem services (e.g. Perrings et al. 1995, Daily 1997, Millennium Ecosystem Assessment 2005). We note that these surveys also stress the large extent of uncertainty about the functioning of ecosystems [Ignorance]. Examples for ecosystem services include biomass production, nitrogen fixation, nutrient cycling, control of water runoff, purification of air and water, soil regeneration, pollination of crops and natural vegetation, and partial climate stabilization – BASICS OF LIFE.
As discussed in Section 2.3 above, Ecological Economists argue that nature too has a value in itself.
The ecological view of the relationship between humans and nature
“Ecologists, and not a few Ecological Economists, tend to regard humans mainly as a biological species like all others, i.e. the human being is regarded as a homo biologicus (Manstetten et al. 1998). In this view, and in contrast to the economic perspective, an elementary and absolute dependence of human beings on nature and its biodiversity becomes obvious. While humans are, to some extent, different from other animals, for instance in that they have a consciousness and free will, to a considerable extent they are just animals. That is, they are characterized by elementary biological dependencies (e.g. MacIntyre 1999). This insight refers to the perspective of absolute scarcity since it presupposes that humans have elementary and non-substitutable needs (such as water, food, fresh air) which have to be satisfied for their mere survival (see Faber and Manstetten 2010: 135f). Thus, the relationship between humans and nature in Ecological Economics appears as a relation between homo biologicus and nature as an absolutely scarce entity, essential and necessary for survival. Thereby, Ecological Economics recognizes an aspect of the relationship between humankind and nature which cannot be regarded within economics (Becker 2003: 48-70)” (Baumgärtner et al. 2006: 490-492) – TELEOLOGICAL CONCEPT OF NATURE.
2.5 The relationship between relative and absolute scarcity
– Time scale: Technical progress may yield new technologies over time which allow the production of substitutes for previously absolutely scarce goods that then become scarce only in a relative sense – BASICS OF TIME. For example, with progress in cardiac transplantation and the development of an artificial heart, the absolute scarcity of the life-supporting function of the natural heart has been transformed into a relative one. As an example of the reverse, in the besieged town considered above, bread may be relatively scarce at the beginning but may become absolutely scarce as the siege continues.
– Spatial scale: A good which is absolutely scarce on a given spatial scale may be relatively scarce on a larger spatial scale. In the example of the besieged town, bread is absolutely scarce only within the town, but it may be relatively scarce when considering the country at large.
– Institutional settings: Institutions, such as e.g. markets and mechanisms of (international) trade, which foster interaction and exchange between economic agents introduce or enlarge possibilities of substitution. For example, a subsistence farmer absolutely depends on his own food production. If this person has access to, say, markets for food and labour, he can transform the absolute scarcity of food into a relative one by trading his own labour for food.
– Organization of interaction: Interactions and exchange between individuals and the institutions which govern these interactions may be organized in an efficient or an inefficient way. Inefficiency means that resources or consumption goods are wasted, such that individuals and society at large fall short of reaping the maximum benefits from a given resource endowment. If social processes are organized in an inefficient manner, the full potential of substitution is not exhausted, and a certain good may be absolutely scarce which could be relatively scarce if the process were organized in a more efficient manner.
– Hierarchical level: An individual’s possibilities of substitution are, in general, more limited than societies. As a consequence, what is absolutely scarce for an individual may be relatively scarce for society at large. As an extreme example, individual freedom and survival are non-substitutable for the individual. However, society at large may consider these as substitutable, for instance in times of war when the freedom and survival of military personnel are traded-off against the freedom and survival of other members of society and society at large.
As a consequence, the question of substitutability and the question of relative versus absolute scarcity cannot be answered in a general way, once and for all, but need to be addressed in a particular context. It requires detailed knowledge about ecosystem functioning, technological possibilities for substitution, human preferences, organization of interaction, institutional setting, etc. However, all these aspects are subject to dynamic change: evolution of nature, technology, preferences and institutions over time. These dynamic developments are uncertain and cannot be predicted in detail” (Baumgärtner et al. 2006: 493) – IGNORANCE.
3. The MINE Project: Focus on Fundamental Concepts
3. Practice
In this Chapter we want to give a summary and present the conclusion of our findings. To this end we first focus on the role of economics in the study of relative and absolute scarcity in biodiversity (Section 3.1). We relate them to the subject of sustainability – SUSTAINABILITY & JUSTICE – since they have important implications for it (Section 3.2). This will show us that relative and absolute scarcity is grounded in a fundamental philosophical difference; hence we will turn to their philosophical dimension which is beyond Mainstream Economics on the one hand and Ecological Economics and ecology at the other (Section 3.3).
3.1 The roles of Mainstream Economics, Ecological Economics and ecology in the study of relative and absolute scarcity of Biodiversity
The merit and deficit of Mainstream Economics
The merit of ecology and Ecological Economics
Ecological Economics and ecology provide such an approach in that they stress the essential and non-substitutable role of biodiversity for human survival (see Section 2.4 above). Thus, they recognize one specific aspect of absolute scarcity of biodiversity. Recall from Section 2.1 that there could be further dimensions of absolute scarcity which are not based on biological reason, e.g. an ethical dimension. However, they regard the problem of biodiversity loss predominantly under this aspect of absolute scarcity” (Baumgärtner et al. 2006: 494) and do not give relative scarcity the importance it deserves.
Integrating the two perspectives
3.2 Scarcity and sustainability
“Our discussion of the distinction between relative and absolute scarcity has immediate implications for the distinction between what has been called in the literature ‘weak’ and ‘strong’ sustainability (e.g. Neumayer 2003, Pearce and Barbier 2000: Chap. 2 – SUSTAINABILITY & JUSTICE). In a sense, the two distinctions correspond to each other. While weak sustainability calls for the maintenance of the aggregate (i.e. natural plus human-made) stock of capital, strong sustainability calls for the separate maintenance of natural capital stock and human-made capital stock. The rationale between this distinction lies in different assumptions about the substitutability between natural and human-made capital: weak sustainability assumes that human-made capital is a perfect substitute for natural capital, i.e. natural capital is scarce only in a relative sense, while strong sustainability assumes that natural capital is essential and cannot be substituted by human-made capital, i.e. it is absolutely scarce (Barbier et al. 1994: 51-56).
3.3 Beyond Mainstream Economics and ecology: the philosophical dimension
Discussion of our images of humankind and nature
“In the end, a comprehensive discussion about biodiversity loss and protection comes down to a discussion of our images of humankind and nature, as well as their interrelationship. Mainstream Economics, Ecological Economics and Ecology provide us with one particular dimension of this image. In Mainstream Economics, the relationship between humans and nature appears as a relationship between homo oeconomicus – HOMO OECONOMICUS & HOMO POLITICUS – and nature as a diverse bundle of substitutable consumption goods and production factors which are not essentially different from manufactured goods and factors. In ecology, this relation appears as a relationship between homo biologicus (i.e. man as purely biological being; Manstetten et al 1998) and nature as an entity which is essential and necessary for his survival. Mainstream Economics, Ecological Economics and Ecology address important dimensions of the human being and its relation to nature: The human being obviously shows both essential dimensions – homo oeconomicus and homo biologicus – and nature is both a set of objects that are subject to rational choice as well as an entity that is essential for human survival.
Discussion of the two perspectives is not sufficient
A plurality of perspectives
Conclusion: a philosophical approach is required
In conclusion, a philosophical approach can achieve at least four tasks:
(ii) identify the dimensions of the problem that are beyond the scope of these two disciplines;
(iii) formulate and analyse the ethical dimension of the problem;
(iv) provide a philosophical framework in which the different underlying perspectives of disciplines such as Mainstream Economics, Ecological Economics, ecology and ethics – RESPONSIBILITY –, as well as their relation can be identified and integrated. We note that this task is pursued in particular by Ecological Economics.
4. Literature
Key Literature
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Baumgärtner, S., Becker, C., Faber, M., Manstetten, R. (2006) “Relative and absolute scarcity of nature. Assessing the roles of economics and ecology for biodiversity conservation.” Ecological Economics 59: 487-498. [The concept RELATIVE & ABSOLUTE SCARCITY is mainly based on this paper.]
Daoud, Adel (2018) Unifying Studies of Scarcity, Abundance, and Sufficiency’, Ecological Economics 147: 20-217. [Pioneering paper on scarcity, abundance and sufficiency. It is comprehensive concerning the literature and groundbreaking in its content.]
Further Reading
References
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Scarcity
Barnett, H.J. and C. Morse (1963), Scarcity and Growth. The Economics of Natural Resource Availability, Baltimore: Johns Hopkins Press.
Barbier, E.B. (1989), Economics, Natural Resource Scarcity and Development. Conventional and Alternative Views, London: Earthscan.
Baumgärtner, S., Becker, C., Faber, M., Manstetten, R. (2006) “Relative and absolute scarcity of nature. Assessing the roles of economics and ecology for biodiversity conservation.” Ecological Economics 59: 487-498. [The concept RELATIVE & ABSOLUTE SCARCITY is mainly based on this paper.]
Daoud, A. (2018) Unifying Studies of Scarcity, Abundance, and Sufficiency’, Ecological Economics 147: 20-217. [Pioneering paper on scarcity, abundance and sufficiency. It is comprehensive concerning the literature and groundbreaking in its content. The author develops new and promising perspectives for further research.]
Faber, M., H. Niemes, and G. Stephan (1983/1987) Entropie, Umweltschutz und Rohstoffverbrauch. Eine naturwissenschaftlich-ökonomische Untersuchung; translated into English by Ingo Pellengahr. Resources. An Essay in Physico-Economics. Springer Verlag, Heidelberg etc. (translated into Chinese 1990; ISBN Y 80555-344-0/X.1.) [This book views absolute scarcity from an ecological economic and thermodynamic perspective.]
Faber, M., R. Manstetten (2007), Was ist Wirtschaft? Von der Politischen Ökonomie zur Ökologischen Ökonomie. Freiburg/München. [See in particular Chapter 12 which not only analyses scarcity in detail but also its relationship to the concept of moderation.]
Mankiw N.G. (2000), Principles of Economics, second ed., Harcourt Brace.
Manstetten, R. (2000) Das Menschenbild der Ökonomie. Der homo oeconomicus und die Anthropologie von Adam Smith, Alber, Freiburg, München.
Montani, G. (1987), Scarcity, in J. Eatwell, M. Milgate and P. Newman (eds.), The New Palgrave. A Dictionary of Economics, Vol. 4, Houndsmill and New York: Palgrave.
Robbins, L. (1932) On the Nature and Significance of Economic Science. London.
Schumpeter, J.A. (1954), History of Economic Analysis, New York: Oxford University Press.
Smith, V.K. (1979), Scarcity and Growth Reconsidered, Baltimore and London: Johns Hopkins University Press.
Mainstream Economics
Boltvinik, J. (2001), Poverty measurement methods – an overview, United Nations Development Programme (UNDP) Poverty Reduction Series Working Paper No. 3, available from: www.undp.org/poverty/publications/pov_red/.
Dasgupta, P. (1995), Population, poverty, and the local environment, Scientific American, 272(2), pp. 40ff.
Debreu, G. (1959), Theory of Value. An Axiomatic Analysis of Economic Equilibrium, New York: Wiley.
Eatwell, J., M. Milgate and R. Newman (eds.) (1987), The New Palgrave. A Dictionary of Economics, 4 vols, London: Maxmillan.
Fisher, A.C. (2000), Introduction to special issue on irreversibility, Resource and Energy Economics, 22, 189-196.
[ILO] International Labour Office (1976), Employment, Growth and Basic Needs: A One-World Problem. Report of the Director-General of the International Labour Office, Geneva.
Malthus, T.R. ([1798]1976), An Essay on the Principle of Population, ed. by P. Appleman New York and London: W.W. Norton and Company.
Mankiw, N.G. (2000), Principles of Economics, second ed., Harcourt Brace.
MasColell, A., M.D. Whinston and J.R. Green (1995), Microeconomic Theory, New York: Oxford University Press.
Polasky, S. and A. Solow (1995), On the value of a collection of species, Journal of Environmental Economics and Management, 29, 298-181.
Polasky, S., A. Solow and J. Broadus (1993), Searching for uncertain benefits and the conservation of biological diversity, Environmental and Resource Economics, 3, 171-181.
Ricardo, D. (1817[1951]), On the Principles of Political Economy and Taxation, ed. by P. Sraffa, Cambridge: Cambridge University Press.
Robbins, L. (1932), An Essay on the Nature and Significance of Economic Science, London: Macmillan.
Roscher, W. (1874), Geschichte der National-Ökonomik in Deutschland, München.
Schläpfer, F., M. Tucker and I. Seidl (2002), Returns from hay cultivation in fertilized low diversity and non-fertilized high diversity grassland, Environmental and Resource Economics, 21, 89-100.
Walras, L. (1926[1954], Elements of Pure Economics, or the theory of social wealth, transl. by W. Jaffe, London, George Allen & Unwin.
Ecological Economics
Baumgärtner, S. (2000), Ambivalent Joint Production and the Natural Environment. An Economic and Thermodynamic Analysis, Heidelberg and New York: Physica.
Bejan, A. (1997), Advanced Engineering Thermodynamics, second ed., New York: Wiley.
Boulding, K.E. (1966), The economics of the coming spaceship Earth, in H. Jarrett (ed.), Environmental Quality in a Growing World, Baltimore and London: Johns Hopkins University Press, pp. 3-14.
Costanza, R. (1989), What is Ecological Economics? Ecological Economics, 1, 1-7.
Costanza, R., R. d’Arge, R. de Groot, S. Farber, W. Grasso, B. Hannon, K. Limburg, S. Naeem, R.V. O’Neill, J. Paruelo, R.G. Raskin, P. Sutton and M. van den Belt (1997), The value of the world’s ecosystem services and natural capital, Nature, 387, 253-260.
Daily, G.C. (ed.) (1997), Nature’s Services. Societal Dependence on Natural Ecosystems, Washington DC: Island Press.
Daly, H.E. (1977): Steady-state Economics, San Francisco: W.H. Freeman and Company.
Daly, H.E. (ed.) (1980), Economics, Ecology, Ethics. Essays Toward a Steady-State Economy, San Francisco: W.H. Freeman.
Daly, H.E. (1990), Toward some operational principles of sustainable development, Ecological Economics, 2, 1-6.
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Ecology
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Biodiversity
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The content of MINE originates from scientific work published in books and peer-reviewed journals. Quotes are indicated by a special typographic style.
The project team would like to thank the publishers Edward Elgar, Elsevier, Routledge, Springer and Taylor & Francis for granting a reproduction permission.
Furthermore, we want to express our gratitude to Bernd Klauer, Reiner Manstetten, Thomas Petersen and Johannes Schiller for supporting the MINE Project and granting the permission to use parts of the content of their book “Sustainability and the Art of Long-Term Thinking.”
We are indebted to Prof. Joachim Funke, Ombudsman for Good Scientific Practice at Heidelberg University and the legal department at Heidelberg University, for their advice and support.
The main sources of this concept is the following publication:
Baumgärtner, S., Faber, M. and Schiller, J. (2006), Joint Production and Responsibility in Ecological Economics. On the Foundation of Environmental Policy. Edward Elgar, Cheltenham.
Copyright notice: All rights reserved. No part of this publication may be reproduced, stored in a retrieval system or transmitted in any form or by any means, electronic, mechanical or photocopying, recording or otherwise without the prior permission of the publisher. The material is reproduced in MINE with permission of the Licensor through PLSclear (Ref. No: 8526, licenced 21.11.2018)