Ecological Resilience and Sustainable Development

Ecological Resilience and Sustainable Development

ECOLOGICAL ECONOMICS 68 (2009) 605– 612 available at www.sciencedirect.com www.elsevier.com/locate/ecolecon SURVEY Critical natural capital revisited: Ecological resilience and sustainable development Fridolin Brand⁎ Institute for Landscape Ecology, Technische Universität München (TUM), Am Hochanger 6, 85350 Freising, Germany ARTICLE DATA ABSTRACT Article history: The maintenance of critical natural capital is an important objective of sustainable Received 25 January 2008 development. Critical natural capital represents a multidimensional concept, as it mirrors Received in revised form 30 July 2008 the different frameworks of various scientific disciplines and social groups in valuing Accepted 19 September 2008 nature. This article revisits the concept of critical natural capital and examines its relation to Available online 23 October 2008 the concept of ecological resilience. I propose that ecological resilience can help a great deal in specifying the ‘ecological criticality’ of specific renewable parts of the natural capital. Keywords: More specifically, I suggest that the degree of ecological resilience is inversely related to the Critical natural capital degree of threat ecosystems are prone to. The concept of ecological resilience may Resilience complement other measures, such as integrity or vulnerability, in estimating the degree of Sustainable development threat specific ecosystems are exposed to. The empirical estimates of ecological resilience Strong sustainability add a further criterion in order to build a comprehensive and clear conception of critical natural capital. © 2008 Elsevier B.V. All rights reserved. 1. Introduction being) ought to be maintained over intergenerational time scales. In this conception, natural capital and man-made Sustainable development represents one of the key challenges capital are viewed as substitutes within specific production of the 21st century (Sachs, 2005; Clark, 2007). Even though processes. Consequently, the stock of the natural capital can there is a wide political consensus on the principal idea of be depleted, unless the utility over time is declining (cf. sustainability, scientific agreement regarding the key question Pezzey, 1992; Norton and Toman, 1997). In contrast, strong ‘what to sustain?’ (Dobson, 1996; NRC, 1999; Kates et al., 2005) sustainability states that natural capital and man-made capital is a far off horizon. It is still controversial what types of capital, must be viewed as complementary. We are obliged to keep i.e. natural capital (e.g. ecosystems, air, water), cultivated each type of capital intact over time. Thus, the whole stock of natural capital (e.g. salmon farms, wineries), man-made natural capital ought to be preserved for current and future capital (e.g. infrastructure), social capital (e.g. political institu- generations in the long run (Daly, 1996). tions), human capital (e.g. skills, education) and knowledge The concept of critical natural capital emerged as a trade-off capital ought to be preserved in favour of current and future between these two extreme positions. It signifies the part of the generations (Costanza et al., 2007). natural capital that performs important and irreplaceable At this conceptual level of sustainability science, basically environmental functions, i.e. ecosystem services (Jax, 2005)that two positions fight for validity (cf. Neumayer, 1999; Ott and cannot be substituted by other types of capital (deGrootetal., Döring, 2004). Weak sustainability holds that utility (or well- 2003; Dietz and Neumayer, 2007). Paradigmatic examples include ⁎ Tel.: +49 89 38377714; fax: +49 8161 714427. E-mail address: [email protected]. 0921-8009/$ – see front matter © 2008 Elsevier B.V. All rights reserved. doi:10.1016/j.ecolecon.2008.09.013 606 ECOLOGICAL ECONOMICS 68 (2009) 605– 612 essential ecosystem services, such as freshwater resources, Gunderson and Holling, 2002; Gunderson and Pritchard, 2002) climate regulation and fertile soils (MEA, 2005). It is this and it is this second kind of resilience to which I refer in this text. importance for the quality of life and the survival of humans The concept of ecological resilience emerged in ecology in that makes critical natural capital such an important objective of the 1960–1970s but has been adopted since then by numerous sustainability. Critical natural capital represents thus the part of scientific disciplines, e.g. sociology, economy or political science the natural environment that ought to be maintained in any (cf. Folke, 2006 for a recent review). For instance, Common and circumstances in favour of present and future generations. In Perrings (1992) examined its relation to ecological economics addition, the identification and management of critical natural and sustainability concepts. It is currently used either as a capital is a promising tool for a sound approach to environmental descriptive concept that is applied primarily to ecological policy (Ekins et al., 2003). The quest for a clear conceptualization systems, i.e. ecological resilience (e.g. Bellwood et al., 2003; of ‘critical natural capital’ is hence worth the effort. Nyström, 2006), or as a boundary object, a term that facilitates Yet conceptual confusion is immense, as numerous scien- communication across disciplinary borders, i.e. social–ecologi- tific disciplines and societal groups bring their own perspective cal resilience (cf. Brand and Jax, 2007). In the latter interpreta- in valuing nature. It is indeed highly unclear what makes tion, the concept is viewed as an innovative perspective to natural capital ‘important’, ‘irreplaceable’, and therefore ‘criti- analyze coupled social–ecological systems (Walker and Salt, cal’. In other words, it is controversial which measure would be 2006; Walker et al., 2006). appropriate to reflect or mirror ‘criticality’. Is it the ecological This article focuses on the former descriptive meaning of importance we ascribe to certain habitats due to a high degree of the term. Ecological resilience is defined as the capacity of an species richness or “naturalness”? Is it the economic value that ecosystem to resist disturbance and still maintain a specified state.In some ecosystem services bring for human society? Or is it the this definition the concept gets close to the stability concept socio-cultural relevance of the “landscape”? The important ‘resistance’, as identified by Grimm and Wissel (1997). This point here is that we urgently need well-founded criteria to may underestimate other important characteristics of ecolo- assess the specific criticality of natural capital stocks (MacDo- gical resilience, such as the capacities for renewal, reorganiza- nald et al., 1999; Ekins et al., 2003). tion and development (Folke, 2006). Yet this definition is in my This article examines the link between the concept of view useful and workable to be used for the measurement of ecological resilience and critical natural capital. I state that the ecological resilience in real-world ecosystems. empirical estimation of ecological resilience can help a great How to measure ecological resilience? Carpenter et al. (2005) deal in assessing the “ecological criticality” of specific parts of recently noticed that ecological resilience cannot be measured renewable natural capital. More specifically, I propose that the directly. Rather it must be estimated by means of resilience amount of resilience can be used to estimate the degree of threat surrogates, i.e. indirect proxies that are derived from theory certain ecosystems are prone to. The concept of ecological used in indicating resilience (cf. for resilience theory Walker resilience therefore adds a further important criterion to build a et al., 2006). Surrogates for ecological resilience refer to the comprehensive conception of criticality. concept of resilience mechanisms, e.g. ecological redundancy, The article is organized as follows. The first section offers a response diversity or ecological memory (e.g. Bellwood et al., short description of the concept of ecological resilience with an 2003; Bengtsson et al., 2003; Nyström, 2006), the concept of emphasis on questions regarding the conceptualization and maintained system identity (Cumming et al., 2005), probabilistic measurement of ecological resilience. Subsequently, the second resilience and percolation theory (Peterson, 2002)orto section revisits the concept of critical natural capital and approaches using the concept of alternative stable states and formulates a comprehensive approach to criticality. Based on ecological thresholds (e.g. Scheffer et al., 2001; Bennett et al., these conceptual reflections, the third section examines the link 2005). Before I will expand in some detail on the latter approach between the concept of ecological resilience and a conception of it must be noted that each estimation of ecological resilience is critical natural capital. Finally, the fourth section concludes with based on a comprehensive resilience analysis, which includes the findings of this paper. the identification of the specific disturbance regime and a societal choice of the desired ecosystem services. Confer for a detailed review of a resilience analysis Carpenter et al. (2001), 2. The concept of ecological resilience Walker et al. (2002) and Resilience Alliance (2007). The threshold (T-) approach to resilience surrogates is used Among the scientific concepts currently used in sustainability widely in the relevant literature (e.g. Carpenter et al., 2001; science, ‘resilience’ is one of

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