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Gotts, N. M. 2007. Resilience, panarchy, and world-systems analysis. Ecology and Society 12(1): 24. [online] URL: http://www.ecologyandsociety.org/vol12/iss1/art24/
Synthesis Resilience, Panarchy, and World-Systems Analysis
1Macaulay Land Use Research Institute
The paper compares two ambitious conceptual structures. The first is the understanding of social-ecological systems developed around the term "resilience," and more recently the term "panarchy," in the work of Holling, Gunderson, and others. The second is Wallerstein's "world-systems" approach to analyzing hierarchical relationships between societies within global capitalism as developed and applied across a broader historical range by Chase-Dunn and others. The two structures have important common features, notably their multiscale explanatory framework, links with ideas concerning complex systems, and interest in cyclical phenomena. They also have important differences. It is argued that there are gaps in both sets of ideas that the other might remedy. Their greatest strengths lie at different spatiotemporal scales and in different disciplinary areas, but each also has weaknesses the other does not address, particularly with regard to the mechanisms underlying proposed cyclic patterns of events. The paper ends with a sketch for a research program within which panarchical and world-systems insights might be synthesised in the study of the "Great European Land-Grab," i.e., the expansion of European capitalism and its distinctive social-ecological systems over the past five centuries.
Key words: adaptive cycle; cross-scale interaction; panarchy; population; resilience; technology; world-systems.
“Panarchy” refers here to the framework for conceptualizing the type of coupled human-environment systems described in Gunderson and Holling (2002) and more briefly, with some changes, in Walker et al. (2006). This framework may be divided into two parts, referred to here as “the resilience conceptual framework” and “the adaptive cycle metaphor.” This paper critically compares aspects of panarchy with the “world-systems” framework (Wallerstein 1974, 1993, Denemark et al. 2000, Hall 2000), specifically the variant of world-systems analysis developed by Chase-Dunn and colleagues (Chase-Dunn and Hall 1997a,b, Chase-Dunn and Babones 2006). The two approaches have much in common as well as important differences. Their commonalities include seeking broad-scale patterns in human social systems and explaining them in terms of processes that affect multiple, distinct, but interacting spatial and temporal scales. They also have close links with ideas about complex systems (Holland 1992, 1998) and place considerable emphasis on cyclic phenomena, an interest they inherit from Schumpeter (1939, 1943) and, via Schumpeter in the panarchist case, Kondratieff (1979 ), alternatively transliterated as “Kondratiev.” Major differences include the focal scale, which is regional for panarchy and planetary for world-systems; greater emphasis on ecological processes and social-ecological interactions in panarchy and on economic, political, and military processes in world-systems theory; and more attention within world-systems analysis to directional change over the course of multiple cycles.
For my purposes here, the following aspects of the panarchical view of ecological and social-ecological systems are central.
The resilience conceptual framework
Characteristics of the resilience conceptual framework include:
The characteristics of the adaptive cycle metaphor include:
World-systems analysis (Wallerstein 1974, Denemark et al. 2000, Chase-Dunn and Hall 1997a, Hall 2000) centers on the premise that the modern world cannot be understood without considering it as a whole, and over long periods of time. The stances of world-systems researchers differ considerably, but all would agree with the first point below, and most with points 2–7.
Chase-Dunn’s model attributes particular importance to the semi-periphery as the site of many major innovations, because these societies have more resources than peripheral societies but are less invested in the old ways than core societies are. Hall and Chase-Dunn (2006) present a number of historical examples, including semi-peripheral societies that founded large empires incorporating what had been former core societies, e.g., the Persian, Macedonian, Roman, Ottoman, and Manchu empires; capitalist city-states such as Tyre, Carthage, Malacca, Venice, and Genoa, which pioneered new trades and industries; and the rise of successive hegemons or leading powers of the capitalist system such as the Dutch Republic, the UK, and the United States. The rise of western Europe itself is held to have occurred from a semi-peripheral position in a multicore world-system, linked by trade in prestige goods and information exchange, that encompassed much of Afroeurasia, i.e., Eurasia plus Africa, during the medieval period.
According to Hall and Chase-Dunn (2006), the problems of environmental degradation and population pressure and conflict have not so far been solved, but rather shifted upscale. Early world-systems analysis paid little heed to specific or regional environmental issues, but in the last decade two special issues of the Journal of World-Systems Research have been dedicated to environmental issues. A number of the articles are comparative, linking world-system position, i.e., core, semi-peripheral, or peripheral, with indices of environmental damage or impact. Core states, as the homelands of the strongest elites, might be expected to avoid or remedy forms of environmental damage that would threaten the welfare of the elite, and perhaps that of the general population, whose support or acquiescence is extremely helpful. However, they may well choose not to control pollution that has only dispersed, long-term effects. Peripheral and semi-peripheral states would be expected to suffer from the effects of environmentally damaging extractive industrial activities that are often controlled by core-state corporations.
Generally, these expectations are borne out. Bartley and Bergesen (1997) cite several quantitative studies indicating that deforestation is most intense in the semi-periphery, where the demand for timber for construction is high but little reforestation occurs. In contrast, Burns et al. (2003) find the highest rates of deforestation in the periphery, which they attribute to recently intensified deforestation there; their own earlier work is cited in Bartley and Bergensen (1997). With regard to greenhouse gas emissions, Burns et al. (1997) report that CO2 output declines monotonically from core to periphery, whereas states in a “semi-core” category, which they define as being between core and semi-periphery, produce most of the world’s CH4 because of their heavy reliance on livestock farming. Grimes and Kentor (2003) find that the penetration of foreign capital raises CO2 production, which they attribute to the fact that transnational corporations tend to relocate environmentally unfriendly production to countries with fewer environmental controls. Roberts et al. (2003) add that, when the amount of CO2 released per unit of economic output is considered, semi-peripheral and “upper peripheral” countries, which depend heavily on foreign capital, do the worst. In a more regionally focused study, Frey (2003) analyzed examples of transfers of industrial processes from the United States, which is part of the core, to the northern border region of Mexico, which is in the semi-periphery. The increased environmental regulation in the United States is one reason for this, and the rapid growth of population and hazardous industrial processes has caused multiple forms of environmental damage.
Among the special issue articles, Bunker (2003) examines the social-ecological history of a specific region in the most detail, analyzing 400 yr of raw material extraction from the Amazon and demonstrating the interactions of regional topography, climate, and ecology with advances in transport technology and the increasing and changing demands of core economies. Each extractive episode involved the transport of greater volumes of goods, from spices to turtle oil to fine woods to rubber to iron ore, more cheaply over greater distances. Some of these products became obsolete, leading to regional economic downturns, e.g., turtle oil when mineral oils came into greater use, and rubber when the rubber tree was domesticated and grown in plantations in southeast Asia. In the Amazon, rubber trees cannot grow close to each other because of an endemic fungus, an important driver of domestication efforts, and hence the replacement of distant native forests by rubber plantations. An iron ore extraction project in the 1980s, driven by rising world demand, brought many workers to construct transport infrastructure. Laid off when construction ended, they began farming, in turn damaging Brazil nut production. The Brazil nut tree needs to be surrounded by other trees for shelter and to support a pollinating bee. Thus, Bunker elucidates the cross-scale linkages that, over the past four centuries, have tied the Amazon basin into the world-system and its technological development, changed its ecology, and also allowed its ecology to influence distant regions.
In this section, some criticisms of each of the approaches discussed are identified, and it is considered how far each might compensate for weaknesses in the other.
Taking the resilience conceptual framework first, points 1–4 above are not questioned here; criticisms of this framework are purely in terms of what it neglects. The adaptive cycle metaphor has been criticized from within the resilience conceptual framework; these criticisms are extended here.
There is general agreement that the four-phase adaptive cycle is not universal across ecological and social-ecological systems: Holling and Gunderson (2002:53-60) themselves describe systems stuck in one region of the three-dimensional space defined by connectivity, potential, and resilience. However, more fundamental criticisms of the adaptive cycle metaphor, and specifically of whether this three-dimensional space adequately represents the key aspects of ecosystem functioning, have recently emerged within the resilience literature. Janssen et al. (2006) distinguish three network characteristics relevant to resilience: centrality, i.e., the existence of key nodes, and two aspects of connectivity, density of links and reachability of nodes from each other, which are only partially independent. They found no simple connectivity-resilience relation. Abel et al. (2006) found the theory of the adaptive cycle useful for recognizing changes in system behavior during the various phases. However, they found several anomalies as well. The phases did not necessarily occur in the order proposed, there was no support for a fall in resilience during the K phase or for a clustering of events late in K, and the potential/connectedness distinction was not useful, so they replaced it with the concepts of natural, physical, human, social, and financial “capitals.”
Turning to cross-scale interactions, they found evidence of cross-scale effects outside the Revolt and Remember templates. In particular, government intervention and, more generally, the ability of power groups to appropriate resources were crucial both in maintaining regional rangeland systems in a particular condition in Zimbabwe and New South Wales and in causing regional collapses. They also noted that the social-ecological systems of Australian Aboriginals collapsed because of British colonization, with no reason to believe that these systems were intrinsically unstable. When describing a social-ecological system in Western Australia, Allison and Hobbs (2004) identified the drivers of its cyclical behavior as the 45–60 yr Kondratieff cycles of global economics, which produced alternating periods of favorable and unfavorable market conditions of roughly equal length, rather than internal dynamics of long, slow accumulation of capital separated by short periods of rapid change.
Thus it is not clear that system collapses are usually due, even in part, to internal dynamics. If a system on a more-or-less predictable trajectory spends a short time in its early phases and a longer time in later ones, as in the classic r to K succession from annuals to perennials to shrubs to trees, then an externally triggered collapse is most likely to occur in the later phases, even if the probability of collapse per unit time remains constant or falls. Conversely, economic and politically mediated links with larger national or transnational systems may be primary determinants of events, rather than merely constraining or triggering factors in the dynamics of the regional system. In such cases, world-systems analysis may have much to offer. It should be noted that the planetary social-ecological system is at the top of a hierarchy; although it is part of larger systems such as the Earth, solar system, and galaxy, these systems are not themselves social-ecological systems. The dynamics of the topmost member of a hierarchy of systems of a particular type must surely have some special features; nothing in the panarchist framework contradicts this, but neither does it appear to have received much attention.
There is a systematic ambiguity in the term “adaptive,” as used in “adaptive cycle.” The key question is: What adapts? In Holland (1992:184-185), adaptation is a property of organisms or of analogous components of an artificial system. In this context, entities that adapt show a characteristic subordination of their parts to the interests of the whole, just as the interests of the individual cells of a healthy animal are subordinated to those of the organism. In explanations of the adaptive cycle metaphor, it frequently appears that the system as a whole adapts and shows an analogous subservience of parts. This is explicit in Holling and Gunderson (2002): in the justification for adding the functions Ω and α quoted above, in “ ... the cycle shifts into a ‘backloop’ to reorganize accumulated resources for the initiation of a new cycle” (Holling and Gunderson 2002:41), and in their intuition (Holling and Gunderson 2002:47) that any complex system, if adaptive, must alternate between the “objectives” of maximizing first production and accumulation, then invention and reassortment. However, in the words of the resilience researcher Levin (2001): “ ... the ecosystem is not an organism and has not been shaped by evolution to perform particular functions, at least, so far as has been shown.” After arguing that natural selection acting on individuals can produce a form of hierarchical organization within an ecosystem in which most species interact strongly with only a few others, and that this can favor ecosystem resilience, Levin (1999) notes that features that reduce resilience, such as the existence of keystone species, can evolve in the same way. From this viewpoint, ecosystems can become either less or more resilient as they become more connected, depending on the details of the connection networks concerned.
Although the panarchical perspective admits political conflict, it has had little to say about social elites and the often violent and oppressive ways in which they maintain themselves. Nevertheless, elites and violent conflict are fundamental to social dynamics and highly relevant to environmental sustainability. Homer-Dixon and Blitt (1998) show how environmental scarcity interacts with power differences to generate destitution, violence, and further environmental destruction; conversely, Diamond (2005) argues that the highly stable Tokugawa shogunate in Japan was able to enforce society-wide measures to reverse deforestation. From the panarchical perspective, Abel et al. (2006) work on political influences on rangeland systems has already been mentioned. Pritchard and Sanderson (2002) note that, even in pluralist political systems, some interest groups can circumscribe debate and shape public preferences, hiding objectively divergent interests, and Alcorn et al. (2003) analyze how the Indonesian state has legitimized elite interests and, in doing so, undermined Dayak social-ecological system management. However, today’s most powerful agents, states and large corporations, with their economic power, media influence, and, for states, armed forces, remain largely unanalyzed. These agents largely determine what kinds of disturbances regional systems need resilience against. Here, perhaps more than anywhere else, world-systems analysis could strengthen work within the resilience conceptual framework.
The panarchical perspective has also had little to say about the long-term growth of world population, energy use and polity size, and the power of technology available for human use. As with the comparative neglect of conflict and elite dynamics, this is perhaps unsurprising, given its disciplinary roots in economics, ecosystem science, institutional research, and adaptive complex system theory (Holling 2003). However, all these factors have enormous implications for the past and future development of social-ecological systems at all scales.
The cumulative nature of technological development and its ability to construct successive layers of designed novelty differentiate it from the nested adaptive cycles of panarchy, although there are cyclic aspects to the replacement of one technical or socio-technical regime by another (Smith 2003, van der Brugge et al. 2005), and techniques can be lost or abandoned. Technological development has seemingly tended to accelerate. Chronologies of major technological innovations usually become denser toward the present (Modis 2002), but this could be because of the differential availability of information, or the perception of which innovations are important. However, there is another line of evidence: long-term human population growth. Until the 1970s, the proportional rate of growth rose almost monotonically for 2000 yr (Johansen and Sornette 2001), and probably far longer (Kremer 1993). This is explicable if population density has been limited by available technology, and larger populations innovate faster as evidence from Kremer (1993) indicates, perhaps simply because in total they give more time to it.
The analysis above does not mean population growth and innovation can accelerate indefinitely. Cohen (1995) explores the consequences of assuming that population growth rate will rise with the spare carrying capacity for additional population, while population growth will, via innovation, increase carrying capacity. This can imply either a singularity, with infinite population reached in a finite time, endless exponential growth, or super-exponential growth giving way to logistic growth so that the population levels off, depending on how innovation’s ability to increase carrying capacity itself changes with increasing population.
Such models depend on innovations being able to spread across a population. Koratayev (2005) notes that, by the first millennium BCE, iron metallurgy was able to spread from its southwest Asian origin to the Atlantic and Pacific coasts of Afroeurasia within a few centuries. Because iron axes and plows are far more efficient than earlier forest-clearing and tillage tools, this must have transformed agro-ecosystems across much of the Earth. Pacey (1990) details extensive technological exchanges between Afroeurasian civilizations in the period 700–1450 CE. Thus the Afroeurasian regions, which include most of the Earth’s population, have in terms of technical innovation formed a single, although decentralized, system for millennia. The history of innovation challenges the linkage of “small” with “fast” and “large” with “slow” in descriptions of panarchies; human social and technical systems have often become larger and faster-changing simultaneously. Clear examples come from historical changes in communication and transport networks. In recent centuries, largely European-derived changes in transport, communication, and military technologies have drastically reduced the autonomy of regional-scale systems.
Of the work cited above, only Koratayev (2005) derives directly from a world-systems perspective. Moreover, the apparent direct influence of population size on innovation speed requires an addition to the iteration model of world-system evolution. World-systems analysis has stressed institutional more than technological change, and in this regard may require some rebalancing, but it has been much more alive than panarchist researchers to the work on technological change described above.
Whereas studies cited earlier show that significant work on regional social-ecological systems from a world-systems perspective is under way, there is nothing to match the breadth and depth of regional studies or of comparative work on thresholds and regime change within the resilience conceptual framework. Moreover, although the two frameworks share a concern with the factors that make for stability or instability in systems, and specifically the insight that measures taken to preserve a desired system feature can lead to eventual collapse and radical reconfiguration of the system, the developing theoretical and empirical work on the assessment of system resilience (Carpenter et al. 2005, Cumming et al. 2005) has no world-systems parallel.
World-systems analysis also has problems that have no relation whatsoever to panarchy. One is the difficulty of operationalizing the semi-periphery concept; Chase-Dunn and Hall (1997a), provide five overlapping meanings for the term. Another relates to the significance, timing, and underlying mechanisms of Kondratieff, hegemonic, and other cycles. The mechanism of Kondratieff cycles has not been agreed upon even by those who accept their existence, and, although most world-systems theorists accept the Dutch Republic, UK, and United States as successive hegemons, some (e.g., Modelski 2000) trace the series even further back. Furthermore, it is clear that the successive instances of hegemony were very different. In particular, the Dutch Republic’s peak share of global economic activity was much less than the UK’s, and the latter was much less than that of the United States. Again, although all world-system networks are said to pulsate and all but kin-based world-systems are considered to have cycles of centralization and decentralization (Chase-Dunn and Hall 1997a:251), detailed mechanisms and the degree of regularity to be expected have not been established. A third such weakness concerns the relationship of population to innovation. Aside from the point made above, the demographic transition, which has led to declining populations in some core states, does not appear to fit the iteration model, even when it is modified to take into account innovation without population pressure under capitalism.
In summary, the panarchical framework and world-systems analysis each have weaknesses the other does not address, and they perhaps share an excessive expectation that homologous cyclic patterns of change will recur across a wide range of situations, given the absence of sufficiently well-specified mechanisms underlying these cyclic patterns. However, the two have strengths in complementary areas, suggesting considerable potential for synergy. Existing work in both traditions (e.g., Bunker 2003, Allison and Hobbs 2004) shows what can be done when analyses of planetary and regional scales and of ecology, politics, and technology are integrated.
Holling (2004) assesses the possibility of using the ideas that are central to panarchy, developed on a regional scale, to help explain the changes that are being brought about on a global scale by the Internet and by climate, economic, and geopolitical changes. He suggests that the “international world of nations” entered the backloop Ω and α phases of an adaptive cycle with the 1989 fall of the Berlin Wall. However, the subsequent years have seen continued economic growth, technical intensification, growth of transnational corporations, and primacy of the United States; all these date at latest from 1945 and appeared most threatened during the 1970s with the American defeat in Indo-China, the oil shocks, and “stagflation.” Holling identifies the Internet as a backloop phenomenon and regards the “global interconnected communications-driven revolution” as a third major transformation after the agricultural and industrial revolutions. However, this has been a very long revolution, under way, in successive waves, for more than two centuries when we consider the telegraph (first visual, then electric), telephone, radio, and television.
It seems impossible to assign the planetary social-ecological system convincingly to any phase of the adaptive cycle. Connectedness and certain kinds of potential are rising, and resilience is probably falling, suggesting that we are in a K phase. At the same time, continuing rapid innovation suggests an r phase, whereas the growing release of stored energy from fossil fuels, plus soil erosion, extinctions, and deforestation would seem to indicate Ω. In contrast, although they disagree on much else, Berry (2000), Devezas et al. (2005), and the world-systems analyst Goldstein (2006) agree that the Kondratieff cycle should produce rising growth and inflation, and technological diffusion rather than radical innovation, over the next decade or more.
Whether through war, full-scale ecological collapse, or a technological and/or socio-political revolution, it seems certain, as Holling (2004) notes, that radical global change is coming in this century, but this is evident even without the panarchical perspective. We urgently need the scientific tools to understand the range of possibilities open to us. Combining the panarchical perspective’s strengths at the regional scale and its key concept of resilience with the insights of world-systems theory could yield an understanding neither can provide alone. This paper ends by sketching a research program within which this could be attempted.
A suggested research program
Crosby (2004) shows how European imperialism, dependent on technical developments, both led to and was facilitated by the introduction, both deliberate and accidental, of European organisms to the “neo-Europes” of Australasia and temperate America, transforming them ecologically as well as socially and technically. This “Great European Land-Grab” is neither a Revolt nor a Remember connection, but rather a takeover of many autonomous systems by a more innovative system at the same hierarchical level. Holling et al. (2002c:96) refer to Crosby’s work, but only with regard to societies that collapse under the effects of both ecological and economic imperialism. The dynamics producing this imperial expansion and those of the resulting expanded system remain unexamined, although it is this system, the focus of world-systems approaches, that we all inhabit.
As Holling et al. (2002b) argue, one road to understanding current global change is by analogy with past events. They propose finding such analogies in regional systems that have collapsed and recovered in the recent past, and these could indeed be fruitful. However, the Great European Land-Grab was a planetary-scale process; if it leads to collapse, there is no containing system from which to draw resources for recovery. It revolutionized global distributions of societies, technologies, and agro-ecosystems and has imposed strong, directional change on effectively all recent regional systems.
The scientific study of unique events is always difficult, but two potential strategies are to find events that share as many of their most important features as possible and to compare spatio-temporally defined parts of such events with each other. To follow the first strategy, I suggest seeking other situations in which populations from a large, rapidly innovating social-ecological system exploited new opportunities to cross long-established boundaries and invade more stable regions, subjecting those regions, and sometimes themselves, to profound transformation. Chase-Dunn and Hall (1997a) have already compared the western European rise to core status and the subsequent expansion of the world-system with other world-system expansions and mergers, and other cases of semi-peripheral rise, but say rather little about the ecological aspects of these events.
Within human history and prehistory, the following sources of case studies are suggested:
Studying the similarities and differences between these and other episodes of radical change involving the transgression of long-established boundaries between social-ecological systems is perhaps our best hope of understanding current global turbulence and hence improving our survival prospects.
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ACKNOWLEDGMENTSWork for this paper was funded by the Scottish Executive Environment and Rural Affairs Department under the "Environment - Land Use and Rural Stewardship" Programme, and by the European Commission under the Sixth Framework Programme CAVES project, no. 012816. Thanks to Robin Matthews and two anonymous referees for useful comments on earlier versions.
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