Abstract
Observation and measurement of the ocean's ecosystems is demanding and costly. It makes verification of our theories difficult and forces us to engage in collective action based upon often very imperfect concepts of the dynamics of the system. Once we establish the institutions of col-lective action we adopt 'official' conceptions of system dynamics and generate expectations about how the natural system will react to our collective actions. In response individuals invest-ment in skills, knowledge, capital, technology, business plans, scientific agendas and so on. The self-interest reflected in these investments filters the amount and the quality of private information provided to the public so that it is consistent with the self-interest of agents who acquire that information. This limits and biases the private information available to managers. If the system being managed is simple (or if we think it is) and the costs of data collection minor, these impairments are not of any account (or we may think they are not); under these circumstance, a public science body should be able to gather whatever information is necessary for continuing adaptive governance. In a complex system, however, these impairments deprive the governance process of valuable information, and reduce the scope of collective action (the set of feasible rules). This creates path dependent lock-in that reduces adaptive capacity, generating, thereby, the circumstances for still another tragedy. Our way out of this dilemma rests in an understanding of the limits of our ability to predict and control natural systems. We are most able to predict a response to our actions at broad, slow moving ecological scales, e.g., a single stock of fish next year. Consequently, we gravitate towards institutional solutions that cater to that predictive ability. But these kinds of solutions impair feedback and make us vulnerable to surprises that develop over a longer period of time and at finer ecological scales. Maintaining adaptive capacity, consequently, means moving toward institutions that are less specific and longer-term, i.e., multi-scale and system based. This tends to improve feedback by reduc-ing the bias and increasing the breadth of private information provided to the public. This cannot be accomplished, however, without taking into account the constraints on the efficient flow of information within institutions/organizations. Recognizing these limita-tions is the other part of our way out. In particular, we cannot afford to base governance on a centralized organization that operates only at a broad scale; by doing so, we misalign private incentives and social objectives, incur very high enforcement costs, forfeit the ability to use a broad range of policies necessary for sustainability and, overall, create an environment in which information about the environment and the impact of our activities is very costly
Highlights
Many of the lessons we have learned in the ocean fishery commons replicate the lessons we have learned elsewhere in terrestrial and other commons (Defeo and Castilla 2005; Acheson 2003; Netting 1981; Ostrom 2007)
Observation and measurement of the ocean’s ecosystems is difficult and costly. It makes verification of our theories difficult and forces us to engage in collective action based upon often very imperfect concepts of the dynamics of the system
Once we establish the institutions of collective action, we adopt ‘official’ conceptions of system dynamics that define the bounds of individual action
Summary
Many of the lessons we have learned in the ocean fishery commons replicate the lessons we have learned elsewhere in terrestrial and other commons (Defeo and Castilla 2005; Acheson 2003; Netting 1981; Ostrom 2007). As a result, is viewed as possible only in the near-term (when it is mostly a matter of short-term extrapolation rather than causality based prediction); longer-term predictability (which is what is relevant to sustainability) is assumed feasible but only in the sense of maintaining broad ecological processes (rather than species specific numerical outcomes) These perceived limitations on predictability and on the ability to control the system inclines practitioners of this perspective towards policies designed to maintain system wide conditions, e.g., predator-prey relationships, population age structure, and habitat, that determine the patterns and dynamics of the system. The principal differences between the classical population and the ecological views come down to the temporal, spatial, and ecological scales at which qualitative understanding, numerical predictability and control, or the ability to influence the system are assumed to be practical This leads to different ideas about what is necessary for sustainability and, especially in systems that have been seriously eroded by fishing and other human activity, different ideas about policies that might rebuild individual stocks and restore ecological processes. These lead to different views about the institutional arrangements necessary to achieve those ends
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