Comparing stakeholder perceptions with empirical outcomes from negotiated rulemaking policies: Is participant satisfaction a proxy for policy success?
Introduction
The U.S. federal government involves the public in regulation of natural resources along a continuum of engagement. At one end lies the command and control method wherein an administrative agency proposes regulations, releases them for public comment, modifies those rules in response, and implements final rules. At the other end of the continuum, stakeholders work directly with administrative agencies to devise regulations through consensus-based, multi-party negotiation, referred to as negotiated rulemaking [1], [2]. Various environmental agencies in the U.S. have embraced the latter approach, including the Environmental Protection Agency, Department of the Interior, and National Oceanic and Atmospheric Administration (NOAA) [3].
Assessing the efficacy of a policy in relation to program goals is fundamental to policy evaluation [4]. One critical metric of resource policy evaluation is whether the policy resulted in the intended goal, which is to improve resource condition, quality and quantity. However, for policies that are designed to protect natural resources, long-term resource monitoring data often are lacking. In lieu of direct data on the resource, other evaluations for environmental policies generated by multi-stakeholder programs may focus solely on the success of the negotiation process, while others focus on outputs or agreements resulting from the negotiation. Other evaluations focus on participant satisfaction with the process, which affects satisfaction with the outputs [5], [6]. Participant satisfaction, however, may not be a good measure, proxy, or indicator of successful ecological outcomes [3], [7], [8], [9], [10], [11]. Coglianese [9] points out that to avoid cognitive dissonance, stakeholders involved in intensive participatory processes such as negotiated rulemaking, may have a more positive view of the outcomes than is warranted by the outcomes themselves [5]. To date, few studies have considered how well stakeholder perceptions align with empirical trends [3], [9], [11], [12]. In other words, few studies have examined whether stakeholder perceptions of mission success or failure are accurate.
One negotiated rulemaking program administered by NOAA is mandated by the Marine Mammal Protection Act of 1972 (MMPA 16 U.S.C. 1361 et seq.). This negotiated rulemaking process, called Take Reduction Planning, develops plans that are designed to reduce harmful interactions between marine mammals and commercial fisheries (16 U.S.C. 1387).
The Take Reduction Planning program of the MMPA requires both long-term monitoring and negotiated rulemaking to mitigate the incidental capture of marine mammals in fisheries (bycatch). A recent study of the MMPA Take Reduction process found that the policy led to measurable empirical reductions in marine mammal bycatch, often referred to as takes [13]. To better understand the relationship between perceived and empirical ecological outcomes, this study quantitatively and qualitatively compares empirical ecological outcomes of marine mammal Take Reduction Plans [13] in relation to stakeholder's perceived outcomes [5]. This study serves to characterize the strength of the relationship between perceived and actual ecological success, directly informing the suitability of participant perceptions as a reliable proxy for empirical policy success.
Section snippets
Background: Marine Mammal Act Take Reduction Planning
Multi-stakeholder Marine Mammal Take Reduction Teams are charged with devising a consensus-based Take Reduction Plan comprising regulatory and non-regulatory measures to mitigate marine mammal bycatch (16 U.S.C. 1387(f)(6)(A)(i)). Take Reduction Teams consist of environmentalists, members of the fishing industry (fishermen, lobbyists, and industry group representatives), scientific researchers, members of Regional Fisheries Management Councils and Commissions, and state and federal managers (16
Empirical ecological outcomes
Quantitative metrics of ecological outcomes from the Take Reduction planning process were based on findings from a recent paper [13], which evaluated the ecological outcomes or success of the Take Reduction planning process of the MMPA. Using data from Marine Mammal Stock Assessment Reports, McDonald et al. [13] ranked the ecological outcomes of five Take Reduction Plans (Atlantic Large Whale, Bottlenose Dolphin, Harbor Porpoise, Pacific Offshore Cetaceans, and Pelagic Longline) by comparing
Ecological analyses
The full database, including both social and ecological data contained 212 records. The empirical ecological effectiveness of marine mammal Take Reduction Plans varied considerably across teams (Table 2) [13]. Relative rankings among the plans also differed slightly between Metrics 1 and 2 (Table 2). Metric 1 ranked the Bottlenose Dolphin and Pacific Offshore Cetaceans plans as the two highest (most effective ecologically). Metric 2 ranked the Bottlenose Dolphin plan (minimum bycatch estimate1)
Discussion
This study characterized, both quantitatively and qualitatively, the relationship between the perceived and empirical ecological outcomes of a policy instrument that governs regulations and voluntary measures created by multi-stakeholder negotiation. This relationship has been discussed theoretically [6] but the paucity of long-term, environmental datasets has precluded direct comparisons of empirical and perceived ecological outcomes. This study revealed that for the Marine Mammal Protection
Conclusions
This research is the first to compare the ecological outcomes of regulations generated by negotiated rulemaking with stakeholder perceptions about those outcomes, both quantitatively and qualitatively. This comparison is only possible because of a rigorous, long-term marine mammal monitoring program provided in the Stock Assessment Reports (http://www.nmfs.noaa.gov/pr/sars/species.htm). Despite its limitations, without the Stock Assessment Reports, there would be no ability to measure the
Acknowledgements
We thank the survey respondents for taking the time to participate in this research and sharing their views. We also thank the NMFS staff responsible for coordinating the Take Reduction Team meetings as well as the meeting facilitators for their openness to this research. Many thanks also to the Marine Mammal Commission (Award No. E4047333) and the Kenan Institute for Ethics for funding.
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Whose reality counts?