Abstract:About a decade ago, the Netherlands Environmental Assessment Agency (PBL) unwittingly embarked on a transition from a technocratic model of science advising to the paradigm of “post-normal science” (PNS). In response to a scandal around uncertainty management in 1999, a Guidance for “Uncertainty Assessment and Communication” was developed with advice from the initiators of the PNS concept and was introduced in 2003. This was followed in 2007 by a “Stakeholder Participation” Guidance. In this article, the autho… Show more
“…Implicit disclosure and the use of such vague terminology not only makes uncertainty classifications presented in the academic literature (e.g., Tennøy, Kvaerner, and Gjerstad 2006;Walker et al 2003;De Jongh 1988) difficult to apply, if not impractical, it also poses challenges to regulatory decision makers in trying to identify whether and where uncertainty exists and how significant these uncertainties are with respect to a project's approval or approval conditions. Consistent with Larsen, Kørnøv, and Driscoll (2013) and Petersen et al (2011), we suggest there is a need for improved understanding of, consistency among, and transparency of uncertainty reporting practices by those involved in the EA process. The Committee on Decision Making Under Uncertainty (2013), for example, suggests that to successfully communicate uncertainty there is a need to develop communication plans and strategies that are sensitive to the needs of stakeholders and decision makers À in this case affected communities and regulatory agencies.…”
Identifying and communicating uncertainty is core to effective environmental assessment (EA). This study evaluates the extent to which uncertainties are considered and addressed in Canadian EA practice. We reviewed the environmental protection plans, follow-up programs, and panel reports (where applicable) of 12 EAs between 1995 and 2012. The types of uncertainties and levels of disclosure varied greatly. When uncertainties were acknowledged, practitioners adopted five different approaches to address them. However, uncertainties were never discussed or addressed in depth. We found a lack of suitable terminology and consistency in how uncertainties are disclosed, reflecting the need for explicit guidance, and we present recommendations for improvement. Canadian Environmental Impact Statements are not as transparent with respect to uncertainties as they should be, and uncertainties in EA need to be better considered and communicated.
“…Implicit disclosure and the use of such vague terminology not only makes uncertainty classifications presented in the academic literature (e.g., Tennøy, Kvaerner, and Gjerstad 2006;Walker et al 2003;De Jongh 1988) difficult to apply, if not impractical, it also poses challenges to regulatory decision makers in trying to identify whether and where uncertainty exists and how significant these uncertainties are with respect to a project's approval or approval conditions. Consistent with Larsen, Kørnøv, and Driscoll (2013) and Petersen et al (2011), we suggest there is a need for improved understanding of, consistency among, and transparency of uncertainty reporting practices by those involved in the EA process. The Committee on Decision Making Under Uncertainty (2013), for example, suggests that to successfully communicate uncertainty there is a need to develop communication plans and strategies that are sensitive to the needs of stakeholders and decision makers À in this case affected communities and regulatory agencies.…”
Identifying and communicating uncertainty is core to effective environmental assessment (EA). This study evaluates the extent to which uncertainties are considered and addressed in Canadian EA practice. We reviewed the environmental protection plans, follow-up programs, and panel reports (where applicable) of 12 EAs between 1995 and 2012. The types of uncertainties and levels of disclosure varied greatly. When uncertainties were acknowledged, practitioners adopted five different approaches to address them. However, uncertainties were never discussed or addressed in depth. We found a lack of suitable terminology and consistency in how uncertainties are disclosed, reflecting the need for explicit guidance, and we present recommendations for improvement. Canadian Environmental Impact Statements are not as transparent with respect to uncertainties as they should be, and uncertainties in EA need to be better considered and communicated.
“…The argument is therefore that rational decision-making is neither typical of proposals subject to IA, nor appropriate (Kørnøv and Thissen, 2000). Furthermore, Petersen et al (2011Petersen et al ( ) describe a "scandal around uncertainty management in 1999 in the Netherlands Environmental Assessment Agency, whereby a senior statistician in the Agency published a national newspaper article criticising their approach of relying heavily on computer models without real measurements to back them up, providing unrealistic accuracy claims (i.e. hiding uncertainty).…”
Section: Figurementioning
confidence: 99%
“…This threatened the Agency's funding and resulted in them attempting to introduce a post-normal science approach to their work via guidance on uncertainty assessment and communication, and guidance on stakeholder participation; albeit they conclude that changing the mind-sets of their staff is a longer-term prospect. This example typifies the field of IA which is traditionally very technocratic, embedded in a utopian rationalist view of the role of science in policy (Petersen et al, 2011) which argues that the assimilation of scientific, value-free information, should influence policy outcomesdespite the evidence to the contrary. This view of IA is institutionalised which, as the Netherlands Environmental Assessment Agency found, makes any redirection a 'scandal'.…”
In the context of continuing uncertainty, ambiguity and ignorance in impact assessment (IA) prediction, the case is made that existing IA processes are based on false 'normal' assumptions that science can solve problems and transfer knowledge into policy. Instead, a 'post-normal science' approach is needed that acknowledges the limits of current levels of scientific understanding. We argue that this can be achieved through embedding evolutionary resilience into IA; using participatory workshops; and emphasizing adaptive management. The goal is an IA process capable of informing policy choices in the face of uncertain influences acting on socio-ecological systems. We propose a specific set of process steps to operationalise this post-normal science approach which draws on work undertaken by the Resilience Alliance. This process differs significantly from current models of IA, as it has a far greater focus on avoidance of, or adaptation to (through incorporating adaptive management subsequent to decisions), unwanted future scenarios rather than a focus on the identification of the implications of a single preferred vision. Implementing such a process * corresponding author 2 would represent a culture change in IA practice as a lack of knowledge is assumed and explicit, and forms the basis of future planning activity, rather than being ignored.
“…Saloranta, 2001); and to 122 explain the processes of science in practice in the light of PNS (e.g. Turnpenny Lorenzoni and 123 Jones, 2009; Petersen et al, 2011). Among the more enduring debates about PNS is the 124 extent to which it represents a normative framework for scientific practice and its links to 125 policy, or rather, is a theoretical model, a description or a heuristic (Farrell, 2011) that offers 126 an explanatory framework for this interaction as it happens in practice.…”
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