ReviewMulti-criteria decision analysis in environmental sciences: Ten years of applications and trends
Highlights
► Comprehensive review of application of formal decision-analytical tools for environmental management is performed. ► Significant increase in the share of application of formal MCDA tools within all environmental applications is reported. ► Application of different MCDA methods to the same problem results in similar ranking of environmental management alternatives. ► MCDA tools found to be very useful for policy decision making.
Introduction
Environmental decisions are often complex and draw upon multidisciplinary knowledge bases which incorporate natural, physical social sciences, politics, and ethics. Environmental decision makers rely on many experimental tests, computational models, and tools to assess human health and ecological risks associated with environmental stressors and the impact of remedial and abatement strategies on risk reduction. However, applying these tools is becoming increasingly difficult for three reasons. First, there are many emerging risks (e.g., climate change, nanotechnology, etc.) for which information is not available and decisions should be made under significant uncertainty. Second, for many traditional stressors and situations multiple lines of evidence regarding the same measure (e.g., risk) are available, but they may point to different management alternatives. Finally, stakeholders, who may have vested interest in specific courses of action, are gaining increased access to all available information and, given the data uncertainty, can justify often opposing courses of action. As such, integration the heterogeneous and uncertain information demands a systematic and understandable framework to organize the technical information and requires expert judgment.
Multi-criteria decision analysis (MCDA) provides a systematic methodology to combine these inputs with cost/benefit information and stakeholder views to rank project alternatives. MCDA is used to discover and quantify decision maker and stakeholder considerations about various (mostly) non-monetary factors in order to compare alternative courses of action. There are numerous approaches that all fall under the umbrella of MCDA, each involving different protocols for eliciting inputs, structures to represent them, algorithms to combine them, and processes to interpret and use formal results in actual advising or decision making contexts. Linkov et al., 2004, Linkov et al., 2006 reviewed the application of MCDA in environmental management focusing on management of contaminated sites published in 1992–2002. MCDA techniques have been applied to optimize policy selection in the remediation of contaminated sites, the reduction of contaminants entering aquatic ecosystems, the optimization of water and coastal resources, and the management of other resources. In some of these studies, the researchers have explicitly taken into account the opinions of local community groups and other stakeholders through focus groups, surveys, and other techniques and formally integrated these opinions into the decision process. Many papers concluded that the application of MCDA methods provides a significant improvement in the decision process and public acceptance of the suggested remedial or abatement policy.
The last decade brought not only an increased interest in the application of formalized decision-analytical tools, but also better structured and complete databases. The goal of this paper is to review the recent literature and identify current trends in MCDA applications to environmental management, and to discuss the possible reasons that the various methods are gaining attention in different applications. In 2003, our search strategy was to find MCDA applications by all means, including searching gray literature. The current challenge was to limit the number of papers for the analysis to a manageable size but still objectively represent the state of the applications. Similar to Linkov et al. (2004), we consider three main MCDA approaches: MAUT, Outranking (including PROMETHEE and ELECTRE), and AHP. These approaches share common mathematical elements, i.e., values for alternatives are assigned for a number of dimensions, and then multiplied by weights and finally combined to produce a total score. The approaches differ significantly in the details of how values are assigned and combined, meaning that the processes have different information – and knowledge – requirements and the calculated scores have different mathematical properties and thus slightly different meanings. Practitioners often view one of the various approaches as most appropriate due to the priority they place on its relative strengths and weaknesses. (e.g., Figueira et al., 2005, Belton and Stewart, 2002).
Section snippets
MCDA methods
MCDA approaches typically require as inputs: scores across several dimensions associated with different alternatives and outcomes; weights relating to tradeoffs across these dimensions. A basic but typical approach is to calculate the total value score for an alternative as a linear weighted sum of its scores across several criteria, i.e., V = Σi wixi, where Σi wi = 1. Also common (though not universal) is a hierarchical structure (as in value hierarchies described in Keeney, 1992, and essential to
Literature review
Our goal was to conduct a state-of-the-application review of MCDA in the environmental field, identifying trends and tools to aid future decision makers in their applications. The growth of MCDA applications was examined over the last two decades, while detailed analysis of applications based on a developed taxonomy describing MCDA approaches practiced in the field was conducted for papers published in 2000–2009.
Results and discussion
This section starts with the analysis of historical environmental MCDA publishing trends in 1990–2010. A detailed analysis by specific MCDA method used and application area was conducted only for 2000–2009 time period. Proportions were calculated both ways to determine if either MCDA methods or application areas were disproportionately represented in a given field (Table 3, Table 4).
Summary
Our review shows that the application of MCDA tools in environmental science has grown significantly over the last two decades. Accounting for the overall growth in environmental publications between 1990 and 2009, we estimated a steady annual percentage growth with the fraction (or share) of MCDA papers increasing by a factor of 7.5. The growth rate was relatively slow but steady in 1990–1999, while significant acceleration is observed during the last decade. Even though the detailed analysis
Acknowledgments
We would like to thank Ms. Laure Canis for help in classifying the papers. Mr. Alex Tkachuk, Drs. Mayank Mohan and Todd Bridges provided helpful discussions and support. This effort was sponsored in part by the Dredging Operations Environmental Research (DOER) and Civil Works Basic Research Program by the U.S. Army Engineer Research and Development Center.
Permission was granted by the US Army Chief of Engineers to publish this information. The views and opinions expressed in this paper are
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