Abstract

Structural equation modeling (SEM) is increasingly being chosen by researchers as a framework for gaining scientific insights from the quantitative analyses of data. New ideas and methods emerging from the study of causality, influences from the field of graphical modeling, and advances in statistics are expanding the rigor, capability, and even purpose of SEM. Guidelines for implementing the expanded capabilities of SEM are currently lacking. In this paper we describe new developments in SEM that we believe constitute a third‐generation of the methodology. Most characteristic of this new approach is the generalization of the structural equation model as a causal graph. In this generalization, analyses are based on graph theoretic principles rather than analyses of matrices. Also, new devices such as metamodels and causal diagrams, as well as an increased emphasis on queries and probabilistic reasoning, are now included. Estimation under a graph theory framework permits the use of Bayesian or likelihood methods. The guidelines presented start from a declaration of the goals of the analysis. We then discuss how theory frames the modeling process, requirements for causal interpretation, model specification choices, selection of estimation method, model evaluation options, and use of queries, both to summarize retrospective results and for prospective analyses.The illustrative example presented involves monitoring data from wetlands on Mount Desert Island, home of Acadia National Park. Our presentation walks through the decision process involved in developing and evaluating models, as well as drawing inferences from the resulting prediction equations. In addition to evaluating hypotheses about the connections between human activities and biotic responses, we illustrate how the structural equation (SE) model can be queried to understand how interventions might take advantage of an environmental threshold to limit Typha invasions.The guidelines presented provide for an updated definition of the SEM process that subsumes the historical matrix approach under a graph‐theory implementation. The implementation is also designed to permit complex specifications and to be compatible with various estimation methods. Finally, they are meant to foster the use of probabilistic reasoning in both retrospective and prospective considerations of the quantitative implications of the results.

Highlights

  • IntroductionStructural equation modeling (when terms defined in the glossary in Box 1 are used for the first time, they are italicized) is a methodology increasingly used by those in the natural sciences to address questions about complex systems (Shipley 2000a, Grace 2006)

  • Structural equation modeling is a methodology increasingly used by those in the natural sciences to address questions about complex systems (Shipley 2000a, Grace 2006)

  • We added to the available information by quantifying degree and type of specific human disturbance activities in the vicinity of wetland catchments using a modification of the rating system developed for wetlands by the Ohio EPA (Mack 2001)

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Summary

Introduction

Structural equation modeling (when terms defined in the glossary in Box 1 are used for the first time, they are italicized) is a methodology increasingly used by those in the natural sciences to address questions about complex systems (Shipley 2000a, Grace 2006). The use of graphical modeling methods for the analysis of multivariate data permits the explicit expression of causal hypotheses. As a result of all these features, we feel that SEM has a unique and important role to play in quantitative science

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