DEDICATIONI dedicate this thesis to my wife Rosa, whose hard work in caring for our new son Jesse has allowed me time to complete this project. I would also like to dedicate this thesis to Rosa's father, Washington Segura Bayas, a generous and hard-working man who tragically lost his life during the course of this study.I would like to thank the members of my committee for their technical support of this project. I thank Dr. Peter Frederick for his insightful advice regarding sampling design and field methods, wading bird foraging ecology, and several revisions of the thesis. I also thank Dr. Jerome Lorenz and Dr. Joel Trexler for their advice on sampling design and field methods. I thank Dr. Thomas Philippi for his financial assistance during pilot sampling in Ecuador and while working as a graduate assistant for several semesters as well as his assistance with sampling design and data analysis. Professor Thomas Philippi, Major Professor I compared wading bird foraging ecology in commercial shrimp ponds and natural mangrove mudflats in the Muisne River Estuary in northwest Ecuador. I estimated foraging habitat suitability by observing the foraging efficiency, diet, and behavior of great (Ardea alba) and snowy (Egretta thula) egrets, censusing birds, and measuring prey availability (i.e. prey density, standing crop, water depth, and diversity).Great egrets had greater foraging efficiency in shrimp ponds, while snowy egret foraging efficiency was greater on mudflats. Over 85% of prey items in snowy egret boluses were from shrimp ponds. Mean density, standing crop, length, and mass of prey items was significantly greater in shrimp ponds, but availability was limited by water depth and diversity. Great and snowy egrets utilized shrimp ponds as their primary foraging grounds, while all other diurnal wading bird species foraged primarily on mudflats, where the diversity of wading birds and their prey was greatest. As ecosystems throughout the world become increasingly impacted by anthropogenic change, the need to assess the significance of this influence on biodiversity and ecological functions is increasing (Kushlan 1993). Evaluating the ability of humanmodified landscapes to serve as surrogates for natural habitats for vertebrate animal populations is a current goal in conservation biology ( Wading birds regularly use anthropogenically disturbed habitats such as rice fields, aquaculture ponds, stormwater retention ponds, salt pans, refuse dumps, and nuclear reactor cooling reservoirs (Velasquez 1992; Bildstein et al. 1994, Richardson et al. 2001, Gawlik 2002. However, the relative suitability of these areas as surrogates for natural foraging grounds is often unknown, especially within the borders of developing nations. The intensity and spatial extent of the habitat alteration, the presence of suitable adjacent habitat, and the species life history characteristics (e.g. morphology, physiology, behavior) all contribute to the net ecological impact of habitat degradation on wading bird populations.Global concern has ...