A comparison of past small dam removals in highly sediment-impacted systems in the U.S.
Highlights
► This study analyzes the evolution of reservoir sediments following dam removal. ► We examine the role of local conditions on rates, volumes, and processes of erosion. ► Cohesive and fine sediment deposits show reduced rates and volumes of erosion. ► Watershed sediment yields provide a satisfactory estimate of initial erosion rates. ► Interactions between multiple variables best describes deposit evolution processes.
Introduction
There have been over 700 documented dam removals or decommissions in the past century (Gleick et al., 2009), with upwards of 350 such removals having occurred in the last decade (American Rivers, 2009). With dam removal continuing to increase in popularity and an inventory of over 80,000 registered dams in the United States (FEMA, 2009), there is a definite need for a set of reliable tools capable of predicting the geomorphic effects of the many dam removals to come. The potential geomorphic effects of dam removal are most extreme in situations where reservoirs have been substantially filled with deposited sediments that are then left to erode naturally via streamflow after removal. The fate of these deposited sediments following dam demolition is acknowledged as being the most poorly understood aspect of dam removal projects (Heinz Center, 2002, Stewart and Grant, 2005). There are numerous process-based models, conceptual (Doyle et al., 2002, Pizzuto, 2002) and numerical (Cui et al., 2006a, Cui et al., 2006b, Greimann and Huang, 2006, Langendoen, 2010), that have been developed over the past decade to predict the erosion and evolution of stored reservoir sediments following dam removal. However, comparison of model-generated predictions of deposit evolution following dam removal to actual post-removal monitoring data is quite rare. In studies where such testing of forecasts has been done, comparisons are made with only one or two removal cases. Most published dam removal studies deal specifically with the analysis of data gathered from individual removal projects. In a few instances, multiple removals have been monitored and compared in a single study (Doyle et al., 2003a, Wildman and MacBroom, 2005), and occasionally there has been some comparison of results from a new removal project with those of past removals (Riggsbee et al., 2007). However, in general there appears to be a significant lack of comparative analysis of post-removal monitoring data, particularly of the evolution of highly sediment-filled reservoirs following dam removal. Fortunately, as the number of independent case studies has grown over the past decade, so too has our ability to learn from, and make use of, the numerous data sets that are now available (Stewart and Grant, 2005, Kibler et al., 2010).
Included in the need for a broad comparison of currently available dam removal data sets is the need to test and validate some of the most basic concepts regarding which parameters are most influential in determining rates and volumes of streamflow-driven deposit erosion. Because of concerns over downstream channel and ecological impacts, stabilization of reservoir deposits, new channel development, and other issues (Grant, 2001, Heinz Center, 2002), a major question surrounding natural erosion of stored reservoir sediments is the volume, rate, and timing of their release following dam removal. Relatively accessible variables such as deposit geometry, sediment grain size and level of cohesion, and annual watershed sediment yield have long been suggested to have specific impacts on the erosional processes that determine the rate, volume, and form of deposit evolution (Harbor, 1993, Egan, 2001, Doyle et al., 2002, Pizzuto, 2002, Stewart and Grant, 2005). With the empirical support of the compiled data sets presented in this paper, we are able to identify the influence of specific parameters on the evolution of stored sediment deposits following dam removal.
Section snippets
Study sites
Although hundreds of dams have been removed within the last two decades, the results of only a surprisingly small percentage of these projects have been published. As of 2002, fewer than 5% of all removals had been published in the scientific literature (Hart et al., 2002). Of the few published studies available, there are even fewer that involve highly sediment-impacted systems. Furthermore, the amount and quality of post-removal monitoring data varies considerably from study to study.
Twelve
Approach
Because of the relative infancy of the practice of dam removal, there has yet to be a well-developed set of case studies with which to test hypotheses and gain knowledge regarding the drivers of deposit evolution over time and under varying conditions. Conceptual predictions of deposit evolution have primarily come from two sources. Originally, analogies between dam removal and more fundamental fluvial geomorphological processes were made (Doyle et al., 2002, Doyle et al., 2003a). Similarities
Sediment properties
In this section we look at the influence of sediment properties on the evolution of reservoir deposits. The primary sediment properties of interest are level of cohesion, consolidation, and grain size. The potential influences of sediment properties on deposit evolution are well documented (Egan, 2001, Pizzuto, 2002, Doyle et al., 2003a, Doyle et al., 2003b, Stewart and Grant, 2005). The level of cohesion and grain size of sediments are directly connected to the erodibility of the material,
Summary and conclusions
We have attempted to identify and validate the potential influences that specific parameters have on the relative rates and volumes of reservoir deposit erosion following small dam removal. Through the compilation of 12 case studies of primarily low head dam removal projects in northern latitudes of the continental U.S., we have assembled a data set that allows for the direct comparison of the results of the individual removals. An analysis of this data set supports some previous notions as
Acknowledgments
The authors are grateful for the financial support of the Landreth Family River Systems Fund of the Woods Institute for the Environment at Stanford University. The authors would also like to thank the following researchers for providing additional data and advice: Martin Doyle, Vicki Ozaki, Jim Evans, Timothy Straub, Cara Walter, and Mackenzie Keith.
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