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DAM REMOVAL 251 <br />Table II. Several past and proposed dam removals discussed in published work and reviewed here <br />Dam River State Date of Removal <br />Washington Water Power Dam South Fork of the Clearwater River Idaho Removed in 1962 <br />Fort Edward Dam Hudson River New York Removed in 1973 <br />Newaygo Dam Muskegon River Michigan Removed in 1969 <br />Woolen Mills Dam Milwaukee River Wisconsin Removed in 1988 <br />Salling Dam AuSable River Michigan Removed in 1992 <br />Columbia Falls Dam Pleasant River Maine Removed in 1989 <br />Savage Rapids Dam Rogue River Oregon Proposed <br />Edwards Dam Kennebec River Maine Proposed <br />Elwha and Glines Canyon dams Elwha River Washington Proposed <br />Rodman Dam Ocklawaha River Florida Proposed <br />The Fort Edward Dam on the Hudson River was removed in 1973. This removal provides some lessons <br />regarding dam removal and the need for comprehensive pre-removal environmental assessment studies. <br />Fort Edward Dam was a 9.1 m high and 180 m long rock and timber crib dam built in 1817, which was <br />near collapse at the time of removal. The owner, Niagara Mohawk Power Corporation, had received <br />an amendment to their licence from the Federal Power Commission (now the Federal Energy Regulatory <br />Commission) which authorized them to remove the dam. One year after removal, the US Army Corps of <br />Engineers documented sediment/debris blockage of the downstream Champlain Canal which connects the <br />Hudson River with Lake Champlain (FPC, 1977). Other areas of the Hudson River were also obstructed <br />by woody debris and sediment moved downstream after removal of the Fort Edward Dam. It was <br />estimated that 336 300 m3 of sediment had moved downstream in one year after removal of the dam, <br />and that 765 000 m3 remained in the floodplain above the dam after the first year of removal. After two <br />years of hearings it was concluded that Niagara Mohawk had complied with all dam removal authori- <br />zation requirements, except the condition to prevent or control water pollution resulting from removal <br />of the dam. It was also concluded that the pre-removal studies were insufficient and that monitoring of <br />sediments should be initiated. The State of New York appropriated $5 million for the clean-up of the <br />downstream materials eroded following removal of the Fort Edward Dam (FERC, 1978). Before removal <br />of the dam, polychlorinated biphenyls (PCBs) were discharged into the Hudson River just upstream <br />(ca. 6 km) from the dam (Tofliemire, 1986). Water levels in the Hudson River above the dam dropped <br />4-6m after dam removal, and downstream PCB transport has been monitored since the Fort Edward <br />Dam was removed. <br />Although completed over 20 years ago, the Fort Edward Dam removal provides cogent evidence as to why <br />comprehensive and holistic environmental assessments must be completed before a dam is removed. The <br />1977 Federal Power Commission ruling on this dam removal found that pre-removal studies must assess <br />the presence and potential movement of sediments and other materials both in the vicinity of the dam <br />and upstream in the reservoir. The judge also found that pre-removal studies must be more precise and <br />unambiguous to determine whether a dam removal should be authorized (FPC, 1977; Lewis, 1992). <br />Sediment movement was also observed following the 1969 removal of the Newaygo Dam on the <br />Muskegon River, Michigan. Removal of this dam resulted in the release of impounded sediment which <br />immediately started migrating through the river channel as a sediment wave (Simons and Simons, 1991). <br />As the sediment conditions before dam removal were unknown, a mathematical model was developed to <br />determine the sediment transport and geomorphic changes that have occurred in the system since dam <br />removal and those expected in the future. The dominant physical processes important to dam removal <br />and incorporated in the model included the flow of water, sediment transport, sediment routing, degrada- <br />tion, aggradation and bed control due to armouring. It was estimated. that about 40% of the original <br />volume of impounded sediment was washed downstream immediately after removal of the dam. The remain- <br />ing sediment is moving downstream as a sediment wave at approximately 1.6 km per year. With time, the