Between 1980 and 2000, the impoundment has trapped an average of 5000 tonnes of sediment per year (Fig. 9). For comparison, the Lower Cuyahoga River suspended sediment load was about 65,000 tonnes yr−1 between 1980 and 2000 (Richards et al., 2008). Therefore, the Middle Cuyahoga River sediment load represents

only about 8% of the Lower Cuyahoga River sediment load. The important sediment sources, and need for dredging the port, lie downstream of the Selleckchem JQ1 Gorge Dam with drainage from the City of Akron and the Ohio-Erie Canal, major tributaries (i.e., Little Cuyahoga River, Furnace Run, Mud Brook, Yellow Creek, Tinkers Creek) and numerous smaller tributaries in the steep-side Cuyahoga Valley National Park. This study suggests that removing the Gorge Dam will not have a significant impact on the dredging needs at the Port of Cleveland. The downstream sediment impacts following dam removal may range from minimal, as described here, to significant. The amount and rate of sediment trapped in a dam pool is dependent on individual site characteristics including

watershed relief, bedrock type, vegetation, land use, climate as well as the trapping efficiency of the dam pool itself. Therefore site-specific studies, such as the one described here, are required to assess the future increase in downstream sediment load following dam removal. Through detailed study of dam pool sediment new insight on past and present watershed practices that affect

http://www.selleckchem.com/products/ABT-888.html sediment yield and sediment type can Carnitine dehydrogenase be obtained. This information is critically important to watershed management, where the focus is often on sediment reduction to improve habitat and to reduce chemical pollution loading. This study of the Gorge Dam impoundment provides a century-long record of anthropogenic and natural changes that have occurred in the Middle Cuyahoga Watershed. The first period spans the years 1912–1926 and is characterized by mud with high trace metal content from the industries and anthropogenic activities that were well-established along the river upstream of the impoundment. The second period spans the years 1926–1978 and is defined by sediment having abundant CCP from the nearby power plant and high trace metals from activities throughout the watershed. During this period, sediment accumulation increased due to development in the watershed. The third period spans the years 1978 to 2011 when both trace metals and CCP decrease dramatically in the dam pool sediments reflecting the effectiveness of environmental regulations. The Middle Cuyahoga River sediment load increased dramatically between 2004 and 2008, and again in 2011 as a result of an increase in extreme flow events, and the erosion of upstream sediment following the removal of the Munroe Falls Dam in 2005. The Middle Cuyahoga River sediment load as determined from the impounded sediment accumulation is similar to the STEPL model estimate.