Dams: Their Impacts on Coastal Environments

The Problem

  • Though long viewed as a benign alternative to other forms of power generation, dams and their reservoirs have been implicated in a wide range of environmental effects including, among many, release of toxic mercury into food webs; emissions of greenhouse gases; severe alteration of rivers, deltas and estuaries; increased coastal erosion; reduced biodiversity and fisheries productivity; and changes in coastal phytoplankton dynamics. One scientific study even estimated that the concentration of reservoirs built at higher latitudes over the last 40 years has caused the earth to spin faster.
  • Dams and water diversions have degraded or rendered inaccessible large areas of critical spawning habitat for salmon and ocher anadromous fish in the U.S. The Atlantic salmon had virtually disappeared from the Connecticut River, the largest river in New England, by 1814 due to a dam constructed upstream in 1798. Salmon catches in Maine averaged 150,000 lbs per year during the late 1800s, but, by 1925, the species was only found in two rivers. Hydropower development is one of the main factors in the decimation of many Pacific salmonid populations, though fisheries, agriculture, logging, mining, the release of hatchery fish, and water pollution have played important roles. Snake River adult chinook salmon, for example, declined from over 1,500,000 individuals during the 1800s to less than 2,000 in 1994. At least 106 major populations of west coast salmon and steelhead are now extinct, and many others are at high risk.
  • Dams and levees inhibit the transport of sediments required to prevent coastal erosion. For example, the Mississippi River now carries only half of its original sediment load which has contributed to the extensive loss of Louisiana's wetlands. Prior to 1930, the Colorado River supplied an estimated 125-150 million tons of suspended sediment to its delta at the Gulf of California; now no sediment (or freshwater) from this river ever reaches the sea.
  • The reduction of freshwater flow into estuaries can reduce their naturally high productivity and species diversity. This occurs via declines in essential nutrient input, alterations to the salinity regime, and increasing the concentrations of toxic chemicals entering the system. Reduced flows can also result in the "drying out" of wetlands and upstream salt water intrusion. The alteration of flood cycles and runoff patterns also affects those biological processes attuned to seasonal flow dynamics.

The Causes

  • Globally, there are approximately 39,000 large dams worldwide with some 193,500 sq mi of land (approximately twice the area covered by the Great Lakes) now inundated by their reservoirs. As of 1990, approximately 13% of freshwater carried by the world's rivers-and ultimately to the ocean-was dammed: this amount is expected to rise to over 20% by early next century.
  • Virtually every river in the contiguous US. is now regulated by dams, locks, or diversions. Currently there are more than 75,000 dams higher than six feet in the U.S. with the reservoirs behind them covering approximately 3% of the nation's land surface. In a given year, 60% of the entire river flow of the US. can be stored behind dams.
  • The vast majority of large dam construction occurred in the U.S. between 1935 and 1965, a time when there was minimal concern over the physical and biological consequences of reservoirs and alteration of downstream flows. Impacts on numerous U.S. estuaries and coastal environments of altered freshwater and sediment input regimes is still largely unquantified, but in many cases is expected to be substantial.

The Context

  • Dams and regulated rivers have provided various benefits for society including generation of electricity, and the reduction of devastating floods, as well as a controlled supply of water which can be used for alleviating drought and a variety of municipal and industrial demands. However, it is being increasingly recognized that dams constitute an important component in the overall degradation occurring in estuaries, deltas, and various nearshore environments.
  • Though smaller dams continue to be constructed, few large dams will ever again be built in the U.S. because of the few realistic sites available, high costs of construction, and increased public awareness of their negative effects.
  • Some downstream effects of dams can be mitigated by changes in dam operations such that normal seasonal flow rates are more accurately mimicked. A few dams in the U.S. are now slated for decommissioning because their environmental impacts are perceived to overwhelm any other societal benefits. Indeed, political support for the removal of environmentally problematic dams has increased dramatically in the past few years.

Further Reading

Collier, M., R.H. Webb, and J.C. Schmidt. 1996. Dams and Rivers - A primer on the downstream effects of dams. US. Geological Survey Circular 1126. Tucson, Arizona.

Kowalewski, M., Avila-Serrano, G.E., Flessa, K.W., and Goodfriend, G.A. Dead delta's former productivity: Two trillion shells at the mouth of the Colorado River. Geology 28(12): 1059-1062.

Milliman, J.D. 1997. Blessed dams or damned dams? Nature 386: 325-327.

Rosenberg, D.M., F. Berkes, R.A. Bodaly, R.E. Hecky, C.A. Kelly and JWM Rudd. 1997. Large-scale impacts of hydroelectric development. Environmental Reviews 5: 27-54.

Rosenberg, D.M., McCully, P., and Pringle, C.M. 2000. Global-scale environmental effects of hydrological alterations: Introduction. Bioscience 50(9): 746-751.

Sahagian, D. 2000. Global physical effects of anthropogenic hydrological alterations: sea level and water redistribution. Global and Planetary Change 25(1-2): 39-48.