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cities or other flood hazard damage-prone <br />areas (see generally papers in Chapter 7, this <br />volume). For example, the Corps of Engineers <br />acquired 8400 acres of wetland along the <br />Charles River north of Boston to reduce future <br />flood losses (Barron, this volume). <br />Flood conveyance. <br />Most riverine wetlands in or along river or <br />stream channels lie within the 100 year <br />"floodway" as defined by the Federal Emergency <br />Management Agency (FEMA) and other flood <br />management agencies. Such natural floodways <br />convey relatively high velocity waters from <br />upstream to downstream points during flooding. <br />FE14A regulations and the regulations adopted by <br />states and local governments in the U.S. <br />prohibit fills or other obstructions in flood- <br />ways which would cumulatively increase flood <br />heights 1 foot (FEMA regulations) or some <br />lesser figure (many state and local <br />regulations). <br />Erosion control. <br />Riverine wetlands help stabilize stream banks <br />and reduce stream meander by reducing the <br />velocity of water flowing through such wetlands <br />and by binding the soil. They also help trap <br />sediment (Greeson et al. 1979; Johnson et al. <br />1985). <br />Pollution control. <br />Riverine wetlands in and along channels play <br />disproportionately large roles (for their size) <br />in removing sediment, litter, and toxic <br />materials from rivers and streams (Greeson et <br />al. 1979; Mitsch and Gosselink 1986; Hammer, <br />this volume; Ferlow and Ferlow, this volume). <br />They also remove sediment. Because they lie <br />parallel to streams and partially in channels, <br />considerable quantities of pollutants may be <br />removed from water flowing through even narrow <br />bands of such wetlands over many miles. <br />However, some of this sediment and pollutants <br />may be resuspended during floods. <br />Fisheries. <br />Riverine wetlands provide spawning and rearing <br />habitat for pike and a variety of other fish. <br />In addition, floodplain wetlands provide <br />substantial food chain support during both <br />flood and normal river stages (Lambou, this <br />volume; Hall and Lambou, this volume; Thayer et <br />al., this volume; Hesse, this volume). <br />Waterfowl. <br />Riverine wetlands provide critical waterfowl <br />habitat including major "flyways" along the <br />major rivers of the U.S. (Johnson et al. 1985). <br />Other Wildlife. <br />Riverine wetlands and riparian habitat provide <br />critical habitat for a broad range of birds, <br />reptiles, amphibians, and small mammals (see, <br />e.g., Brack, this volume). <br />Recreation and aesthetics. <br />Riverine wetlands along navigable streams <br />provide aesthetic and recreational opportu- <br />nities for canoeing, kayaking, boating, hiking, <br />and other activities (e.g., Smardon, this <br />volume; Palmer, this volume; Pitt and Colton, <br />this volume). <br />River Characteristics Important to <br />Riverine Wetlands <br />Riverine wetland characteristics, functions, <br />and values are highly dependent upon what happens <br />to river flows. River characteristics which <br />influence riverine wetland functions and values <br />include: <br />Water quantity. <br />In general, decreases in river water quantity <br />due to water diversions or extractions for <br />agriculture, commercial, industrial, or domes- <br />tic use decrease the size and functions of <br />downstream wetlands. The quantity of water <br />entering and leaving riverine wetlands directly <br />or indirectly determines water depth and <br />determines flushing rates which, in turn, <br />affect water quality. <br />Water depth. <br />Wetland water depth is determined by the amount <br />of water in a river or stream at various times <br />during a year, the width of the river or <br />stream, and the topography (bottom contours) of <br />the wetland. The bottom contours are, in turn, <br />determined by river erosion and deposition <br />and sediment regimes. Mean water depth <br />determines the type of wetland vegetation <br />(marsh, shrub, forest) and the areal extent of <br />the wetland. Water depth also, to some extent, <br />determines habitat value for fish and other <br />wildlife. Water depth is greatly affected by <br />dams and reservoirs including water release <br />regimes, channelization, and dredging. <br />Water quality. <br />Wetland water quality depends, in large <br />measure, upon the natural quality of the water <br />in the adjacent river or stream and the <br />discharge of nonpoint and point sources of <br />pollutants into the river or stream including <br />sediment, toxics, litter, nutrients, etc. <br />Riverine wetland fishery and habitat may be <br />damaged or destroyed by all types of <br />pollutants. The ability of rivers and river <br />wetlands to assimilate various pollutants and <br />recover from pollution discharges depends, in <br />part, upon vegetation, soils, detention time <br />and natural flushing rates and whether these <br />have been reduced by dams or water diversions. <br />Hydroperiod. <br />The hydroperiod of riverine water entering and <br />leaving a riverine wetland plays an important <br />role in determining its pollution assimilative <br />capacity, its flood storage and conveyance <br />capability, and the vegetation successional <br />8