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
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