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![]() Appendix B: Bioengineering for Streambank Erosion Control -- Guidelines 
Bank zone. That portion of the bank usually above the normal high-water level; yet, this 
site is exposed periodically to wave-wash, erosive river currents, ice and debris movement, 
and traffic by animals or man. The site is inundated for at least a 60-day duration once every 
two to three years. The water table in this zone frequently is close to the soil surface due to 
its closeness to the normal river level. 
In the bank zone, both herbaceous (i.e., grasses, clovers, some sedges and other herbs) 
and woody plants are used. These should still be flood tolerant and able to withstand partial 
to complete submergence for up to several weeks. Allen and Klimas (1986) list several grass 
and woody species that can tolerate from 4 to 8 weeks of complete inundation. This list, 
should not be considered exhaustive, however. Whitlow and Harris (1979) provide a listing 
of very flood-tolerant woody species and a few herbaceous species by geographic area within 
the United States that can be used in the bank zone. 
Skeesick and Sheehan (1992) report on several other herbaceous and woody plants that 
can withstand tens of feet of inundation over 3 to 4 months in two different reservoir 
situations in Oregon. These same species are often found along streambanks. Local 
university botanists and plant material specialists within the NRCS should be consulted when 
seeking flood-tolerant plants . Various willows can be used in this zone, but they should be 
shrublike willows such as sandbar willow (S. exigua) and basket willow (S. purpurea var. 
nana). Edminster et al. (1949) and Edminster (1949) describe successful use of basket willow 
for streams and rivers in the Northeast. Shrub-like willow, alder, and dogwood species have 
been used in Europe successfully (Seibert 1968). Red-osier dogwood (Cornus stolonifera) 
and silky dogwood ( C. amomum) also have been used in the Northeast (Edminster et al. 1949 
and Edminster 1949). Seibert (1968) notes that in periods of high water, the upper branches 
of such shrubs reduce the speed of the current and thereby the erosive force of the water. 
The branches of these have great resilience, springing back after currents subside. 
Terrace zone. That portion of the bank inland from the bank zone; it is usually not 
subjected to erosive action of the river except during occasional flooding. This zone may 
include only the level area near the crest of the unaltered "high bank" or may include sharply 
sloping banks on high hills bordering the stream. 
The terrace zone is less significant for bank protection because it is less often flooded, but 
can be easily eroded when it is flooded if vegetation is not present. Vegetation in this zone 
is extremely important for intercepting floodwaters from overbank flooding, serving to reduce 
super-saturation and decrease weight of unstable banks through evapotranspiration processes 
and for tying the upper portion of the streambank together with its soil-binding root network. 
Coppin and Richards (1990) provide a detailed explanation of plant evapotranspiration, but 
summarize by saying, " Apart from increasing the strength of soil by reducing its moisture 
content, evapotranspiration by plants reduces the weight of the soil mass. This weight 
reduction can be important on vegetated slopes where the soil may be potentially unstable." 
As denoted in Figure 6, the terrace zone can contain native grasses, herbs, shrubs, and 
trees that are less flood tolerant than those in the bank zone, but still somewhat flood tolerant. 
B-21 
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