Channel incision has major impacts on stream corridor ecosystems, leading t
o reduced spatial habitat heterogeneity, greater temporal instability, less
stream-floodplain interaction, and shifts in fish community structure. Mos
t literature dealing with channel incision examines physical processes and
erosion control. A study of incised warmwater stream rehabilitation was con
ducted to develop and demonstrate techniques that would be economically fea
sible for integration with more orthodox, extensively employed watershed st
abilization techniques (e.g., structural bank protection, grade control str
uctures, small reservoirs, and land treatment). One-km reaches of each of f
ive northwest Mississippi streams with contributing drainage areas between
16 and 205 km(2) were selected for a 5-year study. During the study two rea
ches were modified by adding woody vegetation and stone structure to rehabi
litate habitats degraded by erosion and channelization. The other three rea
ches provided reference data, as two of them were degraded but not rehabili
tated, and the third was only lightly degraded. Rehabilitation approaches w
ere guided by conceptual models of incised channel evolution and fish commu
nity structure in small warmwater streams. These models indicated that reha
bilitation efforts should focus on aggradational reaches in the downstream
portions of incising watersheds, and that ecological status could be improv
ed by inducing formation and maintenance of stable pool habitats.
Fish and physical habitat attributes were sampled from each stream during t
he Spring and Fall for 5 years, and thalweg and cross-section surveys were
performed twice during the same period. Rehabilitation increased pool habit
at availability, and made the treated sites physically more similar to the
lightly degraded reference site. Fish communities generally responded as su
ggested by the aforementioned conceptual model of fish community structure.
Species composition shifted away from small colonists (principally cyprini
ds and small centrarchids) toward larger centrarchids, catostomids, and ict
alurids. Fish density and species richness increased at one rehabilitated s
ite but remained stable at the other, suggesting that the sites occupied di
fferent initial states and endpoints within the conceptual model, and diffe
red in their accessibility to sources of colonizing organisms. These experi
ments suggest that major gains in stream ecosystem rehabilitation can be ma
de through relatively modest but well-designed efforts to modify degraded p
hysical habitats.