From 1985 to 1988, stream and riparian habitats in Pen branch and Four Mile
branch began recovering from deforestation caused by the previous release
of hot water from nuclear reactors. The Pen branch corridor was replanted w
ith wetland trees in 1995 to expedite recovery and restore the Pen branch e
cosystem. Pen branch, Four Mile branch, and two relatively undisturbed stre
ams were electrofished in 1995/1996 to determine how fish assemblages diffe
red between the previously disturbed and undisturbed streams and whether su
ch difference could be used to measure restoration success in Pen branch. F
ish assemblages were analyzed using nonparametric multivariate statistical
methods and the index of biotic integrity (IBI), a bioassessment method bas
ed on measurement of ecologically sensitive characteristics of fish assembl
ages. Many aspects of fish assemblage structure (e.g. species richness, dis
ease incidence, taxonomic composition at the family level) did not differ b
etween disturbed and undisturbed streams; however, the disturbed streams we
re characterized by higher densities of a number of species. These differen
ces were successfully detected with the multivariate statistical methods, w
hereas, the IBI did not differ between most recovering and undisturbed samp
ling sites. Because fish assemblages are strongly influenced by instream ha
bitat, and because instream habitat is strongly influenced by the riparian
zone, fish assemblages can be used to measure restoration success. Nonparam
etric ordination methods may provide the most sensitive measure of progress
towards restoration goals, although the IBI can be used during early stage
s of recovery to indicate when certain ecologically important aspects of st
ructure and function in recovering streams have reached levels typical of u
ndisturbed streams. (C) 2000 Elsevier Science B.V. All rights reserved.