other sites. Species diversity was greatest at Parcel B followed by C07984 and Sink Branch. Species evenness was greatest at SP11. Subcanopy Tree Species Table 7.5 summarizes subcanopy tree species found at each research site. Species found in all sites were classified as facultative, facultative wet or obligate except for Rhus copallinum, which is designated as an upland species. Density of early successional subcanopy species was highest at SP6 (15 years) followed by C07984. Densities of less than 1500 trees ha" occurred at sites throughout the age range. Fewer than one half of the sites sampled had late successional subcanopy species present. The highest density of late successional subcanopy species was found at Parcel B (19 years) and Sink Branch (18 years), the two oldest sites. Sites between 5 and 17 years old were lacking a late successional subcanopy component with two exceptions, HP5 Phase 3 and Cateye, where several subcanopy species were planted during construction. Subcanopy tree species richness was highest at Parcel B, with 4 species, and lowest at East Lobe and C07984, with one species. Salix caroliniana was present at ten of fourteen sites. Myrica spp. was present at nine of fourteen sites. Less than one half of the sites had species other than Myrica spp. and Salix caroliniana present. Celtis laevigata, Ilex cassine and Cornus foemina were the only late successional subcanopy species occurring. Sapium seribiferum (Chinese Talo) was present at one site but is considered an invasive exotic. Rhus copallinum was also present at one site; it is not considered a wetland species. Species diversity was greatest at Parcel B (0.42) and Sink Branch (0.39). Diversity of all other sites ranged from 0.0 to 0.30. East Lobe and CO7984, each with only one subcanopy species, had a species diversity of 0. Species evenness was undefined at SP1 East Lobe and C07984; this in artifact of the occurrence of only one species. Sites with more than one subcanopy species present had evenness values ranging from 0.32 0.98. Mean DBH of all subcanopy species (Table 7.5) ranged from 0.60-7.7 cm and was greatest at SP1 East Lobe. Early successional species DBH ranged from 0.5-7.7 cm, while DBH of late successional species ranged from 0.7-8.6 cm. Only in sites where late successional species were planted was the DBH of late successional species greater than early successional species. Shrub Species Shrub stem density ranged from 0 to greater than 20000 stems acre-' (Table 7.6). This count includes all stems originating from an individual shrub, but does not reflect 7-36