LACLAIRE: UPLAND TEMPORARY POND VEGETATION IN FLORIDA Table 2. Wetland Indicator Status and Ecological Index Values (EI) (Reed 1988; Wentworth et al. 1988). Category Symbol Definition El Obligate OBL Plants that occur almost always in wetlands under 1 Wetland natural conditions (estimated probability > 99%). Facultative FACW Plants that usually occur in wetlands (estimated 2 Wetland probability > 67% to 99%) but also occur in non- wetlands (estimated probability 1% to 33%). Facultative FAC Plants with a similar likelihood of occurring in both 3 wetlands and nonwetlands(estimated probability 33% to 67%). Facultative FACU Plants that sometimes occur in wetlands(estimated 4 Upland probability 1% to 33%), occur more often in non- wetlands (estimated probability > 67% to 99%). Obligate UPL Plants that occur rarely in wetlands (estimated probability 5 Upland < 1%) but occur almost always in non-wetlands under natural conditions(estimated probability > 99%). Percent cover data from each pond transect were used in conjunction with the wetland indicator status of each species to determine the total percent cover in each pond basin of OBL, FACW, FAC, FACU, and UPL species. These data were compared by hydrologic status of each pond as expressed by months since each pond had held water. Species richness, Shannon's Index, and evenness were calculated for each set of pond transect data. These data were also compared by hydrologic status at each pond as expressed by months since each pond had held water. Species richness is the total number of species found along each pond transect. Shannon's Index, H', is a measure of the average degree of "uncertainty" in predicting the species of an individual chosen at random from a collection of S species and N individuals in a population (Shannon and Weaver 1949). As diversity increases, Shannon's Index will also increase. The equation describing Shannon's Index is as follows: H' = Z (pilnpi) pi = proportional abundance of each species; estimated from the proportion of the number of individuals of a species to the total number of individuals in the sample. Evenness, E, was calculated as the ratio of H' to the natural log of species richness. Evenness would be maximum when all species were equally abundant and would decrease toward zero as the community diverged from evenness.