DODD: ECOLOGY OF SANDHILLS POPULATION OF GASTROPHRYNE CAROLINENSIS 31 possible to determine whether the invertebrate killed the toad or the predator scavenged a carcass. DISCUSSION Life-history of Gastrophryne carolinensis Population Size.-There are no comparable studies on the eastern narrow- mouthed toad in Florida with which to compare the results of this study. At least 900 adult G. carolinensis visited the pond basin (unmarked animals with allowances for a few animals presumed to trespass the fence; Dodd 1991) in each of two of the five years that the fence was checked. The number of animals visiting the pond in 1987 is inexplicably low in relation to 1986, 1988, and 1989. This could be due to a natural population fluctuation, but it makes the interpretation of the 1990 collection data difficult. The most parsimonious explanation for the low pond visitation in 1990 is that the effects of the long-term drought were becoming apparent. Alternatively, the low numbers in 1990 could represent a natural fluctuation. The numbers of breeding adults and juveniles that complete metamorphosis of pond-breeding amphibians are known to fluctuate widely (Shoop 1974; Gibbons and Bennett 1974; Semlitsch 1987; Pechmann et al. 1989; Raymond and Hardy 1990; Pechmann et al. 1991). Recaptures.-Relatively few G. carolinensis were recaptured. Most recaptured individuals were captured in the same season as originally marked, presumably as the toads crossed back and forth between the core of the pond basin and refugia in the surrounding uplands. Other studies on Gastrophryne also report low recapture rates (Anderson 1954; Fitch 1956; Franz et al. 1989). Freiburg (1951) recaptured 33.5% of marked G. olivacea in his 1-year study but only 12.7% more than once. Fitch (1956) marked 1215 G. olivacea between 1949 and 1954, but only 13 "yielded series of records, well spaced, in two or more different years." Of 69 tattooed G. carolinensis trapped in April and May in Louisiana, only five were recaptured (Anderson 1954). Gastrophryne carolinensis may regenerate clipped toes rapidly, become trap- shy or otherwise learn to avoid recapture, move to breeding ponds only once or twice within a 5-year period thus minimizing the chances of recapture, or have very high mortality rates. Rates of toe regrowth are unknown, but little evidence of regrowth was apparent in this study or in studies of G. olivacea (Freiburg 1951). Unpublished data on movements based on cobalt tagging suggest that G. carolinensis may be sedentary and trap-shy (Franz et al. 1989). G. carolinensis also easily crawl vertically upwards (Wright 1932) and cross drift fences (Dodd 1991). Alternative forms of marking and long-term studies are needed to evaluate capture efficiency and individual recognition.