Hellbenders Cryptobranchus alleganiensis were sampled by markrecapture in four rivers: C. a. bishopi in the Spring River, Arkansas, and Eleven Point River, Missouri, and C. a. alleganiensis in the Gasconade and Big Piney rivers, Missouri. Densities ranged from 0.9-6.1 hellbenders per 100 m2, biomass from 66-418 kg per ha. Growth of hellbenders decreased linearly as a function of total length in all populations. Spring River hellbenders exhibited the greatest length-specific growth, Eleven Point River hellbenders the least. Females exhibited a greater length-specific mass than males in all populations. Fecundity was a positive linear function of female body length. The mean number of eggs produced per female was 480, 450, 429 and 365 by the Spring River, Gasconade, Big Piney and Eleven Point river females, respectively. Age-specific production of ova was also greatest by Spring River females because of greater growth and consequent larger body size. It was least by Eleven Point River females. INTRODUCTION Cryptobranchus alleganiensis is a large aquatic salamander with two subspecies. The hellbender C. a. alleganiensis inhabits swift rocky streams from southern New York to northern Georgia and W through Tennessee and the Ohio River Valley to four Nflowing streams in the Ozarks (Dundee, 1971); the Meramec, Gasconade, Big Piney and Niangua rivers. The Ozark hellbender C. a. bishopi is known from the Spring River in Arkansas (Dowling, 1957) and from the Current, Eleven Point and North Fork rivers in Missouri (Firschein, 1951), all S-flowing, heavily spring-fed streams. The hellbender is a habitat specialist because its success is dependent on a constancy of dissolved oxygen, temperature and flow found in swift water areas (Williams et al., 1981). Thus the hellbender may serve as an indicator species for cool, unaltered streams. Smith and Minton (1957) reported that the range of the heilbender was rapidly decreasing because of human modification of stream habitat. In particular, impoundment, channelization, siltation, acid mine drainage and thermal pollution have reduced habitat for hellbenders (Dundee, 1971; Nickerson and Mays, 1973a). The status of the hellbender is uncertain in at least six states; it is endangered in two, and may have been extirpated in Illinois (Williams et al., 1981). Although stable populations exist in the Ozarks (Nickerson and Mays, 1973a), demographic data exist only for Niangua and North Fork river populations (Nickerson and Mays, 1973a; Taber et al., 1975; Topping and Ingersol, 1981; Peterson et al., 1983). Therefore, the objective of this study was to provide information by mark-recapture on the population dynamics of four other populations to serve as a reference for future evaluation of the status of the hellbender
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