Printer Friendly

Sex-biased predation on newts of the genus Taricha by a novel predator and its relationship with tetrodotoxin toxicity.

INTRODUCTION

Unlike many prey species, adult Taricha are highly toxic (Mosher et al., 1964; Wakely et al., 1966; Brodie, 1968; Brodie et al., 1974; Daly et al., 1987; Hanifin et al., 1999, 2002). Early studies of Tancha granulosa (Brodie, 1968) showed that virtually all potential predators were susceptible to tetrodotoxin (TTX), the deadly neurotoxin found in the newts' skin. Tetrodotoxin acts by blocking sodium channels (Narahashi et al., 1967) and death from exposure is usually the result of respiratory failure (Brodie, 1968). The only known predators that do not die from ingesting adult Taricha were garter snakes of the genus Thamnophis (Brodie and Brodie, 1990, 1991). Garter snakes have varying levels of resistance to TTX that apparently coevolved with newt toxicity (Brodie et al., 2002; Hanifin et al., 2008).

Hanifin et al. (2008) have shown that there is great geographic variation in the toxicity of newts throughout their range. Populations of newts throughout the Pacific coast of the United States and Canada have an average range of whole skin toxicity from 0.000 mg TTX to 4.695 mg TTX. These results suggest that predation on Taricha in some localities along their range is possible, although successful predation has almost never been documented by predators other than Thamnophis. Anecdotal accounts of predation attempts on Taricha by various birds usually report the subsequent death of the predator (McAllister et al., 1997; Mobley and Stidham, 2000). However, recently, successful predation on Taricha, whereby the entire newt was consumed whole with no apparent ill effects by great blue herons (Fellers et al., 2008) and bullfrogs (Rana catesbeiana;Jennings and Cook, 1998), has been reported, although other studies found both species susceptible to TTX (Brodie, 1968). The reports of predation by great blue herons and bullfrogs are from areas where newts have very little or no TTX (Hanifin et al., 2008). Additionally, predation attempts on Taricha by a skunk have been observed, but the fate of the skunk is unknown (M. Edgehouse, pers. comm.). The outcome of these individual predator-prey interactions may be highly influenced by variations in newt toxicity.

Not only is there variation in toxicity geographically, but there is variation within a population and between the sexes (Hanifin et al., 2002). Female Taricha have been found to be more toxic in some populations than male Taricha, likely as a maternal investment to protect eggs. This type of investment could lead to phenomena such as sex-biased predation where a predator selectively preys on the sex with lower toxicity. Sex-biased predation is common in predator/prey systems; however, the causes of such sex differences in predation as well as the direction of bias (i.e., male-biased vs. female-biased) vary depending on the habits or life-history traits of both predator and prey species (e.g., Dickman et al., 1991; Norrdahl and Korpimaki, 1998; Christe et al., 2006; Boukal et al., 2008). Christe et al. (2006) investigated sex-biased predation as a source of extrinsic mortality, which may be a possible cause for differences in the lifespan of males and females in various species. They found that sex-biased predation, especially by birds, was common and directed toward male prey. However, Boukal et al. (2008) found that when combining data from a literature review and theoretical modeling to investigate predator-prey relationships, avian predators more often exhibited female-biased predation. Nevertheless, the results from Boukal et al. (2008) also indicate that when considering all of the taxa studied together, male-biased predation is approximately two times as common as female-biased predation.

There are several possible reasons that a species might experience sex-biased predation, and these often influence the direction of bias. Females often have specific traits resulting from fecundity selection that may increase vulnerability to predation (Hairston et al., 1983). For example, females of some species may be larger than males due to selection for increased offspring number. Females may also experience reduced performance during reproductive periods that results in higher mortality by predators (e.g., Seigel and Fitch, 1984; Seigel et al., 1987; Brodie, 1989). Male-biased predation may result from sexual dimorphism (e.g., Andersson, 1994; Christe et al., 2006). In many cases males are much more visible than females due to conspicuous plumage, coloration, size, etc. Males and females often exhibit different behaviors, which may place one sex at a higher risk for predation (e.g., Estes, 1969; Burk, 1981; Christe et al., 2006; Samelius and Alisauskas, 2006). Behavioral differences are often seen in animals that have parental care, wherein the female parent stays close to the nest or burrow while the male parent travels in search of food, exposing the male to higher predation risk.

Breeding episodes, phenology and associated activities may also contribute to a differential predation risk for males and females (e.g., Burk, 1982; McCauley et al., 2000; Christe et al., 2006; Boukal et al., 2008). In many cases, communal breeding may decrease the individual risk of predation due to the benefits of having many individuals to watch for predators and/or help defend against predators, as well as associated dilution effects (e.g., Smith and Graves, 1978; Robinson, 1985; Brown and Brown, 1987). However, Burk (1982) discusses the mating behaviors of insects and the male-biased costs associated with some of these behaviors. Burk found that male insects often swarm to attract mates, which results in high-energy gain with little energy expenditure for feeding bats. Many species of amphibians explosively breed, a behavior thought to be driven by the limited availability of suitable breeding habitats (i.e., vernal pools or seasonal marshes), appropriate climactic conditions (Wells, 1977; Sullivan, 1982), increased predation pressures (Woodward and Mitchell, 1990; Lucas et al., 1996; McCauley et al., 2000), or as a means of decreasing cannibalism on eggs and tadpoles (Wells, 1977; Petranka and Thomas, 1995). Newts of the genus Taricha may be either explosive breeders or prolonged breeders depending on the breeding site (Twitty, 1942; Stebbins, 1951; Pimentel, 1960; Neish, 1971; Petranka, 1998). Explosive breeding in amphibians may be expected to lead to sex-biased predation as in other taxa.

Our study documents extensive predation on the adult Tancha population in Annadel State Park in Santa Rosa, CA between 1998 and 2009. Field observations of predation on adult Tar&ha indicated substantial attacks and/or predation on adult newts during the winter breeding period resulting in injuries and/or death that are inconsistent with Thamnophis or bullfrogs and great blue herons. Furthermore, the observed predation appeared to be male biased. As newts at this site are explosive breeders, we investigated whether predation was in fact sex-biased. Additionally, because these observations contradict the general lack of predation seen on Taricha adults, we further investigated whether local newts were defended by the neurotoxin TTX. In some populations, female Tancha granulosa are more toxic than conspecific males (Hanifin et al., 2002), so we also explored whether sex differences in toxicity might contribute to the observed patterns of predation.

METHODS

Study site.--All work was conducted at Ledson Marsh in Annadel State Park in Santa Rosa, ca. The park is over 2000 ha and includes a variety of habitat types including oak woodland, fir forest, marshland, chaparral, grassland and meadow (Cook and Jennings, 2007). A low dam was built in 1930 in what is now known as Ledson Marsh to retain water in an area of the park that may have once been a vernal pool and wet meadow. The marsh is seasonal and is approximately 11 ha in size when at capacity with water during the winter season. Ledson Marsh serves as a breeding ground for many local amphibians, including California red-legged frogs (Rana draytoni), California newts (Taricha torosa) and rough-skinned newts (T. granulosa) .

Taricha mortality.--We collected Taricha mortality data from Ledson Marsh during the active breeding season (Nov.-Mar.) from 1998 to 2009. We visually searched for newts by wading through the marsh haphazardly at approximately weekly intervals. One to two researchers were present during each survey. Surveys began with the onset of heavy winter rains that were sufficient to completely or nearly fill the marsh (usually Dec. or Jan.). Subsequently, weekly surveys were conducted until the end of the breeding season (usually Feb. or Mar.). During heavy breeding periods, the marsh was sometimes surveyed multiple days during the week. The cold waters during the winter season allowed newts to be recovered during weekly surveys with limited decomposition. Newt carcasses were collected, sexed and assigned one of three injury types--none, punctured or lacerated, and eviscerated. Carcasses categorized as "none" showed no damage to the skin or other external physical injuries (Fig. 1). Newts that were eviscerated and had another injury type were classified as eviscerated. Newt carcasses that had an injury were considered "killed," whereas those without injury were considered "dead." In some cases, newts were collected that had decayed or been torn apart to the poaint that sex, species, and/or injury were unable to be assigned. These unknown newts comprised 12.4% of the total newts collected, and were excluded from all analyses. Gravidity was recorded for female newts. During the years 2007 through 2009, species identifications (Tancha torosa or T. granulosa) were also made. All newt carcasses collected were preserved.

[FIGURE 1 OMITTED]

Quantification of TTX.--Forty live adult newts (10 of each sex and species) were collected from Ledson Marsh in Santa Rosa, CA in Feb. 2007 for quantification of TTX levels. Specimens were frozen within three days of collection at -80 C. Procedures for collection of skin tissue as well as extraction and quantification of TTX were performed as in Hanifin et al. (2002) with minor modifications. Extracts of the tissue were prepared by homogenizing a 5 mm diameter skin punch in 600 [micro]l of 0.1 M acetic acid using a tissue sonicator (550 Sonic Dismembrator, Fisher Scientific). Standards for flourometric High Phase Liquid Chromatography (HPLC) were prepared from tetrodotoxin with citrate buffer available from Sigma (product number T8024-1MG).

Analyses.--All comparisons between newt species, sex or injury type were assessed using Pearson's chi-squared analysis. Comparisons of toxicity levels between species of newts were analyzed using a two-way ANOVA. Comparisons within species and within sex were analyzed using a one-way ANOVA. All toxicity data were log transformed to meet the assumptions of normality and homoscedasticity. Because toxicity data included zeros, 0.00001 was added to each individual value before log transformation. All analyses were performed using SAS/ STAT version 9.1 (SAS Institute).

RESULTS

Taricha mortality.--A total of 932 Taricha (116 of these were unassigned due to decomposition) carcasses were collected between 1998 and 2009 (Table 1). Of those assigned, 597 were male and 219 were female. Few of the females had been killed (i.e., punctured or eviscerated; 16.0%), whereas 97.5% of the males had been killed (Fig. 2). Of those that were killed, males were eviscerated slightly more often than females (59.8% and 54.3%, respectively). Significantly more male than female Tar&ha carcasses were found ([chi square] = 175.81, df = 1, P < 0.0001) over the course of the study. From 2007-2009, the vast majority of newt carcasses found were Taricha torosa. Taricha granulosa represented less than 8% of the newt carcasses collected during those years, which represents a significant difference in mortality between the two newt species ([chi square] = 119.05, df = 1, P < 0.0001).

Whereas the total number of Taricha carcasses collected varied across years (Fig. 3), overall mortality was male-biased. Moreover, there was either no sex-biased mortality or female biased mortality through 2003, followed by a substantial increase in male mortality starting in 2004. The frequency of injury types between the two sexes was also significantly different (Table 1, Fig. 2). Male Taricha were killed significantly more often than females (laceration [chi square] = 287.36, df = 1, P < 0.0001; evisceration [chi square] = 439.51, df = 1, P < 0.0001). Conversely, there was a significantly larger number of female newt carcasses found with no injury than there were of male newts ([chi square] = 92.11, df = 1, P < 0.0001). These females with no injury (n = 184) consisted of primarily gravid individuals (92.4%), indicating that they died before egg laying.

[FIGURE 2 OMITTED]

Quantification of TTX.--HPLC analysis showed a diversity of TTX levels in both species of newts. Taricha torosa had a range of TTX levels from 0.0003-0.0143 mg TTX/[cm.sup.2], whereas T. granulosa had TTX levels from none to 0.0612 mg TTX/[cm.sup.2] (HPLC analysis was done twice on this high toxicity T. granulosa female to confirm the result) (Fig. 4, Table 2). There were only two newts without any TTX and both were T. granulosa males. We did not find any significant differences in the levels of TTX between males and females of T. torosa (F = 0.79, df = 1, P = 0.3845), and only moderate non-significance between males and females of T. granulosa (F = 3.60, df = 1, P = 0.0738). Although T. torosa males had a greater mean toxicity than females, males also had a much larger standard error than that of the females (Table 2, Fig. 4). In contrast, the standard error for T. granulosa was much larger for females than for males. Additionally, T. torosawere significantly more toxic than T. granulosa (F = 8.48, df = 1, P = 0.0061). It was also found that there were no significant differences in toxicity between T. torosa and T. granulosa females (F = 2.79, df = 1, P = 0.1119); however, T. torosa males were significantly more toxic than those of T. granulosa (F = 5.74, df = 1, P = 0.0276).

[FIGURE 3 OMITTED]

[FIGURE 4 OMITTED]

DISCUSSION

Previous work by Hanifin et al. (2003) found that levels of TTX in Taricha granulosa eggs are highly correlated with TTX levels in the dorsal skin of the mother. This suggests that females invest TTX into their eggs, presumably as a source of protection from predation, and that females may be more toxic than males both internally and externally. As an explosively breeding species, male-biased predation rates for Taricha species and sexes at this locality are likely influenced by breeding migration patterns. Migration patterns for Taricha have been found to vary depending on the species and sex of individuals (Twitty, 1942; Stebbins, 1951; Pimentel, 1960; Neish, 1971; Petranka, 1998), which affects the length of time that each is exposed to predators. When migrating to a pond, males often arrive before females and typically stay longer following breeding (Twitty, 1942; Stebbins, 1951). Given this scenario, there should be a higher ratio of males to females in the marsh, which would increase the chances of predation on male Taricha. Studies on explosively breeding anurans also have shown that there are higher abundances of males in breeding locations than females (e.g., Turner, 1960; Calef, 1973). Relative abundances for this breeding location are unknown at this time.

The few females that were found killed (i.e., laceration) during the course of this study, were usually not eviscerated. It is possible that while handling newts, the predator responds to the toxin level and releases more toxic individuals. Garter snakes, Thamnophis sirtalis, limit exposure time to Tancha granulosa based on the toxicity of the newt as well as the snake's own resistance (Williams et al., 2003). Newts are also toxic internally, however, this may be of little impact to a predator as visceral TTX levels are extremely low (0.5 to 0.1 [micro]g/g) as are liver Trx levels (<0.1 [micro]g/g) (Wakely et al., 1966). Numbers of male and female newts found dead and without injury may be due to the courting process. In both species, several males simultaneously attempt to mate with one female (Smith, 1941; Janzen and Brodie, 1988; pers. obs.). It is possible that males competing to mate with a female accidentally drown the female in the process of breeding (Briggs and Storm, 1970; Kargarise Sherman, 1980). The few males found with no injury may also have been drowned in this struggle (Kargarise Sherman, 1980). There were not differences in the amount of search effort at the marsh each year contributing to the inter-annual variation in deaths observed. This variation may be due to predator presence during migration patterns of newts, variation in rainfall patterns, variation in migration patterns or availability of alternate food sources for predators.

Despite efforts to observe predation on newts during the study, predation attempts were not observed and the predator was not identified. Although we were unable to witness an attack, the common raven is likely one of the dominant predators of newts at Ledson Marsh. We frequently observed or heard ravens in the forest surrounding the marsh, but never foraging in the marsh. However, ravens are known to eviscerate other amphibians with toxic skin (Olson, 1989; Brothers, 1994). Ravens will quickly abandon foraging and depart if disturbed (Olson, pers. comm.; Hayes and Price, 2009), so it is not surprising that we did not observe attacks. Most newt carcasses that we found were eviscerated through an abdominal puncture wound or laceration that would require a predator with dexterity consistent with a raven's ability. Also, we found several newt carcasses lying on the top of floating aquatic vegetation [i.e., aquatic fern (Asola sp.)] indicating the carcass was either dropped by a bird or placed there by a predator of light weight. In many cases the newts were found freshly killed, in which case they were still moving, indicating that they were preyed upon rather than scavenged. It is unlikely that the predator was a great blue heron (Fellers et al., 2008) or bullfrog (Jennings and Cook, 1998) as newts preyed upon by these species were swallowed whole and not eviscerated, as we observed.

Other species of birds may also contribute to newt predation. There are examples of evisceration and/or consumption on other amphibian species by Corvids such as gray jays, Stellar's jays, and Clark's nutcrackers (Turner, 1960; Tordoff, 1980; Beiswenger, 1981; Pilliod, 2002; Murray et al., 2005). Stellar's jays and American crows are Corvids in addition to the raven that are found in Sonoma County and may contribute to the observed newt mortality in Ledson Marsh. Also, we cannot rule out small mammals as potential predators. We observed a few dead newts with gnaw marks suggesting a small carnivorous mammal predator. There have been multiple descriptions of attacks on toxic toads by skunks and raccoons in which the toads are often eviscerated (Hanson and Vial, 1956; Wright, 1966; Schaaf and Garton, 1970; Groves, 1980; Woodward and Mitchell, 1990), and both of these species occur at Annadel State Park (DGC, pers. obs.).

Taricha in Annadel state park are preyed upon by a predator that, although unidentified, is novel. Other accounts of successful Taricha predation have involved consumption of whole newts (Jennings and Cook, 1998; Fellers et al., 2008). This study, however, found that newts were often eviscerated, which requires a substantial amount of dexterity. It is likely that given the geographical variation in newt toxicity (Hanifin et al., 2008), there are other locations such as Ledson Marsh where there is a significant amount of predation on Taricha occurring by species other than Thamnophis. It seems possible that the predator in the case of this study is responding to a cue that we have yet to identify or understand as males are killed significantly more often than females, but toxicity is not the clear driver of sex-biased predation in this system.

Acknowledgments.--We thank Cyndy Shafer, Julian Meisler, Trisha Meisler, Judy Brodie and Tyson Stokes for help in the field. Mike Pfrender and Morgan Ernest provided helpful insight and advice during the research and writing of this manuscript. The USU Herp group provided helpful comments on this manuscript. Field studies were conducted under the auspices of California Department of Parks and Recreation and California Department of Fish and Game. Funding for this project was provided by the U.S. National Science Foundation (DEB-0315172 to E.D. Brodie, Jr. and DEB-0650082 to E.D. Brodie III) and the National Institutes of Health (NIH 5 F32 GM080132 to Charles Hanifin). Voucher specimens have been deposited in The University of Texas at Arlington Collection of Vertebrates.

SUBMITTED 27 APRIL 2010

ACCEPTED 28 OCTORER 2010

LITERATURE CITED

ANDERSSON, M. 1994. Sexual Selection, Monographs in Behaviour and Ecology. Princeton University Press, Princeton, New Jersey. 599 p.

BEISWENGER, N. E. 1981. Predation by gray jays on aggregating tadpoles of the boreal toad (Bufo boreas). Copeia, 1981:459-460.

BOUKAL, D. S., L. BEREC AND V. KRIVAN. 2008. Does sex-selective predation stabilize or destabilize predator-prey dynamics? PLOS ONE, 3:e2687.

BRIGGS, J. L. AND R. M. STORM. 1970. Growth and population structure of the cascade frog, Rana cascadae Slater. Herpetologica, 26:283-300.

BRODIE, E. D., JR. 1968. Investigations on the skin toxin of the adult rough-skinned newt, Taricha granulosa. Copeia, 1968:307-313.

--, J. L. HENSEL, JR. AND J. A. JOHNSON. 1974. Toxicity of the urodele amphibians Taricha, Notophthalmus, Cynops and Paramesotriton (Salamandridae). Copeia, 1974:506-511.

--, B. J, RIDENHOUR AND E. D. BRODIE, III. 2002. The evolutionary response of predators to dangerous prey: hotspots and coldspots in the geographic mosaic of coevolution between garter snakes and newts. Evolution, 56:2067-2082.

BRODIE, E. D. III. 1989. Behavioral modification as a means of reducing the cost of reproduction. Am. Nat., 134:225-228.

-- AND E. D. BRODIE, JR. 1990. Tetrodotoxin resistance in garter snakes: an evolutionary response of predators to dangerous prey. Evolution, 44:651-659.

-- AND --. 1991. Evolutionary response of predators to dangerous prey: reduction of toxicity of newts and resistance of garter snakes in island populations. Evolution, 45:221-224.

BROTHERS, D. R. 1994. Bufo boreas (Western toad) predation. Herpetol. Rev., 25:117.

BROWN, C. R. AND M. B. BROWN. 1987. Group-living in Cliff Swallows as an advantage in avoiding predators. Behav. Ecol. and Sociobiol., 21:97-107.

BURK, T. 1981. Signalling and sex in acalyptrate flies. Fla. Entomol., 64:30-43.

--. 1982. Evolutionary significance of predation on sexually signaling males. Fla. Entomol., 65:90-104.

CALEF, G. W. 1973. Spatial distribution and 'effective' breeding population of red-legged frogs (Rana aurora) in Marion Lake, British Columbia. Can. Field Nat., 87:279-284.

CHRISTE, P., L. KELLER AND A. ROULIN. 2006. The predation cost of being a male: implications for sex-specific rates of ageing. Oikos, 114:381-384.

COOK, D. G. AND M. R. JENNINGS, S. 2007. Microhabitat use of the California red-legged frog and introduced bullfrog in a seasonal marsh. Herpetologica, 63:430-440.

DALY, J. W., C. W. MEYERS AND N. WHITTAKER. 1987. Further classification of skin alkaloids from neotropical poison frogs (Dendrobatidae), with a general survey of toxic, noxious substances in the Amphibia. Toxicon, 25:1021-1095.

DICKMAN, C. R., M. PREDAVEC AND A. J. LYNAM. 1991. Differential predation of size and sex classes of mice by the barn owl, Tyoto alba. Oikos, 62:67-76.

ESTES, R. D. 1969. Territorial behavior of the wildebeest (Connochaetes taurinus Burchell, 1823). Z. Tierpsychologie, 26:284-370.

FELLERS, G. M., J. REYNOLDS-TAYLOR AND S. FARRAR. 2008. Tar&ha granulosa predation. Herpetol. Rev., 38:317-318.

GROWS, J. D. 1980. Mass predation on a population of the American toad, Bufo americanus. Am. Midl. Nat., 103:202-203.

HAIRSTON, N. G., W. E. WALTON AND K. T. LI. 1983. The causes and consequences of sex-specific mortality in a freshwater copepod. Limnol. Oceanogr., 28:935-947.

HANIFIN, C. T., M. YOTSU-YAMASHITA, T. YASUMOTA, E. D. BRODIE, III AND E. D. BRODIE, JR. 1999. Toxicity of dangerous prey: variation in Tetrodotoxin levels within and among populations of the newt Taricha granulosa. J. Chem. Ecol., 25:2161-2175.

--, E. D. BRODIE, III AND E. D. BRODIE, JR. 2002. Tetrodotoxin levels of the rough-skin newt, Taricha granulosa, increase in long-term captivity. Toxicon, 40:1149-1153.

--, -- AND --. Tetrodotoxin levels in eggs of the rough skin newt, Taricha granulosa, are correlated with female toxicity. J. Chem. Ecol., 29:1729-1739.

--, -- AND --. Phenotypic mismatches reveal escape from arms-race coevolution. PLOS, 6:471-482.

HANSON, J. A. ANDJ. L. VIAL. 1956. Defensive behavior and effects of toxins in Bufo alvarius. Herpetologica, 12:141-149.

HAYES, M. P. ANN R. F. PRICE. 2009. Bufo boreas boreas (Boreal toad) predation. Herpetol. Rev., 40:68-69.

JENNINGS, M. R. AND D. COOK. 1998. Taricha torosa torosa (Coast Range newt) predation. Herpetol. Rev., 29:230.

JANZEN, F.J. AND E. D. BRODIE, JR. 1988. Tall tails and sexy males: sexual behavior of the rough skinned newts (Taricha granulosa) in a natural breeding pond. Copeia, 1989:1068-1071.

KARGARISE SHERMAN, C. 1980. A comparison of the natural history and mating systems of two anurans: Yosemite toads (Bufo canorus) and black toads (Bufo exsui). Unpublished Ph.D. thesis, University of Michigan, Ann Arbor, Michigan. 394 p.

LUCAS, J. R., R. D. HOWARD AND J. G. PALMER. 1996. Callers and satellites: chorus behavior in anurans as a stochastic dynamic game. Anim. Behav., 51:501-518.

MCALLISTER, K. R., J. SKRILETZ, B. HALL AND M. M. GARNER. 1997. Taricha granulosa (rough-skin newt) toxicity. Herpetol. Rev., 28:82.

McCAULEY, S.J., S. S. BOUCHARD, B.J. FARINA, K. ISVARAN, S. QUADER, D. W. WOOD AND C. M. ST. MARY. 2000. Energetic dynamics and anuran breeding phenology: insights from a dynamic game. Behav. Ecol., 11:429-436.

MOBLEY, J. A. AND T. A. STIDHAM. 2000. Great horned owl death from predation of a toxic California newt. Wilson Bull., 112:563-564.

MOSHER, H. S., F. A. FUHRMAN, H. D. BUCHWALD AND H. G. FISCHER. 1964. Tarichatoxin tetrodotoxin: a potent neurotoxin. Science, 144:1100-1110.

MURRAY, M. P., C. A. PEARL AND R. B. BURY. 2005. Apparent predation by gray jays, Perisoreus canadensis, on long-toed salamanders, Ambystoma macrodactylum, in the Oregon Cascade Range. Can. Field Nat., 119:291-292.

NARAHASHI, T., J. w. MOORE AND R. N. POSTON. 1967. Tetrodotoxin derivatives: chemical structure and blockage of nerve membrane conductance. Science, 156:976-979.

NEISH, I. C. 1971. Comparison of size, structure, and distributional patterns of two salamander populations in Marion Lake, British Columbia. J. Fish. Res. Board. Can., 28:49-58.

NORRDAHL, K. AND E. KORPIMAKI. 1998. Does mobility or sex of voles affect risk of predation by mammalian predators? Ecology, 79:226-232.

OLSON, D. H. 1989. Predation on breeding western toads (Bufo boreas). Copeia, 1989:391-397. PETRANKA, J. W. AND D. A. G. THOMAS. 1995. Explosive breeding reduces egg and tadpole cannibalism in the wood frog, Rana sylvatica. Anim. Behav., 50:731-739.

--. 1998. Salamanders of the United States and Canada. Smithsonian Institution Press, Washington, DC. 587 p.

PILLIOD, D. S. 2002. Clark's nutcracker (Nucifraga columbiana) predation on tadpoles of the Columbia spotted frog (Rana luteiventris). Northwest. Nat., 83:59-61.

PIMENTEL, R. A. 1960. Inter- and intrahabitat movements of the rough-skinned newt, Taricha torosa granulosa (Skilton). Am. Midl. Nat., 63:470-496.

ROBINSON, S. K. 1985. Coloniality in the yellow-rumped cacique as a defense against nest predators. Auk, 102:506-519.

SAMELIUS, G. AND R. T. ALISAUSKAS. 2006. Sex-biased costs in nest defence behaviours by lesser snow geese (Chen caerulescens); consequences of parental roles? Behav. Ecol. Sociobiol., 59:805-810.

SCHAAF, R. T. AND J. S. GARTON. 1970. Raccoon predation on the American toad, Bufo americanus. Herpetologica, 26:334-335.

SEIGEL, R. A. AND H. S. FITCH. 1984. Ecological patterns of relative clutch mass in snakes. Oecologia, 61:293-301.

--, M. M. HUGGINS AND N. B. FORD. 1987. Reduction in locomotor ability as a cost of reproduction in gravid snakes. Oecologia, 73:481-485.

SMITH, R. E. 1941. Mating behavior in Triturus torosus and related newts. Copeia, 1941:255-262.

SMITH, M. J. AND H. B. GRAVES. 1978. Some factors influencing mobbing behaviour in barn swallows (Hirundo rustica). Behav. Biol., 23:355-372.

STEBBINS, R. C. 1951. Amphibians of western North America. University of California Press, Berkeley. 539 p.

SULLIVAN, B. K. 1982. Sexual selection in Woodhouse's toad (Bufo woodhousei) I. Chorus organization. Anim. Behav., 30:680-686.

TORDOW, W., III. 1980. Selective predation of gray jays, Perisoreus canadensis, upon boreal chorus frogs, Pseudacris triseriata. Evolution, 34:1004-1008.

TURNER, F. B. 1960. Population structure and dynamics of the western spotted frog, Rana p. pretiosa Baird & Girard, in Yellowstone Park, Wyoming. Ecol. Monogr., 30:251-278.

TWITTY, V. C. 1942. The species of California Triturus. Copeia, 1942:65-76.

WAKELY, J. F., G.J. FUHRMAN, F. A. FUHRMAN, H. G. FISCHER AND H. S. MOSHER. 1966. The occurrence of Tetrodotoxin (tarichatoxin) in Amphibia and the distribution of the toxin in the organs of newts (Taricha). Toxicon, 3:195-203.

WELLS, K. D. 1977. The social behaviour of anuran amphibians. Anim. Behav., 25:666-693.

WILLIAMS, B. L., E. D. BRODIE, JR. AND E. D. BRODIE, III. 2003. Coevolution of deadly toxins and predator resistance: self-assessment of resistance by garter snakes leads to behavioral rejection of toxic newt prey. Herpetologica, 59:155-163.

WOODWARD, B. D. AND S. MITCHELL. 1990. Predation of frogs in breeding choruses. Southwest. Nat., 35:449-450.

WRIGHT, J. W. 1966. Predation on the Colorado river toad, Bufo alvarius. Herpetologica, 22:127-128.

AMBER N. STOKES (1)

Department of Biology, Utah State University, 5305 Old Main Hill, Logan 84322

DAVID G. COOK

Sonoma County Water Agency, 404 Aviation Blvd, Santa Rosa, California 95403

CHARLES T. HANIFIN

Hopkins Manne Station, Stanford University, Pacific Grove, California 93950

EDMUND D. BRODIE III

Mountain Lake Biological Station and Department of Biology, University of Virginia, P. 0. Box 400328, Charlottesville 22904

AND

EDMUND D. BRODIE, JR

Department of Biology, Utah State University, 5305 Old Main Hill, Logan 84322

(1) Corresponding author: e-mail: amnoelleb@biology.usu.edu
TABLE 1.--Total numbers of dead male and female Taricha collected
each year according to injury type. Injury designations are N = none,
L = laceration and E = evisceration. Gravid is the total number of
the female carcasses collected that were also gravid

                       Male Taricha

                       Injury type

Year        N         L         E       Total

1998        0          5         5        10
1999        1          6         7        14
2000        6          6         4        16
2001        0          0         0         0
2002        0          2         1         3
2003        2          2         2         6
2004        3        107       111       221
2005        0         16        16        32
2006        0         77        78       155
2007        2          0         3         5
2008        1         12       101       114
2009        0          1        20        21
Total      15        234       348       597

                           Female Taricha

                             Injury type

Year        N         L         E       Gravid     Total

1998        22        0         1         23         23
1999         1        4         0          4          5
2000        45        3         5         53         53
2001         0        0         0          0          0
2002        16        0         2         18         18
2003        11        0         2         13         13
2004        37        7         3         46         47
2005        11        1         2         10         14
2006        10        0         0         10         10
2007        18        1         2         16         21
2008        12        0         2         12         14
2009         1        0         0          1          1
Total      184       16        19        206        219

TABLE 2.--Comparison of levels of TTX mg/cm 2 in Taricha torosa and
T. granulosa males and females. Sample sizes within each group were
equivalent, with N = 10 for each sex

                                                  Predicted whole
                      TTX/[cm.sup.2]               newt toxicity
Species/Sex       (mg, mean [+ or -] se)      (mg, mean [+ or -] se)

T. torosa
  Male           0.00871 [+ or -] 0.00278     0.3266 [+ or -] 0.10606
  Female         0.00724 [+ or -] 0.00124     0.2203 [+ or -] 0.04745
T. granulosa
  Male           0.00211 [+ or -] 0.00106     0.0583 [+ or -] 0.02911
  Female         0.00852 [+ or -] 0.00587     0.2285 [+ or -] 0.15813

                   Range TTX/[cm.sup.2]
Species/Sex                (cm)

T. torosa
  Male                0.0003-0.0243
  Female              0.0029-0.0143
T. granulosa
  Male                0.0000-0.0108
  Female              0.0001-0.0612
COPYRIGHT 2011 University of Notre Dame, Department of Biological Sciences
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2011 Gale, Cengage Learning. All rights reserved.

Article Details
Printer friendly Cite/link Email Feedback
Author:Stokes, Amber N.; Cook, David G.; Hanifin, Charles T.; Brodie, Edmund D., III; Brodie, Edmund D., Jr
Publication:The American Midland Naturalist
Article Type:Report
Geographic Code:1U9CA
Date:Apr 1, 2011
Words:5199
Previous Article:The effects of climate modes on growing-season length and timing of reproduction in the pacific northwest as revealed by biophysical modeling of...
Next Article:Ruffed grouse selection of drumming sites in the Black Hills National Forest.
Topics:

Terms of use | Privacy policy | Copyright © 2020 Farlex, Inc. | Feedback | For webmasters