Non-native species impacts on pond occupancy by an anuran

Non-native fish and bullfrogs (Lithobates catesbeianus) are frequently cited as contributing to the decline of ranid frogs in the western United States, so we hypothesized that non-native species, habitat, or a combination of these relate to the probability of local extinction for northern red-legged frogs (Rana aurora) in Oregon, USA. We also hypothesized that the probability of colonization relates to land use, wetland size, or riparian forest. In a 5-yr study, we found no support for an effect of non-native species on northern red-legged frogs. Instead, probability of local extinction decreased with the extent of emergent vegetation and riparian forest. This finding suggests that managers consider the role of habitat when confronting non-native species problems. © 2010 The Wildlife Society.     

拉萨国家级自然保护区拉鲁湿地发现牛蛙

原产于美国落基山脉以东地区的牛蛙(Rana Catesbeiana )是一种非常危险的外来物种。 2014年6月14-24日在拉萨市国家级自然保护区拉鲁湿地内发现成 、幼体 的牛蛙。建议借助政府、知名宗教人士、媒介等力量,以制度、呼吁、宣传等有效渠道,尽快解决湿地放生牛蛙的问题,以降低湿地现有牛蛙的种群增长及栖息地的进一步扩大。     

Genetic reconstruction of a bullfrog invasion to elucidate vectors of introduction and secondary spread

Reconstructing historical colonization pathways of an invasive species is critical for uncovering factors that determine invasion success and for designing management strategies. The American bullfrog (Lithobates catesbeianus) is endemic to eastern North America, but now has a global distribution and is considered to be one of the worst invaders in the world. In Montana, several introduced populations have been reported, but little is known of their sources and vectors of introduction and secondary spread. We evaluated the genetic composition of introduced populations at local (Yellowstone River floodplain) and regional (Montana and Wyoming) scales in contrast to native range populations. Our objectives were to (1) estimate the number of introductions, (2) identify probable native sources, (3) evaluate genetic variation relative to sources, and (4) characterize properties of local‐ and regional‐scale spread. We sequenced 937 bp of the mitochondrial cytochrome b locus in 395 tadpoles collected along 100 km of the Yellowstone River, from three additional sites in MT and a proximate site in WY. Pairwise Φ_ST revealed high divergence among nonnative populations, suggesting at least four independent introductions into MT from diverse sources. Three cyt b haplotypes were identical to native haplotypes distributed across the Midwest and Great Lakes regions, and AMOVA confirmed the western native region as a likely source. While haplotype (H_d = 0.69) and nucleotide diversity (π = 0.005) were low in introduced bullfrogs, the levels of diversity did not differ significantly from source populations. In the Yellowstone, two identified haplotypes implied few introduction vectors and a significant relationship between genetic and river distance was found. Evidence for multiple invasions and lack of subsequent regional spread emphasizes the importance of enforcing legislation prohibiting bullfrog importation and the need for continuing public education to prevent transport of bullfrogs in MT. More broadly, this study demonstrates how genetic approaches can reveal key properties of a biological invasion to inform management strategies.     

Territorial male bullfrogs (Rana catesbeiana) do not assess fighting ability based on size-related variation in acoustic signals

Some animals use communication signals to assess their opponent'ssize and fighting ability during aggressive conflicts. Malefrogs assess their opponent's size based on the fundamentalfrequency (pitch) of advertisement calls, which is negativelycorrelated with body size, an important determinant of fightingability in frogs. I conducted a field playback experiment to investigate whether territorial male bullfrogs assess the sizeof opponents based solely on size-related variation in fundamentalfrequency. I repeatedly broadcast synthetic bullfrog advertisementcalls to three groups of males. Playback stimuli simulateda large male (n = 24), a small male (n = 24), or an acousticallysize-matched male (n = 34). Neither the simulated size of theopponent, the subject's own size, nor the degree of size asymmetrybetween the subject and simulated intruder had significanteffects on the magnitude of responses during the playback testor on the rate of habituation that occurred with repeated stimulation.Post-hoc analyses of effect sizes and statistical power indicatedthat the effects in this study were quite small compared toprevious studies in other frogs. More important, power analysesindicated that this study had high power (1 - ß >0.90) to detect the magnitude of effect sizes observed in previous studies. Thus, territorial male bullfrogs do not appear to assessan opponent's fighting ability based solely on the fundamentalfrequency of acoustic signals. These results contrast starklywith theoretical predictions and previous empirical work withfrogs.