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Hirano Y, Kobayashi M, Hashimoto Y, Kato H, Nishihiro J. Effect of local‐ and landscape‐scale factors on the distribution of the spring‐dependent species
Geothelphusa dehaani
and larval
Anotogaster sieboldii. Ecol Res 2022. [DOI: 10.1111/1440-1703.12352] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/30/2022]
Affiliation(s)
- Yuna Hirano
- Department of Environmental Science Toho University Funabashi Japan
- Center for Climate Change Adaptation National Institute for Environmental Studies Tsukuba Japan
| | - Miho Kobayashi
- Department of Environmental Science Toho University Funabashi Japan
| | - Yuka Hashimoto
- Department of Environmental Science Toho University Funabashi Japan
| | - Hiroki Kato
- Department of Environmental Science Toho University Funabashi Japan
- Center for Climate Change Adaptation National Institute for Environmental Studies Tsukuba Japan
| | - Jun Nishihiro
- Center for Climate Change Adaptation National Institute for Environmental Studies Tsukuba Japan
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2
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Colomer MÀ, Margalida A, Sanuy I, Llorente GA, Sanuy D, Pujol-Buxó E. A computational model approach to assess the effect of climate change on the growth and development of tadpoles. Ecol Modell 2021. [DOI: 10.1016/j.ecolmodel.2021.109763] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 10/20/2022]
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3
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Mota‐Ferreira M, Beja P. Combining geostatistical and biotic interaction model to predict amphibian refuges under crayfish invasion across dendritic stream networks. DIVERS DISTRIB 2020. [DOI: 10.1111/ddi.13047] [Citation(s) in RCA: 2] [Impact Index Per Article: 0.5] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/28/2022] Open
Affiliation(s)
- Mário Mota‐Ferreira
- EDP Biodiversity Chair CIBIO/InBio Centro de Investigação em Biodiversidade e Recursos Genéticos Universidade do Porto Vila do Conde Portugal
- CIBIO/InBio Centro de Investigação em Biodiversidade e Recursos Genéticos Instituto Superior de Agronomia Universidade de Lisboa Lisboa Portugal
| | - Pedro Beja
- EDP Biodiversity Chair CIBIO/InBio Centro de Investigação em Biodiversidade e Recursos Genéticos Universidade do Porto Vila do Conde Portugal
- CIBIO/InBio Centro de Investigação em Biodiversidade e Recursos Genéticos Instituto Superior de Agronomia Universidade de Lisboa Lisboa Portugal
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4
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Liu X, Wang S, Ke Z, Cheng C, Wang Y, Zhang F, Xu F, Li X, Gao X, Jin C, Zhu W, Yan S, Li Y. More invaders do not result in heavier impacts: The effects of non-native bullfrogs on native anurans are mitigated by high densities of non-native crayfish. J Anim Ecol 2018; 87:850-862. [DOI: 10.1111/1365-2656.12793] [Citation(s) in RCA: 24] [Impact Index Per Article: 4.0] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 07/12/2017] [Accepted: 11/28/2017] [Indexed: 11/29/2022]
Affiliation(s)
- Xuan Liu
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
| | - Supen Wang
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
| | - Zunwei Ke
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
- University of Chinese Academy of Sciences; Beijing China
- Department of Biology, Chemistry and Environmental Engineering; Hanjiang Normal University; Shiyan China
| | - Chaoyuan Cheng
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
- University of Chinese Academy of Sciences; Beijing China
| | - Yihua Wang
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
- University of Chinese Academy of Sciences; Beijing China
| | - Fang Zhang
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
- University of Chinese Academy of Sciences; Beijing China
- College of Life Sciences; Anhui Normal University; Wuhu China
| | - Feng Xu
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
- University of Chinese Academy of Sciences; Beijing China
- Key Laboratory of Biogeography and Bioresources in Arid Land; Xinjiang Institute of Ecology and Geography; Chinese Academy of Sciences; Urumqi China
| | - Xianping Li
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
- University of Chinese Academy of Sciences; Beijing China
| | - Xu Gao
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
- University of Chinese Academy of Sciences; Beijing China
| | - Changnan Jin
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
- University of Chinese Academy of Sciences; Beijing China
- Chinese National Geography; Institute of Geographic Science and Nature Resources Research; Chinese Academy of Sciences; Beijing China
| | - Wei Zhu
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
- University of Chinese Academy of Sciences; Beijing China
| | - Shaofei Yan
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
- University of Chinese Academy of Sciences; Beijing China
- School of Resources and Environmental Engineering; Anhui University; Hefei China
| | - Yiming Li
- Key Laboratory of Animal Ecology and Conservation Biology; Institute of Zoology; Chinese Academy of Sciences; Beijing China
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5
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Gonçalves V, Gherardi F, Rebelo R. Bivalve or gastropod? Using profitability estimates to predict prey choice by P. clarkii. Acta Ethol 2017. [DOI: 10.1007/s10211-017-0251-x] [Citation(s) in RCA: 3] [Impact Index Per Article: 0.4] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/28/2022]
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6
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The Effects of Crayfish Predation and Vegetation Cover on Tadpole Growth, Survival, and Nonlethal Injury. J HERPETOL 2016. [DOI: 10.1670/14-176] [Citation(s) in RCA: 5] [Impact Index Per Article: 0.6] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/08/2022]
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7
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Zabierek K, Epp K. Antipredator response of Eurycea nana to a nocturnal and a diurnal predator: avoidance is not affected by circadian cycles of predators. AMPHIBIA-REPTILIA 2016. [DOI: 10.1163/15685381-00003070] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/19/2022]
Abstract
Both predators and prey exhibit cyclic shifts in activity throughout the day, which should cause the threat posed by predators to change in a recurrent pattern. If the threat posed by a predator is dependent on their circadian foraging cycle, prey may respond more or less intensely to predators at different times of day, thereby maximizing the effectiveness and efficiency of avoidance behaviors. We examined whether predator-naïveEurycea nana, a federally threatened neotenic salamander, exhibits a different antipredator response to chemical cues of a diurnal predator, the green sunfish (Lepomis cyanellus), and a nocturnal predator, the red swamp crayfish (Procambarus clarkii). We predicted thatE. nanawould show more intense antipredator responses (reduced activity) to a diurnal predator during the day and to a nocturnal predator at night. We found that, although there was significant antipredator behavior ofE. nanatoward sunfish, there was no detectable response to crayfish and no effect of time of day on responses to either predator, suggesting that eitherE. nanadoes not innately exhibit circadian patterns in avoidance of these species or that those patterns were undetectable in this study. Future studies should examine whether experience with predators may cause these salamanders to be more sensitive to the diel variation in threat, as has been found with some other amphibians and fish. Due to the threatened nature of this species, understanding the factors that influence antipredator behavior are crucial for management.
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Affiliation(s)
| | - Kristen Epp
- Department of Biology, Eastern Connecticut State University, 83 Windham St, Willimantic, CT 06226, USA
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8
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Brannelly LA, McMahon TA, Hinton M, Lenger D, Richards-Zawacki CL. Batrachochytrium dendrobatidis in natural and farmed Louisiana crayfish populations: prevalence and implications. DISEASES OF AQUATIC ORGANISMS 2015; 112:229-235. [PMID: 25590773 DOI: 10.3354/dao02817] [Citation(s) in RCA: 17] [Impact Index Per Article: 1.9] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 06/04/2023]
Abstract
The pathogenic chytrid fungus Batrachochytrium dendrobatidis (Bd) has been linked to global declines and extinctions of amphibians, making it one of the most devastating wildlife pathogens known. Understanding the factors that affect disease dynamics in this system is critical for mitigating infection and protecting threatened species. Crayfish are hosts of this pathogen and can transmit Bd to amphibians. Because they co-occur with susceptible amphibian communities, crayfish may be important alternative hosts for Bd. Understanding the prevalence and seasonal dynamics of crayfish infections is of agricultural and ecological interest in areas where crayfish are farmed and traded for human consumption. We conducted a survey of Bd in farmed and natural crayfish (Procambarus spp.) populations in Louisiana, USA. We found that Bd prevalence and infection intensity was low in both farmed and native populations and that prevalence varied seasonally in wild Louisiana crayfish. This seasonal pattern mirrors that seen in local amphibians. As crayfish are an important globally traded freshwater taxon, even with low prevalence, they could be an important vector in the spread of Bd.
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Affiliation(s)
- Laura A Brannelly
- One Health Research Group, College of Medical and Veterinary Sciences, James Cook University, Townsville, Queensland, Australia
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9
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Bucciarelli GM, Blaustein AR, Garcia TS, Kats LB. Invasion Complexities: The Diverse Impacts of Nonnative Species on Amphibians. COPEIA 2014. [DOI: 10.1643/ot-14-014] [Citation(s) in RCA: 54] [Impact Index Per Article: 5.4] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/24/2022]
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10
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Wilson NJ, Williams CR. A critical review of freshwater crayfish as amphibian predators: Capable consumers of toxic prey? Toxicon 2014; 82:9-17. [DOI: 10.1016/j.toxicon.2014.02.005] [Citation(s) in RCA: 7] [Impact Index Per Article: 0.7] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 11/11/2013] [Revised: 02/05/2014] [Accepted: 02/06/2014] [Indexed: 11/16/2022]
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11
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Divergent responses of exposed and naive Pacific tree frog tadpoles to invasive predatory crayfish. Oecologia 2013; 174:241-52. [DOI: 10.1007/s00442-013-2745-1] [Citation(s) in RCA: 11] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 11/03/2012] [Accepted: 07/29/2013] [Indexed: 11/26/2022]
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12
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Pujol-Buxó E, San Sebastián O, Garriga N, Llorente GA. How does the invasive/native nature of species influence tadpoles’ plastic responses to predators? OIKOS 2012. [DOI: 10.1111/j.1600-0706.2012.20617.x] [Citation(s) in RCA: 16] [Impact Index Per Article: 1.3] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/28/2022]
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13
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Francesco Ficetola G, Siesa ME, Manenti R, Bottoni L, De Bernardi F, Padoa-Schioppa E. Early assessment of the impact of alien species: differential consequences of an invasive crayfish on adult and larval amphibians. DIVERS DISTRIB 2011. [DOI: 10.1111/j.1472-4642.2011.00797.x] [Citation(s) in RCA: 41] [Impact Index Per Article: 3.2] [Reference Citation Analysis] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 10/18/2022] Open
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14
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Ortiz-Santaliestra ME, Fernández-Benéitez MJ, Marco A, Lizana M. Influence of ammonium nitrate on larval anti-predatory responses of two amphibian species. AQUATIC TOXICOLOGY (AMSTERDAM, NETHERLANDS) 2010; 99:198-204. [PMID: 20493565 DOI: 10.1016/j.aquatox.2010.04.020] [Citation(s) in RCA: 8] [Impact Index Per Article: 0.6] [Reference Citation Analysis] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 02/05/2010] [Revised: 04/15/2010] [Accepted: 04/24/2010] [Indexed: 05/29/2023]
Abstract
Sublethal effects of toxicants can upset normal behavioural responses to predators, leading to increased predation. For example, sensory capabilities can be impaired by toxicants, leading to difficulty in detecting predators or other threats. Alteration of locomotor abilities by pollutants can also explain the difficulty of tadpoles to escape from predators. Here we assess the effects of a nitrogenous fertilizer on the response to predators shown by anuran tadpoles. In a first experiment, we chronically exposed Iberian painted frog (Discoglossus galganoi) and spadefoot toad (Pelobates cultripes) tadpoles to environmentally relevant concentrations of ammonium nitrate. After the exposure, we tested tadpoles' ability to avoid predation by the red crayfish (Procambarus clarkii). In a second experiment, we analysed the escape behaviour of P. cultripes tadpoles as a function of ammonium nitrate exposure and presence of predatory crayfishes. Tadpoles of both species that were exposed to ammonium nitrate were consumed by crayfishes faster than controls (mean time of predation: Dg controls=18.03 h, 90.3 mg N-NO(3)NH(4)/L=7.48 h; Pc controls=16.12h, 90.3 mg N-NO(3)NH(4)/L=9.46 h). Control larval P. cultripes showed specific anti-predator escape responses, whereas those exposed to the fertilizer did not. We demonstrate, for the first time in amphibians, how nitrogenous fertilizers can affect larval defensive behaviours, and thereby increase the risk of predation. Our results emphasize the importance of considering environmental stresses on the ecotoxicological studies with amphibians.
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Mandrillon AL, Saglio P. Developmental windows and origins of the chemical cues mediating hatching responses to injured conspecific eggs in the common frog (Rana temporaria). CAN J ZOOL 2008. [DOI: 10.1139/z08-017] [Citation(s) in RCA: 7] [Impact Index Per Article: 0.4] [Reference Citation Analysis] [Abstract] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/22/2022]
Abstract
In amphibians, embryonic exposure to chemical cues resulting from a predation event on conspecific eggs can influence hatching traits. However, there is no information on the precise origin of the active substances, or on the critical period of embryonic development mediating such a process. In this context, common frog ( Rana temporaria L., 1758) eggs were exposed at Gosner stage 2, 16, or 20 to chemical cues simulating predation on whole eggs, jelly envelopes, or embryos. Embryonic movement rate, hatching time, and developmental stage at hatching appeared unaffected by the nature of the treatment. In contrast, the embryonic treatments strongly affected the morphology of hatchlings, with the groups exposed to crushed whole eggs and jelly envelopes showing longer (exposures at stages 16 and 20) and deeper (exposure at stage 20) tails than their unexposed counterparts. In addition, exposure at stage 20 to crushed embryos also produced hatchlings with longer tails than the controls. Thus, morphological plasticity at hatching can result from a relatively short period of embryonic exposure to conspecific chemical cues. This critical period occurs at the completion of neurulation (stage 16), with the most marked effects resulting from an exposure at the last stage of embryonic development (stage 20).
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Affiliation(s)
- A.-L. Mandrillon
- Laboratoire d’Ecologie Aquatique, Unité Mixte de Recherche Ecologie et Santé des Ecosystèmes, Institut National de la Recherche Agronomique, 65, rue de Saint-Brieuc, 35042, Rennes CEDEX, France
| | - P. Saglio
- Laboratoire d’Ecologie Aquatique, Unité Mixte de Recherche Ecologie et Santé des Ecosystèmes, Institut National de la Recherche Agronomique, 65, rue de Saint-Brieuc, 35042, Rennes CEDEX, France
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