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Compensatory effects of recruitment and survival when amphibian populations are perturbed by disease
1. The need to increase our understanding of factors that regulate animal population dynamics has been catalysed by recent, observed declines in wildlife populations worldwide. Reliable estimates of demographic parameters are critical for addressing basic and applied ecological questions and underst...
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Published in: | The Journal of applied ecology 2011-08, Vol.48 (4), p.873-879 |
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description | 1. The need to increase our understanding of factors that regulate animal population dynamics has been catalysed by recent, observed declines in wildlife populations worldwide. Reliable estimates of demographic parameters are critical for addressing basic and applied ecological questions and understanding the response of parameters to perturbations (e.g. disease, habitat loss, climate change). However, to fully assess the impact of perturbation on population dynamics, all parameters contributing to the response of the target population must be estimated. 2. We applied the reverse-time model of Pradel in Program MARK to 6 years of capture—recapture data from two populations of Anaxyrus boreas (boreal toad) populations, one with disease and one without. We then assessed a priori hypotheses about differences in survival and recruitment relative to local environmental conditions and the presence of disease. 3. We further explored the relative contribution of survival probability and recruitment rate to population growth and investigated how shifts in these parameters can alter population dynamics when a population is perturbed. 4. High recruitment rates (0·41) are probably compensating for low survival probability (range 0·51—0·54) in the population challenged by an emerging pathogen, resulting in a relatively slow rate of decline. In contrast, the population with no evidence of disease had high survival probability (range 0·75—0·78) but lower recruitment rates (0·25). 5. Synthesis and applications. We suggest that the relationship between survival and recruitment may be compensatory, providing evidence that populations challenged with disease are not necessarily doomed to extinction. A better understanding of these interactions may help to explain, and be used to predict, population regulation and persistence for wildlife threatened with disease. Further, reliable estimates of population parameters such as recruitment and survival can guide the formulation and implementation of conservation actions such as repatriations or habitat management aimed to improve recruitment. |
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The need to increase our understanding of factors that regulate animal population dynamics has been catalysed by recent, observed declines in wildlife populations worldwide. Reliable estimates of demographic parameters are critical for addressing basic and applied ecological questions and understanding the response of parameters to perturbations (e.g. disease, habitat loss, climate change). However, to fully assess the impact of perturbation on population dynamics, all parameters contributing to the response of the target population must be estimated. 2. We applied the reverse-time model of Pradel in Program MARK to 6 years of capture—recapture data from two populations of Anaxyrus boreas (boreal toad) populations, one with disease and one without. We then assessed a priori hypotheses about differences in survival and recruitment relative to local environmental conditions and the presence of disease. 3. We further explored the relative contribution of survival probability and recruitment rate to population growth and investigated how shifts in these parameters can alter population dynamics when a population is perturbed. 4. High recruitment rates (0·41) are probably compensating for low survival probability (range 0·51—0·54) in the population challenged by an emerging pathogen, resulting in a relatively slow rate of decline. In contrast, the population with no evidence of disease had high survival probability (range 0·75—0·78) but lower recruitment rates (0·25). 5. Synthesis and applications. We suggest that the relationship between survival and recruitment may be compensatory, providing evidence that populations challenged with disease are not necessarily doomed to extinction. A better understanding of these interactions may help to explain, and be used to predict, population regulation and persistence for wildlife threatened with disease. 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Psychology ; General aspects ; host–pathogen dynamics ; Pests and disease ; Population dynamics ; Population ecology ; Population growth rate ; reverse‐time Pradel model ; Toads ; United States ; Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution</subject><ispartof>The Journal of applied ecology, 2011-08, Vol.48 (4), p.873-879</ispartof><rights>2011 British Ecological Society</rights><rights>2011 The Authors. Journal of Applied Ecology © 2011 British Ecological Society</rights><rights>2015 INIST-CNRS</rights><rights>Copyright Blackwell Publishing Ltd. 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The need to increase our understanding of factors that regulate animal population dynamics has been catalysed by recent, observed declines in wildlife populations worldwide. Reliable estimates of demographic parameters are critical for addressing basic and applied ecological questions and understanding the response of parameters to perturbations (e.g. disease, habitat loss, climate change). However, to fully assess the impact of perturbation on population dynamics, all parameters contributing to the response of the target population must be estimated. 2. We applied the reverse-time model of Pradel in Program MARK to 6 years of capture—recapture data from two populations of Anaxyrus boreas (boreal toad) populations, one with disease and one without. We then assessed a priori hypotheses about differences in survival and recruitment relative to local environmental conditions and the presence of disease. 3. We further explored the relative contribution of survival probability and recruitment rate to population growth and investigated how shifts in these parameters can alter population dynamics when a population is perturbed. 4. High recruitment rates (0·41) are probably compensating for low survival probability (range 0·51—0·54) in the population challenged by an emerging pathogen, resulting in a relatively slow rate of decline. In contrast, the population with no evidence of disease had high survival probability (range 0·75—0·78) but lower recruitment rates (0·25). 5. Synthesis and applications. We suggest that the relationship between survival and recruitment may be compensatory, providing evidence that populations challenged with disease are not necessarily doomed to extinction. A better understanding of these interactions may help to explain, and be used to predict, population regulation and persistence for wildlife threatened with disease. Further, reliable estimates of population parameters such as recruitment and survival can guide the formulation and implementation of conservation actions such as repatriations or habitat management aimed to improve recruitment.</description><subject>Amphibia</subject><subject>Amphibia. Reptilia</subject><subject>amphibian decline</subject><subject>Amphibians</subject><subject>Animal diseases</subject><subject>Animal populations</subject><subject>Animal, plant and microbial ecology</subject><subject>Applied ecology</subject><subject>Batrachochytrium dendrobatidis</subject><subject>Biological and medical sciences</subject><subject>boreal toad</subject><subject>Conservation biology</subject><subject>Demography</subject><subject>Depopulation</subject><subject>disease</subject><subject>Environmental conditions</subject><subject>Epidemiology</subject><subject>Extinction</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General aspects</subject><subject>host–pathogen dynamics</subject><subject>Pests and disease</subject><subject>Population dynamics</subject><subject>Population ecology</subject><subject>Population growth rate</subject><subject>reverse‐time Pradel model</subject><subject>Toads</subject><subject>United States</subject><subject>Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution</subject><issn>0021-8901</issn><issn>1365-2664</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2011</creationdate><recordtype>article</recordtype><recordid>eNpdkUuL1EAQgBtRcBz9CUIjiKfE6nTSj4MHGdYXC3rQc1PpVNgOedmd7O78exNnWcG6VEF9VRT1McYF5GKL910upKqyQqkyL0CIHAqAKr9_wg6PjafsAFCIzFgQz9mLlDoAsJWUB9acpmGmMeEyxTOntiW_JD61PJKPa1gGGheOY8PTGm_DLfb87oZGjsN8E-qAI5-nee1xCdOYOEbiM8VljTU1vD7zJiTCRC_Zsxb7RK8e8pH9-nT18_Qlu_7--evp43Xmy6KqslKUVQ0ohScET1pp4b1SNWrwsrUtWNFoLYRR1qMAq2syWilL1nogLeSRvbvsneP0e6W0uCEkT32PI01rcsZIKI02eiPf_Ed20xrH7ThnbKEE6O07R_b2AcLksW8jjj4kN8cwYDy7opSFLk25cR8u3F3o6fzYF-B2Q65zuwi3i3C7IffXkLt3335c7dU2__oy36XNwr_9YDSAkPIPZZeQcg</recordid><startdate>201108</startdate><enddate>201108</enddate><creator>Muths, Erin</creator><creator>Scherer, Rick D.</creator><creator>Pilliod, David S.</creator><general>Blackwell Publishing</general><general>Blackwell Publishing Ltd</general><general>Blackwell</general><scope>IQODW</scope><scope>7SN</scope><scope>7SS</scope><scope>7T7</scope><scope>7U7</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>M7N</scope><scope>P64</scope><scope>RC3</scope><scope>7ST</scope><scope>7U6</scope><scope>F1W</scope><scope>H95</scope><scope>L.G</scope></search><sort><creationdate>201108</creationdate><title>Compensatory effects of recruitment and survival when amphibian populations are perturbed by disease</title><author>Muths, Erin ; Scherer, Rick D. ; Pilliod, David S.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4255-4145b0a31cea0ce7671cc66ba70c3f9f091d7711869ca1097be87669e99c0e713</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2011</creationdate><topic>Amphibia</topic><topic>Amphibia. Reptilia</topic><topic>amphibian decline</topic><topic>Amphibians</topic><topic>Animal diseases</topic><topic>Animal populations</topic><topic>Animal, plant and microbial ecology</topic><topic>Applied ecology</topic><topic>Batrachochytrium dendrobatidis</topic><topic>Biological and medical sciences</topic><topic>boreal toad</topic><topic>Conservation biology</topic><topic>Demography</topic><topic>Depopulation</topic><topic>disease</topic><topic>Environmental conditions</topic><topic>Epidemiology</topic><topic>Extinction</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General aspects</topic><topic>host–pathogen dynamics</topic><topic>Pests and disease</topic><topic>Population dynamics</topic><topic>Population ecology</topic><topic>Population growth rate</topic><topic>reverse‐time Pradel model</topic><topic>Toads</topic><topic>United States</topic><topic>Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Muths, Erin</creatorcontrib><creatorcontrib>Scherer, Rick D.</creatorcontrib><creatorcontrib>Pilliod, David S.</creatorcontrib><collection>Pascal-Francis</collection><collection>Ecology Abstracts</collection><collection>Entomology Abstracts (Full archive)</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Toxicology Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Genetics Abstracts</collection><collection>Environment Abstracts</collection><collection>Sustainability Science Abstracts</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 1: Biological Sciences & Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><jtitle>The Journal of applied ecology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Muths, Erin</au><au>Scherer, Rick D.</au><au>Pilliod, David S.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Compensatory effects of recruitment and survival when amphibian populations are perturbed by disease</atitle><jtitle>The Journal of applied ecology</jtitle><date>2011-08</date><risdate>2011</risdate><volume>48</volume><issue>4</issue><spage>873</spage><epage>879</epage><pages>873-879</pages><issn>0021-8901</issn><eissn>1365-2664</eissn><coden>JAPEAI</coden><abstract>1. The need to increase our understanding of factors that regulate animal population dynamics has been catalysed by recent, observed declines in wildlife populations worldwide. Reliable estimates of demographic parameters are critical for addressing basic and applied ecological questions and understanding the response of parameters to perturbations (e.g. disease, habitat loss, climate change). However, to fully assess the impact of perturbation on population dynamics, all parameters contributing to the response of the target population must be estimated. 2. We applied the reverse-time model of Pradel in Program MARK to 6 years of capture—recapture data from two populations of Anaxyrus boreas (boreal toad) populations, one with disease and one without. We then assessed a priori hypotheses about differences in survival and recruitment relative to local environmental conditions and the presence of disease. 3. We further explored the relative contribution of survival probability and recruitment rate to population growth and investigated how shifts in these parameters can alter population dynamics when a population is perturbed. 4. High recruitment rates (0·41) are probably compensating for low survival probability (range 0·51—0·54) in the population challenged by an emerging pathogen, resulting in a relatively slow rate of decline. In contrast, the population with no evidence of disease had high survival probability (range 0·75—0·78) but lower recruitment rates (0·25). 5. Synthesis and applications. We suggest that the relationship between survival and recruitment may be compensatory, providing evidence that populations challenged with disease are not necessarily doomed to extinction. A better understanding of these interactions may help to explain, and be used to predict, population regulation and persistence for wildlife threatened with disease. Further, reliable estimates of population parameters such as recruitment and survival can guide the formulation and implementation of conservation actions such as repatriations or habitat management aimed to improve recruitment.</abstract><cop>Oxford, UK</cop><pub>Blackwell Publishing</pub><doi>10.1111/j.1365-2664.2011.02005.x</doi><tpages>7</tpages><oa>free_for_read</oa></addata></record> |
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subjects | Amphibia Amphibia. Reptilia amphibian decline Amphibians Animal diseases Animal populations Animal, plant and microbial ecology Applied ecology Batrachochytrium dendrobatidis Biological and medical sciences boreal toad Conservation biology Demography Depopulation disease Environmental conditions Epidemiology Extinction Fundamental and applied biological sciences. Psychology General aspects host–pathogen dynamics Pests and disease Population dynamics Population ecology Population growth rate reverse‐time Pradel model Toads United States Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution |
title | Compensatory effects of recruitment and survival when amphibian populations are perturbed by disease |
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