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Prior information reduces uncertainty about the consequences of deer overabundance on forest birds

Identifieur interne : 005643 ( PascalFrancis/Curation ); précédent : 005642; suivant : 005644

Prior information reduces uncertainty about the consequences of deer overabundance on forest birds

Auteurs : Tara G. Martin [Australie, Canada] ; Peter Arcese [Canada] ; Petra M. Kuhnert [Australie] ; Anthony J. Gaston [Canada] ; Jean-Louis Martin [France]

Source :

RBID : Pascal:13-0294509

Descripteurs français

English descriptors

Abstract

Prior scientific knowledge inspires ecological research, hypotheses and debate but is rarely used explicitly to formulate predictive models. Bayesian statistics provide a formal way to include informative priors and evaluate their influence on parameter estimates. We use case studies of the influence of overabundant deer on bird species abundance in the Gulf Island, San Juan and Haida Gwaii archipelagos of western North America to demonstrate the utility of informative priors and Bayesian modelling to determine the consequences of overabundance. We found that by including informative priors about deer browsing impacts on bird species from a study undertaken in Haida Gwaii, the precision of estimates from a similar study undertaken in the Gulf and San Juan archipelagos could be significantly increased. Uncertainty about regional ecological impacts underpins many agencies failure to take management actions. We demonstrate here, that informative priors, when used logically and transparently, can be a highly cost effective way to increase understanding of ecological processes. In some cases, it may be the only way to inform decision-making when scarce resources limit support for long term field research or the threat is sufficiently great that immediate action is required. For several bird species examined here, the inclusion of informative priors strengthened the conclusion that their populations were negatively affected by changes in vegetation structure caused by deer browsing. Our findings suggest that deer browsing in these island archipelagos must be managed if the risk of local extinctions among native flora and fauna is to be avoided.
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A11 01  1    @1 MARTIN (Tara G.)
A11 02  1    @1 ARCESE (Peter)
A11 03  1    @1 KUHNERT (Petra M.)
A11 04  1    @1 GASTON (Anthony J.)
A11 05  1    @1 MARTIN (Jean-Louis)
A14 01      @1 CSIRO Ecosystem Sciences, EcoSciences Precinct, 41 Boggo Rd., Dutton Park @2 Queensland 4102 @3 AUS @Z 1 aut.
A14 02      @1 Centre for Applied Conservation Research, Forest Sciences, University of British Columbia, 2424 Main Mall @2 Vancouver V6T 1Z4 @3 CAN @Z 1 aut. @Z 2 aut.
A14 03      @1 CSIRO Mathematics, Informatics and Statistics, Private Bag 2, Glen Osmond @2 South Australia 5064 @3 AUS @Z 3 aut.
A14 04      @1 Environment Canada, 1125 Colonel Drive @2 Ottawa K1S 5B6 @3 CAN @Z 4 aut.
A14 05      @1 CNRS Centre d'Écologie Fonctionnelle et Évolutive, UMR 5175, 1919 route de Mende @2 34293 Montpellier @3 FRA @Z 5 aut.
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C01 01    ENG  @0 Prior scientific knowledge inspires ecological research, hypotheses and debate but is rarely used explicitly to formulate predictive models. Bayesian statistics provide a formal way to include informative priors and evaluate their influence on parameter estimates. We use case studies of the influence of overabundant deer on bird species abundance in the Gulf Island, San Juan and Haida Gwaii archipelagos of western North America to demonstrate the utility of informative priors and Bayesian modelling to determine the consequences of overabundance. We found that by including informative priors about deer browsing impacts on bird species from a study undertaken in Haida Gwaii, the precision of estimates from a similar study undertaken in the Gulf and San Juan archipelagos could be significantly increased. Uncertainty about regional ecological impacts underpins many agencies failure to take management actions. We demonstrate here, that informative priors, when used logically and transparently, can be a highly cost effective way to increase understanding of ecological processes. In some cases, it may be the only way to inform decision-making when scarce resources limit support for long term field research or the threat is sufficiently great that immediate action is required. For several bird species examined here, the inclusion of informative priors strengthened the conclusion that their populations were negatively affected by changes in vegetation structure caused by deer browsing. Our findings suggest that deer browsing in these island archipelagos must be managed if the risk of local extinctions among native flora and fauna is to be avoided.
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C03 02  X  FRE  @0 Forêt @5 02
C03 02  X  ENG  @0 Forests @5 02
C03 02  X  SPA  @0 Bosque @5 02
C03 03  X  FRE  @0 Aves @2 NS @5 03
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C03 05  X  SPA  @0 Protección fauna @5 05
C03 06  X  FRE  @0 Golfe @5 06
C03 06  X  ENG  @0 Gulf @5 06
C03 06  X  SPA  @0 Golfo @5 06
C03 07  X  FRE  @0 Ile @5 07
C03 07  X  ENG  @0 Island @5 07
C03 07  X  SPA  @0 Isla @5 07
C03 08  X  FRE  @0 Protection environnement @5 08
C03 08  X  ENG  @0 Environmental protection @5 08
C03 08  X  SPA  @0 Protección medio ambiente @5 08
C03 09  X  FRE  @0 Cervidae @2 NS @5 55
C03 09  X  ENG  @0 Cervidae @2 NS @5 55
C03 09  X  SPA  @0 Cervidae @2 NS @5 55
C03 10  X  FRE  @0 Odocoileus hemionus @2 NS @5 56
C03 10  X  ENG  @0 Odocoileus hemionus @2 NS @5 56
C03 10  X  SPA  @0 Odocoileus hemionus @2 NS @5 56
C07 01  X  FRE  @0 Vertebrata @2 NS
C07 01  X  ENG  @0 Vertebrata @2 NS
C07 01  X  SPA  @0 Vertebrata @2 NS
C07 02  X  FRE  @0 Artiodactyla @2 NS
C07 02  X  ENG  @0 Artiodactyla @2 NS
C07 02  X  SPA  @0 Artiodactyla @2 NS
C07 03  X  FRE  @0 Ungulata @2 NS
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N21       @1 280
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Pascal:13-0294509

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<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE">
<s0>Golfe</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG">
<s0>Gulf</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA">
<s0>Golfo</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE">
<s0>Ile</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG">
<s0>Island</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA">
<s0>Isla</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE">
<s0>Protection environnement</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG">
<s0>Environmental protection</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA">
<s0>Protección medio ambiente</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE">
<s0>Cervidae</s0>
<s2>NS</s2>
<s5>55</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG">
<s0>Cervidae</s0>
<s2>NS</s2>
<s5>55</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA">
<s0>Cervidae</s0>
<s2>NS</s2>
<s5>55</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE">
<s0>Odocoileus hemionus</s0>
<s2>NS</s2>
<s5>56</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG">
<s0>Odocoileus hemionus</s0>
<s2>NS</s2>
<s5>56</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA">
<s0>Odocoileus hemionus</s0>
<s2>NS</s2>
<s5>56</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="01" i2="X" l="ENG">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="01" i2="X" l="SPA">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="FRE">
<s0>Artiodactyla</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="ENG">
<s0>Artiodactyla</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="SPA">
<s0>Artiodactyla</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="FRE">
<s0>Ungulata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="ENG">
<s0>Ungulata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="SPA">
<s0>Ungulata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="FRE">
<s0>Mammalia</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="ENG">
<s0>Mammalia</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="SPA">
<s0>Mammalia</s0>
<s2>NS</s2>
</fC07>
<fN21>
<s1>280</s1>
</fN21>
<fN44 i1="01">
<s1>OTO</s1>
</fN44>
<fN82>
<s1>OTO</s1>
</fN82>
</pA>
</standard>
</inist>
</record>

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