LeHavreV1, PascalFrancis, Curation, bibRecord, 000101

Modelling the efficacy of proposed mitigation areas for shorebirds: a case study on the Seine estuary, France

Identifieur interne : 000101 ( PascalFrancis/Curation ); précédent : 000100; suivant : 000102

Modelling the efficacy of proposed mitigation areas for shorebirds: a case study on the Seine estuary, France

Auteurs : Sarah E. A. Le V. Dit Durell [Royaume-Uni] ; Richard A. Stillman [Royaume-Uni] ; Patrick Triplet [France] ; Christophe Aulert [France] ; Damien Ono Dit Biot [France] ; Agnès Bouchet [France] ; Sylvain Duhamel [France] ; Sebastien Mayot [France] ; John D. Goss-Custard [Royaume-Uni]

Source :

Biological conservation [ 0006-3207 ] ; 2005.

RBID : Pascal:05-0160850

Descripteurs français

Pascal (Inist)
- Prévention pollution, Aves, Etude cas, France, Modèle, Habitat, Perte, Protection environnement, Estuaire Seine.
Wicri :
- geographic : France.
- topic : Habitat.

English descriptors

KwdEn :
- Aves, Case study, Environmental protection, France, Habitat, Loss, Models, Pollution prevention.

Abstract

A behaviour-based model was used to explore the effect of an extension of the port at Le Havre (Port 2000), and the effect of proposed mitigation measures, on the mortality and body condition of the three main shorebird species that overwinter in the estuary of the river Seine, France. In the model, a 20% reduction in the area of mudflats on the north side of the estuary had little effect on curlew Numenius arquata mortality and body condition but significantly increased mortality and decreased body condition in dunlin Calidris alpina and oystercatchers Haematopus ostralegus. Disturbance of feeding birds both day and night had a significant effect on the mortality and body condition of all three shorebird species, as did disturbance of roosting birds. Disturbance of feeding birds in the daytime only had a significant effect on dunlin mortality and body condition, but not that of curlew and oystercatchers. In the model, the creation of a buffer zone to reduce disturbance of feeding birds restored shorebird mortality and body condition to pre-disturbance levels. A new mudflat area was also effective in mitigating the effect of habitat loss on all three shorebirds and in mitigating the effect of roost disturbance on dunlin and curlew. However, a new mudflat area was not effective in mitigating the effect of roost disturbance on oystercatcher mortality and body condition. The effectiveness of the mitigating mudflat depended as much on its size as its quality. We believe that this is the first time that anyone has been able to forecast the efficacy of proposed mitigation measures.

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A11	`04`	`1`		`@1 AULERT (Christophe)`
A11	`05`	`1`		`@1 BIOT (Damien Ono Dit)`
A11	`06`	`1`		`@1 BOUCHET (Agnès)`
A11	`07`	`1`		`@1 DUHAMEL (Sylvain)`
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A14	`03`			`@1 Maison de l'Estuaire, Observatoire de l'Avifaune, 20 rue Jean Courret @2 76600 Le Havre @3 FRA @Z 4 aut. @Z 5 aut.`
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C01	`01`		`ENG`	@0 A behaviour-based model was used to explore the effect of an extension of the port at Le Havre (Port 2000), and the effect of proposed mitigation measures, on the mortality and body condition of the three main shorebird species that overwinter in the estuary of the river Seine, France. In the model, a 20% reduction in the area of mudflats on the north side of the estuary had little effect on curlew Numenius arquata mortality and body condition but significantly increased mortality and decreased body condition in dunlin Calidris alpina and oystercatchers Haematopus ostralegus. Disturbance of feeding birds both day and night had a significant effect on the mortality and body condition of all three shorebird species, as did disturbance of roosting birds. Disturbance of feeding birds in the daytime only had a significant effect on dunlin mortality and body condition, but not that of curlew and oystercatchers. In the model, the creation of a buffer zone to reduce disturbance of feeding birds restored shorebird mortality and body condition to pre-disturbance levels. A new mudflat area was also effective in mitigating the effect of habitat loss on all three shorebirds and in mitigating the effect of roost disturbance on dunlin and curlew. However, a new mudflat area was not effective in mitigating the effect of roost disturbance on oystercatcher mortality and body condition. The effectiveness of the mitigating mudflat depended as much on its size as its quality. We believe that this is the first time that anyone has been able to forecast the efficacy of proposed mitigation measures.
C02	`01`	`X`		`@0 002A14D02B`
C03	`01`	`X`	`FRE`	`@0 Prévention pollution @5 01`
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C03	`04`	`X`	`FRE`	`@0 France @2 NG @5 04`
C03	`04`	`X`	`ENG`	`@0 France @2 NG @5 04`
C03	`04`	`X`	`SPA`	`@0 Francia @2 NG @5 04`
C03	`05`	`X`	`FRE`	`@0 Modèle @5 05`
C03	`05`	`X`	`ENG`	`@0 Models @5 05`
C03	`05`	`X`	`SPA`	`@0 Modelo @5 05`
C03	`06`	`X`	`FRE`	`@0 Habitat @5 06`
C03	`06`	`X`	`ENG`	`@0 Habitat @5 06`
C03	`06`	`X`	`SPA`	`@0 Habitat @5 06`
C03	`07`	`X`	`FRE`	`@0 Perte @5 07`
C03	`07`	`X`	`ENG`	`@0 Loss @5 07`
C03	`07`	`X`	`SPA`	`@0 Pérdida @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 Estuaire Seine @4 INC @5 87`
C07	`01`	`X`	`FRE`	`@0 Vertebrata @2 NS`
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Le document en format XML

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<front><div type="abstract" xml:lang="en">A behaviour-based model was used to explore the effect of an extension of the port at Le Havre (Port 2000), and the effect of proposed mitigation measures, on the mortality and body condition of the three main shorebird species that overwinter in the estuary of the river Seine, France. In the model, a 20% reduction in the area of mudflats on the north side of the estuary had little effect on curlew Numenius arquata mortality and body condition but significantly increased mortality and decreased body condition in dunlin Calidris alpina and oystercatchers Haematopus ostralegus. Disturbance of feeding birds both day and night had a significant effect on the mortality and body condition of all three shorebird species, as did disturbance of roosting birds. Disturbance of feeding birds in the daytime only had a significant effect on dunlin mortality and body condition, but not that of curlew and oystercatchers. In the model, the creation of a buffer zone to reduce disturbance of feeding birds restored shorebird mortality and body condition to pre-disturbance levels. A new mudflat area was also effective in mitigating the effect of habitat loss on all three shorebirds and in mitigating the effect of roost disturbance on dunlin and curlew. However, a new mudflat area was not effective in mitigating the effect of roost disturbance on oystercatcher mortality and body condition. The effectiveness of the mitigating mudflat depended as much on its size as its quality. We believe that this is the first time that anyone has been able to forecast the efficacy of proposed mitigation measures.</div>
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<fA11 i1="01" i2="1"><s1>LE V. DIT DURELL (Sarah E. A.)</s1>
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<fA11 i1="02" i2="1"><s1>STILLMAN (Richard A.)</s1>
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<fA11 i1="03" i2="1"><s1>TRIPLET (Patrick)</s1>
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<fA11 i1="05" i2="1"><s1>BIOT (Damien Ono Dit)</s1>
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<fA11 i1="06" i2="1"><s1>BOUCHET (Agnès)</s1>
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<fA11 i1="07" i2="1"><s1>DUHAMEL (Sylvain)</s1>
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<fA11 i1="08" i2="1"><s1>MAYOT (Sebastien)</s1>
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<fA11 i1="09" i2="1"><s1>GOSS-CUSTARD (John D.)</s1>
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<fA14 i1="01"><s1>Centre, for Ecology and Hydrology (CEH), Dorset, Winfrith Technology Centre</s1>
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<fA14 i1="02"><s1>GOP/SMACOPI, 1 Place de l'Amiral Courbet</s1>
<s2>80100 Abbeville</s2>
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<sZ>3 aut.</sZ>
</fA14>
<fA14 i1="03"><s1>Maison de l'Estuaire, Observatoire de l'Avifaune, 20 rue Jean Courret</s1>
<s2>76600 Le Havre</s2>
<s3>FRA</s3>
<sZ>4 aut.</sZ>
<sZ>5 aut.</sZ>
</fA14>
<fA14 i1="04"><s1>Groupe Ornithologique Normand, Université</s1>
<s2>14032 Caen</s2>
<s3>FRA</s3>
<sZ>6 aut.</sZ>
</fA14>
<fA14 i1="05"><s1>Cellule de Suivi du Littoral Haut Normand, 16 quai Casimir Delavigne</s1>
<s2>76600 Le Havre</s2>
<s3>FRA</s3>
<sZ>7 aut.</sZ>
<sZ>8 aut.</sZ>
</fA14>
<fA14 i1="06"><s2>30 The Strand, Topsham, Exeter EX3 0AY, Devon</s2>
<s3>GBR</s3>
<sZ>9 aut.</sZ>
</fA14>
<fA20><s1>67-77</s1>
</fA20>
<fA21><s1>2005</s1>
</fA21>
<fA23 i1="01"><s0>ENG</s0>
</fA23>
<fA43 i1="01"><s1>INIST</s1>
<s2>14169</s2>
<s5>354000126714500080</s5>
</fA43>
<fA44><s0>0000</s0>
<s1>© 2005 INIST-CNRS. All rights reserved.</s1>
</fA44>
<fA45><s0>24 ref.</s0>
</fA45>
<fA47 i1="01" i2="1"><s0>05-0160850</s0>
</fA47>
<fA60><s1>P</s1>
</fA60>
<fA61><s0>A</s0>
</fA61>
<fA64 i1="01" i2="1"><s0>Biological conservation</s0>
</fA64>
<fA66 i1="01"><s0>GBR</s0>
</fA66>
<fC01 i1="01" l="ENG"><s0>A behaviour-based model was used to explore the effect of an extension of the port at Le Havre (Port 2000), and the effect of proposed mitigation measures, on the mortality and body condition of the three main shorebird species that overwinter in the estuary of the river Seine, France. In the model, a 20% reduction in the area of mudflats on the north side of the estuary had little effect on curlew Numenius arquata mortality and body condition but significantly increased mortality and decreased body condition in dunlin Calidris alpina and oystercatchers Haematopus ostralegus. Disturbance of feeding birds both day and night had a significant effect on the mortality and body condition of all three shorebird species, as did disturbance of roosting birds. Disturbance of feeding birds in the daytime only had a significant effect on dunlin mortality and body condition, but not that of curlew and oystercatchers. In the model, the creation of a buffer zone to reduce disturbance of feeding birds restored shorebird mortality and body condition to pre-disturbance levels. A new mudflat area was also effective in mitigating the effect of habitat loss on all three shorebirds and in mitigating the effect of roost disturbance on dunlin and curlew. However, a new mudflat area was not effective in mitigating the effect of roost disturbance on oystercatcher mortality and body condition. The effectiveness of the mitigating mudflat depended as much on its size as its quality. We believe that this is the first time that anyone has been able to forecast the efficacy of proposed mitigation measures.</s0>
</fC01>
<fC02 i1="01" i2="X"><s0>002A14D02B</s0>
</fC02>
<fC03 i1="01" i2="X" l="FRE"><s0>Prévention pollution</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG"><s0>Pollution prevention</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="SPA"><s0>Prevención polución</s0>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE"><s0>Aves</s0>
<s2>NS</s2>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="ENG"><s0>Aves</s0>
<s2>NS</s2>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="SPA"><s0>Aves</s0>
<s2>NS</s2>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE"><s0>Etude cas</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG"><s0>Case study</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA"><s0>Estudio caso</s0>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE"><s0>France</s0>
<s2>NG</s2>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG"><s0>France</s0>
<s2>NG</s2>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA"><s0>Francia</s0>
<s2>NG</s2>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE"><s0>Modèle</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG"><s0>Models</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA"><s0>Modelo</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE"><s0>Habitat</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG"><s0>Habitat</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA"><s0>Habitat</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE"><s0>Perte</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG"><s0>Loss</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA"><s0>Pérdida</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>Estuaire Seine</s0>
<s4>INC</s4>
<s5>87</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>Europe</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="ENG"><s0>Europe</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="SPA"><s0>Europa</s0>
<s2>NG</s2>
</fC07>
<fN21><s1>108</s1>
</fN21>
<fN44 i1="01"><s1>OTO</s1>
</fN44>
<fN82><s1>OTO</s1>
</fN82>
</pA>
</standard>
</inist>
</record>

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Modelling the efficacy of proposed mitigation areas for shorebirds: a case study on the Seine estuary, France

Modelling the efficacy of proposed mitigation areas for shorebirds: a case study on the Seine estuary, France

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