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A theoretical study of river fragmentation by dams and its effects on white sturgeon populations

Identifieur interne : 000349 ( PascalFrancis/Corpus ); précédent : 000348; suivant : 000350

A theoretical study of river fragmentation by dams and its effects on white sturgeon populations

Auteurs : Henriette I. Jager ; James A. Chandler ; Kenneth B. Lepla ; Webb Van Winkle

Source :

RBID : Pascal:01-0258604

Descripteurs français

English descriptors

Abstract

Most of the world's large rivers are fragmented by dams. Fragmentation of the river ecosystem alters migration patterns among fish populations and converts free-flowing river to reservoir habitat. In this study, we used an individual-based genetic metapopulation model to study the effects of fragmentation on the population viability and genetic diversity of a large-river fish, the white sturgeon, Acipenser transmontanus. In the first of two simulation experiments, we fragmented a 200 km river reach by building 1 to 20 virtual dams. Increased fragmentation produced an exponential decline in the likelihood of persistence, but no extinction threshold to suggest a minimum viable length of river. Compounding isolation with the loss of free-flowing habitat did not further reduce viability until free-flowing habitat was nearly eliminated, at which point extinction was certain. Genetic diversity within (among) populations decreased (increased) as we built' the first several dams. Adding more dams caused the number of persisting populations to decline and eroded genetic diversity within and among populations. Our second simulation experiment evaluated the effects of different levels of upstream and downstream migration between river segments. The results of these migration experiments highlighted the importance of balanced migration rates. We found that extinction risk was high for populations linked by high downstream, and low upstream, migration rates, as is often the case in impounded rivers. Our results support the view that migration patterns will play a significant role in determining the viability of riverine fishes, such as the white sturgeon, in river ecosystems fragmented by dams.

Notice en format standard (ISO 2709)

Pour connaître la documentation sur le format Inist Standard.

pA  
A01 01  1    @0 0378-1909
A02 01      @0 EBFID3
A03   1    @0 Environ. biol. fishes
A05       @2 60
A06       @2 4
A08 01  1  ENG  @1 A theoretical study of river fragmentation by dams and its effects on white sturgeon populations
A11 01  1    @1 JAGER (Henriette I.)
A11 02  1    @1 CHANDLER (James A.)
A11 03  1    @1 LEPLA (Kenneth B.)
A11 04  1    @1 VAN WINKLE (Webb)
A14 01      @1 Environmental Sciences Division, P.O. Box 2008, Oak Ridge National Laboratory @2 Oak Ridge, TN 37831-6036 @3 USA @Z 1 aut.
A14 02      @1 Aquatic Section, Environmental Affairs, Idaho Power Co. @2 Boise, ID 83702 @3 USA @Z 2 aut. @Z 3 aut.
A20       @1 347-361
A21       @1 2001
A23 01      @0 ENG
A43 01      @1 INIST @2 17564 @5 354000095137800030
A44       @0 0000 @1 © 2001 INIST-CNRS. All rights reserved.
A45       @0 1 p.3/4
A47 01  1    @0 01-0258604
A60       @1 P
A61       @0 A
A64 01  1    @0 Environmental biology of fishes
A66 01      @0 NLD
C01 01    ENG  @0 Most of the world's large rivers are fragmented by dams. Fragmentation of the river ecosystem alters migration patterns among fish populations and converts free-flowing river to reservoir habitat. In this study, we used an individual-based genetic metapopulation model to study the effects of fragmentation on the population viability and genetic diversity of a large-river fish, the white sturgeon, Acipenser transmontanus. In the first of two simulation experiments, we fragmented a 200 km river reach by building 1 to 20 virtual dams. Increased fragmentation produced an exponential decline in the likelihood of persistence, but no extinction threshold to suggest a minimum viable length of river. Compounding isolation with the loss of free-flowing habitat did not further reduce viability until free-flowing habitat was nearly eliminated, at which point extinction was certain. Genetic diversity within (among) populations decreased (increased) as we built' the first several dams. Adding more dams caused the number of persisting populations to decline and eroded genetic diversity within and among populations. Our second simulation experiment evaluated the effects of different levels of upstream and downstream migration between river segments. The results of these migration experiments highlighted the importance of balanced migration rates. We found that extinction risk was high for populations linked by high downstream, and low upstream, migration rates, as is often the case in impounded rivers. Our results support the view that migration patterns will play a significant role in determining the viability of riverine fishes, such as the white sturgeon, in river ecosystems fragmented by dams.
C02 01  X    @0 002A14D02C
C03 01  X  FRE  @0 Migration animale @5 01
C03 01  X  ENG  @0 Animal migration @5 01
C03 01  X  SPA  @0 Migración animal @5 01
C03 02  X  FRE  @0 Cours eau @5 02
C03 02  X  ENG  @0 Stream @5 02
C03 02  X  SPA  @0 Curso agua @5 02
C03 03  X  FRE  @0 Barrage @5 03
C03 03  X  ENG  @0 Dam @5 03
C03 03  X  SPA  @0 Presa @5 03
C03 04  X  FRE  @0 Bassin retenue @5 04
C03 04  X  ENG  @0 Impoundment @5 04
C03 04  X  SPA  @0 Presa retención @5 04
C03 05  X  FRE  @0 Lac artificiel @5 05
C03 05  X  ENG  @0 Artificial lake @5 05
C03 05  X  SPA  @0 Lago artificial @5 05
C03 06  X  FRE  @0 Diversité génétique @5 06
C03 06  X  ENG  @0 Genetic diversity @5 06
C03 06  X  SPA  @0 Diversidad genética @5 06
C03 07  X  FRE  @0 Démographie @5 07
C03 07  X  ENG  @0 Demography @5 07
C03 07  X  SPA  @0 Demografía @5 07
C03 08  X  FRE  @0 Modèle simulation @5 08
C03 08  X  ENG  @0 Simulation model @5 08
C03 08  X  SPA  @0 Modelo simulación @5 08
C03 09  X  FRE  @0 Métapopulation @5 09
C03 09  X  ENG  @0 Metapopulation @5 09
C03 09  X  SPA  @0 Metapoblación @5 09
C03 10  X  FRE  @0 Gestion population @5 10
C03 10  X  ENG  @0 Population management @5 10
C03 10  X  SPA  @0 Gestión población @5 10
C03 11  X  FRE  @0 Etats Unis @2 NG @5 11
C03 11  X  ENG  @0 United States @2 NG @5 11
C03 11  X  SPA  @0 Estados Unidos @2 NG @5 11
C03 12  X  FRE  @0 Fragmentation @5 12
C03 12  X  ENG  @0 Fragmentation @5 12
C03 12  X  SPA  @0 Fragmentación @5 12
C03 13  X  FRE  @0 Habitat @5 13
C03 13  X  ENG  @0 Habitat @5 13
C03 13  X  SPA  @0 Habitat @5 13
C03 14  X  FRE  @0 Acipenser transmontanus @2 NS @5 55
C03 14  X  ENG  @0 Acipenser transmontanus @2 NS @5 55
C03 14  X  SPA  @0 Acipenser transmontanus @2 NS @5 55
C03 15  X  FRE  @0 Rivière Columbia @2 NG @4 INC @5 89
C03 16  X  FRE  @0 Espèce anadrome @4 CD @5 96
C03 16  X  ENG  @0 Anadromous species @4 CD @5 96
C03 17  X  FRE  @0 Rivière Snake @2 NG @4 CD @5 97
C03 17  X  ENG  @0 Snake River @2 NG @4 CD @5 97
C07 01  X  FRE  @0 Amérique du Nord @2 NG
C07 01  X  ENG  @0 North America @2 NG
C07 01  X  SPA  @0 America del norte @2 NG
C07 02  X  FRE  @0 Amérique @2 NG
C07 02  X  ENG  @0 America @2 NG
C07 02  X  SPA  @0 America @2 NG
C07 03  X  FRE  @0 Milieu eau douce @5 17
C07 03  X  ENG  @0 Freshwater environment @5 17
C07 03  X  SPA  @0 Medio agua dulce @5 17
C07 04  X  FRE  @0 Facteur milieu @5 18
C07 04  X  ENG  @0 Environmental factor @5 18
C07 04  X  SPA  @0 Factor medio @5 18
C07 05  X  FRE  @0 Pisces @2 NS
C07 05  X  ENG  @0 Pisces @2 NS
C07 05  X  SPA  @0 Pisces @2 NS
C07 06  X  FRE  @0 Vertebrata @2 NS
C07 06  X  ENG  @0 Vertebrata @2 NS
C07 06  X  SPA  @0 Vertebrata @2 NS
C07 07  X  FRE  @0 Acipenseridae @2 NS @4 INC @5 70
N21       @1 176

Format Inist (serveur)

NO : PASCAL 01-0258604 INIST
ET : A theoretical study of river fragmentation by dams and its effects on white sturgeon populations
AU : JAGER (Henriette I.); CHANDLER (James A.); LEPLA (Kenneth B.); VAN WINKLE (Webb)
AF : Environmental Sciences Division, P.O. Box 2008, Oak Ridge National Laboratory/Oak Ridge, TN 37831-6036/Etats-Unis (1 aut.); Aquatic Section, Environmental Affairs, Idaho Power Co./Boise, ID 83702/Etats-Unis (2 aut., 3 aut.)
DT : Publication en série; Niveau analytique
SO : Environmental biology of fishes; ISSN 0378-1909; Coden EBFID3; Pays-Bas; Da. 2001; Vol. 60; No. 4; Pp. 347-361; Bibl. 1 p.3/4
LA : Anglais
EA : Most of the world's large rivers are fragmented by dams. Fragmentation of the river ecosystem alters migration patterns among fish populations and converts free-flowing river to reservoir habitat. In this study, we used an individual-based genetic metapopulation model to study the effects of fragmentation on the population viability and genetic diversity of a large-river fish, the white sturgeon, Acipenser transmontanus. In the first of two simulation experiments, we fragmented a 200 km river reach by building 1 to 20 virtual dams. Increased fragmentation produced an exponential decline in the likelihood of persistence, but no extinction threshold to suggest a minimum viable length of river. Compounding isolation with the loss of free-flowing habitat did not further reduce viability until free-flowing habitat was nearly eliminated, at which point extinction was certain. Genetic diversity within (among) populations decreased (increased) as we built' the first several dams. Adding more dams caused the number of persisting populations to decline and eroded genetic diversity within and among populations. Our second simulation experiment evaluated the effects of different levels of upstream and downstream migration between river segments. The results of these migration experiments highlighted the importance of balanced migration rates. We found that extinction risk was high for populations linked by high downstream, and low upstream, migration rates, as is often the case in impounded rivers. Our results support the view that migration patterns will play a significant role in determining the viability of riverine fishes, such as the white sturgeon, in river ecosystems fragmented by dams.
CC : 002A14D02C
FD : Migration animale; Cours eau; Barrage; Bassin retenue; Lac artificiel; Diversité génétique; Démographie; Modèle simulation; Métapopulation; Gestion population; Etats Unis; Fragmentation; Habitat; Acipenser transmontanus; Rivière Columbia; Espèce anadrome; Rivière Snake
FG : Amérique du Nord; Amérique; Milieu eau douce; Facteur milieu; Pisces; Vertebrata; Acipenseridae
ED : Animal migration; Stream; Dam; Impoundment; Artificial lake; Genetic diversity; Demography; Simulation model; Metapopulation; Population management; United States; Fragmentation; Habitat; Acipenser transmontanus; Anadromous species; Snake River
EG : North America; America; Freshwater environment; Environmental factor; Pisces; Vertebrata
SD : Migración animal; Curso agua; Presa; Presa retención; Lago artificial; Diversidad genética; Demografía; Modelo simulación; Metapoblación; Gestión población; Estados Unidos; Fragmentación; Habitat; Acipenser transmontanus
LO : INIST-17564.354000095137800030
ID : 01-0258604

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Pascal:01-0258604

Le document en format XML

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<term>Demography</term>
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<div type="abstract" xml:lang="en">Most of the world's large rivers are fragmented by dams. Fragmentation of the river ecosystem alters migration patterns among fish populations and converts free-flowing river to reservoir habitat. In this study, we used an individual-based genetic metapopulation model to study the effects of fragmentation on the population viability and genetic diversity of a large-river fish, the white sturgeon, Acipenser transmontanus. In the first of two simulation experiments, we fragmented a 200 km river reach by building 1 to 20 virtual dams. Increased fragmentation produced an exponential decline in the likelihood of persistence, but no extinction threshold to suggest a minimum viable length of river. Compounding isolation with the loss of free-flowing habitat did not further reduce viability until free-flowing habitat was nearly eliminated, at which point extinction was certain. Genetic diversity within (among) populations decreased (increased) as we built' the first several dams. Adding more dams caused the number of persisting populations to decline and eroded genetic diversity within and among populations. Our second simulation experiment evaluated the effects of different levels of upstream and downstream migration between river segments. The results of these migration experiments highlighted the importance of balanced migration rates. We found that extinction risk was high for populations linked by high downstream, and low upstream, migration rates, as is often the case in impounded rivers. Our results support the view that migration patterns will play a significant role in determining the viability of riverine fishes, such as the white sturgeon, in river ecosystems fragmented by dams.</div>
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<s0>Artificial lake</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA">
<s0>Lago artificial</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE">
<s0>Diversité génétique</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG">
<s0>Genetic diversity</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA">
<s0>Diversidad genética</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE">
<s0>Démographie</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG">
<s0>Demography</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA">
<s0>Demografía</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE">
<s0>Modèle simulation</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG">
<s0>Simulation model</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA">
<s0>Modelo simulación</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE">
<s0>Métapopulation</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG">
<s0>Metapopulation</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA">
<s0>Metapoblación</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE">
<s0>Gestion population</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG">
<s0>Population management</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA">
<s0>Gestión población</s0>
<s5>10</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE">
<s0>Etats Unis</s0>
<s2>NG</s2>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="X" l="ENG">
<s0>United States</s0>
<s2>NG</s2>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="X" l="SPA">
<s0>Estados Unidos</s0>
<s2>NG</s2>
<s5>11</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE">
<s0>Fragmentation</s0>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="ENG">
<s0>Fragmentation</s0>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="SPA">
<s0>Fragmentación</s0>
<s5>12</s5>
</fC03>
<fC03 i1="13" i2="X" l="FRE">
<s0>Habitat</s0>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="ENG">
<s0>Habitat</s0>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="SPA">
<s0>Habitat</s0>
<s5>13</s5>
</fC03>
<fC03 i1="14" i2="X" l="FRE">
<s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>55</s5>
</fC03>
<fC03 i1="14" i2="X" l="ENG">
<s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>55</s5>
</fC03>
<fC03 i1="14" i2="X" l="SPA">
<s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>55</s5>
</fC03>
<fC03 i1="15" i2="X" l="FRE">
<s0>Rivière Columbia</s0>
<s2>NG</s2>
<s4>INC</s4>
<s5>89</s5>
</fC03>
<fC03 i1="16" i2="X" l="FRE">
<s0>Espèce anadrome</s0>
<s4>CD</s4>
<s5>96</s5>
</fC03>
<fC03 i1="16" i2="X" l="ENG">
<s0>Anadromous species</s0>
<s4>CD</s4>
<s5>96</s5>
</fC03>
<fC03 i1="17" i2="X" l="FRE">
<s0>Rivière Snake</s0>
<s2>NG</s2>
<s4>CD</s4>
<s5>97</s5>
</fC03>
<fC03 i1="17" i2="X" l="ENG">
<s0>Snake River</s0>
<s2>NG</s2>
<s4>CD</s4>
<s5>97</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE">
<s0>Amérique du Nord</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="X" l="ENG">
<s0>North America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="X" l="SPA">
<s0>America del norte</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="FRE">
<s0>Amérique</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="ENG">
<s0>America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="SPA">
<s0>America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="03" i2="X" l="FRE">
<s0>Milieu eau douce</s0>
<s5>17</s5>
</fC07>
<fC07 i1="03" i2="X" l="ENG">
<s0>Freshwater environment</s0>
<s5>17</s5>
</fC07>
<fC07 i1="03" i2="X" l="SPA">
<s0>Medio agua dulce</s0>
<s5>17</s5>
</fC07>
<fC07 i1="04" i2="X" l="FRE">
<s0>Facteur milieu</s0>
<s5>18</s5>
</fC07>
<fC07 i1="04" i2="X" l="ENG">
<s0>Environmental factor</s0>
<s5>18</s5>
</fC07>
<fC07 i1="04" i2="X" l="SPA">
<s0>Factor medio</s0>
<s5>18</s5>
</fC07>
<fC07 i1="05" i2="X" l="FRE">
<s0>Pisces</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="ENG">
<s0>Pisces</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="SPA">
<s0>Pisces</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="FRE">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="ENG">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="SPA">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="FRE">
<s0>Acipenseridae</s0>
<s2>NS</s2>
<s4>INC</s4>
<s5>70</s5>
</fC07>
<fN21>
<s1>176</s1>
</fN21>
</pA>
</standard>
<server>
<NO>PASCAL 01-0258604 INIST</NO>
<ET>A theoretical study of river fragmentation by dams and its effects on white sturgeon populations</ET>
<AU>JAGER (Henriette I.); CHANDLER (James A.); LEPLA (Kenneth B.); VAN WINKLE (Webb)</AU>
<AF>Environmental Sciences Division, P.O. Box 2008, Oak Ridge National Laboratory/Oak Ridge, TN 37831-6036/Etats-Unis (1 aut.); Aquatic Section, Environmental Affairs, Idaho Power Co./Boise, ID 83702/Etats-Unis (2 aut., 3 aut.)</AF>
<DT>Publication en série; Niveau analytique</DT>
<SO>Environmental biology of fishes; ISSN 0378-1909; Coden EBFID3; Pays-Bas; Da. 2001; Vol. 60; No. 4; Pp. 347-361; Bibl. 1 p.3/4</SO>
<LA>Anglais</LA>
<EA>Most of the world's large rivers are fragmented by dams. Fragmentation of the river ecosystem alters migration patterns among fish populations and converts free-flowing river to reservoir habitat. In this study, we used an individual-based genetic metapopulation model to study the effects of fragmentation on the population viability and genetic diversity of a large-river fish, the white sturgeon, Acipenser transmontanus. In the first of two simulation experiments, we fragmented a 200 km river reach by building 1 to 20 virtual dams. Increased fragmentation produced an exponential decline in the likelihood of persistence, but no extinction threshold to suggest a minimum viable length of river. Compounding isolation with the loss of free-flowing habitat did not further reduce viability until free-flowing habitat was nearly eliminated, at which point extinction was certain. Genetic diversity within (among) populations decreased (increased) as we built' the first several dams. Adding more dams caused the number of persisting populations to decline and eroded genetic diversity within and among populations. Our second simulation experiment evaluated the effects of different levels of upstream and downstream migration between river segments. The results of these migration experiments highlighted the importance of balanced migration rates. We found that extinction risk was high for populations linked by high downstream, and low upstream, migration rates, as is often the case in impounded rivers. Our results support the view that migration patterns will play a significant role in determining the viability of riverine fishes, such as the white sturgeon, in river ecosystems fragmented by dams.</EA>
<CC>002A14D02C</CC>
<FD>Migration animale; Cours eau; Barrage; Bassin retenue; Lac artificiel; Diversité génétique; Démographie; Modèle simulation; Métapopulation; Gestion population; Etats Unis; Fragmentation; Habitat; Acipenser transmontanus; Rivière Columbia; Espèce anadrome; Rivière Snake</FD>
<FG>Amérique du Nord; Amérique; Milieu eau douce; Facteur milieu; Pisces; Vertebrata; Acipenseridae</FG>
<ED>Animal migration; Stream; Dam; Impoundment; Artificial lake; Genetic diversity; Demography; Simulation model; Metapopulation; Population management; United States; Fragmentation; Habitat; Acipenser transmontanus; Anadromous species; Snake River</ED>
<EG>North America; America; Freshwater environment; Environmental factor; Pisces; Vertebrata</EG>
<SD>Migración animal; Curso agua; Presa; Presa retención; Lago artificial; Diversidad genética; Demografía; Modelo simulación; Metapoblación; Gestión población; Estados Unidos; Fragmentación; Habitat; Acipenser transmontanus</SD>
<LO>INIST-17564.354000095137800030</LO>
<ID>01-0258604</ID>
</server>
</inist>
</record>

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