Serveur d'exploration sur l'esturgeon

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Primary factors affecting sturgeon populations in the Southeastern United States : Fishing mortality and degradation of essential habitats

Identifieur interne : 000358 ( PascalFrancis/Corpus ); précédent : 000357; suivant : 000359

Primary factors affecting sturgeon populations in the Southeastern United States : Fishing mortality and degradation of essential habitats

Auteurs : Mark R. Collins ; S. Gordon Rogers ; Theodore I. J. Smith ; Mary L. Moser

Source :

RBID : Pascal:00-0448958

Descripteurs français

English descriptors

Abstract

Atlantic and shortnose sturgeons are highly valued for their eggs (caviar) and flesh, but stocks of both species are depleted. The shortnose sturgeon is listed as an endangered species, and a long-term (multidecade) moratorium on fishing for Atlantic sturgeon is specified in the recently updated fishery management plan of the Atlantic States Marine Fisheries Commission. Thus, identification, protection, and enhancement of essential habitats are priority issues for management agencies. As anadromous (Atlantic) and nearly anadromous (shortnose) species, these sturgeons use a wide variety of habitats; variations occur latitudinally, seasonally, and among different life stages. Spawning habitats have been identified in two southeastern rivers for shortnose sturgeon, but to date no spawning sites have been verified for Atlantic sturgeon. Some life stages of both species (including young juveniles) concentrate in or are restricted to small portions of estuaries during summer. Deterioration of water quality (especially dissolved oxygen) appears to be degrading the nursery function of these summer refugia, creating a recruitment bottleneck. Protection of essential habitats, especially nursery/summer habitats, from human-caused dissolved-oxygen reductions and other impacts is critical. By-catch, primarily in riverine/estuarine gillnet and estuarine/marine trawl fisheries, appears to be the second major source of mortality for southern sturgeons. Reserves, or no-fishing zones, could protect populations by reducing or eliminating by-catch mortality. This protection would be especially valuable in high salinity foraging areas (used primarily during cool months) and during spawning migrations. Proposed management strategies aimed at conservation and restoration of sturgeon populations therefore focus on two areas: protection of essential habitats and establishment of reserves to provide protection from fishing gears that generate substantial sturgeon by-catch. Specific management recommendations were developed on a system-by-system basis.

Notice en format standard (ISO 2709)

Pour connaître la documentation sur le format Inist Standard.

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A01 01  1    @0 0007-4977
A02 01      @0 BMRSAW
A03   1    @0 Bull. mar. sci.
A05       @2 66
A06       @2 3
A08 01  1  ENG  @1 Primary factors affecting sturgeon populations in the Southeastern United States : Fishing mortality and degradation of essential habitats
A09 01  1  ENG  @1 Essential Fish Habitat and Marine Reserves
A11 01  1    @1 COLLINS (Mark R.)
A11 02  1    @1 ROGERS (S. Gordon)
A11 03  1    @1 SMITH (Theodore I. J.)
A11 04  1    @1 MOSER (Mary L.)
A12 01  1    @1 COLEMAN (Felicia) @9 ed.
A12 02  1    @1 TRAVIS (Joseph) @9 ed.
A14 01      @1 South Carolina Department of Natural Resources, Marine Resources Research Institute, P.O. Box 12559 @2 Charleston, South Carolina 29422 @3 USA @Z 1 aut. @Z 3 aut.
A14 02      @1 Satilla Management Associates, Inc., P.O. Box 177 @2 Waynesville, Georgia 31566 @3 USA @Z 2 aut.
A14 03      @1 University of North Carolina-Wilmington, Center for Marine Science Research, 7205 Wrightsville Ave. @2 Wilmington, North Carolina 28403 @3 USA @Z 4 aut.
A15 01      @1 Florida State University @3 USA @Z 1 aut. @Z 2 aut.
A20       @1 917-928
A21       @1 2000
A23 01      @0 ENG
A43 01      @1 INIST @2 11286 @5 354000091314920260
A44       @0 0000 @1 © 2000 INIST-CNRS. All rights reserved.
A45       @0 1 p.1/4
A47 01  1    @0 00-0448958
A60       @1 P @2 C
A61       @0 A
A64 01  1    @0 Bulletin of marine science
A66 01      @0 USA
C01 01    ENG  @0 Atlantic and shortnose sturgeons are highly valued for their eggs (caviar) and flesh, but stocks of both species are depleted. The shortnose sturgeon is listed as an endangered species, and a long-term (multidecade) moratorium on fishing for Atlantic sturgeon is specified in the recently updated fishery management plan of the Atlantic States Marine Fisheries Commission. Thus, identification, protection, and enhancement of essential habitats are priority issues for management agencies. As anadromous (Atlantic) and nearly anadromous (shortnose) species, these sturgeons use a wide variety of habitats; variations occur latitudinally, seasonally, and among different life stages. Spawning habitats have been identified in two southeastern rivers for shortnose sturgeon, but to date no spawning sites have been verified for Atlantic sturgeon. Some life stages of both species (including young juveniles) concentrate in or are restricted to small portions of estuaries during summer. Deterioration of water quality (especially dissolved oxygen) appears to be degrading the nursery function of these summer refugia, creating a recruitment bottleneck. Protection of essential habitats, especially nursery/summer habitats, from human-caused dissolved-oxygen reductions and other impacts is critical. By-catch, primarily in riverine/estuarine gillnet and estuarine/marine trawl fisheries, appears to be the second major source of mortality for southern sturgeons. Reserves, or no-fishing zones, could protect populations by reducing or eliminating by-catch mortality. This protection would be especially valuable in high salinity foraging areas (used primarily during cool months) and during spawning migrations. Proposed management strategies aimed at conservation and restoration of sturgeon populations therefore focus on two areas: protection of essential habitats and establishment of reserves to provide protection from fishing gears that generate substantial sturgeon by-catch. Specific management recommendations were developed on a system-by-system basis.
C02 01  X    @0 002A14D02B
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C03 01  X  ENG  @0 Endangered species @5 01
C03 01  X  SPA  @0 Especie amenazada @5 01
C03 02  X  FRE  @0 Déclin population @5 02
C03 02  X  ENG  @0 Population decline @5 02
C03 02  X  SPA  @0 Declinación poblacional @5 02
C03 03  X  FRE  @0 Habitat @5 03
C03 03  X  ENG  @0 Habitat @5 03
C03 03  X  SPA  @0 Habitat @5 03
C03 04  X  FRE  @0 Mortalité @5 04
C03 04  X  ENG  @0 Mortality @5 04
C03 04  X  SPA  @0 Mortalidad @5 04
C03 05  X  FRE  @0 Prise accessoire @5 05
C03 05  X  ENG  @0 By-catches @5 05
C03 05  X  SPA  @0 Presa accesoria @5 05
C03 06  X  FRE  @0 Pêcherie @5 06
C03 06  X  ENG  @0 Fishery @5 06
C03 06  X  SPA  @0 Pesquería @5 06
C03 07  X  FRE  @0 Dégradation environnement @5 07
C03 07  X  ENG  @0 Ecological damage @5 07
C03 07  X  SPA  @0 Degradación ecológica @5 07
C03 08  X  FRE  @0 Gestion population @5 08
C03 08  X  ENG  @0 Population management @5 08
C03 08  X  SPA  @0 Gestión población @5 08
C03 09  X  FRE  @0 Recommandation @5 09
C03 09  X  ENG  @0 Recommendation @5 09
C03 09  X  SPA  @0 Recomendación @5 09
C03 10  X  FRE  @0 Géorgie @2 NG @5 11
C03 10  X  ENG  @0 Georgia @2 NG @5 11
C03 10  X  SPA  @0 Georgia @2 NG @5 11
C03 11  X  FRE  @0 Caroline du Nord @2 NG @5 12
C03 11  X  ENG  @0 North Carolina @2 NG @5 12
C03 11  X  SPA  @0 Carolina del norte @2 NG @5 12
C03 12  X  FRE  @0 Caroline du Sud @2 NG @5 13
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C03 12  X  SPA  @0 Carolina del Sur @2 NG @5 13
C03 13  X  FRE  @0 Acipenser brevisrostrum @2 NS @4 INC @5 64
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C07 02  X  SPA  @0 America del norte @2 NG
C07 03  X  FRE  @0 Amérique @2 NG
C07 03  X  ENG  @0 America @2 NG
C07 03  X  SPA  @0 America @2 NG
C07 04  X  FRE  @0 Protection faune @5 17
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C07 05  X  ENG  @0 Environmental protection @5 18
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C07 06  X  FRE  @0 Milieu aquatique @5 19
C07 06  X  ENG  @0 Aquatic environment @5 19
C07 06  X  SPA  @0 Medio acuático @5 19
C07 07  X  FRE  @0 Pisces @2 NS @5 60
C07 07  X  ENG  @0 Pisces @2 NS @5 60
C07 07  X  SPA  @0 Pisces @2 NS @5 60
C07 08  X  FRE  @0 Vertebrata @2 NS
C07 08  X  ENG  @0 Vertebrata @2 NS
C07 08  X  SPA  @0 Vertebrata @2 NS
C07 09  X  FRE  @0 Acipenseridae @2 NS @4 INC @5 70
N21       @1 297
pR  
A30 01  1  ENG  @1 William R. and Lenore Mote International Symposium in Fisheries Ecology @2 2 @3 Sarasota, Florida USA @4 1998-11-04

Format Inist (serveur)

NO : PASCAL 00-0448958 INIST
ET : Primary factors affecting sturgeon populations in the Southeastern United States : Fishing mortality and degradation of essential habitats
AU : COLLINS (Mark R.); ROGERS (S. Gordon); SMITH (Theodore I. J.); MOSER (Mary L.); COLEMAN (Felicia); TRAVIS (Joseph)
AF : South Carolina Department of Natural Resources, Marine Resources Research Institute, P.O. Box 12559/Charleston, South Carolina 29422/Etats-Unis (1 aut., 3 aut.); Satilla Management Associates, Inc., P.O. Box 177/Waynesville, Georgia 31566/Etats-Unis (2 aut.); University of North Carolina-Wilmington, Center for Marine Science Research, 7205 Wrightsville Ave./Wilmington, North Carolina 28403/Etats-Unis (4 aut.); Florida State University/Etats-Unis (1 aut., 2 aut.)
DT : Publication en série; Congrès; Niveau analytique
SO : Bulletin of marine science; ISSN 0007-4977; Coden BMRSAW; Etats-Unis; Da. 2000; Vol. 66; No. 3; Pp. 917-928; Bibl. 1 p.1/4
LA : Anglais
EA : Atlantic and shortnose sturgeons are highly valued for their eggs (caviar) and flesh, but stocks of both species are depleted. The shortnose sturgeon is listed as an endangered species, and a long-term (multidecade) moratorium on fishing for Atlantic sturgeon is specified in the recently updated fishery management plan of the Atlantic States Marine Fisheries Commission. Thus, identification, protection, and enhancement of essential habitats are priority issues for management agencies. As anadromous (Atlantic) and nearly anadromous (shortnose) species, these sturgeons use a wide variety of habitats; variations occur latitudinally, seasonally, and among different life stages. Spawning habitats have been identified in two southeastern rivers for shortnose sturgeon, but to date no spawning sites have been verified for Atlantic sturgeon. Some life stages of both species (including young juveniles) concentrate in or are restricted to small portions of estuaries during summer. Deterioration of water quality (especially dissolved oxygen) appears to be degrading the nursery function of these summer refugia, creating a recruitment bottleneck. Protection of essential habitats, especially nursery/summer habitats, from human-caused dissolved-oxygen reductions and other impacts is critical. By-catch, primarily in riverine/estuarine gillnet and estuarine/marine trawl fisheries, appears to be the second major source of mortality for southern sturgeons. Reserves, or no-fishing zones, could protect populations by reducing or eliminating by-catch mortality. This protection would be especially valuable in high salinity foraging areas (used primarily during cool months) and during spawning migrations. Proposed management strategies aimed at conservation and restoration of sturgeon populations therefore focus on two areas: protection of essential habitats and establishment of reserves to provide protection from fishing gears that generate substantial sturgeon by-catch. Specific management recommendations were developed on a system-by-system basis.
CC : 002A14D02B
FD : Espèce menacée; Déclin population; Habitat; Mortalité; Prise accessoire; Pêcherie; Dégradation environnement; Gestion population; Recommandation; Géorgie; Caroline du Nord; Caroline du Sud; Acipenser brevisrostrum; Acipenser oxyrinchus
FG : Etats Unis; Amérique du Nord; Amérique; Protection faune; Protection environnement; Milieu aquatique; Pisces; Vertebrata; Acipenseridae
ED : Endangered species; Population decline; Habitat; Mortality; By-catches; Fishery; Ecological damage; Population management; Recommendation; Georgia; North Carolina; South Carolina
EG : United States; North America; America; Animal conservation; Environmental protection; Aquatic environment; Pisces; Vertebrata
SD : Especie amenazada; Declinación poblacional; Habitat; Mortalidad; Presa accesoria; Pesquería; Degradación ecológica; Gestión población; Recomendación; Georgia; Carolina del norte; Carolina del Sur
LO : INIST-11286.354000091314920260
ID : 00-0448958

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Pascal:00-0448958

Le document en format XML

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<div type="abstract" xml:lang="en">Atlantic and shortnose sturgeons are highly valued for their eggs (caviar) and flesh, but stocks of both species are depleted. The shortnose sturgeon is listed as an endangered species, and a long-term (multidecade) moratorium on fishing for Atlantic sturgeon is specified in the recently updated fishery management plan of the Atlantic States Marine Fisheries Commission. Thus, identification, protection, and enhancement of essential habitats are priority issues for management agencies. As anadromous (Atlantic) and nearly anadromous (shortnose) species, these sturgeons use a wide variety of habitats; variations occur latitudinally, seasonally, and among different life stages. Spawning habitats have been identified in two southeastern rivers for shortnose sturgeon, but to date no spawning sites have been verified for Atlantic sturgeon. Some life stages of both species (including young juveniles) concentrate in or are restricted to small portions of estuaries during summer. Deterioration of water quality (especially dissolved oxygen) appears to be degrading the nursery function of these summer refugia, creating a recruitment bottleneck. Protection of essential habitats, especially nursery/summer habitats, from human-caused dissolved-oxygen reductions and other impacts is critical. By-catch, primarily in riverine/estuarine gillnet and estuarine/marine trawl fisheries, appears to be the second major source of mortality for southern sturgeons. Reserves, or no-fishing zones, could protect populations by reducing or eliminating by-catch mortality. This protection would be especially valuable in high salinity foraging areas (used primarily during cool months) and during spawning migrations. Proposed management strategies aimed at conservation and restoration of sturgeon populations therefore focus on two areas: protection of essential habitats and establishment of reserves to provide protection from fishing gears that generate substantial sturgeon by-catch. Specific management recommendations were developed on a system-by-system basis.</div>
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<fC01 i1="01" l="ENG">
<s0>Atlantic and shortnose sturgeons are highly valued for their eggs (caviar) and flesh, but stocks of both species are depleted. The shortnose sturgeon is listed as an endangered species, and a long-term (multidecade) moratorium on fishing for Atlantic sturgeon is specified in the recently updated fishery management plan of the Atlantic States Marine Fisheries Commission. Thus, identification, protection, and enhancement of essential habitats are priority issues for management agencies. As anadromous (Atlantic) and nearly anadromous (shortnose) species, these sturgeons use a wide variety of habitats; variations occur latitudinally, seasonally, and among different life stages. Spawning habitats have been identified in two southeastern rivers for shortnose sturgeon, but to date no spawning sites have been verified for Atlantic sturgeon. Some life stages of both species (including young juveniles) concentrate in or are restricted to small portions of estuaries during summer. Deterioration of water quality (especially dissolved oxygen) appears to be degrading the nursery function of these summer refugia, creating a recruitment bottleneck. Protection of essential habitats, especially nursery/summer habitats, from human-caused dissolved-oxygen reductions and other impacts is critical. By-catch, primarily in riverine/estuarine gillnet and estuarine/marine trawl fisheries, appears to be the second major source of mortality for southern sturgeons. Reserves, or no-fishing zones, could protect populations by reducing or eliminating by-catch mortality. This protection would be especially valuable in high salinity foraging areas (used primarily during cool months) and during spawning migrations. Proposed management strategies aimed at conservation and restoration of sturgeon populations therefore focus on two areas: protection of essential habitats and establishment of reserves to provide protection from fishing gears that generate substantial sturgeon by-catch. Specific management recommendations were developed on a system-by-system basis.</s0>
</fC01>
<fC02 i1="01" i2="X">
<s0>002A14D02B</s0>
</fC02>
<fC03 i1="01" i2="X" l="FRE">
<s0>Espèce menacée</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG">
<s0>Endangered species</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="SPA">
<s0>Especie amenazada</s0>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE">
<s0>Déclin population</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="ENG">
<s0>Population decline</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="SPA">
<s0>Declinación poblacional</s0>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE">
<s0>Habitat</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG">
<s0>Habitat</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA">
<s0>Habitat</s0>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE">
<s0>Mortalité</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG">
<s0>Mortality</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA">
<s0>Mortalidad</s0>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE">
<s0>Prise accessoire</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG">
<s0>By-catches</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA">
<s0>Presa accesoria</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE">
<s0>Pêcherie</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG">
<s0>Fishery</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA">
<s0>Pesquería</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE">
<s0>Dégradation environnement</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG">
<s0>Ecological damage</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA">
<s0>Degradación ecológica</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE">
<s0>Gestion population</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG">
<s0>Population management</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA">
<s0>Gestión población</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE">
<s0>Recommandation</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG">
<s0>Recommendation</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA">
<s0>Recomendación</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE">
<s0>Géorgie</s0>
<s2>NG</s2>
<s5>11</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG">
<s0>Georgia</s0>
<s2>NG</s2>
<s5>11</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA">
<s0>Georgia</s0>
<s2>NG</s2>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE">
<s0>Caroline du Nord</s0>
<s2>NG</s2>
<s5>12</s5>
</fC03>
<fC03 i1="11" i2="X" l="ENG">
<s0>North Carolina</s0>
<s2>NG</s2>
<s5>12</s5>
</fC03>
<fC03 i1="11" i2="X" l="SPA">
<s0>Carolina del norte</s0>
<s2>NG</s2>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE">
<s0>Caroline du Sud</s0>
<s2>NG</s2>
<s5>13</s5>
</fC03>
<fC03 i1="12" i2="X" l="ENG">
<s0>South Carolina</s0>
<s2>NG</s2>
<s5>13</s5>
</fC03>
<fC03 i1="12" i2="X" l="SPA">
<s0>Carolina del Sur</s0>
<s2>NG</s2>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="FRE">
<s0>Acipenser brevisrostrum</s0>
<s2>NS</s2>
<s4>INC</s4>
<s5>64</s5>
</fC03>
<fC03 i1="14" i2="X" l="FRE">
<s0>Acipenser oxyrinchus</s0>
<s2>NS</s2>
<s4>INC</s4>
<s5>65</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE">
<s0>Etats Unis</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="X" l="ENG">
<s0>United States</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="X" l="SPA">
<s0>Estados Unidos</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="FRE">
<s0>Amérique du Nord</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="ENG">
<s0>North America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="SPA">
<s0>America del norte</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="03" i2="X" l="FRE">
<s0>Amérique</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="03" i2="X" l="ENG">
<s0>America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="03" i2="X" l="SPA">
<s0>America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="04" i2="X" l="FRE">
<s0>Protection faune</s0>
<s5>17</s5>
</fC07>
<fC07 i1="04" i2="X" l="ENG">
<s0>Animal conservation</s0>
<s5>17</s5>
</fC07>
<fC07 i1="04" i2="X" l="SPA">
<s0>Protección fauna</s0>
<s5>17</s5>
</fC07>
<fC07 i1="05" i2="X" l="FRE">
<s0>Protection environnement</s0>
<s5>18</s5>
</fC07>
<fC07 i1="05" i2="X" l="ENG">
<s0>Environmental protection</s0>
<s5>18</s5>
</fC07>
<fC07 i1="05" i2="X" l="SPA">
<s0>Protección medio ambiente</s0>
<s5>18</s5>
</fC07>
<fC07 i1="06" i2="X" l="FRE">
<s0>Milieu aquatique</s0>
<s5>19</s5>
</fC07>
<fC07 i1="06" i2="X" l="ENG">
<s0>Aquatic environment</s0>
<s5>19</s5>
</fC07>
<fC07 i1="06" i2="X" l="SPA">
<s0>Medio acuático</s0>
<s5>19</s5>
</fC07>
<fC07 i1="07" i2="X" l="FRE">
<s0>Pisces</s0>
<s2>NS</s2>
<s5>60</s5>
</fC07>
<fC07 i1="07" i2="X" l="ENG">
<s0>Pisces</s0>
<s2>NS</s2>
<s5>60</s5>
</fC07>
<fC07 i1="07" i2="X" l="SPA">
<s0>Pisces</s0>
<s2>NS</s2>
<s5>60</s5>
</fC07>
<fC07 i1="08" i2="X" l="FRE">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="08" i2="X" l="ENG">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="08" i2="X" l="SPA">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="09" i2="X" l="FRE">
<s0>Acipenseridae</s0>
<s2>NS</s2>
<s4>INC</s4>
<s5>70</s5>
</fC07>
<fN21>
<s1>297</s1>
</fN21>
</pA>
<pR>
<fA30 i1="01" i2="1" l="ENG">
<s1>William R. and Lenore Mote International Symposium in Fisheries Ecology</s1>
<s2>2</s2>
<s3>Sarasota, Florida USA</s3>
<s4>1998-11-04</s4>
</fA30>
</pR>
</standard>
<server>
<NO>PASCAL 00-0448958 INIST</NO>
<ET>Primary factors affecting sturgeon populations in the Southeastern United States : Fishing mortality and degradation of essential habitats</ET>
<AU>COLLINS (Mark R.); ROGERS (S. Gordon); SMITH (Theodore I. J.); MOSER (Mary L.); COLEMAN (Felicia); TRAVIS (Joseph)</AU>
<AF>South Carolina Department of Natural Resources, Marine Resources Research Institute, P.O. Box 12559/Charleston, South Carolina 29422/Etats-Unis (1 aut., 3 aut.); Satilla Management Associates, Inc., P.O. Box 177/Waynesville, Georgia 31566/Etats-Unis (2 aut.); University of North Carolina-Wilmington, Center for Marine Science Research, 7205 Wrightsville Ave./Wilmington, North Carolina 28403/Etats-Unis (4 aut.); Florida State University/Etats-Unis (1 aut., 2 aut.)</AF>
<DT>Publication en série; Congrès; Niveau analytique</DT>
<SO>Bulletin of marine science; ISSN 0007-4977; Coden BMRSAW; Etats-Unis; Da. 2000; Vol. 66; No. 3; Pp. 917-928; Bibl. 1 p.1/4</SO>
<LA>Anglais</LA>
<EA>Atlantic and shortnose sturgeons are highly valued for their eggs (caviar) and flesh, but stocks of both species are depleted. The shortnose sturgeon is listed as an endangered species, and a long-term (multidecade) moratorium on fishing for Atlantic sturgeon is specified in the recently updated fishery management plan of the Atlantic States Marine Fisheries Commission. Thus, identification, protection, and enhancement of essential habitats are priority issues for management agencies. As anadromous (Atlantic) and nearly anadromous (shortnose) species, these sturgeons use a wide variety of habitats; variations occur latitudinally, seasonally, and among different life stages. Spawning habitats have been identified in two southeastern rivers for shortnose sturgeon, but to date no spawning sites have been verified for Atlantic sturgeon. Some life stages of both species (including young juveniles) concentrate in or are restricted to small portions of estuaries during summer. Deterioration of water quality (especially dissolved oxygen) appears to be degrading the nursery function of these summer refugia, creating a recruitment bottleneck. Protection of essential habitats, especially nursery/summer habitats, from human-caused dissolved-oxygen reductions and other impacts is critical. By-catch, primarily in riverine/estuarine gillnet and estuarine/marine trawl fisheries, appears to be the second major source of mortality for southern sturgeons. Reserves, or no-fishing zones, could protect populations by reducing or eliminating by-catch mortality. This protection would be especially valuable in high salinity foraging areas (used primarily during cool months) and during spawning migrations. Proposed management strategies aimed at conservation and restoration of sturgeon populations therefore focus on two areas: protection of essential habitats and establishment of reserves to provide protection from fishing gears that generate substantial sturgeon by-catch. Specific management recommendations were developed on a system-by-system basis.</EA>
<CC>002A14D02B</CC>
<FD>Espèce menacée; Déclin population; Habitat; Mortalité; Prise accessoire; Pêcherie; Dégradation environnement; Gestion population; Recommandation; Géorgie; Caroline du Nord; Caroline du Sud; Acipenser brevisrostrum; Acipenser oxyrinchus</FD>
<FG>Etats Unis; Amérique du Nord; Amérique; Protection faune; Protection environnement; Milieu aquatique; Pisces; Vertebrata; Acipenseridae</FG>
<ED>Endangered species; Population decline; Habitat; Mortality; By-catches; Fishery; Ecological damage; Population management; Recommendation; Georgia; North Carolina; South Carolina</ED>
<EG>United States; North America; America; Animal conservation; Environmental protection; Aquatic environment; Pisces; Vertebrata</EG>
<SD>Especie amenazada; Declinación poblacional; Habitat; Mortalidad; Presa accesoria; Pesquería; Degradación ecológica; Gestión población; Recomendación; Georgia; Carolina del norte; Carolina del Sur</SD>
<LO>INIST-11286.354000091314920260</LO>
<ID>00-0448958</ID>
</server>
</inist>
</record>

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