EsturgeonV1, PascalFrancis, Curation, bibRecord, 000151

An energy budget for the Kootenai River, Idaho (USA), with application for management of the Kootenai white sturgeon, Acipenser transmontanus

Identifieur interne : 000151 ( PascalFrancis/Curation ); précédent : 000150; suivant : 000152

An energy budget for the Kootenai River, Idaho (USA), with application for management of the Kootenai white sturgeon, Acipenser transmontanus

Auteurs : Eric B. Snyder [États-Unis] ; G. Wayne Minshall [États-Unis]

Source :

Aquatic sciences [ 1015-1621 ] ; 2005.

RBID : Pascal:06-0137151

Descripteurs français

Pascal (Inist)
- Budget énergétique, Rivière, Idaho, Gestion population, Autochtone, Matière organique, Autotrophie, Milieu lotique, Ecosystème, Milieu aquatique, Milieu eau douce, Acipenser transmontanus.
Wicri :
- topic : Milieu aquatique.

English descriptors

KwdEn :
- Acipenser transmontanus, Aquatic environment, Autochthonous, Autotrophy, Ecosystem, Energy budget, Freshwater environment, Idaho, Lotic environment, Organic matter, Population management, Rivers.

Abstract

An energy budget provides a useful tool for examining the exchange of energy between trophic levels. In this study we examined the potential for autotrophic productivity and organic material to support higher trophic levels in three distinct geomorphic segments of the Kootenai River, USA. This approach is particularly important given that several species of fish, including the endangered Kootenai white sturgeon (Acipenser transmontanus), have been in decline since the installation of a large hydropower and flood control dam on the river. Previous research indicated that (i) the reservoir formed by Libby Dam was retaining significant quantities of nutrients and organic material and (ii) phosphorus was limiting periphyton accrual downstream from the reservoir. Thus food limitation was a likely mechanism contributing to the decline in fish populations. Net daily metabolism (NDM) was positive during only 30 % of the growing seasons from 1993 to 1995 indicating that autochthonous production was rarely sufficient to support higher trophic levels. All reaches were generally exporting transported organic matter (TOM). Results of an energy budget indicated that macroinvertebrate standing crop was generally lower than that which could be sustained by the relatively short bursts of positive NDM. Estimated fish biomass was higher than that sustained by positive NDM or stored TOM at energetic conversion efficiencies (C.E.) of 10% at average and maximum estimated active metabolic rate. Autotrophic and detrital sources were generally insufficient to support the estimated fish biomass. This study combines detailed analyses of both the autotrophic and detrital energy pathways and thereby suggests a mechanistic explanation for the decline in fish abundance ultimately caused by impoundment.

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A03		`1`		`@0 Aquat. sci.`
A05				`@2 67`
A06				`@2 4`
A08	`01`	`1`	`ENG`	`@1 An energy budget for the Kootenai River, Idaho (USA), with application for management of the Kootenai white sturgeon, Acipenser transmontanus`
A11	`01`	`1`		`@1 SNYDER (Eric B.)`
A11	`02`	`1`		`@1 MINSHALL (G. Wayne)`
A14	`01`			`@1 Biology Department, Grand Valley State University, 1 Campus Drive @2 Allendale, MI 49401 @3 USA @Z 1 aut.`
A14	`02`			`@1 Department of Biological Sciences, Box 8007, Idaho State University @2 Pocatello, ID 83209 @3 USA @Z 2 aut.`
A20				`@1 472-485`
A21				`@1 2005`
A23	`01`			`@0 ENG`
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A44				`@0 0000 @1 © 2006 INIST-CNRS. All rights reserved.`
A45				`@0 2 p.1/4`
A47	`01`	`1`		`@0 06-0137151`
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A61				`@0 A`
A64	`01`	`1`		`@0 Aquatic sciences`
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C01	`01`		`ENG`	@0 An energy budget provides a useful tool for examining the exchange of energy between trophic levels. In this study we examined the potential for autotrophic productivity and organic material to support higher trophic levels in three distinct geomorphic segments of the Kootenai River, USA. This approach is particularly important given that several species of fish, including the endangered Kootenai white sturgeon (Acipenser transmontanus), have been in decline since the installation of a large hydropower and flood control dam on the river. Previous research indicated that (i) the reservoir formed by Libby Dam was retaining significant quantities of nutrients and organic material and (ii) phosphorus was limiting periphyton accrual downstream from the reservoir. Thus food limitation was a likely mechanism contributing to the decline in fish populations. Net daily metabolism (NDM) was positive during only 30 % of the growing seasons from 1993 to 1995 indicating that autochthonous production was rarely sufficient to support higher trophic levels. All reaches were generally exporting transported organic matter (TOM). Results of an energy budget indicated that macroinvertebrate standing crop was generally lower than that which could be sustained by the relatively short bursts of positive NDM. Estimated fish biomass was higher than that sustained by positive NDM or stored TOM at energetic conversion efficiencies (C.E.) of 10% at average and maximum estimated active metabolic rate. Autotrophic and detrital sources were generally insufficient to support the estimated fish biomass. This study combines detailed analyses of both the autotrophic and detrital energy pathways and thereby suggests a mechanistic explanation for the decline in fish abundance ultimately caused by impoundment.
C02	`01`	`X`		`@0 002A14B04C`
C03	`01`	`X`	`FRE`	`@0 Budget énergétique @5 01`
C03	`01`	`X`	`ENG`	`@0 Energy budget @5 01`
C03	`01`	`X`	`SPA`	`@0 Presupuesto energético @5 01`
C03	`02`	`X`	`FRE`	`@0 Rivière @5 02`
C03	`02`	`X`	`ENG`	`@0 Rivers @5 02`
C03	`02`	`X`	`SPA`	`@0 Río @5 02`
C03	`03`	`X`	`FRE`	`@0 Idaho @2 NG @5 03`
C03	`03`	`X`	`ENG`	`@0 Idaho @2 NG @5 03`
C03	`03`	`X`	`SPA`	`@0 Idaho @2 NG @5 03`
C03	`04`	`X`	`FRE`	`@0 Gestion population @5 04`
C03	`04`	`X`	`ENG`	`@0 Population management @5 04`
C03	`04`	`X`	`SPA`	`@0 Gestión población @5 04`
C03	`05`	`X`	`FRE`	`@0 Autochtone @5 05`
C03	`05`	`X`	`ENG`	`@0 Autochthonous @5 05`
C03	`05`	`X`	`SPA`	`@0 Autóctono @5 05`
C03	`06`	`X`	`FRE`	`@0 Matière organique @5 06`
C03	`06`	`X`	`ENG`	`@0 Organic matter @5 06`
C03	`06`	`X`	`SPA`	`@0 Materia orgánica @5 06`
C03	`07`	`X`	`FRE`	`@0 Autotrophie @5 07`
C03	`07`	`X`	`ENG`	`@0 Autotrophy @5 07`
C03	`07`	`X`	`SPA`	`@0 Autotrofia @5 07`
C03	`08`	`X`	`FRE`	`@0 Milieu lotique @5 08`
C03	`08`	`X`	`ENG`	`@0 Lotic environment @5 08`
C03	`08`	`X`	`SPA`	`@0 Ambiente lotico @5 08`
C03	`09`	`X`	`FRE`	`@0 Ecosystème @5 09`
C03	`09`	`X`	`ENG`	`@0 Ecosystem @5 09`
C03	`09`	`X`	`SPA`	`@0 Ecosistema @5 09`
C03	`10`	`X`	`FRE`	`@0 Milieu aquatique @5 10`
C03	`10`	`X`	`ENG`	`@0 Aquatic environment @5 10`
C03	`10`	`X`	`SPA`	`@0 Medio acuático @5 10`
C03	`11`	`X`	`FRE`	`@0 Milieu eau douce @5 23`
C03	`11`	`X`	`ENG`	`@0 Freshwater environment @5 23`
C03	`11`	`X`	`SPA`	`@0 Medio agua dulce @5 23`
C03	`12`	`X`	`FRE`	`@0 Acipenser transmontanus @2 NS @5 49`
C03	`12`	`X`	`ENG`	`@0 Acipenser transmontanus @2 NS @5 49`
C03	`12`	`X`	`SPA`	`@0 Acipenser transmontanus @2 NS @5 49`
C07	`01`	`X`	`FRE`	`@0 Etats Unis @2 NG`
C07	`01`	`X`	`ENG`	`@0 United States @2 NG`
C07	`01`	`X`	`SPA`	`@0 Estados Unidos @2 NG`
C07	`02`	`X`	`FRE`	`@0 Amérique du Nord @2 NG`
C07	`02`	`X`	`ENG`	`@0 North America @2 NG`
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 Cours eau @5 17`
C07	`04`	`X`	`ENG`	`@0 Stream @5 17`
C07	`04`	`X`	`SPA`	`@0 Curso agua @5 17`
C07	`05`	`X`	`FRE`	`@0 Gestion ressources @5 18`
C07	`05`	`X`	`ENG`	`@0 Resource management @5 18`
C07	`05`	`X`	`SPA`	`@0 Gestión recursos @5 18`
C07	`06`	`X`	`FRE`	`@0 Pisces @2 NS @5 29`
C07	`06`	`X`	`ENG`	`@0 Pisces @2 NS @5 29`
C07	`06`	`X`	`SPA`	`@0 Pisces @2 NS @5 29`
C07	`07`	`X`	`FRE`	`@0 Vertebrata @2 NS`
C07	`07`	`X`	`ENG`	`@0 Vertebrata @2 NS`
C07	`07`	`X`	`SPA`	`@0 Vertebrata @2 NS`
C07	`08`	`X`	`FRE`	`@0 Acipenseridae @4 INC @5 70`
N21				`@1 086`

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Le document en format XML

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<front><div type="abstract" xml:lang="en">An energy budget provides a useful tool for examining the exchange of energy between trophic levels. In this study we examined the potential for autotrophic productivity and organic material to support higher trophic levels in three distinct geomorphic segments of the Kootenai River, USA. This approach is particularly important given that several species of fish, including the endangered Kootenai white sturgeon (Acipenser transmontanus), have been in decline since the installation of a large hydropower and flood control dam on the river. Previous research indicated that (i) the reservoir formed by Libby Dam was retaining significant quantities of nutrients and organic material and (ii) phosphorus was limiting periphyton accrual downstream from the reservoir. Thus food limitation was a likely mechanism contributing to the decline in fish populations. Net daily metabolism (NDM) was positive during only 30 % of the growing seasons from 1993 to 1995 indicating that autochthonous production was rarely sufficient to support higher trophic levels. All reaches were generally exporting transported organic matter (TOM). Results of an energy budget indicated that macroinvertebrate standing crop was generally lower than that which could be sustained by the relatively short bursts of positive NDM. Estimated fish biomass was higher than that sustained by positive NDM or stored TOM at energetic conversion efficiencies (C.E.) of 10% at average and maximum estimated active metabolic rate. Autotrophic and detrital sources were generally insufficient to support the estimated fish biomass. This study combines detailed analyses of both the autotrophic and detrital energy pathways and thereby suggests a mechanistic explanation for the decline in fish abundance ultimately caused by impoundment.</div>
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<fC01 i1="01" l="ENG"><s0>An energy budget provides a useful tool for examining the exchange of energy between trophic levels. In this study we examined the potential for autotrophic productivity and organic material to support higher trophic levels in three distinct geomorphic segments of the Kootenai River, USA. This approach is particularly important given that several species of fish, including the endangered Kootenai white sturgeon (Acipenser transmontanus), have been in decline since the installation of a large hydropower and flood control dam on the river. Previous research indicated that (i) the reservoir formed by Libby Dam was retaining significant quantities of nutrients and organic material and (ii) phosphorus was limiting periphyton accrual downstream from the reservoir. Thus food limitation was a likely mechanism contributing to the decline in fish populations. Net daily metabolism (NDM) was positive during only 30 % of the growing seasons from 1993 to 1995 indicating that autochthonous production was rarely sufficient to support higher trophic levels. All reaches were generally exporting transported organic matter (TOM). Results of an energy budget indicated that macroinvertebrate standing crop was generally lower than that which could be sustained by the relatively short bursts of positive NDM. Estimated fish biomass was higher than that sustained by positive NDM or stored TOM at energetic conversion efficiencies (C.E.) of 10% at average and maximum estimated active metabolic rate. Autotrophic and detrital sources were generally insufficient to support the estimated fish biomass. This study combines detailed analyses of both the autotrophic and detrital energy pathways and thereby suggests a mechanistic explanation for the decline in fish abundance ultimately caused by impoundment.</s0>
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<fC02 i1="01" i2="X"><s0>002A14B04C</s0>
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<s5>01</s5>
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<s5>01</s5>
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<s5>01</s5>
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<s5>02</s5>
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<s5>02</s5>
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<fC03 i1="02" i2="X" l="SPA"><s0>Río</s0>
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<s5>03</s5>
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<s5>03</s5>
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<s2>NG</s2>
<s5>03</s5>
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<s5>04</s5>
</fC03>
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<s5>04</s5>
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<s5>05</s5>
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<s5>05</s5>
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<s5>05</s5>
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<fC03 i1="06" i2="X" l="FRE"><s0>Matière organique</s0>
<s5>06</s5>
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<fC03 i1="06" i2="X" l="ENG"><s0>Organic matter</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA"><s0>Materia orgánica</s0>
<s5>06</s5>
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<s5>07</s5>
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<fC03 i1="07" i2="X" l="ENG"><s0>Autotrophy</s0>
<s5>07</s5>
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<fC03 i1="07" i2="X" l="SPA"><s0>Autotrofia</s0>
<s5>07</s5>
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<fC03 i1="08" i2="X" l="FRE"><s0>Milieu lotique</s0>
<s5>08</s5>
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<fC03 i1="08" i2="X" l="ENG"><s0>Lotic environment</s0>
<s5>08</s5>
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<s5>08</s5>
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<s5>09</s5>
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<s5>09</s5>
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<fC03 i1="09" i2="X" l="SPA"><s0>Ecosistema</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE"><s0>Milieu aquatique</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG"><s0>Aquatic environment</s0>
<s5>10</s5>
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<fC03 i1="10" i2="X" l="SPA"><s0>Medio acuático</s0>
<s5>10</s5>
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<fC03 i1="11" i2="X" l="FRE"><s0>Milieu eau douce</s0>
<s5>23</s5>
</fC03>
<fC03 i1="11" i2="X" l="ENG"><s0>Freshwater environment</s0>
<s5>23</s5>
</fC03>
<fC03 i1="11" i2="X" l="SPA"><s0>Medio agua dulce</s0>
<s5>23</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE"><s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03>
<fC03 i1="12" i2="X" l="ENG"><s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03>
<fC03 i1="12" i2="X" l="SPA"><s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>49</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>Cours eau</s0>
<s5>17</s5>
</fC07>
<fC07 i1="04" i2="X" l="ENG"><s0>Stream</s0>
<s5>17</s5>
</fC07>
<fC07 i1="04" i2="X" l="SPA"><s0>Curso agua</s0>
<s5>17</s5>
</fC07>
<fC07 i1="05" i2="X" l="FRE"><s0>Gestion ressources</s0>
<s5>18</s5>
</fC07>
<fC07 i1="05" i2="X" l="ENG"><s0>Resource management</s0>
<s5>18</s5>
</fC07>
<fC07 i1="05" i2="X" l="SPA"><s0>Gestión recursos</s0>
<s5>18</s5>
</fC07>
<fC07 i1="06" i2="X" l="FRE"><s0>Pisces</s0>
<s2>NS</s2>
<s5>29</s5>
</fC07>
<fC07 i1="06" i2="X" l="ENG"><s0>Pisces</s0>
<s2>NS</s2>
<s5>29</s5>
</fC07>
<fC07 i1="06" i2="X" l="SPA"><s0>Pisces</s0>
<s2>NS</s2>
<s5>29</s5>
</fC07>
<fC07 i1="07" i2="X" l="FRE"><s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="ENG"><s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="SPA"><s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="08" i2="X" l="FRE"><s0>Acipenseridae</s0>
<s4>INC</s4>
<s5>70</s5>
</fC07>
<fN21><s1>086</s1>
</fN21>
</pA>
</standard>
</inist>
</record>

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{{Explor lien
   |wiki=    Wicri/Eau
   |area=    EsturgeonV1
   |flux=    PascalFrancis
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   |type=    RBID
   |clé=     Pascal:06-0137151
   |texte=   An energy budget for the Kootenai River, Idaho (USA), with application for management of the Kootenai white sturgeon, Acipenser transmontanus
}}

This area was generated with Dilib version V0.6.27.
Data generation: Sat Mar 25 15:37:54 2017. Site generation: Tue Feb 13 14:18:49 2024

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An energy budget for the Kootenai River, Idaho (USA), with application for management of the Kootenai white sturgeon, Acipenser transmontanus

An energy budget for the Kootenai River, Idaho (USA), with application for management of the Kootenai white sturgeon, Acipenser transmontanus

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Descripteurs français

English descriptors

Abstract

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