Modeling spatial and temporal variation of suitable nursery habitats for Atlantic sturgeon in the Chesapeake Bay
Identifieur interne :
000140 ( PascalFrancis/Curation );
précédent :
000139;
suivant :
000141
Modeling spatial and temporal variation of suitable nursery habitats for Atlantic sturgeon in the Chesapeake Bay
Auteurs : Edwin J. Niklitschek [
Chili] ;
David H. Secor [
États-Unis]
Source :
-
Estuarine, coastal and shelf science : (Print) [ 0272-7714 ] ; 2005.
RBID : Pascal:05-0329218
Descripteurs français
English descriptors
Abstract
For rare and endangered species, bioenergetics modeling can represent a valuable approach for understanding issues of habitat value and connectivity among potential habitats within nurseries in restoration programs. We used multivariable bioenergetics and survival models for Atlantic sturgeon to generate spatially explicit maps of potential production in the Chesapeake Bay. For the period 1993-2002, spatial and temporal patterns in water quality effects (temperature, dissolved oxygen [DO] and salinity) on potential production were evaluated. In addition, two forecasted scenarios were modeled: one implementing newly revised U.S. Environmental Protection Agency (EPA) DO-criteria for the Chesapeake Bay, and the other assuming a bay-wide increase of 1 °C due to an underlying trend in regional climate. Atlantic sturgeon's low (survival/growth) tolerance to temperatures >28 °C was a critical constraint during their first 1-2 summers of life. Hatched in freshwater (spring to mid-summer), young-of-the-year were predicted to occupy cooler (deeper) areas as temperature approached sub-lethal levels. While most thermal refuges were located down-estuary, a large fraction of potential refuges were unsuitable due to persistent hypoxia and/or salinity levels beyond the limited osmoregulatory capabilities of early juvenile Atlantic sturgeon. As a result, suitable summer habitats for juvenile Atlantic sturgeons in the Chesapeake Bay were predicted to be spatially restricted and variable between years, ranging from 0 to 35% of the modeled bay surface area. In critical (drought) years, almost no summer habitat was predicted to be available for juvenile Atlantic sturgeon. Value and size of nursery habitat was highly sensitive to climatic oscillations and anthropogenic interventions affecting freshwater inflow, water temperature and/or DO. Achieving EPA DO-criteria for the Chesapeake Bay was predicted to increase total suitable habitat by 13% for an average year, while increasing water temperature by just 1 °C bay-wide would reduce suitable habitat by 65%.
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| A09 | 01 | 1 | ENG | @1 Connectivity in the life cycles of fishes and invertebrates that use estuaries |
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| A11 | 01 | 1 | | @1 NIKLITSCHEK (Edwin J.) |
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| A11 | 02 | 1 | | @1 SECOR (David H.) |
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| A12 | 01 | 1 | | @1 ROOKER (Jay R.) @9 ed. |
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| A12 | 02 | 1 | | @1 SECOR (David H.) @9 ed. |
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| A14 | 01 | | | @1 Universidad Austral de Chile, Centro Trapananda, Portales 73 @2 Coyhaique XI Region @3 CHL @Z 1 aut. |
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| A14 | 02 | | | @1 University of Maryland Center for Environmental Science, Chesapeake Biological Laboratory, I William @2 St. Solomons, MD 20688 @3 USA @Z 2 aut. |
|---|
| A15 | 01 | | | @1 Chesapeake Biological Laboratory, University of Maryland Center for Environmental Science, PO Box 38 @2 Solomons, MD 20688 @3 USA @Z 2 aut. |
|---|
| A15 | 02 | | | @1 Texas A&M University, Department of Marine Biology, 5007 Avenue U @2 Galveston, TX 77551 @3 USA @Z 1 aut. |
|---|
| A18 | 01 | 1 | | @1 Estuarine Research Federation (ERF) @2 Port Republic, MD @3 USA @9 org-cong. |
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| C01 | 01 | | ENG | @0 For rare and endangered species, bioenergetics modeling can represent a valuable approach for understanding issues of habitat value and connectivity among potential habitats within nurseries in restoration programs. We used multivariable bioenergetics and survival models for Atlantic sturgeon to generate spatially explicit maps of potential production in the Chesapeake Bay. For the period 1993-2002, spatial and temporal patterns in water quality effects (temperature, dissolved oxygen [DO] and salinity) on potential production were evaluated. In addition, two forecasted scenarios were modeled: one implementing newly revised U.S. Environmental Protection Agency (EPA) DO-criteria for the Chesapeake Bay, and the other assuming a bay-wide increase of 1 °C due to an underlying trend in regional climate. Atlantic sturgeon's low (survival/growth) tolerance to temperatures >28 °C was a critical constraint during their first 1-2 summers of life. Hatched in freshwater (spring to mid-summer), young-of-the-year were predicted to occupy cooler (deeper) areas as temperature approached sub-lethal levels. While most thermal refuges were located down-estuary, a large fraction of potential refuges were unsuitable due to persistent hypoxia and/or salinity levels beyond the limited osmoregulatory capabilities of early juvenile Atlantic sturgeon. As a result, suitable summer habitats for juvenile Atlantic sturgeons in the Chesapeake Bay were predicted to be spatially restricted and variable between years, ranging from 0 to 35% of the modeled bay surface area. In critical (drought) years, almost no summer habitat was predicted to be available for juvenile Atlantic sturgeon. Value and size of nursery habitat was highly sensitive to climatic oscillations and anthropogenic interventions affecting freshwater inflow, water temperature and/or DO. Achieving EPA DO-criteria for the Chesapeake Bay was predicted to increase total suitable habitat by 13% for an average year, while increasing water temperature by just 1 °C bay-wide would reduce suitable habitat by 65%. |
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| C03 | 02 | X | FRE | @0 Variation temporelle @5 02 |
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| C03 | 02 | X | ENG | @0 Time variation @5 02 |
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| C03 | 02 | X | SPA | @0 Variación temporal @5 02 |
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| C03 | 03 | X | FRE | @0 Nourricerie @5 03 |
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| C03 | 03 | X | ENG | @0 Nursery (animal) @5 03 |
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| C03 | 04 | X | FRE | @0 Habitat @5 04 |
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| C03 | 04 | X | ENG | @0 Habitat @5 04 |
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| C03 | 04 | X | SPA | @0 Habitat @5 04 |
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| C03 | 05 | X | FRE | @0 Pisces @2 NS @5 05 |
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| C03 | 05 | X | ENG | @0 Pisces @2 NS @5 05 |
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| C03 | 05 | X | SPA | @0 Pisces @2 NS @5 05 |
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| C03 | 06 | X | FRE | @0 Estuaire @5 06 |
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| C03 | 06 | X | ENG | @0 Estuaries @5 06 |
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| C03 | 06 | X | SPA | @0 Estuario @5 06 |
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| C03 | 07 | X | FRE | @0 Milieu saumâtre @5 07 |
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| C03 | 07 | X | ENG | @0 Brackish water environment @5 07 |
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| C03 | 07 | X | SPA | @0 Medio salobre @5 07 |
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| C03 | 08 | X | FRE | @0 Acipenser sturio @2 NS @5 49 |
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| C03 | 08 | X | ENG | @0 Acipenser sturio @2 NS @5 49 |
|---|
| C03 | 08 | X | SPA | @0 Acipenser sturio @2 NS @5 49 |
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| C03 | 09 | X | FRE | @0 Baie Chesapeake @4 CD @5 96 |
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| C03 | 09 | X | ENG | @0 Chesapeake Bay @4 CD @5 96 |
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| C03 | 09 | X | SPA | @0 Bahía Chesapeake @4 CD @5 96 |
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| C07 | 01 | X | FRE | @0 Vertebrata @2 NS |
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| C07 | 01 | X | ENG | @0 Vertebrata @2 NS |
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| C07 | 01 | X | SPA | @0 Vertebrata @2 NS |
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| C07 | 02 | X | FRE | @0 Acipenseridae @4 INC @5 70 |
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| N21 | | | | @1 234 |
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| N44 | 01 | | | @1 OTO |
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| N82 | | | | @1 OTO |
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|
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| pR |
| A30 | 01 | 1 | ENG | @1 Estuarine Research Federation 2003 Seattle Meeting. Special Symposium on Fish Connectivity @3 Seattle USA @4 2003-09-14 |
|---|
|
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Le document en format XML
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<author><name sortKey="Niklitschek, Edwin J" sort="Niklitschek, Edwin J" uniqKey="Niklitschek E" first="Edwin J." last="Niklitschek">Edwin J. Niklitschek</name>
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<affiliation wicri:level="1"><inist:fA14 i1="02"><s1>University of Maryland Center for Environmental Science, Chesapeake Biological Laboratory, I William</s1>
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</keywords><front><div type="abstract" xml:lang="en">For rare and endangered species, bioenergetics modeling can represent a valuable approach for understanding issues of habitat value and connectivity among potential habitats within nurseries in restoration programs. We used multivariable bioenergetics and survival models for Atlantic sturgeon to generate spatially explicit maps of potential production in the Chesapeake Bay. For the period 1993-2002, spatial and temporal patterns in water quality effects (temperature, dissolved oxygen [DO] and salinity) on potential production were evaluated. In addition, two forecasted scenarios were modeled: one implementing newly revised U.S. Environmental Protection Agency (EPA) DO-criteria for the Chesapeake Bay, and the other assuming a bay-wide increase of 1 °C due to an underlying trend in regional climate. Atlantic sturgeon's low (survival/growth) tolerance to temperatures >28 °C was a critical constraint during their first 1-2 summers of life. Hatched in freshwater (spring to mid-summer), young-of-the-year were predicted to occupy cooler (deeper) areas as temperature approached sub-lethal levels. While most thermal refuges were located down-estuary, a large fraction of potential refuges were unsuitable due to persistent hypoxia and/or salinity levels beyond the limited osmoregulatory capabilities of early juvenile Atlantic sturgeon. As a result, suitable summer habitats for juvenile Atlantic sturgeons in the Chesapeake Bay were predicted to be spatially restricted and variable between years, ranging from 0 to 35% of the modeled bay surface area. In critical (drought) years, almost no summer habitat was predicted to be available for juvenile Atlantic sturgeon. Value and size of nursery habitat was highly sensitive to climatic oscillations and anthropogenic interventions affecting freshwater inflow, water temperature and/or DO. Achieving EPA DO-criteria for the Chesapeake Bay was predicted to increase total suitable habitat by 13% for an average year, while increasing water temperature by just 1 °C bay-wide would reduce suitable habitat by 65%.</div>
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</fA11><fA11 i1="02" i2="1"><s1>SECOR (David H.)</s1>
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<s9>ed.</s9>
</fA12><fA12 i1="02" i2="1"><s1>SECOR (David H.)</s1>
<s9>ed.</s9>
</fA12><fA14 i1="01"><s1>Universidad Austral de Chile, Centro Trapananda, Portales 73</s1>
<s2>Coyhaique XI Region</s2>
<s3>CHL</s3>
<sZ>1 aut.</sZ>
</fA14><fA14 i1="02"><s1>University of Maryland Center for Environmental Science, Chesapeake Biological Laboratory, I William</s1>
<s2>St. Solomons, MD 20688</s2>
<s3>USA</s3>
<sZ>2 aut.</sZ>
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<s3>USA</s3>
<sZ>2 aut.</sZ>
</fA15><fA15 i1="02"><s1>Texas A&M University, Department of Marine Biology, 5007 Avenue U</s1>
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<s3>USA</s3>
<sZ>1 aut.</sZ>
</fA15><fA18 i1="01" i2="1"><s1>Estuarine Research Federation (ERF)</s1>
<s2>Port Republic, MD</s2>
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<s9>org-cong.</s9>
</fA18><fA20><s1>135-148</s1>
</fA20><fA21><s1>2005</s1>
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</fA66><fC01 i1="01" l="ENG"><s0>For rare and endangered species, bioenergetics modeling can represent a valuable approach for understanding issues of habitat value and connectivity among potential habitats within nurseries in restoration programs. We used multivariable bioenergetics and survival models for Atlantic sturgeon to generate spatially explicit maps of potential production in the Chesapeake Bay. For the period 1993-2002, spatial and temporal patterns in water quality effects (temperature, dissolved oxygen [DO] and salinity) on potential production were evaluated. In addition, two forecasted scenarios were modeled: one implementing newly revised U.S. Environmental Protection Agency (EPA) DO-criteria for the Chesapeake Bay, and the other assuming a bay-wide increase of 1 °C due to an underlying trend in regional climate. Atlantic sturgeon's low (survival/growth) tolerance to temperatures >28 °C was a critical constraint during their first 1-2 summers of life. Hatched in freshwater (spring to mid-summer), young-of-the-year were predicted to occupy cooler (deeper) areas as temperature approached sub-lethal levels. While most thermal refuges were located down-estuary, a large fraction of potential refuges were unsuitable due to persistent hypoxia and/or salinity levels beyond the limited osmoregulatory capabilities of early juvenile Atlantic sturgeon. As a result, suitable summer habitats for juvenile Atlantic sturgeons in the Chesapeake Bay were predicted to be spatially restricted and variable between years, ranging from 0 to 35% of the modeled bay surface area. In critical (drought) years, almost no summer habitat was predicted to be available for juvenile Atlantic sturgeon. Value and size of nursery habitat was highly sensitive to climatic oscillations and anthropogenic interventions affecting freshwater inflow, water temperature and/or DO. Achieving EPA DO-criteria for the Chesapeake Bay was predicted to increase total suitable habitat by 13% for an average year, while increasing water temperature by just 1 °C bay-wide would reduce suitable habitat by 65%.</s0>
</fC01><fC02 i1="01" i2="X"><s0>002A14B04D</s0>
</fC02><fC02 i1="02" i2="X"><s0>002A15B</s0>
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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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<s5>03</s5>
</fC03><fC03 i1="04" i2="X" l="FRE"><s0>Habitat</s0>
<s5>04</s5>
</fC03><fC03 i1="04" i2="X" l="ENG"><s0>Habitat</s0>
<s5>04</s5>
</fC03><fC03 i1="04" i2="X" l="SPA"><s0>Habitat</s0>
<s5>04</s5>
</fC03><fC03 i1="05" i2="X" l="FRE"><s0>Pisces</s0>
<s2>NS</s2>
<s5>05</s5>
</fC03><fC03 i1="05" i2="X" l="ENG"><s0>Pisces</s0>
<s2>NS</s2>
<s5>05</s5>
</fC03><fC03 i1="05" i2="X" l="SPA"><s0>Pisces</s0>
<s2>NS</s2>
<s5>05</s5>
</fC03><fC03 i1="06" i2="X" l="FRE"><s0>Estuaire</s0>
<s5>06</s5>
</fC03><fC03 i1="06" i2="X" l="ENG"><s0>Estuaries</s0>
<s5>06</s5>
</fC03><fC03 i1="06" i2="X" l="SPA"><s0>Estuario</s0>
<s5>06</s5>
</fC03><fC03 i1="07" i2="X" l="FRE"><s0>Milieu saumâtre</s0>
<s5>07</s5>
</fC03><fC03 i1="07" i2="X" l="ENG"><s0>Brackish water environment</s0>
<s5>07</s5>
</fC03><fC03 i1="07" i2="X" l="SPA"><s0>Medio salobre</s0>
<s5>07</s5>
</fC03><fC03 i1="08" i2="X" l="FRE"><s0>Acipenser sturio</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03><fC03 i1="08" i2="X" l="ENG"><s0>Acipenser sturio</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03><fC03 i1="08" i2="X" l="SPA"><s0>Acipenser sturio</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03><fC03 i1="09" i2="X" l="FRE"><s0>Baie Chesapeake</s0>
<s4>CD</s4>
<s5>96</s5>
</fC03><fC03 i1="09" i2="X" l="ENG"><s0>Chesapeake Bay</s0>
<s4>CD</s4>
<s5>96</s5>
</fC03><fC03 i1="09" i2="X" l="SPA"><s0>Bahía Chesapeake</s0>
<s4>CD</s4>
<s5>96</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>Acipenseridae</s0>
<s4>INC</s4>
<s5>70</s5>
</fC07><fN21><s1>234</s1>
</fN21><fN44 i1="01"><s1>OTO</s1>
</fN44><fN82><s1>OTO</s1>
</fN82><pR><fA30 i1="01" i2="1" l="ENG"><s1>Estuarine Research Federation 2003 Seattle Meeting. Special Symposium on Fish Connectivity</s1>
<s3>Seattle USA</s3>
<s4>2003-09-14</s4>
</fA30>
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|type= RBID
|clé= Pascal:05-0329218
|texte= Modeling spatial and temporal variation of suitable nursery habitats for Atlantic sturgeon in the Chesapeake Bay
}}
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Data generation: Sat Mar 25 15:37:54 2017. Site generation: Tue Feb 13 14:18:49 2024 |  |
