Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period
Abstract The results of the studies within the framework of the international expedition onboard R/V Vladimir Parshin in September–October 2005 are presented. Intensive development of Bacillariophyceae and Dynophyceae was recorded in the coastal waters of Bulgaria, Turkey, and in the Danube River De...
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| Autor*in: |
Stel’makh, L. V. [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2009 |
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| Schlagwörter: |
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| Anmerkung: |
© Pleiades Publishing, Ltd. 2009 |
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| Übergeordnetes Werk: |
Enthalten in: Oceanology - Moscow : MAIK Nauka/Interperiodica Publ., 2006, 49(2009), 1 vom: Feb., Seite 83-92 |
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| Übergeordnetes Werk: |
volume:49 ; year:2009 ; number:1 ; month:02 ; pages:83-92 |
| Links: |
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| DOI / URN: |
10.1134/S000143700901010X |
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| Katalog-ID: |
SPR020143079 |
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| 100 | 1 | |a Stel’makh, L. V. |e verfasserin |4 aut | |
| 245 | 1 | 0 | |a Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period |
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| 520 | |a Abstract The results of the studies within the framework of the international expedition onboard R/V Vladimir Parshin in September–October 2005 are presented. Intensive development of Bacillariophyceae and Dynophyceae was recorded in the coastal waters of Bulgaria, Turkey, and in the Danube River Delta during the period of the investigations. The increase in the algae population was accompanied by rising of the Chlorophyll a concentration up to 2.0–5.5 mg $ m^{−3} $. In the deep water region, it did not exceed 0.54 mg $ m^{−3} $. The phytoplankton growth rate in the surface water layer varied from 0.1 to 1.0 $ day^{−1} $. The phytoplankton growth rate and $ NO_{2} $+$ NO_{3} $ concentration, as well as the silicon concentration, were correlative, as was described by the Michaelis-Menten equation. The phytoplankton growth was affected by the integral impact of basic nutrients. The zooplankton grazing varied from 0.10 to 0.69 $ day^{−1} $, and the average values in different regions may vary by 1.5 times. The microalgae size range is one of the major factors of the grazing regulation. The rate of the phytoplankton consumption was decreasing according the increasing of the largest diatom Pseudosolenia calcaravis impact on the total biomass of the nano- and microphytoplankton. | ||
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| 650 | 4 | |a Dilution Factor |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Grazing Rate |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Zooplankton Grazing |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Grazing Impact |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Babich, I. I. |4 aut | |
| 700 | 1 | |a Tugrul, S. |4 aut | |
| 700 | 1 | |a Moncheva, S. |4 aut | |
| 700 | 1 | |a Stefanova, K. |4 aut | |
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10.1134/S000143700901010X doi (DE-627)SPR020143079 (SPR)S000143700901010X-e DE-627 ger DE-627 rakwb eng Stel’makh, L. V. verfasserin aut Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period 2009 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Pleiades Publishing, Ltd. 2009 Abstract The results of the studies within the framework of the international expedition onboard R/V Vladimir Parshin in September–October 2005 are presented. Intensive development of Bacillariophyceae and Dynophyceae was recorded in the coastal waters of Bulgaria, Turkey, and in the Danube River Delta during the period of the investigations. The increase in the algae population was accompanied by rising of the Chlorophyll a concentration up to 2.0–5.5 mg $ m^{−3} $. In the deep water region, it did not exceed 0.54 mg $ m^{−3} $. The phytoplankton growth rate in the surface water layer varied from 0.1 to 1.0 $ day^{−1} $. The phytoplankton growth rate and $ NO_{2} $+$ NO_{3} $ concentration, as well as the silicon concentration, were correlative, as was described by the Michaelis-Menten equation. The phytoplankton growth was affected by the integral impact of basic nutrients. The zooplankton grazing varied from 0.10 to 0.69 $ day^{−1} $, and the average values in different regions may vary by 1.5 times. The microalgae size range is one of the major factors of the grazing regulation. The rate of the phytoplankton consumption was decreasing according the increasing of the largest diatom Pseudosolenia calcaravis impact on the total biomass of the nano- and microphytoplankton. Phytoplankton (dpeaa)DE-He213 Dilution Factor (dpeaa)DE-He213 Grazing Rate (dpeaa)DE-He213 Zooplankton Grazing (dpeaa)DE-He213 Grazing Impact (dpeaa)DE-He213 Babich, I. I. aut Tugrul, S. aut Moncheva, S. aut Stefanova, K. aut Enthalten in Oceanology Moscow : MAIK Nauka/Interperiodica Publ., 2006 49(2009), 1 vom: Feb., Seite 83-92 (DE-627)509755704 (DE-600)2227888-6 1531-8508 nnns volume:49 year:2009 number:1 month:02 pages:83-92 https://dx.doi.org/10.1134/S000143700901010X lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 49 2009 1 02 83-92 |
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10.1134/S000143700901010X doi (DE-627)SPR020143079 (SPR)S000143700901010X-e DE-627 ger DE-627 rakwb eng Stel’makh, L. V. verfasserin aut Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period 2009 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Pleiades Publishing, Ltd. 2009 Abstract The results of the studies within the framework of the international expedition onboard R/V Vladimir Parshin in September–October 2005 are presented. Intensive development of Bacillariophyceae and Dynophyceae was recorded in the coastal waters of Bulgaria, Turkey, and in the Danube River Delta during the period of the investigations. The increase in the algae population was accompanied by rising of the Chlorophyll a concentration up to 2.0–5.5 mg $ m^{−3} $. In the deep water region, it did not exceed 0.54 mg $ m^{−3} $. The phytoplankton growth rate in the surface water layer varied from 0.1 to 1.0 $ day^{−1} $. The phytoplankton growth rate and $ NO_{2} $+$ NO_{3} $ concentration, as well as the silicon concentration, were correlative, as was described by the Michaelis-Menten equation. The phytoplankton growth was affected by the integral impact of basic nutrients. The zooplankton grazing varied from 0.10 to 0.69 $ day^{−1} $, and the average values in different regions may vary by 1.5 times. The microalgae size range is one of the major factors of the grazing regulation. The rate of the phytoplankton consumption was decreasing according the increasing of the largest diatom Pseudosolenia calcaravis impact on the total biomass of the nano- and microphytoplankton. Phytoplankton (dpeaa)DE-He213 Dilution Factor (dpeaa)DE-He213 Grazing Rate (dpeaa)DE-He213 Zooplankton Grazing (dpeaa)DE-He213 Grazing Impact (dpeaa)DE-He213 Babich, I. I. aut Tugrul, S. aut Moncheva, S. aut Stefanova, K. aut Enthalten in Oceanology Moscow : MAIK Nauka/Interperiodica Publ., 2006 49(2009), 1 vom: Feb., Seite 83-92 (DE-627)509755704 (DE-600)2227888-6 1531-8508 nnns volume:49 year:2009 number:1 month:02 pages:83-92 https://dx.doi.org/10.1134/S000143700901010X lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 49 2009 1 02 83-92 |
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10.1134/S000143700901010X doi (DE-627)SPR020143079 (SPR)S000143700901010X-e DE-627 ger DE-627 rakwb eng Stel’makh, L. V. verfasserin aut Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period 2009 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Pleiades Publishing, Ltd. 2009 Abstract The results of the studies within the framework of the international expedition onboard R/V Vladimir Parshin in September–October 2005 are presented. Intensive development of Bacillariophyceae and Dynophyceae was recorded in the coastal waters of Bulgaria, Turkey, and in the Danube River Delta during the period of the investigations. The increase in the algae population was accompanied by rising of the Chlorophyll a concentration up to 2.0–5.5 mg $ m^{−3} $. In the deep water region, it did not exceed 0.54 mg $ m^{−3} $. The phytoplankton growth rate in the surface water layer varied from 0.1 to 1.0 $ day^{−1} $. The phytoplankton growth rate and $ NO_{2} $+$ NO_{3} $ concentration, as well as the silicon concentration, were correlative, as was described by the Michaelis-Menten equation. The phytoplankton growth was affected by the integral impact of basic nutrients. The zooplankton grazing varied from 0.10 to 0.69 $ day^{−1} $, and the average values in different regions may vary by 1.5 times. The microalgae size range is one of the major factors of the grazing regulation. The rate of the phytoplankton consumption was decreasing according the increasing of the largest diatom Pseudosolenia calcaravis impact on the total biomass of the nano- and microphytoplankton. Phytoplankton (dpeaa)DE-He213 Dilution Factor (dpeaa)DE-He213 Grazing Rate (dpeaa)DE-He213 Zooplankton Grazing (dpeaa)DE-He213 Grazing Impact (dpeaa)DE-He213 Babich, I. I. aut Tugrul, S. aut Moncheva, S. aut Stefanova, K. aut Enthalten in Oceanology Moscow : MAIK Nauka/Interperiodica Publ., 2006 49(2009), 1 vom: Feb., Seite 83-92 (DE-627)509755704 (DE-600)2227888-6 1531-8508 nnns volume:49 year:2009 number:1 month:02 pages:83-92 https://dx.doi.org/10.1134/S000143700901010X lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 49 2009 1 02 83-92 |
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10.1134/S000143700901010X doi (DE-627)SPR020143079 (SPR)S000143700901010X-e DE-627 ger DE-627 rakwb eng Stel’makh, L. V. verfasserin aut Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period 2009 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Pleiades Publishing, Ltd. 2009 Abstract The results of the studies within the framework of the international expedition onboard R/V Vladimir Parshin in September–October 2005 are presented. Intensive development of Bacillariophyceae and Dynophyceae was recorded in the coastal waters of Bulgaria, Turkey, and in the Danube River Delta during the period of the investigations. The increase in the algae population was accompanied by rising of the Chlorophyll a concentration up to 2.0–5.5 mg $ m^{−3} $. In the deep water region, it did not exceed 0.54 mg $ m^{−3} $. The phytoplankton growth rate in the surface water layer varied from 0.1 to 1.0 $ day^{−1} $. The phytoplankton growth rate and $ NO_{2} $+$ NO_{3} $ concentration, as well as the silicon concentration, were correlative, as was described by the Michaelis-Menten equation. The phytoplankton growth was affected by the integral impact of basic nutrients. The zooplankton grazing varied from 0.10 to 0.69 $ day^{−1} $, and the average values in different regions may vary by 1.5 times. The microalgae size range is one of the major factors of the grazing regulation. The rate of the phytoplankton consumption was decreasing according the increasing of the largest diatom Pseudosolenia calcaravis impact on the total biomass of the nano- and microphytoplankton. Phytoplankton (dpeaa)DE-He213 Dilution Factor (dpeaa)DE-He213 Grazing Rate (dpeaa)DE-He213 Zooplankton Grazing (dpeaa)DE-He213 Grazing Impact (dpeaa)DE-He213 Babich, I. I. aut Tugrul, S. aut Moncheva, S. aut Stefanova, K. aut Enthalten in Oceanology Moscow : MAIK Nauka/Interperiodica Publ., 2006 49(2009), 1 vom: Feb., Seite 83-92 (DE-627)509755704 (DE-600)2227888-6 1531-8508 nnns volume:49 year:2009 number:1 month:02 pages:83-92 https://dx.doi.org/10.1134/S000143700901010X lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 49 2009 1 02 83-92 |
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10.1134/S000143700901010X doi (DE-627)SPR020143079 (SPR)S000143700901010X-e DE-627 ger DE-627 rakwb eng Stel’makh, L. V. verfasserin aut Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period 2009 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Pleiades Publishing, Ltd. 2009 Abstract The results of the studies within the framework of the international expedition onboard R/V Vladimir Parshin in September–October 2005 are presented. Intensive development of Bacillariophyceae and Dynophyceae was recorded in the coastal waters of Bulgaria, Turkey, and in the Danube River Delta during the period of the investigations. The increase in the algae population was accompanied by rising of the Chlorophyll a concentration up to 2.0–5.5 mg $ m^{−3} $. In the deep water region, it did not exceed 0.54 mg $ m^{−3} $. The phytoplankton growth rate in the surface water layer varied from 0.1 to 1.0 $ day^{−1} $. The phytoplankton growth rate and $ NO_{2} $+$ NO_{3} $ concentration, as well as the silicon concentration, were correlative, as was described by the Michaelis-Menten equation. The phytoplankton growth was affected by the integral impact of basic nutrients. The zooplankton grazing varied from 0.10 to 0.69 $ day^{−1} $, and the average values in different regions may vary by 1.5 times. The microalgae size range is one of the major factors of the grazing regulation. The rate of the phytoplankton consumption was decreasing according the increasing of the largest diatom Pseudosolenia calcaravis impact on the total biomass of the nano- and microphytoplankton. Phytoplankton (dpeaa)DE-He213 Dilution Factor (dpeaa)DE-He213 Grazing Rate (dpeaa)DE-He213 Zooplankton Grazing (dpeaa)DE-He213 Grazing Impact (dpeaa)DE-He213 Babich, I. I. aut Tugrul, S. aut Moncheva, S. aut Stefanova, K. aut Enthalten in Oceanology Moscow : MAIK Nauka/Interperiodica Publ., 2006 49(2009), 1 vom: Feb., Seite 83-92 (DE-627)509755704 (DE-600)2227888-6 1531-8508 nnns volume:49 year:2009 number:1 month:02 pages:83-92 https://dx.doi.org/10.1134/S000143700901010X lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 49 2009 1 02 83-92 |
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Stel’makh, L. V. @@aut@@ Babich, I. I. @@aut@@ Tugrul, S. @@aut@@ Moncheva, S. @@aut@@ Stefanova, K. @@aut@@ |
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Intensive development of Bacillariophyceae and Dynophyceae was recorded in the coastal waters of Bulgaria, Turkey, and in the Danube River Delta during the period of the investigations. The increase in the algae population was accompanied by rising of the Chlorophyll a concentration up to 2.0–5.5 mg $ m^{−3} $. In the deep water region, it did not exceed 0.54 mg $ m^{−3} $. The phytoplankton growth rate in the surface water layer varied from 0.1 to 1.0 $ day^{−1} $. The phytoplankton growth rate and $ NO_{2} $+$ NO_{3} $ concentration, as well as the silicon concentration, were correlative, as was described by the Michaelis-Menten equation. The phytoplankton growth was affected by the integral impact of basic nutrients. The zooplankton grazing varied from 0.10 to 0.69 $ day^{−1} $, and the average values in different regions may vary by 1.5 times. The microalgae size range is one of the major factors of the grazing regulation. 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Stel’makh, L. V. |
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Stel’makh, L. V. misc Phytoplankton misc Dilution Factor misc Grazing Rate misc Zooplankton Grazing misc Grazing Impact Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period |
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Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period Phytoplankton (dpeaa)DE-He213 Dilution Factor (dpeaa)DE-He213 Grazing Rate (dpeaa)DE-He213 Zooplankton Grazing (dpeaa)DE-He213 Grazing Impact (dpeaa)DE-He213 |
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Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period |
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phytoplankton growth rate and zooplankton grazing in the western part of the black sea in the autumn period |
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Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period |
| abstract |
Abstract The results of the studies within the framework of the international expedition onboard R/V Vladimir Parshin in September–October 2005 are presented. Intensive development of Bacillariophyceae and Dynophyceae was recorded in the coastal waters of Bulgaria, Turkey, and in the Danube River Delta during the period of the investigations. The increase in the algae population was accompanied by rising of the Chlorophyll a concentration up to 2.0–5.5 mg $ m^{−3} $. In the deep water region, it did not exceed 0.54 mg $ m^{−3} $. The phytoplankton growth rate in the surface water layer varied from 0.1 to 1.0 $ day^{−1} $. The phytoplankton growth rate and $ NO_{2} $+$ NO_{3} $ concentration, as well as the silicon concentration, were correlative, as was described by the Michaelis-Menten equation. The phytoplankton growth was affected by the integral impact of basic nutrients. The zooplankton grazing varied from 0.10 to 0.69 $ day^{−1} $, and the average values in different regions may vary by 1.5 times. The microalgae size range is one of the major factors of the grazing regulation. The rate of the phytoplankton consumption was decreasing according the increasing of the largest diatom Pseudosolenia calcaravis impact on the total biomass of the nano- and microphytoplankton. © Pleiades Publishing, Ltd. 2009 |
| abstractGer |
Abstract The results of the studies within the framework of the international expedition onboard R/V Vladimir Parshin in September–October 2005 are presented. Intensive development of Bacillariophyceae and Dynophyceae was recorded in the coastal waters of Bulgaria, Turkey, and in the Danube River Delta during the period of the investigations. The increase in the algae population was accompanied by rising of the Chlorophyll a concentration up to 2.0–5.5 mg $ m^{−3} $. In the deep water region, it did not exceed 0.54 mg $ m^{−3} $. The phytoplankton growth rate in the surface water layer varied from 0.1 to 1.0 $ day^{−1} $. The phytoplankton growth rate and $ NO_{2} $+$ NO_{3} $ concentration, as well as the silicon concentration, were correlative, as was described by the Michaelis-Menten equation. The phytoplankton growth was affected by the integral impact of basic nutrients. The zooplankton grazing varied from 0.10 to 0.69 $ day^{−1} $, and the average values in different regions may vary by 1.5 times. The microalgae size range is one of the major factors of the grazing regulation. The rate of the phytoplankton consumption was decreasing according the increasing of the largest diatom Pseudosolenia calcaravis impact on the total biomass of the nano- and microphytoplankton. © Pleiades Publishing, Ltd. 2009 |
| abstract_unstemmed |
Abstract The results of the studies within the framework of the international expedition onboard R/V Vladimir Parshin in September–October 2005 are presented. Intensive development of Bacillariophyceae and Dynophyceae was recorded in the coastal waters of Bulgaria, Turkey, and in the Danube River Delta during the period of the investigations. The increase in the algae population was accompanied by rising of the Chlorophyll a concentration up to 2.0–5.5 mg $ m^{−3} $. In the deep water region, it did not exceed 0.54 mg $ m^{−3} $. The phytoplankton growth rate in the surface water layer varied from 0.1 to 1.0 $ day^{−1} $. The phytoplankton growth rate and $ NO_{2} $+$ NO_{3} $ concentration, as well as the silicon concentration, were correlative, as was described by the Michaelis-Menten equation. The phytoplankton growth was affected by the integral impact of basic nutrients. The zooplankton grazing varied from 0.10 to 0.69 $ day^{−1} $, and the average values in different regions may vary by 1.5 times. The microalgae size range is one of the major factors of the grazing regulation. The rate of the phytoplankton consumption was decreasing according the increasing of the largest diatom Pseudosolenia calcaravis impact on the total biomass of the nano- and microphytoplankton. © Pleiades Publishing, Ltd. 2009 |
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Phytoplankton growth rate and zooplankton grazing in the western part of the Black Sea in the autumn period |
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Babich, I. I. Tugrul, S. Moncheva, S. Stefanova, K. |
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2024-07-03T14:10:15.346Z |
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|
| score |
7.400055 |