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key role of aluminium in phosphorus availability, food web structure, and plankton dynamics in strongly acidified lakes
We studied extracellular acid phosphatase activity (AcPA) of planktonic microorganisms, aluminium (Al) speciation, and phosphorus (P) cycling in three atmospherically acidified (pH of 4.5â5.1) mountain forest lakes: Äertovo jezero (CT), Prášilské jezero (PR), and PleÅ¡né jezero (PL) in the Bo...
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Published in: | Biológia 2006-01, Vol.61 (20), p.S441-S451 |
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description | We studied extracellular acid phosphatase activity (AcPA) of planktonic microorganisms, aluminium (Al) speciation, and phosphorus (P) cycling in three atmospherically acidified (pH of 4.5â5.1) mountain forest lakes: Äertovo jezero (CT), Prášilské jezero (PR), and PleÅ¡né jezero (PL) in the Bohemian Forest (Å umava, Böhmerwald). Microorganisms dominated pelagic food webs of the lakes and crustacean zooplankton were important only in PR, with the lowest Al concentrations (193 µg Lâ1) due to 3â4 times lower terrestrial input. The lakes differed substantially in Al speciation, i.e., in the proportion of ionic and particulate forms, with the highest proportion of ionic Al in the most acid CT (pH = 4.5). The P concentration in the inlet of PL (mean: 22.9 µg Lâ1) was about five times higher than in CT and PR (3.9 and 5.1 µg Lâ1, respectively). Average total biomass of planktonic microorganisms in PL (593 µg C Lâ1) was, however, only â¼2-times higher than in CT and PR (235 and 272 µg C Lâ1, respectively). Enormous AcPA (means: 2.17â6.82 µmol Lâ1 hâ1) and high planktonic C : P ratios suggested severe P limitation of the plankton in all lakes. Comparing 1998 and 2003 seasons, we observed changes in water composition (pH and Al speciation) leading to a significant increase in phytoplankton biomass in the lakes. The increase in the seston C : P ratio during the same time, however, indicates a progressive P deficiency of the lakes. The terrestrial Al inputs, together with in-lake processes controlling the formation of particulate Al, reduced P availability for planktonic microorganisms and were responsible for the differences in AcPA. At pH < 5, moreover, ionic Al forms caused inhibition of extracellular phosphatases. We postulate that both particulate and ionic Al forms affect P availability (i.e., inhibition of extracellular phosphatases and inactivation of P), specifically shape the plankton composition in the lakes and affect plankton recovery from the acid stress. |
doi_str_mv | 10.2478/s11756-007-0077-5 |
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Microorganisms dominated pelagic food webs of the lakes and crustacean zooplankton were important only in PR, with the lowest Al concentrations (193 µg Lâ1) due to 3â4 times lower terrestrial input. The lakes differed substantially in Al speciation, i.e., in the proportion of ionic and particulate forms, with the highest proportion of ionic Al in the most acid CT (pH = 4.5). The P concentration in the inlet of PL (mean: 22.9 µg Lâ1) was about five times higher than in CT and PR (3.9 and 5.1 µg Lâ1, respectively). Average total biomass of planktonic microorganisms in PL (593 µg C Lâ1) was, however, only â¼2-times higher than in CT and PR (235 and 272 µg C Lâ1, respectively). Enormous AcPA (means: 2.17â6.82 µmol Lâ1 hâ1) and high planktonic C : P ratios suggested severe P limitation of the plankton in all lakes. Comparing 1998 and 2003 seasons, we observed changes in water composition (pH and Al speciation) leading to a significant increase in phytoplankton biomass in the lakes. The increase in the seston C : P ratio during the same time, however, indicates a progressive P deficiency of the lakes. The terrestrial Al inputs, together with in-lake processes controlling the formation of particulate Al, reduced P availability for planktonic microorganisms and were responsible for the differences in AcPA. At pH < 5, moreover, ionic Al forms caused inhibition of extracellular phosphatases. We postulate that both particulate and ionic Al forms affect P availability (i.e., inhibition of extracellular phosphatases and inactivation of P), specifically shape the plankton composition in the lakes and affect plankton recovery from the acid stress.</description><identifier>ISSN: 1336-9563</identifier><identifier>ISSN: 0006-3088</identifier><identifier>EISSN: 1336-9563</identifier><identifier>DOI: 10.2478/s11756-007-0077-5</identifier><language>eng</language><publisher>Heidelberg: Versita</publisher><subject>Acid phosphatase ; Acidification ; Aluminum ; Availability ; bacterioplankton ; Biomass ; carbon biomass ; Composition ; Crustacea ; Crustaceans ; Dynamic structural analysis ; extracellular phosphatases ; Food availability ; Food chains ; Food webs ; forests ; Freshwater ; hydrochemistry ; Inactivation ; Lakes ; Microorganisms ; Mountain forests ; Mountains ; pH effects ; Phosphatase ; Phosphorus ; Phytoplankton ; Plankton ; plankton stoichiometry ; recovery ; Seston ; Speciation ; Zooplankton</subject><ispartof>Biológia, 2006-01, Vol.61 (20), p.S441-S451</ispartof><rights>Institute of Zoology, Slovak Academy of Sciences 2006.</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c386t-17040d4c5f1f8b8ed60eb4fa87856edea6dc7a7afc8b6b281c9b7d06f28a41423</citedby><cites>FETCH-LOGICAL-c386t-17040d4c5f1f8b8ed60eb4fa87856edea6dc7a7afc8b6b281c9b7d06f28a41423</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,27903,27904</link.rule.ids></links><search><creatorcontrib>Vrba, Jaroslav</creatorcontrib><creatorcontrib>JiÅà KopáÄek</creatorcontrib><creatorcontrib>Thomas Bittl</creatorcontrib><creatorcontrib>JiÅà Nedoma</creatorcontrib><creatorcontrib>Alena Å trojsovÃ</creatorcontrib><creatorcontrib>Linda NedbalovÃ</creatorcontrib><creatorcontrib>LeoÅ¡ Kohout</creatorcontrib><creatorcontrib>Jan Fott</creatorcontrib><title>key role of aluminium in phosphorus availability, food web structure, and plankton dynamics in strongly acidified lakes</title><title>Biológia</title><description>We studied extracellular acid phosphatase activity (AcPA) of planktonic microorganisms, aluminium (Al) speciation, and phosphorus (P) cycling in three atmospherically acidified (pH of 4.5â5.1) mountain forest lakes: Äertovo jezero (CT), Prášilské jezero (PR), and PleÅ¡né jezero (PL) in the Bohemian Forest (Å umava, Böhmerwald). Microorganisms dominated pelagic food webs of the lakes and crustacean zooplankton were important only in PR, with the lowest Al concentrations (193 µg Lâ1) due to 3â4 times lower terrestrial input. The lakes differed substantially in Al speciation, i.e., in the proportion of ionic and particulate forms, with the highest proportion of ionic Al in the most acid CT (pH = 4.5). The P concentration in the inlet of PL (mean: 22.9 µg Lâ1) was about five times higher than in CT and PR (3.9 and 5.1 µg Lâ1, respectively). Average total biomass of planktonic microorganisms in PL (593 µg C Lâ1) was, however, only â¼2-times higher than in CT and PR (235 and 272 µg C Lâ1, respectively). Enormous AcPA (means: 2.17â6.82 µmol Lâ1 hâ1) and high planktonic C : P ratios suggested severe P limitation of the plankton in all lakes. Comparing 1998 and 2003 seasons, we observed changes in water composition (pH and Al speciation) leading to a significant increase in phytoplankton biomass in the lakes. The increase in the seston C : P ratio during the same time, however, indicates a progressive P deficiency of the lakes. The terrestrial Al inputs, together with in-lake processes controlling the formation of particulate Al, reduced P availability for planktonic microorganisms and were responsible for the differences in AcPA. At pH < 5, moreover, ionic Al forms caused inhibition of extracellular phosphatases. We postulate that both particulate and ionic Al forms affect P availability (i.e., inhibition of extracellular phosphatases and inactivation of P), specifically shape the plankton composition in the lakes and affect plankton recovery from the acid stress.</description><subject>Acid phosphatase</subject><subject>Acidification</subject><subject>Aluminum</subject><subject>Availability</subject><subject>bacterioplankton</subject><subject>Biomass</subject><subject>carbon biomass</subject><subject>Composition</subject><subject>Crustacea</subject><subject>Crustaceans</subject><subject>Dynamic structural analysis</subject><subject>extracellular phosphatases</subject><subject>Food availability</subject><subject>Food chains</subject><subject>Food webs</subject><subject>forests</subject><subject>Freshwater</subject><subject>hydrochemistry</subject><subject>Inactivation</subject><subject>Lakes</subject><subject>Microorganisms</subject><subject>Mountain forests</subject><subject>Mountains</subject><subject>pH effects</subject><subject>Phosphatase</subject><subject>Phosphorus</subject><subject>Phytoplankton</subject><subject>Plankton</subject><subject>plankton stoichiometry</subject><subject>recovery</subject><subject>Seston</subject><subject>Speciation</subject><subject>Zooplankton</subject><issn>1336-9563</issn><issn>0006-3088</issn><issn>1336-9563</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2006</creationdate><recordtype>article</recordtype><recordid>eNp1kUtr3TAQhU1poGnSH9BVBYWu4kaSZUl3GUL6gEAXSdZirMetcmXrVrJ68b-vjAsthS4OM4vvnBk4TfOW4I-UCXmdCRE9bzEWq0Tbv2jOSdfxdtfz7uVf-6vmdc7PGDPRY3LenA52QSkGi6JDEMroJ19G5Cd0_B5zVSoZwU_wAQYf_LxcIRejQSc7oDynoueS7BWCyaBjgOkwxwmZZYLR67ymVCZO-7Ag0N54561BAQ42XzZnDkK2b37Pi-bp093j7Zf2_tvnr7c3963uJJ9bIjDDhuneEScHaQ3HdmAOpJA9t8YCN1qAAKflwAcqid4NwmDuqARGGO0umg9b7jHFH8XmWY0-axvqrzaWrCgWOyK7FXz_D_gcS5rqb4pyziTvBMeVIhulU8w5WaeOyY-QFkWwWotQWxGqlrBKqL56bjbPCcJsk7H7VJa6_DnwXy8nFD8wRmrGuy3DQVSwTz6rpweKCceYYsqJ6H4B0n2bgw</recordid><startdate>20060101</startdate><enddate>20060101</enddate><creator>Vrba, Jaroslav</creator><creator>JiÅà KopáÄek</creator><creator>Thomas Bittl</creator><creator>JiÅà Nedoma</creator><creator>Alena Å trojsovÃ</creator><creator>Linda NedbalovÃ</creator><creator>LeoÅ¡ Kohout</creator><creator>Jan Fott</creator><general>Versita</general><general>Springer Nature B.V</general><scope>FBQ</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QG</scope><scope>7QL</scope><scope>7QP</scope><scope>7QR</scope><scope>7SN</scope><scope>7SS</scope><scope>7T5</scope><scope>7T7</scope><scope>7TK</scope><scope>7TM</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>H94</scope><scope>K9.</scope><scope>M7N</scope><scope>P64</scope><scope>RC3</scope><scope>F1W</scope><scope>H95</scope><scope>L.G</scope></search><sort><creationdate>20060101</creationdate><title>key role of aluminium in phosphorus availability, food web structure, and plankton dynamics in strongly acidified lakes</title><author>Vrba, Jaroslav ; JiÅà KopáÄek ; Thomas Bittl ; JiÅà Nedoma ; Alena Å trojsovà ; Linda Nedbalovà ; LeoÅ¡ Kohout ; Jan Fott</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c386t-17040d4c5f1f8b8ed60eb4fa87856edea6dc7a7afc8b6b281c9b7d06f28a41423</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2006</creationdate><topic>Acid phosphatase</topic><topic>Acidification</topic><topic>Aluminum</topic><topic>Availability</topic><topic>bacterioplankton</topic><topic>Biomass</topic><topic>carbon biomass</topic><topic>Composition</topic><topic>Crustacea</topic><topic>Crustaceans</topic><topic>Dynamic structural analysis</topic><topic>extracellular phosphatases</topic><topic>Food availability</topic><topic>Food chains</topic><topic>Food webs</topic><topic>forests</topic><topic>Freshwater</topic><topic>hydrochemistry</topic><topic>Inactivation</topic><topic>Lakes</topic><topic>Microorganisms</topic><topic>Mountain forests</topic><topic>Mountains</topic><topic>pH effects</topic><topic>Phosphatase</topic><topic>Phosphorus</topic><topic>Phytoplankton</topic><topic>Plankton</topic><topic>plankton stoichiometry</topic><topic>recovery</topic><topic>Seston</topic><topic>Speciation</topic><topic>Zooplankton</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Vrba, Jaroslav</creatorcontrib><creatorcontrib>JiÅà KopáÄek</creatorcontrib><creatorcontrib>Thomas Bittl</creatorcontrib><creatorcontrib>JiÅà Nedoma</creatorcontrib><creatorcontrib>Alena Å trojsovÃ</creatorcontrib><creatorcontrib>Linda NedbalovÃ</creatorcontrib><creatorcontrib>LeoÅ¡ Kohout</creatorcontrib><creatorcontrib>Jan Fott</creatorcontrib><collection>AGRIS</collection><collection>CrossRef</collection><collection>Animal Behavior Abstracts</collection><collection>Bacteriology Abstracts (Microbiology B)</collection><collection>Calcium & Calcified Tissue Abstracts</collection><collection>Chemoreception Abstracts</collection><collection>Ecology Abstracts</collection><collection>Entomology Abstracts (Full archive)</collection><collection>Immunology Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Neurosciences Abstracts</collection><collection>Nucleic Acids Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>AIDS and Cancer Research Abstracts</collection><collection>ProQuest Health & Medical Complete (Alumni)</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Genetics Abstracts</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 1: Biological Sciences & Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><jtitle>Biológia</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Vrba, Jaroslav</au><au>JiÅà KopáÄek</au><au>Thomas Bittl</au><au>JiÅà Nedoma</au><au>Alena Å trojsovÃ</au><au>Linda NedbalovÃ</au><au>LeoÅ¡ Kohout</au><au>Jan Fott</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>key role of aluminium in phosphorus availability, food web structure, and plankton dynamics in strongly acidified lakes</atitle><jtitle>Biológia</jtitle><date>2006-01-01</date><risdate>2006</risdate><volume>61</volume><issue>20</issue><spage>S441</spage><epage>S451</epage><pages>S441-S451</pages><issn>1336-9563</issn><issn>0006-3088</issn><eissn>1336-9563</eissn><abstract>We studied extracellular acid phosphatase activity (AcPA) of planktonic microorganisms, aluminium (Al) speciation, and phosphorus (P) cycling in three atmospherically acidified (pH of 4.5â5.1) mountain forest lakes: Äertovo jezero (CT), Prášilské jezero (PR), and PleÅ¡né jezero (PL) in the Bohemian Forest (Å umava, Böhmerwald). Microorganisms dominated pelagic food webs of the lakes and crustacean zooplankton were important only in PR, with the lowest Al concentrations (193 µg Lâ1) due to 3â4 times lower terrestrial input. The lakes differed substantially in Al speciation, i.e., in the proportion of ionic and particulate forms, with the highest proportion of ionic Al in the most acid CT (pH = 4.5). The P concentration in the inlet of PL (mean: 22.9 µg Lâ1) was about five times higher than in CT and PR (3.9 and 5.1 µg Lâ1, respectively). Average total biomass of planktonic microorganisms in PL (593 µg C Lâ1) was, however, only â¼2-times higher than in CT and PR (235 and 272 µg C Lâ1, respectively). Enormous AcPA (means: 2.17â6.82 µmol Lâ1 hâ1) and high planktonic C : P ratios suggested severe P limitation of the plankton in all lakes. Comparing 1998 and 2003 seasons, we observed changes in water composition (pH and Al speciation) leading to a significant increase in phytoplankton biomass in the lakes. The increase in the seston C : P ratio during the same time, however, indicates a progressive P deficiency of the lakes. The terrestrial Al inputs, together with in-lake processes controlling the formation of particulate Al, reduced P availability for planktonic microorganisms and were responsible for the differences in AcPA. At pH < 5, moreover, ionic Al forms caused inhibition of extracellular phosphatases. We postulate that both particulate and ionic Al forms affect P availability (i.e., inhibition of extracellular phosphatases and inactivation of P), specifically shape the plankton composition in the lakes and affect plankton recovery from the acid stress.</abstract><cop>Heidelberg</cop><pub>Versita</pub><doi>10.2478/s11756-007-0077-5</doi><tpages>1</tpages><oa>free_for_read</oa></addata></record> |
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subjects | Acid phosphatase Acidification Aluminum Availability bacterioplankton Biomass carbon biomass Composition Crustacea Crustaceans Dynamic structural analysis extracellular phosphatases Food availability Food chains Food webs forests Freshwater hydrochemistry Inactivation Lakes Microorganisms Mountain forests Mountains pH effects Phosphatase Phosphorus Phytoplankton Plankton plankton stoichiometry recovery Seston Speciation Zooplankton |
title | key role of aluminium in phosphorus availability, food web structure, and plankton dynamics in strongly acidified lakes |
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