Algal and aquatic plant carbon concentrating mechanisms in relation to environmental change
Carbon dioxide concentrating mechanisms (also known as inorganic carbon concentrating mechanisms; both abbreviated as CCMs) presumably evolved under conditions of low CO 2 availability. However, the timing of their origin is unclear since there are no sound estimates from molecular clocks, and even...
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description | Carbon dioxide concentrating mechanisms (also known as inorganic carbon concentrating mechanisms; both abbreviated as CCMs) presumably evolved under conditions of low CO
2
availability. However, the timing of their origin is unclear since there are no sound estimates from molecular clocks, and even if there were, there are no proxies for the functioning of CCMs. Accordingly, we cannot use previous episodes of high CO
2
(e.g. the Palaeocene–Eocene Thermal Maximum) to indicate how organisms with CCMs responded. Present and predicted environmental change in terms of increased CO
2
and temperature are leading to increased CO
2
and HCO
3
−
and decreased CO
3
2−
and pH in surface seawater, as well as decreasing the depth of the upper mixed layer and increasing the degree of isolation of this layer with respect to nutrient flux from deeper waters. The outcome of these forcing factors is to increase the availability of inorganic carbon, photosynthetic active radiation (PAR) and ultraviolet B radiation (UVB) to aquatic photolithotrophs and to decrease the supply of the nutrients (combined) nitrogen and phosphorus and of any non-aeolian iron. The influence of these variations on CCM expression has been examined to varying degrees as acclimation by extant organisms. Increased PAR increases CCM expression in terms of CO
2
affinity, whilst increased UVB has a range of effects in the organisms examined; little relevant information is available on increased temperature. Decreased combined nitrogen supply generally increases CO
2
affinity, decreased iron availability increases CO
2
affinity, and decreased phosphorus supply has varying effects on the organisms examined. There are few data sets showing interactions amongst the observed changes, and even less information on genetic (adaptation) changes in response to the forcing factors. In freshwaters, changes in phytoplankton species composition may alter with environmental change with consequences for frequency of species with or without CCMs. The information available permits less predictive power as to the effect of the forcing factors on CCM expression than for their overall effects on growth. CCMs are currently not part of models as to how global environmental change has altered, and is likely to further alter, algal and aquatic plant primary productivity. |
doi_str_mv | 10.1007/s11120-011-9632-6 |
format | Article |
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2
availability. However, the timing of their origin is unclear since there are no sound estimates from molecular clocks, and even if there were, there are no proxies for the functioning of CCMs. Accordingly, we cannot use previous episodes of high CO
2
(e.g. the Palaeocene–Eocene Thermal Maximum) to indicate how organisms with CCMs responded. Present and predicted environmental change in terms of increased CO
2
and temperature are leading to increased CO
2
and HCO
3
−
and decreased CO
3
2−
and pH in surface seawater, as well as decreasing the depth of the upper mixed layer and increasing the degree of isolation of this layer with respect to nutrient flux from deeper waters. The outcome of these forcing factors is to increase the availability of inorganic carbon, photosynthetic active radiation (PAR) and ultraviolet B radiation (UVB) to aquatic photolithotrophs and to decrease the supply of the nutrients (combined) nitrogen and phosphorus and of any non-aeolian iron. The influence of these variations on CCM expression has been examined to varying degrees as acclimation by extant organisms. Increased PAR increases CCM expression in terms of CO
2
affinity, whilst increased UVB has a range of effects in the organisms examined; little relevant information is available on increased temperature. Decreased combined nitrogen supply generally increases CO
2
affinity, decreased iron availability increases CO
2
affinity, and decreased phosphorus supply has varying effects on the organisms examined. There are few data sets showing interactions amongst the observed changes, and even less information on genetic (adaptation) changes in response to the forcing factors. In freshwaters, changes in phytoplankton species composition may alter with environmental change with consequences for frequency of species with or without CCMs. The information available permits less predictive power as to the effect of the forcing factors on CCM expression than for their overall effects on growth. CCMs are currently not part of models as to how global environmental change has altered, and is likely to further alter, algal and aquatic plant primary productivity.</description><identifier>ISSN: 0166-8595</identifier><identifier>EISSN: 1573-5079</identifier><identifier>DOI: 10.1007/s11120-011-9632-6</identifier><identifier>PMID: 21327536</identifier><language>eng</language><publisher>Dordrecht: Springer Netherlands</publisher><subject>Algae ; Aquatic Organisms - physiology ; Aquatic plants ; Autotrophic Processes ; Biochemistry ; Biomedical and Life Sciences ; Carbon ; Carbon - metabolism ; Carbon Dioxide - metabolism ; Climate Change ; Ecosystem ; Environment ; Environmental aspects ; Fresh Water ; Hydrogen-Ion Concentration ; Iron - metabolism ; Life Sciences ; Nitrogen - metabolism ; Nuclear radiation ; Phosphorus - metabolism ; Photosynthesis ; Photosynthesis - physiology ; Phytoplankton - physiology ; Plant Genetics and Genomics ; Plant Physiological Phenomena ; Plant Physiology ; Plant Sciences ; Plants - metabolism ; Review ; Sea-water ; Seawater ; Temperature ; Ultraviolet Rays</subject><ispartof>Photosynthesis research, 2011-09, Vol.109 (1-3), p.281-296</ispartof><rights>Springer Science+Business Media B.V. 2011</rights><rights>COPYRIGHT 2011 Springer</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c552t-a6ae8ed365096d8f29774493083305368e05ef3d141e1ade02589586436cfc8d3</citedby><cites>FETCH-LOGICAL-c552t-a6ae8ed365096d8f29774493083305368e05ef3d141e1ade02589586436cfc8d3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://link.springer.com/content/pdf/10.1007/s11120-011-9632-6$$EPDF$$P50$$Gspringer$$H</linktopdf><linktohtml>$$Uhttps://link.springer.com/10.1007/s11120-011-9632-6$$EHTML$$P50$$Gspringer$$H</linktohtml><link.rule.ids>314,780,784,27924,27925,41488,42557,51319</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/21327536$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Raven, John A.</creatorcontrib><creatorcontrib>Giordano, Mario</creatorcontrib><creatorcontrib>Beardall, John</creatorcontrib><creatorcontrib>Maberly, Stephen C.</creatorcontrib><title>Algal and aquatic plant carbon concentrating mechanisms in relation to environmental change</title><title>Photosynthesis research</title><addtitle>Photosynth Res</addtitle><addtitle>Photosynth Res</addtitle><description>Carbon dioxide concentrating mechanisms (also known as inorganic carbon concentrating mechanisms; both abbreviated as CCMs) presumably evolved under conditions of low CO
2
availability. However, the timing of their origin is unclear since there are no sound estimates from molecular clocks, and even if there were, there are no proxies for the functioning of CCMs. Accordingly, we cannot use previous episodes of high CO
2
(e.g. the Palaeocene–Eocene Thermal Maximum) to indicate how organisms with CCMs responded. Present and predicted environmental change in terms of increased CO
2
and temperature are leading to increased CO
2
and HCO
3
−
and decreased CO
3
2−
and pH in surface seawater, as well as decreasing the depth of the upper mixed layer and increasing the degree of isolation of this layer with respect to nutrient flux from deeper waters. The outcome of these forcing factors is to increase the availability of inorganic carbon, photosynthetic active radiation (PAR) and ultraviolet B radiation (UVB) to aquatic photolithotrophs and to decrease the supply of the nutrients (combined) nitrogen and phosphorus and of any non-aeolian iron. The influence of these variations on CCM expression has been examined to varying degrees as acclimation by extant organisms. Increased PAR increases CCM expression in terms of CO
2
affinity, whilst increased UVB has a range of effects in the organisms examined; little relevant information is available on increased temperature. Decreased combined nitrogen supply generally increases CO
2
affinity, decreased iron availability increases CO
2
affinity, and decreased phosphorus supply has varying effects on the organisms examined. There are few data sets showing interactions amongst the observed changes, and even less information on genetic (adaptation) changes in response to the forcing factors. In freshwaters, changes in phytoplankton species composition may alter with environmental change with consequences for frequency of species with or without CCMs. The information available permits less predictive power as to the effect of the forcing factors on CCM expression than for their overall effects on growth. CCMs are currently not part of models as to how global environmental change has altered, and is likely to further alter, algal and aquatic plant primary productivity.</description><subject>Algae</subject><subject>Aquatic Organisms - physiology</subject><subject>Aquatic plants</subject><subject>Autotrophic Processes</subject><subject>Biochemistry</subject><subject>Biomedical and Life Sciences</subject><subject>Carbon</subject><subject>Carbon - metabolism</subject><subject>Carbon Dioxide - metabolism</subject><subject>Climate Change</subject><subject>Ecosystem</subject><subject>Environment</subject><subject>Environmental aspects</subject><subject>Fresh Water</subject><subject>Hydrogen-Ion Concentration</subject><subject>Iron - metabolism</subject><subject>Life Sciences</subject><subject>Nitrogen - metabolism</subject><subject>Nuclear radiation</subject><subject>Phosphorus - metabolism</subject><subject>Photosynthesis</subject><subject>Photosynthesis - physiology</subject><subject>Phytoplankton - physiology</subject><subject>Plant Genetics and Genomics</subject><subject>Plant Physiological Phenomena</subject><subject>Plant Physiology</subject><subject>Plant Sciences</subject><subject>Plants - metabolism</subject><subject>Review</subject><subject>Sea-water</subject><subject>Seawater</subject><subject>Temperature</subject><subject>Ultraviolet Rays</subject><issn>0166-8595</issn><issn>1573-5079</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2011</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><recordid>eNp1kUFP3DAQhS1UBAvtD-ilsnrjEBjbseMcVwhaJKRKhZ56sIwz2QYlzmIniP57ZhUo4lD5YGnme-N5fox9FnAqAKqzLISQUIAQRW2ULMweWwldqUJDVX9gKxDGFFbX-pAd5XwPANYIdcAOpVCy0sqs2O91v_E997Hh_mH2Uxf4tvdx4sGnuzHyMMaAcUrUiRs-YPjjY5eHzLvIE_ZUJmgaOcbHLo1xIJbG7agNfmT7re8zfnq5j9mvy4vb8-_F9Y9vV-fr6yJoLafCG48WG2U01KaxrayrqixrBVYpoCUtgsZWNaIUKHyDILWttTWlMqENtlHH7Osyd5vGhxnz5O7HOUV60llbV1ZZJQk6XSCyi66L7UimAp0Gh45cYttRfa2MNFCVUpPg5J2AmAmfpo2fc3ZXNz_fs2JhQxpzTti6beoGn_46AW4XlVuichSV20XlDGm-vGw93w3Y_FO8ZkOAXIBMLfrO9Gbr_1OfAbjinNs</recordid><startdate>20110901</startdate><enddate>20110901</enddate><creator>Raven, John A.</creator><creator>Giordano, Mario</creator><creator>Beardall, John</creator><creator>Maberly, Stephen C.</creator><general>Springer Netherlands</general><general>Springer</general><general>Springer Nature B.V</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>ISR</scope><scope>3V.</scope><scope>7QP</scope><scope>7X7</scope><scope>7XB</scope><scope>88A</scope><scope>88E</scope><scope>88I</scope><scope>8AO</scope><scope>8FE</scope><scope>8FH</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>ABUWG</scope><scope>AFKRA</scope><scope>AZQEC</scope><scope>BBNVY</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FYUFA</scope><scope>GHDGH</scope><scope>GNUQQ</scope><scope>HCIFZ</scope><scope>K9.</scope><scope>LK8</scope><scope>M0S</scope><scope>M1P</scope><scope>M2P</scope><scope>M7N</scope><scope>M7P</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PRINS</scope><scope>Q9U</scope></search><sort><creationdate>20110901</creationdate><title>Algal and aquatic plant carbon concentrating mechanisms in relation to environmental change</title><author>Raven, John A. ; Giordano, Mario ; Beardall, John ; Maberly, Stephen C.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c552t-a6ae8ed365096d8f29774493083305368e05ef3d141e1ade02589586436cfc8d3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2011</creationdate><topic>Algae</topic><topic>Aquatic Organisms - physiology</topic><topic>Aquatic plants</topic><topic>Autotrophic Processes</topic><topic>Biochemistry</topic><topic>Biomedical and Life Sciences</topic><topic>Carbon</topic><topic>Carbon - metabolism</topic><topic>Carbon Dioxide - metabolism</topic><topic>Climate Change</topic><topic>Ecosystem</topic><topic>Environment</topic><topic>Environmental aspects</topic><topic>Fresh Water</topic><topic>Hydrogen-Ion Concentration</topic><topic>Iron - metabolism</topic><topic>Life Sciences</topic><topic>Nitrogen - metabolism</topic><topic>Nuclear radiation</topic><topic>Phosphorus - metabolism</topic><topic>Photosynthesis</topic><topic>Photosynthesis - physiology</topic><topic>Phytoplankton - physiology</topic><topic>Plant Genetics and Genomics</topic><topic>Plant Physiological Phenomena</topic><topic>Plant Physiology</topic><topic>Plant Sciences</topic><topic>Plants - metabolism</topic><topic>Review</topic><topic>Sea-water</topic><topic>Seawater</topic><topic>Temperature</topic><topic>Ultraviolet Rays</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Raven, John A.</creatorcontrib><creatorcontrib>Giordano, Mario</creatorcontrib><creatorcontrib>Beardall, John</creatorcontrib><creatorcontrib>Maberly, Stephen C.</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Gale In Context: Science</collection><collection>ProQuest Central (Corporate)</collection><collection>Calcium & Calcified Tissue Abstracts</collection><collection>Health & Medical Collection</collection><collection>ProQuest Central (purchase pre-March 2016)</collection><collection>Biology Database (Alumni Edition)</collection><collection>Medical Database (Alumni Edition)</collection><collection>Science Database (Alumni Edition)</collection><collection>ProQuest Pharma Collection</collection><collection>ProQuest SciTech Collection</collection><collection>ProQuest Natural Science Collection</collection><collection>Hospital Premium Collection</collection><collection>Hospital Premium Collection (Alumni Edition)</collection><collection>ProQuest Central (Alumni) (purchase pre-March 2016)</collection><collection>ProQuest Central (Alumni Edition)</collection><collection>ProQuest Central UK/Ireland</collection><collection>ProQuest Central Essentials</collection><collection>Biological Science Collection</collection><collection>ProQuest Central</collection><collection>ProQuest Natural Science Collection</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central</collection><collection>Health Research Premium Collection</collection><collection>Health Research Premium Collection (Alumni)</collection><collection>ProQuest Central Student</collection><collection>SciTech Premium Collection</collection><collection>ProQuest Health & Medical Complete (Alumni)</collection><collection>Biological Sciences</collection><collection>Health & Medical Collection (Alumni Edition)</collection><collection>PML(ProQuest Medical Library)</collection><collection>Science Database</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biological Science Database</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>ProQuest Central China</collection><collection>ProQuest Central Basic</collection><jtitle>Photosynthesis research</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Raven, John A.</au><au>Giordano, Mario</au><au>Beardall, John</au><au>Maberly, Stephen C.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Algal and aquatic plant carbon concentrating mechanisms in relation to environmental change</atitle><jtitle>Photosynthesis research</jtitle><stitle>Photosynth Res</stitle><addtitle>Photosynth Res</addtitle><date>2011-09-01</date><risdate>2011</risdate><volume>109</volume><issue>1-3</issue><spage>281</spage><epage>296</epage><pages>281-296</pages><issn>0166-8595</issn><eissn>1573-5079</eissn><abstract>Carbon dioxide concentrating mechanisms (also known as inorganic carbon concentrating mechanisms; both abbreviated as CCMs) presumably evolved under conditions of low CO
2
availability. However, the timing of their origin is unclear since there are no sound estimates from molecular clocks, and even if there were, there are no proxies for the functioning of CCMs. Accordingly, we cannot use previous episodes of high CO
2
(e.g. the Palaeocene–Eocene Thermal Maximum) to indicate how organisms with CCMs responded. Present and predicted environmental change in terms of increased CO
2
and temperature are leading to increased CO
2
and HCO
3
−
and decreased CO
3
2−
and pH in surface seawater, as well as decreasing the depth of the upper mixed layer and increasing the degree of isolation of this layer with respect to nutrient flux from deeper waters. The outcome of these forcing factors is to increase the availability of inorganic carbon, photosynthetic active radiation (PAR) and ultraviolet B radiation (UVB) to aquatic photolithotrophs and to decrease the supply of the nutrients (combined) nitrogen and phosphorus and of any non-aeolian iron. The influence of these variations on CCM expression has been examined to varying degrees as acclimation by extant organisms. Increased PAR increases CCM expression in terms of CO
2
affinity, whilst increased UVB has a range of effects in the organisms examined; little relevant information is available on increased temperature. Decreased combined nitrogen supply generally increases CO
2
affinity, decreased iron availability increases CO
2
affinity, and decreased phosphorus supply has varying effects on the organisms examined. There are few data sets showing interactions amongst the observed changes, and even less information on genetic (adaptation) changes in response to the forcing factors. In freshwaters, changes in phytoplankton species composition may alter with environmental change with consequences for frequency of species with or without CCMs. The information available permits less predictive power as to the effect of the forcing factors on CCM expression than for their overall effects on growth. CCMs are currently not part of models as to how global environmental change has altered, and is likely to further alter, algal and aquatic plant primary productivity.</abstract><cop>Dordrecht</cop><pub>Springer Netherlands</pub><pmid>21327536</pmid><doi>10.1007/s11120-011-9632-6</doi><tpages>16</tpages><oa>free_for_read</oa></addata></record> |
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subjects | Algae Aquatic Organisms - physiology Aquatic plants Autotrophic Processes Biochemistry Biomedical and Life Sciences Carbon Carbon - metabolism Carbon Dioxide - metabolism Climate Change Ecosystem Environment Environmental aspects Fresh Water Hydrogen-Ion Concentration Iron - metabolism Life Sciences Nitrogen - metabolism Nuclear radiation Phosphorus - metabolism Photosynthesis Photosynthesis - physiology Phytoplankton - physiology Plant Genetics and Genomics Plant Physiological Phenomena Plant Physiology Plant Sciences Plants - metabolism Review Sea-water Seawater Temperature Ultraviolet Rays |
title | Algal and aquatic plant carbon concentrating mechanisms in relation to environmental change |
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