Comparison of the effect of platinum on producers in aquatic environment
An enhanced worldwide application of platinum group elements (PGE), in particular platinum, has been observed during recent decades. An increased concentration of PGE was determined in collected samples of great amount of aqueous ecosystems.The aim was to compare phytotoxic effect of platinum (PtCl4...
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Veröffentlicht in: | Neuro-endocrinology letters 2012, Vol.33 Suppl 3, p.107-112 |
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creator | Bednarova, Ivana Haasova, Vendula Mikulaskova, Hana Nemcova, Barbora Strakova, Lenka Beklova, Miroslava |
description | An enhanced worldwide application of platinum group elements (PGE), in particular platinum, has been observed during recent decades. An increased concentration of PGE was determined in collected samples of great amount of aqueous ecosystems.The aim was to compare phytotoxic effect of platinum (PtCl4) by performing two different bioassays on green algae Pseudokirchneriella subcapitata and macrophyte duckweed, Lemna minor. MEDTHODS: The algal experiment (Pseudokichneriella subcapitata) followed OECD 201, the concentration row for PtCl4 was: 0.05; 0.01; 0.25; 0.5; 1 µM. The duckweed (Lemna minor) experiment was conducted according to OECD 221, employed PtCl4 concentrations were: 5; 10; 25; 50; 100 µM. Plants were cultivated as a microbiotest, using micro-volumes.
The results of the algal test showed significant growth inhibition of the final biomass. The values of 72hEC5(µ), 72hEC10(µ), 72hEC20(µ) counted on a basis of average specific growth rate (µ) were 0.31 µM, 0.58 µM and 1.12 µM of PtCl4, respectively. The values, obtained on a basis of the area under the growth curves (A), were 0.04 µM (72hEC5(A)), 0.24 µM (72hEC10(A)) and 0.64 µM (72hEC20(A)). The experiment with duckweed showed 50% of growth inhibition and the values of 168hEC50(µ) were 19.55 µM and 168hEC50(A) 13.63 µM of PtCl4.
The fronds of duckweed showed strong adverse effect of platinum influence (chlorosis, necrosis). The algal test and the estimation of 72hEC5(A) appears to be the most sensitive. |
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The results of the algal test showed significant growth inhibition of the final biomass. The values of 72hEC5(µ), 72hEC10(µ), 72hEC20(µ) counted on a basis of average specific growth rate (µ) were 0.31 µM, 0.58 µM and 1.12 µM of PtCl4, respectively. The values, obtained on a basis of the area under the growth curves (A), were 0.04 µM (72hEC5(A)), 0.24 µM (72hEC10(A)) and 0.64 µM (72hEC20(A)). The experiment with duckweed showed 50% of growth inhibition and the values of 168hEC50(µ) were 19.55 µM and 168hEC50(A) 13.63 µM of PtCl4.
The fronds of duckweed showed strong adverse effect of platinum influence (chlorosis, necrosis). The algal test and the estimation of 72hEC5(A) appears to be the most sensitive.</description><identifier>ISSN: 0172-780X</identifier><identifier>PMID: 23353852</identifier><language>eng</language><publisher>Sweden</publisher><subject>Biological Assay ; Biomass ; Chlorophyta - drug effects ; Chlorophyta - growth & development ; Dose-Response Relationship, Drug ; Ecosystem ; Platinum - toxicity ; Platinum Compounds - toxicity ; Toxicity Tests ; Water Pollutants, Chemical - toxicity</subject><ispartof>Neuro-endocrinology letters, 2012, Vol.33 Suppl 3, p.107-112</ispartof><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,4010</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/23353852$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Bednarova, Ivana</creatorcontrib><creatorcontrib>Haasova, Vendula</creatorcontrib><creatorcontrib>Mikulaskova, Hana</creatorcontrib><creatorcontrib>Nemcova, Barbora</creatorcontrib><creatorcontrib>Strakova, Lenka</creatorcontrib><creatorcontrib>Beklova, Miroslava</creatorcontrib><title>Comparison of the effect of platinum on producers in aquatic environment</title><title>Neuro-endocrinology letters</title><addtitle>Neuro Endocrinol Lett</addtitle><description>An enhanced worldwide application of platinum group elements (PGE), in particular platinum, has been observed during recent decades. An increased concentration of PGE was determined in collected samples of great amount of aqueous ecosystems.The aim was to compare phytotoxic effect of platinum (PtCl4) by performing two different bioassays on green algae Pseudokirchneriella subcapitata and macrophyte duckweed, Lemna minor. MEDTHODS: The algal experiment (Pseudokichneriella subcapitata) followed OECD 201, the concentration row for PtCl4 was: 0.05; 0.01; 0.25; 0.5; 1 µM. The duckweed (Lemna minor) experiment was conducted according to OECD 221, employed PtCl4 concentrations were: 5; 10; 25; 50; 100 µM. Plants were cultivated as a microbiotest, using micro-volumes.
The results of the algal test showed significant growth inhibition of the final biomass. The values of 72hEC5(µ), 72hEC10(µ), 72hEC20(µ) counted on a basis of average specific growth rate (µ) were 0.31 µM, 0.58 µM and 1.12 µM of PtCl4, respectively. The values, obtained on a basis of the area under the growth curves (A), were 0.04 µM (72hEC5(A)), 0.24 µM (72hEC10(A)) and 0.64 µM (72hEC20(A)). The experiment with duckweed showed 50% of growth inhibition and the values of 168hEC50(µ) were 19.55 µM and 168hEC50(A) 13.63 µM of PtCl4.
The fronds of duckweed showed strong adverse effect of platinum influence (chlorosis, necrosis). The algal test and the estimation of 72hEC5(A) appears to be the most sensitive.</description><subject>Biological Assay</subject><subject>Biomass</subject><subject>Chlorophyta - drug effects</subject><subject>Chlorophyta - growth & development</subject><subject>Dose-Response Relationship, Drug</subject><subject>Ecosystem</subject><subject>Platinum - toxicity</subject><subject>Platinum Compounds - toxicity</subject><subject>Toxicity Tests</subject><subject>Water Pollutants, Chemical - toxicity</subject><issn>0172-780X</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2012</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNo1j01LxDAYhHNQ3HX1L0iOXgr5aNrmKEVdYcGLgreSJm8w0iTdJBX893ZxPQ3DMwwzF2hLaMuqtiMfG3Sd8xchTArGr9CGcS54J9gW7fvoZ5VcjgFHi8snYLAWdDm5eVLFhcXjFc4pmkVDytgFrI7LSjSG8O1SDB5CuUGXVk0Zbs-6Q-9Pj2_9vjq8Pr_0D4dqZpSWimo6cktsY0fFSM07rqWQIAzhyoLhsm3UaKXS0ArTUEpXLru2HsFo2wHjO3T_17sOOi6Qy-Bd1jBNKkBc8kA5bWsiSXeK3p2jy-jBDHNyXqWf4f89_wXohVYM</recordid><startdate>2012</startdate><enddate>2012</enddate><creator>Bednarova, Ivana</creator><creator>Haasova, Vendula</creator><creator>Mikulaskova, Hana</creator><creator>Nemcova, Barbora</creator><creator>Strakova, Lenka</creator><creator>Beklova, Miroslava</creator><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>7X8</scope></search><sort><creationdate>2012</creationdate><title>Comparison of the effect of platinum on producers in aquatic environment</title><author>Bednarova, Ivana ; Haasova, Vendula ; Mikulaskova, Hana ; Nemcova, Barbora ; Strakova, Lenka ; Beklova, Miroslava</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-p211t-1c1b3f0f6fba204383c959e5d03afed3976abf9ace75d61113c99874bedcf8e23</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2012</creationdate><topic>Biological Assay</topic><topic>Biomass</topic><topic>Chlorophyta - drug effects</topic><topic>Chlorophyta - growth & development</topic><topic>Dose-Response Relationship, Drug</topic><topic>Ecosystem</topic><topic>Platinum - toxicity</topic><topic>Platinum Compounds - toxicity</topic><topic>Toxicity Tests</topic><topic>Water Pollutants, Chemical - toxicity</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Bednarova, Ivana</creatorcontrib><creatorcontrib>Haasova, Vendula</creatorcontrib><creatorcontrib>Mikulaskova, Hana</creatorcontrib><creatorcontrib>Nemcova, Barbora</creatorcontrib><creatorcontrib>Strakova, Lenka</creatorcontrib><creatorcontrib>Beklova, Miroslava</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>MEDLINE - Academic</collection><jtitle>Neuro-endocrinology letters</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Bednarova, Ivana</au><au>Haasova, Vendula</au><au>Mikulaskova, Hana</au><au>Nemcova, Barbora</au><au>Strakova, Lenka</au><au>Beklova, Miroslava</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Comparison of the effect of platinum on producers in aquatic environment</atitle><jtitle>Neuro-endocrinology letters</jtitle><addtitle>Neuro Endocrinol Lett</addtitle><date>2012</date><risdate>2012</risdate><volume>33 Suppl 3</volume><spage>107</spage><epage>112</epage><pages>107-112</pages><issn>0172-780X</issn><abstract>An enhanced worldwide application of platinum group elements (PGE), in particular platinum, has been observed during recent decades. An increased concentration of PGE was determined in collected samples of great amount of aqueous ecosystems.The aim was to compare phytotoxic effect of platinum (PtCl4) by performing two different bioassays on green algae Pseudokirchneriella subcapitata and macrophyte duckweed, Lemna minor. MEDTHODS: The algal experiment (Pseudokichneriella subcapitata) followed OECD 201, the concentration row for PtCl4 was: 0.05; 0.01; 0.25; 0.5; 1 µM. The duckweed (Lemna minor) experiment was conducted according to OECD 221, employed PtCl4 concentrations were: 5; 10; 25; 50; 100 µM. Plants were cultivated as a microbiotest, using micro-volumes.
The results of the algal test showed significant growth inhibition of the final biomass. The values of 72hEC5(µ), 72hEC10(µ), 72hEC20(µ) counted on a basis of average specific growth rate (µ) were 0.31 µM, 0.58 µM and 1.12 µM of PtCl4, respectively. The values, obtained on a basis of the area under the growth curves (A), were 0.04 µM (72hEC5(A)), 0.24 µM (72hEC10(A)) and 0.64 µM (72hEC20(A)). The experiment with duckweed showed 50% of growth inhibition and the values of 168hEC50(µ) were 19.55 µM and 168hEC50(A) 13.63 µM of PtCl4.
The fronds of duckweed showed strong adverse effect of platinum influence (chlorosis, necrosis). The algal test and the estimation of 72hEC5(A) appears to be the most sensitive.</abstract><cop>Sweden</cop><pmid>23353852</pmid><tpages>6</tpages></addata></record> |
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subjects | Biological Assay Biomass Chlorophyta - drug effects Chlorophyta - growth & development Dose-Response Relationship, Drug Ecosystem Platinum - toxicity Platinum Compounds - toxicity Toxicity Tests Water Pollutants, Chemical - toxicity |
title | Comparison of the effect of platinum on producers in aquatic environment |
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