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231224s2012 xx |||||o 00| ||eng c |
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|a 10.1007/s10646-012-0865-8
|2 doi
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|a pubmed24n0718.xml
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|a (DE-627)NLM215572505
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|a (NLM)22350106
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|a DE-627
|b ger
|c DE-627
|e rakwb
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|a eng
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| 100 |
1 |
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|a Okamura, Hideo
|e verfasserin
|4 aut
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| 245 |
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|a Effects of metal pyrithione antifoulants on freshwater macrophyte Lemna gibba G3 determined by image analysis
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|c 2012
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|a Text
|b txt
|2 rdacontent
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|a ƒaComputermedien
|b c
|2 rdamedia
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| 338 |
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|a ƒa Online-Ressource
|b cr
|2 rdacarrier
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|a Date Completed 10.09.2012
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|a Date Revised 21.10.2021
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|a published: Print-Electronic
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|a Citation Status MEDLINE
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|a Copper pyrithione (CuPT(2)) and zinc pyrithione (ZnPT(2)) are two popular antifouling agents that prevent biofouling. Research into the environmental effects of metal pyrithiones has mainly focused on aquatic animal species such as fish and crustaceans, and little attention has been paid to primary producers. There have been few reports on residues in environmental matrices because of the high photolabile characteristics of the agents. Residue analyses and ecological effects of the metabolites and metal pyrithiones are not yet fully understood. This study was undertaken to assess the effects of CuPT(2), ZnPT(2), and six metabolites (PT(2): 2,2'-dithio-bispyridine N-oxide, PS(2): 2,2'-dithio-bispyridine, PSA: pyridine-2-sulfonic acid, HPT: 2-mercaptopyridine N-oxide, HPS: 2-mercaptopyridine, and PO: pyridine N-oxide) on a freshwater macrophyte. A 7-day static bioassay using axenic duckweed Lemna gibba G3 was performed under laboratory conditions. Toxic effects of test compounds were assessed by biomass reduction and morphological changes were determined in image analysis. Concentrations of ZnPT(2) and CuPT(2) and those of PT(2) and HPT in the medium were determined by derivatizing 2,2'-dithio-bispyridine mono-N-oxide with pyridine disulfide/ethylene diamine tetra-acetic acid reagent that was equimolar with pyrithione. The toxic intensity of the compounds was calculated from the measured concentrations after 7-day exposure. ZnPT(2), CuPT(2), PT(2), and HPT inhibited the growth of L. gibba with EC(50) ranging from 77 to 140 μg/l as calculated from the total frond number as the conventional index, whereas the other four metabolites had less effect even at 10 mg/l. The presence of the former four toxic derivatives resulted in abnormally shaped and unhealthily colored fronds, whose size was about 20% of the control fronds. EC(50), calculated from the healthy frond area determined in image analysis, ranged from 10 to 53 μg/l. Thus, image analysis as part of a duckweed bioassay can detect the toxic effects of pyrithione derivatives with 3-10 times higher sensitivity than the traditional index
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|a Journal Article
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|a Research Support, Non-U.S. Gov't
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|a Organometallic Compounds
|2 NLM
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|a Pyridines
|2 NLM
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| 650 |
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|a Water Pollutants, Chemical
|2 NLM
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| 650 |
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7 |
|a copper pyrithione
|2 NLM
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| 650 |
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|a pyridine N-oxide
|2 NLM
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| 650 |
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|a 91F12JJJ4H
|2 NLM
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| 650 |
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|a pyrithione zinc
|2 NLM
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| 650 |
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|a R953O2RHZ5
|2 NLM
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| 700 |
1 |
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|a Togosmaa, Luvsantsend
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Sawamoto, Takuya
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Fukushi, Keiichi
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Nishida, Tomoaki
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Beppu, Toshio
|e verfasserin
|4 aut
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| 773 |
0 |
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|i Enthalten in
|t Ecotoxicology (London, England)
|d 1992
|g 21(2012), 4 vom: 21. Mai, Seite 1102-11
|w (DE-627)NLM098212214
|x 1573-3017
|7 nnns
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| 773 |
1 |
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|g volume:21
|g year:2012
|g number:4
|g day:21
|g month:05
|g pages:1102-11
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| 856 |
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|u http://dx.doi.org/10.1007/s10646-012-0865-8
|3 Volltext
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|a GBV_ILN_350
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|a AR
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|d 21
|j 2012
|e 4
|b 21
|c 05
|h 1102-11
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