Combined toxicity of triclosan, 2,4-dichlorophenol and 2,4,6-trichlorophenol to zebrafish (Danio rerio)
•The highest TCSD toxicity is at a TCS:2,4,6-TCP:2,4-DCP concentration ratio of 1:2:4.•The interactions of TCS and its two derivatives produce partly synergistic toxicity.•TCSD produces dose-dependent effects on hatching, malformation and mortality.•ALP and ORO staining prove TCSD affected vascular...
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description | •The highest TCSD toxicity is at a TCS:2,4,6-TCP:2,4-DCP concentration ratio of 1:2:4.•The interactions of TCS and its two derivatives produce partly synergistic toxicity.•TCSD produces dose-dependent effects on hatching, malformation and mortality.•ALP and ORO staining prove TCSD affected vascular branches and fat metabolism.•AO and AB staining proves TCSD affects apoptotic cells and cartilage development.
Triclosan (TCS), 2,4,6-trichlorophenol (2,4,6-TCP) and 2,4-dichlorophenol (2,4-DCP) are the most prevalent chlorinated phenolic pollutants in aquatic environments. Our results showed LC50 and EC50 values of 0.51, 1.11, 2.45mg/L, and 0.36, 0.74, 1.53mg/L for TCS, 2,4,6-TCP and 2,4-DCP, respectively, to 120hpf zebrafish. The highest TCSD (the mixture of TCS, 2,4,6-TCP and 2,4-DCP) toxicity was observed at a TCS:2,4,6-TCP:2,4-DCP concentration ratio of 1:2:4. LC50 and EC50 values of TCSD mixtures for 120-hpf zebrafish were 2.28 and 1.16mg/L, respectively. Two toxicity assessment methods (Toxic Unit and Mixture Toxicity Index) indicated that TCSD interactions produced partly additive toxicity. TCSD exposure decreased zebrafish hatching rate and led to a series of malformations. Following alkaline phosphatase staining, a large area of vascular ablation was observed with almost complete disappearance of vascular branches and a smaller coverage range. Prominent reddening of the yolk sac and visceral mass after oil red O staining implied that TCSD exposure severely affected fat metabolism. Following acridine orange staining, cell death occurred in eyes while high TCSD concentrations (0.84mg/L) induced cardiovascular circulation dysfunction. Alcian blue staining increased the α angle between Meckel’s cartilages and β angle between two ceratobranchial. Basihyal and palatoquadrate became shorter and developmental abnormality or defects occurred in the fifth ceratobranchial. Overall, these results provide a theoretical basis for systematically evaluating the combined toxicity of the prevalent chlorinated phenolic pollutants in real-world aquatic environments. |
doi_str_mv | 10.1016/j.etap.2017.11.006 |
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Triclosan (TCS), 2,4,6-trichlorophenol (2,4,6-TCP) and 2,4-dichlorophenol (2,4-DCP) are the most prevalent chlorinated phenolic pollutants in aquatic environments. Our results showed LC50 and EC50 values of 0.51, 1.11, 2.45mg/L, and 0.36, 0.74, 1.53mg/L for TCS, 2,4,6-TCP and 2,4-DCP, respectively, to 120hpf zebrafish. The highest TCSD (the mixture of TCS, 2,4,6-TCP and 2,4-DCP) toxicity was observed at a TCS:2,4,6-TCP:2,4-DCP concentration ratio of 1:2:4. LC50 and EC50 values of TCSD mixtures for 120-hpf zebrafish were 2.28 and 1.16mg/L, respectively. Two toxicity assessment methods (Toxic Unit and Mixture Toxicity Index) indicated that TCSD interactions produced partly additive toxicity. TCSD exposure decreased zebrafish hatching rate and led to a series of malformations. Following alkaline phosphatase staining, a large area of vascular ablation was observed with almost complete disappearance of vascular branches and a smaller coverage range. Prominent reddening of the yolk sac and visceral mass after oil red O staining implied that TCSD exposure severely affected fat metabolism. Following acridine orange staining, cell death occurred in eyes while high TCSD concentrations (0.84mg/L) induced cardiovascular circulation dysfunction. Alcian blue staining increased the α angle between Meckel’s cartilages and β angle between two ceratobranchial. Basihyal and palatoquadrate became shorter and developmental abnormality or defects occurred in the fifth ceratobranchial. Overall, these results provide a theoretical basis for systematically evaluating the combined toxicity of the prevalent chlorinated phenolic pollutants in real-world aquatic environments.</description><identifier>ISSN: 1382-6689</identifier><identifier>EISSN: 1872-7077</identifier><identifier>DOI: 10.1016/j.etap.2017.11.006</identifier><identifier>PMID: 29169085</identifier><language>eng</language><publisher>Netherlands: Elsevier B.V</publisher><subject>2,4,6-Trichlorophenol ; 2,4-Dichlorophenol ; 2,4-Dichlorophenol and 2,4,6-trichlorophenol ; Acridine orange ; Alkaline phosphatase ; Animals ; Animals, Genetically Modified ; Anthelmintics - toxicity ; Anti-Infective Agents, Local - toxicity ; Apoptosis ; Aquatic ecology ; Aquatic environment ; Cell death ; Chlorophenols - toxicity ; Danio rerio ; Drug Synergism ; Embryo, Nonmammalian - abnormalities ; Embryo, Nonmammalian - drug effects ; Exposure ; Fat metabolism ; Hatching ; Joint toxicity ; Metabolism ; Mixtures of triclosan ; Mutagens - toxicity ; Partly additive effect ; Phenolic compounds ; Phenols ; Pollutants ; Staining ; Staining and histopathological observation ; Toxicity ; Trichlorophenol ; Triclosan ; Triclosan - toxicity ; Water Pollutants, Chemical - toxicity ; Yolk ; Yolk sac ; Zebrafish ; Zebrafish - abnormalities ; Zebrafish - embryology ; Zebrafish - genetics</subject><ispartof>Environmental toxicology and pharmacology, 2018-01, Vol.57, p.9-18</ispartof><rights>2017 Elsevier B.V.</rights><rights>Copyright © 2017 Elsevier B.V. All rights reserved.</rights><rights>Copyright Elsevier Science Ltd. Jan 2018</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c384t-6a68ad9e7af827fb204625d814e811f78292435b8658d60b94d7cecf16400df53</citedby><cites>FETCH-LOGICAL-c384t-6a68ad9e7af827fb204625d814e811f78292435b8658d60b94d7cecf16400df53</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://dx.doi.org/10.1016/j.etap.2017.11.006$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,778,782,3539,27907,27908,45978</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/29169085$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Zhang, Yuhuan</creatorcontrib><creatorcontrib>Liu, Mi</creatorcontrib><creatorcontrib>Liu, Jinfeng</creatorcontrib><creatorcontrib>Wang, Xuedong</creatorcontrib><creatorcontrib>Wang, Caihong</creatorcontrib><creatorcontrib>Ai, Weiming</creatorcontrib><creatorcontrib>Chen, Shaobo</creatorcontrib><creatorcontrib>Wang, Huili</creatorcontrib><title>Combined toxicity of triclosan, 2,4-dichlorophenol and 2,4,6-trichlorophenol to zebrafish (Danio rerio)</title><title>Environmental toxicology and pharmacology</title><addtitle>Environ Toxicol Pharmacol</addtitle><description>•The highest TCSD toxicity is at a TCS:2,4,6-TCP:2,4-DCP concentration ratio of 1:2:4.•The interactions of TCS and its two derivatives produce partly synergistic toxicity.•TCSD produces dose-dependent effects on hatching, malformation and mortality.•ALP and ORO staining prove TCSD affected vascular branches and fat metabolism.•AO and AB staining proves TCSD affects apoptotic cells and cartilage development.
Triclosan (TCS), 2,4,6-trichlorophenol (2,4,6-TCP) and 2,4-dichlorophenol (2,4-DCP) are the most prevalent chlorinated phenolic pollutants in aquatic environments. Our results showed LC50 and EC50 values of 0.51, 1.11, 2.45mg/L, and 0.36, 0.74, 1.53mg/L for TCS, 2,4,6-TCP and 2,4-DCP, respectively, to 120hpf zebrafish. The highest TCSD (the mixture of TCS, 2,4,6-TCP and 2,4-DCP) toxicity was observed at a TCS:2,4,6-TCP:2,4-DCP concentration ratio of 1:2:4. LC50 and EC50 values of TCSD mixtures for 120-hpf zebrafish were 2.28 and 1.16mg/L, respectively. Two toxicity assessment methods (Toxic Unit and Mixture Toxicity Index) indicated that TCSD interactions produced partly additive toxicity. TCSD exposure decreased zebrafish hatching rate and led to a series of malformations. Following alkaline phosphatase staining, a large area of vascular ablation was observed with almost complete disappearance of vascular branches and a smaller coverage range. Prominent reddening of the yolk sac and visceral mass after oil red O staining implied that TCSD exposure severely affected fat metabolism. Following acridine orange staining, cell death occurred in eyes while high TCSD concentrations (0.84mg/L) induced cardiovascular circulation dysfunction. Alcian blue staining increased the α angle between Meckel’s cartilages and β angle between two ceratobranchial. Basihyal and palatoquadrate became shorter and developmental abnormality or defects occurred in the fifth ceratobranchial. Overall, these results provide a theoretical basis for systematically evaluating the combined toxicity of the prevalent chlorinated phenolic pollutants in real-world aquatic environments.</description><subject>2,4,6-Trichlorophenol</subject><subject>2,4-Dichlorophenol</subject><subject>2,4-Dichlorophenol and 2,4,6-trichlorophenol</subject><subject>Acridine orange</subject><subject>Alkaline phosphatase</subject><subject>Animals</subject><subject>Animals, Genetically Modified</subject><subject>Anthelmintics - toxicity</subject><subject>Anti-Infective Agents, Local - toxicity</subject><subject>Apoptosis</subject><subject>Aquatic ecology</subject><subject>Aquatic environment</subject><subject>Cell death</subject><subject>Chlorophenols - toxicity</subject><subject>Danio rerio</subject><subject>Drug Synergism</subject><subject>Embryo, Nonmammalian - abnormalities</subject><subject>Embryo, Nonmammalian - drug effects</subject><subject>Exposure</subject><subject>Fat metabolism</subject><subject>Hatching</subject><subject>Joint toxicity</subject><subject>Metabolism</subject><subject>Mixtures of triclosan</subject><subject>Mutagens - toxicity</subject><subject>Partly additive effect</subject><subject>Phenolic compounds</subject><subject>Phenols</subject><subject>Pollutants</subject><subject>Staining</subject><subject>Staining and histopathological observation</subject><subject>Toxicity</subject><subject>Trichlorophenol</subject><subject>Triclosan</subject><subject>Triclosan - toxicity</subject><subject>Water Pollutants, Chemical - toxicity</subject><subject>Yolk</subject><subject>Yolk sac</subject><subject>Zebrafish</subject><subject>Zebrafish - abnormalities</subject><subject>Zebrafish - embryology</subject><subject>Zebrafish - genetics</subject><issn>1382-6689</issn><issn>1872-7077</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2018</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp9kU2P0zAQhi0Eot3CH-CAInHZlZrgcRzbkbigLl9SJS5wthx7TF2lcbHTFeXXk6gFIQ6cZjTzzDujeQl5AbQCCuL1vsLRHCtGQVYAFaXiEVmCkqyUVMrHU14rVgqh2gW5yXlPKTR1rZ6SBWtBtFQ1S_JtEw9dGNAVY_wRbBjPRfTFmILtYzbDumBrXrpgd31M8bjDIfaFGdxcXoty5v7ujLH4iV0yPuRdcXtvhhCLhCnEu2fkiTd9xufXuCJf37_7svlYbj9_-LR5uy1trfhYCiOUcS1K4xWTvmOUC9Y4BRwVgJeKtYzXTadEo5ygXcudtGg9CE6p8029IrcX3WOK30-YR30I2WLfmwHjKWtoheKcS5jRV_-g-3hKw3SdntYyxhpBYaLYhbIp5pzQ62MKB5POGqiebdB7PdugZxs0gJ5smIZeXqVP3QHdn5Hff5-ANxcAp188BEw624CDRRcS2lG7GP6n_wsbEJcL</recordid><startdate>201801</startdate><enddate>201801</enddate><creator>Zhang, Yuhuan</creator><creator>Liu, Mi</creator><creator>Liu, Jinfeng</creator><creator>Wang, Xuedong</creator><creator>Wang, Caihong</creator><creator>Ai, Weiming</creator><creator>Chen, Shaobo</creator><creator>Wang, Huili</creator><general>Elsevier B.V</general><general>Elsevier Science Ltd</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>7QP</scope><scope>7ST</scope><scope>7TK</scope><scope>7U7</scope><scope>C1K</scope><scope>SOI</scope><scope>7X8</scope></search><sort><creationdate>201801</creationdate><title>Combined toxicity of triclosan, 2,4-dichlorophenol and 2,4,6-trichlorophenol to zebrafish (Danio rerio)</title><author>Zhang, Yuhuan ; Liu, Mi ; Liu, Jinfeng ; Wang, Xuedong ; Wang, Caihong ; Ai, Weiming ; Chen, Shaobo ; Wang, Huili</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c384t-6a68ad9e7af827fb204625d814e811f78292435b8658d60b94d7cecf16400df53</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2018</creationdate><topic>2,4,6-Trichlorophenol</topic><topic>2,4-Dichlorophenol</topic><topic>2,4-Dichlorophenol and 2,4,6-trichlorophenol</topic><topic>Acridine orange</topic><topic>Alkaline phosphatase</topic><topic>Animals</topic><topic>Animals, Genetically Modified</topic><topic>Anthelmintics - toxicity</topic><topic>Anti-Infective Agents, Local - toxicity</topic><topic>Apoptosis</topic><topic>Aquatic ecology</topic><topic>Aquatic environment</topic><topic>Cell death</topic><topic>Chlorophenols - toxicity</topic><topic>Danio rerio</topic><topic>Drug Synergism</topic><topic>Embryo, Nonmammalian - abnormalities</topic><topic>Embryo, Nonmammalian - drug effects</topic><topic>Exposure</topic><topic>Fat metabolism</topic><topic>Hatching</topic><topic>Joint toxicity</topic><topic>Metabolism</topic><topic>Mixtures of triclosan</topic><topic>Mutagens - toxicity</topic><topic>Partly additive effect</topic><topic>Phenolic compounds</topic><topic>Phenols</topic><topic>Pollutants</topic><topic>Staining</topic><topic>Staining and histopathological observation</topic><topic>Toxicity</topic><topic>Trichlorophenol</topic><topic>Triclosan</topic><topic>Triclosan - toxicity</topic><topic>Water Pollutants, Chemical - toxicity</topic><topic>Yolk</topic><topic>Yolk sac</topic><topic>Zebrafish</topic><topic>Zebrafish - abnormalities</topic><topic>Zebrafish - embryology</topic><topic>Zebrafish - genetics</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Zhang, Yuhuan</creatorcontrib><creatorcontrib>Liu, Mi</creatorcontrib><creatorcontrib>Liu, Jinfeng</creatorcontrib><creatorcontrib>Wang, Xuedong</creatorcontrib><creatorcontrib>Wang, Caihong</creatorcontrib><creatorcontrib>Ai, Weiming</creatorcontrib><creatorcontrib>Chen, Shaobo</creatorcontrib><creatorcontrib>Wang, Huili</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Calcium & Calcified Tissue Abstracts</collection><collection>Environment Abstracts</collection><collection>Neurosciences Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Environment Abstracts</collection><collection>MEDLINE - Academic</collection><jtitle>Environmental toxicology and pharmacology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Zhang, Yuhuan</au><au>Liu, Mi</au><au>Liu, Jinfeng</au><au>Wang, Xuedong</au><au>Wang, Caihong</au><au>Ai, Weiming</au><au>Chen, Shaobo</au><au>Wang, Huili</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Combined toxicity of triclosan, 2,4-dichlorophenol and 2,4,6-trichlorophenol to zebrafish (Danio rerio)</atitle><jtitle>Environmental toxicology and pharmacology</jtitle><addtitle>Environ Toxicol Pharmacol</addtitle><date>2018-01</date><risdate>2018</risdate><volume>57</volume><spage>9</spage><epage>18</epage><pages>9-18</pages><issn>1382-6689</issn><eissn>1872-7077</eissn><abstract>•The highest TCSD toxicity is at a TCS:2,4,6-TCP:2,4-DCP concentration ratio of 1:2:4.•The interactions of TCS and its two derivatives produce partly synergistic toxicity.•TCSD produces dose-dependent effects on hatching, malformation and mortality.•ALP and ORO staining prove TCSD affected vascular branches and fat metabolism.•AO and AB staining proves TCSD affects apoptotic cells and cartilage development.
Triclosan (TCS), 2,4,6-trichlorophenol (2,4,6-TCP) and 2,4-dichlorophenol (2,4-DCP) are the most prevalent chlorinated phenolic pollutants in aquatic environments. Our results showed LC50 and EC50 values of 0.51, 1.11, 2.45mg/L, and 0.36, 0.74, 1.53mg/L for TCS, 2,4,6-TCP and 2,4-DCP, respectively, to 120hpf zebrafish. The highest TCSD (the mixture of TCS, 2,4,6-TCP and 2,4-DCP) toxicity was observed at a TCS:2,4,6-TCP:2,4-DCP concentration ratio of 1:2:4. LC50 and EC50 values of TCSD mixtures for 120-hpf zebrafish were 2.28 and 1.16mg/L, respectively. Two toxicity assessment methods (Toxic Unit and Mixture Toxicity Index) indicated that TCSD interactions produced partly additive toxicity. TCSD exposure decreased zebrafish hatching rate and led to a series of malformations. Following alkaline phosphatase staining, a large area of vascular ablation was observed with almost complete disappearance of vascular branches and a smaller coverage range. Prominent reddening of the yolk sac and visceral mass after oil red O staining implied that TCSD exposure severely affected fat metabolism. Following acridine orange staining, cell death occurred in eyes while high TCSD concentrations (0.84mg/L) induced cardiovascular circulation dysfunction. Alcian blue staining increased the α angle between Meckel’s cartilages and β angle between two ceratobranchial. Basihyal and palatoquadrate became shorter and developmental abnormality or defects occurred in the fifth ceratobranchial. Overall, these results provide a theoretical basis for systematically evaluating the combined toxicity of the prevalent chlorinated phenolic pollutants in real-world aquatic environments.</abstract><cop>Netherlands</cop><pub>Elsevier B.V</pub><pmid>29169085</pmid><doi>10.1016/j.etap.2017.11.006</doi><tpages>10</tpages></addata></record> |
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subjects | 2,4,6-Trichlorophenol 2,4-Dichlorophenol 2,4-Dichlorophenol and 2,4,6-trichlorophenol Acridine orange Alkaline phosphatase Animals Animals, Genetically Modified Anthelmintics - toxicity Anti-Infective Agents, Local - toxicity Apoptosis Aquatic ecology Aquatic environment Cell death Chlorophenols - toxicity Danio rerio Drug Synergism Embryo, Nonmammalian - abnormalities Embryo, Nonmammalian - drug effects Exposure Fat metabolism Hatching Joint toxicity Metabolism Mixtures of triclosan Mutagens - toxicity Partly additive effect Phenolic compounds Phenols Pollutants Staining Staining and histopathological observation Toxicity Trichlorophenol Triclosan Triclosan - toxicity Water Pollutants, Chemical - toxicity Yolk Yolk sac Zebrafish Zebrafish - abnormalities Zebrafish - embryology Zebrafish - genetics |
title | Combined toxicity of triclosan, 2,4-dichlorophenol and 2,4,6-trichlorophenol to zebrafish (Danio rerio) |
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