Transcriptional and cellular effects of benzotriazole UV stabilizers UV‐234 and UV‐328 in the freshwater invertebrates Chlamydomonas reinhardtii and Daphnia magna
Benzotriazole ultra violet stabilizers (BZT‐UVs) are compounds used in many applications and products to prevent photochemical degradation. Despite their widespread presence in aquatic ecosystems and persistence in the environment, there are very limited data on their effects and toxicity, and their...
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description | Benzotriazole ultra violet stabilizers (BZT‐UVs) are compounds used in many applications and products to prevent photochemical degradation. Despite their widespread presence in aquatic ecosystems and persistence in the environment, there are very limited data on their effects and toxicity, and their modes of action remain largely unknown. The objectives of the present study were to evaluate the chronic effects of 2 BZT‐UVs, 2‐(2H‐benzotriazol‐2‐yl)‐4,6‐bis(1‐methyl‐1‐phenylethyl)phenol (UV‐234) and 2‐(2H‐benzotriazol‐2‐yl)‐4,6‐di‐tert‐pentylphenol (UV‐328), on the freshwater green algae Chlamydomonas reinhardtii and the freshwater crustacean Daphnia magna. Organisms were exposed to 0.01 and 10 μg/L of UV‐234, UV‐328, as well as a mixture of the 2 compounds. Life‐history endpoints (viability, reproduction, and growth) and oxidative stress–related biomarkers (gene transcription, reactive oxygen species [ROS] production, and lipid peroxidation) were measured. Daphnia magna growth, reproduction, and gene transcription were not impacted by 21‐d individual or mixed exposure. After 96‐h of exposure, no differences were observed on the cellular viability of C. reinhardtii for either of the 2 BZT‐UVs. In the algae, results showed increased ROS production in response to UV‐328 and lipid peroxidation following exposure to UV‐234. Synergistic effects of the 2 BZT‐UVs were evident at the transcriptional level with 2 to 6 times up‐regulation of glutathione peroxidase (gpx) in response to the mixture for all treatment conditions. The transcription of superoxide dismutase (sod), catalase (cat), and ascorbic peroxidase (apx) was also regulated by UV‐234 and UV‐328 in the green algae, most likely as a result of ROS production and lipid peroxidation. Results from the present study suggest potential impacts of UV‐234 and UV‐328 exposure on the antioxidant defense system in C. reinhardtii. Environ Toxicol Chem 2017;36:3333–3342. © 2017 Crown in the Right of Canada. Published by Wiley Periodicals Inc., on behalf of SETAC. |
doi_str_mv | 10.1002/etc.3908 |
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De ; Houde, Magali</creator><creatorcontrib>Giraudo, Maeva ; Cottin, Guillaume ; Esperanza, Marta ; Gagnon, Pierre ; Silva, Amila O. De ; Houde, Magali</creatorcontrib><description>Benzotriazole ultra violet stabilizers (BZT‐UVs) are compounds used in many applications and products to prevent photochemical degradation. Despite their widespread presence in aquatic ecosystems and persistence in the environment, there are very limited data on their effects and toxicity, and their modes of action remain largely unknown. The objectives of the present study were to evaluate the chronic effects of 2 BZT‐UVs, 2‐(2H‐benzotriazol‐2‐yl)‐4,6‐bis(1‐methyl‐1‐phenylethyl)phenol (UV‐234) and 2‐(2H‐benzotriazol‐2‐yl)‐4,6‐di‐tert‐pentylphenol (UV‐328), on the freshwater green algae Chlamydomonas reinhardtii and the freshwater crustacean Daphnia magna. Organisms were exposed to 0.01 and 10 μg/L of UV‐234, UV‐328, as well as a mixture of the 2 compounds. Life‐history endpoints (viability, reproduction, and growth) and oxidative stress–related biomarkers (gene transcription, reactive oxygen species [ROS] production, and lipid peroxidation) were measured. Daphnia magna growth, reproduction, and gene transcription were not impacted by 21‐d individual or mixed exposure. After 96‐h of exposure, no differences were observed on the cellular viability of C. reinhardtii for either of the 2 BZT‐UVs. In the algae, results showed increased ROS production in response to UV‐328 and lipid peroxidation following exposure to UV‐234. Synergistic effects of the 2 BZT‐UVs were evident at the transcriptional level with 2 to 6 times up‐regulation of glutathione peroxidase (gpx) in response to the mixture for all treatment conditions. The transcription of superoxide dismutase (sod), catalase (cat), and ascorbic peroxidase (apx) was also regulated by UV‐234 and UV‐328 in the green algae, most likely as a result of ROS production and lipid peroxidation. Results from the present study suggest potential impacts of UV‐234 and UV‐328 exposure on the antioxidant defense system in C. reinhardtii. Environ Toxicol Chem 2017;36:3333–3342. © 2017 Crown in the Right of Canada. Published by Wiley Periodicals Inc., on behalf of SETAC.</description><identifier>ISSN: 0730-7268</identifier><identifier>EISSN: 1552-8618</identifier><identifier>DOI: 10.1002/etc.3908</identifier><identifier>PMID: 28708270</identifier><language>eng</language><publisher>United States: Blackwell Publishing Ltd</publisher><subject>Algae ; Animals ; Antioxidants ; Antioxidants - metabolism ; Aquatic ecosystems ; Aquatic plants ; Aquatic toxicology ; Ascorbate Peroxidases - metabolism ; Benzotriazole ; Benzotriazole UV stabilizers ; Biodegradation ; Biomarkers ; Catalase ; Catalase - metabolism ; Chlamydomonas reinhardtii ; Chlamydomonas reinhardtii - drug effects ; Chlamydomonas reinhardtii - genetics ; Chlorophyta ; Chronic effects ; Contaminant of emerging concern ; Crustaceans ; Daphnia - drug effects ; Daphnia - genetics ; Daphnia - metabolism ; Daphnia magna ; Exposure ; Fresh Water ; Freshwater crustaceans ; Freshwater invertebrates ; Freshwater organisms ; Glutathione ; Glutathione peroxidase ; Glutathione Peroxidase - metabolism ; Invertebrates ; Life Cycle Stages ; Life history ; Lipid peroxidation ; Lipid Peroxidation - drug effects ; Lipids ; Oxidative stress ; Oxidative Stress - drug effects ; Peroxidase ; Peroxidation ; Phenols ; Photochemicals ; Reactive oxygen species ; Reactive Oxygen Species - metabolism ; Reproduction (biology) ; Reproduction - drug effects ; Shellfish ; Superoxide dismutase ; Superoxide Dismutase - metabolism ; Synergistic effect ; Toxicity ; Transcription ; Transcription, Genetic ; Transcriptomics ; Triazoles - toxicity ; Ultraviolet radiation ; Up-Regulation ; UV stabilizers</subject><ispartof>Environmental toxicology and chemistry, 2017-12, Vol.36 (12), p.3333-3342</ispartof><rights>2017 Crown in the Right of Canada. 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De</creatorcontrib><creatorcontrib>Houde, Magali</creatorcontrib><title>Transcriptional and cellular effects of benzotriazole UV stabilizers UV‐234 and UV‐328 in the freshwater invertebrates Chlamydomonas reinhardtii and Daphnia magna</title><title>Environmental toxicology and chemistry</title><addtitle>Environ Toxicol Chem</addtitle><description>Benzotriazole ultra violet stabilizers (BZT‐UVs) are compounds used in many applications and products to prevent photochemical degradation. Despite their widespread presence in aquatic ecosystems and persistence in the environment, there are very limited data on their effects and toxicity, and their modes of action remain largely unknown. The objectives of the present study were to evaluate the chronic effects of 2 BZT‐UVs, 2‐(2H‐benzotriazol‐2‐yl)‐4,6‐bis(1‐methyl‐1‐phenylethyl)phenol (UV‐234) and 2‐(2H‐benzotriazol‐2‐yl)‐4,6‐di‐tert‐pentylphenol (UV‐328), on the freshwater green algae Chlamydomonas reinhardtii and the freshwater crustacean Daphnia magna. Organisms were exposed to 0.01 and 10 μg/L of UV‐234, UV‐328, as well as a mixture of the 2 compounds. Life‐history endpoints (viability, reproduction, and growth) and oxidative stress–related biomarkers (gene transcription, reactive oxygen species [ROS] production, and lipid peroxidation) were measured. Daphnia magna growth, reproduction, and gene transcription were not impacted by 21‐d individual or mixed exposure. After 96‐h of exposure, no differences were observed on the cellular viability of C. reinhardtii for either of the 2 BZT‐UVs. In the algae, results showed increased ROS production in response to UV‐328 and lipid peroxidation following exposure to UV‐234. Synergistic effects of the 2 BZT‐UVs were evident at the transcriptional level with 2 to 6 times up‐regulation of glutathione peroxidase (gpx) in response to the mixture for all treatment conditions. The transcription of superoxide dismutase (sod), catalase (cat), and ascorbic peroxidase (apx) was also regulated by UV‐234 and UV‐328 in the green algae, most likely as a result of ROS production and lipid peroxidation. Results from the present study suggest potential impacts of UV‐234 and UV‐328 exposure on the antioxidant defense system in C. reinhardtii. Environ Toxicol Chem 2017;36:3333–3342. © 2017 Crown in the Right of Canada. Published by Wiley Periodicals Inc., on behalf of SETAC.</description><subject>Algae</subject><subject>Animals</subject><subject>Antioxidants</subject><subject>Antioxidants - metabolism</subject><subject>Aquatic ecosystems</subject><subject>Aquatic plants</subject><subject>Aquatic toxicology</subject><subject>Ascorbate Peroxidases - metabolism</subject><subject>Benzotriazole</subject><subject>Benzotriazole UV stabilizers</subject><subject>Biodegradation</subject><subject>Biomarkers</subject><subject>Catalase</subject><subject>Catalase - metabolism</subject><subject>Chlamydomonas reinhardtii</subject><subject>Chlamydomonas reinhardtii - drug effects</subject><subject>Chlamydomonas reinhardtii - genetics</subject><subject>Chlorophyta</subject><subject>Chronic effects</subject><subject>Contaminant of emerging concern</subject><subject>Crustaceans</subject><subject>Daphnia - drug effects</subject><subject>Daphnia - genetics</subject><subject>Daphnia - metabolism</subject><subject>Daphnia magna</subject><subject>Exposure</subject><subject>Fresh Water</subject><subject>Freshwater crustaceans</subject><subject>Freshwater invertebrates</subject><subject>Freshwater organisms</subject><subject>Glutathione</subject><subject>Glutathione peroxidase</subject><subject>Glutathione Peroxidase - metabolism</subject><subject>Invertebrates</subject><subject>Life Cycle Stages</subject><subject>Life history</subject><subject>Lipid peroxidation</subject><subject>Lipid Peroxidation - drug effects</subject><subject>Lipids</subject><subject>Oxidative stress</subject><subject>Oxidative Stress - drug effects</subject><subject>Peroxidase</subject><subject>Peroxidation</subject><subject>Phenols</subject><subject>Photochemicals</subject><subject>Reactive oxygen species</subject><subject>Reactive Oxygen Species - metabolism</subject><subject>Reproduction (biology)</subject><subject>Reproduction - drug effects</subject><subject>Shellfish</subject><subject>Superoxide dismutase</subject><subject>Superoxide Dismutase - metabolism</subject><subject>Synergistic effect</subject><subject>Toxicity</subject><subject>Transcription</subject><subject>Transcription, Genetic</subject><subject>Transcriptomics</subject><subject>Triazoles - toxicity</subject><subject>Ultraviolet radiation</subject><subject>Up-Regulation</subject><subject>UV stabilizers</subject><issn>0730-7268</issn><issn>1552-8618</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2017</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp1kc1O3DAURq0KVKa0Up8AWWLTTcB_sZ0lGlpaCakb6DZy4uvGyEkG2wOaWfUR-hR9MJ6kZga668r6rOPjq_sh9JGSM0oIO4fcn_GG6DdoQeuaVVpSfYAWRHFSKSb1EXqX0h0hVDZN8xYdMa2IZoos0J-baKbUR7_Kfp5MwGayuIcQ1sFEDM5BnxOeHe5g2s45erOdA-DbHzhl0_ngtxBTiU-_fjMudq93gTON_YTzANhFSMOjyRDLzQPEDF0sKeHlEMy4sfNYPk44gp8GE232fqe5NKth8gaP5udk3qNDZ0KCDy_nMbr98vlm-bW6_n71bXlxXfVcS12BUMIxAZ1Ttu6cBq6dsUJQJV1TRhIaLHPgjKhp55i2gpdNSApSWuJUzY_R6d67ivP9GlJu7-Z1LHtJLW2krjVXVBTq057q45xSBNeuoh9N3LSUtM-FtKWQ9rmQgp68CNfdCPYf-NpAAao98OgDbP4raguzE_4FY_CY1A</recordid><startdate>201712</startdate><enddate>201712</enddate><creator>Giraudo, Maeva</creator><creator>Cottin, Guillaume</creator><creator>Esperanza, Marta</creator><creator>Gagnon, Pierre</creator><creator>Silva, Amila O. De</creator><creator>Houde, Magali</creator><general>Blackwell Publishing 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>7QO</scope><scope>7SN</scope><scope>7SS</scope><scope>7ST</scope><scope>7T7</scope><scope>7TK</scope><scope>7U7</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>K9.</scope><scope>P64</scope><scope>RC3</scope><scope>SOI</scope><orcidid>https://orcid.org/0000-0003-4296-146X</orcidid></search><sort><creationdate>201712</creationdate><title>Transcriptional and cellular effects of benzotriazole UV stabilizers UV‐234 and UV‐328 in the freshwater invertebrates Chlamydomonas reinhardtii and Daphnia magna</title><author>Giraudo, Maeva ; Cottin, Guillaume ; Esperanza, Marta ; Gagnon, Pierre ; Silva, Amila O. De ; Houde, Magali</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c3868-e474f24ebf7d5bf8e38fad44176f932848ed2fefa451bf28d4387061e66d0f753</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2017</creationdate><topic>Algae</topic><topic>Animals</topic><topic>Antioxidants</topic><topic>Antioxidants - metabolism</topic><topic>Aquatic ecosystems</topic><topic>Aquatic plants</topic><topic>Aquatic toxicology</topic><topic>Ascorbate Peroxidases - metabolism</topic><topic>Benzotriazole</topic><topic>Benzotriazole UV stabilizers</topic><topic>Biodegradation</topic><topic>Biomarkers</topic><topic>Catalase</topic><topic>Catalase - metabolism</topic><topic>Chlamydomonas reinhardtii</topic><topic>Chlamydomonas reinhardtii - drug effects</topic><topic>Chlamydomonas reinhardtii - genetics</topic><topic>Chlorophyta</topic><topic>Chronic effects</topic><topic>Contaminant of emerging concern</topic><topic>Crustaceans</topic><topic>Daphnia - drug effects</topic><topic>Daphnia - genetics</topic><topic>Daphnia - metabolism</topic><topic>Daphnia magna</topic><topic>Exposure</topic><topic>Fresh Water</topic><topic>Freshwater crustaceans</topic><topic>Freshwater invertebrates</topic><topic>Freshwater organisms</topic><topic>Glutathione</topic><topic>Glutathione peroxidase</topic><topic>Glutathione Peroxidase - metabolism</topic><topic>Invertebrates</topic><topic>Life Cycle Stages</topic><topic>Life history</topic><topic>Lipid peroxidation</topic><topic>Lipid Peroxidation - drug effects</topic><topic>Lipids</topic><topic>Oxidative stress</topic><topic>Oxidative Stress - drug effects</topic><topic>Peroxidase</topic><topic>Peroxidation</topic><topic>Phenols</topic><topic>Photochemicals</topic><topic>Reactive oxygen species</topic><topic>Reactive Oxygen Species - metabolism</topic><topic>Reproduction (biology)</topic><topic>Reproduction - drug effects</topic><topic>Shellfish</topic><topic>Superoxide dismutase</topic><topic>Superoxide Dismutase - metabolism</topic><topic>Synergistic effect</topic><topic>Toxicity</topic><topic>Transcription</topic><topic>Transcription, Genetic</topic><topic>Transcriptomics</topic><topic>Triazoles - toxicity</topic><topic>Ultraviolet radiation</topic><topic>Up-Regulation</topic><topic>UV stabilizers</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Giraudo, Maeva</creatorcontrib><creatorcontrib>Cottin, Guillaume</creatorcontrib><creatorcontrib>Esperanza, Marta</creatorcontrib><creatorcontrib>Gagnon, Pierre</creatorcontrib><creatorcontrib>Silva, Amila O. 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De</au><au>Houde, Magali</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Transcriptional and cellular effects of benzotriazole UV stabilizers UV‐234 and UV‐328 in the freshwater invertebrates Chlamydomonas reinhardtii and Daphnia magna</atitle><jtitle>Environmental toxicology and chemistry</jtitle><addtitle>Environ Toxicol Chem</addtitle><date>2017-12</date><risdate>2017</risdate><volume>36</volume><issue>12</issue><spage>3333</spage><epage>3342</epage><pages>3333-3342</pages><issn>0730-7268</issn><eissn>1552-8618</eissn><abstract>Benzotriazole ultra violet stabilizers (BZT‐UVs) are compounds used in many applications and products to prevent photochemical degradation. Despite their widespread presence in aquatic ecosystems and persistence in the environment, there are very limited data on their effects and toxicity, and their modes of action remain largely unknown. The objectives of the present study were to evaluate the chronic effects of 2 BZT‐UVs, 2‐(2H‐benzotriazol‐2‐yl)‐4,6‐bis(1‐methyl‐1‐phenylethyl)phenol (UV‐234) and 2‐(2H‐benzotriazol‐2‐yl)‐4,6‐di‐tert‐pentylphenol (UV‐328), on the freshwater green algae Chlamydomonas reinhardtii and the freshwater crustacean Daphnia magna. Organisms were exposed to 0.01 and 10 μg/L of UV‐234, UV‐328, as well as a mixture of the 2 compounds. Life‐history endpoints (viability, reproduction, and growth) and oxidative stress–related biomarkers (gene transcription, reactive oxygen species [ROS] production, and lipid peroxidation) were measured. Daphnia magna growth, reproduction, and gene transcription were not impacted by 21‐d individual or mixed exposure. After 96‐h of exposure, no differences were observed on the cellular viability of C. reinhardtii for either of the 2 BZT‐UVs. In the algae, results showed increased ROS production in response to UV‐328 and lipid peroxidation following exposure to UV‐234. Synergistic effects of the 2 BZT‐UVs were evident at the transcriptional level with 2 to 6 times up‐regulation of glutathione peroxidase (gpx) in response to the mixture for all treatment conditions. The transcription of superoxide dismutase (sod), catalase (cat), and ascorbic peroxidase (apx) was also regulated by UV‐234 and UV‐328 in the green algae, most likely as a result of ROS production and lipid peroxidation. Results from the present study suggest potential impacts of UV‐234 and UV‐328 exposure on the antioxidant defense system in C. reinhardtii. Environ Toxicol Chem 2017;36:3333–3342. © 2017 Crown in the Right of Canada. Published by Wiley Periodicals Inc., on behalf of SETAC.</abstract><cop>United States</cop><pub>Blackwell Publishing Ltd</pub><pmid>28708270</pmid><doi>10.1002/etc.3908</doi><tpages>10</tpages><orcidid>https://orcid.org/0000-0003-4296-146X</orcidid></addata></record> |
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subjects | Algae Animals Antioxidants Antioxidants - metabolism Aquatic ecosystems Aquatic plants Aquatic toxicology Ascorbate Peroxidases - metabolism Benzotriazole Benzotriazole UV stabilizers Biodegradation Biomarkers Catalase Catalase - metabolism Chlamydomonas reinhardtii Chlamydomonas reinhardtii - drug effects Chlamydomonas reinhardtii - genetics Chlorophyta Chronic effects Contaminant of emerging concern Crustaceans Daphnia - drug effects Daphnia - genetics Daphnia - metabolism Daphnia magna Exposure Fresh Water Freshwater crustaceans Freshwater invertebrates Freshwater organisms Glutathione Glutathione peroxidase Glutathione Peroxidase - metabolism Invertebrates Life Cycle Stages Life history Lipid peroxidation Lipid Peroxidation - drug effects Lipids Oxidative stress Oxidative Stress - drug effects Peroxidase Peroxidation Phenols Photochemicals Reactive oxygen species Reactive Oxygen Species - metabolism Reproduction (biology) Reproduction - drug effects Shellfish Superoxide dismutase Superoxide Dismutase - metabolism Synergistic effect Toxicity Transcription Transcription, Genetic Transcriptomics Triazoles - toxicity Ultraviolet radiation Up-Regulation UV stabilizers |
title | Transcriptional and cellular effects of benzotriazole UV stabilizers UV‐234 and UV‐328 in the freshwater invertebrates Chlamydomonas reinhardtii and Daphnia magna |
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