Responses of Aquatic Nontarget Organisms in Experiments Simulating a Scenario of Contamination by Imidacloprid in a Freshwater Environment
Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L −1 . In the present study, we evaluated the effects of the highest IMI concentration detected in surface water (320.0 µg L −1 ) on the survival of...
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| Published in | Archives of environmental contamination and toxicology Vol. 80; no. 2; pp. 437 - 449 |
|---|---|
| Main Authors | , , , , , , |
| Format | Journal Article |
| Language | English |
| Published |
New York
Springer US
01.02.2021
Springer Nature B.V |
| Subjects | |
| Online Access | Get full text |
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| Abstract | Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L
−1
. In the present study, we evaluated the effects of the highest IMI concentration detected in surface water (320.0 µg L
−1
) on the survival of
Chironomus sancticaroli
,
Daphnia similis,
and
Danio rerio
in three different scenarios of water contamination. The enzymatic activities of glutathione S-transferase (GST), catalase (CAT), and ascorbate peroxidase (APX) in
D. rerio
also were determined. For this evaluation, we have simulated a lotic environment using an indoor system of artificial channels developed for the present study. In this system, three scenarios of contamination by IMI (320.0 µg L
−1
) were reproduced: one using reconstituted water (RW) and the other two using water samples collected in unpolluted (UW) and polluted (DW) areas of a river. The results indicated that the tested concentration was not able to cause mortality in
D. similis
and
D. rerio
in any proposed treatment (RW, UW, and DW). However,
C. sancticaroli
showed 100% of mortality in the presence of IMI in the three proposed treatments, demonstrating its potential to impact the community of aquatic nontarget insects negatively. Low IMI concentrations did not offer risks to
D. rerio
survival. However, we observed alterations in GST, CAT, and APX activities in treatments that used IMI and water with no evidence of pollution (i.e., RW and UW). These last results demonstrated that fish are more susceptible to the effects of IMI in unpolluted environments. |
|---|---|
| AbstractList | Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L-1. In the present study, we evaluated the effects of the highest IMI concentration detected in surface water (320.0 µg L-1) on the survival of Chironomus sancticaroli, Daphnia similis, and Danio rerio in three different scenarios of water contamination. The enzymatic activities of glutathione S-transferase (GST), catalase (CAT), and ascorbate peroxidase (APX) in D. rerio also were determined. For this evaluation, we have simulated a lotic environment using an indoor system of artificial channels developed for the present study. In this system, three scenarios of contamination by IMI (320.0 µg L-1) were reproduced: one using reconstituted water (RW) and the other two using water samples collected in unpolluted (UW) and polluted (DW) areas of a river. The results indicated that the tested concentration was not able to cause mortality in D. similis and D. rerio in any proposed treatment (RW, UW, and DW). However, C. sancticaroli showed 100% of mortality in the presence of IMI in the three proposed treatments, demonstrating its potential to impact the community of aquatic nontarget insects negatively. Low IMI concentrations did not offer risks to D. rerio survival. However, we observed alterations in GST, CAT, and APX activities in treatments that used IMI and water with no evidence of pollution (i.e., RW and UW). These last results demonstrated that fish are more susceptible to the effects of IMI in unpolluted environments.Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L-1. In the present study, we evaluated the effects of the highest IMI concentration detected in surface water (320.0 µg L-1) on the survival of Chironomus sancticaroli, Daphnia similis, and Danio rerio in three different scenarios of water contamination. The enzymatic activities of glutathione S-transferase (GST), catalase (CAT), and ascorbate peroxidase (APX) in D. rerio also were determined. For this evaluation, we have simulated a lotic environment using an indoor system of artificial channels developed for the present study. In this system, three scenarios of contamination by IMI (320.0 µg L-1) were reproduced: one using reconstituted water (RW) and the other two using water samples collected in unpolluted (UW) and polluted (DW) areas of a river. The results indicated that the tested concentration was not able to cause mortality in D. similis and D. rerio in any proposed treatment (RW, UW, and DW). However, C. sancticaroli showed 100% of mortality in the presence of IMI in the three proposed treatments, demonstrating its potential to impact the community of aquatic nontarget insects negatively. Low IMI concentrations did not offer risks to D. rerio survival. However, we observed alterations in GST, CAT, and APX activities in treatments that used IMI and water with no evidence of pollution (i.e., RW and UW). These last results demonstrated that fish are more susceptible to the effects of IMI in unpolluted environments. Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L−1. In the present study, we evaluated the effects of the highest IMI concentration detected in surface water (320.0 µg L−1) on the survival of Chironomus sancticaroli, Daphnia similis, and Danio rerio in three different scenarios of water contamination. The enzymatic activities of glutathione S-transferase (GST), catalase (CAT), and ascorbate peroxidase (APX) in D. rerio also were determined. For this evaluation, we have simulated a lotic environment using an indoor system of artificial channels developed for the present study. In this system, three scenarios of contamination by IMI (320.0 µg L−1) were reproduced: one using reconstituted water (RW) and the other two using water samples collected in unpolluted (UW) and polluted (DW) areas of a river. The results indicated that the tested concentration was not able to cause mortality in D. similis and D. rerio in any proposed treatment (RW, UW, and DW). However, C. sancticaroli showed 100% of mortality in the presence of IMI in the three proposed treatments, demonstrating its potential to impact the community of aquatic nontarget insects negatively. Low IMI concentrations did not offer risks to D. rerio survival. However, we observed alterations in GST, CAT, and APX activities in treatments that used IMI and water with no evidence of pollution (i.e., RW and UW). These last results demonstrated that fish are more susceptible to the effects of IMI in unpolluted environments. Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L⁻¹. In the present study, we evaluated the effects of the highest IMI concentration detected in surface water (320.0 µg L⁻¹) on the survival of Chironomus sancticaroli, Daphnia similis, and Danio rerio in three different scenarios of water contamination. The enzymatic activities of glutathione S-transferase (GST), catalase (CAT), and ascorbate peroxidase (APX) in D. rerio also were determined. For this evaluation, we have simulated a lotic environment using an indoor system of artificial channels developed for the present study. In this system, three scenarios of contamination by IMI (320.0 µg L⁻¹) were reproduced: one using reconstituted water (RW) and the other two using water samples collected in unpolluted (UW) and polluted (DW) areas of a river. The results indicated that the tested concentration was not able to cause mortality in D. similis and D. rerio in any proposed treatment (RW, UW, and DW). However, C. sancticaroli showed 100% of mortality in the presence of IMI in the three proposed treatments, demonstrating its potential to impact the community of aquatic nontarget insects negatively. Low IMI concentrations did not offer risks to D. rerio survival. However, we observed alterations in GST, CAT, and APX activities in treatments that used IMI and water with no evidence of pollution (i.e., RW and UW). These last results demonstrated that fish are more susceptible to the effects of IMI in unpolluted environments. Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L . In the present study, we evaluated the effects of the highest IMI concentration detected in surface water (320.0 µg L ) on the survival of Chironomus sancticaroli, Daphnia similis, and Danio rerio in three different scenarios of water contamination. The enzymatic activities of glutathione S-transferase (GST), catalase (CAT), and ascorbate peroxidase (APX) in D. rerio also were determined. For this evaluation, we have simulated a lotic environment using an indoor system of artificial channels developed for the present study. In this system, three scenarios of contamination by IMI (320.0 µg L ) were reproduced: one using reconstituted water (RW) and the other two using water samples collected in unpolluted (UW) and polluted (DW) areas of a river. The results indicated that the tested concentration was not able to cause mortality in D. similis and D. rerio in any proposed treatment (RW, UW, and DW). However, C. sancticaroli showed 100% of mortality in the presence of IMI in the three proposed treatments, demonstrating its potential to impact the community of aquatic nontarget insects negatively. Low IMI concentrations did not offer risks to D. rerio survival. However, we observed alterations in GST, CAT, and APX activities in treatments that used IMI and water with no evidence of pollution (i.e., RW and UW). These last results demonstrated that fish are more susceptible to the effects of IMI in unpolluted environments. Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L −1 . In the present study, we evaluated the effects of the highest IMI concentration detected in surface water (320.0 µg L −1 ) on the survival of Chironomus sancticaroli , Daphnia similis, and Danio rerio in three different scenarios of water contamination. The enzymatic activities of glutathione S-transferase (GST), catalase (CAT), and ascorbate peroxidase (APX) in D. rerio also were determined. For this evaluation, we have simulated a lotic environment using an indoor system of artificial channels developed for the present study. In this system, three scenarios of contamination by IMI (320.0 µg L −1 ) were reproduced: one using reconstituted water (RW) and the other two using water samples collected in unpolluted (UW) and polluted (DW) areas of a river. The results indicated that the tested concentration was not able to cause mortality in D. similis and D. rerio in any proposed treatment (RW, UW, and DW). However, C. sancticaroli showed 100% of mortality in the presence of IMI in the three proposed treatments, demonstrating its potential to impact the community of aquatic nontarget insects negatively. Low IMI concentrations did not offer risks to D. rerio survival. However, we observed alterations in GST, CAT, and APX activities in treatments that used IMI and water with no evidence of pollution (i.e., RW and UW). These last results demonstrated that fish are more susceptible to the effects of IMI in unpolluted environments. |
| Author | da Silva, Flávio Teixeira Queiroz, Lucas Gonçalves Pinto, Ernani de Almeida, Éryka Costa de Paiva, Teresa Cristina Brazil do Prado, Caio César Achiles Dörr, Felipe Augusto |
| Author_xml | – sequence: 1 givenname: Lucas Gonçalves orcidid: 0000-0003-3305-1042 surname: Queiroz fullname: Queiroz, Lucas Gonçalves email: lucasgoncalvesqueiroz@gmail.com organization: Department of Biotechnology, School of Engineering of Lorena, University of São Paulo – sequence: 2 givenname: Caio César Achiles surname: do Prado fullname: do Prado, Caio César Achiles organization: Department of Biotechnology, School of Engineering of Lorena, University of São Paulo – sequence: 3 givenname: Éryka Costa surname: de Almeida fullname: de Almeida, Éryka Costa organization: Department of Clinical and Toxicological Analyses, School of Pharmaceutical Sciences, University of São Paulo – sequence: 4 givenname: Felipe Augusto surname: Dörr fullname: Dörr, Felipe Augusto organization: Department of Clinical and Toxicological Analyses, School of Pharmaceutical Sciences, University of São Paulo – sequence: 5 givenname: Ernani surname: Pinto fullname: Pinto, Ernani organization: Department of Clinical and Toxicological Analyses, School of Pharmaceutical Sciences, University of São Paulo – sequence: 6 givenname: Flávio Teixeira surname: da Silva fullname: da Silva, Flávio Teixeira organization: Department of Biotechnology, School of Engineering of Lorena, University of São Paulo – sequence: 7 givenname: Teresa Cristina Brazil surname: de Paiva fullname: de Paiva, Teresa Cristina Brazil organization: Department of Basic and Environmental Sciences, School of Engineering of Lorena, University of São Paulo |
| BackLink | https://www.ncbi.nlm.nih.gov/pubmed/33275184$$D View this record in MEDLINE/PubMed |
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| PublicationDate | 20210200 2021-02-00 2021-Feb 20210201 |
| PublicationDateYYYYMMDD | 2021-02-01 |
| PublicationDate_xml | – month: 2 year: 2021 text: 20210200 |
| PublicationDecade | 2020 |
| PublicationPlace | New York |
| PublicationPlace_xml | – name: New York – name: United States |
| PublicationTitle | Archives of environmental contamination and toxicology |
| PublicationTitleAbbrev | Arch Environ Contam Toxicol |
| PublicationTitleAlternate | Arch Environ Contam Toxicol |
| PublicationYear | 2021 |
| Publisher | Springer US Springer Nature B.V |
| Publisher_xml | – name: Springer US – name: Springer Nature B.V |
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| Snippet | Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L
−1
.... Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L . In... Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L−1. In... Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L-1. In... Several studies have indicated the presence of the neonicotinoid insecticide imidacloprid (IMI) in aquatic ecosystems in concentrations up to 320.0 µg L⁻¹. In... |
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| SubjectTerms | Animals Aquatic ecosystems Aquatic insects Aquatic Organisms Archives & records ascorbate peroxidase Ascorbic acid Catalase Chironomidae Chironomus Contamination Crustaceans Danio rerio Daphnia - drug effects Daphnia similis Earth and Environmental Science Ecosystem Ecotoxicology Environment Environmental Chemistry Environmental Health Enzymatic activity Enzymes fish Fresh Water freshwater Freshwater environments Glutathione Glutathione Transferase Imidacloprid Indoor environments Insecticides Insecticides - analysis Insects L-Ascorbate peroxidase Lotic environment lotic systems Monitoring/Environmental Analysis Mortality Neonicotinoids - analysis Neonicotinoids - toxicity Nitro Compounds - analysis Nitro Compounds - toxicity Nontarget organisms Peroxidase Pesticides Pollution rivers Soil Science & Conservation Surface water Survival Toxicology Water analysis Water Pollutants, Chemical - analysis Water Pollutants, Chemical - toxicity Water pollution Water sampling Zebrafish |
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| Title | Responses of Aquatic Nontarget Organisms in Experiments Simulating a Scenario of Contamination by Imidacloprid in a Freshwater Environment |
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