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Effects of three pesticides on superoxide dismutase and glutathione-S-transferase activities and reproduction of Daphnia magna

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Treść / Zawartość
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Języki publikacji
EN
Abstrakty
EN
Applying pesticides to crops is one of the causes of water pollution by surface runoff, and chlorpyrifos, trifluralin and chlorothalonil are used respectively as insecticide, herbicide and fungicide for crop plants widely. To explore effects of three pesticides on aquatic organisms, superoxide dismutase (SOD) and glutathione S-transferase (GST) activities were determined after 24 h and 48 h exposure of D. magna with ages of 6–24 h to several low concentrations of chlorpyrifos (0.36, 0.72, 1.43, 2.86, 5.72 μg∙L−1), trifluralin (0.17, 0.33, 0.66, 1.33, 2.65 mg∙L−1) and chlorothalonil (0.09, 0.18, 0.36, 0.72, 1.43 mg∙L−1) respectively. Main reproductive parameters including first pregnancy time, first brood time, the number of first brood and total fecundity after 21 d exposures at the same concentrations of pesticides as described above were also measured. The results showed that the activities of GST increased in lower concentrations and decreased in higher concentrations after 24 h exposure to three pesticides, respectively. The activities of SOD showed the same changes after 48 h exposure. With the time prolonged, the activities of GST decreased while the activities of SOD increased. After 21 d exposure, the first pregnancy time and first brood time were delayed, while the number of the first brood and total fecundity per female decreased with increasing concentrations. These results corroborated that GST activity was more sensitive to those pesticides than SOD activity, and there was a significant relationship between total fecundity and pesticides-dose(r>0.94, n=6), GST activity after 48 h exposure and total fecundity after 21 d exposure (r>0.92, n=6).
Rocznik
Strony
80--86
Opis fizyczny
Bibliogr. 28 poz., tab., wykr.
Twórcy
autor
  • Nanjing University of Information Science and Technology, China Jiangsu Collaborative Innovation Centre of atmospheric environment and equipment technology (AEET)
  • Nanjing University of Information Science and Technology, China Jiangsu Key Laboratory of Agricultural Meteorology, College of Applied Meteorology
autor
  • Nanjing University of Information Science and Technology, China Jiangsu Collaborative Innovation Centre of atmospheric environment and equipment technology (AEET)
autor
  • Nanjing Institute of Environmental Sciences, China, MEP
Bibliografia
  • [1]. Bajet, C.M., Kumar, A., Calingacion, M.N. & Narvacan, T.C. (2012). Toxicological assessment of pesticides used in the Pagsanjan-Lumban catchment to selected non-target aquatic organisms in Laguna Lake, Philippines. Agricultural Water Management, 106, pp. 42–49.
  • [2]. Barata, C., Solayan, A. & Porte, C. (2004). Role of B-esterases in assessing toxicity of organophosphorus (chlorpyrifos, malathion) and carbamate (carbofuran) pesticides to Daphnia magna, Aquatic Toxicology, 66, pp. 125–139.
  • [3]. Calabrese, E.J. (2005). Paradigm lost, paradigm found: The re-emergence of hormesis as a fundamental dose response model in the toxicological sciences, Environmental Pollution, 138, pp. 378–411.
  • [4]. Chen, R., Liu, H., Li, D.X. & Chen, Y. (2006). A review of glutathione S-transferase in aquatic animal, Journal of Xiamen University (Natural Science), 45, pp. 176–184.
  • [5]. Dodson, S.I., Merritt, C.M., Shannaphan, J.P. & Schults, C.M. (1999). Low exposure concentrations of atrazine increase male production in Daphnia pulicaria, Environment Toxicology and Chemistry, 18, pp. 1568–1573.
  • [6]. Gadagbui, B.K.M. & James, M.O. (2000). The influence of diet on the regional distribution of glutathione S-transferase activity in channel catfish intestine, Journal of Biochemical and Molecular Toxicology, 14, pp. 148–154.
  • [7]. Hayasaka, D., Korenaga, T., Suzuki, K., Saito, F., Sánchez-Bayo, F. & Goka, K. (2012). Cumulative ecological impacts of two successive annual treatments of imidacloprid and fipronil on aquatic communities of paddy mesocosms, Ecotoxicology and Environmental Safety, 80, pp. 355–362.
  • [8]. ISO (1989). Water quality-determination of the inhibition of the mobility of Daphnia magna straus (Cladocero: crustacea), pp. 6341–1989.
  • [9]. Li, Y.X. & Yang, J.M. (1997). Comparison of the toxicity and the influence of enzyme activity of four kinds of insecticides to Daphnia magna, Acta Scientiarum Natualium Universitatis Pekinensis, 33, pp. 197–202.
  • [10]. Lin, X. & Xue, B. (1997). Effects of pesticides on human immune system, Foreign Medical Sciences (Section Hygiene), 24, pp. 337–340.
  • [11]. OECD (2008). OECD-211 Guidelines for testing of chemicals: Daphnia magna reproduction test, Geneva 2008.
  • [12]. Palma, P., Palma, V.L., Matos, C., Fernandes, R.M., Bohn, A., Soares, A.M.V.M. & Barbosa, I.R. (2009). Assessment of the pesticides atrazine, endosulfan sulphate and chlorpyrifos for juvenoid-related endocrine activity using Daphnia magna, Chemosphere, 76, pp. 335–340.
  • [13]. Peng, Y., Fan, C.P., Liao, W., Liu, X.Y., Wu, X.Y. & Nie, X.P. (2012). Toxic effects of 2,2’,4,4’-tetrabromodiphenyl ether on Daphnia magna, Asian Journal of Ecotoxicology, 7, pp. 79–86.
  • [14]. Ren, Z.M., Zha, J.M., Ma, M., Wang, Z.J. & Gerhardt, A. (2007). The early warning of aquatic organophosphorus pesticide contamination by on-line monitoring behavioral changes of Daphnia magna, Environmental Monitoring and Assessment, 134, pp. 373–383.
  • [15]. Rodriguez-Mozaz, S., Marco, M.P., de Alda, L., Maria, J. & Barceló, D. (2004). Biosensors for environmental monitoring of endocrine disruptors: a review article, Analytical and bioanalytical chemistry, 378, pp. 588–598.
  • [16]. Shi, F., Jia, X., Zhao, C. & Chen, Y. (2010). Antioxidant activities of various extracts from Artemisisa selengensis Turcz (LuHao), Molecules, 15, pp. 4934–4946.
  • [17]. Smalling, K.L., Kuivila, K.M., Orlando, J.L., Phillips, B.M., Anderson, B.S., Siegler, K., Hunt, J.W. & Hamilton, M. (2013). Environmental fate of fungicides and other current-use pesticides in a central California estuary, Marine Pollution Bulletin, 73, pp. 144–153.
  • [18]. US EPA (1996). Aquatic invertebrate acute toxicity test, freshwater daphnids. EPA 712-C-96-114 Ecological Effects Test Guidelines. United States Environmental Protection Agency, Washington 1996.
  • [19]. Van der Oost, R., Beyer, J. & Vermeulen, N.P.E. (2003). Fish bioaccumulation and biomarkers in environmental risk assessment: a review, Environmental Toxicology and Pharmacology, 13, pp. 57–149.
  • [20]. Wang, C., Zhou, Q.H. & Wu, Z.B. (2011). Research advances of a kind of organophosphate pesticide chlorpyrifos, Environmental Science & Technology, 34, pp. 123–127.
  • [21]. Wiszniowski J., Halle A.T, Richard C., et al. (2011) Toxicity of sulcotrione photoproducts mixture towards Vibrio fisheri in the environment, Archives of Environmental Protection, 37, pp. 15–22.
  • [22]. Xiong, Q.L., Shi, Y.J., Lu, Y.L., Li, Q.S. & Gosens, J. (2013). Toxic effects of 2, 2’, 4, 4’-tetrabromodiphenyl ether (BDE-47) to Daphnia magna, Asian Journal of Ecotoxicology, 8, pp. 97–104.
  • [23]. Xu, Y.G., Zhang, J.L., Li, X.F. & Liu, L. (2013). Study on chronic toxicity of Difenoconazle to Daphnia magna and its effect on GST enzymatic activity, Hubei Agricultural Sciences, 52, pp. 79–83.
  • [24]. Ye, W.H., Liu, W.P. & Tan, Y.J. (2004). Daphnia magna toxicity and subsequent recovery during a subchronic toxicity test with Bifenthrin, Chinese Journal of Pesticides, 43, pp. 86–89.
  • [25]. Zhang, C.J., Wang, L. & Wang, Q. (2009). Effects of phenolic compounds on glutathione-S-transferase and acetylcholinesterase in Moina macrocopa, Asian Journal of Ecotoxicology, 4, pp. 258–264.
  • [26]. Zhang, Z.B. (1987). Effects of agricultural chemicals on farmland ecosystem (2), Journal of Ecology, 7, pp. 30–34.
  • [27]. Zhou, F.B. (2008). Strengthen control on pollutant discharged of pesticide industry by stipulating discharge standards, China agrochemicals, 4, pp. 4–9.
  • [28]. Zhou, Y.X. & Zhang, Z.S. (1989). Toxicity Test Method for Aquatic Organisms, Agriculture Press, Beijing 1989.
Uwagi
Opracowanie ze środków MNiSW w ramach umowy 812/P-DUN/2016 na działalność upowszechniającą naukę (zadania 2017).
Typ dokumentu
Bibliografia
Identyfikator YADDA
bwmeta1.element.baztech-ea10ecf6-8c17-4422-9bfd-7f1e3f5602b3
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