In vitro agonistic and antagonistic endocrine disrupting effects of organic extracts from waste water of different treatment processes

Kaifeng RAO , Na LI , Mei MA , Zijian WANG

Front. Environ. Sci. Eng. ›› 2014, Vol. 8 ›› Issue (1) : 69 -78.

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Front. Environ. Sci. Eng. ›› 2014, Vol. 8 ›› Issue (1) : 69 -78. DOI: 10.1007/s11783-013-0502-7
RESEARCH ARTICLE
RESEARCH ARTICLE

In vitro agonistic and antagonistic endocrine disrupting effects of organic extracts from waste water of different treatment processes

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Abstract

Effluents from wastewater treatment plant (WWTP) have been reported to have a broad spectrum of endocrine disrupting compounds (EDCs). The majority of studies have focused on the occurrence of estrogenic activity, while ignoring nuclear hormone receptors (NRs) pathways. In the present study, a battery of in vitro yeast bioassays and a cell bioassay, including antagonistic and agonistic effects on estrogen receptor (ER), androgen receptor (AR), progesterone receptor (PR), estrogen-related receptor (ERR) and aryl hydrocarbon receptor (AHR), were conducted to evaluate the removal efficiencies of EDCs by different treatment processes of a WWTP located in Beijing. Estrogenic, anti-estrogenic, anti- androgenic, anti-progesteronic, anti-ERR and the activation of AHR activities were detected in samples from all treatment processes and the receiving water. The concentration of estrogenic contaminants with estradiol (E2) equivalent concentrations ranged from 0.82 × 10-9 to 3.54 × 10-9 g E2-EQ·L-1. The concentration of anti-estrogenic contaminants with 4-hydroxytamoxifen (4-OHT) equivalent concentrations ranged from 1.24 × 10-6 to 2.36 × 10-6 g 4-OHT-EQ·L-1. The concentration of anti-androgenic contaminants ranged from 2.21 × 10-8 to 3.52 × 10-6 g flutamide-EQ·L-1. The concentration of anti-progesteronic contaminants ranged from 3.15 × 10-5 to 2.71 × 10-4 g RU486-EQ·L-1. The concentration of anti-ERR contaminants ranged from 7.09 × 10-5 to 6.50 × 10-4 g 4-OHT-EQ·L-1. The concentration of AHR activators ranged from 1.7 × 10-10 to 3.4 × 10-10 g TCDD-EQ·L-1. These processes including secondary clarifier, coagulation, as well as coal and sand filtration could eliminated 67.2% of estrogenic contaminants, 47.0% of anti-estrogenic contaminants, 98.3% of anti-androgenic contaminants, 88.4% of anti-progesteronic contaminants, 65.4% of anti-ERR contaminants and 46.9% of AHR activators. WWTP effluents contain multiple receptor disruptors may have very complex adverse effects on exposed organisms.

Keywords

waste water / in vitro / recombinant yeast assay / ethoxyresorufin-O-deethylase (EROD) / receptor / endocrine

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Kaifeng RAO, Na LI, Mei MA, Zijian WANG. In vitro agonistic and antagonistic endocrine disrupting effects of organic extracts from waste water of different treatment processes. Front. Environ. Sci. Eng., 2014, 8(1): 69-78 DOI:10.1007/s11783-013-0502-7

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References

[1]

Colborn T, vom Saal F S, Soto A M. Developmental effects of endocrine-disrupting chemicals in wildlife and humans. Environmental Health Perspectives, 1993, 101(5): 378-384

[2]

Heberer T, Feldmann D, Redderoen K, Altmann H J. Zimmermann. Production of Drinking Water from Highly Contaminated Surface Waters: Removal of Organic, Inorganic, and Microbial Contaminants Applying Mobile Membrane Filtration Units. Weinheim: Wiley-VCH, 2002

[3]

Stackelberg P E, Furlong E T, Meyer M T, Zaugg S D, Henderson A K, Reissman D B. Persistence of pharmaceutical compounds and other organic wastewater contaminants in a conventional drinking-water-treatment plant. The Science of The Total Environment, 2004, 329(1-3): 99-113

[4]

Johnson A C, Williams R J, Simpson P, Kanda R. What difference might sewage treatment performance make to endocrine disruption in rivers? Environmental Pollution, 2007, 147(1): 194-202

[5]

Clara M, Strenn B, Gans O, Martinez E, Kreuzinger N, Kroiss H. Removal of selected pharmaceuticals, fragrances and endocrine disrupting compounds in a membrane bioreactor and conventional wastewater treatment plants. Water Research, 2005, 39(19): 4797-4807

[6]

Jobling S, Burn R W, Thorpe K, Williams R, Tyler C. Statistical modeling suggests that antiandrogens in effluents from wastewater treatment works contribute to widespread sexual disruption in fish living in English rivers. Environmental Health Perspectives, 2009, 117(5): 797-802

[7]

Kristensen T, Baatrup E, Bayley M. p,p′-DDE fails to reduce the competitive reproductive fitness in Nigerian male guppies. Ecotoxicology and Environmental Safety, 2006, 63(1): 148-157

[8]

Li J, Li N, Ma M, Giesy J P, Wang Z. In vitro profiling of the endocrine disrupting potency of organochlorine pesticides. Toxicology Letters, 2008, 183(1-3): 65-71

[9]

Li J, Ma M, Wang Z. In vitro profiling of endocrine disrupting effects of phenols. Toxicology In vitro: an international journal published in association with BIBRA, 2010, 24(1): 201-207

[10]

Benfenati E, Barcelò D, Johnson I, Galassi S, Levsen K. Emerging organic contaminants in leachates from industrial waste landfills and industrial effluent. Trends in Analytical Chemistry, 2003, 22(10): 757-765

[11]

Sánchez-Avila J, Bonet J, Velasco G, Lacorte S. Determination and occurrence of phthalates, alkylphenols, bisphenol A, PBDEs, PCBs and PAHs in an industrial sewage grid discharging to a Municipal Wastewater Treatment Plant. The Science of The Total Environment, 2009, 407(13): 4157-4167

[12]

Overington J P, Al-Lazikani B, Hopkins A L. How many drug targets are there? Nature Reviews. Drug Discovery, 2006, 5(12): 993-996

[13]

Kolodziej E P, Sedlak D L. Rangeland grazing as a source of steroid hormones to surface waters. Environmental Science & Technology, 2007, 41(10): 3514-3520

[14]

Durhan E J, Lambright C S, Makynen E A, Lazorchak J, Hartig P C, Wilson V S, Gray L E, Ankley G T. Identification of metabolites of trenbolone acetate in androgenic runoff from a beef feedlot. Environmental Health Perspectives, 2005, 114(S-1): 65-68

[15]

Westerhoff P, Yoon Y, Snyder S, Wert E. Fate of endocrine-disruptor, pharmaceutical, and personal care product chemicals during simulated drinking water treatment processes. Environmental Science & Technology, 2005, 39(17): 6649-6663

[16]

Molinamolina J M, Hillenweck A, Jouanin I, Zalko D, Cravedi J P, Fernández M F, Pillon A, Nicolas J C, Olea N, Balaguer P. Steroid receptor profiling of vinclozolin and its primary metabolites. Toxicology and Applied Pharmacology, 2006, 216(1): 44-54

[17]

Ma M, Li J, Wang Z. Assessing the detoxication efficiencies of wastewater treatment processes using a battery of bioassays/biomarkers. Archives of Environmental Contamination and Toxicology, 2005, 49(4): 480-487

[18]

Tillitt D E, Ankley G T, Verbrugge D A, Giesy J P, Ludwig J P, Kubiak T J. H4IIE rat hepatoma cell bioassay-derived 2,3,7,8-tetrachlorodibenzo-p-dioxin equivalents in colonial fish-eating waterbird eggs from the Great Lakes. Archives of Environmental Contamination and Toxicology, 1991, 21(1): 91-101

[19]

Qiao M, Chen Y, Zhang Q, Huang S, Ma M, Wang C, Wang Z. Identification of Ah receptor agonists in sediment of Meiliang Bay, Taihu Lake, China. Environmental Science & Technology, 2006, 40(5): 1415-1419

[20]

Shen C, Huang S, Wang Z, Qiao M, Tang X, Yu C, Shi D, Zhu Y, Shi J, Chen X, Setty K, Chen Y. Identification of ah receptor agonists in soil of E-waste recycling sites from Taizhou area in China. Environmental Science & Technology, 2008, 42(1): 49-55

[21]

Gaido K W, Leonard L S, Lovell S, Gould J C, Babaï D, Portier C J, McDonnell D P. Evaluation of chemicals with endocrine modulating activity in a yeast-based steroid hormone receptor gene transcription assay. Toxicology and Applied Pharmacology, 1997, 143(1): 205-212

[22]

Li J, Ma M, Wang Z J. A two-hybrid yeast assay to quantify the effects of xenobiotics on thyroid hormone-mediated gene expression. Environmental Toxicology and Chemistry/SETAC, 2008, 27(1): 159-167

[23]

Wang J X, Xie P, Kettrup A, Schramm K W. Inhibition of progesterone receptor activity in recombinant yeast by soot from fossil fuel combustion emissions and air particulate materials. The Science of The Total Environment, 2005, 349(1-3): 120-128

[24]

Donato M T, Gómez-Lechón M J, Castell J V. A microassay for measuring cytochrome P450IA1 and P450IIB1 activities in intact human and rat hepatocytes cultured on 96-well plates. Analytical Biochemistry, 1993, 213(1): 29-33

[25]

Wang C, Wang Y, Kiefer F, Yediler A, Wang Z, Kettrup A. Ecotoxicological and chemical characterization of selected treatment process effluents of municipal sewage treatment plant. Ecotoxicology and Environmental Safety, 2003, 56(2): 211-217

[26]

Bradford M M. A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. Analytical Biochemistry, 1976, 72(1-2): 248-254

[27]

Wu Z W, Wang X J, Zhao F G, You L. The Emission Soot of Biomass Fuels Combustion as a Source of Endocrine Disrupters. Philadelphia, PA, ETATS-UNIS: Taylor&amp, Francis, 2002

[28]

Cargouët M, Perdiz D, Mouatassim-Souali A, Tamisier-Karolak S, Levi Y. Assessment of river contamination by estrogenic compounds in Paris area (France). The Science of The Total Environment, 2004, 324(1-3): 55-66

[29]

Svenson A, Allard A S, Ek M. Removal of estrogenicity in Swedish municipal sewage treatment plants. Water Research, 2003, 37(18): 4433-4443

[30]

Fawell J K, Sheahan D, James H A, Hurst M, Scott S. Oestrogens and oestrogenic activity in raw and treated water in Severn Trent Water. Water Research, 2001, 35(5): 1240-1244

[31]

Desbrow C, Routledge E J, Brighty G C, Sumpter J P, Waldock M. Identification of estrogenic chemicals in STW effluent. 1. Chemical fractionation and in vitro biological screening. Environmental Science & Technology, 1998, 32(11): 1549-1558

[32]

Ying G G, Kookana R S, Ru Y J. Occurrence and fate of hormone steroids in the environment. Environment International, 2002, 28(6): 545-551

[33]

Jobling S, Nolan M, Tyler C R, Brighty G, Sumpter J P. Widespread sexual disruption in wild fish. Environmental Science & Technology, 1998, 32(17): 2498-2506

[34]

Conroy O, Sáez A E, Quanrud D, Ela W, Arnold R G. Changes in estrogen/anti-estrogen activities in ponded secondary effluent. The Science of the total environment, 2007, 382(2-3): 311-323

[35]

van der Oost R, Beyer J, Vermeulen N P E. Fish bioaccumulation and biomarkers in environmental risk assessment: a review. Environmental Toxicology and Pharmacology, 2003, 13(2): 57-149

[36]

Vega-López A, Ramón-Gallegos E, Galar-Martínez M, Jiménez-Orozco F A, García-Latorre E, Domínguez-Lípez M L. Estrogenic, anti-estrogenic and cytotoxic effects elicited by water from the type localities of the endangered goodeid fish Girardinichthys viviparus. Comparative Biochemistry and Physiology-Part C: Toxicology & Pharmacology, 2007, 145(3): 394-403

[37]

Sohoni P, Sumpter J P. Several environmental oestrogens are also anti-androgens. The Journal of endocrinology, 1998, 158(3): 327-339

[38]

Xu L C, Sun H, Chen J F, Bian Q, Qian J, Song L, Wang X R. Evaluation of androgen receptor transcriptional activities of bisphenol A, octylphenol and nonylphenol in vitro. Toxicology, 2005, 216(2-3): 197-203

[39]

Kiparissis Y, Metcalfe T L, Balch G C, Metcalfe C D. Effects of the antiandrogens, vinclozolin and cyproterone acetate on gonadal development in the Japanese medaka (Oryzias latipes). Aquatic Toxicology (Amsterdam, Netherlands), 2003, 63(4): 391-403

[40]

Tollefsen K E, Harman C, Smith A, Thomas K V. Estrogen receptor (ER) agonists and androgen receptor (AR) antagonists in effluents from Norwegian North Sea oil production platforms. Marine Pollution Bulletin, 2007, 54(3): 277-283

[41]

Graham J D, Clarke C L. Physiological action of progesterone in target tissues. Endocrine Reviews, 1997, 18(4): 502-519

[42]

Vonier P M, Crain D A, McLachlan J A, Guillette L J Jr, Arnold S F. Interaction of environmental chemicals with the estrogen and progesterone receptors from the oviduct of the American alligator. Environmental Health Perspectives, 1996, 104(12): 1318-1322

[43]

Pickford D B, Morris I D. Effects of endocrine-disrupting contaminants on amphibian oogenesis: methoxychlor inhibits progesterone-induced maturation of Xenopus laevis oocytes in vitro. Environmental Health Perspectives, 1999, 107(4): 285-292

[44]

Klotz D M, Ladlie B L, Vonier P M, McLachlan J A, Arnold S F. o,p’-DDT and its metabolites inhibit progesterone-dependent responses in yeast and human cells. Molecular and Cellular Endocrinology, 1997, 129(1): 63-71

[45]

Wen D X, Xu Y F, Mais D E, Goldman M E, McDonnell D P. The A and B isoforms of the human progesterone receptor operate through distinct signaling pathways within target cells. Molecular and Cellular Biology, 1994, 14(12): 8356-8364

[46]

Horard B, Vanacker J M. Estrogen receptor-related receptors: orphan receptors desperately seeking a ligand. Journal of Molecular Endocrinology, 2003, 31(3): 349-357

[47]

Takayanagi S, Tokunaga T, Liu X, Okada H, Matsushima A, Shimohigashi Y. Endocrine disruptor bisphenol A strongly binds to human estrogen-related receptor gamma (ERRgamma) with high constitutive activity. Toxicology Letters, 2006, 167(2): 95-105

[48]

Greschik H, Flaig R, Renaud J P, Moras D. Structural basis for the deactivation of the estrogen-related receptor gamma by diethylstilbestrol or 4-hydroxytamoxifen and determinants of selectivity. The Journal of Biological Chemistry, 2004, 279(32): 33639-33646

[49]

Tremblay G B, Bergeron D, Giguere V. 4-Hydroxytamoxifen is an isoform-specific inhibitor of orphan estrogen-receptor-related (ERR) nuclear receptors beta and gamma. Endocrinology, 2001, 142(10): 4572-4575

[50]

Ariazi E A, Clark G M, Mertz J E. Estrogen-related receptor alpha and estrogen-related receptor gamma associate with unfavorable and favorable biomarkers, respectively, in human breast cancer. Cancer Research, 2002, 62(22): 6510-6518

[51]

Aoki Y. Polychlorinated biphenyls, polychlorinated dibenzo-p-dioxins, and polychlorinated dibenzofurans as endocrine disrupters—what we have learned from Yusho disease. Environmental Research, 2001, 86(1): 2-11

[52]

Díaz-Ferrero J, Rodríguez-Larena M C, Comellas L, Jiménez B.Bioanalytical methods applied to endocrine disrupting polychlorinated biphenyls, polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans: a review. TrAC Trends in Analytical Chemistry, 16(10): 563-573

[53]

Balaguer P, Joyeux A, Denison M S, Vincent R, Gillesby B E, Zacharewski T. Assessing the estrogenic and dioxin-like activities of chemicals and complex mixtures using in vitro recombinant receptor-reporter gene assays. Canadian Journal of Physiology and Pharmacology, 1996, 74(2): 216-222

[54]

Louiz I, Kinani S, Gouze M E, Ben-Attia M, Menif D, Bouchonnet S, Porcher J M, Ben-Hassine O K, Aït-Aïssa S. Monitoring of dioxin-like, estrogenic and anti-androgenic activities in sediments of the Bizerta lagoon (Tunisia) by means of in vitro cell-based bioassays: contribution of low concentrations of polynuclear aromatic hydrocarbons (PAHs). The Science of The Total Environment, 2008, 402(2-3): 318-329

[55]

Reungoat J, Macova M, Escher B I, Carswell S, Mueller J F, Keller J. Removal of micropollutants and reduction of biological activity in a full scale reclamation plant using ozonation and activated carbon filtration. Water Research, 2010, 44(2): 625-637

[56]

Macova M, Escher B I, Reungoat J, Carswell S, Chue K L, Keller J, Mueller J F. Monitoring the biological activity of micropollutants during advanced wastewater treatment with ozonation and activated carbon filtration. Water Research, 2010, 44(2): 477-492

[57]

Blanchard M, Teil M J, Ollivon D, Legenti L, Chevreuil M. Polycyclic aromatic hydrocarbons and polychlorobiphenyls in wastewaters and sewage sludges from the Paris area (France). Environmental Research, 2004, 95(2): 184-197

[58]

Busetti F, Heitz A, Cuomo M, Badoer S, Traverso P. Determination of sixteen polycyclic aromatic hydrocarbons in aqueous and solid samples from an Italian wastewater treatment plant. Journal of Chromatography. A, 2006, 1102(1-2): 104-115

[59]

Smirnov A D, Schecter A, Päpke O, Beljak A A. Conclusions from Ufa, Russia, drinking water dioxin cleanup experiments involving different treatment technologies. Chemosphere, 1996, 32(3): 479-489

[60]

Ternes T A, Meisenheimer M, McDowell D, Sacher F, Brauch H J, Haist-Gulde B, Preuss G, Wilme U, Zulei-Seibert N. Removal of pharmaceuticals during drinking water treatment. Environmental Science & Technology, 2002, 36(17): 3855-3863

[61]

Nelson J, Bishay F, van Roodselaar A, Ikonomou M, Law F C. The use of in vitro bioassays to quantify endocrine disrupting chemicals in municipal wastewater treatment plant effluents. The Science of The Total Environment, 2007, 374(1): 80-90

[62]

Servos M R, Bennie D T, Burnison B K, Jurkovic A, McInnis R, Neheli T, Schnell A, Seto P, Smyth S A, Ternes T A. Distribution of estrogens, 17β-estradiol and estrone, in Canadian municipal wastewater treatment plants. The Science of The Total Environment, 2005, 336(1-3): 155-170

[63]

Kraus W L, Weis K E, Katzenellenbogen B S. Inhibitory cross-talk between steroid hormone receptors: differential targeting of estrogen receptor in the repression of its transcriptional activity by agonist- and antagonist-occupied progestin receptors. Molecular and Cellular Biology, 1995, 15(4): 1847-1857

[64]

Ohtake F, Fujii-Kuriyama Y, Kawajiri K, Kato S. Cross-talk of dioxin and estrogen receptor signals through the ubiquitin system. The Journal of Steroid Biochemistry and Molecular Biology, 2011, 127(1-2): 102-107

[65]

Tran D Q, Klotz D M, Ladlie B L, Ide C F, McLachlan J A, Arnold S F. Inhibition of progesterone receptor activity in yeast by synthetic chemicals. Biochemical and Biophysical Research Communications, 1996, 229(2): 518-523

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