Toxic effects induced by nonylphenol (NP) and ethoxylated nonylphenol (NP-9) in Caenorhabditis elegans
Needs in the field of cleanliness and asepsis have evolved over time. Among the most widely used chemicals in the world today are emerging pollutants. One of these contaminants is nonylphenol ethoxylate (NP-9), also known as Tergitol, and its degradation product, nonylphenol (NP), active ingredients...
- Autores:
-
De la Parra Guerra, Ana Cristina
- Tipo de recurso:
- Doctoral thesis
- Fecha de publicación:
- 2020
- Institución:
- Universidad de Cartagena
- Repositorio:
- Repositorio Universidad de Cartagena
- Idioma:
- eng
- OAI Identifier:
- oai:repositorio.unicartagena.edu.co:11227/16525
- Acceso en línea:
- https://hdl.handle.net/11227/16525
http://dx.doi.org/10.57799/11227/11859
- Palabra clave:
- Toxicología ambiental
Contaminantes – Toxicología
Toxicology
Química toxicológica
- Rights
- openAccess
- License
- Derechos Reservados - Universidad de Cartagena, 2020
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dc.title.eng.fl_str_mv |
Toxic effects induced by nonylphenol (NP) and ethoxylated nonylphenol (NP-9) in Caenorhabditis elegans |
title |
Toxic effects induced by nonylphenol (NP) and ethoxylated nonylphenol (NP-9) in Caenorhabditis elegans |
spellingShingle |
Toxic effects induced by nonylphenol (NP) and ethoxylated nonylphenol (NP-9) in Caenorhabditis elegans Toxicología ambiental Contaminantes – Toxicología Toxicology Química toxicológica |
title_short |
Toxic effects induced by nonylphenol (NP) and ethoxylated nonylphenol (NP-9) in Caenorhabditis elegans |
title_full |
Toxic effects induced by nonylphenol (NP) and ethoxylated nonylphenol (NP-9) in Caenorhabditis elegans |
title_fullStr |
Toxic effects induced by nonylphenol (NP) and ethoxylated nonylphenol (NP-9) in Caenorhabditis elegans |
title_full_unstemmed |
Toxic effects induced by nonylphenol (NP) and ethoxylated nonylphenol (NP-9) in Caenorhabditis elegans |
title_sort |
Toxic effects induced by nonylphenol (NP) and ethoxylated nonylphenol (NP-9) in Caenorhabditis elegans |
dc.creator.fl_str_mv |
De la Parra Guerra, Ana Cristina |
dc.contributor.advisor.none.fl_str_mv |
Olivero Verbel, Jesús |
dc.contributor.author.none.fl_str_mv |
De la Parra Guerra, Ana Cristina |
dc.subject.armarc.none.fl_str_mv |
Toxicología ambiental Contaminantes – Toxicología Toxicology Química toxicológica |
topic |
Toxicología ambiental Contaminantes – Toxicología Toxicology Química toxicológica |
description |
Needs in the field of cleanliness and asepsis have evolved over time. Among the most widely used chemicals in the world today are emerging pollutants. One of these contaminants is nonylphenol ethoxylate (NP-9), also known as Tergitol, and its degradation product, nonylphenol (NP), active ingredients present in nonionic surfactants used as herbicides, cosmetics, paints, plastics, disinfectants and detergents. These chemicals and their metabolites are commonly found in environmental matrices. The objectives of this research work were: 1. To assess the toxicity of NP and NP-9 in C. elegans. 2. To determine the gene expression profile for different toxicity mechanisms in C. elegans. 3. To determine the intergenerational effects caused by exposure to NP-9 in C. elegans. 4. To identify possible intergenerational neurotoxic effects from exposure to NP-9 in C. elegans. Wild-type L4 larvae were exposed to different concentrations of the surfactants to measure functional endpoints like; lethality, length, width, locomotion and lifespan. Transgenic green fluorescent protein (GFP) strains were employed to estimate changes in relative gene expression and promote the activation of toxicity signaling pathways related to mtl-2, gst-1, gpx-4, gpx-6, sod-4, hsp-70 and hsp-4. Additionally, stress response was also assessed using a daf-16::GFP transgenic strain. RT-qPCR was utilized to measure mRNA expression for neurotoxicity-related genes (unc-30, unc-25, dop-3, dat-1, mgl-1, and eat-4). In the results of the first aim, lethality was concentration dependent, with 24-h LC50 of 122 μM and 3215 μM for NP and NP-9, respectively. Both compounds inhibited nematode growth, although NP was more potent; and at non-lethal concentrations, nematode locomotion was reduced. The increase in the expression of tested genes was significant at 10 μM for NP-9 and 0.001 μM for NP, implying a likely role for the activation of oxidative and cellular stress, as well as metabolism pathways. Except for glutathione peroxidase, which has a bimodal concentration-response curve for NP, typical of endocrine disruption, the other curves for this xenobiotic in the strains evaluated were almost flat for most concentrations, until reaching 50–100 μM, where the effect peaked. NP and NP-9 induced the and nuclear translocation of DAF-16, suggesting that transcription of stress-response genes may be mediated by the insulin/IGF-1 signaling pathway. In contrast, NP-9 induced a concentrationdependent response for the sod-4 hsp-4 mutants, with higher fluorescence induction than NP at similar levels. For the second aim, data were obtained from parent worms (P0) and the first generation (F1). Lethality of the nematode was concentration-dependent, with 48 h-LC50 values of 3215 and 1983 μM in P0 and F1, respectively. Non-lethal concentrations of NP-9 reduced locomotion. Lifespan was also decreased by the xenobiotic, but the negative effect was greater in P0 than in F1. Non-monotonic concentrationresponse curves were observed for body length and width in both generations. The gene expression profile in P0 was different from that registered in F1, although the expression of sod-4, hsp-70, gpx-6 and mtl-2 increased with the surfactant concentration in both generations. None of the tested genes followed a classical concentration-neurotoxicity relationship. In P0, dopamine presented an Inverted-U curve, while GABA and glutamate displayed a bimodal type. However, in F1, inverted U-shaped curves were revealed for these genes. In short, NP and NP-9 affect the physiology of C. elegans and modulate gene expression related to reactive oxygen species (ROS) production, cellular stress and metabolism of xenobiotics. Additionally, the NP-9 isomer induced intergenerational responses in nematode through mechanisms involving ROS, and alterations of the GABA, glutamate, and dopamine pathways. |
publishDate |
2020 |
dc.date.issued.none.fl_str_mv |
2020 |
dc.date.accessioned.none.fl_str_mv |
2023-06-20T16:56:38Z |
dc.date.available.none.fl_str_mv |
2023-06-20T16:56:38Z |
dc.type.spa.fl_str_mv |
Trabajo de grado - Doctorado |
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http://purl.org/coar/version/c_970fb48d4fbd8a85 |
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dc.language.iso.spa.fl_str_mv |
eng |
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Derechos Reservados - Universidad de Cartagena, 2020 |
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Derechos Reservados - Universidad de Cartagena, 2020 https://creativecommons.org/licenses/by-nc/4.0/ Atribución-NoComercial 4.0 Internacional (CC BY-NC 4.0) http://purl.org/coar/access_right/c_abf2 |
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Universidad de Cartagena |
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Facultad de Ciencias Farmacéuticas |
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Olivero Verbel, JesúsDe la Parra Guerra, Ana Cristina2023-06-20T16:56:38Z2023-06-20T16:56:38Z2020https://hdl.handle.net/11227/16525http://dx.doi.org/10.57799/11227/11859Needs in the field of cleanliness and asepsis have evolved over time. Among the most widely used chemicals in the world today are emerging pollutants. One of these contaminants is nonylphenol ethoxylate (NP-9), also known as Tergitol, and its degradation product, nonylphenol (NP), active ingredients present in nonionic surfactants used as herbicides, cosmetics, paints, plastics, disinfectants and detergents. These chemicals and their metabolites are commonly found in environmental matrices. The objectives of this research work were: 1. To assess the toxicity of NP and NP-9 in C. elegans. 2. To determine the gene expression profile for different toxicity mechanisms in C. elegans. 3. To determine the intergenerational effects caused by exposure to NP-9 in C. elegans. 4. To identify possible intergenerational neurotoxic effects from exposure to NP-9 in C. elegans. Wild-type L4 larvae were exposed to different concentrations of the surfactants to measure functional endpoints like; lethality, length, width, locomotion and lifespan. Transgenic green fluorescent protein (GFP) strains were employed to estimate changes in relative gene expression and promote the activation of toxicity signaling pathways related to mtl-2, gst-1, gpx-4, gpx-6, sod-4, hsp-70 and hsp-4. Additionally, stress response was also assessed using a daf-16::GFP transgenic strain. RT-qPCR was utilized to measure mRNA expression for neurotoxicity-related genes (unc-30, unc-25, dop-3, dat-1, mgl-1, and eat-4). In the results of the first aim, lethality was concentration dependent, with 24-h LC50 of 122 μM and 3215 μM for NP and NP-9, respectively. Both compounds inhibited nematode growth, although NP was more potent; and at non-lethal concentrations, nematode locomotion was reduced. The increase in the expression of tested genes was significant at 10 μM for NP-9 and 0.001 μM for NP, implying a likely role for the activation of oxidative and cellular stress, as well as metabolism pathways. Except for glutathione peroxidase, which has a bimodal concentration-response curve for NP, typical of endocrine disruption, the other curves for this xenobiotic in the strains evaluated were almost flat for most concentrations, until reaching 50–100 μM, where the effect peaked. NP and NP-9 induced the and nuclear translocation of DAF-16, suggesting that transcription of stress-response genes may be mediated by the insulin/IGF-1 signaling pathway. In contrast, NP-9 induced a concentrationdependent response for the sod-4 hsp-4 mutants, with higher fluorescence induction than NP at similar levels. For the second aim, data were obtained from parent worms (P0) and the first generation (F1). Lethality of the nematode was concentration-dependent, with 48 h-LC50 values of 3215 and 1983 μM in P0 and F1, respectively. Non-lethal concentrations of NP-9 reduced locomotion. Lifespan was also decreased by the xenobiotic, but the negative effect was greater in P0 than in F1. Non-monotonic concentrationresponse curves were observed for body length and width in both generations. The gene expression profile in P0 was different from that registered in F1, although the expression of sod-4, hsp-70, gpx-6 and mtl-2 increased with the surfactant concentration in both generations. None of the tested genes followed a classical concentration-neurotoxicity relationship. In P0, dopamine presented an Inverted-U curve, while GABA and glutamate displayed a bimodal type. However, in F1, inverted U-shaped curves were revealed for these genes. In short, NP and NP-9 affect the physiology of C. elegans and modulate gene expression related to reactive oxygen species (ROS) production, cellular stress and metabolism of xenobiotics. Additionally, the NP-9 isomer induced intergenerational responses in nematode through mechanisms involving ROS, and alterations of the GABA, glutamate, and dopamine pathways.DoctoradoDoctor(a) en Toxicología Ambientalapplication/pdfengUniversidad de CartagenaFacultad de Ciencias FarmacéuticasCartagena de IndiasDoctorado en Toxicología AmbientalDerechos Reservados - Universidad de Cartagena, 2020https://creativecommons.org/licenses/by-nc/4.0/info:eu-repo/semantics/openAccessAtribución-NoComercial 4.0 Internacional (CC BY-NC 4.0)http://purl.org/coar/access_right/c_abf2Toxic effects induced by nonylphenol (NP) and ethoxylated nonylphenol (NP-9) in Caenorhabditis elegansTrabajo de grado - Doctoradoinfo:eu-repo/semantics/publishedVersionhttp://purl.org/coar/resource_type/c_db06Textinfo:eu-repo/semantics/doctoralThesishttps://purl.org/redcol/resource_type/TDhttp://purl.org/coar/version/c_970fb48d4fbd8a85Toxicología ambientalContaminantes – ToxicologíaToxicologyQuímica toxicológicaAcevedo, R., Sabater, C., Olivero-Verbel, J. (2018). Ecotoxicological assessment of perchlorate using in vitro and in vivo assays. Environmental Science and Pollution Research 25(14), 13697-13708. https://doi.org/10.1007/s11356- 018-1565-6Acosta-Coley, I., Duran-Izquierdo, M., Rodriguez-Cavallo, E., Mercado-Camargo, J., Mendez-Cuadro, D., Olivero-Verbel, J. (2019). Quantification of microplastics along the Caribbean Coastline of Colombia: Pollution profile and biological effects on Caenorhabditis elegans. Marine Pollution Bulletin 146, 574-583. https://doi.org/10.1016/j.marpolbul.2019.06.084.Ademollo, N., Ferrara, F., Delise, M., Fabietti, F., Funari, E. (2008). Nonylphenol and octylphenol in human breast milk. Environment Internactional 34 (7), 984–987. https://doi.org/10.1016/j.envint.2008.03.001Amrit, F.R.G., Ratnappan, R., Keith, S.A., Ghazi, A. (2014). The C. elegans lifespan assay toolkit. Methods 68 (3), 465-475. https://doi.org/10.1016/j.ymeth.2014.04.002Anbalagan, C., Lafayette, I., Antoniou-Kourounioti, M., Gutierrez, C., Martin, J.R., Chowdhuri, D.K., De Pomerai, D.I. (2013) Use of transgenic GFP reporter strains of the nematode Caenorhabditis elegans to investigate the patterns of stress responses induced by pesticides and by organic extracts from agricultural soils. Ecotoxicology 22, 72–85. https://doi.org/10.1007/s10646-012-1004-2Anderson, G.L., Boyd, W.A., Williams, P. (2001). Assessment of sublethal endpoints for toxicity testing with the nematode Caenorhabditis elegans. Environmental Toxicology and Chemistry 20(4), 833-838. https://doi.org/10.1002/etc.5620200419Anderson, G.L., Cole, R.D., Williams, P.L. (2004). Assessing behavioral toxicity with Caenorhabditis elegans. Environmental Toxicology and Chemistry: An International Journal, 23(5), 1235-1240Andrade, A.L., Pacheco, A., Da cunha, C.L., Mendes, A.S. (2006). Disruptores endocrinos: potencial problema para la salud pública y medio ambiente. Biomédica 17(2), 146-150.Ali, S., Sharda Rajini, P. (2012). Elicitation of dopaminergic features of Parkinson's disease in C. elegans by monocrotophos, an organophosphorous insecticide. CNS & Neurological Disorders-Drug Targets (Formerly Current Drug Targets-CNS & Neurological Disorders), 11(8), 993- 1000.Aly, H.A., Domènech, Ò., Banjar, Z.M. (2012). Effect of nonylphenol on male reproduction: analysis of rat epididymal biochemical markers and antioxidant defense enzymes. Toxicology and applied pharmacology, 261(2), 134-141.Araujo, F.G., Bauerfeldt, G.F., Cid, Y.P. (2018). Nonylphenol: Properties, legislation, toxicity and determination. Anais da Academia Brasileira de Ciências (AHEAD), 0-0. ISSN 1678-2690. http://dx.doi.org/10.1590/0001- 3765201720170023Aronzon, C.M. (2013). Evaluación de la toxicidad de los contaminantes Cobre, Nonilfenol y Diazinón sobre embriones y larvas de Rhinella (Bufo) arenarum. Doctoral disertación, Universidad de Buenos Aires. Argentina. Pág. 1-250.Arditsoglou, A., Voutsa, D. (2008). Determination of phenolic and steroid endocrine disrupting compounds in environmental matrices. Environmental science and pollution research 15(3, 228-236. https://doi.org/10.1065/espr2007.12.45Arnold, M.C., Badireddy, A.R., Wiesner, M.R., Di Giulio, R.T., Meyer, J.N. (2013). Cerium oxide nanoparticles are more toxic than equimolar bulk cerium oxide in Caenorhabditis elegans. Archives of Environmental Contamination and Toxicology 65(2), 224-233. https://doi.org/10.1007/s00244-013-9905-5Atienzar, F.A., Billinghurst, Z., Depledge, M.H. (2002). 4-nNonylphenol and 17-β estradiol may induce common DNA effects in developing barnacle larvae. Environmental pollution, 120(3), 735-738.Avila, D.S., Benedetto, A., Au, C., Bornhorst, J., Aschner, M. (2016). Involvement of heat shock proteins on Mn-induced toxicity in Caenorhabditis elegans. BMC. Pharmacology and Toxicology 17 (1), 54. 10.1186/s40360-016-0097-2Ayuda-Durán, B., González-Manzano, S., Miranda-Vizuete, A., Dueñas, M., Santos-Buelga, C., González-Paramás, A.M. (2019). Epicatechin modulates stress-resistance in C. elegans via insulin/IGF-1 signaling pathway. PLoS One 14(1), e0199483. Doi: 10.1371/journal.pone.0199483Back, P., Braeckman, B.P., Matthijssens, F. (2012). ROS in aging Caenorhabditis elegans: damage or signaling?. Oxidative Medicine and Cellular Longevity 2012. Doi:10.1155/2012/608478Bakke, D. (2003). Human and ecological risk assessment of nonylphenol polyethoxylate-based (NPE) surfactants in Forest Service herbicide applications. USDA Forest Service Pacific Southwest Region, Vallejo (USA)Bal, N., Kumar, A., Nugegoda, D. (2017). Assessing multigenerational effects of prednisolone to the freshwater snail, Physa acuta (Gastropoda: Physidae). J. Hazardous Materials 339, 281-291. https://doi.org/10.1016/j.jhazmat.2017.06.024Barceló, D. (2003). Trends in Analytical Chemistry, 22, xiv.Baraldo, G., Etemad, S., Weiss, A.K., Jansen-Dürr, P., Mack, H.I. (2019). Modulation of serotonin signaling by the putative oxaloacetate decarboxylase FAHD-1 in Caenorhabditis elegans. PloS One 14 (8), 10.1371/journal.pone.0220434Baumeister, R., Schaffitzel, E., Hertweck, M. (2006). Endocrine signaling in Caenorhabditis elegans controls stress response and longevity. Journal of Endocrinology 190(2), 191-202. https://doi.org/10.1677/joe.1.06856Bian, T., Zhu, X., Guo, J., Zhuang, Z., Cai, Z., Zhao, X. (2018). Toxic effect of the novel chiral insecticide IPP and its biodegradation intermediate in nematode Caenorhabditis elegans. Ecotoxicology and Environmental Safety 164, 604-610. https://doi.org/10.1016/j.ecoenv.2018.08.059PublicationORIGINAL2020_TESIS DE GRADO_ANA C. DE LA PARRA GUERRA.pdf2020_TESIS DE GRADO_ANA C. 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