Does light pollution affect zebrafish embryos response to mycophenolic acid?
Main Author: | |
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Publication Date: | 2023 |
Format: | Master thesis |
Language: | eng |
Source: | Repositórios Científicos de Acesso Aberto de Portugal (RCAAP) |
Download full: | http://hdl.handle.net/10773/41455 |
Summary: | In recent years, the process of urbanization has led to a significant escalation in light pollution within natural aquatic ecosystems. This light pollution, resulting from the increased presence of artificial light at night (ALAN), disrupts natural light levels. ALAN disturbs circadian rhythms by inhibiting the nighttime secretion of melatonin. Urban freshwater environments, in addition to contending with light pollution, are also subject to chemical contamination due to improper disposal, pharmaceutical residues in organic fertilizers, and wastewater from urban areas and healthcare facilities, pharmaceuticals such as antineoplastic drugs, which are continuously released into the environment and accumulate in various ecosystems. The aim of this work was to assess whether ALAN alters the response of Danio rerio embryos to the antineoplastic drug mycophenolic acid (MPA). To assess embryos response to MPA the organisms were exposed to a set of concentrations ranging from 16 to 288 μg/L for 120 hours. Embryos’ mortality, hatching, and malformations rates were observed every 24 hours for the 120 hours of exposure, and heart rate was assessed at 48 hours. Moreover, at the end of the exposure, a behaviour test was performed on larvae and the body length, interocular distance, and swimming bladder size were measured, and a set of biochemical biomarkers related with oxidative stress, neurotoxicity and energy metabolism were analysed. To assess ALAN effects and its interaction with MPA, embryos were exposed to three different light intensities (0, 1 and 10 lux) and four different MPA concentrations (0, 36, 90 and 225 μg/L). The same endpoints as in the MPA experiments were analysed. The results indicate that MPA decreases survival of embryos and impairs the normal development of zebrafish embryos, by decreasing hatching rate and inducing malformations. At behavioural level, the exposure to this cytostatic drug also affected the swimming behaviour of zebrafish larva. Furthermore, MPA affected the antioxidant system of zebrafish embryos and altered their energy metabolism. No effects of ALAN were observed for D. rerio life history traits, but it led to an earlier onset of malformations induced by MPA, reduced the behavioural response to MPA and modified MPA responses at a biochemical level, namely catalase activity, protein, and carbohydrate contents. In conclusion, ALAN has the potential to modify the response of D. rerio embryos to MPA, thus underscoring the relevance of including it in ecological risk assessments of antineoplastic drugs. Nevertheless, the precise underlying mechanisms remain unidentified. The findings of this work emphasize the critical need to investigate the combined impacts of chemical contamination and light pollution, both prevalent and concomitant stressors in urban freshwater ecosystems. |
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Does light pollution affect zebrafish embryos response to mycophenolic acid?Antineoplastic drugsArtificial light at nightChemical contaminationDanio rerioMycophenolic acidUrban aquatic ecosystemsIn recent years, the process of urbanization has led to a significant escalation in light pollution within natural aquatic ecosystems. This light pollution, resulting from the increased presence of artificial light at night (ALAN), disrupts natural light levels. ALAN disturbs circadian rhythms by inhibiting the nighttime secretion of melatonin. Urban freshwater environments, in addition to contending with light pollution, are also subject to chemical contamination due to improper disposal, pharmaceutical residues in organic fertilizers, and wastewater from urban areas and healthcare facilities, pharmaceuticals such as antineoplastic drugs, which are continuously released into the environment and accumulate in various ecosystems. The aim of this work was to assess whether ALAN alters the response of Danio rerio embryos to the antineoplastic drug mycophenolic acid (MPA). To assess embryos response to MPA the organisms were exposed to a set of concentrations ranging from 16 to 288 μg/L for 120 hours. Embryos’ mortality, hatching, and malformations rates were observed every 24 hours for the 120 hours of exposure, and heart rate was assessed at 48 hours. Moreover, at the end of the exposure, a behaviour test was performed on larvae and the body length, interocular distance, and swimming bladder size were measured, and a set of biochemical biomarkers related with oxidative stress, neurotoxicity and energy metabolism were analysed. To assess ALAN effects and its interaction with MPA, embryos were exposed to three different light intensities (0, 1 and 10 lux) and four different MPA concentrations (0, 36, 90 and 225 μg/L). The same endpoints as in the MPA experiments were analysed. The results indicate that MPA decreases survival of embryos and impairs the normal development of zebrafish embryos, by decreasing hatching rate and inducing malformations. At behavioural level, the exposure to this cytostatic drug also affected the swimming behaviour of zebrafish larva. Furthermore, MPA affected the antioxidant system of zebrafish embryos and altered their energy metabolism. No effects of ALAN were observed for D. rerio life history traits, but it led to an earlier onset of malformations induced by MPA, reduced the behavioural response to MPA and modified MPA responses at a biochemical level, namely catalase activity, protein, and carbohydrate contents. In conclusion, ALAN has the potential to modify the response of D. rerio embryos to MPA, thus underscoring the relevance of including it in ecological risk assessments of antineoplastic drugs. Nevertheless, the precise underlying mechanisms remain unidentified. The findings of this work emphasize the critical need to investigate the combined impacts of chemical contamination and light pollution, both prevalent and concomitant stressors in urban freshwater ecosystems.Nos últimos anos, o processo de urbanização conduziu a um aumento significativo da poluição luminosa nos ecossistemas aquáticos naturais. Esta poluição luminosa, resultante do aumento da presença de luz artificial noturna (ALAN), perturba os níveis de luz natural. A ALAN perturba os ritmos circadianos, inibindo a secreção noturna de melatonina. Os ambientes urbanos de água doce, além de sofrerem com a poluição luminosa, também estão sujeitos à contaminação química devido ao descarte inadequado, resíduos farmacêuticos em fertilizantes orgânicos e águas residuais de áreas urbanas e unidades de saúde, produtos farmacêuticos como drogas antineoplásicas, que são continuamente liberados no ambiente e se acumulam em vários ecossistemas. O objetivo deste trabalho foi avaliar se o ALAN altera a resposta dos embriões de Danio rerio ao medicamento antineoplásico ácido micofenólico (MPA). Para avaliar a resposta dos embriões ao MPA, os organismos foram expostos a um conjunto de concentrações que variaram de 16 a 288 μg/L durante 120 horas. As taxas de mortalidade, eclosão e malformações dos embriões foram observadas a cada 24 horas durante as 120 horas de exposição, e a frequência cardíaca foi avaliada às 48 horas. Além disso, no final da exposição, as larvas foram submetidas a um teste de comportamento, tendo sido medidos o comprimento do corpo, a distância interocular e o tamanho da bexiga natatória, e foi analisado um conjunto de biomarcadores bioquímicos relacionados com o stress oxidativo, a neurotoxicidade e o metabolismo energético. Para avaliar os efeitos do ALAN e a sua interação com o MPA, os embriões foram expostos a três intensidades de luz diferentes (0, 1 e 10 lux) e a quatro concentrações diferentes de MPA (0, 36, 90 e 225 μg/L). Foram analisados os mesmos parâmetros que nas experiências com MPA. Os resultados indicam que o MPA diminui a sobrevivência dos embriões e prejudica o desenvolvimento normal dos embriões de peixe-zebra, diminuindo a taxa de eclosão e induzindo malformações. A nível comportamental, a exposição a esta droga citostática também afetou o comportamento de natação das larvas de peixe-zebra. Além disso, o MPA afetou o sistema antioxidante dos embriões de peixe-zebra e alterou o seu metabolismo energético. Não foram observados efeitos do ALAN nas características da história de vida do D. rerio, mas levou a um início mais precoce das malformações induzidas pelo MPA, reduziu a resposta comportamental ao MPA e modificou as respostas ao MPA a nível bioquímico, nomeadamente a atividade da catalase, o conteúdo de proteínas e hidratos de carbono. Em conclusão, o ALAN tem o potencial de modificar a resposta dos embriões de D. rerio ao MPA, sublinhando assim a relevância de o incluir nas avaliações de risco ecológico dos medicamentos antineoplásicos. No entanto, os mecanismos exatos subjacentes continuam por identificar. Os resultados deste trabalho sublinham a necessidade crítica de investigar os impactos combinados da contaminação química e da poluição luminosa, fatores de stress prevalecentes e concomitantes nos ecossistemas urbanos de água doce.2025-12-27T00:00:00Z2023-12-13T00:00:00Z2023-12-13info:eu-repo/semantics/publishedVersioninfo:eu-repo/semantics/masterThesisapplication/pdfhttp://hdl.handle.net/10773/41455engCosta, Maria Santos de Sousa einfo:eu-repo/semantics/embargoedAccessreponame:Repositórios Científicos de Acesso Aberto de Portugal (RCAAP)instname:FCCN, serviços digitais da FCT – Fundação para a Ciência e a Tecnologiainstacron:RCAAP2024-05-06T04:54:43Zoai:ria.ua.pt:10773/41455Portal AgregadorONGhttps://www.rcaap.pt/oai/openaireinfo@rcaap.ptopendoar:https://opendoar.ac.uk/repository/71602025-05-28T14:24:01.959504Repositórios Científicos de Acesso Aberto de Portugal (RCAAP) - FCCN, serviços digitais da FCT – Fundação para a Ciência e a Tecnologiafalse |
dc.title.none.fl_str_mv |
Does light pollution affect zebrafish embryos response to mycophenolic acid? |
title |
Does light pollution affect zebrafish embryos response to mycophenolic acid? |
spellingShingle |
Does light pollution affect zebrafish embryos response to mycophenolic acid? Costa, Maria Santos de Sousa e Antineoplastic drugs Artificial light at night Chemical contamination Danio rerio Mycophenolic acid Urban aquatic ecosystems |
title_short |
Does light pollution affect zebrafish embryos response to mycophenolic acid? |
title_full |
Does light pollution affect zebrafish embryos response to mycophenolic acid? |
title_fullStr |
Does light pollution affect zebrafish embryos response to mycophenolic acid? |
title_full_unstemmed |
Does light pollution affect zebrafish embryos response to mycophenolic acid? |
title_sort |
Does light pollution affect zebrafish embryos response to mycophenolic acid? |
author |
Costa, Maria Santos de Sousa e |
author_facet |
Costa, Maria Santos de Sousa e |
author_role |
author |
dc.contributor.author.fl_str_mv |
Costa, Maria Santos de Sousa e |
dc.subject.por.fl_str_mv |
Antineoplastic drugs Artificial light at night Chemical contamination Danio rerio Mycophenolic acid Urban aquatic ecosystems |
topic |
Antineoplastic drugs Artificial light at night Chemical contamination Danio rerio Mycophenolic acid Urban aquatic ecosystems |
description |
In recent years, the process of urbanization has led to a significant escalation in light pollution within natural aquatic ecosystems. This light pollution, resulting from the increased presence of artificial light at night (ALAN), disrupts natural light levels. ALAN disturbs circadian rhythms by inhibiting the nighttime secretion of melatonin. Urban freshwater environments, in addition to contending with light pollution, are also subject to chemical contamination due to improper disposal, pharmaceutical residues in organic fertilizers, and wastewater from urban areas and healthcare facilities, pharmaceuticals such as antineoplastic drugs, which are continuously released into the environment and accumulate in various ecosystems. The aim of this work was to assess whether ALAN alters the response of Danio rerio embryos to the antineoplastic drug mycophenolic acid (MPA). To assess embryos response to MPA the organisms were exposed to a set of concentrations ranging from 16 to 288 μg/L for 120 hours. Embryos’ mortality, hatching, and malformations rates were observed every 24 hours for the 120 hours of exposure, and heart rate was assessed at 48 hours. Moreover, at the end of the exposure, a behaviour test was performed on larvae and the body length, interocular distance, and swimming bladder size were measured, and a set of biochemical biomarkers related with oxidative stress, neurotoxicity and energy metabolism were analysed. To assess ALAN effects and its interaction with MPA, embryos were exposed to three different light intensities (0, 1 and 10 lux) and four different MPA concentrations (0, 36, 90 and 225 μg/L). The same endpoints as in the MPA experiments were analysed. The results indicate that MPA decreases survival of embryos and impairs the normal development of zebrafish embryos, by decreasing hatching rate and inducing malformations. At behavioural level, the exposure to this cytostatic drug also affected the swimming behaviour of zebrafish larva. Furthermore, MPA affected the antioxidant system of zebrafish embryos and altered their energy metabolism. No effects of ALAN were observed for D. rerio life history traits, but it led to an earlier onset of malformations induced by MPA, reduced the behavioural response to MPA and modified MPA responses at a biochemical level, namely catalase activity, protein, and carbohydrate contents. In conclusion, ALAN has the potential to modify the response of D. rerio embryos to MPA, thus underscoring the relevance of including it in ecological risk assessments of antineoplastic drugs. Nevertheless, the precise underlying mechanisms remain unidentified. The findings of this work emphasize the critical need to investigate the combined impacts of chemical contamination and light pollution, both prevalent and concomitant stressors in urban freshwater ecosystems. |
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2023 |
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2023-12-13T00:00:00Z 2023-12-13 2025-12-27T00:00:00Z |
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