ABSTRACT
A contaminação de corpos d'água por fármacos é um tema de extrema relevância, tendo em vista problemas como a escassez de água, florações de cianobactérias tóxicas e lançamentos clandestinos de efluentes domésticos. Sendo assim, este trabalho teve como objetivo determinar a presença de cafeína (CAF), fluoxetina (FLX), levotiroxina (LVX) e bezafibrato (BZF) em mananciais do estado de São Paulo, bem como avaliar a toxicidade desses compostos à cianobactéria Microcystis aeruginosa LTPNA 08. Um método por LC-MS/MS foi desenvolvido e validado, de acordo com a RDC nº 166 da ANVISA, para a detecção de CAF, FLX, LVX e BZF em amostras ambientais. As represas Guarapiranga e Billings, bem como os rios Taiçupeba, Sorocaba, Baixo Cotia, Grande e Paraíba foram monitorados de abril a setembro de 2017. A toxicidade dos fármacos foi avaliada por meio do monitoramento do crescimento, produção de microcistinas e viabilidade celular da cianobactéria M. aeruginosa LTPNA 08. CAF foi detectada em todas as amostras analisadas, com concentrações que variaram de 6,6 ng.L-1 a 16,47 µg.L-1. No Rio Cotia foram verificadas as maiores concentrações de CAF, FLX e BZF (16,47 µg.L-1; 3,5 ng.L-1 e 322 ng.L-1, respectivamente). A LVX, cujos produtos de biotransformação não foram monitorados, não foi detectada em nenhuma amostra analisada. A concentração de 50 µg.L-1 de FLX inibiu o crescimento da cianobactéria em 82,3% (CE50: 31,4 µg.L-1). Em relação à produção de microcistinas totais, os fármacos inibiram a liberação da fração extracelular para a maior concentração testada ao longo do tempo de monitoramento, embora não tenham demonstrado efeito sobre a viabilidade celular. Sendo assim, considerando-se que fármacos estão presentes nos mananciais monitorados no estado de São Paulo e que a FLX pode causar efeito sobre a M. aeruginosa, os efeitos decorrentes da exposição a concentrações ambientais contínuas e cumulativas de fármacos em corpos d'água devem ser estudados. Além disso, uma vez que a ocorrência destas substâncias e outros contaminantes antropogênicos no ambiente aquático natural é uma questão emergente devido aos efeitos adversos potenciais que estes compostos representam para a vida aquática e os seres humanos, os tipos e níveis destes compostos, que têm um impacto maior na qualidade da água, deve ser constantemente monitorada. Práticas de gestão que investem em saneamento e na redução da descarga de efluentes não tratados, e um plano de proteção de recursos hídricos com o objetivo de garantir a segurança da água seriam medidas essenciais para reduzir o aporte de contaminantes nos corpos d'água do estado de São Paulo
Contamination of water bodies by drugs is a subject of extreme relevance considering related problems such as water scarcity, harmful cyanobacterial blooms and discharge of untreated domestic effluents. Therefore, the aim of this work was to determine the presence of caffeine (CAF), fluoxetine (FLX), levothyroxine (LVX) and bezafibrate (BZF) in springs in the State of São Paulo, and to evaluate the toxicity of these compounds in cyanobacteria Microcystis aeruginosa LTPNA 08. A LC-MS/MS method was developed and validated according to RDC nº 166 of ANVISA to assess the concentration of CAF, FLX, LVX and BZF in environmental samples. Guarapiranga and Billings reservoirs, as well as the Taiçupeba, Sorocaba, Baixo Cotia, Grande and Paraíba rivers were monitored from April to September 2017.The drugs toxicity in M. aeruginosa LTPNA 08 was assessed by monitoring their effects on cyanobacterial growth, microcystins production and cell viabilityby flow cytometry. CAF was detected in all analyzed samples at concentrations ranging from 6.6 ng to 16.47 µg.L-1.Among studied sites, Cotia river showed the highest concentrations of CAF, FLX and BZF (16.47 µg.L-1, 3.5 ng.L-1 and 322 ng.L-1, respectively). LVX, which biotransformation products were not monitored, was not detected in any of the analyzed samples. Regarding the drugs toxicity, 50 µg.L-1 of FLX inhibited the cyanobacterial grow thin 82.3% (EC50 of 31.4 µg.L-1). Although no effect on cell viability was seen by flow cytometry, the highest concentrations of all compounds tested were able to inhibit the release of microcystins. Therefore, considering that some of the drugs monitored showed to be present in water sources in São Paulo State and that FLX affects cyanobacteria M. aeruginosa growth, the effects of continuous and cumulative exposure at environmental drug concentrations of in water bodies should be evaluated. Also, since the occurrence of these substances and other anthropogenic contaminants in the natural aquatic environment is an emerging issue due to the potential adverse effects these compounds pose to aquatic life and humans, thet ypes and levels of these compounds, which have a greater impact on water quality, should be constantly monitored. Management practices investing in sanitation and in reducing discharge of untreated effluents, as well as a plan for water resources protection with the goal of ensuring water security would be essential measures in reducing drugs loading into water bodies situated in São Paulo State
Subject(s)
Pharmaceutical Preparations/analysis , /classification , Microcystis/growth & development , Spectrophotometry/methods , Thyroxine/toxicity , Bezafibrate/toxicity , Caffeine/toxicity , Fluoxetine/toxicity , Flow Cytometry/instrumentationABSTRACT
Hyposalivation is an important clinical side effect related to the use of antidepressants. Fluoxetine hydrochloride is a selective serotonin reuptake inhibitor used in the treatment of depression and anxiety disorders. Nizatidine, an H2 blocker, has a saliva stimulatory effect. The aim of the study was to investigate the histological and immunohistochemical changes resulting from chronic use of fluoxetine in adult rat parotid glands. The possible role of pilocarpine with nizatidine as an additional treatment to fluoxetine was also investigated. Thirty-six adult male albino rats were divided into four groups. Group I was the control group; group II received fluoxetine with tap water; group III received fluoxetine with pilocarpine; and group IV received fluoxetine, pilocarpine, and nizatidine. At the end of the experiment, after 60 days, samples from parotid glands were prepared for light and electron microscopic examination. The optical density of Fas expression and the area percentage of alpha smooth muscle actin [alpha-SMA] and collagen fibers were measured morphometrically and statistically analyzed. Examination of the fluoxetine-treated group revealed disfigurement, coalescence, and vacuolation of the serous acini. The interstitium showed collagen deposition and cellular infiltration. Ultrastructurally, dilated rough endoplasmic reticulum, numerous vacuoles, and granules of low electron density were noticed. Statistically, the area percentage of alpha-SMA and the optical density of Fas immunoreactivity showed a significant increase in group II when compared with other groups. Pilocarpine in group III offered a degree of recovery from the adverse effects of fluoxetine. In contrast, group IV showed a relatively normal parotid structure when fluoxetine was used together with pilocarpine and nizatidine. Fluoxetine adversely affected the histological structure of parotid glands. Nizatidine might be recommended as a combined form of treatment with pilocarpine in cases of hyposalivation caused by fluoxetine
Subject(s)
Male , Animals, Laboratory , Fluoxetine/toxicity , Pilocarpine , Nizatidine , Immunohistochemistry , Rats/immunologyABSTRACT
The aim of the present study was to compare the toxic effects of fluoxetine (F) (8 and 16 mg/kg) and venlafaxine (V) (40 and 80 mg/kg) administered during the third week of pregnancy on early development of rats. Both antidepressants were administered by gavage on pregnancy days 15 to 20 to groups of 10 to 12 animals each. Duration of gestation, food and water consumption, number of live pups and birth weight were recorded. Litters were culled to six pups at birth (day 1) and followed for growth until weaning (day 25). On day 60, a male and a female from each litter were injected with the 5-HT1 agonist, 5-methoxy-N,N-dimethyltryptamine (6 mg/kg, ip) and the serotonergic syndrome was graded. Fluoxetine but not venlafaxine reduced the duration of pregnancy when compared to the control (C) group (F = 21.1 days and C = 21.6 days, mean, P<0.02; maximum = 22 days and minimum = 21 days in both groups). The highest doses of both fluoxetine, 16 mg/kg (F16), and venlafaxine, 80 mg/kg (V80), reduced the food intake of pregnant rats, resulting in different rates of body weight gain during treatment (from pregnancy day 15 to day 20): F16 = 29.0 g, V80 = 28.7 g vs C = 39.5 g (median). Birth weight was influenced by treatment and sex (P<0.05; two-way ANOVA). Both doses of fluoxetine or venlafaxine reduced the body weight of litters; however, the body weight of litters from treated dams was equal to the weight of control litters by the time of weaning. At weaning there was no significant difference in weight between sexes. There was no difference among groups in number of live pups at birth, stillbirths, mortality during the lactation period or in the manifestation of serotonergic syndrome in adult rats. The occurrence of low birth weight among pups born to dams which did not show reduced food ingestion or reduction of body weight gain during treatment with lower doses of fluoxetine or venlafaxine suggests that these drugs may have a deleterious effect on prenatal development when administered during pregnancy. In addition, fluoxetine slightly but significantly affected the duration of pregnancy (about half a day), an effect not observed in the venlafaxine-treated groups