979 resultados para Co-exposure


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The most common scenario in occupational settings is the co-exposure to several risk factors. This aspect has to be considered in the risk assessment process because can alter the toxicity and the health effects when dealing with a co-exposure to two or more chemical agents. A study was developed aiming to elucidate if there is occupational co-exposure to aflatoxin B1 (AFB1) and ochratoxin (OTA) in Portuguese swine production. To assess occupational exposure to both mycotoxins, a biomarker of internal dose was used. The same blood samples from workers of seven swine farms and controls were consider to measure AFB1 and OTA. Twenty one workers (75%) showed detectable levels of AFB1 with values ranging from <1 ng/ml to 8.94 ng/ml and with significantly higher concentration when compared with controls. In the case of OTA, there wasn't found a statistical difference between workers and controls and the values for workers group ranged from 0.34 ng/ml to 3.12 ng/ml and 1.76 ng/ml to 3.42 ng/ml for control group. The results suggest that occupational exposure to AFB1 occurs. However, in the case of OTA results, seems that food consumption plays an important role in both groups exposure. The results claim attention for the possible implications on health of this co-exposure.

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Persistence of HIV-1 reservoirs within the Central Nervous System (CNS) remains a significant challenge to the efficacy of potent anti-HIV-1 drugs. The primary human Brain Microvascular Endothelial Cells (HBMVEC) constitutes the Blood Brain Barrier (BBB) which interferes with anti-HIV drug delivery into the CNS. The ATP binding cassette (ABC) transporters expressed on HBMVEC can efflux HIV-1 protease inhibitors (HPI), enabling the persistence of HIV-1 in CNS. Constitutive low level expression of several ABC-transporters, such as MDR1 (a.k.a. P-gp) and MRPs are documented in HBMVEC. Although it is recognized that inflammatory cytokines and exposure to xenobiotic drug substrates (e.g HPI) can augment the expression of these transporters, it is not known whether concomitant exposure to virus and anti-retroviral drugs can increase drug-efflux functions in HBMVEC. Our in vitro studies showed that exposure of HBMVEC to HIV-1 significantly up-regulates both MDR1 gene expression and protein levels; however, no significant increases in either MRP-1 or MRP-2 were observed. Furthermore, calcein-AM dye-efflux assays using HBMVEC showed that, compared to virus exposure alone, the MDR1 mediated drug-efflux function was significantly induced following concomitant exposure to both HIV-1 and saquinavir (SQV). This increase in MDR1 mediated drug-efflux was further substantiated via increased intracellular retention of radiolabeled [3H-] SQV. The crucial role of MDR1 in 3H-SQV efflux from HBMVEC was further confirmed by using both a MDR1 specific blocker (PSC-833) and MDR1 specific siRNAs. Therefore, MDR1 specific drug-efflux function increases in HBMVEC following co-exposure to HIV-1 and SQV which can reduce the penetration of HPIs into the infected brain reservoirs of HIV-1. A targeted suppression of MDR1 in the BBB may thus provide a novel strategy to suppress residual viral replication in the CNS, by augmenting the therapeutic efficacy of HAART drugs.

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Introduction - Occupational exposures are characterized by being complex and associated to co-exposure to several contaminants by different exposure routes. Even if exposure occurs to only a chemical agent, it can have different exposure routes and can result in different health effects. The waste management setting is recognized by the presence of several chemical and biologic agents in the workplaces. Recently, it was reported occupational exposure to Aflatoxin B1 (AFB1) in one Portuguese waste management industry. However, data regarding to fungal burden showed that exposure to other mycotoxins should be expected. Aim of the study - The aim of the present work was to know if workers from this waste management industry were exposed to other mycotoxins besides AFB1.

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Despite considerable advances in reducing the production of dioxin-like toxicants in recent years, contamination of the food chain still occasionally occurs resulting in huge losses to the agri-food sector and risk to human health through exposure. Dioxin-like toxicity is exhibited by a range of stable and bioaccumulative compounds including polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs), produced by certain types of combustion, and man-made coplanar polychlorinated biphenyls (PCBs), as found in electrical transformer oils. While dioxinergic compounds act by a common mode of action making exposure detection biomarker based techniques a potentially useful tool, the influence of co-contaminating toxicants on such approaches needs to be considered. To assess the impact of possible interactions, the biological responses of H4IIE cells to challenge by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in combination with PCB-52 and benzo-a-pyrene (BaP) were evaluated by a number of methods in this study. Ethoxyresorufin-O-deethylase (EROD) induction in TCDD exposed cells was suppressed by increasing concentrations of PCB-52, PCB-153, or BaP up to 10 mu M. BaP levels below 1 mu M suppressed TCDD stimulated EROD induction, but at higher concentrations, EROD induction was greater than the maximum observed when cells were treated with TCDD alone. A similar biphasic interaction of BaP with TCDD co-exposure was noted in the AlamarBlue assay and to a lesser extent with PCB-52. Surface enhanced laser desorption/ionization-time of flight mass spectrometry (SELDI-TOF) profiling of peptidomic responses of cells exposed to compound combinations was compared. Cells co-exposed to TCDD in the presence of BaP or PCB-52 produced the most differentiated spectra with a substantial number of non-additive interactions observed. These findings suggest that interactions between dioxin and other toxicants create novel, additive, and non-additive effects, which may be more indicative of the types of responses seen in exposed animals than those of single exposures to the individual compounds.

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BACKGROUND: Aflatoxin and fumonisin are toxic food contaminants. Knowledge about effects of their exposure and co-exposure on child growth is inadequate.

OBJECTIVE: To investigate the association between child growth and aflatoxin and fumonisin exposure in Tanzania.

METHODS: A total of 166 children were recruited at 6 to 14 months of age and studied at recruitment, and at the sixth and twelfth month following recruitment. Blood and urine samples were collected and analysed for plasma aflatoxin albumin adducts (AF-alb) using ELISA, and urinary fumonisin B1 (UFB1) using LC-MS, respectively. Anthropometric measurements were taken and growth index Z-scores were computed.

RESULTS: AF-alb geometric mean concentrations (95% confidence intervals) were 4.7 (3.9, 5.6), 12.9 (9.9, 16.7) and 23.5 (19.9, 27.7) pg/mg albumin at recruitment, six months, and 12 months from recruitment, respectively. At these respective sampling times, geometric mean UFB1 concentrations (95% CI) were 313.9 (257.4, 382.9), 167.3 (135.4, 206.7) and 569.5 (464.5, 698.2) pg/mL urine, and the prevalence of stunted children were 44%, 55% and 56%, respectively. UFB1 concentrations at recruitment were negatively associated with length for age Z-scores (LAZ) at six months (p = 0.016) and at 12 months from recruitment (p = 0.014). The mean UFB1 of the three sampling times (at recruitment, at six and 12 months from recruitment) in each child was negatively associated with LAZ (p < 0.001) and length velocity (p = 0.004) at 12 months from recruitment. The negative association between AF-alb and child growth did not reach statistical significance.

CONCLUSIONS: Exposure to fumonisin alone, or co-exposure with aflatoxins may contribute to child growth impairment.

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flatoxins are fungal toxins that possess acute life threatening toxicity, carcinogenic properties and other potential chronic adverse effects. Dietary exposure to aflatoxins is considered a major public health concern, especially for subsistence farming communities in sub-Saharan Africa and South Asia, where dietary staple food crops such as groundnuts and maize are often highly contaminated with aflatoxin due to hot and humid climates and poor storage, together with low awareness of risk and lack of enforcement of regulatory limits. Biomarkers have been developed and applied in many epidemiological studies assessing aflatoxin exposure and the associated health effects in these high-risk population groups. This review discusses the recent epidemiological evidence for aflatoxin exposure, co-exposure with other mycotoxins and associated health effects in order to provide evidence on risk assessment, and highlight areas where further research is necessary. Aflatoxin exposure can occur at any stage of life and is a major risk factor for hepatocellular carcinoma, especially when hepatitis B infection is present. Recent evidence suggests that aflatoxin may be an underlying determinant of stunted child growth, and may lower cell-mediated immunity, thereby increasing disease susceptibility. However, a causal relationship between aflatoxin exposure and these latter adverse health outcomes has not been established, and the biological mechanisms for these have not been elucidated, prompting further research. Furthermore, there is a dearth of information regarding the health effects of co-exposure to aflatoxin with other mycotoxins. Recent developments of biomarkers provide opportunities for important future research in this area.

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Tese de doutoramento, Farmácia (Toxicologia), Universidade de Lisboa, Faculdade de Farmácia, 2014

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Characterize ethylbenzene and xylene air concentrations, and explore the biological exposure markers (urinary t,t-muconic acid (t,t-MA) and unmetabolized toluene) among petroleum workers offshore. Offshore workers have increased health risks due to simultaneous exposures to several hydrocarbons present in crude oil. We discuss the pooled benzene exposure results from our previous and current studies and possible co-exposure interactions. BTEX air concentrations were measured during three consecutive 12-h work shifts among 10 tank workers, 15 process operators, and 18 controls. Biological samples were collected pre-shift on the first day of study and post-shift on the third day of the study. The geometric mean exposure over the three work shifts were 0.02 ppm benzene, 0.05 ppm toluene, 0.03 ppm ethylbenzene, and 0.06 ppm xylene. Benzene in air was significantly correlated with unmetabolized benzene in blood (r = 0.69, p < 0.001) and urine (r = 0.64, p < 0.001), but not with urinary t,t-MA (r = 0.27, p = 0.20). Toluene in air was highly correlated with the internal dose of toluene in both blood (r = 0.70, p < 0.001) and urine (r = 0.73, p < 0.001). Co-exposures were present; however, an interaction of metabolism was not likely at these low benzene and toluene exposures. Urinary benzene, but not t,t-MA, was a reliable biomarker for benzene at low exposure levels. Urinary toluene was a useful biomarker for toluene exposure. Xylene and ethylbenzene air levels were low. Dermal exposure assessment needs to be performed in future studies among these workers.

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Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

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Mycotoxins are an important group of naturally occurring substances known to contaminate a huge variety of agricultural products, feed and food commodities. The main concern is their widespread presence and toxic effects on humans and animals as they have been described as cytotoxic, nephrotoxic, hepatotoxic, teratogenic, immunosuppressive, mutagenic and/or carcinogenic. However, until now, risk assessments and regulations have usually been performed on individual mycotoxins despite humans and animals are being frequently exposed to a multitude of mycotoxins simultaneously. Moreover, even though some exposures through inhalation and dermal contact may potentially occur, only oral ingestion has been considered as the sole route of exposure in all the evaluations. However, more recent studies have also demonstrated airborne exposure to mycotoxins in different occupational settings with emphasis on agricultural professions. In these cases, skin contact with mold-infested substrates and inhalation of spore-borne toxins are the most important sources of exposure. Still, mycotoxins are not normally recongnize as na occupational hazard and exposure is different from the one ocurring by food intake. In this case, exposure is charaterized to be acute and simultaneous to other mycotoxins and also to fungi and dust. All these features increase the challenge implicated in the risk assessment process. Some topics will be presented and discussed in detailed such as: What occupational settings should be consider in this case; possible exposure routes; exposure characterization; how to assess exposure; co-exposure; aggregate exposure and cumulative risk assessment.

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It is nowadays recognized that the risk of human co-exposure to multiple mycotoxins is real. In the last years, a number of studies have approached the issue of co-exposure and the best way to develop a more precise and realistic assessment. Likewise, the growing concern about the combined effects of mycotoxins and their potential impact on human health has been reflected by the increasing number of toxicological studies on the combined toxicity of these compounds. Nevertheless, risk assessment of these toxins, still follows the conventional paradigm of single exposure and single effects, incorporating only the possibility of additivity but not taking into account the complex dynamics associated to interactions between different mycotoxins or between mycotoxins and other food contaminants. Considering that risk assessment is intimately related to the establishment of regulatory guidelines, once the risk assessment is completed, an effort to reduce or manage the risk should be followed to protect public health. Risk assessment of combined human exposure to multiple mycotoxins thus poses several challenges to scientists, risk assessors and risk managers and opens new avenues for research. This presentation aims to give an overview of the different challenges posed by the likelihood of human co-exposure to mycotoxins and the possibility of interactive effects occurring after absorption, towards knowledge generation to support a more accurate human risk assessment and risk management. For this purpose, a physiologically-based framework that includes knowledge on the bioaccessibility, toxicokinetics and toxicodynamics of multiple toxins is proposed. Regarding exposure assessment, the need of harmonized food consumption data, availability of multianalyte methods for mycotoxin quantification, management of left-censored data and use of probabilistic models will be highlight, in order to develop a more precise and realistic exposure assessment. On the other hand, the application of predictive mathematical models to estimate mycotoxins’ combined effects from in vitro toxicity studies will be also discussed. Results from a recent Portuguese project aimed at exploring the toxic effects of mixtures of mycotoxins in infant foods and their potential health impact will be presented as a case study, illustrating the different aspects of risk assessment highlighted in this presentation. Further studies on hazard and exposure assessment of multiple mycotoxins, using harmonized approaches and methodologies, will be crucial towards an improvement in data quality and contributing to holistic risk assessment and risk management strategies for multiple mycotoxins in foodstuffs.

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Fumonisin B1 (FB1) is a mycotoxin produced by the fungus Fusarium verticillioides, which commonly infects corn and other agricultural products. Fusarium species can also be found in moisture-damaged buildings, and therefore there may also be human exposure to Fusarium mycotoxins, including FB1. FB1 affects the metabolism of sphingolipids by inhibiting the enzyme ceramide synthase. It is neuro-, hepato- and nephrotoxic, and it is classified as possibly carcinogenic to humans. This study aimed to clarify the mechanisms behind FB1-induced neuro- and immunotoxicity. Four neural and glial cell lines of human, rat and mouse origin were exposed to graded doses of FB1 and the effects on the production of reactive oxygen species, lipid peroxidation, intracellular glutathione levels, cell viability and apoptosis were investigated. Furthermore, the effects of FB1, alone or together with lipopolysaccharide (LPS), on the mRNA and protein expression levels of different cytokines and chemokines were studied in human dendritic cells (DC). FB1 induced oxidative stress and cell death in all cell lines studied. Generally, the effects were only seen after prolonged exposure at 10 and 100 µM of FB1. Signs of apoptosis were also seen in all four cell lines. The sensitivities of the cell lines used in this study towards FB1 may be classified as human U-118MG glioblastoma > mouse GT1-7 hypothalamic > rat C6 glioblastoma > human SH-SY5Y neuroblastoma cells. When comparing cell lines of human origin, it can be concluded that glial cells seem to be more sensitive towards FB1 toxicity than those of neural origin. After exposure to FB1, significantly increased levels of the cytokine interferon-γ (IFNγ) were detected in human DC. This observation was further confirmed by FB1-induced levels of the chemokine CXCL9, which is known to be regulated by IFNγ. During co-exposure of DC to both LPS and FB1, significant inhibitions of the LPS-induced levels of the pro-inflammatory cytokines interleukin-6 (IL-6) and IL-1β, and their regulatory chemokines CCL3 and CCL5 were observed. FB1 can thus affect immune responses in DC, and therefore, it is rather likely that it also affects other types of cells participating in the immune defence system. When evaluating the toxicity potential of FB1, it is important to consider the effects on different cell types and cell-cell interactions. The results of this study represent new information, especially about the mechanisms behind FB1-induced oxidative stress, apoptosis and immunotoxicity, as well as the varying sensitivities of different cell types towards FB1.

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O consumo de tabaco está freqüentemente associado ao consumo de álcool e a maioria dos usuários inicia o uso e abuso destas drogas na adolescência. Como a ansiedade pode ser um fator de risco para a etiologia do uso e da retirada destas drogas, no presente estudo investigamos os efeitos da fumaça do cigarro e/ou exposição ao etanol durante a adolescência nos níveis de ansiedade ao final do período de exposição e em período curto e longo após retirada. Do 30 ao 45 dia de vida pós-natal (PN30-PN45), camundongos Suíços de ambos os sexos foram expostos a fumaça do cigarro gerada a partir da queima de cigarros para pesquisa contendo 1,7mg de nicotina 8 h/dia e/ou ao etanol (2g/kg, 25%, v/v) através de injeção intraperitoneal em dias alternados. Assim foram utilizados 4 grupos experimentais: 1) SMK+ETOH (exposição a fumaça de cigarro e injeção i.p. de etanol); 2) SMK (exposição a fumaça de cigarro e a salina i.p.); 3) ETOH (exposição a ar e injeção i.p. de etanol); 4) VEH (exposição a ar e injeção i.p. salina). Ao final do período de exposição (PN44-45) e durante a retirada de curta (PN49-50) e longa duração (PN74-75) utilizamos o Labirinto em Cruz Elevado (LCE) para avaliar os níveis de ansiedade e o Teste de Campo Aberto (CA) para avaliar os níveis de ansiedade e a atividade locomotora. Ao final do período de exposição, as fêmeas do grupo SMK apresentaram uma resposta ansiolítica no LCE. Esta resposta foi intensificada pela co-exposição ao etanol. A retirada de curto prazo da fumaça do cigarro provocou um efeito ansiogênico. Os machos do grupo ETOH apresentaram um efeito ansiogênico no LCE ao final do período de exposição, no entanto, este efeito não persistiu em um período curto de retirada. Embora nem os efeitos da fumaça de cigarro, nem os efeitos do etanol tenham persistido após um período longo de retirada, os animais do grupo SMK+ETOH apresentaram uma resposta ansiogênica no CA. Assim, nossos resultados sugerem que fêmeas adolescentes são mais susceptíveis aos efeitos ansiolíticos do fumo do tabaco. O efeito mais intenso no grupo SMK+ETOH sugere que as fêmeas co-usam estas drogas para chegar a níveis mais baixos de ansiedade. Além disso, um aumento da ansiedade após um período longo da retirada conjunta do cigarro e do etanol, pode facilitar as recaídas ao uso destas drogas.

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Adolescentes humanos frequentemente associam o fumo do tabaco ao consumo de bebidas alcoólicas. A despeito desta associação, pouco se sabe sobre a neurobiologia básica da coexposição no cérebro adolescente. No presente estudo, avaliamos os efeitos da exposição, que ocorreu do 30 ao 45 dia de vida pós natal (PN30 a PN45), à nicotina e/ou ao etanol durante a adolescência (PN38-45) e da retirada (PN50-57) na memória visuoespacial através do Labirinto Aquático de Morris (LAM: 6 sessões + 1 prova, 3 tentativas/sessão, latência = 2 min), em 4 grupos de camundongos Suíços machos e fêmeas: (1) exposição concomitante à NIC [solução de nicotina free base (50 μg/ml) em sacarina a 2% para beber] e ETOH [solução de etanol (25%, 2 g/kg) injetada i.p. em dias alternados]; (2) exposição à NIC; (3) exposição ao ETOH; (4) veículo (VEH). Uma vez que os resultados comportamentais podem sofrer a interferência de alterações motoras, avaliamos (a) a atividade locomotora no Teste de Campo Aberto (sessão única, 5 min) e (b) a coordenação e o equilíbrio no Teste de Locomoção Forçada sobre Cilindro Giratório (5 tentativas, latência = 2 min). Para os efeitos da exposição à NIC e/ou ao ETOH na eficiência do transporte de aminoácidos excitatórios, avaliamos a captação de [3H] D-aspartato no hipocampo. A expressão do transportador glial GLAST/EAAT1 foi avaliada por Western-blot. Durante a exposição, animais ETOH e NIC+ETOH apresentaram déficits de memória nas sessões de teste e de prova no LAM enquanto, na retirada, os grupos NIC e NIC+ETOH apresentaram prejuízos na retenção. Não houve diferenças significativas entre os grupos de tratamento em nenhum dos parâmetros testados em ambos os testes motores, tanto na exposição quanto na abstinência. Os grupos NIC, ETOH e NIC+ETOH tiveram uma diminuição significativa na captação de [3H] D-aspartato ao final do período de exposição, com uma normalização da atividade dos EAATs na retirada das drogas. O tratamento com NIC e ETOH reduziu ainda a expressão de GLAST/EAAT1 no hipocampo em ambas as idades testadas. O uso de etanol na adolescência causa prejuízos à memória de camundongos, com um efeito negativo mais acentuado quando associado à nicotina. Contudo, a retirada da nicotina apresentou um efeito mandatório nos danos encontrados. Ambas as drogas, isoladamente ou na coexposição, alteram os níveis de atividade e expressão dos EAATs, sugerindo que os resultados bioquímicos estejam implicados nas alterações comportamentais encontradas.

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O Transtorno do Déficit de Atenção e Hiperatividade (TDAH) é uma desordem neurocomportamental caracterizada por graus variados de desatenção, atividade motora excessiva e impulsividade. Sua etiologia não é completamente conhecida, porém, um grande número de evidências sugere que, além de fatores de risco genéticos, a exposição gestacional ao etanol e a altas doses de cafeína contribuem para a manifestação deste transtorno. O etanol, presente na composição de bebidas alcoólicas, e a cafeína, presente na composição de diversas bebidas (refrigerantes, chás, café, e energéticos), alimentos derivados do cacau e medicamentos estão entre as substâncias neuroativas mais consumidas no mundo. Apesar das evidências epidemiológicas do uso combinado de cafeína e etanol por gestantes, as interações entre estas substâncias têm recebido pouca atenção em estudos experimentais. Este fato é particularmente importante visto que alguns estudos apontam que cafeína é capaz de ampliar alguns aspectos importantes da ação de outras substâncias com potencial neurotóxico. Nesse estudo avaliamos os efeitos da co-exposição à cafeína e ao etanol durante o desenvolvimento na atividade locomotora em camundongos adolescentes. Para tanto, camundongos Suíços foram expostos do primeiro dia gestacional até o vigésimo primeiro dia pós-natal (PN21), a solução de cafeína 0,1g/L (Grupo CAF1, 10 ninhadas), a solução de cafeína 0,3g/L (Grupo CAF3, 10 ninhadas) ou tiveram acesso à água potável (Grupo CAF0, 10 ninhadas). Em dias alternados de PN2 a PN8, os animais de cada ninhada receberam uma injeção intraperitoneal de 0,25 l/g de etanol (grupo ETOH25), 0,5 l/g de etanol (grupo ETOH50) ou de solução salina (grupo ETOH0). Em PN30, a atividade locomotora foi avaliada por 15 minutos no teste de Campo Aberto. A análise dos níveis de etanol sérico, realizada em uma amostra independente de animais em PN8, indicou que, para as duas doses de etanol, a alcoolemia dos animais do grupo CAF3 foi significativamente maior do que as dos grupos CAF0 e CAF1, que não diferiram entre si. No teste de campo aberto, apenas os animais expostos ao etanol apresentaram aumento da atividade locomotora. Tanto o grupo ETOH25 quanto o grupo ETOH50 tiveram a atividade maior que o grupo ETOH0. A exposição à cafeína, por si só, não afetou a atividade locomotora dos animais nem potencializou os efeitos do etanol. No grupo CAF3, a atividade locomotora não foi afetada pela exposição ao etanol. Nossos dados confirmam o papel da exposição precoce ao etanol na manifestação da hiperatividade locomotora. Além disso, a exposição à cafeína durante o desenvolvimento pode exercer um papel protetor para a manifestação da hiperatividade locomotora induzida pela exposição precoce ao etanol.