70 resultados para CYP1A1


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Induction of cytochrome P4501A1 (CYP1A1) in the hepatoma Hepa1c1c7 cell line results in an elevation in the excretion rate of 8-oxoguanine (oxo8Gua), a biomarker of oxidative DNA damage and the major repair product of 8-oxo-2'-deoxyguanosine (oxo8dG) residues in DNA. Treatment of this cell line with 2,3,7,8-tetrachloro-p-dibenzodioxin (TCDD), a nonmetabolized environmental contaminant, and indolo(3,2-b)carbazole (ICZ), a metabolite of a natural pesticide found in cruciferous vegetables, is shown to both induce CYP1A1 activity and elevate the excretion rate of oxo8Gua; 7,8-benzoflavone (7,8-BF or alpha-naphthoflavone), an inhibitor of CYP1A1 activity and an antagonist of the aryl hydrocarbon (Ah) receptor, reduced the excretion rate of oxo8Gua. The essential role of Ah-receptor, which mediates the induction of CYP1A1, is shown by the inability of TCDD to induce CYP1A1 and to increase excretion of oxo8Gua in Ah receptor-defective c4 mutant cells. While there was a significant 7.0-fold increase over 2 days in the excretion rate of oxo8Gua into the growth medium of TCDD-treated Hepa1c1c7 cells compared to control, no significant increase was detected in the steady-state level of oxo8dG in the DNA presumably due to efficient DNA repair. Thus, the induction of CYP1A1 appears to lead to a leak of oxygen radicals and consequent oxidative DNA damage that could lead to mutation and cancer.

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Cytochrome P450 1A2 (CYP1A2) is a predominantly hepatic enzyme known to be important in the metabolism of numerous foreign chemicals of pharmacologic, toxicologic, and carcinogenic significance. CYP1A2 substrates include aflatoxin B1, acetaminophen, and a variety of environmental arylamines. To define better the developmental and metabolic functions of this enzyme, we developed a CYP1A2-deficient mouse line by homologous recombination in embryonic stem cells. Mice homozygous for the targeted Cyp1a2 gene, designated Cyp1a2(-/-), are completely viable and fertile; histologic examination of 15-day embryos, newborn pups, and 3-week-old mice revealed no abnormalities. No CYP1A2 mRNA was detected by Northern blot analysis. Moreover, mRNA levels of Cyp1a1, the other gene in the same subfamily, appear unaffected by loss of the Cyp1a2 gene. Because the muscle relaxant zoxazolamine is a known substrate for CYP1A2, we studied the Cyp1a2(-/-) genotype by using the zoxazolamine paralysis test: the Cyp1a2(-/-) mice exhibited dramatically lengthened paralysis times relative to the Cyp1a2(+/+) wild-type animals, and the Cyp1a2(+/-) heterozygotes showed an intermediate effect. Availability of a viable and fertile CYP1A2-deficient mouse line will provide a valuable tool for researchers wishing to define the precise role of CYP1A2 in numerous metabolic and pharmacokinetic processes.

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Objective: The Ile462Val substitution in the cytochrome P450 1A1 gene (CYP1A1) results in increased enzymatic activity. Preliminary data suggesting a link between this polymorphism and lung cancer risk in Caucasians are inconsistent, reflecting small sample sizes and the relatively low frequency of the variant. Methods: The data set consisted of 1050 primary non-small cell lung cancer cases and 581 controls, a large homogenous population designed specifically to address previous inconsistencies. Patients were genotyped using a PCR-RFLP technique. Results: Carriers of the valine allele, CYP1A1*2C, (Ile/Val or Val/Val genotypes) were significantly over-represented in non-small cell lung cancer compared to controls (OR=1.9; 95% CI=1.2-2.9; p=0.005) when adjusted for confounders, particularly in women (OR=4.6; 95% CI=1.7-12.4; p=0.003). The valine variant was statistically significantly over-represented in cases of lung cancer younger than the median age (64 years) (OR=2.5; 95% CI=1.3-4.8; p=0.005) and cases with less than the median cumulative tobacco-smoke exposure (46 pack-years) (OR=2.4; 95% CI=1.3-4.7; p=0.007). Conclusions: These new data establish an association between the CYP1A1 Ile462Val polymorphism and the risk of developing non-small cell lung cancer, especially among women.

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Although cytosolic glutathione S-transterase (GST) enzymes occupy a key position in biological detoxification processes, two of the most relevant human isoenzymes. GST1-1 and GSTM1-1, are genetically deleted (non-functional alleles GSTT1*0 and GsTM1*0) in a high percentage of the human population, with major ethnic differences. The structures of the GSTT and GSTM gene areas explain the underlying genetic processes. GSTT1-1 is highly conserved during evolution and plays a major role in phase-II biotransformation of a number of drugs and industrial chemicals. e.g. cytostatic drugs, hydrocarbons and halogenated hydrocarbons. GSTM1-1 is particularly relevant in the deactivation of carcinogenic intermediates of polycyclic aromatic hydrocarbons. Several lines of evidence Suggest that hGSTT1-1 and/or hGSTM1-1 play a role in the deactivation of reactive oxygen species that are likely to be involved in cellular processes of inflammation, ageing and degenerative diseases. There is cumulating evidence that combinations of the GSTM1*0 state with other genetic traits affecting the metabolism of carcinogens (CYP1A1, GSTP1) may predispose the aero-digestivc tract and lung, especially in smokers, to a higher risk of cancer. The GSTM1*0 status appears also associated with a modest increase in the risk of bladder cancer, consistent with a GSTM1 interaction with carcinogenic tobacco smoke constituents. Both human GST deletions, although largely counterbalanced by overlapping substrate affinities within the GST superfamily, have consequences when the organism comes into contact with distinct man-made chemicals. This appears relevant in industrial toxicology and in drug metabolism.

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Brazil is among the largest cashew nut producers of the world. However, the roasting process is still carried out artisanally, especially in the Brazilian semiarid region. In face of this occupational problem, the aim of this study was to perform a physical-chemical characterization of the particulate matter (PM) emitted by the roasting of cashew nuts, as well as to determine the occupational risk and molecular mechanisms associated. The most evident PM characteristics were the prevalence of fine particles, typical biomass burning morphologies such as tar ball and the presence of the elements K, Cl, S, Ca and Fe. In addition, atmospheric modeling analyses suggest that these particles can reach neighboring regions of the emission source. Polycyclic aromatic hydrocarbons (PAHs) with carcinogenic potential, such as benzo[a]pyrene, dibenz[a,h]anthracene, benzo[a]anthracene, benzo[b]fluoranthene, chrysene, benzo[k]fluoranthene, indeno[1,2,3-c,d]pyrene and benzo[j]fluoranthene were the most abundant PAHs found in the two air monitoring campaigns. Among the identified oxy-PAH the benzanthrone (7H-benz[d,e]anthracen-7-one) had the highest concentration and the evaluation of lifetime cancer risk showed an increase of 12 to 37 cases of cancer for every 10,000 exposed people. Chemical analysis of roasted cashew nuts identified the PAHs: phenanthrene, benzo[g,h,i]perylene, pyrene and benzo[a]pyrene, besides the 3-pentadecilfenol allergen (urushiol analogue) as prevalent. Occupational exposure to PAHs was confirmed by the increase of urinary 1-hydroxypyrene levels and genotoxic effects were evidenced by the increase on micronuclei and nuclear bud frequency in exfoliated buccal mucosa cells among the exposed workers. Other biomarkers of effects such as karyorrhexis, pyknotic, karyolytic, condensed chromatin and binucleated cells also have their frequencies increased when compared to an unexposed control group. The investigation of the molecular mechanisms associated with the PM organic extract showed cytotoxicity in human lung cell lines (A549) at concentrations ≥ 4 nM BaPeq. Using non-cytotoxic doses the extract was able to activate proteins involved in the DNA damage response pathway (Chk1 and p53). Moreover, the specific contribution of the four most representative PAHs in the cashew nut roasting sample showed that benzo[a]pyrene was the most efficient to activate Chk1 and p53. Finally, the organic extract was able to increase persistently the mRNA expression involved in the PAHs metabolism (CYP1A1 and CYP1B1), inflammatory response (IL-8 and TNF-α) and cell cycle arrest (CDKN1A) for DNA repair (DDB2). The high PM concentrations and its biological effects associated warn of the serious harmful effects of artisanal cashew nut roasting and urgent actions should be taken to the sustainable development of this activity.

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Brazil is among the largest cashew nut producers of the world. However, the roasting process is still carried out artisanally, especially in the Brazilian semiarid region. In face of this occupational problem, the aim of this study was to perform a physical-chemical characterization of the particulate matter (PM) emitted by the roasting of cashew nuts, as well as to determine the occupational risk and molecular mechanisms associated. The most evident PM characteristics were the prevalence of fine particles, typical biomass burning morphologies such as tar ball and the presence of the elements K, Cl, S, Ca and Fe. In addition, atmospheric modeling analyses suggest that these particles can reach neighboring regions of the emission source. Polycyclic aromatic hydrocarbons (PAHs) with carcinogenic potential, such as benzo[a]pyrene, dibenz[a,h]anthracene, benzo[a]anthracene, benzo[b]fluoranthene, chrysene, benzo[k]fluoranthene, indeno[1,2,3-c,d]pyrene and benzo[j]fluoranthene were the most abundant PAHs found in the two air monitoring campaigns. Among the identified oxy-PAH the benzanthrone (7H-benz[d,e]anthracen-7-one) had the highest concentration and the evaluation of lifetime cancer risk showed an increase of 12 to 37 cases of cancer for every 10,000 exposed people. Chemical analysis of roasted cashew nuts identified the PAHs: phenanthrene, benzo[g,h,i]perylene, pyrene and benzo[a]pyrene, besides the 3-pentadecilfenol allergen (urushiol analogue) as prevalent. Occupational exposure to PAHs was confirmed by the increase of urinary 1-hydroxypyrene levels and genotoxic effects were evidenced by the increase on micronuclei and nuclear bud frequency in exfoliated buccal mucosa cells among the exposed workers. Other biomarkers of effects such as karyorrhexis, pyknotic, karyolytic, condensed chromatin and binucleated cells also have their frequencies increased when compared to an unexposed control group. The investigation of the molecular mechanisms associated with the PM organic extract showed cytotoxicity in human lung cell lines (A549) at concentrations ≥ 4 nM BaPeq. Using non-cytotoxic doses the extract was able to activate proteins involved in the DNA damage response pathway (Chk1 and p53). Moreover, the specific contribution of the four most representative PAHs in the cashew nut roasting sample showed that benzo[a]pyrene was the most efficient to activate Chk1 and p53. Finally, the organic extract was able to increase persistently the mRNA expression involved in the PAHs metabolism (CYP1A1 and CYP1B1), inflammatory response (IL-8 and TNF-α) and cell cycle arrest (CDKN1A) for DNA repair (DDB2). The high PM concentrations and its biological effects associated warn of the serious harmful effects of artisanal cashew nut roasting and urgent actions should be taken to the sustainable development of this activity.

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Avec l’ère industrielle sont venus les polluants environnementaux. Ils sont de plus en plus pointés du doigt pour une variété d’effets indésirables en particulier pour leur potentiel à affecter la santé humaine. Les pesticides font partie de ces polluants et leurs usages ne font que croître depuis une vingtaine d’années. Ces produits qui servent à améliorer la production agricole en éliminant les pestes qui ravagent les récoltes sont souvent peu étudiés à long terme avant d’être homologués. L’effet perturbateur au niveau cellulaire et les effets à long terme de ces pesticides sont peu connus. Pour ce projet de maîtrise, nous avons observé l’effet de deux pesticides, l’imidaclopride et l’acide 2-methyl-4-chlorophenoxyacetic (MCPA), sur les voies de signalisation du récepteur à la dioxine (AhR) et du récepteur aux androgènes (AR). L’imidaclopride est un insecticide de la famille des néonicotinoïdes, une classe de plus en plus utilisée. Ce pesticide est surtout connu pour être en lien avec le déclin des colonies d’abeilles depuis une décennie. Le MCPA est un des herbicides les plus utilisés au Québec, il est persistant et souvent retrouvé dans les eaux de la province. Nous avons traité des cellules du cancer du sein et des cellules du cancer de la prostate avec ces pesticides et nous avons vérifié si leur présence perturbait les deux voies de signalisation cellulaire à l’étude. Le récepteur AhR est un facteur de transcription activé par un ligand. Le TCDD, une dioxine, est le meilleur ligand exogène connu à ce jour de ce récepteur. Par contre, ses ligands naturels, des dérivés du tryptophane ou des facteurs de virulence de bactéries, l’activent de façon beaucoup moins forte. Lors de l’activation de la voie AhR, les gènes CYP1A1 et CYP1B1 sont transcrits et codent pour des enzymes du cytochrome P450 qui transforment les ligands en produits plus facilement éliminables. Dans un contexte où de l’œstradiol (E2) est présent dans les cellules, il y a une interaction croisée entre le récepteur à l’œstrogène (ER) et le récepteur AhR, qui fait en sorte que l’expression de CYP1A1 est réprimée. Cela se traduit en un ratio d’enzyme CYP1A1 à CYP1B1 différent qui pourrait augmenter la possibilité d’une accumulation de métabolites génotoxiques. En effet, CYP1B1 hydroxyle le ligand d’AhR mais aussi l’œstradiol en 4-hydroxyœstradiol (4-OHE), dont l’accumulation peut amener des mutations dans l’ADN alors que l’enzyme CYP1A1 l’hydroxyle en 2-hydroxyœstradiol (2-OHE), qui n’as aucun effet néfaste répertorié sur la cellule. Dans les cellules du cancer du sein, le MCPA appliqué en champs induisait fortement l’expression de CYP1B1 comparable à l’échantillon traité au témoin positif (TCDD), alors que CYP1A1 l’était que très légèrement par rapport au témoin non-traité. Au niveau protéique, CYP1A1 n’était qu’exprimée dans le témoin positif (TCDD) et ce, en quantité moindre lorsqu’il y avait présence d’œstradiol. CYP1B1 était fortement exprimée dans l’échantillon de TCDD, ce qui était attendu, mais aussi dans tous les échantillons traités au MCPA de NuFarm. Ces effets ne sont pas notés avec l’ingrédient actif du MCPA. La présence d’un ou plusieurs autres produits ajoutés dans le MCPA de la compagnie NuFarm en combinaison avec l’ingrédient actif pourrait activer la voie de signalisation d’AhR et causer ce débalancement dans l’expression des gènes CYP1A1 et CYP1B1. Nos résultats indiquent que plusieurs concentrations de l’ingrédient actif de l’imidaclopride ne perturbe pas les voies cellulaires d’AhR ni AR, alors que, le MCPA perturbe ces deux voies cellulaires. Par contre, c’est seulement celui produit par la compagnie NuFarm qui est utilisé en champs. Cette formulation appliquée en terrain agricole inclut l’ingrédient actif ainsi que les antigels, les surfactants et les adjuvants qui permettent au produit d’être plus efficace. L’ingrédient actif du MCPA seul n’affectait pas les deux voies. Le récepteur aux androgènes (AR) est aussi un facteur de transcription qui se lie à l’ADN afin de réguler l’expression des gènes et il est particulièrement important pour le développement et le maintien du phénotype masculin. Depuis une vingtaine d’années, des problèmes de baisse de libido et de fertilité s’accentuent dans notre société et semblent être reliés à la baisse de testostérone des hommes (Travison et al. 2007). Cette molécule est d’ailleurs un des deux ligands du récepteur AR, le deuxième étant la 5-dihydrotestostérone (DHT). Le facteur environnemental plutôt que le mode de vie semble être un facteur déterminant dans l’étude qui portait sur ce déclin. Les pesticides ont déjà été soupçonnés pour avoir un potentiel anti-androgénique, mais aucune étude ne fait un lien de causalité direct. Dans le projet de maitrise présenté dans ce document, l’expression des gènes marqueurs PSA (antigène spécifique de la prostate) et PCA3 (antigène du cancer de la prostate) a été quantifiée pour savoir si les pesticides ont un effet perturbateur sur la voie du récepteur AR. Dans les cellules du cancer de la prostate, l’expression de PSA et PCA3 était semblable au non-traité dans l’échantillon traité au MCPA (NuFarm), et ce, même après l’ajout de DHT, qui active l’expression de ces deux gènes. Cette fois-ci, l’ingrédient actif seul faisait en sorte que les deux gènes marqueurs étaient moins exprimés lors de l’ajout de la DHT, par rapport au témoin. Il semblerait que l’ingrédient actif est à la base de ce changement d’expression de nos gènes marqueurs. Donc, le MCPA pourrait avoir un effet anti-androgénique dans les cellules du cancer de la prostate. Donc, le MCPA est un pesticide qui affecte les voies de signalisation cellulaires AhR et AR. Il est particulier de noter que le pesticide appliqué en champ perturbe nettement plus les voies cellulaires. Il sera important de continuer à étudier les effets des pesticides sur l’homme au niveau cellulaire et de comprendre comment ils pourraient contribuer au développement du cancer.

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Microplastics are present in marine habitats worldwide and may be ingested by low trophic organisms such as fish larvae, with uncertain physiological consequences. The present study aims at assessing the impact of polyethylene (PE 10-45µM) microbeads ingestion in European sea bass (Dicentrarchus labrax) larvae. Fish were fed an inert diet including 0, 104 and 105 fluorescent microbeads per gram from 7 until 43 days post-hatching (dph). Microbeads were detected in the gastrointestinal tract in all fish fed diet incorporating PE. Our data revealed an efficient elimination of PE beads from the gut since no fluorescent was observed in the larvae after 48h depuration. While the mortality rate increased significantly with the amount of microbeads scored per larvae at 14 and 20 dph, only ingestion of the highest concentration slightly impacted mortality rates. Larval growth and inflammatory response through Interleukine-1-beta (IL-1) gene expression were not found to be affected while cytochrome-P450-1A1 (cyp1a1) expression level was significantly positively correlated with the number of microbeads scored per larva at 20 dph. Overall, these results suggest that ingestion of PE microbeads had limited impact on sea bass larvae possibly due to their high potential of egestion

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We compared the effects of a single acute dose, or chronic fetal exposure, to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the male reproductive system of the Wistar(Han) rat. Tissue samples were taken from dams on GD16 and GD21, and from offspring on PND70 and 120. Steady state concentration of TCDD was demonstrated in the chronic study: body burdens were comparable in both studies. Fetal TCDD concentrations were comparable after acute and chronic exposure, and demonstrate more potent toxicity after chronic versus acute dosing. In maternal liver, cytochrome P450 (CYP)1A1 and CYP1A2 RNA were induced. In fetus, there was induction of both CYP1A1 and CYP1A2 RNA at medium and high doses, but inadequate evidence for induction at low dose in either study. The low level induction of CYP1A1 RNA at low dose in fetus argues against AhR activation in fetus as a mechanism of toxicity of TCDD in causing delay in balanopreputial separation, and the greater induction of CYP1A1 RNA in PND70 offspring liver suggests that lactational transfer of TCDD is crucial to this toxicity. These data characterise the maternal and fetal disposition of TCDD, induction of CYP1A1 RNA as a measure of AhR activation, and suggest that lactational transfer of TCDD determines the difference in delay in balanopreputial separation between the two studies.

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2-(4-Amino-3-methylphenyl)-5-fluorobenzothiazole (5F 203) and related compounds are a series of anti-cancer candidate pharmaceuticals (Table 1.), that have been shown to activate the AhR. We show that these compounds are high affinity ligands for the rat AhR, but a quantitative assay for their ability to induce CYP1A1 RNA in H4IIEC3 cells, a measure of activation of the AhR, showed a poor relationship between affinity for the AhR and ability to induce CYP1A1 RNA. 5F 203, an agonist with low potency, was able to antagonise the induction of CYP1A1 RNA by TCDD, while IH 445, a potent agonist, did not antagonise the induction of CYP1A1 RNA by TCDD, and Schild analysis confirmed 5F 203 to be a potent antagonist of the induction of CYP1A1 RNA by TCDD in H4IIEC3 cells. In contrast, several benzothiazoles show potent induction of CYP1A1 RNA in human MCF-7 cells, and 5F 203 is unable to detectably antagonise the induction of CYP1A1 RNA in MCF-7 cells, showing a species difference in antagonism. Evaluation of the antiproliferative activity of benzothiazoles showed that the ability to agonise the AhR correlated with growth inhibition both in H4IIEC3 cells for a variety of benzothiazoles, and between H4IIEC3 and MCF-7 cells for 5F 203, suggesting an important role of agonism of the AhR in the anti-proliferative activity of benzothiazoles.