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ANTECEDENTES: Los efectos antiinflamatorios de la dafnetina (7,8-dihidroxicumarina) han sido bien documentados, pero su potencial como agente anticanceroso es controversial y no se ha explorado suficientemente. MATERIAL Y MÉTODOS: En este trabajo se evalúa el efecto antiproliferativo in vitro de la dafnetina en tres líneas celulares mediante ensayos de MTT, así como su efecto antitumoral in vivo en cuatro diferentes tipos de tumores en ratones. RESULTADOS: Con una correlación entre los resultados in vitro e in vivo, los tipos de células probadas tienen diferente sensibilidad al compuesto. Las siguientes líneas celulares están ordenadas de acuerdo con la potencia antiproliferativa in vitro de la dafnetina: células de melanoma B16 (IC50 = 54 ± 2.8 µM) > células de adenocarcinoma de mama MXT (IC50 = 74 ± 6.4 µM) > células de carcinoma de colon C26 (IC50 = 108 ± 7.3 µM). In vivo, la dosis antitumoral óptima de dafnetina fue de 40 mg/kg, y las magnitudes de inhibición fueron las siguientes: tumor B16 (48%) > tumor MXT (40%) > tumor fibrosarcoma S180 (30%) > tumor C26 (20%). CONCLUSIÓN: Los resultados indican que la dafnetina podría tener un impacto como adyuvante para mejorar la efectividad de la quimioterapia convencional.

BACKGROUND: The anti-inflammatory effects of daphnetin (7,8-dihidroxicoumarin) have been well-documented, but the potential of daphnetin as an anticancer agent is controversial and remains insufficiently explored. MATERIAL AND METHODS: In this work, we evaluated the in vitro anti-proliferative effect of daphnetin in three cell lines by 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyltetrazolium bromide assays, as well as its in vivo antitumor effect in four different types of mouse tumor. RESULTS: With a correlation between in vitro and in vivo results, the tested cell types have different sensitivity to the compound. The following cell lines are arranged according to the in vitro anti-proliferative potency of daphnetin: B16 melanoma cells (inhibitory concentrations 50 [IC50] = 54 ± 2.8 µM) > mitoxantrone (MXT) breast adenocarcinoma cells (IC50 = 74 ± 6.4 µM) > C26 colon carcinoma cells (IC50 = 108 ± 7.3 µM). In vivo, the optimal antitumor dose of daphnetin was 40 mg/kg and the magnitudes of inhibition were the following: B16 tumor (48%) > MXT tumor (40%) > S180 fibrosarcoma tumor (30%) > C26 tumor (20%). CONCLUSION: Our results indicate that daphnetin might have an impact as adjuvant to improve the effectiveness of conventional chemotherapy.

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The present study examines the induction of mixed-function oxidase (MFO) enzymes, including CYP content CYP1A (EROD) activity and alcohol dehydrogenase activity (ADH), in an endemic Mexican fish species, the black-fin goodeid Girardinichthys viviparus, exposed to the water of two localities, Lake Texcoco (LTX) and Lake Zumpango, and to the same matrices enriched in polychlorinated biphenyls (PCBs) to simulate the potential toxic effects of sublethal increases in these xenobiotics. Fishes of both sexes born in the laboratory were exposed for 1, 2, 4, 8, and 16 days. Water from the two types of localities of the black-fin goodeid contains MFO inducers. Of the two, the most contaminated is LTX water, which also contains PCBs. EROD activity was higher in all treatments with female compared with male fish. This suggests greater metabolic compromise in female fish as a response to damage caused by these xenobiotics. In this species, CYP induction displayed two patterns that were not always concurrent with higher CYP1A activity. In the enriched matrix system, biotransformation processes were notably altered. Increased ADH may indicate that this enzyme is involved in the biotransformation of PCBs and their metabolites, particularly in male fish, and provides at least a part of reductive power required by the MFO enzymes; however, specific studies are needed to clarify this point.

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The present study examines the relationships between cytochrome P4501A (CYP1A) activity and vitellogenin (VTG) induction in Ameca splendens elicited by a polychlorinated biphenyl (PCB) mixture. Ethoxyresorufin-O-deethylase (EROD) activity, mRNA levels of VTG, and VTG induction were evaluated in male and female fish exposed for 1, 2, 4, 8, and 16 d to a commercial PCB mixture. Polychlorinated biphenyls induced higher EROD in both sexes and this induction was higher in females than in males. Maximum EROD and VTG induction occurred on day 1 in females, while in males these maxima occurred on days 8 and 16. A correlation between EROD and VTG induction was found only in males (p<0.001), and VTG induction was also higher in males than in females (p<0.01). Exposure to PCBs elicited increases in VTG expression and induction over time in males, while in females these decreased at the end of the exposure period. Deficiencies in the feedback mechanisms of male A. splendens exposed in the wild to xenoestrogens such as PCBs have probably contributed to alter the sex ratio of wild populations of this species.

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Girardinichthys viviparus is a Mexican endangered endemic fish species living only in Lake Texcoco (LTX), one of two extant type localities for this species. The other type locality is Lake Zumpango (LZ). LTX and LZ are fed by wastewater treated at secondary level that contains several endocrine disrupting chemicals. Our goal was to assess the estrogenic and anti-estrogenic effects elicited in G. viviparus by water from the two type localities and by these same matrices enriched with PCBs in order to understand potential damage due to increased xenobiotic levels. Estrogenic and anti-estrogenic effects were evaluated in vitro by E-screen assay in MCF-7 cells and cytotoxicity by MTT assay. PCBs were quantified in type localities. In vivo vitellogenin (VTG) induction was determined by a hybrid ELISA in adult laboratory-born fish exposed during 1, 2, 4, 8 and 16 days to LTX or LZ water in static exposure systems, and by the same matrices enriched with PCBs. We found PCBs only in LTX, but the water from both type localities elicit estrogenic and anti-estrogenic effects in vitro. Cytotoxicity was not observed in MCF-7 cells exposed to LTX or LZ water. VTG induction was higher with LTX water than with LZ water; also the response of males was greater than in females. In the PCB-enriched matrices, VTG induction in both sexes exposed to LTX water was reduced compared to un-enriched matrices. Thus, the sublethal increases in PCB levels may be hazardous to both sexes since they are linked probably to hepatotoxicity.

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