Bioavailability and toxicity of pentachlorophenol in contaminated soil evaluated on coelomocytes of Eisenia andrei (Annelida: Lumbricidae).

Pentachlorophenol (PCP) is widely distributed and highly persistent in soil, and represents a threat to the health of ecosystems. The present study aimed to assess the toxicity and bioavailability of PCP in soils as a function of different aging periods with the attempt to select a good toxicological assay for Eisenia andrei Bouché (Annelida: Lumbricidae). The experiments were performed on soil contaminated with PCP at 15 and 150ppm. After different aging periods (20, 60 and 120 days from spiking), bioavailability and toxicity were evaluated on E. andrei kept for 7 and 14 days in treated soils. The actual bioavailability decreased in relation to the aging for both PCP concentrations. No membrane damage was observed on coelomocytes collected by ethanol extrusion. Modifications in distribution of coelomocyte subpopulations were detected by flow cytometry on samples aged for 60 and 120 days at 150ppm PCP contamination. The reduction of lysosomal membrane stability, measured by neutral red retention time, was observed in all treatments. Worm mortality increased with aging in soils spiked with 150ppm of PCP. In conclusion, aging did not seem to reduce PCP cytotoxicity. This is the first report on in vivo toxicity of PCP evaluated on coelomocytes of E. andrei using different assays.

Influence of mycotoxin zearalenone and its derivatives (alpha and beta zearalenol) on apoptosis and proliferation of cultured granulosa cells from equine ovaries.

BACKGROUND: The mycotoxin zearalenone (ZEA) and its derivatives, alpha and beta-zearalenol (alpha and beta-ZOL), synthesized by genera Fusarium, often occur as contaminants in cereal grains and animal feeds. The importance of ZEA on reproductive disorders is well known in domestic animals species, particularly in swine and cattle. In the horse, limited data are available to date on the influence of dietary exposure to ZEA on reproductive health and on its in vitro effects on reproductive cells. The aim of this study was to evaluate the effects of ZEA and its derivatives, alpha and beta-ZOL, on granulosa cells (GCs) from the ovaries of cycling mares. METHODS: The cell proliferation was evaluated by using the 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyltetrazolium bromide (MTT) test after 3 days exposure at different concentrations of ZEA and its derivatives (from 1 x 10-7 to 0.1 microM). The apoptosis induction was evaluated after 1 day exposure, by DNA analysis using flow cytometry. RESULTS: An increase in cell proliferation with respect to the control was observed in the presence of ZEA at 1 x 10-3 and 1 x 10-4 microM and apoptosis was induced by all mycotoxins at different concentrations. CONCLUSION: The simultaneous presence of apoptosis and proliferation in GC cultures treated with zearalenones could indicate that these mycotoxins could be effective in inducing follicular atresia. These effects of zearalenones may result from both direct interaction with oestrogen-receptors as well as interaction with the enzymes 3alpha (beta)-hydroxysteroid dehydrogenase (HSD), involved in the synthesis and metabolism of endogenous steroid hormones. These cellular disturbances, described for the first time in equine GCs cultured in vitro, could be hypothesized as referred to reproductive failures of unknown ethiology in the mare.

T-2 toxin immunotoxicity on human B and T lymphoid cell lines.

T-2 toxin belongs to a group of mycotoxins synthesized by Fusarium fungi that are widely encountered as natural contaminants in cereals. Human lymphoid cell lines of T (MOLT-4) or B (IM-9) lineage were used to characterize the cytotoxic effects mediated by T-2 at different concentrations (0.1 pg/ml to 1 microg/ml). After 24 h, membrane damage was observed by Trypan blue dye exclusion in IM-9 cells with a 50% cytotoxic concentration (CC50) of 0.2 ng/ml, whereas CC50 for MOLT-4 cells was 0.6 microg/ml (gmicro). At a T-2 concentration of 0.01 microg/ml, apoptosis was seen in MOLT-4 cells by Annexin V binding as early as after 4 h. T-2 toxin determined sustained (48 h) immunosuppression on both cell lines, as evaluated by BrdU and MTT assays. Cytotoxicity appeared to be due to early apoptosis in MOLT-4 cells, as indicated by increased Annexin V binding and activation of caspase-3, and to direct cell membrane damage in IM-9 cells.

Cytotoxicity induced by nivalenol, deoxynivalenol, and fumonisin B1 in the SF-9 insect cell line.

The toxicity of the mycotoxins nivalenol (NIV), deoxynivalenol (DON), and fumonisin B1 (FB1) was studied in the lepidopteran Spodoptera frugiperda (SF-9) cells, by the trypan blue dye-exclusion and 3-(4,5-dimethylthiozole-2-yl)-2,5-biphenyl tetrazolium bromide (MTT) tests, uptake analyses of cytotoxicity, and cell metabolism, respectively. Deoxyribonucleic acid analysis by flow cytometry was used to identify apoptosis and cell cycle distribution. After 48 h of exposure, the MTT and trypan blue dye-exclusion tests indicated that NIV was significantly more toxic than DON, and both were significantly more toxic than FB1. The IC50 (mycotoxin concentration resulting in 50% inhibition of proliferation) values for NIV and DON were 4.5 and 41 microM, and the CC50 (mycotoxin concentration that caused 50% cytotoxicity) values were 9.5 and 45 microM, respectively. At the highest concentration of FB1 (100 microM), there was 80% viability. With the same incubation time, cell cycle distribution showed an arrest of cells in the G0/G1 phase in the presence of NIV (up to 0.3 microM), DON (up to 3 microM), and FB1 (up to 10 microM). Morphological evidence of apoptosis was related to the toxicity of the substances in that the more toxic NIV induced late apoptosis, whereas DON and FB1 produced less-severe morphological changes characteristic of early apoptosis. This study suggests that NIV is more toxic than DON, which in turn is more toxic than FB1. These mycotoxins can modify the normal progression of the cell cycle and induce an apoptotic process.

Cytotoxicity of fungal metabolites to lepidopteran (Spodoptera frugiperda) cell line (SF-9).

The toxicity of sixteen fungal metabolites produced by some entomopathogenic fungi or biological control fungi agents was evaluated on lepidopteran Spodoptera frugiperda (SF-9) cell line by Trypan blue dye exclusion and MTT-colorimetric assay, after 48 h of incubation. No statistical difference was found between IC50values (50% Inhibiting Concentration) and CC50 values (50% Cytotoxicity Concentration) obtained by MTT test and Trypan blue dye exclusion for each fungal metabolite. By MTT assay, the cytotoxicity ranking was fusarenon X (IC50 0.3 microM) = diacetoxyscirpenol (IC50 0.5 microM) = beauvericin (IC50 2.5 microM) = nivalenol (IC50 5.3 microM) = enniatin (IC50 6.6 microM) > or = gliotoxin (IC50 7.5 microM) > zearalenone (IC50 17.5 microM) > deoxynivalenol (IC50 47.6 microM). By Trypan blue dye exclusion the cytotoxicity ranking was fusarenon X (CC50 0.4 microM) = diacetoxyscirpenol (CC50 1.1 microM) beauvericin = (CC50 3.0 microM)=gliotoxin (CC50 4.0 microM) = enniatin (CC50 6.7 microM) > or = nivalenol (CC50 9.5 microM) > zearalenone (CC50 18.3 microM) > deoxynivalenol (CC50 45.0 microM). The comparison with other bioassays showed that the SF-9 insect cell line could represent a further tool to screen for the toxic effects of fungal metabolites especially for beauvericin, gliotoxin, and zearalenone.

Cytotoxic effects of the mycotoxin beauvericin to human cell lines of myeloid origin.

Beauvericin, a cyclic hexadepsipeptide of potential importance to the health of humans and domestic animals, has been reported to exert cytotoxic effects on several mammalian cell types and to induce apoptosis. We investigated the cytotoxicity of this compound to two human cell lines of myeloid origin: the monocytic lymphoma cells U-937 and the promyelocytic leukemia cells HL-60. In some experiments HL-60 cells partially differentiated towards the eosinophilic phenotype were also used. Cultures of U-937 cells and HL-60 cells in stationary phase were exposed to beauvericin at concentrations ranging from 100 nM to 300 microM for periods of time of 4 and 24h, respectively. The effects of beauvericin on cell viability were assessed by the Trypan blue exclusion method. In another set of experiments, performed with U-937 cells, the mycotoxin was included in the culture medium at passaging, in order to assess its possible effects on cell growth. Viability of both U-937 cells and HL-60 cells was not affected by beauvericin at concentrations up to 3 microM, after 4h exposure, whereas a steady decline was seen at higher concentrations. Similarly, after an exposure time of 24h, a decline in viability was observed in cultures exposed to beauvericin at a concentration of 10 microM or higher. Thus, 50% cytotoxic concentrations at 24h of congruent with 30 microM and congruent with 15 microM were estimated for U-937 cells and HL-60 cells, respectively.Similar experiments were performed with cultures of HL-60 cells partially differentiated towards the eosinophilic phenotype, revealing that, in 4h exposure experiments (but not in 24h experiments), the viability of these cultures underwent a significantly less pronounced decline, in comparison to undifferentiated HL-60 cultures. Interestingly, when U-937 cells were allowed to proliferate in the presence of the mycotoxin, included in the culture medium at passaging, a substantial cytotoxicity was observed at lower concentrations, compared with prevalently resting, stationary phase cultures. Accordingly, a definite inhibition of the proliferative capability of the cells was detected. The information provided by this work may be useful in selecting appropriate myeloid cell models for the development of biossays aimed at detecting beauvericin (and, possibly, other mycotoxins) in foods and other commodities.

Beauvericin cytotoxicity to the invertebrate cell line SF-9.

The cyclic hexadepsipeptide beauvericin, initially known as a secondary metabolite produced by the entomopathogenic fungus Beauveria bassiana and toxic to Artemia salina larvae, has been more recently recognized as an important mycotoxin synthesized by a number of Fusarium strains, which parasite maize, wheat and rice. Therefore, this mycotoxin may enter the food chain, causing yet unknown effects to the health of both domestic animals and humans. The cytotoxic effects of beauvericin on mammalian cells have been studied. We investigated the cytotoxicity of this compound in an in vitro invertebrate model, viz. the insect cell line SF-9 (immortalized pupal ovarian cells of the lepidopter Spodoptera frugiperda). Cultures of SF-9 cells in the stationary phase were exposed to beauvericin at concentrations ranging from 100 nM to 300 microM, for different periods of time (from 30' to 120 h). The effects on cell viability were assessed by the trypan blue exclusion method. After 4 h of incubation no significant decrease in cell viability was recorded in SF-9 cell cultures exposed to low concentrations of beauvericin, i.e. 100 nM and 300 nM. However, a slight decrease in viability (3.9%) was seen already in cells exposed to the mycotoxin at the 1 microM concentration. This effect became gradually more evident at higher concentrations (approximately equal to 28% at 30 microM, approximately equal to 50% at 100 microM, approximately equal to 68% at 300 microM). An even more pronounced reduction in cell viability was observed after a 24 h exposure. Under these conditions, 1 microM beauvericin caused an approx. 10% decrease in the number of viable cells, which became more significant at higher concentrations approximately equal to 23% at 3 microM, approximately equal to 47% at 10 microM, approximately equal to 65% at 30 microM, approximately equal to 90% at 100 microM, approximately equal to 99% at 300 microM). Therefore, the 50% cytotoxic concentrations (CC50) at 4 h and 24 h could be estimated as 85 microM and 10 microM, respectively. In time-course experiments, no effect of beauvericin (30 microM) on cell viability could be seen after exposure for periods of time as long as 30', 1 h and 2 h, respectively. In contrast, when SF-9 cells were exposed to the mycotoxin for longer periods of time, from 8 h to 120 h, we recorded a strong cytotoxic effect already in the low micromolar concentration range. Thus, the CC50 after both 72 h and 120 h exposure times was assessed as 2.5 microM. Higher concentrations caused a virtually 100% cell death. The data collected suggest that beauvericin exerts a substantial dose- and time-dependent cytotoxic effect on invertebrate cells, comparable to the effects described in mammalian cells.