Test systems to screen for estrogenicity and appropriate biomarkers of human exposure are require... more Test systems to screen for estrogenicity and appropriate biomarkers of human exposure are required for epidemiological studies of endocrine disruption. We addressed these issues by developing and standardising a method to assess the total estrogenic xenobiotic burden in human adipose tissue. In this study, which is the continuation of a previous work, we have improved the protocol for extensive fractionation of a higher number of tissue samples in order to investigate bioaccumulated xenoestrogens that are candidates for estrogenicity and to assess their combined estrogenic effect. This was achieved by extensive HPLC separation of xenoestrogens from endogenous hormones followed by testing of individual fractions in the E-Screen test for estrogenicity. Organochlorine pesticides, PCBs and halogenated bisphenols and alkylphenols were collected in the most lipophilic fractions, followed by progestins, androgens and estradiol esters, and then by steroidal estrogens; phyto- and myco-estrogens were collected around the end of the run. These results were confirmed by exhaustive chemical analysis. In 458 human adipose tissue samples, the total effective xenoestrogen burden was positive in 75% of samples in the pooled fraction that contained organohalogenated xenoestrogens (mean 515.3 pM Eeq/g lipid; range 0–14.5 nM) and in 82% of samples in the pooled fraction where natural estrogens eluted (mean 696.6 pM Eeq/g lipid; range 0–12.9 nM). Organochlorine pesticides emerged as candidate chemicals for the estrogenicity of the first pooled fraction, because DDT and derivatives were present in 98.3% of the samples. However, no correlation was found between the concentration of any single chemical and the estrogenicity determined in the bioassay. There may be several reasons for this lack of concordance: (i) the estrogenic effects depicted in the E-Screen bioassay are a consequence of the combined effect of several organohalogens or (ii) the proliferative effect is due to other chemicals not measured. Because additive, synergistic or antagonistic mechanisms may account for the final effect observed in the pooled fractions, the approach proposed in this work is more appropriate for exposure assessment in epidemiological studies than the determination of individual chemicals in human samples.
The widespread presence of organochlorine (OC) pesticides in human samples may be explained by th... more The widespread presence of organochlorine (OC) pesticides in human samples may be explained by the environmental exposure of the population. Foods are considered a constant source of exposure, despite compliance with maximum permitted residue levels. This study aimed to examine the relationship between nutritional habits of women in Southeast Spain and their serum concentrations of OCs. A semi-quantitative questionnaire was used to estimate the frequency of consumption of foods by two age groups of women, pre-menopausal (Pre-M) and post-menopausal (Post-M), and their serum pesticide levels were measured by gas chromatography (GC) with electron capture detector and confirmed by GC and mass spectrometry. The Pre-M group showed significantly higher serum concentrations of all OCs studied with the exception of DDE. The groups significantly differed in consumption of all food groups with the exception of fruit. In the Pre-M group, the mean serum p,p-DDT concentration was significantly associated with milk/yoghurt (p<0.045) and red meat (p<0.023), serum o,p-DDT with red meat (p<0.049), serum aldrin with eggs (p<0.038) and poultry (p<0.024), and serum DDE with eggs (p<0.025). In the Post-M group, serum lindane was associated with fresh and cured cheese (p<0.001), red meat (p<0.001) and white and oily fish (p<0.001), and both serum DDE and dieldrin were associated with fresh cheese, cured cheese, red meat, and white and oily fish (p<0.001). These results confirm foods as a source of human exposure to persistent organic molecules. Consideration should be given to the reduction of permitted residue levels to minimize this threat to human and animal health.
Objective: The present study aimed to determine whether the combined effects of environmental est... more Objective: The present study aimed to determine whether the combined effects of environmental estrogens measured as the total effective xenoestrogen burden (TEXB-alpha) are a risk factor for breast cancer over and above the risk potentially linked to specific pesticides. Methods: We measured the levels of 16 organochlorine pesticides as well as TEXB in adipose tissue of 198 women at the time of breast cancer diagnosis. These were compared with findings in 260 age and hospital matched control women without breast cancer. Results: The median levels of p,p′-DDE (1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene), aldrin, endosulfan ether and lindane (the pesticides detected in >40% of the study population) were higher in cases than controls, although the differences did not reach statistical significance. After adjusting for potential confounders, the odds ratio (OR) for breast cancer in women with detectable levels of aldrin was 1.55 (95% confidence interval (CI) 1.00–2.40). Among the postmenopausal women, the OR for aldrin and lindane was 1.84 (95% CI 1.06–3.18) and 1.76 (95% CI 1.04–2.98), respectively. Among cases with body mass index (BMI) below the median (28.6 kg/m2), the OR was 3.42 (95% CI 1.22–9.58) for women in the highest quartile of TEXB-alpha versus those in the lowest. The subgroup of leaner postmenopausal women showed an increased risk (OR: 5.67; 95% CI 1.59–20.21) for those in the highest tertile versus those in the lowest. Conclusions: We found an increased risk for breast cancer in the leaner women, especially in the leaner postmenopausal subgroup, related to the TEXB-alpha. The pesticides aldrin and lindane are also individually associated with risk.
Foetal exposure of male rats to di(n-butyl) phthalate (DBP) induces testicular changes similar to... more Foetal exposure of male rats to di(n-butyl) phthalate (DBP) induces testicular changes similar to testicular dysgenesis syndrome in humans, including the formation of focal ‘dysgenetic areas’ within post-natal testes, surrounded by otherwise normal tubules exhibiting complete spermatogenesis. We hypothesize that these dysgenetic areas form when Sertoli (and other) cells are ‘trapped’ during the abnormal formation of large Leydig cell (LC) clusters in foetal life and by post-natal day (d) 4 these groups of intermingled cells attempt to form seminiferous tubules. It is likely that the malformed tubules resulting correspond to the dysgenetic areas evident in later life. This also provides a plausible explanation for the occurrence of LCs within seminiferous cords/tubules in or bordering the dysgenetic areas. In our previous studies intratubular LCs (ITLCs) were identified by immunostaining for 3β-hydroxysteroid dehydrogenase (3β-HSD), the definitive LC cytoplasmic marker. However, the possibility remained that the ‘presumptive’ ITLCs were in fact Sertoli cells that had aberrantly gained the ability to express 3β-HSD. Therefore, the aim of the present study was to fully characterize the ITLCs induced by in utero DBP exposure in d25 rats using a number of LC- (3β-HSD, P450 side-chain cleavage enzyme, insulin-like factor 3, oestrogen receptor alpha) and Sertoli cell- (vimentin, Wilm's tumour-1) specific markers. Our results show that ITLCs express all four LC-specific markers but do not express either of the Sertoli cell markers. It is therefore concluded that the ITLCs are bona fide LCs that are abnormally located within the seminiferous tubules of DBP-exposed rats in post-natal life.
To determine the existence of an acid stress response in Helicobacter pylori the global changes i... more To determine the existence of an acid stress response in Helicobacter pylori the global changes in the proteins synthesized by the bacterium when subjected to an acid stress were studied. H. pylori ATCC43504 previously adapted to pH 7 did not show an acid stress response as detected by the two-dimensional electrophoretic pattern of 35S-labeled proteins when incubated at pH 3. This was probably due to the neutralization of the external medium by the action of urease. However, H. pylori DW504UreI-negative, a mutant strain unable to transport urea into the cell, showed a large number of proteins changed, as is typical in an acid stress response. Some of these proteins were identified by N-terminal sequencing.
Test systems to screen for estrogenicity and appropriate biomarkers of human exposure are require... more Test systems to screen for estrogenicity and appropriate biomarkers of human exposure are required for epidemiological studies of endocrine disruption. We addressed these issues by developing and standardising a method to assess the total estrogenic xenobiotic burden in human adipose tissue. In this study, which is the continuation of a previous work, we have improved the protocol for extensive fractionation of a higher number of tissue samples in order to investigate bioaccumulated xenoestrogens that are candidates for estrogenicity and to assess their combined estrogenic effect. This was achieved by extensive HPLC separation of xenoestrogens from endogenous hormones followed by testing of individual fractions in the E-Screen test for estrogenicity. Organochlorine pesticides, PCBs and halogenated bisphenols and alkylphenols were collected in the most lipophilic fractions, followed by progestins, androgens and estradiol esters, and then by steroidal estrogens; phyto- and myco-estrogens were collected around the end of the run. These results were confirmed by exhaustive chemical analysis. In 458 human adipose tissue samples, the total effective xenoestrogen burden was positive in 75% of samples in the pooled fraction that contained organohalogenated xenoestrogens (mean 515.3 pM Eeq/g lipid; range 0–14.5 nM) and in 82% of samples in the pooled fraction where natural estrogens eluted (mean 696.6 pM Eeq/g lipid; range 0–12.9 nM). Organochlorine pesticides emerged as candidate chemicals for the estrogenicity of the first pooled fraction, because DDT and derivatives were present in 98.3% of the samples. However, no correlation was found between the concentration of any single chemical and the estrogenicity determined in the bioassay. There may be several reasons for this lack of concordance: (i) the estrogenic effects depicted in the E-Screen bioassay are a consequence of the combined effect of several organohalogens or (ii) the proliferative effect is due to other chemicals not measured. Because additive, synergistic or antagonistic mechanisms may account for the final effect observed in the pooled fractions, the approach proposed in this work is more appropriate for exposure assessment in epidemiological studies than the determination of individual chemicals in human samples.
The widespread presence of organochlorine (OC) pesticides in human samples may be explained by th... more The widespread presence of organochlorine (OC) pesticides in human samples may be explained by the environmental exposure of the population. Foods are considered a constant source of exposure, despite compliance with maximum permitted residue levels. This study aimed to examine the relationship between nutritional habits of women in Southeast Spain and their serum concentrations of OCs. A semi-quantitative questionnaire was used to estimate the frequency of consumption of foods by two age groups of women, pre-menopausal (Pre-M) and post-menopausal (Post-M), and their serum pesticide levels were measured by gas chromatography (GC) with electron capture detector and confirmed by GC and mass spectrometry. The Pre-M group showed significantly higher serum concentrations of all OCs studied with the exception of DDE. The groups significantly differed in consumption of all food groups with the exception of fruit. In the Pre-M group, the mean serum p,p-DDT concentration was significantly associated with milk/yoghurt (p<0.045) and red meat (p<0.023), serum o,p-DDT with red meat (p<0.049), serum aldrin with eggs (p<0.038) and poultry (p<0.024), and serum DDE with eggs (p<0.025). In the Post-M group, serum lindane was associated with fresh and cured cheese (p<0.001), red meat (p<0.001) and white and oily fish (p<0.001), and both serum DDE and dieldrin were associated with fresh cheese, cured cheese, red meat, and white and oily fish (p<0.001). These results confirm foods as a source of human exposure to persistent organic molecules. Consideration should be given to the reduction of permitted residue levels to minimize this threat to human and animal health.
Objective: The present study aimed to determine whether the combined effects of environmental est... more Objective: The present study aimed to determine whether the combined effects of environmental estrogens measured as the total effective xenoestrogen burden (TEXB-alpha) are a risk factor for breast cancer over and above the risk potentially linked to specific pesticides. Methods: We measured the levels of 16 organochlorine pesticides as well as TEXB in adipose tissue of 198 women at the time of breast cancer diagnosis. These were compared with findings in 260 age and hospital matched control women without breast cancer. Results: The median levels of p,p′-DDE (1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene), aldrin, endosulfan ether and lindane (the pesticides detected in >40% of the study population) were higher in cases than controls, although the differences did not reach statistical significance. After adjusting for potential confounders, the odds ratio (OR) for breast cancer in women with detectable levels of aldrin was 1.55 (95% confidence interval (CI) 1.00–2.40). Among the postmenopausal women, the OR for aldrin and lindane was 1.84 (95% CI 1.06–3.18) and 1.76 (95% CI 1.04–2.98), respectively. Among cases with body mass index (BMI) below the median (28.6 kg/m2), the OR was 3.42 (95% CI 1.22–9.58) for women in the highest quartile of TEXB-alpha versus those in the lowest. The subgroup of leaner postmenopausal women showed an increased risk (OR: 5.67; 95% CI 1.59–20.21) for those in the highest tertile versus those in the lowest. Conclusions: We found an increased risk for breast cancer in the leaner women, especially in the leaner postmenopausal subgroup, related to the TEXB-alpha. The pesticides aldrin and lindane are also individually associated with risk.
Foetal exposure of male rats to di(n-butyl) phthalate (DBP) induces testicular changes similar to... more Foetal exposure of male rats to di(n-butyl) phthalate (DBP) induces testicular changes similar to testicular dysgenesis syndrome in humans, including the formation of focal ‘dysgenetic areas’ within post-natal testes, surrounded by otherwise normal tubules exhibiting complete spermatogenesis. We hypothesize that these dysgenetic areas form when Sertoli (and other) cells are ‘trapped’ during the abnormal formation of large Leydig cell (LC) clusters in foetal life and by post-natal day (d) 4 these groups of intermingled cells attempt to form seminiferous tubules. It is likely that the malformed tubules resulting correspond to the dysgenetic areas evident in later life. This also provides a plausible explanation for the occurrence of LCs within seminiferous cords/tubules in or bordering the dysgenetic areas. In our previous studies intratubular LCs (ITLCs) were identified by immunostaining for 3β-hydroxysteroid dehydrogenase (3β-HSD), the definitive LC cytoplasmic marker. However, the possibility remained that the ‘presumptive’ ITLCs were in fact Sertoli cells that had aberrantly gained the ability to express 3β-HSD. Therefore, the aim of the present study was to fully characterize the ITLCs induced by in utero DBP exposure in d25 rats using a number of LC- (3β-HSD, P450 side-chain cleavage enzyme, insulin-like factor 3, oestrogen receptor alpha) and Sertoli cell- (vimentin, Wilm's tumour-1) specific markers. Our results show that ITLCs express all four LC-specific markers but do not express either of the Sertoli cell markers. It is therefore concluded that the ITLCs are bona fide LCs that are abnormally located within the seminiferous tubules of DBP-exposed rats in post-natal life.
To determine the existence of an acid stress response in Helicobacter pylori the global changes i... more To determine the existence of an acid stress response in Helicobacter pylori the global changes in the proteins synthesized by the bacterium when subjected to an acid stress were studied. H. pylori ATCC43504 previously adapted to pH 7 did not show an acid stress response as detected by the two-dimensional electrophoretic pattern of 35S-labeled proteins when incubated at pH 3. This was probably due to the neutralization of the external medium by the action of urease. However, H. pylori DW504UreI-negative, a mutant strain unable to transport urea into the cell, showed a large number of proteins changed, as is typical in an acid stress response. Some of these proteins were identified by N-terminal sequencing.
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