The production of plastic products, which requires phthalate plasticizers, has resulted in the problems for human health, especially that of reproductive health. Phthalate exposure can induce reproductive disorders at various regulatory levels. The aim of this review was to compile the evidence concerning the association between phthalates and reproductive diseases, phthalates-induced reproductive disorders, and their possible endocrine and intracellular mechanisms. Phthalates may induce alterations in puberty, the development of testicular dysgenesis syndrome, cancer, and fertility disorders in both males and females. At the hormonal level, phthalates can modify the release of hypothalamic, pituitary, and peripheral hormones. At the intracellular level, phthalates can interfere with nuclear receptors, membrane receptors, intracellular signaling pathways, and modulate gene expression associated with reproduction. To understand and to treat the adverse effects of phthalates on human health, it is essential to expand the current knowledge concerning their mechanism of action in the organism.
The aim of the present study was to investigate the role of RNA polymerase I (RPI) transcription in nucleolar development during major transcriptional activation (MTA) in cattle. Late eight-cell embryos were cultured in the absence (control group) or presence of actinomycin D (AD) (RPI inhibition, AD 0.2 microg/ml; total transcriptional inhibition, AD 2.0 microg/ml). Late four-cell embryos were cultured to late eight-cell stage in 0.2 microg/ml AD (MTA prevention, ADLT (long-term total transcriptional inhibition group). Embryos were processed for autoradiography, transmission electron microscopy, fluorescent in situ hybridization (ribosomal RNA, rRNA), silver staining (nucleolar proteins), and immunofluorescence (RPI). Control embryos displayed extranucleolar and nucleolar transcription, functional nucleoli, and distinct RPI localization. Nuclei (97%) showed large rRNA clusters, in 94.1% co-localized with nucleolar proteins deposits. In AD 0.2 group, only extranucleolar transcription was detected. Segregated dense-fibrillar and granular components, but no fibrillar centers, were observed. RPI was dispersed. Nuclei (55%) presented rRNA clusters, in 38.8% co-localized with silver-stained deposits. AD 2.0 and ADLT groups displayed no transcription and disintegrating nucleolar precursors. AD 2.0 (34%) and 14% (ADLT) of nuclei presented clusters of maternally inherited rRNA. In AD 2.0 group, RPI was dispersed, but 17.2% of nuclei showed colocalization of rRNA with nucleolar proteins. In ADLT group, RPI was lacking and clustering of nucleolar proteins was hampered. In conclusion, rDNA transcription is not required for targeting of rRNA processing proteins, rRNA is maternally inherited and target to rDNA independent of transcription, and de novo transcription is required for proper nucleologenesis in cattle.
Spot urine samples were collected in summer and winter season to examine the association between temperature variation and phthalate concentration in an occupationally exposed group. We analysed samples by high-performance liquid chromatography with mass spectrometry (HPLC-MS/MS) to determine the concentrations of four phthalate metabolites: mono (2-ethylhexyl) phthalate (MEHP), monobutyl phthalate (MnBP), monoethyl phthalate (MEP), and monoisononyl phthalate (MiNP). We observed significantly higher urinary concentrations of all monitored phthalate metabolites collected during the summer in occupationally exposed group (MEP p < 0.0015, MiNP p < 0.0001, MnBP p < 0.00019, and MEHP p < 0.05); however, in general, population was noticed this difference only for MEHP (p < 0.05) in winter season. We conclude that increasing indoor and outdoor temperature is related to phthalate exposure in specific types of work environment.
Many toxic substances in the workplace can modify human health and quality of life and there is still insufficient data on respiratory outcomes in adults exposed to phthalates. The aim of this work was to assess in waste management workers from the Nitra region of Slovakia (n = 30) the extent of exposure to phthalates and health-related outcomes. Four urinary phthalate metabolites mono(2-ethylhexyl) phthalate (MEHP), monobutyl phthalate (MnBP), monoethyl phthalate (MEP) and monoisononyl phthalate (MiNP) were determined by high-performance liquid chromatography with mass spectrometry (HPLC-MS/MS). Urinary concentration of MEHP was positively associated with ratio of forced expiratory volume in 1 s to forced vital capacity % (FEV1/FVC) (r = 0.431; p = 0.018) and MiNP with fat free mass index (FFMI) (r = 0.439; p = 0.015). The strongest predictor of pulmonary function was the pack/year index as smoking history that predicted a decrease of pulmonary parameters, the FEV1/FVC, % of predicted values of peak expiratory flow (PEF % of PV) and FEV1 % of PV. Unexpectedly, urinary MEHP and MINP were positively associated with pulmonary function expressed as PEF % of PV and FEV1/FVC. We hypothesize that occupational exposure to phthalates estimated from urinary metabolites (MEHP, MiNP) can modify pulmonary function on top of lifestyle factors.
The aim of our work was to find associations between urinary phthalate metabolite concentrations and occupation, consumer practices and body composition. We divided our cohort (n = 129) into occupationally exposed subjects, community service workers (group A; n = 45) and workers from plastic industry (group B; n = 35) and group of general population (control group C, n = 49). To estimate levels of five phthalate metabolites, we used high-performance liquid chromatography and tandem mass spectrometry analysis. We found in plastic industry workers compared to community service workers and subjects of the control group significantly higher urinary concentration mono (2-ethyl-5-hydroxyhexyl) phthalate (MEHHP), mono (2-ethyl-5-oxohexyl) phthalate (MEOHP), mono (2-etylhexyl) phthalate (MEHP), sum di-(2-ethyl-5-oxohexyl) phthalate (DEHP), mono-iso-butyl phthalate (MiBP) and mono-n-butyl phthalate (MnBP). We identified by multivariate analysis of covariance inverse relationship between MEHP and body parameters as waist-to-height ratio, body mass index, waist-to-hip ratio, hip circumference and waist circumference among females, whereas in males, no significant association was found. Results of our study show, despite of variability in terms of occupational exposure to phthalates, that plastic manufactory represents a higher occupational risk in comparison with waste management. The differences in anthropometric parameters between the two occupationally exposed groups and the general population are suggesting a detrimental effect of occupational exposure on body weight homeostasis.
The aim of this study was to evaluate the turkey spermatozoa motility in in vitro conditions and to prove the effect of different conditions of incubation -diluents, temperature and age of birds. Spermatozoa were obtained from adult turkey's line of Big 6, and spermatozoa motility parameters were evaluated using a computer-assisted semen analyzer (CASA) system. Significant decrease of spermatozoa motility at laboratory temperature (22°C) was detected from time 0 (94.15%) till 180 minutes of incubation (53.91%). At the cool media incubation (5°C), this difference was lower (95.41 and 78.86%, respectively), and the differences were significant from 30 minutes of incubation till 180 minutes. Progressive spermatozoa motility replicated the tendency of total spermatozoa motility. When the physiological solution to commercial diluent at 5°C was compared, the spermatozoa motility and progressive motility in both groups were very consistent for 90 minutes of incubation. Subsequently, significantly higher spermatozoa motility was detected at time periods 120, 150 and 180 minutes of incubation in commercial diluent. Motility was also higher in this group after 24 hours. Influence of age on spermatozoa motility parameters was analysed at 22°C at the time 0 and after 30 minutes of incubation. Analysis of spermatozoa motility as well as progressive spermatozoa motility proved higher values in Group A (aged 35-42 weeks) compared to Group B (aged 63-73 weeks). These results clearly suggest that low temperature and commercial diluents maintain motility parameters during longer time periods and the increasing age of birds has negative impact on motility parameters.
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