Exposure to pyrethroid pesticides and ovarian reserve.

INTRODUCTION: Synthetic pyretroids are among the most common pesticides currently used worldwide. Animal studies suggest that exposure to pyrethroids could dysregulated the function of the ovary, mainly follicular development and/or synthesis of the reproductive hormone. Nevertheless data regarding the effect of exposure on female ovarian function is limited. So the aim of the present study is to assess the effect of exposure to synthetic pyrethroids on ovarian reserve. MATERIALS AND METHODS: The study population consists of 511 females aged 25-39 years attending infertility clinics for diagnostic purposes, because of couples' infertility. Validated gas chromatography ion-tap mass spectrometry method was used to assess the urinary concentrations of pyrethroid metabolites (CDDCA (cis-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane carboxylic acid), TDDCA (trans-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane carboxylic acid), 3PBA (3-phenoxybenzoic acid) and DBCA (cis-2,2-dibromovinyl-2,2-dimethylcyclopropane-1-carboxylic acid)). Ovarian reserve was assessed using parameters of ovarian reserve (antral follicle count and concentrations of hormones: AMH (anti-Mullerian hormone), FSH (follicle stimulating hormone) and E2 (estradiol)). RESULTS: In the present analysis the association was found between urinary concentrations of 3-PBA and levels of AMH (p = 0.03), FSH (p = 0.04) and antral follicle count (p = 0.02). Urinary level of CDCCA, TDCCA and DBCA was not associated with any examined parameters of ovarian reserve. CONCLUSIONS: Synthetic pyrethroids may affect female ovarian reserve. As this is the first, preliminary study the results need confirmation in a further detailed investigations.

The association between environmental exposure to pyrethroids and sperm aneuploidy.

The aim of the present study is to determine whether the environmental exposure to pyrethroids was associated with males sperm chromosome disomy. The study population consisted of 195 men who attended the infertility clinic for diagnostic purposes and who had normal semen concentration of 20-300×10(6) mL(-1) or slight oligozoospermia (semen concentration of 15-20×10(6) mL(-1)) (WHO, 1999). Participants were interviewed and provided a semen sample. The pyrethroids metabolites: 3-phenoxybenzoic acid (3PBA), cis-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane carboxylic acid (CDCCA), trans-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane carboxylic acid (TDCCA) and cis-2,2-dibromovinyl-2,2-dimethylcyclopropane-1-carboxylic acid (DBCA) were analysed in the urine using a validated gas chromatography ion-tap mass spectrometry method. Sperm aneuploidy was assessed using multicolor FISH (DNA probes specific for chromosomes X, Y, 18, 13, 21). Our results showed that CDCCA >50th percentile was associated with disomy of chromosome 18 (p=0.05) whereas the level of TDCCA in urine >50th percentile was related to XY disomy (p=0.04) and disomy of chromosome 21 (p=0.05). Urinary 3PBA level ⩽50 and >50 percentile was related to disomy of sex chromosomes: XY disomy (p=0.05 and p=0.02 respectively), Y disomy (p=0.04 and 0.02 respectively), disomy of chromosome 21 (p=0.04 and p=0.04 respectively) and total disomy (p=0.03 and p=0.04 respectively). Additionally disomy of chromosome 18 was positively associated with urinary level of 3PBA >50 percentile (p=0.03). The results reported here are found that pyrethroids may be a sperm aneugens. These findings may be of concern due to increased pyrethroid use and prevalent human exposure.

The effect of environmental exposure to pyrethroids and DNA damage in human sperm.

The present study was designed to investigate whether environmental exposure to pyrethroids was associated with sperm DNA damage. Between January 2008 and April 2011 286 men under 45 years of age with a normal sperm concentration of 15-300 10(6)/ml [WHO 2010] were recruited from an infertility clinic in Lodz, Poland. Participants were interviewed and provided urine, saliva, and semen samples. The pyrethroids metabolites: 3-phenoxybenzoic acid (3PBA), cis-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane carboxylic acid (CDCCA), trans-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane carboxylic acid (TDCCA), and cis-2,2-dibromovinyl-2,2-dimethylcyclopropane-carboxylic acid (DBCA) were analyzed in the urine using a validated gas chromatography ion-tap mass spectrometry method. Sperm DNA damage was assessed using a flow cytometry based on sperm chromatin structure assay (SCSA). A positive association was observed between CDCCA >50th percentile and the percentage of medium DNA fragmentation index (M DFI) and percentage of immature sperms (HDS) (p = 0.04, p = 0.04 respectively). The level of 3PBA >50th percentile in urine was positively related to the percentage of high DNA fragmentation index (H DFI) (p = 0.03). The TDCCA, DBCA levels, and the sum of pyrethroid metabolites were not associated with any sperm DNA damage measures. Our results suggest that environmental pyrethroid exposure may affect sperm DNA damage measures index indicated the reproductive effects of pyrethroid exposure on adult men. In view of the importance of human reproductive health and the widespread usage of pyrethroids, it is important to further investigate these correlations.

Semen quality and the level of reproductive hormones after environmental exposure to pyrethroids.

OBJECTIVES: The aim of this study was to determine whether the environmental exposure to pyrethroids affects semen quality and the level of reproductive hormones in men. METHODS: The study population consisted of 334 men who attended the infertility clinic for diagnostic purposes and who had normal semen concentration of 15 to 300 mln/mL. Participants were interviewed and provided a semen sample. The pyrethroids metabolites-3-phenoxybenzoic acid (3PBA), cis-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane carboxylic acid (CDCCA), trans-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane carboxylic acid (TDCCA), and cis-2,2-dibromovinyl-2,2-dimethylcyclopropane-1-carboxylic acid (DBCA) were analyzed in the urine using a validated gas chromatography ion-trap mass spectrometry method. RESULTS: Urinary pyrethroids metabolites levels were significantly associated with an increase in the percentage of sperm with abnormal morphology and decrease in sperm concentration, the level of testosterone, and computer-aided semen analysis parameters. CONCLUSIONS: Environmental pyrethroids exposure may affect semen quality and the level of reproductive hormones.

Biomonitoring of pyrethroid exposure among rural and urban populations in northern Poland.

The aim of this study was to determine for the first time in Poland, levels of exposure to synthetic pyrethroids in preschool and school age children and their parents living in urban and rural areas. For this purpose concentrations of pyrethroid metabolites: 3-phenoxybenzoic acid (3-PBA), 2,2-dibromovinyl-2,2-dimethylcyclopropanecarboxylic acid (Br2CA), cis-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane-1-carboxylic acid (cis-Cl2CA) and trans-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane-1-carboxylic acid (trans-Cl2CA) were determined in 374 urine samples using a validated GC-MS method. All measured metabolites were detected more frequently and in higher concentrations in rural areas. 3-PBA was detected in 77.4% and 93.8% of samples from urban and rural areas, respectively. Its geometric mean (GM) concentration in rural population was higher than in urban (0.364 vs. 0.223 ng mL(-1) and 0.272 vs. 0.155 µg g(-1) creatinine, p<0.0001). Among remaining metabolites, only cis- and trans-Cl2CA were detected in more than 50.0% of samples in rural population. Average concentrations of 3-PBA in children were higher than in adults, both in urban and rural areas. Moderate to very strong positive correlations were noticed between concentrations of pairs of pyrethroid metabolites in urine samples. Significant, moderate correlations between the concentrations of particular metabolites in parents and their children were observed in the urban population (range: r=0.2911-0.3919 for non-adjusted and 0.3827-0.4693 for creatinine adjusted concentrations), while in rural areas there were no such relationship. Application of pesticide formulations on pets in the past 6 months was associated with increased 3-PBA urinary concentration. Further studies on pesticide exposure among children in rural areas are needed to identify and possibly reduce or eliminate the sources of exposure.