In addition, two reviews concluded that there are numerous indications that exposure to pesticides may contribute to spontaneous abortion and/or stillbirth , but it is unclear whether this should be considered as an endocrine disrupting effect . Another study found no correlations between infertility and self-reported overall pesticide exposure, working in the agricultural sector, or living on a farm during the two years before the diagnosis of infertility or the last pregnancy . The risk of this pesticide actually inducing a biological effect depends on its properties, but the effect will only occur when exposure reaches a particular level . The testing is the first step toward including hormone data in the regulation of pesticides and industrial chemicals. In 2009, the EPA ordered industry to use the in-vitro assays to screen 67 pesticides for their potential effect on hormones. Mary Emma Young of CropLife America, which represents the pesticide industry, said the group is reviewing the new study and could not yet comment on it. Animal and in vitro studies are widely used and are often the first indicators of potential reproductive or developmental effects. The female ovarian cycle is the result of a balanced cooperation between several organs and is determined by a complex interaction of hormones. In monkeys, ovulatory levels of estradiol were reduced after high doses of hexachlorobenzene , which also induced anovulatory cycles and suppression of circulating levels of estradiol , and a dose dependent suppression of serum progesterone concentrations during the luteal phase . The exposure frequency is unpredictable, ranging from a fewdays to a few weeks, depending on crop type and geographical location4,5. Thailand is a developing country that relies heavily on pesticide use inagriculture to sustain its economy. Urine was analyzedfor levels of specific- and non-specific metabolites of organophosphates (OPs),pyrethroids, select herbicides, and fungicides. All authors contributed substantially to the conception of the outline of the review, gave advise during the literature study, and critically revised subsequent versions of the manuscript. These often provide the first indications of potential reproductive effects of a chemical, but it is difficult to extrapolate the effects found in laboratory animals to effects that might be expected in women. A disadvantage of the studies described is that they were mostly laboratory animal and cell culture studies. A slightly increased risk for central nervous system defects was also observed. Follicle stimulating hormone (FSH), luteinizing hormone (LH), steroidhormones (e.g. testosterone, estradiol), and the testicular hormone inhibinb8,9,10,11,12,13,14,15 inmen. Examples of these pesticides are 2,4-D, chlorpyrifos, prothiofos, fenthion,permethrin, cypermethrin, and cyfluthrin7. Current-use pesticides in Thailand are considered,"non-persistent," as they break down easily in the environment and donot tend to bioaccumulate in the human body6.|There are several studies that have examined the association of organochlorine pesticides with sex hormones among males who have been occupationally exposed or live in highly contaminated areas. Among 178 males living near the United States Great Lakes with measurements of DDE, testosterone, and sex hormone binding globulin (SHBG), no correlation of exposure with hormone levels was observed (Persky, Turyk et al. 2001). This may contribute, at least in part, to the observed reduction in the total antioxidant capacity of the seminal fluid in OP pesticides-exposed individuals (27), resulting in germ cell damage and consequent low sperm count and concentration. Therefore, the data presented in this study provide a robust indication and strengthens available evidence that OP pesticides exposure lowers semen quality by reducing sperm count, concentration, motility, and normal morphology. Although seminal fluid leukocyte levels were higher in OP pesticides-exposed individuals compared with unexposed controls using both studies that were included in this study (26), this was not significant when the studies were pooled together. This study reports a significant decline in sperm count, concentration, progressive and total motility, and normal morphology in individuals who were exposed to OP pesticides compared with unexposed controls.|Criteria for enrollment included having goodphysical health, working on farms and applying pesticides, and willingness toprovide biological samples and survey data relevant to the study. Alterations ofreproductive hormone levels may lead to a decline in semen quality (i.e.concentration, motility, and morphology) and sperm DNA damage/fragmentation. Thai farmersgenerously apply pesticides with minimal or no use of appropriate protectiveequipment, resulting in a high magnitude of exposure to a wide variety of pesticidesand pesticide classes. Positive significant associations were found betweensome OP pesticides and total testosterone. Furthermore, we have to take into account that dose, timing, and duration of exposure are critical to the ability of a pesticide to cause harmful effects. In this review, we described the different ways in which pesticides may disrupt the hormonal function of the female reproductive system and in particular the ovarian cycle. Again, a cause-effect relation between these defects and exposure to endocrine disrupting pesticides could not be established.|Weighted geometric means and 95% confidence intervals (95% CIs) were calculated for the continuous skewed hormone (age-adjusted) and pesticide concentrations, by covariates. Concentrations of testosterone (ng/dL), SHBG (nmol/L), serum albumin (g/dL), and estradiol (pg/mL) were used to calculate concentrations of unbound (free) testosterone and estradiol according to the method supplied by Vermeulen (Belgorosky, Escobar et al. 1987, Vermeulen, Verdonck et al. 1999). We excluded males under 20 years old, using hormone-modifying medications (e.g., antiandrogens, 5-alpha-reductase inhibitors, hormone modifiers, adrenal cortical steroids) or with missing data for any pesticide or covariate (body mass index, education, and smoking history). BMI was considered as a potential effect modifier since it is a proxy for fat mass and organochlorine pesticides are stored in fat, which could potentially impact sex hormone metabolism in this tissue compartment.|The first exposure quartile was considered the referent group in all categorical analyses. A correction factor of 0.644 was applied to the β-hexachlorocyclohexane concentrations for the 1999–2000 cycle as advised by NHANES. This included lipid-adjusted concentrations (ng/g lipid) of β-hexachlorocyclohexane, HCB, heptachlor epoxide, oxychlordane, p,p’-DDE, p,p’-DDT, trans-nonachlor, and mirex. A one-third subsample of participants aged 12 years and older was selected for organochlorine pesticide measurements.|This might explain the contradictory results between our study and thestudy of Meeker, et al.11 whichreported an inverse association between testosterone levels and urinary metabolitelevels of the OP insecticide chlorpyrifos11. For 2,4-D, some studiesreported evidence of testosterone reduction following exposure (oraladministration)32. Four, we found no negativerelationship between TCPY and testosterone levels, unlike the study reported byMeeker et al.11. However, thestudy by Blanco-Munoz et al. (2010) documented a marginally positive associationbetween urinary DEP and testosterone levels9. Two, when DEP and DEDTP were modeled separately ascategorical variables, evidence of positive relationships was found for totaltestosterone levels. In this study, due to a wide range of detection frequencies across analytes,we chose not to impute urinary pesticide metabolite values below the LODs in orderto avoid the introduction of possible biases25. To save time, farmers often mixed different classes of pesticidestogether and applied this mixture on their crops.|The aim of this review is to give an overview of the various ways in which pesticides may disrupt the hormonal function of the female reproductive system and in particular the ovarian cycle. Previous studies primarily focused on interference with the estrogen and/or androgen receptor, but the hormonal function may be disrupted in many more ways through pesticide exposure. Perry said she hopes agencies like the Environmental Protection Agency begin to factor the impact of chemicals and pesticides on reproductive health in their assessments.|The manuscript will undergo copyediting, typesetting, and review of the resulting proof before it is published in its final form. Participant flow diagram showing sample exclusions and final numbers for statistical analysis. Residual confounding may also be present due to imperfect methods for adjusting for serum lipids.|The Funnel plot was asymmetrical denoting the presence of publication bias. Furthermore, funnel plot asymmetry was found, which is consistent with the presence of publication bias. Confirming the absence of publication bias, funnel plot symmetry was also discovered (Figure 9). Asymmetry in the funnel plot, which was discovered, is yet another indication of publication bias. The asymmetry of the Funnel plot indicated significant publication bias. The Funnel plot was significantly asymmetrical, indicating that publication bias was present.} Forest plot (A) and publication bias funnel plot (B) of the effect of organophosphate pesticide exposure on total sperm motility (%). The study consisted of a total of 766 male subjects (349 exposed to OP pesticides and 417 unexposed controls). This study demonstrates that OP pesticides exposure reduced sperm count, concentration, total and progressive motility, and normal sperm morphology, possibly via a testosterone-independent mechanism. A total of 766 male subjects (349 exposed to OP pesticides and 417 unexposed controls) were included in the meta-analysis. This study provides a systematic review and meta-analysis of the impacts of OP pesticides on semen quality and male reproductive hormones.