When does the sex ratio of offspring of the paternal 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure decrease: In the spermatozoa stage or at fertilization?

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Abstract

Recent animal experiments confirmed that paternal 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure decreases the sex ratio of offspring at birth without altering litter size. However, the timing of this decrease remained unclear. Male mice were administered TCDD at 7–12 weeks of age and mated with non-treated females. The Y-bearing/X-bearing sperm ratio was examined by real-time PCR and FISH methods, and the sex ratio of the 2-cell embryos collected from non-treated females that had been mated with TCDD-exposed males were investigated by nested PCR. The Y-bearing/X-bearing sperm ratio was not significantly decreased in the TCDD group. However, the sex ratio of the 2-cell embryos of the TCDD group was significantly lower than that of the control group. These results may have resulted from a decrease in fertility of Y-bearing sperm. Thus, the results of this study suggested that the sex ratio of the offspring was decreased at fertilization and not during the spermatozoa stage.

Introduction

In recent years the public has become more aware that exposure of males to certain environmental or occupational agents affects their offspring. Occupational exposure in various industries has led to increased incidences of miscarriage [1] and various birth defects [2]. It has also been shown that paternal cranial irradiation leads to epigenetic alterations in offspring [3]. Prominent among these reports are those by Mocarelli et al. [4], [5] showing that paternal 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure in Seveso, Italy, led to a decrease in male offspring.

In 1976, TCDD was released in an explosion at a chemical plant near Seveso, Italy, resulting in the highest concentrations of TCDD ever recorded in humans. Subsequent data linked a decrease in male births in Seveso to the increased TCDD concentration in fathers, and the altered sex ratio (the proportion of male offspring) was especially pronounced in the children of fathers exposed to TCDD before age 19 [4], [5]. In addition to the Seveso incident, Ryan et al. [6], in a study conducted in Ufa, Russia, suggested that human exposure to high levels of dioxin is associated with the birth of more girls only in cases of paternal exposure. In our previous study, we exposed young male mice to two concentrations of TCDD (TCDD2/0.4 group and TCDD2000/400 group; an initial loading dose of 2 or 2000 ng TCDD/kg, followed by a weekly maintenance dose of 0.4 or 400 ng TCDD/kg) to re-create the Seveso incident and evaluated the sex ratio of their offspring at birth [7]. The reason why we used young male mice (7 weeks at the start of administration) in that study was that the sex ratio of offspring of males exposed to TCDD during adolescence showed a greater decrease than that of males who were older than that when the incident occurred [4], [5]. The results from the previous study revealed that paternal TCDD administration produced a dose-dependent reduction in the sex ratio of offspring (F1) and a significantly lower proportion of male offspring in the high-dose (TCDD2000/400) group. In addition, the induction intensity of CYP1A1 in the liver varied among individuals in the TCDD group, and the dimensions of the CYP1A1 immunoreactive area were correlated with the sex ratio of the offspring. This means that the high sensitivity subgroup of male parents to TCDD was strongly related to the decrease in male offspring. We also reported that TCDD exposure does not influence litter size; the number of male offspring decreases by TCDD exposure, while the number of female offspring increases. From these data, we presumed that paternal TCDD exposure decreased the sex ratio of offspring and altered it before implantation occurred. However, the mechanisms underlying the reduction in male offspring and the timing of this change have remained unclear.

The purpose of this study was to investigate when the sex ratio of the offspring decreases. We examined the Y-bearing/X-bearing sperm ratio as well as the sex ratio of 2-cell embryos by exposure to the same dose (an initial loading dose of 2000 ng TCDD/kg, followed by a weekly maintenance dose of 400 ng TCDD/kg) as used in our previous study [7], because this dose group showed a significant decrease in the sex ratio of offspring at birth. The effects of TCDD exposure to sperm concentration and motility were also examined.

Section snippets

Chemicals

TCDD was obtained from Wako Pure Chemical Industries, Ltd. (Osaka, Japan). Sesame oil, used for dissolving TCDD and for vehicle treatment as a control, was purchased from Kanto Chemical Co., Inc. (Tokyo, Japan).

Animals and treatments

Male and female ICR mice were purchased from Japan SLC, Inc. (Hamamatsu, Japan) and bred at Kobe University (Kobe, Japan). They were maintained under controlled conditions of temperature (23 ± 2 °C) and humidity (50 ± 10%) on a 12 h light, 12 h dark cycle. The animals were given an MR-A1

Epididymal sperm concentration and motility

Epididymal sperm concentrations of five males per group and sperm motility of seven males in the control group and five males in the TCDD group were examined. Fig. 1, Fig. 2 show the effects of TCDD exposure on sperm concentration and motility. Compared with the control group, the TCDD group showed a lower level of caudal epididymal sperm concentration [Control: 4.28 ± 0.79 × 107/ml; TCDD: 2.29 ± 0.70 × 107/ml; P = 0.10], because one of the mice in the TCDD group showed a very low sperm concentration.

Discussion

In theory, the sex allocation ratio of many species of mammals is almost 1:1. However, in reality this is not necessarily true. There have been many reports about changes in the sex ratio of human offspring. Severe periconceptional life events have been found to reduce the sex ratio in offspring [10]. The proportion of male offspring decreases with increasing parental age, and is higher in white people than in black people [11]. The sex ratio varies with the coital rate and with the time taken

Conflicts of interest

The authors have no conflicts of interest that would have inappropriately influenced the work presented in this manuscript.

Acknowledgments

The authors would like to express their heartfelt thanks to Prof. Chiharu Tohyama (The University of Tokyo) for his excellent advice during this research.

This work was supported in part by Grants-in-Aid for Scientific Research (B) (15390510, 18380089) and for Scientific Research on Priority Areas (1) (14042260) from the Ministry of Education, Culture, Sports, Science and Technology of Japan to N.H.

References (21)

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