何先知, 李雨昕, 李嘉敏, 孙宾, 李媛媛, 翟庆峰. 高效氯氰菊酯和甲维盐联合染毒大鼠生殖激素分泌及动情周期的变化[J]. 环境与职业医学, 2023, 40(1): 83-88. DOI: 10.11836/JEOM22161
引用本文: 何先知, 李雨昕, 李嘉敏, 孙宾, 李媛媛, 翟庆峰. 高效氯氰菊酯和甲维盐联合染毒大鼠生殖激素分泌及动情周期的变化[J]. 环境与职业医学, 2023, 40(1): 83-88. DOI: 10.11836/JEOM22161
HE Xianzhi, LI Yuxin, LI Jiamin, SUN Bin, LI Yuanyuan, ZHAI Qingfeng. Secretion of reproductive hormones and estrous cycle in rats interfered by combined exposure to beta-cypermethrin and emamectin benzoate[J]. Journal of Environmental and Occupational Medicine, 2023, 40(1): 83-88. DOI: 10.11836/JEOM22161
Citation: HE Xianzhi, LI Yuxin, LI Jiamin, SUN Bin, LI Yuanyuan, ZHAI Qingfeng. Secretion of reproductive hormones and estrous cycle in rats interfered by combined exposure to beta-cypermethrin and emamectin benzoate[J]. Journal of Environmental and Occupational Medicine, 2023, 40(1): 83-88. DOI: 10.11836/JEOM22161

高效氯氰菊酯和甲维盐联合染毒大鼠生殖激素分泌及动情周期的变化

Secretion of reproductive hormones and estrous cycle in rats interfered by combined exposure to beta-cypermethrin and emamectin benzoate

  • 摘要: 背景

    高效氯氰菊酯与甲维盐广泛应用于温室种植业中的虫害防治,两者共同暴露可增加其在生物体内的蓄积,对人体健康产生影响。

    目的

    基于下丘脑-垂体-卵巢(HPO)轴中生殖激素水平的变化探讨高效氯氰菊酯和甲维盐联合染毒对雌鼠动情周期的影响。

    方法

    24只健康成年SD大鼠随机分为空白对照组、高效氯氰菊酯组(Beta-CYP,剂量为53 mg·m−3)、甲维盐组(EMB,剂量为8 mg·m−3)、高效氯氰菊酯与甲维盐联合染毒组(Beta-CYP+EMB,剂量为53 mg·m−3+8 mg·m−3),每组6只,每周雾化吸入6 d,连续13周。染毒过程中实时观察大鼠一般状况,在染毒第12周开始对大鼠进行为期10 d的生殖道涂片,观察其动情周期。染毒结束后第2天处死大鼠,取卵巢组织进行HE染色,观察组织病理学变化。ELISA 法检测大鼠血清促性腺激素释放激素(GnRH)、卵泡刺激素(FSH)、黄体生成素(LH)、雌二醇(E2)水平。实验结果均以均数±标准差( \overlinex\pm s )表示;多组间比较采用单因素方差分析,组间的两两比较用 LSD检验法。检验水准α=0.05。

    结果

    染毒4周后,Beta-CYP组与Beta-CYP+EMB组大鼠表现持续亢奋,易激,EMB组出现精神欠佳、活动减少、反应迟缓症状,而对照组大鼠无异常。到染毒的第90天,对照组大鼠体重升至(314.51±2.44)g,Beta-CYP+EMB组大鼠体重仅升至(253.47±1.50)g。对照组大鼠各类细胞形态无异常变化,Beta-CYP组、EMB组以及Beta-CYP+EMB组大鼠均出现体积较小的深染核,Beta-CYP+EMB组大鼠角化上皮细胞形态发育异常。与对照组大鼠的动情周期(97.83±4.17)h相比,Beta-CYP组与EMB组大鼠动情周期分别延长至(134.33±7.53)h、(126.50±5.28)h,Beta-CYP+EMB组大鼠动情周期延长至(156.00±6.66)h。方差分析结果表明,Beta-CYP+EMB组大鼠动情间期阴道涂片中白细胞(527.17±15.83)、角化上皮细胞(35.67±4.32)、未角化上皮细胞(70.50±4.51)的细胞数相比于对照组(分别为752.50±28.89,50.50±2.74,101.33±7.92)均降低,且差异具有统计学意义(均P<0.001)。对照组大鼠GnRH与FSH水平为(5.13±0.59)、(0.76±0.09) IU·L−1,Beta-CYP+EMB组大鼠GnRH与FSH水平分别升至(16.86±0.59)、(3.80±0.19) IU·L−1P<0.05);对照组大鼠LH与E2的水平分别为(12.93±0.81) IU·L−1、(22.23±1.44) pmol·L−1,Beta-CYP+EMB组大鼠LH与E2水平分别降至(5.63±0.41) IU·L−1、(10.45±0.78) pmol·L−1P<0.05)。

    结论

    高效氯氰菊酯和甲维盐联合染毒可能通过干扰HPO轴中生殖激素的分泌最终影响雌鼠动情周期。

     

    Abstract: Backgroud

    Beta-cypermethrin and emamectin benzoate are widely used for the prevention and control of pests in the greenhouse planting industry, and their combined exposure may increase the accumulation of beta-cypermethrin and emamectin benzoate in organisms and affect human health.

    Objective

    Based on the changes in reproductive hormone levels in the hypothalamic-pituitary-ovarian (HPO) axis, to investigate the effect of combined exposure to beta-cypermethrin and emamectin benzoate on the estrous cycle of female mice.

    Methods

    Twenty-four healthy adult SD rats were randomly divided into a blank control group, a beta-cypermethrin group (Beta-CYP, 53 mg·m−3), an emamectin benzoate group (EMB, 8 mg·m−3), and a beta-cypermethrin and emamectin benzoate combined exposure group (Beta-CYP+EMB, Beta-CYP 53 mg·m−3 + EMB 8 mg·m−3). Six rats in each group were exposed to the designed treatment protocol by aerosol inhalation 6 d a week for 13 weeks. The general condition of the rats was observed in real time during the treatment. From the 12th week of exposure, a 10-day reproductive tract smear was performed on the rats to observe the estrous cycle. The rats were neutralized on the second day after the end of the treatment protocol, and the ovarian tissues were stained with HE to observe histopathological changes. Serum levels of gonadotropin-releasing hormone (GnRH), follicle-stimulating hormone (FSH), luteinizing hormone (LH), and estradiol (E2) were measured by ELISA. Experimental results were expressed as mean ± standard deviation ( \overlinex\pm s ). One-way ANOVA was used for comparison among groups, and LSD test for pairwise comparison between groups. The significance level was α=0.05.

    Results

    After four weeks of the treatment protocol, the rats in the Beta-CYP group and the Beta-CYP+EMB group continued to be hyperactive and irritable, while the EMB group showed symptoms of mental disorder, decreased activity, and slow response. On the 90th day of the treatment protocol, the body weight of rats in the control group increased to (314.51±2.44) g, and that in the Beta-CYP+EMB group only increased to (253.47±1.50) g. There was no abnormal cellular morphology in the control group; however, small deeply stained nuclei appeared in the Beta-CYP group, the EMB group, and the Beta-CYP+EMB group, and abnormal morphological development of keratinized epithelial cells in the Beta-CYP+EMB group was found. The estrous cycle of rats in the control group was (97.83±4.17) h, and compared with the control group, the estrous cycles of rats in the Beta-CYP group, the EMB group, and the Beta-CYP+EMB group were prolonged to (134.33±7.53) h, (126.50±5.28) h, and (156.00±6.66) h, respectively. The results of ANOVA showed that the numbers of leukocytes (527.17±15.83), keratinized epithelial cells (35.67±4.32), and non-keratinized epithelial cells (70.50±4.51) in the vaginal smears during diestrus in the Beta-CYP+EMB group were significantly lower than those in the control group (752.50±28.89, 50.50±2.74, 101.33±7.92) (P<0.001). The hormone levels of GnRH and FSH in the control group were (5.13±0.59) and (0.76±0.09) IU·L−1 respectively, while the levels in the Beta-CYP+EMB group were increased to (16.86±0.59) and (3.80±0.19) IU·L−1 respectively (P<0.05). The levels of LH and E2 in the control group were (12.93±0.81) IU·L−1 and (22.23±1.44) pmol·L−1 respectively, and the levels in the Beta-CYP+EMB group were decreased to (5.63±0.41) IU·L−1 and (10.45±0.78) pmol·L−1 respectively (P<0.05).

    Conclusion

    The combined exposure to beta-cypermethrin and emamectin benzoate may ultimately affect the estrous cycle of female rats by interfering with the secretion of reproductive hormones involved in the HPO axis.

     

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