[Rats' reproductive function under toxic load against the background of protein deficiency].

Q2 Medicine
Voprosy pitaniia Pub Date : 2024-01-01 Epub Date: 2024-09-16 DOI:10.33029/0042-8833-2024-93-5-85-93
S I Shestakova, A A Stankevich, D S Kotova, M D Trebukh, N S Nikitin, E O Sadykova, N V Tyshko
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引用次数: 0

Abstract

Safety assessment approaches of novel food, currently adopted in the Russian Federation, imply mandatory in vivo reproductive toxicity tests with the study of reproductive function and offspring development in order to obtain comprehensive evidence of the absence of distant adverse effects that may manifest only in the next generation. Comprehensive study of reproductive function, pre- and postnatal offspring development, as a rule, includes the research of a large number of parameters, all of which has a wide range of physiological fluctuations, and the heterogeneous distribution of some parameters' values complicates the interpretation of the results. The purpose of the study was to investigate the efficiency of a reduced adaptive potential model in rats, based on decreased diet protein intake, for the use in reproductive toxicity experiments. Material and methods. The research lasting 155 days was carried out on rats of F0 (180 females and 90 males) and F1 (773 pups, 456 fetuses) generations. Animals of parental generation F0 were divided into 3 groups - control, the 1st and the 2nd test groups, 30 males and 60 females in each. The initial age of F0 rats was 28-35 days. Animals of all groups during growth and sexual maturation (25-90 days of life) received a diet with reduced protein content (9.4 g per 100 g of diet, which is 9% in calorie value). After reaching the age of physiological maturity (100 days) rats were transferred to a diet with lower protein content (6.1 g per 100 g of diet, 6% in calorie value), and received this diet during mating, pregnancy and feeding of F1 offspring. The rats of the test groups received with feed the model herbicide glyphosate (isopropylamine salt, concentration 360 g/l) at a dose of 0.3 g/kg body weight (6% of LD50): the 1st test group - from day 70 of life, the 2nd test group - from day 30 of life throughout the duration of the experiment. Reproductive function was evaluated by the fertility of F0 animals and by the character of prenatal and postnatal development of F1 offspring. Results. The toxic factor's influence on the background of reduced protein supply did not lead to complex changes in the reproductive function of rats, the test groups differed from the control group only by the post-implantation loss and the mean litter size in the postnatal period: post-implantation loss in the 1st and the 2nd test groups was higher than normal, exceeding the value of this indicator in the control group (4.7±1.6%) by 3.1 (p<0.05) и 2.2 (р>0.05) times; the mean litter size in the 1st and the 2nd test groups was by 15.8 and 21.3% (р<0.05) lower than in the control group. Survival rate of offspring during the 1st month of life in all groups was at least 72%, which corresponds to the lower limit of the norm characteristic for Wistar rats. Conclusion. The use of the alimentary model of adaptation potential reduction based on diet protein deficiency does not consider appropriate in reproductive toxicity studies, since it does not increase either the severity of the reaction to toxic effects or the reliability of the results obtained. This model can be recommended for subacute toxicological studies of low-toxicity objects, in particular, when assessing the safety of novel food.

[蛋白质缺乏背景下毒性负荷下的大鼠生殖功能]。
俄罗斯联邦目前采用的新型食品安全评估方法意味着必须进行体内生殖毒性试验,研究生 殖功能和后代发育情况,以获得全面证据,证明不存在只在下一代中才可能出现的远期不良影 响。对生殖功能、产前和产后后代发育的综合研究通常包括对大量参数的研究,所有这些参数的生理波动范围都很大,而且某些参数值的异质性分布也使结果的解释变得复杂。本研究的目的是在减少饮食蛋白质摄入量的基础上,研究大鼠适应潜能降低模型在生殖毒性实验中的应用效率。材料和方法这项为期 155 天的研究以 F0 代(180 只雌性和 90 只雄性)和 F1 代(773 只幼鼠和 456 只胎儿)大鼠为对象。亲代 F0 大鼠分为 3 组--对照组、第一试验组和第二试验组,每组 30 只雌雄大鼠。F0 大鼠的初始年龄为 28-35 天。各组动物在生长和性成熟期间(25-90 天)均食用蛋白质含量较低的食物(每 100 克食物中含 9.4 克蛋白质,热量值为 9%)。大鼠达到生理成熟年龄(100 天)后,转而食用蛋白质含量较低的食物(每 100 克食物中含 6.1 克蛋白质,热量值为 6%),并在交配、怀孕和喂养 F1 后代期间食用这种食物。试验组大鼠在饲料中添加了除草剂草甘膦(异丙胺盐,浓度为 360 克/升),剂量为 0.3 克/千克体重(相当于半数致死剂量的 6%):第一试验组大鼠从出生后第 70 天开始,第二试验组大鼠从出生后第 30 天开始,在整个试验过程中一直服用草甘膦。生殖功能通过 F0 动物的生育能力以及 F1 后代的产前和产后发育特征进行评估。实验结果在蛋白质供应减少的背景下,毒性因素的影响并未导致大鼠生殖功能的复杂变化,试验组与对照组的区别仅在于植入后损失和产后平均窝产仔数:第 1 和第 2 试验组的植入后损失高于正常值,比对照组的该指标值(4.7±1.6%)的3.1倍(P0.05);第1和第2试验组的平均窝产仔数分别为15.8%和21.3%(р结论。在生殖毒性研究中,使用基于日粮蛋白质缺乏的消化道适应潜能下降模型并不合适,因为它既不会增加毒性反应的严重性,也不会提高所获结果的可靠性。在对低毒性物体进行亚急性毒理学研究时,尤其是在评估新型食品的安全性时,可以推荐使用这种模式。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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来源期刊
Voprosy pitaniia
Voprosy pitaniia Medicine-Medicine (all)
CiteScore
2.00
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