Trentacoste S V, Friedmann A S, Youker R T, Breckenridge C B, Zirkin B R
Department of Biochemistry and Molecular Biology, Johns Hopkins School of Hygiene and Public Health, Baltimore, Maryland 21205, USA.
J Androl. 2001 Jan-Feb;22(1):142-8.
Previous studies have reported that atrazine, a widely used herbicide that selectively inhibits photosynthesis in broadleaf and grassy weeds, has adverse effects on reproductive function in the male, suggesting a direct effect of atrazine on the hypothalamicpituitary-testicular axis. As yet, however, no studies have critically examined the doses of atrazine that elicit such effects, and few have focused on the mechanism by which atrazine acts. Herein we report a dose-response study of the effects of atrazine ingestion on reproductive function in male Sprague-Dawley rats during a critical developmental period, the peripubertal period. Atrazine was administered by gavage to rats from day 22 to day 47 of age, at doses of 1-200 mg/kg body weight per day. Atrazine administration of up to 50 mg/kg per day had no effect on any of the measured variables. Serum testosterone concentration was reduced by atrazine at doses of 100 and 200 mg/kg per day, as were seminal vesicle and ventral prostate weights. Intratesticular testosterone concentration was reduced in parallel with serum testosterone, suggesting that the reductions in serum testosterone resulted from reduced testosterone production by Leydig cells or from changes in testosterone metabolism within the testis, or both. Serum luteinizing hormone (LH) concentration was reduced despite the reduced serum testosterone, suggesting an effect on the hypothalamus, the pituitary gland, or both. At the termination of the study, the average body weight of rats receiving atrazine at 100 mg/kg per day was found to be reduced by approximately 9%. This suggested the possibility that the effects of atrazine on the reproductive tract may not be direct, but rather, the noted deficits of the male reproductive tract resulted from reduced food intake by the treated rats. We tested this by feeding control (vehicle-gavaged) rats amounts of food equivalent to that consumed by the atrazine-fed rats, and then assessing reproductive tract endpoints. Even mild food restriction resulted in reductions in serum testosterone concentration, in the weights of androgen-dependent organs, and in serum LH concentration; the same deficits that were seen in atrazine-gavaged rats. Indeed, the effects of atrazine on the male reproductive tract seen in rats receiving atrazine at greater than 50 mg/kg per day could not be distinguished from the effects of reduced food consumption. These results suggest that caution must be exercised before concluding that atrazine (or any potentially toxic chemical) has direct, detrimental effects.
先前的研究报道,阿特拉津是一种广泛使用的除草剂,可选择性抑制阔叶杂草和禾本科杂草的光合作用,对雄性生殖功能有不良影响,这表明阿特拉津对下丘脑 - 垂体 - 睾丸轴有直接作用。然而,迄今为止,尚无研究严格考察引发此类效应的阿特拉津剂量,且很少有研究关注阿特拉津的作用机制。在此,我们报告一项关于在关键发育时期即青春期前后,雄性斯普拉格 - 道利大鼠摄入阿特拉津对生殖功能影响的剂量反应研究。从第22天至第47天,通过灌胃法给大鼠施用阿特拉津,剂量为每天每千克体重1 - 200毫克。每天施用高达50毫克/千克的阿特拉津对任何测量变量均无影响。每天剂量为100毫克/千克和200毫克/千克的阿特拉津会降低血清睾酮浓度,精囊和腹侧前列腺重量也会降低。睾丸内睾酮浓度与血清睾酮平行降低,这表明血清睾酮降低是由于睾丸间质细胞睾酮生成减少或睾丸内睾酮代谢变化,或两者兼而有之。尽管血清睾酮降低,但血清促黄体生成素(LH)浓度仍降低,这表明对下丘脑、垂体或两者均有影响。在研究结束时,发现每天接受100毫克/千克阿特拉津的大鼠平均体重降低了约9%。这表明阿特拉津对生殖道的影响可能不是直接的,相反,所观察到的雄性生殖道缺陷是由受试大鼠食物摄入量减少导致的。我们通过给对照(灌胃赋形剂)大鼠喂食与阿特拉津喂养大鼠消耗的食物量相当的食物,然后评估生殖道终点来对此进行测试。即使是轻度的食物限制也会导致血清睾酮浓度降低、雄激素依赖性器官重量降低以及血清LH浓度降低;这些缺陷与灌胃阿特拉津的大鼠中所见相同。实际上,每天接受超过50毫克/千克阿特拉津的大鼠中观察到的阿特拉津对雄性生殖道的影响与食物消耗减少的影响无法区分。这些结果表明,在得出阿特拉津(或任何潜在有毒化学物质)具有直接有害影响的结论之前,必须谨慎行事。