Hoivik Debie J, Qualls Charles W, Mirabile Rosanna C, Cariello Neal F, Kimbrough Carie L, Colton Heidi M, Anderson Steven P, Santostefano Michael J, Morgan Ronda J Ott, Dahl Ray R, Brown Alan R, Zhao Zhiyang, Mudd Paul N, Oliver William B, Brown H Roger, Miller Richard T
GlaxoSmithKline Pharmaceuticals, Five Moore Drive, Research Triangle Park, North Carolina, USA and Upper Merion, Pennsylvania, USA.
Carcinogenesis. 2004 Sep;25(9):1757-69. doi: 10.1093/carcin/bgh182. Epub 2004 May 6.
There is little primate risk factor data in the literature evaluating the relationship between proposed mechanisms of PPAR agonist-induced hepatocarcinogenesis at clinically relevant therapeutic exposures. These studies were conducted to characterize the hepatic effects of fenofibrate and ciprofibrate in the cynomolgus monkey. Male cynomolgus monkeys were given fenofibrate (250, 1250 or 2500 mg/kg/day) or ciprofibrate (3, 30, 150 or 400 mg/kg/day) for up to 15 days. The highest doses used were approximately 4 times (fenofibrate) and 9.4 times (ciprofibrate) the human therapeutic exposure for these agents based on AUC (area under the curve). For both compounds, there was a treatment-related increase in liver weight and periportal hepatocellular hypertrophy, which was related to increases in peroxisomes (up to 2.8 times controls) and mitochondria (up to 2.5 times controls). An increase in smooth endoplasmic reticulum probably contributed to the hypertrophy. There was no indication of cell proliferation as determined by the number of mitotic figures and this was confirmed by evaluating cell proliferation by immunohistochemical staining for the Ki-67 antigen. Consistent with the findings by light microscopy, there was no treatment-related effect on the level of mRNA for proteins known to be involved in the control of hepatocyte cell division or apoptosis (e.g. P21, Cyclin D1, PCNA, CDKN1A). Furthermore, there was minimal indication of oxidative stress. Thus, there was no evidence of lipofuscin accumulation, and there was no remarkable increase in the mRNA levels for most proteins known to respond to oxidative stress (e.g. catalase, glutathione peroxidase). A mild induction in the mRNA levels of cellular beta-oxidation and detoxification enzymes (e.g. acyl CoA oxidase, thioredoxin reductase) was observed. Collectively, the data from these studies suggest that the primate responds to PPARalpha agonists in a manner that is different from the rodent suggesting that the primate may be refractory to PPAR-induced hepatocarcinogenesis.
在文献中,几乎没有灵长类动物的风险因素数据来评估在临床相关治疗暴露水平下,PPAR激动剂诱导肝癌发生的潜在机制之间的关系。开展这些研究是为了明确非诺贝特和环丙贝特对食蟹猴肝脏的影响。给雄性食蟹猴服用非诺贝特(250、1250或2500毫克/千克/天)或环丙贝特(3、30、150或400毫克/千克/天),持续15天。基于曲线下面积(AUC),所使用的最高剂量分别约为这些药物人类治疗暴露量的4倍(非诺贝特)和9.4倍(环丙贝特)。对于这两种化合物,均出现了与治疗相关的肝脏重量增加和门周肝细胞肥大,这与过氧化物酶体(高达对照的2.8倍)和线粒体(高达对照的2.5倍)数量增加有关。滑面内质网的增加可能导致了肥大。通过有丝分裂象数量确定,未发现细胞增殖迹象,通过对Ki-67抗原进行免疫组化染色评估细胞增殖也证实了这一点。与光镜检查结果一致,对于已知参与肝细胞分裂或凋亡控制的蛋白质(如P21、细胞周期蛋白D1、增殖细胞核抗原、CDKN1A)的mRNA水平,未发现与治疗相关的影响。此外,氧化应激迹象极少。因此,没有脂褐素积累的证据,并且对于大多数已知对氧化应激有反应的蛋白质(如过氧化氢酶、谷胱甘肽过氧化物酶),其mRNA水平也没有显著增加。观察到细胞β氧化和解毒酶(如酰基辅酶A氧化酶、硫氧还蛋白还原酶)的mRNA水平有轻度诱导。总体而言,这些研究的数据表明,灵长类动物对PPARα激动剂的反应方式与啮齿动物不同,这表明灵长类动物可能对PPAR诱导的肝癌发生具有抗性。