Harttig U, Hendricks J D, Stoner G D, Bailey G S
Department of Food Science and Technology, Oregon State University, Corvallis 97331-6602, USA.
Carcinogenesis. 1996 Nov;17(11):2403-9. doi: 10.1093/carcin/17.11.2403.
This study investigated pre-initiation and post-initiation effects of dietary ellagic acid (EA) on 7,12-dimethylbenz[a]anthracene (DMBA) multi-organ carcinogenesis in rainbow trout (Oncorhynchus mykiss). EA at 100, 250 (study 2), 1000 and 2000 (study 1) p.p.m. suppressed stomach adenopapilloma incidence by 33, 60, 70 and 78% (P < or = 0.001), respectively, as well as tumor multiplicity (P < 0.01) and size (P < 0.001) when fed continuously following DMBA initiation. However, continuous EA feeding also produced modest (250 p.p.m.) to extensive (1000, 2000 p.p.m.) growth rate suppression in these studies. Retrospective logistic regression modeling of the data allowed separation of growth-related from non-growth-related inhibitory effects. By this approach: (i) tumor development showed a similarly strong dependence (same regression slope) on animal growth rate in all treatment groups; (ii) EA-mediated reduction in mean population growth contributed to suppressed stomach tumor response above 250 p.p.m. EA; and (iii) even at high, toxic doses EA displayed inhibitory mechanisms additional to, and distinct from, growth suppression effect. The effects of post-initiation EA were organ specific. Chronic EA treatment significantly suppressed swim-bladder as well as stomach tumor incidence at doses > or = 1000 p.p.m., but increased liver tumor incidence at doses > or = 250 p.p.m. Three protocols examined EA effects on the initiation process. EA fed at 1000 p.p.m. concurrently with 750 p.p.m. dietary DMBA for 7 weeks modestly reduced stomach tumor incidence (from 85 to 78%, P < 0.05) and multiplicity (from 6.3 +/- 4.3 to 4.9 +/- 2.9, P < 0.01), but did not alter swim-bladder or liver response. The effect of EA pretreatment prior to DMBA single-dose initiation by gill uptake was also examined. When fed for 1 week prior to initiation, 2000 p.p.m. EA again imposed a small reduction in stomach adenoma incidence (from 88 to 78%; P < 0.05) and multiplicity (from 5.5 +/- 3.2 to 4.4 +/- 3.2; P < 0.01). However, when EA was pre-fed for 3 weeks instead of 1 week, protection in the stomach was lost and response in liver and swim-bladder significantly increased. In sum, these studies demonstrate that EA influence on DMBA tumorigenesis in this multi-organ model is highly protocol dependent and organ specific. Post-initiation dietary EA consistently suppressed stomach tumor development in trout, at EA doses far lower than those required for protection in rodents. At higher doses, however, EA also displayed toxicity and a potential in some protocols to enhance tumor response in other organs.
本研究调查了膳食鞣花酸(EA)在虹鳟鱼(Oncorhynchus mykiss)中对7,12-二甲基苯并[a]蒽(DMBA)多器官致癌作用的启动前和启动后效应。在研究2中,100、250 ppm的EA以及在研究1中1000和2000 ppm的EA,在DMBA启动后持续投喂时,分别使胃腺乳头状瘤的发生率降低了33%、60%、70%和78%(P≤0.001),同时使肿瘤多发性(P<0.01)和大小(P<0.001)降低。然而,在这些研究中,持续投喂EA也产生了适度(250 ppm)到广泛(1000、2000 ppm)的生长速率抑制。对数据进行回顾性逻辑回归建模,可将与生长相关的抑制作用和与生长无关的抑制作用区分开来。通过这种方法:(i)在所有治疗组中,肿瘤发展对动物生长速率表现出相似的强烈依赖性(相同的回归斜率);(ii)EA介导的平均群体生长减少导致EA浓度高于250 ppm时胃肿瘤反应受到抑制;(iii)即使在高剂量且有毒的情况下,EA也表现出除生长抑制作用之外且与之不同的抑制机制。启动后EA的作用具有器官特异性。慢性EA处理在剂量≥1000 ppm时显著抑制了鳔以及胃肿瘤的发生率,但在剂量≥250 ppm时增加了肝肿瘤的发生率。三种方案研究了EA对启动过程的影响。在7周内,1000 ppm的EA与750 ppm的膳食DMBA同时投喂,适度降低了胃肿瘤的发生率(从85%降至78%,P<0.05)和多发性(从6.3±4.3降至4.9±2.9,P<0.01),但未改变鳔或肝的反应。还研究了在通过鳃摄取进行DMBA单剂量启动之前EA预处理的效果。在启动前投喂1周,2000 ppm的EA再次使胃腺瘤的发生率略有降低(从88%降至78%;P<0.05)和多发性降低(从5.5±3.2降至4.4±3.2;P<0.01)。然而,当EA预投喂3周而非1周时,胃的保护作用丧失,肝和鳔的反应显著增加。总之,这些研究表明,在这个多器官模型中,EA对DMBA肿瘤发生的影响高度依赖于实验方案且具有器官特异性。启动后膳食EA持续抑制鳟鱼胃肿瘤的发展,所需的EA剂量远低于啮齿动物中的保护剂量。然而,在更高剂量时,EA也表现出毒性,并且在某些方案中有可能增强其他器官的肿瘤反应。