Natl Toxicol Program Tech Rep Ser. 1990 Feb;313:1-140.
Mirex (95% pure), formerly used a systemic insecticide and as a fire retardant, was studied for toxicologic and carcinogenic effects by administering diets containing 0, 0.1, 1.0, 10, 25, or 50 ppm mirex to groups of 52 F344/N rats of each sex for 104 weeks. Doses selected for the 2-year studies were based primarily on the effects on body weights and survival of rats in a 26-week study. During the first 6 months of the 2-year study, because of good survival and the absence of observable toxic effects in female rats, additional groups (termed second study) of 52 F344/N female rats were started at higher dietary concentrations of 0, 50, and 100 ppm mirex. Based on feed consumption data, the estimated average intake per day was 0, 0.007, 0.075, 0.75, 1.95, and 3.85 mg mirex/kg body weight for male rats and female rats in the first study, and 0, 3.9, and 7.7 mg/kg for female rats in the additional study. Body Weights, Feed Consumption, and Survival in Two-Year Studies: Mean body weights of male rats that received 25 or 50 ppm mirex were 5%-18% lower than those of the controls throughout most of the study; mean body weights of female rats that received 50 or 100 ppm mirex were 4%-18% lower than those of the controls after week 40; mean body weights of groups receiving 0.1, 1.0, or 10 ppm were similar to those of controls. Feed consumption by dosed male rats was 83%-91% that by controls, and that by dosed female rats was 86%-99% that by controls. The top dietary exposure groups of rats received the equivalent of 3.85 mg mirex/kg body weight, whereas the 100-ppm group of female rats (second study) averaged 7.7 mg/kg. At the end of the study, survival of male rats that received 25 or 50 ppm of mirex was lower than that of controls, whereas survival of all dosed groups of female rats was similar to that of controls (male: control, 44/52; 0.1 ppm, 37/52; 1 ppm, 36/52; 10 ppm, 37/52; 25 ppm, 19/52; 50 ppm, 15/52; female-- first study: 38/52; 38/52; 35/52; 41/52; 35/52; female-- second study: control, 44/52; 50 ppm, 44/52; 100 ppm, 39/52). Nonneoplastic and Neoplastic Effects in the Two-Year Studies: The most notable compound-related effects were observed in the liver of male and female rats. Fatty metamorphosis, cytomegaly, angiectasis (males only), and necrosis of the liver were observed at increased incidences in dosed rats. The incidences of of neoplastic nodules of the liver were dose related, and in the 10-, 25-, and 50-ppm groups of males and the 50- and 100-ppm groups of females (second study), they were markedly greater than those in controls (52/group-- male: control, 3; 0.1 ppm, 5; 1 ppm, 5;10 ppm, 14; 25 ppm, 15; 50 ppm, 26; female (second study): control, 2; 50 ppm, 23; 100 ppm, 30). In the first study in female rats, the incidences of neoplastic nodules were not significantly different between control and dosed groups (10; 5; 4; 5; 9; 7). The 10 neoplastic nodules of the liver seen in the control group (19%) was significantly greater than the mean incidence observed historically (57/2,015; 2.8%). The incidences of hepatocellular carcinomas in control and dosed groups were relatively low and were not significantly different between groups. The incidences of pheochromocytomas of the adrenal gland occurred with a positive trend in male rats (8/51; 7/52; 13/52; 11/52; 18/51, 19/51); the incidences in the 25- and 50-ppm male rats were greater than that in controls; malignant pheochromocytomas were observed in 2 controls and in 2 mirex-exposed male rats. The incidence of pheochromocytomas in 50-ppm female rats in the first study was marginally greater than that in controls (control, 1/51; 50 ppm, 6/52); this borderline increase was not observed in the second female rat study and thus is not considered to be due to the dietary administration of mirex. Nephropathy occurred at similar incidences in control and mirex-exposed groups of male and female rats; however, the severity of this nonneoplastic lesion was judged to be slightly greater in the groups given 25, 50, or 100 ppm mirex (male: severe vs. moderate in controls; femas given 25, 50, or 100 ppm mirex (male: severe vs. moderate in controls; female: moderate to severe vs. moderate). Hyperplasia of the transitional epithelium of the kidney pelvis was observed in dosed male rats (0/51; 2/51; 2/52; 5/52; 14/51; 9/52). Transitional cell papillomas of the renal pelvis in male rats occurred with a positive trend (P<0.02) (0/51; 0/51; 0/52; 1/51; 3/52). The highest incidence previously observed in untreated male F344/N rats in NTP studies is 1/48, and the mean historical incidence is 5/1,968 (0.3%). In both the first and second studies in female rats, the incidence of mononuclear cell leukemia showed dosed-related increases (first study: 8/52; 8/52; 11/52; 14/52; 18/52; 18/52; second study: 6/52; 9/52; 14/52). When the data from both studies are combined, the incidences are significantly increased in the 10-, 25-, 50-, and 100-ppm groups. The mean historical incidence is 19% (375/2,021). For the thyroid gland, there was a positive trend for follicular cell neoplasms in male rats (0/51; 1/50; 0/47; 1/47; 0/35; 4/49) and a negative trend for C-cell neoplasms in male rats (8/51; 6/50; 4/47; 7/47; 3/35; 0/49) and infemale rats in the first study (12/50; 13/50; 7/48; 9/47; 6/48; 2/46). Neither observation is considered to be associated with the dietary administration of mirex. Genetic Toxicology: Mirex was not mutagenic in the Salmonella typhimurium-microsome assay when tested in a preincubation protocol in the presence or absence of exogenous metabolic activation in strains TA98, TA100, TA1535, or TA1537. Mirex did not induce either sister chromatid exchanges or chromosomal aberrations in Chinese hamster ovary cells in the presence or absence of S9. Conclusions: Under the conditions of these 2-year feed studies of mirex, there is clear evidence of carcinogenic activity for male and female F344/N rats, as primarily indicated by marked increased incidences of benign neoplastic nodules of the liver, as well as by increased incidences of pheochromocytomas of the adrenal gland and transitional cell papillomas of the kidney in males and by increased incidences of mononuclear cell leukemia in females. Nonneoplastic effects induced by mirex include cytomegaly, fatty metamorphosis, angiectasis (males only), and cellular necrosis in the liver. Synonyms and Trade Names: 1,1a,2,2,3,3a,4,5,5,5a,5b,6-dodecachlorooctahydro-1,3,4-metheno-1H-cyclobta[cd]pentalene; hexachloropentadiene dimer; dodecachloropentacyclodecane; perchloropentacyclodecane; hexachlorocyclopentadiene dimer; Dechloranereg.; Ferriamicidereg.
灭蚁灵(纯度95%),曾用作全身性杀虫剂和阻燃剂,通过给每组52只不同性别的F344/N大鼠喂食含0、0.1、1.0、10、25或50 ppm灭蚁灵的饲料,持续104周,来研究其毒理学和致癌作用。两年研究中所选剂量主要基于26周研究中对大鼠体重和存活率的影响。在两年研究的前6个月,由于雌性大鼠存活率高且未观察到明显毒性作用,另外启动了几组(称为第二项研究)52只F344/N雌性大鼠,喂食更高浓度(0、50和100 ppm)的灭蚁灵饲料。根据饲料消耗数据,第一项研究中雄性和雌性大鼠每天的估计平均摄入量分别为0、0.007、0.075、0.75、1.95和3.85 mg灭蚁灵/千克体重,第二项研究中雌性大鼠为0、3.9和7.7 mg/千克。
两年研究中的体重、饲料消耗和存活率:在大部分研究期间,摄入25或50 ppm灭蚁灵的雄性大鼠平均体重比对照组低5%-18%;摄入50或100 ppm灭蚁灵的雌性大鼠在第40周后平均体重比对照组低4%-18%;摄入0.1、1.0或10 ppm的组平均体重与对照组相似。给药雄性大鼠的饲料消耗量为对照组的83%-91%,给药雌性大鼠为对照组的86%-99%。大鼠的最高饮食暴露组摄入相当于3.85 mg灭蚁灵/千克体重,而100 ppm雌性大鼠组(第二项研究)平均为7.7 mg/千克。研究结束时,摄入25或50 ppm灭蚁灵的雄性大鼠存活率低于对照组,而所有给药雌性大鼠组的存活率与对照组相似(雄性:对照组,44/52;0.1 ppm,37/52;1 ppm,36/52;10 ppm,37/52;25 ppm,19/52;50 ppm,15/52;雌性 - 第一项研究:38/52;38/52;35/52;41/52;35/52;雌性 - 第二项研究:对照组,44/52;50 ppm,44/52;100 ppm,39/52)。
在雄性和雌性大鼠的肝脏中观察到最显著的与化合物相关的效应。给药大鼠肝脏中脂肪变性、细胞肿大、血管扩张(仅雄性)和坏死的发生率增加。肝脏肿瘤性结节的发生率与剂量相关,在雄性10、25和50 ppm组以及雌性50和100 ppm组(第二项研究)中,明显高于对照组(每组52只 - 雄性:对照组,3个;0.1 ppm,5个;1 ppm,5个;10 ppm,14个;25 ppm,15个;50 ppm,26个;雌性(第二项研究):对照组,2个;50 ppm,23个;100 ppm,30个)。在雌性大鼠的第一项研究中,对照组和给药组之间肿瘤性结节的发生率无显著差异(10个;5个;4个;5个;9个;7个)。对照组中观察到的10个肝脏肿瘤性结节(19%)明显高于历史观察到的平均发生率(57/2,015;2.8%)。对照组和给药组肝细胞癌的发生率相对较低,组间无显著差异。雄性大鼠肾上腺嗜铬细胞瘤的发生率呈上升趋势(8/51;7/52;13/52;11/52;18/51,19/51);25和50 ppm雄性大鼠的发生率高于对照组;在2只对照组和2只接触灭蚁灵的雄性大鼠中观察到恶性嗜铬细胞瘤。第一项研究中50 ppm雌性大鼠嗜铬细胞瘤的发生率略高于对照组(对照组,1/51;50 ppm,6/52);在第二项雌性大鼠研究中未观察到这种临界增加,因此不认为是由于饮食中给予灭蚁灵所致。雄性和雌性大鼠对照组和接触灭蚁灵组肾病的发生率相似;然而,在给予25、50或100 ppm灭蚁灵的组中,这种非肿瘤性病变的严重程度被判定略高(雄性:对照组严重程度与中度相比;给予25、50或100 ppm灭蚁灵的雌性大鼠(雄性:对照组严重程度与中度相比;雌性:中度至严重与中度相比)。给药雄性大鼠中观察到肾盂移行上皮增生(0/51;2/51;2/52;5/52;14/51;9/52)。雄性大鼠肾盂移行细胞乳头状瘤呈上升趋势(P<0.02)(0/51;0/51;0/52;1/51;3/52)。在NTP研究中,未处理的雄性F344/N大鼠先前观察到的最高发生率为1/48,历史平均发生率为5/1,968(0.3%)。在雌性大鼠的第一项和第二项研究中,单核细胞白血病的发生率均呈剂量相关增加(第一项研究:8/52;8/52;11/52;14/52;18/52;18/52;第二项研究:6/52;9/52;14/52)。当两项研究的数据合并时,10、25、50和100 ppm组的发生率显著增加。历史平均发生率为19%(375/2,021)。对于甲状腺,雄性大鼠滤泡细胞肿瘤呈上升趋势(0/51;1/50;0/47;1/47;0/35;4/49),雄性大鼠C细胞肿瘤呈下降趋势(8/51;6/50;4/47;7/47;3/35;0/49),雌性大鼠在第一项研究中也呈下降趋势(12/50;13/50;7/48;9/47;6/48;2/46)。这两种观察结果均不认为与饮食中给予灭蚁灵有关。
在有或无外源性代谢激活的预孵育方案中,于TA98、TA100、TA1535或TA1537菌株中测试时,灭蚁灵在鼠伤寒沙门氏菌 - 微粒体试验中无致突变性。在有或无S9的情况下,灭蚁灵在中华仓鼠卵巢细胞中均未诱导姐妹染色单体交换或染色体畸变。
在这些灭蚁灵的两年饲料研究条件下,有明确证据表明F344/N雄性和雌性大鼠具有致癌活性,主要表现为肝脏良性肿瘤性结节的发生率显著增加,以及雄性肾上腺嗜铬细胞瘤和肾盂移行细胞乳头状瘤的发生率增加,雌性单核细胞白血病的发生率增加。灭蚁灵诱导的非肿瘤效应包括肝脏细胞肿大、脂肪变性、血管扩张(仅雄性)和细胞坏死。
1,1a,2,2,3,3a,4,5,5,5a,5b,6 - 十二氯八氢 - 1,3,4 - 亚甲基 - 1H - 环丁烷[cd]戊搭烯;六氯戊二烯二聚体;十二氯五环癸烷;全氯五环癸烷;六氯环戊二烯二聚体;Dechlorane reg.;Ferriamicide reg.