Howard P C, Beland F A
Department of Environmental Health Sciences, School of Medicine, Case Western Reserve University, Cleveland, OH.
Res Rep Health Eff Inst. 1994 May(66):1-17; discussion 19-25.
Copollutants found in air samples and other complex chemical mixtures may alter the metabolism, and thus the biological activity, of chemical carcinogens. As an initial step to determine whether the metabolism and DNA binding of carcinogenic nitrated polycyclic aromatic hydrocarbons found in diesel exhaust particles are altered by copollutants, we studied the effect of pyrene on the metabolism and DNA binding of 1-nitropyrene, and the effect of pyrene and 1-nitropyrene on the metabolism and DNA adduct formation of 1,6-dinitropyrene in male B6C3F1 mice. In in vitro incubations using liver microsomes from untreated mice, pyrene was a mixed-type inhibitor, with a 6.42-microM appKi. 2-Aminofluorene and 3-amino-2-methoxydibenzofuran were also effective inhibitors of 1-nitropyrene metabolism. Pyrene did not affect the total in vivo excretion of 1-nitropyrene when coadministered to mice at either a 10-fold or a 250-fold molar excess. At the higher dose of pyrene, however, the urinary excretion of 1-nitropyrene metabolites decreased by approximately 20%, whereas the concentration of fecal metabolites increased by the same amount. Similar in vivo experiments were conducted using 2-aminofluorene as the inhibitor. The excretion of 1-nitropyrene was not significantly affected by 2-aminofluorene treatment. Treatment-related DNA adducts were not detected by 32P-postlabeling analyses of liver DNA when 1-nitropyrene was administered by itself or with a 20- or 250-fold molar excess of pyrene. The coadministration of pyrene or 1-nitropyrene had no effect on the total excretion of 1,6-dinitropyrene metabolites. A single major adduct that coeluted with N-(deoxyguanosin-8-yl)-1-amino-6-nitropyrene was detected in hepatic DNA from mice treated with 1,6-dinitropyrene. The concentration of this adduct was significantly decreased by the coadministration of a 25-fold molar excess of pyrene and was significantly increased by simultaneous treatment with a 25-fold molar excess of 1-nitropyrene. These results demonstrate the effect of copollutants on potentially carcinogenic components of diesel exhaust and urban air.
在空气样本和其他复杂化学混合物中发现的共存污染物可能会改变化学致癌物的代谢,进而改变其生物活性。作为确定柴油废气颗粒中发现的致癌性硝化多环芳烃的代谢和DNA结合是否会因共存污染物而改变的第一步,我们研究了芘对1-硝基芘代谢和DNA结合的影响,以及芘和1-硝基芘对雄性B6C3F1小鼠中1,6-二硝基芘代谢和DNA加合物形成的影响。在使用未处理小鼠肝脏微粒体的体外孵育中,芘是一种混合型抑制剂,其表观抑制常数(appKi)为6.42微摩尔。2-氨基芴和3-氨基-2-甲氧基二苯并呋喃也是1-硝基芘代谢的有效抑制剂。当以10倍或250倍摩尔过量与小鼠共同给药时,芘不影响1-硝基芘在体内的总排泄量。然而,在芘的较高剂量下,1-硝基芘代谢物的尿排泄量减少了约20%,而粪便代谢物的浓度则增加了相同的量。使用2-氨基芴作为抑制剂进行了类似的体内实验。2-氨基芴处理对1-硝基芘的排泄没有显著影响。当单独给予1-硝基芘或与20倍或250倍摩尔过量的芘共同给药时,通过对肝脏DNA进行32P后标记分析未检测到与处理相关的DNA加合物。芘或1-硝基芘的共同给药对1,6-二硝基芘代谢物的总排泄没有影响。在用1,6-二硝基芘处理的小鼠肝脏DNA中检测到一种与N-(脱氧鸟苷-8-基)-1-氨基-6-硝基芘共洗脱的单一主要加合物。当以25倍摩尔过量的芘共同给药时,这种加合物的浓度显著降低,而当同时用25倍摩尔过量的1-硝基芘处理时,其浓度显著增加。这些结果证明了共存污染物对柴油废气和城市空气中潜在致癌成分的影响。