van Bekkum Y M, van den Broek P H, Scheepers P T, Bos R P
Department of Pharmacology and Toxicology, 235 BEG, University of Nijmegen, P.O. Box 9101, NL-6500 HB Nijmegen, The Netherlands.
Chem Res Toxicol. 1998 Nov;11(11):1382-90. doi: 10.1021/tx980162x.
1-Nitropyrene (1-NP) has been proposed as a marker for exposure to diesel exhaust particles (DEP). Since the extent of the actual intake of 1-NP adsorbed on DEP will be relatively low, sensitive and selective methods are needed regarding human exposure assessment. Two analytical methods are presented for the assessment of 1-NP metabolites in urine of male Sprague-Dawley rats administered a single intragastric dose of native DEP (SRM 2975, 20 mg, 35.7 microgram of 1-NP/g). Enzymatically hydrolyzed urine was extracted using Blue Rayon. The extracts were analyzed directly, using HPLC with postcolumn on-line reduction and fluorescence detection (HPLC-Flu), or were processed further for GC/MS/MS analysis. Although sensitive to several metabolites, the HPLC-Flu method lacked selectivity for quantitation of some important metabolites in rat urinary extracts, and therefore seems suitable for screening purposes only. With regard to GC/MS/MS analysis, derivatization with heptafluorobutyrylimidazole (HFBI) yielded low limits of determination for hydroxy-1-aminopyrenes, hydroxy-N-acetyl-1-aminopyrenes (converted to derivatized hydroxy-1-aminopyrenes by the reagent), and 1-aminopyrene (1.8-9.2 fmol on the column). Derivatization of hydroxy-1-nitropyrenes yielded relatively high limits of determination, and therefore, hydroxy-1-nitropyrenes were reduced to hydroxy-1-aminopyrenes prior to derivatization with HFBI. Intragastric administration of DEP to rats resulted in urinary excretion of 6-hydroxy-N-acetyl-1-aminopyrene, 8-hydroxy-N-acetyl-1-aminopyrene, 6-hydroxy-1-nitropyrene, 8-hydroxy-1-nitropyrene, and 3-hydroxy-1-nitropyrene (7, 1.2, 1.6, 0.3, and 0.5% of the dose within 12 h, respectively). 1-Nitropyrene, N-acetyl-1-aminopyrene, and 3-, 6-, and 8-hydroxy-1-aminopyrene were not observed as urinary metabolites following administration of a single dose of DEP. The observed excretion pattern and urinary metabolite concentrations suggest that 1-NP present on unmodified DEP becomes bioavailable to a large extent and is metabolized in the same way as was previously observed following administration of pure 1-NP. The presented methods are promising for assessment of human exposure to 1-NP, e.g., following exposure to DEP, because of the possibility of analyzing large volumes of urine, the conversion of three types of metabolites to one (the amino metabolites), and the low detection limits that are achieved.
1-硝基芘(1-NP)已被提议作为接触柴油尾气颗粒(DEP)的标志物。由于吸附在DEP上的1-NP实际摄入量相对较低,因此在人体暴露评估方面需要灵敏且具有选择性的方法。本文介绍了两种分析方法,用于评估单次经胃给予天然DEP(标准参考物质2975,20毫克,1-NP含量为35.7微克/克)的雄性Sprague-Dawley大鼠尿液中的1-NP代谢物。酶解后的尿液用蓝光人造丝进行萃取。萃取物直接用带有柱后在线还原和荧光检测的高效液相色谱法(HPLC-Flu)进行分析,或者进一步处理用于气相色谱/串联质谱(GC/MS/MS)分析。尽管HPLC-Flu方法对几种代谢物敏感,但在定量大鼠尿液提取物中的一些重要代谢物时缺乏选择性,因此似乎仅适用于筛查目的。关于GC/MS/MS分析,用七氟丁酰咪唑(HFBI)衍生化后,对羟基-1-氨基芘、羟基-N-乙酰-1-氨基芘(被该试剂转化为衍生化的羟基-1-氨基芘)和1-氨基芘的测定下限较低(柱上为1.8 - 9.2飞摩尔)。羟基-1-硝基芘的衍生化测定下限相对较高,因此,在使用HFBI衍生化之前,先将羟基-1-硝基芘还原为羟基-1-氨基芘。给大鼠经胃给予DEP后,尿液中排泄出6-羟基-N-乙酰-1-氨基芘、8-羟基-N-乙酰-1-氨基芘、6-羟基-1-硝基芘、8-羟基-1-硝基芘和3-羟基-1-硝基芘(12小时内分别占剂量的7%、1.2%、1.6%;0.3%和0.5%)。单次给予DEP后,未观察到1-硝基芘、N-乙酰-1-氨基芘以及3-、6-和8-羟基-1-氨基芘作为尿液代谢物。观察到的排泄模式和尿液代谢物浓度表明,未改性DEP上存在 的1-NP在很大程度上具有生物可利用性,并且其代谢方式与先前给予纯1-NP后观察到的相同。由于能够分析大量尿液、将三种类型的代谢物转化为一种(氨基代谢物)以及实现较低的检测限,本文所介绍的方法在评估人体对1-NP的暴露(例如接触DEP后)方面很有前景。