ABSTRACT:Geranyl nitrile (GN) and citronellyl nitrile (CN) are fragrance components used in consumer and personal care products. Differences in the clastogenicity of these two terpenes are postulated to result from differential biotransformation, presumably involving the conjugated nitrile moiety. The metabolic clearance and biotransformation of GN and CN were compared in primary hepatocytes from mice, rats, and humans. For determination of intrinsic clearance, GN and CN were incubated with hepatocytes in sealed vials, and the headspace was sampled periodically by solid-phase microextraction and analyzed by gas chromatography/mass spectrometry. For metabolite identification, GN and CN were incubated with hepatocytes from each species for 60 min, and reaction mixtures were extracted and analyzed by mass spectroscopy. Both GN and CN were rapidly metabolized in hepatocytes from all species (T 1/2 , 0.7-11.6 min). Within a species, intrinsic clearance was similar for both compounds and increased in the order human < rat Ͻ Ͻ mouse. Major common pathways for biotransformation of GN and CN involved 1) epoxidation of the 6-alkenyl moiety followed by conjugation with glutathione, 2) hydroxylation of the terminal methyl group(s) followed by direct conjugation with glucuronic acid in rodents or further oxidation to the corresponding acid in human cells, and 3) hydroxylation of the allylic C 5 position. No evidence for either phase I or phase II metabolism of the conjugated nitrile moiety was obtained. Thus, the presumed metabolic basis for differences in genotoxicity remains elusive.Geranyl nitrile (3,7-dimethyl-2,6-octadienenitrile, GN) and citronellyl nitrile (3,7-dimethyl-6-octenenitrile, CN) are monoterpene nitriles used extensively as fragrance ingredients (Fig. 1). Commercial GN consists of an isomeric mixture of geranyl nitrile (E isomer) and neryl nitrile (Z isomer). These compounds are common components in a wide variety of consumer products, including soaps, shampoos, cosmetics, perfumes, detergents, and insect repellents. In 1995 and 1996, 238 metric tons of GN and 45 metric tons of CN were used worldwide (Potter et al., 2001). The primary expected route of human exposure for both compounds is via dermal contact. However, there is also potential for oral exposure from detergent residues on dinnerware and for inhalation exposure via volatilization or aerosol formation. The extent of systemic bioavailability of these compounds by the various potential routes of human exposure has not been assessed.The acute toxicity of both nitriles is low, with oral LD 50 values in rats of approximately 3 g/kg for both compounds and dermal LD 50 values in rabbits of approximately 4 g/kg (RIFM, 1974a,b). The acute toxicity of geranyl nitrile is also low by the inhalation route, with a 4-h LC 50 greater than 5.2 mg/l [BASF (1989) Acute toxicity studies on geranyl nitrile and citronellyl nitrile (unpublished report)]. In a 28-day subchronic study, decreased body weight, minor changes in clinical chemistry and urinalysis parameters, ...