The concentrations of functionalized polycyclic aromatic hydrocarbons (PAHs), i.e., oxygenated PAHs (OPAHs), nitrated PAHs (NPAHs), and chlorinated PAHs (ClPAHs), in soluble organic fractions of automobile exhaust particles (NIST SRM 1975 and NIES CRM No.8) and airborne particles (NIST SRM1648a and PM2.5 collected at Kyoto, Japan) were simultaneously determined using gas chromatography-mass spectrometry with negative chemical ionization (GC-NCI-MS). The concentrations of PAH derivatives in standard reference materials determined by GC-NCI-MS were in good agreement with the certified and literature values. Ten OPAHs, 12 NPAHs, and 12 ClPAHs were detected in ambient PM2.5 collected in Kyoto, Japan by the proposed analytical method. 28 OPAHs, 37 NPAHs, and 16 ClPAHs and applied the method to their quantification in SRMs and ambient particulate matter samples. MATERIAL AND METHODS Chemicals and reagents The target compounds in this study were 28 OPAHs, 37 NPAHs, and 16 ClPAHs. The abbreviations used for the individual OPAHs, NPAHs, and ClPAHs are shown in Table S1. The analytical standards of OPAHs and NPAHs were purchased from a variety of commercial suppliers. With the exceptions of 2-chloroanthracene (2-ClAnt) and 9-chloroanthracene (9-ClAnt), which were purchased from Sigma-Aldrich (MO, USA), the analytical standards of ClPAHs were synthesized by the authors. The detailed synthetic procedures for these ClPAHs have been reported in previous studies (30, 32, 33). The following deuterated compounds were used as internal standards: 9-fluorenone-d8 (9-FluO-d8), 9,10-anthraquinone-d8 (9,10-AntQ-d8), 1-nitropyrene-d9 (1-NPyr-d9), and 6-nitrobenzo[a]pyrene (6-NBaP-d11). 9-FluO-d8 was purchased from Kanto Chemical Co., Inc. (Tokyo, Japan), and the remaining compounds were purchased from C/D/N Isotopes Inc. (Quebec, Canada). The solvents used for extraction and cleanup were pesticide analysis grade and were obtained from Wako Pure Chemical Industries, Ltd. (Osaka, Japan) or Kanto Chemical Co., Inc.