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Conditions for silylation of benzidine (BZ) and 3,3′-dichlorobenzidine (DCBZ) have been optimized. Reactivity, repeatability, and derivative stability were compared for the silylating reagents N-Methyl-N-(trimethylsilyl)trifluoroacetamide (MSTFA) and N-Methyl-N-(tert-butyldimethylsilyl)trifluoroacetamide (MTBDMSTFA) and the catalysts 3% trimethylsilylimidazole (TMS-I) and 0.3% NH4-I–dithioerythritol. The results showed that derivatization with MTBDMSTFA/NH4-I containing 0.1 mg dithioerythritol was superior to other methods. The silylation conditions selected were reaction with (MTBDMSTFA)–NH4I, 1000:3, with catalysis by dithioerythritol, at 80 °C for 80 min. The TBDMS derivatives of BZ and DCBZ had very good chromatographic properties and very sensitive detection was achieved by gas chromatography with electron-impact ionization mass spectrometry (GC-EIMS). Simultaneous determination of BZ and DCBZ in water was developed on the basis of the TBDMS derivatives. Deuterated BZ (d8-BZ) was chosen as internal standard (IS) for analysis of water samples. BZ and DCBZ were extracted from water at pH 8.5 with dichloromethane and the extract was then dried and silylated. Recoveries of BZ and DCBZ were approximately 102 and 103% at a concentration of 2.0 ng mL−1. The coefficients of variation for BZ and DCBZ were less than 9 and 4% at concentrations of 0.2 and 0.5 ng mL−1, respectively. The method detection limits for 200 mL water were 0.004 ng mL−1 for BZ and 0.02 ng mL−1 for DCBZ.  相似文献   
2.
A liquid chromatography-electrospray ionization tandem mass spectrometric method (LC-ESI-MS/MS) has been developed for the determination of benzidine (BZ) and 3, 3′-dichlorobenzidine (DCBZ) from surface water. Parent ion of DCBZ gave strong signal with ESI by dissolving with 15?mM ammonium formate, which is also used as mobile phase. Deuterated BZ (d8-BZ) was chosen as the internal standard (IS). BZ and DCBZ were extracted by solid-phase extraction on Oasis hydrophilic-lipophilic balance (HLB) from water at pH 8.0. The coefficients of variation of BZ and DCBZ were less than 13.1% and the detection limits were 0.004?ng?L?1 for BZ and 0.7?ng?L?1 for DCBZ using 0.5?L surface water. The detection limit shows fair lower value than the water quality criteria for BZ and DCBZ established by the US EPA. When the proposed method was used to analyze the target compounds in sixteen surface water samples, BZ was detected in a concentration range of 0.15–2.33?ng?L?1 in four of sixteen surface water samples  相似文献   
3.
甲醛还原法制备2,2'-二氯氢化偶氮苯   总被引:15,自引:0,他引:15  
二氯氧化偶氮苯;二氯联苯胺;还原过程;甲醛还原法制备2;2'-二氯氢化偶氮苯  相似文献   
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