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Updated: Jan 17, 2026

On-line Analysis of Nitrogen Containing Compounds in Complex Hydrocarbon Matrixes
Published on: August 5, 2016
Nitrogen Isotope Analysis of Aliphatic and Aromatic Amines by GC-C-IRMS and the Application for Tracing Atmospheric
Heizeng Chen1,2, Zicong Wang1,2, Meicheng Wen1,2
1Guangdong Key Laboratory of Environmental Catalysis and Health Risk Control, Guangdong-Hong Kong-Macao Joint Laboratory for Contaminants Exposure and Health, Institute of Environmental Health and Pollution Control, Guangdong University of Technology, Guangzhou, China.
Rationale:
Compounds-specific stable isotope analysis (CSIA) is an advanced tool for assessing the sources and fates of organic amines in environments. The use of gas chromatography-combustion-isotope ratio mass spectrometry (GC-C-IRMS) remains constrained by the thermal stability, high polarity, and the typically low environmental concentrations of organic amines.
Methods:
The development of suitable derivatization strategies for polar organic amines can broaden the applicability of GC-C-IRMS. To establish a nitrogen stable isotope analytical method for polar organic amines in the atmosphere, derivatization with isobutyl chloroformate (IBCF) reagent was adopted. Method performance was evaluated using six aliphatic amines and three aromatic amines.
Results:
The derivatization method demonstrated good reproducibility, high linearity, and no detectable isotopic fractionation. Accurate and precise nitrogen stable isotope measurements were achieved using the IBCF derivatization reagent. Deviations of δ15N values from reference measurements obtained by elemental analyzer-isotope ratio mass spectrometry (EA-IRMS) were small (< 0.3‰) and within the typical uncertainty of GC-C-IRMS (< 0.6‰). Method detection limits (MDLs) for the nine organic amines ranged from 2.06 to 4.12 nmol N injected on column.
Conclusions:
The applicability of the developed method was demonstrated through analysis of atmospheric methylamine (MA). The measured δ15N values of MA varied significantly across sources, ranging from -11.6‰ to -9.1‰ for vehicular exhaust, -20.2‰ to -15.7‰ for coastal samples, and -26.7‰ to -22.2‰ for municipal solid waste sanitary sources, indicating that δ15N values effectively distinguish MA sources.
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