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Cyanogen chloride (ClCN) has been widely used in industrial production. ClCN is also listed in the Schedule of the Chemical Weapons Convention (CWC). The use of traditional colorimetric analysis or gas chromatography for the detection of ClCN has been characterized by low efficiency and poor sensitivity. In this study, a method was established for the qualitative analysis and quantitative detection of ClCN in organic and water matrices by gas chromatography-mass spectrometry (GC-MS) based on thiol derivatization. 1-Butylthiol was selected as the optimal derivatization reagent. The optimal temperature for thiol derivatization in the organic matrices was 40 ℃ and the reaction time was 10 min. The pH for derivatization was approximately 9. The ClCN in the organic matrices was directly analyzed by GC-MS after derivatization. The conditions of ClCN derivatization in the water matrices were the same as those in the organic matrices. After the derivatization of ClCN, headspace-solid phase microextraction (HS-SPME) was employed during sample preparation for water matrices. Different temperatures for HS-SPME were explored, and the optimal temperature was found to be 55 ℃. The product of thiol derivatization was confirmed as butyl thiocyanate. The main fragmentation patterns and mass spectrometric cleavage pathway were investigated by GC-MS/MS. The quantitative determination of ClCN in organic and water matrices was conducted via the internal standard and external standard methods, respectively. ClCN showed good linearity in the corresponding ranges in the organic and water matrices. The correlation coefficients for both matrices were greater than 0.99. The linearities of ClCN in the organic and water matrices were in the range of 20-2000 μg/L and 20-1200 μg/L, respectively. An organic sample and water samples from different substrates were selected to verify the accuracy and precision of the method at three spiked levels. The average spiked recoveries of ClCN in the organic sample and water samples were 87.3%-98.8% and 97.6%-102.2%, respectively. The corresponding relative standard deviations (RSDs, n=6) were 2.1%-4.7% and 2.8%-4.2%. The derivatization method established in this study showed good reaction specificity. The method was successfully applied in the analysis of samples obtained from the Organisation for the Prohibition of Chemical Weapons (OPCW). The method established in this study for the detection of ClCN showed high sensitivity and precision, and could aid in the analysis and detection of ClCN in the environment.

Type Ⅱ ribosome-inactivating proteins (RIPs) are an important class of protein toxins that consist of A and B chains linked by an interchain disulfide bond. The B-chain with lectin-like activity is responsible for binding to the galactose-containing receptors on eukaryotic cell surfaces, which is essential for A-chain internalization by endocytosis. The A-chain has N-glycosidase activity that irreversibly depurinates a specific adenine from 28S ribosomal RNA (28S rRNA) and terminates protein synthesis. The synergistic effect of the A-B chain inactivates the ribosome, inhibits protein synthesis, and exhibits high cytotoxicity. Ricin and abrin that are expressed by the plants Ricinus communis and Abrus precatorius, respectively, are typical type Ⅱ RIPs. The toxicity of ricin and abrin are 385 times and 2885 times, respectively, more that of the nerve agent VX. Owing to their ease of preparation, wide availability, and potential use as a bioterrorism agent, type Ⅱ RIPs have garnered increasing attention in recent years. Ricin is listed as a prohibited substance under schedule 1A of the Chemical Weapons Convention (CWC). The occurrence of ricin-related bioterrorism incidents in recent years has promoted the development of accurate, sensitive, and rapid detection and identification technology for type Ⅱ RIPs. Significant progress has been made in the study of toxicity mechanisms and detection methods of type Ⅱ RIPs, which primarily involve qualitative and quantitative analysis methods including immunological assays, mass spectrometry analysis methods, and toxin activity detection methods based on depurination and cytotoxicity. Immunoassays generally involve the specific recognition of antigens and antibodies, which is based on oligonucleotide molecular recognition elements called aptamers. These methods are fast and highly sensitive, but for highly homologous proteins in complex samples, they provide false positive results. With the rapid development of biological mass spectrometry detection technology, techniques such as electrospray ionization (ESI) and matrix-assisted laser desorption ionization (MALDI) are widely used in the identification of proteins. These methods not only provide accurate information on molecular weight and structure of proteins, but also demonstrate accurate quantification. Enzyme digestion combined with mass spectrometry is the predominantly used detection method. Accurate identification of protein toxins can be achieved by fingerprint analysis of enzymatically digested peptides. For analysis of protein toxins in complex samples, abundant peptide markers are obtained using a multi-enzyme digestion strategy. Targeted mass spectrometry analysis of peptide markers is used to obtain accurate qualitative and quantitative information, which effectively improves the accuracy and sensitivity of the identification of type Ⅱ RIP toxins. Although immunoassay and mass spectrometry detection methods can provide accurate identification of type Ⅱ RIPs, they cannot determine whether the toxins will retain potency. The widely used detection methods for activity analysis of type Ⅱ RIPs include depurination assay based on N-glycosidase activity and cytotoxicity assay. Both the methods provide simple, rapid, and sensitive analysis of type Ⅱ RIP toxicity, and complement other detection methods. Owing to the importance of type Ⅱ RIP toxins, the Organization for the Prohibition of Chemical Weapons (OPCW) has proposed clear technical requirements for the identification and analysis of relevant samples. We herein reviewed the structural characteristics, mechanism of action, and the development and application of type Ⅱ RIP detection methods; nearly 70 studies on type Ⅱ RIP toxins and their detection methods have been cited. In addition to the technical requirements of OPCW for the unambiguous identification of biotoxins, the trend of future development of type Ⅱ RIP-based detection technology has been explored.

Sulfur mustard (SM) is a blister chemical warfare agent with severe cytotoxicity and genotoxicity. It can extensively alkylate important macromolecules in organisms, such as proteins, DNA, and lipids, and produce a series of metabolites, among which the characteristic ones can be used as biomarkers. The exact toxicological mechanisms of SM remain unclear but mainly involve the DNA lesions induced by alkylation and oxidative stress caused by glutathione depletion. Various methods have been used to analyze DNA damage caused by SM. Among these methods, liquid chromatography-tandem mass spectrometry (LC-MS/MS) technology stands out and makes it possible to observe damage in view of biomarkers induced by SM. Sample preparation is critical for detection by LC-MS/MS and mainly includes DNA isolation, adduct hydrolysis, and adduct purification. Moreover, optimization of chromatographic conditions, selection of MS transitions, and quantitative strategies are also essential. SM-DNA adducts are generally considered to be N7-HETEG, O6-HETEG, N7-BisG, and N3-HETEA. This article proposes some other possibilities of SM-DNA adducts for the identification of SM genotoxicity.