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The limitations and capabilities of wipe samples analysis in control of contamination of facilities with highly toxic organic compounds

https://doi.org/10.47183/mes.2021.018

Abstract

Wipe sampling is widely used for microbiological control purposes. Sanitary and chemical studies also include analysis of samples wiped from the work surfaces during routine and periodic working conditions safety inspections at chemical facilities. The analysis also allows assessing the toxicity and hazard of items/structures that could be in contact with highly toxic substances. This study aimed to investigate the capabilities and limitations of the surface wipe sample analysis method in control of residual contamination of equipment and building structures of a former chemical weapons destruction facilities (CWDF) with sulfur mustard and O-isobutyl-S-(2-diethylaminoethyl) methylphosphonothioate (VR), as well as their degradation products. Gas chromatography with tandem mass spectrometry (GC-MS/MS) enabled identification of the sulfur mustard markers, high-performance liquid chromatography with tandem mass spectrometry (HPLC-MS/MS) allowed identifying VR markers. An assessment of the matrix influence on the results of GC-MS/MS and HPLC-MS/MS analysis was carried out. The matrix effect was established to affect the results the most in case of HPLC-MS/MS analysis: for GC-MS/MS analysis of target substances, the matrix factor averaged at 60–80%, for HPLC-MS/MS it was less than 40%. The average percent sulfur mustard recoveries from three types of surfaces (PVC tiles, laminate and metal plates) was 9 ± 2%, 0.13 ± 0.02% and 0.10 ± 0.03%; in case of VR, the recoveries was 2.7 ± 0.5%, 11.8 ± 0.3% and 0.8 ± 0.1%, respectively. The limits of detection for sulfur mustard by GC-MS/MS and VR by HPLC-MS/MS were established at 0.001 MPL and 0.02 MPL, respectively. The developed approaches were applied to the analysis of wipe samples from the surfaces of the equipment and engineering structures of the former CWDF.

About the Authors

M. D. Shachneva
Research Institute of Hygiene, Occupational Pathology and Human Ecology
Russian Federation

Mariya D. Shachneva

Kapitolovo, r.p. Kuzmolovsky, Vsevolozhsky r., 188663 Leningradskaya obl.



M. A. Leninskii
Research Institute of Hygiene, Occupational Pathology and Human Ecology
Russian Federation

Leningradskaya obl.



E. I. Savelieva
Research Institute of Hygiene, Occupational Pathology and Human Ecology
Russian Federation

Leningradskaya obl.



References

1. Saveleva E.I., Radilov A.S., Kuznecova T.A., Apraksin V.F. Issledovanie sostava gazovydelenij bitumno-solevyh mass, vkljuchajushhih produkty unichtozhenija iprita. Zhurnal prikladnoj himii. 1999; 72 (9): 1501–5. Russian.

2. Munro N.B., Talmage S.S., Griffin G.D., Waters L.C., Watson A.P., King J.F., et al. The sources, fate, and toxicity of chemical warfare agent degradation products. Environmental Health Perspectives. 1999. 107 (12): 933–74.

3. Crenshaw M.D., Hayes T.L., Miller T.L., Shahnuon C.M. Comparison of the hydrolytic stability of S-(N,N-diethylaminoethyl) isobutyl methylphosphonothiolate with VX in dilute solution. J Appl Toxicol. 2001; 21 (S3–S6): 53–56.

4. Willison S. Wipe selection for the analysis of surface materials containing chemical warfare agent nitrogen mustard degradation products by ultra-high pressure liquid chromatography–tandem mass spectrometry. Journal of Chromatography A. 2012; 1270: 72–79.

5. Postanovlenie Glavnogo gosudarstvennogo sanitarnogo vracha Rossijskoj Federacii ot 28.01.2021 # 2 «Ob utverzhdenii sanitarnyh pravil i norm SanPiN 1.2.3685-21 «Gigienicheskie normativy i trebovanija k obespecheniju bezopasnosti i (ili) bezvrednosti dlja cheloveka faktorov sredy obitanija» (Zaregistrirovano 29.01.2021 # 62296). Available from: https://docs.cntd.ru/document/573500115 (data obrashhenija: 25.05.2021). Russian.

6. Saveleva E.I., Leninskii M.A., Vasileva I.A., Karakashev G.V., Samchenko N.A. Opredelenie sledovyh kolichestv O-izobutil-S- [(2-dijetilamino)jetil] metilfosfonotioata i toksichnogo produkta ego gidroliza metodom vysokojeffektivnoj zhidkostnoj hromatografii s tandemnym mass-spektrometricheskim detektirovaniem. Analitika i kontrol'. 2021; 25 (3): 43. Russian.

7. Annesley T.M. Ion Suppression in Mass Spectrometry. Clin. Chem. 2003; 49: 1041–4.

8. Jessome L.L., Volmer D.A. Ion Suppression: A Major Concern in Mass Spectrometry. LCGC North America. 2006; 24: 498–511.

9. Antignac J., Wasch K., Monteau F., Brabander H., Andre F., Le Bizec B. The ion suppression phenomenon in liquid chromatography– mass spectrometry and its consequences in the field of residue analysis. Anal Chim Acta. 2005; 529: 129.

10. Hernon-Kenny L.A., Behringer D.L., Crenshaw M.D. Comparison of latex body paint with wetted gauze wipes for sampling the chemical warfare agents VX and sulfur mustard from common indoor surfaces. Forensic Science International. 2016; 262: 143–9.

11. Wilson S.A. Investigation of the Persistence of Nerve Agent Degradation Analytes on Surfaces through Wipe Sampling and Detection with Ultrahigh Performance Liquid Chromatography-Tandem Mass Spectrometry. Anal Chem. 2015; 87: 1034–41.


Review

For citations:


Shachneva M.D., Leninskii M.A., Savelieva E.I. The limitations and capabilities of wipe samples analysis in control of contamination of facilities with highly toxic organic compounds. Extreme Medicine. 2021;23(2):41-47. https://doi.org/10.47183/mes.2021.018

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ISSN 2713-2757 (Print)
ISSN 2713-2765 (Online)