Dergiler / Atmospheric Pollution Research / 2017 / Cilt: 8 - Sayı: 4

Determination of hydrogen cyanide in residential ambient air using SPME coupled with GCeMS

Sayfa
678–685
DOI
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⚡ TL;DR(1 Cümlede Hızlı Çıkarım)

Environmental Protection Agency (0.72 ppbv) and it used simpler and less time consuming method compared to the conventional sample preparation method, enabling rapid community exposure assessment.

📌 3 Maddede Bu Makale

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Amaç & Hipotez:Hydrogen cyanide (HCN) is commonly released into the atmosphere from vehicle emissions, biomass burning and industrial processes such as gold mining, pesticide production, and chemical manufacturing.
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Temel Bulgular & Veri:Air samples were collected at a distance of 0.1,1.0 and 2.0 km away from the gold mine.
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Sonuç & Katkı:Environmental Protection Agency (0.72 ppbv) and it used simpler and less time consuming method compared to the conventional sample preparation method, enabling rapid community exposure assessment.
🔬Tür:Araştırma Makalesi
📍Kapsam:Genişletilmiş Akademik Örneklem
⚙️Değişkenler:Alan Parametreleri

Özet

Hydrogen cyanide (HCN) is commonly released into the atmosphere from vehicle emissions, biomass burning and industrial processes such as gold mining, pesticide production, and chemical manufacturing. The aim of this study was to quantify the ambient HCN concentration in a residential area close to a gold mine using solid-phase micro extraction (SPME) coupled with gas chromatographyemass spectrometry (GCeMS) and calculate it's potential health risks. Air samples were collected at a distance of 0.1,1.0 and 2.0 km away from the gold mine. All cyanide compounds were extracted using 75 mm carbowax/ polydimethylsiloxane-coated SPME fibre and analysed using GCeMS. Calibration curve was constructed using standard concentrations ranged between 5 and 500 mgL 1. This method showed good linearity (r2 ¼ 0.999) and accuracy (recoveries ¼ 84e119%), reproducibility (relative standard deviation < 11.5%) and the LOD was 0.16 ppbv. HCN was detected in 68% of samples ranging between 0.16 and 8.56 ppbv. HCN concentration was significantly higher (p < 0.05) for samples taken at 0.1 km away from the gold mine compared to concentrations at 1.0 and 2.0 km. The non-carcinogenic risk of HCN from air inhalation was negligible as the calculated hazard quotient was less than 1. The method used in this study was sensitive enough to detect ambient HCN concentrations at levels which were below the reference concentration for long term inhalation exposure by the U.S. Environmental Protection Agency (0.72 ppbv) and it used simpler and less time consuming method compared to the conventional sample preparation method, enabling rapid community exposure assessment.

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Bu Makaleye Atıf Yap

MAZRAH, S., ZAİN, S. M., SHAHARUDİN, R., KAMALUDDİN, M. A., DAUD, S. F. (2017). Determination of hydrogen cyanide in residential ambient air using SPME coupled with GCeMS. Atmospheric Pollution Research, Cilt: 8 - Sayı: 4, 678–685. https://ajindex.com/articles/351384

Kaynakça (5)

  1. ACGIH (American Conference of Governmental Industrial Hygienists), 1996. Documentation of the Threshold Limit Values and Biological Exposure Indices: Hydrogen Cyanide, seventh ed. ACGIH, Cincinnati, OH. Ambrose, J.L., Zhou, Y., Haase, K., Mayne, H.R., Talbot, R., Sive, B.C., 2012. A gas chromatographic instrument for measurement of hydrogen cyanide in the lower atmosphere. Atmos. Meas. Tech. 5,1229e1240. http://dx.doi.org/10.5194/ amt-5-1229-2012.
  2. Apel, E.C., Hornbrook, R.S., Hills, A.J., Blake, N.J., Barth, M.C., Weinheimer, A., Cantrell, C., Rutledge, S.A., Basarab, B., Crawford, J., et al., 2015. Upper tropospheric ozone production from lightning NOx-impacted convection: smoke ingestion case study from the DC3 campaign. J. Geophys. Res. Atmos. 120, 2505e2523. http://dx.doi.org/10.1002/2014JD022121. ATSDR (Agency for Toxic Substances and Disease Registry), 2006. Toxicological Profile for Cyanide. Public Health Service, U.S. Department of Health and Human Services, Atlanta, GA. http://www.atsdr.cdc.gov/toxprofiles/tp8.pdf.
  3. Belardi, R.P., Pawliszyn, J.B., 1989. The application of chemically modified fused silica fibers in the extraction of organics from water matrix samples and their rapid transfer to capillary columns. Water Pollut. Res. J. Can. 24 (1), 179e191. Boadas-Vaello, P., Jover, E., Llorens, J., Bayona, J.M., 2008. Determination of cyanide and volatile alkylnitriles in whole blood by headspace solid-phase microextraction and gas chromatography with nitrogen phosphorus detection. J. Chromatogr. B e Anal. Technol. Biomed. Life Sci. 870,17e21. http://dx.doi.org/ 10.1016/j.jchromb.2008.05.031. Calafat, A.M., Stanfill, S.B., 2002. Rapid quantitation of cyanide in whole blood by automated headspace gas chromatography. J. Chromatogr. B e Anal. Technol. Biomed. Life Sci. 772, 131e137. http://dx.doi.org/10.1016/S1570-0232(02) 00067-3.
  4. Crounse, J.D., DeCarlo, P.F., Blake, D.R., Emmons, L.K., Campos, T.L., Apel, E.C., Clarke, A.D., Weinheimer, A.J., McCabe, D.C., Yokelson, R.J., Jimenez, J.L., Wenberg, P.O., 2009. Biomass burning and urban air pollution over the Central Mexican Plateu. Atmos. Chem. Phys. 9, 4929e4944. Cyanides, aerosol and gas. Method 7904, Issue 2, NIOSH Manual of Analytical Methods (NMAM), Fourth Edition, 15 August 1994.
  5. Desharnais, B., Huppe, G., Lamarche, M., Mireault, P., Skinner, C.D., 2012. Cyanide quantification in post-mortem biological matrices by headspace GCeMS. Forensic Sci. Int. 222, 346e351. http://dx.doi.org/10.1016/j.forsciint.20