The study of genotoxicity and immunotoxicity in workers occupationally exposed to cyanide
Object Workers are exposed to a wide range of organic and inorganic pollutants during their work, which may cause them serious health damage related to occupational exposure, depending on the type of exposure, its duration, and the type of safety measures applied in the workplace. The current study...
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Published in | Toxicology and environmental health sciences Vol. 16; no. 1; pp. 99 - 105 |
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Main Authors | , |
Format | Journal Article |
Language | English |
Published |
Singapore
Springer Nature Singapore
01.03.2024
Springer Nature B.V |
Subjects | |
Online Access | Get full text |
ISSN | 2005-9752 2233-7784 |
DOI | 10.1007/s13530-023-00202-8 |
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Abstract | Object
Workers are exposed to a wide range of organic and inorganic pollutants during their work, which may cause them serious health damage related to occupational exposure, depending on the type of exposure, its duration, and the type of safety measures applied in the workplace. The current study aimed to determine occupational exposure to inorganic cyanide compounds in automotive painting workshops, determine immunotoxicity and genotoxicity, and compare the results with those of a non-exposed group.
Method
Seventeen male works in automotive painting distributed in ten workshops within Baghdad, Iraq, were included. They were divided into two age groups (22–33) and (34–44) years, with a main age of 33.116.4.
Result
The result of immunological and cytogenetic studies and the concentration of cyanide in plasma compared with a non-exposed group of the same age T-lymphocyte subgroup rates (CD4+, CD3+, CD16+, CD8+, CD56+, and natural killer (NK) cells), as well as genotoxicity, were measured via the micronucleus (MN) assay and Total Chromosomal Aberrations (TCAs). The difference between the two groups (5.7 MN/250 cells) and the control group (1.35 MN/250 cells) was statistically significant (
P
0.05), and this increase corresponds to the incidence of Total Chromosomal Aberrations (TCAs), which was 0.39 in the exposed group and 0.11 in the control group. Plasma-thiocyanate (P-SCN), a marker of cyanide exposure, was detected in the plasma and found to be substantially higher (0.54 M) when compared to non-exposed subjects (P 0.05).
Conclusions
The immunological and cytogenetic indicators showed a clear perception of the extent of damage that may be caused to the genetic material upon permanent exposure to mono-cyanides. However, we need more studies and assessments to find out whether the effect of cyanide is cumulative or immediate and has only an acute toxic effect, or if it is chronic at low concentrations and sub-lethal dose. |
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AbstractList | ObjectWorkers are exposed to a wide range of organic and inorganic pollutants during their work, which may cause them serious health damage related to occupational exposure, depending on the type of exposure, its duration, and the type of safety measures applied in the workplace. The current study aimed to determine occupational exposure to inorganic cyanide compounds in automotive painting workshops, determine immunotoxicity and genotoxicity, and compare the results with those of a non-exposed group.MethodSeventeen male works in automotive painting distributed in ten workshops within Baghdad, Iraq, were included. They were divided into two age groups (22–33) and (34–44) years, with a main age of 33.116.4.ResultThe result of immunological and cytogenetic studies and the concentration of cyanide in plasma compared with a non-exposed group of the same age T-lymphocyte subgroup rates (CD4+, CD3+, CD16+, CD8+, CD56+, and natural killer (NK) cells), as well as genotoxicity, were measured via the micronucleus (MN) assay and Total Chromosomal Aberrations (TCAs). The difference between the two groups (5.7 MN/250 cells) and the control group (1.35 MN/250 cells) was statistically significant (P 0.05), and this increase corresponds to the incidence of Total Chromosomal Aberrations (TCAs), which was 0.39 in the exposed group and 0.11 in the control group. Plasma-thiocyanate (P-SCN), a marker of cyanide exposure, was detected in the plasma and found to be substantially higher (0.54 M) when compared to non-exposed subjects (P 0.05).ConclusionsThe immunological and cytogenetic indicators showed a clear perception of the extent of damage that may be caused to the genetic material upon permanent exposure to mono-cyanides. However, we need more studies and assessments to find out whether the effect of cyanide is cumulative or immediate and has only an acute toxic effect, or if it is chronic at low concentrations and sub-lethal dose. Object Workers are exposed to a wide range of organic and inorganic pollutants during their work, which may cause them serious health damage related to occupational exposure, depending on the type of exposure, its duration, and the type of safety measures applied in the workplace. The current study aimed to determine occupational exposure to inorganic cyanide compounds in automotive painting workshops, determine immunotoxicity and genotoxicity, and compare the results with those of a non-exposed group. Method Seventeen male works in automotive painting distributed in ten workshops within Baghdad, Iraq, were included. They were divided into two age groups (22–33) and (34–44) years, with a main age of 33.116.4. Result The result of immunological and cytogenetic studies and the concentration of cyanide in plasma compared with a non-exposed group of the same age T-lymphocyte subgroup rates (CD4+, CD3+, CD16+, CD8+, CD56+, and natural killer (NK) cells), as well as genotoxicity, were measured via the micronucleus (MN) assay and Total Chromosomal Aberrations (TCAs). The difference between the two groups (5.7 MN/250 cells) and the control group (1.35 MN/250 cells) was statistically significant ( P 0.05), and this increase corresponds to the incidence of Total Chromosomal Aberrations (TCAs), which was 0.39 in the exposed group and 0.11 in the control group. Plasma-thiocyanate (P-SCN), a marker of cyanide exposure, was detected in the plasma and found to be substantially higher (0.54 M) when compared to non-exposed subjects (P 0.05). Conclusions The immunological and cytogenetic indicators showed a clear perception of the extent of damage that may be caused to the genetic material upon permanent exposure to mono-cyanides. However, we need more studies and assessments to find out whether the effect of cyanide is cumulative or immediate and has only an acute toxic effect, or if it is chronic at low concentrations and sub-lethal dose. |
Author | Haleem, Azhar M. Hussein, Nehia N. |
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Cites_doi | 10.1093/jat/29.2.105 10.1039/b004562o 10.26505/DJM.17024890827 10.1016/j.chemosphere.2016.11.009 10.1039/b110593k 10.1080/15287397909529770 10.1520/JFS13913J 10.1093/annhyg/mei075 10.1016/j.imlet.2014.11.003 10.1093/jat/bks017 10.1093/jat/bku020 10.1016/S0378-4274(02)00016-4 10.1093/clinchem/31.4.591 10.1016/j.aca.2010.01.028 10.1186/s40038-016-0012-3 10.1016/j.mrgentox.2011.01.001 |
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References | IARC (2012) Metals, arsenic, dusts and fibers. IARC Monogr Eval Carcinog Risks Hum, 100C: 1–499. PMID: 18335640Niknahad H, Ghelichkhani E. 2002. Antagonism of cyanide poisoning by dihydroxyacetone. Toxicol Lett 132:95–100 LundquistPRoslingHSörboBDetermination of cyanide in whole blood, erythrocytes and plasmaClin Chem1985315915951:CAS:528:DyaL2MXitFKgtbc%3D10.1093/clinchem/31.4.5913978792 OSHA (2004b) Appendix A. Occupational safety and health standards. List of highly hazardous Chemicals, toxics, and reactive. Washington, DC: Occupational Safety and Health Administration. Code of Federal regulations. 29 CFR 1910.119, App A. http://www.osha.gov/pls/oshaweb/owadisp.show_document?p_table=STANDARDS&p_id=9761. NolteKBDasguptaAPrevention of occupational cyanide exposure in autopsy prosectorsJ Forensic Sci19964111461471:STN:280:DyaK2s%2FovVyjtQ%3D%3D10.1520/JFS13913J8934715 MateusFHLeperaJSTanchoteVLDetermination of acetonitrile and cyanide in rat blood: application to an experimental studyJ Analy Toxico2005291051091:CAS:528:DC%2BD2MXhslemsLk%3D10.1093/jat/29.2.105 McKennaSTHullTRThe fire toxicity of polyurethane foamsFire Sci Rev2016511271:CAS:528:DC%2BC28XmsFaktb0%3D10.1186/s40038-016-0012-3 AnjoekaPErikTGunnarSIvanaBJoopVDickHLiesbethPInhalation exposure to isocyanates of car body repair shop workers and industrial spray paintersAnn Occup Hyg2006501114 GarridoMAIsocyanate emissions from pyrolysis of mattresses containing polyurethane foamChemosphere20171686676752017Chmsp.168..667G1:CAS:528:DC%2BC28XhvVahtbrF10.1016/j.chemosphere.2016.11.00927836276 PhilbrickDJHopkinsJBHillDCAlexanderJCThomsonRGEffects of prolonged cyanide and thiocyanate feeding in ratsToxico Envi Health197955795921:CAS:528:DyaE1MXltlGjtLk%3D10.1080/15287397909529770 HaleemAMAl-SabaghAACytotoxic and immunotoxic associated with occupational chemical exposure, Baghdad, IraqDiyala J Med201917216617310.26505/DJM.17024890827 RothMGViégasJRothDMOccupational genotoxicity risk evaluation through the comet assay and the micronucleus testGen Mol Res200324410417 IARCSome non-heterocyclic polycyclic aromatic hydrocarbons and some related exposuresIARC Monogr Eval Carcinog Risks Hum2010921853 BhandariRKOdaRPPetrikovicsIThompsonDECyanide toxicokinetics: the behavior of cyanide, thiocyanate and 2-Amino-2-Thiazoline-4- Automotiveboxylic acid in multiple animal modelsJ Anal Toxicol2014382182251:CAS:528:DC%2BC2cXls1GnsLs%3D10.1093/jat/bku020247112953977587 DasDSarkarBMukhopadhyaySBanerjeeCBiswasSAn altered ratio of CD4+ And CD8+ T lymphocytes in cervical cancer tissues and peripheral blood – A prognostic clue?Asian Pac J Cancer Prev20181924714781:CAS:528:DC%2BC1MXisFKltrw%3D294806665980936 VermaRBabuAHuman chromosomes: manual of Basic techniques1989New YorkPregramon press NIOSH (2004) Cyanide compounds. NIOSH pocket guide to chemical hazards. Washington, DC: National Institute for Occupational Safety and Health. http://www.cdc.gov/niosh/npg/npg.html. Jun 06 KarlssonDDahlinJSkarpingGDetermination of isocyanates, aminoisocyanates and amines in air formed during the thermal degradation of polyurethaneJ Environ Monit200242162221:CAS:528:DC%2BD38Xit12ht70%3D10.1039/b110593k11993759 YousoSLRockwoodGALogueBAThe analysis of protein-bound thiocyanate in plasma of smokers and non-smokers as a marker of cyanide exposureJ Analy Toxico2012362652691:CAS:528:DC%2BC38XmtVehurs%3D10.1093/jat/bks017 BoutinMDufresneAOstiguyCLesageJDetermination of airborne isocyanates generated during the thermal degradation of car paint in body repair shopsAnn Occup Hyg20065043853931:CAS:528:DC%2BD28XotVWntLg%3D10.1093/annhyg/mei07516434466Epub 2006 Jan 24 YousoSLRockwoodGALeeJPLogueBADetermination of cyanide exposure by gas-chromatography mass-spectrometry analysis of cyanide-exposed plasma proteinsAnal Chim Acta201067724281:CAS:528:DC%2BC3cXhtFyltbnF10.1016/j.aca.2010.01.02820850585 RudolfOKauêTGAlvesBMLenhaniMBVanessaMPâmelaCGCarlinaACDetermination of lymphocyte subset reference ranges in peripheral blood of healthy adults by a dual-platform flow cytometry methodImmunol Lett20151639610110.1016/j.imlet.2014.11.003 OSHA (2004a) Air contaminants. Occupational safety and health standards for shipyard employment. Washington, DC: Occupational Safety and Health Administration. Code of Federal regulations. 29 CFR 1915.1000. http://www.osha.gov/pls/oshaweb/owadisp.show_document?p_table=standards&p_id=10286 NIOSH (2005) Cyanide compounds. NIOSH pocket guide to chemical hazards. Washington, DC: National Institute for Occupational Safety and Health. http://www.cdc.gov/niosh/npg/npg.html. September 07 KarlssonDSpanneMDaleneMAirborne thermal degradation products of polyurethene coatings in car repair shopsJ Environ Monit200024624691:CAS:528:DC%2BD3cXmvFeqtr4%3D10.1039/b004562o11254051 LestónGJTorresRJVilares PintoMRCunhaLPristaJBiomonitoring of a population of Portuguese workers exposed to leadMutat Res2011721818810.1016/j.mrgentox.2011.01.001 P Lundquist (202_CR18) 1985; 31 KB Nolte (202_CR9) 1996; 41 SL Youso (202_CR25) 2010; 677 SL Youso (202_CR15) 2012; 36 202_CR24 RK Bhandari (202_CR5) 2014; 38 ST McKenna (202_CR6) 2016; 5 202_CR7 MA Garrido (202_CR4) 2017; 168 202_CR8 M Boutin (202_CR10) 2006; 50 IARC (202_CR2) 2010; 92 R Verma (202_CR13) 1989 P Anjoeka (202_CR3) 2006; 50 202_CR1 D Das (202_CR23) 2018; 19 D Karlsson (202_CR12) 2002; 4 202_CR14 AM Haleem (202_CR20) 2019; 17 GJ Lestón (202_CR19) 2011; 721 MG Roth (202_CR21) 2003; 2 D Karlsson (202_CR11) 2000; 2 O Rudolf (202_CR22) 2015; 163 FH Mateus (202_CR17) 2005; 29 DJ Philbrick (202_CR16) 1979; 5 |
References_xml | – reference: YousoSLRockwoodGALeeJPLogueBADetermination of cyanide exposure by gas-chromatography mass-spectrometry analysis of cyanide-exposed plasma proteinsAnal Chim Acta201067724281:CAS:528:DC%2BC3cXhtFyltbnF10.1016/j.aca.2010.01.02820850585 – reference: YousoSLRockwoodGALogueBAThe analysis of protein-bound thiocyanate in plasma of smokers and non-smokers as a marker of cyanide exposureJ Analy Toxico2012362652691:CAS:528:DC%2BC38XmtVehurs%3D10.1093/jat/bks017 – reference: NolteKBDasguptaAPrevention of occupational cyanide exposure in autopsy prosectorsJ Forensic Sci19964111461471:STN:280:DyaK2s%2FovVyjtQ%3D%3D10.1520/JFS13913J8934715 – reference: NIOSH (2005) Cyanide compounds. NIOSH pocket guide to chemical hazards. Washington, DC: National Institute for Occupational Safety and Health. http://www.cdc.gov/niosh/npg/npg.html. September 07 – reference: HaleemAMAl-SabaghAACytotoxic and immunotoxic associated with occupational chemical exposure, Baghdad, IraqDiyala J Med201917216617310.26505/DJM.17024890827 – reference: BhandariRKOdaRPPetrikovicsIThompsonDECyanide toxicokinetics: the behavior of cyanide, thiocyanate and 2-Amino-2-Thiazoline-4- Automotiveboxylic acid in multiple animal modelsJ Anal Toxicol2014382182251:CAS:528:DC%2BC2cXls1GnsLs%3D10.1093/jat/bku020247112953977587 – reference: AnjoekaPErikTGunnarSIvanaBJoopVDickHLiesbethPInhalation exposure to isocyanates of car body repair shop workers and industrial spray paintersAnn Occup Hyg2006501114 – reference: RothMGViégasJRothDMOccupational genotoxicity risk evaluation through the comet assay and the micronucleus testGen Mol Res200324410417 – reference: LundquistPRoslingHSörboBDetermination of cyanide in whole blood, erythrocytes and plasmaClin Chem1985315915951:CAS:528:DyaL2MXitFKgtbc%3D10.1093/clinchem/31.4.5913978792 – reference: OSHA (2004a) Air contaminants. Occupational safety and health standards for shipyard employment. Washington, DC: Occupational Safety and Health Administration. Code of Federal regulations. 29 CFR 1915.1000. http://www.osha.gov/pls/oshaweb/owadisp.show_document?p_table=standards&p_id=10286 – reference: IARC (2012) Metals, arsenic, dusts and fibers. IARC Monogr Eval Carcinog Risks Hum, 100C: 1–499. PMID: 18335640Niknahad H, Ghelichkhani E. 2002. Antagonism of cyanide poisoning by dihydroxyacetone. Toxicol Lett 132:95–100 – reference: McKennaSTHullTRThe fire toxicity of polyurethane foamsFire Sci Rev2016511271:CAS:528:DC%2BC28XmsFaktb0%3D10.1186/s40038-016-0012-3 – reference: VermaRBabuAHuman chromosomes: manual of Basic techniques1989New YorkPregramon press – reference: BoutinMDufresneAOstiguyCLesageJDetermination of airborne isocyanates generated during the thermal degradation of car paint in body repair shopsAnn Occup Hyg20065043853931:CAS:528:DC%2BD28XotVWntLg%3D10.1093/annhyg/mei07516434466Epub 2006 Jan 24 – reference: LestónGJTorresRJVilares PintoMRCunhaLPristaJBiomonitoring of a population of Portuguese workers exposed to leadMutat Res2011721818810.1016/j.mrgentox.2011.01.001 – reference: OSHA (2004b) Appendix A. Occupational safety and health standards. List of highly hazardous Chemicals, toxics, and reactive. Washington, DC: Occupational Safety and Health Administration. Code of Federal regulations. 29 CFR 1910.119, App A. http://www.osha.gov/pls/oshaweb/owadisp.show_document?p_table=STANDARDS&p_id=9761. – reference: GarridoMAIsocyanate emissions from pyrolysis of mattresses containing polyurethane foamChemosphere20171686676752017Chmsp.168..667G1:CAS:528:DC%2BC28XhvVahtbrF10.1016/j.chemosphere.2016.11.00927836276 – reference: KarlssonDDahlinJSkarpingGDetermination of isocyanates, aminoisocyanates and amines in air formed during the thermal degradation of polyurethaneJ Environ Monit200242162221:CAS:528:DC%2BD38Xit12ht70%3D10.1039/b110593k11993759 – reference: RudolfOKauêTGAlvesBMLenhaniMBVanessaMPâmelaCGCarlinaACDetermination of lymphocyte subset reference ranges in peripheral blood of healthy adults by a dual-platform flow cytometry methodImmunol Lett20151639610110.1016/j.imlet.2014.11.003 – reference: NIOSH (2004) Cyanide compounds. NIOSH pocket guide to chemical hazards. Washington, DC: National Institute for Occupational Safety and Health. http://www.cdc.gov/niosh/npg/npg.html. Jun 06 – reference: DasDSarkarBMukhopadhyaySBanerjeeCBiswasSAn altered ratio of CD4+ And CD8+ T lymphocytes in cervical cancer tissues and peripheral blood – A prognostic clue?Asian Pac J Cancer Prev20181924714781:CAS:528:DC%2BC1MXisFKltrw%3D294806665980936 – reference: MateusFHLeperaJSTanchoteVLDetermination of acetonitrile and cyanide in rat blood: application to an experimental studyJ Analy Toxico2005291051091:CAS:528:DC%2BD2MXhslemsLk%3D10.1093/jat/29.2.105 – reference: PhilbrickDJHopkinsJBHillDCAlexanderJCThomsonRGEffects of prolonged cyanide and thiocyanate feeding in ratsToxico Envi Health197955795921:CAS:528:DyaE1MXltlGjtLk%3D10.1080/15287397909529770 – reference: IARCSome non-heterocyclic polycyclic aromatic hydrocarbons and some related exposuresIARC Monogr Eval Carcinog Risks Hum2010921853 – reference: KarlssonDSpanneMDaleneMAirborne thermal degradation products of polyurethene coatings in car repair shopsJ Environ Monit200024624691:CAS:528:DC%2BD3cXmvFeqtr4%3D10.1039/b004562o11254051 – volume: 29 start-page: 105 year: 2005 ident: 202_CR17 publication-title: J Analy Toxico doi: 10.1093/jat/29.2.105 – volume: 2 start-page: 462 year: 2000 ident: 202_CR11 publication-title: J Environ Monit doi: 10.1039/b004562o – volume: 17 start-page: 166 issue: 2 year: 2019 ident: 202_CR20 publication-title: Diyala J Med doi: 10.26505/DJM.17024890827 – volume: 168 start-page: 667 year: 2017 ident: 202_CR4 publication-title: Chemosphere doi: 10.1016/j.chemosphere.2016.11.009 – volume: 4 start-page: 216 year: 2002 ident: 202_CR12 publication-title: J Environ Monit doi: 10.1039/b110593k – volume: 5 start-page: 579 year: 1979 ident: 202_CR16 publication-title: Toxico Envi Health doi: 10.1080/15287397909529770 – volume: 41 start-page: 146 issue: 1 year: 1996 ident: 202_CR9 publication-title: J Forensic Sci doi: 10.1520/JFS13913J – volume: 50 start-page: 385 issue: 4 year: 2006 ident: 202_CR10 publication-title: Ann Occup Hyg doi: 10.1093/annhyg/mei075 – volume-title: Human chromosomes: manual of Basic techniques year: 1989 ident: 202_CR13 – volume: 163 start-page: 96 year: 2015 ident: 202_CR22 publication-title: Immunol Lett doi: 10.1016/j.imlet.2014.11.003 – volume: 36 start-page: 265 year: 2012 ident: 202_CR15 publication-title: J Analy Toxico doi: 10.1093/jat/bks017 – ident: 202_CR7 – volume: 50 start-page: 1 issue: 1 year: 2006 ident: 202_CR3 publication-title: Ann Occup Hyg – volume: 38 start-page: 218 year: 2014 ident: 202_CR5 publication-title: J Anal Toxicol doi: 10.1093/jat/bku020 – volume: 2 start-page: 410 issue: 4 year: 2003 ident: 202_CR21 publication-title: Gen Mol Res – ident: 202_CR1 doi: 10.1016/S0378-4274(02)00016-4 – volume: 31 start-page: 591 year: 1985 ident: 202_CR18 publication-title: Clin Chem doi: 10.1093/clinchem/31.4.591 – volume: 677 start-page: 24 year: 2010 ident: 202_CR25 publication-title: Anal Chim Acta doi: 10.1016/j.aca.2010.01.028 – volume: 5 start-page: 1 issue: 1 year: 2016 ident: 202_CR6 publication-title: Fire Sci Rev doi: 10.1186/s40038-016-0012-3 – volume: 92 start-page: 1 year: 2010 ident: 202_CR2 publication-title: IARC Monogr Eval Carcinog Risks Hum – volume: 19 start-page: 471 issue: 2 year: 2018 ident: 202_CR23 publication-title: Asian Pac J Cancer Prev – ident: 202_CR14 – ident: 202_CR8 – volume: 721 start-page: 81 year: 2011 ident: 202_CR19 publication-title: Mutat Res doi: 10.1016/j.mrgentox.2011.01.001 – ident: 202_CR24 |
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SubjectTerms | Aberration Age Biomedical and Life Sciences Biomedicine CD16 antigen CD3 antigen CD4 antigen CD56 antigen CD8 antigen Chromosome aberrations Cyanides Cytogenetics Damage Environmental Health Exposure Genotoxicity Immunology Immunotoxicity Lethal dose Low concentrations Lymphocytes Lymphocytes T Natural killer cells Occupational exposure Occupational health Original Article Pharmacology/Toxicology Safety measures Statistical analysis Subgroups Sublethal dosage Thiocyanates Workshops |
Title | The study of genotoxicity and immunotoxicity in workers occupationally exposed to cyanide |
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