Polymorphisms of xenobiotic metabolism enzyme genes cyp2e1, gstm1, gstt1, ephx1 as biomarkers of sensitivity to exposure to water disinfection byproducts (using chloroform as an example)

View or download the full article: 
UDC: 
614.777-047.36
Authors: 

E.V. Drazdova1, K.V. Kaliasniova1, V.E. Syakhovich2, N.А. Dalhina1

Organization: 

1Scientific and Practical Center for Hygiene, 8 Akademicheskaya Str., Minsk, 220012, Republic of Belarus
2National Anti-Doping Laboratory, 31 ag. Lesnoi, Minsk region, 223040, Republic of Belarus

Abstract: 

Chloroform accumulation in the body and the increase in its steady-state concentrations in blood of exposed people have been established to be associated with polymorphisms of enzyme genes in a genotype involved in metabolism of water disinfection byproducts (A415G of EPHX1 gene, C1091T of CYP2E1 gene, zero mutations of GSTT1 and GSTM1 genes) (р < 0.000001). These polymorphisms in a genotype correlate with higher chloroform levels in blood of people consuming chlorinated drinking water: by 43.8 % and higher for GSTM1 gene polymorphism; by 68.2 % and higher for GSTT1; by 80.4 % and higher for EPHX1 (р < 0.01). EPHX1 genetic polymorphism makes chloroform accumulation much more probable (levels in blood ≥ Р75), which is the most pronounced when combined with GSTТ1 genetic polymorphism.

The study results allow us to consider hetero- and homozygous polymorphic genotypes AG/GG for the EPHX1 gene, CT/TT for the CYP2E1 gene, and the null allele in the GSTT1 and GSTM1 genes as genetic predisposition factors for chloroform accumulation in the body. This increases the probability of health outcomes associated with chronic exposure to this disinfection byproduct.

The A415G polymorphism of the EPHX1 gene and null alleles of GSTT1 gene, their combinations including the combination with the null allele of the GSTM1 gene and/or the C1091T polymorphism of the CYP2E1 gene can be used as the most informative biomarkers of sensitivity when assessing risks associated with exposure to trihalomethanes (chloroform) at levels not exceeding MPC in water.

Keywords: 
CYP2E1, GSTM1, GSTT1, EPHX1 genes, disinfection byproducts, drinking water, gene polymorphism, biomonitoring, health risk assessment, biomarkers of susceptibility
Drоzdova E.V., Kolesneva Е.V., Syakhovich V.E., Dalhina N.А. Polymorphisms of xenobiotic metabolism enzyme genes CYP2E1, GSTM1, GSTT1, EPHX1 as biomarkers of sensitivity to exposure to water disinfection byproducts (using chloroform as an example). Health Risk Analysis, 2023, no. 1, pp. 157–170. DOI: 10.21668/health.risk/2023.1.15.eng
References: 
  1. Guidelines for drinking-water quality, 4th ed. with adds. Geneva, WHO, 2017, 564 p.
  2. Sharma V.K., Zboril R., McDonald T.J. Formation and toxicity of brominated disinfection byproducts during chlorination and chloramination of water: a review. J. Environ. Sci. Health B, 2014, vol. 49, no. 3, pp. 212–228. DOI: 10.1080/03601234.2014.858576
  3. Egorova N.A., Bukshuk A.A., Krasovskiy G.N. Hygienic assessment of drinking water chlorination by-products in view of multiroute exposure. Gigiena i sanitariya, 2013, vol. 92, no. 2, pp. 18–24 (in Russian).
  4. EPA/600/R-06/087. Exposures and internal doses of trihalomethanes in humans: multi-route contributions from drinking water. Available at: http://nepis.epa.gov/Adobe/PDF/.pdf (January 15, 2018).
  5. Kujlu R., Mahdavianpour M., Ghanbari F. Multi-route human health risk assessment from trihalomethanes in drinking and non-drinking water in Abadan, Iran. Environmental Science and Pollution Research, 2020, vol. 27, pp. 42621–42630.
  6. Nieuwenhuijsen M.J., Smith R., Golfinopoulos S. [et al.]. Health impacts of long-term exposure to disinfection by-products in drinking water in Europe: HIWATE. J. Water Health, 2009, vol. 7, no 2, pp. 185–207. DOI: 10.2166/wh.2009.073
  7. Richardson S.D., Plewa M.J., Wagner E.D., Schoeny R., DeMarini D.M. Occurrence, genotoxicity, and carcinogenicity of regulated and emerging disinfection byproducts in drinking water: a review and roadmap for research. Mutat. Res., 2007, vol. 636, no. 1–3, pp. 178–242. DOI: 10.1016/j.mrrev.2007.09.001
  8. Drozdova E.V., Buraya V.V., Girina V.V., Suravets T.Z., Firago A.V. On the formation of drinking water disinfection by-products (regulated and emergent), their genotoxicity and carcinogenic effects: review and perspectives for further studies. Zdorov'e i okruzhayushchaya sreda, 2016, no. 26, pp. 12–16 (in Russian).
  9. Tellez Tovar S.S., Rodriguez Susa M. Cancer risk assessment from exposure to trihalomethanes in showers by inhala-tion. Environ. Res., 2021, vol. 196, pp. 110401. DOI: 10.1016/j.envres.2020.110401
  10. Evlampidou I., Font-Ribera L., Rojas-Rueda D., Gracia-Lavedan E. [et al.]. Trihalomethanes in Drinking Water and Bladder Cancer Burden in the European Union. Environ. Health Perspect., 2020, vol. 128, no. 1, pp. 17001. DOI: 10.1289/EHP4495
  11. Villanueva C.M., Gracia-Lavedan E., Bosetti C., Righi E. [et al.]. Colorectal cancer and long-term exposure to trihal-omethanes in drinking water: a multicenter case-control study in Spain and Italy. Environ. Health Perspect., 2017, vol. 125, no. 1, pp. 56–65. DOI: 10.1289/EHP155
  12. Drozdova E.V., Sychik S.I., Hrynchak V.A., Rjabceva S.N. Experimental models of animal chronic pathology in assessing health risks for sensitive population groups. Health Risk Analysis, 2022, no. 2, pp. 185–195. DOI: 10.21668/health.risk/2022.2.17.eng
  13. Backer L.C., Ashley D.L., Bonin M.A., Cardinali F.L. [et al.]. Household exposures to drinking water disinfection by-products: whole blood trihalomethane levels. J. Expo. Anal. Environ. Epidemiol., 2000, vol. 10, no. 4, pp. 321–326. DOI: 10.1038/sj.jea.7500098
  14. Zaitseva N.V., May I.V., Klein S.V., Sedusova E.V. An experience of establishing and proving of harm to the public health caused by consumption of drinking water containing hyperchlorination products. ZNiSO, 2015, vol. 273, no. 12, pp. 16–18 (in Russian).
  15. Zemlyanova М.А., Pustovalova О.V., Mazunina D.L., Sbov А.S. Biochemical marker indices of negative impacts in children under the exposure to the chlororganic compounds with drinking water. Gigiena i sanitariya, 2016, vol. 95, no. 1, pp. 97–101. DOI: 10.18821/0016-9900-2016-95-1-97-101 (in Russian).
  16. Chetverkina K.V. On determination of reference chloroform content in children’s blood. Health Risk Analysis, 2018, no. 3, pp. 85–93. DOI: 10.21668/health.risk/2018.3.09.eng
  17. Blount B.C., Aylward L.L., Kind J.S., Backer L.S., Hays S.M. Human exposure assessment for DBPs: factors influencing blood trihalomethane levels. Encyclopedia of Environmental Health, 2011, vol. 3, pp. 100–107. DOI: 10.1016/B978-0-444-52272-6.00103-3
  18. Ashley D.L., Blount B.C., Singer P.C. [et al.]. Changes in blood trihalomethane concentrations resulting from differences in water quality and water use activities. Arch. Environ. Occup. Health, 2005, vol. 60, no. 1, pp. 7–15. DOI: 10.3200/AEOH.60.1.7-15
  19. Nuckols J.R., Ashley D.L., Lyu C., Gordon S.M. [et al.]. Influence of tap water quality and household water use activ-ities on indoor air and internal dose levels of trihalomethanes. Environ. Health Perspect., 2005, vol. 113, no. 7, pp. 863–870. DOI: 10.1289/ehp.7141
  20. Backer L.C., Lan Q., Blount B.C., Nuckols J.R. [et al.]. Exogenous and Endogenous Determinants of Blood Trihalo-methane Levels after Showering. Environ. Health Perspect., 2008, vol. 116, no. 1, pp. 57–63. DOI: 10.1289/ehp.10049
  21. Riederer A.M., Dhingra R., Blount B.C., Steenland K. Predictors of blood trihalomethane concentrations in NHANES 1999–2006. Environ. Health Perspect., 2014, vol. 122, no. 7, pp. 695–702. DOI: 10.1289/ehp.1306499
  22. Caccamo D., Cesareo E., Mariani S., Raskovic D. [et al.]. Xenobiotic Sensor- and Metabolism-Related Gene Variants in Environmental Sensitivity-Related Illnesses: A Survey on the Italian Population. Oxid. Med. Cell. Longev., 2013, vol. 2013, pp. 831969. DOI: 10.1155/2013/831969
  23. Gandarilla-Esparza D.D., Calleros-Rincón E.Y., Macias H.M., González-Delgado M.F. [et al.]. FOXE1 polymorphisms and chronic exposure to nitrates in drinking water cause metabolic dysfunction, thyroid abnormalities, and genotoxic damage in women. Genet. Mol. Biol., 2021, vol. 44, no. 3, pp. e20210020. DOI: 10.1590/1678-4685-GMB-2021-0020
  24. Thier R., Brüning T., Roos P.H., Rihs H.P. [et al.]. Markers of genetic susceptibility in human environmental hygiene and toxicology: the role of selected CYP, NAT and GST genes. Int. J. Hyg. Environ. Health, 2003, vol. 206, no. 3, pp. 149–171. DOI: 10.1078/1438-4639-00209
  25. Autrup H. Genetic polymorphysms in human xenobiotica metabolizing enzymes as suscectibility factors in toxic re-sponse. Mutat. Res., 2000, vol. 464, no. 1, pp. 65–76. DOI: 10.1016/s1383-5718(99)00167-9
  26. Salas L.A., Bustamante M., Gonzalez J.R., Gracia-Lavedan E. [et al.]. DNA methylation levels and long-term trihal-omethane exposure in drinking water: an epigenome-wide association study. Epigenetics, 2015, vol. 10, no. 7, pp. 650–661. DOI: 10.1080/15592294.2015.1057672
  27. Kogevinas M., Bustamante M., Gracia-Lavedán E., Ballester F. [et al.]. Drinking Water Disinfection By-products, Genetic Polymorphisms, and Birth Outcomes in a European Mother-Child Cohort Study. Epidemiology, 2016, vol. 27, no. 6, pp. 903–911. DOI: 10.1097/EDE.0000000000000544
  28. Cantor K.P., Villanueva C.M., Silverman D.T., Figueroa J.D. [et al.]. Polymorphisms in GSTT1, GSTZ1, and CYP2E1, Disinfection By-products, and Risk of Bladder Cancer in Spain. Environ. Health Perspect., 2010, vol. 118, no. 11, pp. 1545–1550. DOI: 10.1289/ehp.1002206
  29. Infante-Rivard C. Drinking Water Contaminants, Gene Polymorphisms, and Fetal Growth. Environ. Health Perspect., 2004, vol. 112, no. 11, pp. 1213–1216. DOI: 10.1289/ehp.7003
  30. Zhou B., Yang P., Gong Y.-J., Zeng Q. [et al.]. Effect modification of CYP2E1 and GSTZ1 genetic polymorphisms on associations between prenatal disinfection by-products exposure and birth outcomes. Environ. Pollut., 2018, vol. 243, pt B, pp. 1126–1133. DOI: 10.1016/j.envpol.2018.09.083
  31. Bonou S.G., Levallois P., Giguère Y., Rodriguez M., Bureau A. Prenatal exposure to drinking-water chlorination by-products, cytochrome P450 gene polymorphisms and small-for-gestational-age neonates. Reprod. Toxicol., 2017, vol. 73, pp. 75–86. DOI: 10.1016/j.reprotox.2017.07.019
  32. Yang P., Zeng Q., Cao W.-C., Wang Y.-X. [et al.]. Interactions between CYP2E1, GSTZ1 and GSTT1 polymorphisms and exposure to drinking water trihalomethanes and their association with semen quality. Environ. Res., 2016, vol. 147, pp. 445–452. DOI: 10.1016/j.envres.2016.03.009
  33. Garte S., Gaspari L., Alexandrie A.K., Ambrosone C. [et al.]. Metabolic gene polymorphism frequencies in control populations. Cancer Epidemiol. Biomarkers Prev., 2001, vol. 10, no. 12, pp. 1239–1248.
  34. Drozdova E.V., Sychik S.I., Syakhovich V.E., Pakhadnia K.N. [et al.]. Chloroform content in the blood of the popula-tion as a biomarker of exposure to drinking water disinfection by-products. Meditsinskii zhurnal, 2023, vol. 83, no. 1, pp. 23–32. DOI: 10.51922/1818-426X.2023.1.23 (in Russian).
Received: 
07.10.2022
Approved: 
13.03.2023
Accepted for publication: 
21.03.2023

You are here