Human exposure assessment of organophosphate esters (OPEs) through dust ingestion and dermal absorption in Colombian cities

Rafael Olivero-Verbel , Boris Johnson-Restrepo , Ethel Eljarrat

Journal of Environmental Exposure Assessment ›› 2022, Vol. 1 ›› Issue (2) : 8

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Journal of Environmental Exposure Assessment ›› 2022, Vol. 1 ›› Issue (2) :8 DOI: 10.20517/jeea.2021.08
Research Article

Human exposure assessment of organophosphate esters (OPEs) through dust ingestion and dermal absorption in Colombian cities

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Abstract

Concentrations of 19 organophosphate esters (OPEs) were determined in dust samples collected from house and car indoor microenvironments in three Colombian cities. ∑OPE concentrations ranged from 1.31 to 599 μg/g. Mean concentrations of dust homes were 82.6, 48.3, and 46.7 μg/g for Cartagena, Bogotá, and Medellín, respectively. The pollution inside cars was somewhat higher than in houses, with a mean value of 231 μg/g. Sixteen compounds were detected, being TPHP, DCP, TEP, and TCEP the most frequently detected. As for OPEs with higher levels in houses, we found (mean ± SD) 35.2 ± 37.1 μg/g for TDCIPP in Cartagena, 35.6 ± 80.2 μg/g for TPHP in Cartagena, 15.9 ± 31.4 μg/g for DCP in Cartagena, 35.7 ± 19.1 μg/g for TBOEP in Bogotá, 15.7 ± 14.8 μg/g for 4IPPDPP in Medellín, and 17.5 ± 22.9 μg/g for TCEP in Cartagena, while the highest OPE value found in cars was 176 ± 144 μg/g for TDCIPP. The estimated daily intake (EDI) of OPEs through dust ingestion ranged from 0.001 ng/kg bw/day for adults to 110 ng/kg bw/day for toddlers, while dermal absorption ranged from 0.02 ng/kg bw/day for adults to 42.7 ng/kg bw/day for infants. Overall, the EDIs of dust ingestion were three times greater than those of dust dermal absorption. The estimated EDIs were several orders of magnitude below the corresponding reference doses. However, the incremental lifetime cancer risk (ILCR) for TCEP ranged from 1.1 × 10-5 for infants in Bogotá to 4.3 × 10-4 for adults in Cartagena, while ILCR for TEHP ranged from 8.8 × 10-7 for infants in Bogotá to 1.1 × 10-5 for adults in Bogotá. These estimated ILCRs were higher than the safe limit value of 1 × 10-6 and showed that these populations are exposed to moderate cancer risk.

Keywords

Cancer risk / car dust / daily intake / home dust / indoor / Monte Carlo simulations

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Rafael Olivero-Verbel, Boris Johnson-Restrepo, Ethel Eljarrat. Human exposure assessment of organophosphate esters (OPEs) through dust ingestion and dermal absorption in Colombian cities. Journal of Environmental Exposure Assessment, 2022, 1(2): 8 DOI:10.20517/jeea.2021.08

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References

[1]

de Wit CA.An overview of brominated flame retardants in the environment.Chemosphere2002;46:583-624

[2]

Alaee M.An overview of commercially used brominated flame retardants, their applications, their use patterns in different countries/regions and possible modes of release.Environ Int2003;29:683-9

[3]

Saito I,Seto H.Indoor organophosphate and polybrominated flame retardants in Tokyo.Indoor Air2007;17:28-36

[4]

Johnson-Restrepo B.An assessment of sources and pathways of human exposure to polybrominated diphenyl ethers in the United States.Chemosphere2009;76:542-8

[5]

Khan MU,Zhang G.First insight into the levels and distribution of flame retardants in potable water in Pakistan: an underestimated problem with an associated health risk diagnosis.Sci Total Environ2016;565:346-59

[6]

Li HL,Zhang ZF.Semi-volatile organic compounds in infant homes: Levels, influence factors, partitioning, and implications for human exposure.Environ Pollut2019;251:609-18

[7]

Wang R,Xie Z.Occurrence and spatial distribution of organophosphate ester flame retardants and plasticizers in 40 rivers draining into the Bohai Sea, north China.Environ Pollut2015;198:172-8

[8]

Mizouchi S,Takigami H.Exposure assessment of organophosphorus and organobromine flame retardants via indoor dust from elementary schools and domestic houses.Chemosphere2015;123:17-25

[9]

Meyer J.Organophosphate flame retardants and plasticisers in wastewater treatment plants.J Environ Monit2004;6:599-605

[10]

Rodil R,Concha-Graña E,Muniategui-Lorenzo S.Emerging pollutants in sewage, surface and drinking water in Galicia (NW Spain).Chemosphere2012;86:1040-9

[11]

Li J,Li Y.Assessing the threats of organophosphate esters (flame retardants and plasticizers) to drinking water safety based on USEPA oral reference dose (RfD) and oral cancer slope factor (SFO).Water Res2019;154:84-93

[12]

Li W,Asimakopoulos AG.Organophosphate esters in indoor dust from 12 countries: concentrations, composition profiles, and human exposure.Environ Int2019;133:105178

[13]

Giulivo M,Eljarrat E.Analysis of organophosphorus flame retardants in environmental and biotic matrices using on-line turbulent flow chromatography-liquid chromatography-tandem mass spectrometry.J Chromatogr A2016;1474:71-8

[14]

Garcia-Garin O,Aguilar A.Organophosphate contaminants in North Atlantic fin whales.Sci Total Environ2020;721:137768

[15]

Canbaz D,van Ree R.Immunotoxicity of organophosphate flame retardants TPHP and TDCIPP on murine dendritic cells in vitro.Chemosphere2017;177:56-64

[16]

Du Z,Gao S.Aryl organophosphate flame retardants induced cardiotoxicity during zebrafish embryogenesis: by disturbing expression of the transcriptional regulators.Aquat Toxicol2015;161:25-32

[17]

Voorhees JR,Lein PJ.Neurotoxicity in preclinical models of occupational exposure to organophosphorus compounds.Front Neurosci2016;10:590 PMCID:PMC5241311

[18]

Hales BF.Effects of brominated and organophosphate ester flame retardants on male reproduction.Andrology2020;8:915-23

[19]

Wang C,Li H,Wang X.Review of emerging contaminant tris(1,3-dichloro-2-propyl)phosphate: Environmental occurrence, exposure, and risks to organisms and human health.Environ Int2020;143:105946

[20]

WHO (World Health Organization). Tri-n-butyl phosphate, Geneva, Switzerland. Environmental Health Criteria 112. Available from: https://inchem.org/documents/ehc/ehc/ehc112.htm [Last accessed on 2 Mar 2022]

[21]

Wu M,Cao Z.Characterization and human exposure assessment of organophosphate flame retardants in indoor dust from several microenvironments of Beijing, China.Chemosphere2016;150:465-71

[22]

Liu X,Jo A,Choi K.Effects of TDCPP or TPP on gene transcriptions and hormones of HPG axis, and their consequences on reproduction in adult zebrafish (Danio rerio).Aquat Toxicol2013;134-135:104-11

[23]

Zhao F,Fang Y.Effects of tris(1,3-dichloro-2-propyl)phosphate on pathomorphology and gene/protein expression related to thyroid disruption in rats.Toxicol Res (Camb)2016;5:921-30 PMCID:PMC6062395

[24]

IARC (International Agency for Research on Cancer). IARC monographs on the evaluation of carcinogenic risks to humans. Available from: https://monographs.iarc.who.int/wp-content/uploads/2018/06/mono77.pdf [Last accessed on 2 Mar 2022]

[25]

European Commission. European Union Risk Assessment Report. Tris (2-chloroethyl) phosphate, TCEP. Available from: https://echa.europa.eu/documents/10162/2663989d-1795-44a1-8f50-153a81133258 [Last accessed on 2 Mar 2022]

[26]

Wei GL,Zhuo MN.Organophosphorus flame retardants and plasticizers: sources, occurrence, toxicity and human exposure.Environ Pollut2015;196:29-46

[27]

Sakhi AK,Becher R.Concentrations of selected chemicals in indoor air from Norwegian homes and schools.Sci Total Environ2019;674:1-8

[28]

Ageel HK,Abdallah MA.Occurrence, human exposure, and risk of microplastics in the indoor environment.Environ Sci Process Impacts2022;24:17-31

[29]

Abdallah MA.Organophosphate flame retardants in indoor dust from Egypt: implications for human exposure.Environ Sci Technol2014;48:4782-9

[30]

Li W,Gao L,Liu J.Occurrence, distribution and risk of organophosphate esters in urban road dust in Beijing, China.Environ Pollut2018;241:566-75

[31]

Sun Y,Sverko E.Organophosphate flame retardants in college dormitory dust of northern Chinese cities: occurrence, human exposure and risk assessment.Sci Total Environ2019;665:731-8

[32]

Zhou L,Gruber D.Organophosphate flame retardants (OPFRs) in indoor and outdoor air in the Rhine/Main area, Germany: comparison of concentrations and distribution profiles in different microenvironments.Environ Sci Pollut Res Int2017;24:10992-1005

[33]

U.S. Environmental Protection Agency. Guidance on selecting age groups for monitoring and assessing childhood exposures to environmental contaminants. Available from: https://www.epa.gov/sites/default/files/2013-09/documents/agegroups.pdf [Last accessed on 2 Mar 2022]

[34]

U.S. Environmental Protection Agency. HPV Chemical Hazard Characterizations. Available from: http://iaspub.epa.gov/oppthpv/hpv_hc_characterization.get_report [Last accessed on 2 Mar 2022]

[35]

U.S. Environmental Protection Agency. EPA’s Exposure Factors Handbook (EFH). Available from: https://www.epa.gov/expobox/about-exposure-factors-handbook [Last accessed on 2 Mar 2022]

[36]

Maceira A,Marcé RM.Occurrence of plastic additives in outdoor air particulate matters from two industrial parks of Tarragona, Spain: human inhalation intake risk assessment.J Hazard Mater2019;373:649-59

[37]

Wang Y,Han X,Zh H.Organophosphate di- and tri-esters in indoor and outdoor dust from China and its implications for human exposure.Sci Total Environ2019;700:134502

[38]

U.S. Environmental Protection Agency. Exposure Factors Handbook 2011 Edition (Final Report). Available from: https://cfpub.epa.gov/ncea/risk/recordisplay.cfm?deid=236252 [Last accessed on 2 Mar 2022]

[39]

U.S. Environmental Protection Agency. Provisional Peer Reviewed Toxicity Values for Tris(2-ethylhexyl)phosphate (CASRN 78-42-2). Available from: https://cfpub.epa.gov/ncea/pprtv/documents/Tris2ethylhexylphosphate.pdf [Last accessed on 2 Mar 2022]

[40]

U.S. Environmental Protection Agency. Provisional Peer Reviewed Toxicity Values for Triphenylphosphine oxide (CASRN 791-28-6). Available from: https://cfpub.epa.gov/ncea/pprtv/documents/TriphenylphosphineOxide.pdf [Last accessed on 2 Mar 2022]

[41]

U.S. Environmental Protection Agency. Provisional Peer-Reviewed Toxicity Values for Tris(2-chloroethyl)phosphate (TCEP) (CASRN 115-96-8). Available from: https://cfpub.epa.gov/ncea/pprtv/documents/Tris2chloroethylphosphate.pdf [Last accessed on 2 Mar 2022]

[42]

U.S. Environmental Protection Agency. Provisional Peer-Reviewed Toxicity Values for Tris(1-chloro-2-propyl)phosphate (CASRN 13674-84-5). Available from: http://www.epa.gov/dfe/pubs/projects/flameret/about.htm [Last accessed on 2 Mar 2022]

[43]

ATSDR (Agency for Toxic Substances and Disease Registry). Toxicological profile for Phosphate Ester Flame Retardants. Available from: https://www.atsdr.cdc.gov/toxprofiles/tp202.pdf [Last accessed on 2 Mar 2022]

[44]

US-EPA. Risk assessment guidance for Superfund. Volume I, Human health evaluation manual. Part A. Available from: https://www.epa.gov/sites/default/files/2015-09/documents/rags_a.pdf [Last accessed on 2 Mar 2022]

[45]

Kim UJ,Li W.Occurrence of and human exposure to organophosphate flame retardants/plasticizers in indoor air and dust from various microenvironments in the United States.Environ Int2019;125:342-9

[46]

Esplugas R,Mari M.Emerging and legacy flame retardants in indoor air and dust samples of Tarragona Province (Catalonia, Spain).Sci Total Environ2022;806:150494

[47]

Tokumura M,Tatsu K.Organophosphate flame retardants in the indoor air and dust in cars in Japan.Environ Monit Assess2017;189:48

[48]

Tao F,de Wit CA.Organohalogenated Flame Retardants and Organophosphate Esters in Office Air and Dust from Sweden.Environ Sci Technol2019;53:2124-33

[49]

Zhou L.Distributions of organophosphate flame retardants (OPFRs) in three dust size fractions from homes and building material markets.Environ Pollut2019;245:343-52

[50]

Ali N,Van den Eede N.Occurrence of alternative flame retardants in indoor dust from New Zealand: indoor sources and human exposure assessment.Chemosphere2012;88:1276-82

[51]

Tajima S,Kawai T.Detection and intake assessment of organophosphate flame retardants in house dust in Japanese dwellings.Sci Total Environ2014;478:190-9

[52]

Quednow K.Temporal concentration changes of DEET, TCEP, terbutryn, and nonylphenols in freshwater streams of Hesse, Germany: possible influence of mandatory regulations and voluntary environmental agreements.Environ Sci Pollut Res Int2009;16:630-40

[53]

Chen Y,Covaci A,Cui X.Novel and legacy flame retardants in paired human fingernails and indoor dust samples.Environ Int2019;133:105227

[54]

Wang G,Zhao X,Wang H.Geographical distributions and human exposure of organophosphate esters in college library dust from Chinese cities.Environ Pollut2019;255:113332

[55]

Kanchanapiya P,Songngam S.Organophosphate flame retardants in car dust from Thailand and implications for human exposure.IJCEA2021;12:1-6

[56]

WHO. EHC 218: Flame Retardants: Tris(2-butoxyethyl) phosphate, Tris(2-Ethylhexyl) Phosphate and Tetrakis (Hydroxymethyl) Phosphonium Salts. Available from: http://apps.who.int/iris/bitstream/handle/10665/42248/WHO_EHC_218.pdf?sequence=1 [Last accessed on 2 Mar 2022]

[57]

WHO. EHC 209: Flame Retardants: Tris-(Chloropropyl)Phosphate and Tris-(2-Chloroethyl)phosphate. Available from: https://www.who.int/ipcs/publications/ehc/who_ehc_209.pdf [Last accessed on 2 Mar 2022]

[58]

Ali N,Ismail IMI.Exposure to Phthalate and organophosphate esters via indoor dust and PM10 is a cause of concern for the exposed Saudi population.Int J Environ Res Public Health2021;18:2125 PMCID:PMC7926922

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