1.6 Conclusions
The use of sorbent-based microextraction techniques is a current trend in sample preparation that will surely continue its consolidation during next years as a result of their inherent advantages related with Green Analytical Chemistry principles. Such techniques have also been applied with success for the extraction of PAEs from different types of water samples. Among them, SPME has been mostly used, followed by dSPE. SBSE, as a variation of SPME, has also been applied but in extremely few occasions together with other small variants of each of the technique. Though commercial sorbents can also be used for such purpose, the latest achievements in this field have been done using laboratory made coatings, mainly using nanomaterials such as MWCNTs, graphene, GO, coated m-NPs, etc., as well as new polymers or nanoporous materials such as MOFs. In this last case, a suitable characterization of them using different surface characterization techniques is necessary as well as clear demonstration of their stability and batch-to-batch reproducibility. In all probability, this will constitute an active research area in the near future.
Once suitably optimized, the application of all these extraction procedures has demonstrated that PAEs are present in nearly any type of water sample as a result of their capacity to migrate from plastics, which is probably their main source. Further studies should also continue to be assessed in order to continue monitoring their presence in all environmental compartments.
Acknowledgements
J.G.S. would like to thank “Cabildo de Tenerife” for the Agustín de Betancourt contract at the Universidad de La Laguna.
References
1. Feng, C.-H., Jiang, S.-R., Micro-scale quantitation of ten phthalate esters in water samples and cosmetics using capillary liquid chromatography coupled to UV detection: effective strategies to reduce the production of organic waste. Microchim. Acta, 177, 167, 2012.
2. Rahman, M., Brazel, C.S., The plasticizer market: an assessment of traditional plasticizers and research trends to meet new challenges. Prog. Polym. Sci., 29, 1223, 2004.
3. Ceresana. Market study: Plasticizers (5th edition), 2019.
4. Net, S., Sempéré, R., Delmont, A., Paluselli, A., Ouddane, B., Occurrence, fate, behavior and ecotoxicological state of phthalates in different environmental matrices. Environ. Sci. Technol., 49, 4019, 2015.
5. Gao, D., Li, Z., Wang, H., Liang, H., An overview of phthalate acid ester pollution in China over the last decade: Environmental occurrence and human exposure. Sci. Total Environ., 645, 1400, 2018.
6. Hermabessiere, L., Dehaut, A., Paul-Pont, I., Lacroix, C., Jezequel, R., Soudant, P., Duflos, G., Occurrence and effects of plastic additives on marine environments and organisms: A review. Chemosphere, 182, 781, 2017.
7. Ding, M., Kang, Q., Zhang, S., Zhao, F., Mu, D., Zhang, H., Yang, M., Hu, J., Contribution of phthalates and phthalate monoesters from drinking water to daily intakes for the general population. Chemosphere, 229, 125, 2019.
8. Benjamin, S., Masai, E., Kamimura, N., Takahashi, K., Anderson, R.C., Faisal, P.A., Phthalates impact human health: Epidemiological evidences and plausible mechanism of action. J. Hazard. Mater., 340, 360, 2017.
9. Arcadi, F.A., Costa, C., Imperatore, C., Marchese, A., Rapisarda, A., Salemi, M., Trimarchi, G.R., Costa, G., Oral toxicity of bis(2-ethylhexyl) phthalate during pregnancy and suckling in the long–Evans rat. Food Chem. Toxicol., 36, 963, 1998.
10. Latini, G., De Felice, C., Verrotti, A., Plasticizers, infant nutrition and reproductive health. Reprod. Toxicol., 19, 27, 2004.
11. Benson, R., Hazard to the developing male reproductive system from cumulative exposure to phthalate esters—dibutyl phthalate, diisobutyl phthalate, butylbenzyl phthalate, diethylhexyl phthalate, dipentyl phthalate, and diisononyl phthalate. Regul. Toxicol. Pharmacol., 53, 90, 2009.
12. Lhuguenot, J.-C., Mitchell, A.M., Milner, G., Lock, E.A., Elcombe, C.R., The metabolism of di(2-ethylhexyl) phthalate (DEHP) and mono-(2-ethylhexyl) phthalate (MEHP) in rats: In vivo and in vitro dose and time dependency of metabolism. Toxicol. Appl. Pharmacol., 80, 11, 1985.
13. Jonsson, S., Ejlertsson, J., Ledin, A., Mersiowsky, I., Svensson, B.H., Monoand diesters from o-phthalic acid in leachates from different European landfills. Water Res., 37, 609, 2003.
14. Jornet-Martínez, N., Muñoz-Ortuño, M., Moliner-Martínez, Y., Herráez-Hernández, R., Campíns-Falcó, P., On-line in-tube solid phase microextraction-capillary liquid chromatography method for monitoring degradation products of di-(2-ethylhexyl) phthalate in waters. J. Chromatogr. A, 1347, 157, 2014.
15. Commission of the European Communities. Communication from the Commission to the Council and the European Parliament on the implementation of the community strategy for endocrine disrupters—a range of substances suspected of interfering with the hormone systems of humans and wildlife, COM1999, Brussels, 1999.
16. International Agency for Research on Cancer. Agents Classified by the IARC Monographs, Volumes 1–123, 2018.
17. US Environmental Protection Agency. National Primary Drinking Water Regulations, Federal register, Part 12, 40 CFR Part 141, 1991.
18. Guidelines for Drinking-Water Quality, third ed. World Health Organization, Volume 1, 2008.
19. Directive 2008/105/EC of the European Parliament and of the Council of 16 December 2008 on environmental quality standards in the field of water policy, amending and subsequently repealing Council Directives 82/176/EEC, 83/513/EEC, 84/156/EEC, 84/491/EEC, 86/280/EEC and amending Directive 2000/60/EC of the European Parliament and of the Council. Off. J. Eur. Union, L 348, 84, 2008.
20. Amanzadeh, H., Yamini, Y., Moradi, M., Asl, Y.A., Determination of phthalate esters in drinking water and edible vegetable oil samples by headspace solid phase microextraction using graphene/polyvinylchloride nanocomposite coated fiber coupled to gas chromatography-flame ionization detector. J. Chromatogr. A, 1465, 38, 2016.
21. Cao, X.-L., Determination of phthalates and adipate in bottled water by headspace solid-phase microextraction and gas chromatography/mass spectrometry. J. Chromatogr. A, 1178, 231, 2008.
22. González-Sálamo, J., Socas-Rodríguez, B., Hernández-Borges, J., Rodríguez-Delgado, M.Á., Determination of phthalic acid esters in water samples using core-shell poly(dopamine) magnetic nanoparticles and gas chromatography tandem mass spectrometry. J. Chromatogr. A, 1530, 35, 2017.
23. Wang, X., Feng, J., Tian, Y., Li, C., Ji, X., Luo, C., Sun, M., Melamine-formaldehyde aerogel functionalized with polydopamine as in-tube solid-phase microextraction coating for the determination of phthalate esters. Talanta, 199, 317, 2019.
24. Zhou, Q., Fang, Z., Liao, X., Determination of phthalate esters from environmental water samples by micro-solid-phase extraction using TiO2 nanotube arrays before high-performance liquid chromatography. J. Sep.