Microplastics (MPs) are particles smaller than 5 mm in diameter, formed mostly by fragmentation of plastic waste or produced as primary MPs, and they present a global environmental pollution problem. Very problematic is the leaching of toxic chemical additives from the material and MPs’ capability to serve as vectors for organic pollutants in aquatic environment. Pollutants are adsorbed on the hydrophobic surface of MPs via hydrophobic, electrostatic, and non-covalent interactions. Adsorption capacity depends on characteristics of MPs, chemical properties of micropollutants, and environmental factors. The presence of MPs can generate different radicals that modify photodegradation of organic compounds in freshwater and seawater.
The aim of this research was the optimization of analytical methods for photodegradation products adsorbed on MPs for two groups of important environmental pollutants. First group are phthalate esters (represented by dimethyl and dibutyl phthalate) and their photodegradation products. Second group are polycyclic aromatic hydrocarbons, PAH (naphthalene, acenaphthene, phenanthrene, fluoranthene) and some of their photodegradation products.
A separation method was developed for mix of all pollutants listed above, using high-performance liquid chromatography (HPLC-DAD). For sample pretreatment, solid-phase extraction (SPE) was optimized for each group separately. Comparison of different columns (LC-8 and HLB), elution solvents (methanol and acetonitrile in different ratios), washing steps (Milli Q water), effect of sample pH (3.0 – 4.7) and ionic strength (addition of NaCl) were investigated. Finally, the optimized HPLC method was transferred to liquid chromatography – tandem mass spectrometry (LC-MS/MS). Different scan modes were used to identify the degradation products.
The complete method was applied to model aqueous samples of PAH containing already desorbed compounds from MPs particles after UV radiation and model aqueous samples of dibutyl phthalate treated with electrooxidation. Based on fragmentation patterns I successfully proposed identity of some peaks. Interferences were observed in all the samples. With additional high-resolution MS analysis of PAH samples, I confirmed structures of the degradation products.
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