Photo-aging of PVC in deionized water,estuary water,and seawater
To better understand the changes of PVC after long-term aging in marine environments, an UVA accelerated aging experiment was con-
ducted. PVC samples were exposed to UVA radiation for 15 days in deionized water, estuarine water, and seawater. The changes in PVC particle size after 15 days of aging were analyzed by the OMiPA. As shown in Fig.2a, the values of ∣ln∣ for the three environments were 0.108 ± 0.006, 0.123 ± 0.021, and 0.188 ± 0.007, respectively. The results indicate that the particle size of PVC changed differently in the three water environments, with more small particles produced in the aged PVC in water environments, especially in seawater where the particle size reduction was more pronounced. Additionally, the oxygen- containing functional groups formed on the surface of aged MPs cause changes in surface potential and hydrophilicity. As shown in Fig.2b, the zeta potential of pristine PVC was − 0.090 ± 0.187 mV, while after aging, the zeta potentials of PVC in the three water qualities were − 3.296 ± 0.987, − 4.361 ± 1.015, and − 7.138 ± 1.627 mV, respectively. This indicates that UV aging results in more negative charges on the surface of MPs, increasing their polarity and tendency towards insta- bility, especially in adsorbing positively charged pollutants. FTIR anal- ysis, as shown in Fig.2c, revealed the appearance of new absorption peaks at 1600, 1715, and 3435 cm− 1 on the surface of aged PVC in different water environments, corresponding to stretching vibrations of -C=C- groups, stretching vibrations of -C=O groups (associated with -COOH groups), and stretching vibrations of -OH groups. This suggests the formation of oxygen-related functional groups on the surface of PVC during aging, making the MPs more susceptible to fragmentation(Ouyang et al.,2022). The CI value (1715 cm− 1/974 cm− 1) serves as a quantitative indicator of the degree of MPs aging. As shown in Fig.2d, the CI values of aged PVC after 15 days in the three water bodies increased significantly compared to pristine MPs, further indicating the accumulation of oxygen elements on the surface material during pho- toaging. Through the aforementioned analysis, it was found that PVC undergoes photoaging in different water bodies, with a faster aging rate observed in seawater. These findings shed light on the changes of PVC after long-term photoaging in marine environments, including alter- ations in particle size, surface potential and hydrophilicity, and the formation of functional groups, which could significantly affect the stability and adsorption capacity of MPs.

