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Updated: Apr 28, 2026

Protocol for Microplastics Sampling on the Sea Surface and Sample Analysis
Published on: December 16, 2016
Release of microplastics and metals from antifouling paint during weathering in simulated cold climates
Guadalupe Santos1, Georgina C Kalogerakis1, Jun-Ray Macairan1
1Department of Chemical Engineering, McGill University, Montreal, Quebec, H3A 0C5, Canada. nathalie.tufenkji@mcgill.ca.
Abstract:
Marine antifouling paints are often overlooked as a source of microplastic pollution in the aquatic environment even though they may release microplastics and metals, including metallic nanoparticles, into the environment, especially following exposure to environmental stressors. Notably, photodegradation via sunlight and seasonal freeze-thaw cycles are impactful weathering processes that can affect boat hulls in cold climates. In this study, steel coupons coated with marine antifouling paint were submerged in water and exposed to three laboratory-controlled weathering treatments, namely, UV irradiation (UV), freeze-thaw (FT), and UV irradiation combined with freeze-thaw (UV-FT) over 42 days. Water samples were analyzed using optical photothermal infrared spectroscopy (O-PTIR), inductively coupled plasma mass spectrometry (ICP-MS), single particle ICP-MS, and microscopic imaging in order to quantify microplastics, metals and inorganic nanoparticles released from the painted surfaces. Weathering treatments released microplastics through photochemical degradation (UV) and ice abrasion. Meanwhile, for heavy metals, Cu was dominantly released in its microplastic-bound form and Zn in its dissolved form. UV-exposed paint likely underwent oxidative degradation, whereas FT exposure likely caused damage via ice abrasion, resulting in the production of paint microplastics in both cases. The IR and Raman signals showed that paint microplastics generally had high similarity to their respective painted coupons, except for the UV treatment, indicating that paint microplastics can be traced to their original source. Of the three treatments, the combined treatment of UV and FT released the highest concentrations of Cu and Zn over 42 days (49 000 ± 20 000 µg g-1 and 14 000 ± 7000 µg g-1, respectively). Cu was released at higher concentrations under weathering conditions that involved abrasion (i.e., UV-FT and FT). In contrast, more Zn was measured in the UV, HC, and CC treatments. Our findings provide a better understanding of the mechanisms leading to the release of paint-derived contaminants into the environment and further highlight the risks posed by the extensive use of marine antifouling paints.
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