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Accelerated transformation and enhanced gastrointestinal toxicity of tire wear particles during photo-chlorination mediated by reactive species

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Tiny plastic particles from worn tires end up in our water, and this study found that when they're exposed to both sunlight and chlorine (like what happens during water treatment), they break down faster and become more toxic than expected. In lab tests, these transformed particles caused more damage to human stomach cells and mouse intestinal tissue, including harming their ability to absorb nutrients. This suggests that the disinfection processes meant to make our water safer could actually make tire particle pollution more harmful to our gut health, a risk that current water treatment systems aren't designed to address.

Polymers
Body Systems
Models
Study Type Environmental

Elevated concentrations of microplastic in surface water and wastewater necessitate understanding their transformation during disinfection and subsequent discharge. This process occurs inevitably when microplastics enter disinfection systems or are discharged from wastewater treatment plants. However, the behavior of tire wear particles (TWPs), an important and complex microplastic component, remains poorly understood during photo-chlorination. Here, we show that photo-chlorination significantly accelerates TWP transformation and degrades the released organic matter compared to dark-aging, photo-aging, or chlorination alone. Specifically, photo-chlorination induces extensive physical damage, surface oxidation, and chlorine addition in TWPs while simultaneously consuming released organic matter to produce a broader diversity of byproducts. The photolysis of free chlorine generates hydroxyl radicals (HO•) and O, which primarily drive TWP oxidation, while reactive chlorine species (RCS) and HO• induce chlorination reactions. The oxidative effects of HO• and O on TWPs and released organic matter subsequently enhance RCS-mediated degradation of these organic compounds. Critically, photo-chlorinated TWPs and their transformation products exhibit enhanced cytotoxicity toward human gastric epithelial cells, as well as intensified proliferative toxicity and nutrient uptake inhibition in mouse small intestinal organoids. These findings provide new insights into the environmental behavior of TWPs and highlight their potential toxicological implications in impacted water systems.

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