The photochemical behavior of microplastics (MPs)-dissolved organic matter (PDOM) has received considerable attention, the molecular mechanism by which it undergoes photoresponsive transformation to generate reactive oxygen species (ROS) for the removal of organic pollutants remains unclear. This study combines fluorescence, mass spectrometry, and theoretical models to analyse the differences in the molecular mechanisms of PDOM, biochar-DOM (BDOM) and soil-DOM (SDOM) photoresponsive releasing ROS for selective degradation of organic pollutants. During the photoresponse process, molecular compounds in DOMs mainly undergo demethylation, decarboxylation, deoxygenation reactions to selectively degrade organic pollutants. However, differences in DOMs’ molecular structure composition and transformation patterns lead to varying ROS production. BDOMs containing higher proportion of aromatic compounds (26.68 %) exhibit stronger photoreactivity, resulting in better degradation efficiency of pollutants (>90 %). The high selectivity of PDOM for degradation of organic pollutants stems from the interconversion mode between its high and low oxygen compounds. PDOM degrades large molecular pollutants into less biotoxic small molecular intermediates through both radical and non-radical pathways, thereby reducing environmental hazards (1.5–948 times) posed by pollutants. The results show that although MPs is harmful to aquatic environment, it plays a positive role in regulating the structure of organic carbon pool and reducing environmental risks of other pollutants.