1Anthropogenic stressors, such as climate change or chemical pollution, affect indi-2 vidual species and alter species interactions. Moreover, species interactions can modify 3 effects of anthropogenic stressors on interacting species -a process which may vary 4 amongst stressors or stressor combinations. Most ecotoxicological work focuses on 5 single stressors on single species. Here, we test hypotheses about multiple stressors 6 (climate change and tire wear particles) and interacting species, and whether species 7 interactions modify responses. We use duckweed and its microbiome to model responses 8 of plant-microbe interactions. Climate change is occurring globally, and with increasing 9 urbanization, tire wear particles increasingly contaminate road runoff. Their leachate is 10 associated with zinc, PAHs, plastic additives, and other toxic compounds. We crossed 11 perpendicular gradients of temperature and CO 2 in a well plate with factorial manip-12 ulation of leachate from tire wear particles and presence of duckweed microbiomes. 13 We measured duckweed and microbial growth, duckweed greenness, and plant-microbe 14 growth correlations. We found that tire leachate and warmer temperatures enhanced 15 duckweed and microbial growth, but microbes diminished positive responses in duck-16 weed, meaning microbiomes became costly for duckweed. These costs of microbiomes 17 were less-than-additive with warming and leachate, and might be caused by leachate-18 disrupted endocrine signaling in duckweed. We observed reduced greenness at higher 19 CO 2 without tire leachate, suggesting a relative increase in plant nutrient demand, and 20 possibly underlying positive plant-microbe growth correlations in these conditions, as 21 microbes presumably increase nutrient availability. However, with tire leachate, growth 22 correlations were never positive, and shifted negative at lower CO 2 , further suggesting 23 leachate favors mutualism disruption. In summary, while individual stressors of global 24 change can affect individual species, in ecology we know species interact; and in ecotox-25 icology, we know stressors interact. Our results demonstrate this complexity: multiple 26 stressors can affect species interactions, and species interactions can alter effects of 27 multiple stressors. 28