Abstract
Freshwater lakes are globally significant sources of potent greenhouse gases (GHGs), but how their GHGs emissions respond to changing nutrient levels remains unclear. Here, we demonstrated that nitrous oxide (N(2)O) production pathways in lake sediments are tightly linked to trophic state, whereas methane (CH(4)) production appears to be multifactorial Through global metagenomics and controlled batch experiments. In eutrophic sediments, N(2)O is efficiently removed through complete denitrification, with nitrification serving as the main production pathway, whereas oligotrophic sediments produce N(2)O primarily via incomplete denitrification. By simulating nutrient transitions using an innovative cross-inoculation experiment, we further revealed that lake sediments systematically shift between these N(2)O production pathways as their trophic state changes, from denitrification-driven to nitrification-dominated during eutrophication, with the inverse pattern during oligotrophication. Consequently, N(2)O emissions can be effectively mitigated by inhibiting nitrification in eutrophic lakes and restricting incomplete denitrification in oligotrophic ones. Our findings establish trophic status as a key driver of N(2)O production sources in lake sediments.