Inorganic electron donors improve low C/N wastewater denitrification performance and management. This study used an integrated strategy combining proteomics, machine learning, and electron transfer system characterization to elucidate FeS's regulatory mechanisms on microbial denitrification during carbon source depletion. Monitoring results revealed significant differences in denitrification performance between two experimental groups (designated as CK and FD) during both carbon-available (Stage 1) and carbon-depleted (Stage 2) phases. Overall, the denitrification indicators (NO3--N, NO2--N, and TN) of the FD group significantly outperformed those of the CK group in Stage 2. The electron transport system activity (ETSA) in the FD group was consistently higher than that in the CK group. Electrochemical analysis further demonstrated higher electron exchange efficiency of microorganisms in the FD system. Morphology and elemental analysis indicated bacterial surface transformation in FD samples, characterized by significant membrane distortion and attachment of nanoparticles (NPs). Proteomics-driven random forest (RF) modeling identified stage-specific regulatory patterns of FeS, demonstrating distinct mechanistic signatures among differentially up-regulated proteins. Briefly, in Stage 1, bacteria mobilized proteins TenA and GtsB to efficiently utilize glucose, and fully exploiting periplasmic electrons through CYC, NapA, and NosD. In Stage 2, metabolic activities shifted toward conservation. Bacteria upregulated PhaZ to utilize limited endogenous carbon sources, captured more electron donors via the Fe2+ channel opened by OmpU, and mobilized UbiH and NarG to optimize transmembrane electron transfer. These findings are pivotal for developing inorganic electron donor regulation strategies to maintain stable system performance in low C/N wastewater treatment processes.