EDTA has become a major organic pollutant in the environment because of its extreme usage and resistance to biodegradation. Recently, two critical enzymes, EDTA monooxygenase (EmoA) and NADH:FMN oxidoreductase (EmoB), belonging to the newly established two-component flavin-diffusible monooxygenase family, were identified in the EDTA degradation pathway in Mesorhizobium sp. BNC1. EmoA is an FMNH 2 -dependent enzyme that requires EmoB to provide FMNH 2 for the conversion of EDTA to ethylenediaminediacetate. To understand the molecular basis of this FMN-mediated reaction, the crystal structures of the apo-form, FMN⅐FMN complex, and FMN⅐NADH complex of EmoB were determined at 2.5 Å resolution. The structure of EmoB is a homotetramer consisting of four ␣/-single-domain monomers of five parallel -strands flanked by five ␣-helices, which is quite different from those of other known two-component flavin-diffusible monooxygenase family members, such as PheA2 and HpaC, in terms of both tertiary and quaternary structures. For the first time, the crystal structures of both the FMN⅐FMN and FMN⅐NADH complexes of an NADH:FMN oxidoreductase were determined. Two stacked isoalloxazine rings and nicotinamide/isoalloxazine rings were at a proper distance for hydride transfer. The structures indicated a ping-pong reaction mechanism, which was confirmed by activity assays. Thus, the structural data offer detailed mechanistic information for hydride transfer between NADH to an enzyme-bound FMN and between the bound FMNH 2 and a diffusible FMN.EDTA has quietly become a major organic pollutant, currently present in the environment at higher concentrations than any other organic pollutant (1). A high level of EDTA in natural waters is due to its extensive usage, such as in industrial cleaning to remove calcium deposits, in detergent as a sequestering agent, in phytoremediation to mobilize heavy metals, and in scientific laboratories as a chelating agent (2, 3). EDTA is recalcitrant to biodegradation and exists mainly in metal⅐EDTA complexes, many of which are toxic (4, 5). In addition, the codisposal of EDTA with radionuclides has led to the enhanced mobilization of radionuclides in groundwater, rapidly spreading radioactive contamination (3, 6 -8). Concerns over EDTA recalcitrance and the potential mobilization of heavy metals and radionuclides have led the European Union, Australia, and some parts of the United States to ban EDTA in detergent. It is now also being carefully controlled in many other products to reduce contamination of water resources.Several bacteria that can degrade EDTA and the related compound, nitrilotriacetate, and use them as a sole source of carbon and energy have been isolated (9 -12). They are phylogenetically related to Mesorhizobium and Agrobacterium species (11), likely forming a new branch within the Phyllobacteriaceae, the "Mesorhizobia" family (13). In these bacteria, reduced flavin mononucleotide (FMNH 2 )-dependent EDTA monooxygenase (EmoA) and NADH:FMN oxidoreductase (EmoB) together oxidize EDTA to e...