The reduction of HgII to HgI or Hg0 can lead to significant changes in Hg toxicity and mobility in the environment. Photochemical reduction is the primary process for the reduction of HgII to Hg0 in sunlit environments; however, dark reduction of HgII can occur via microbial metabolic processes and/or reduction by reduced natural organic matter, FeII mineral phases, FeII sorbed to minerals, or aqueous FeII. Here, we demonstrate a novel HgII reduction pathway involving another environmentally relevant reductant, MnII. Abiotic reduction of HgIIO by MnII was studied as a function of pH and anion environment (perchlorate, sulfate, chloride) using X-ray absorption spectroscopy to characterize the solid-phase Hg and Mn species. At circumneutral pH of 7.5, about 70% of HgII was reduced to elemental Hg0 within 2 h. In contrast, 12 h were needed to achieve the same extent of reduction at pH 6.9. In the presence of sulfate and chloride, HgI species were formed. HgII reduction was initially rapid and coupled with the oxidation of soluble MnII-oxides to insoluble MnIV-oxides, followed by a significantly slower reduction of HgII during the MnII-catalyzed transformation of the MnIV-oxides to hydroxide and oxyhydroxide minerals. The observed reduction of HgII by MnII at circumneutral pH could be an important transformation pathway for environmental Hg, affecting its bioavailability and mobility under mildly reducing conditions.