Chronic exposure to arsenic (As) by drinking shallow groundwater causes widespread disease in Bangladesh and neighboring countries. The release of As naturally present in sediment to groundwater has been linked to the reductive dissolution of iron oxides coupled to the microbial respiration of organic carbon (OC). The source of OC driving this microbial reduction-carbon deposited with the sediments or exogenous carbon transported by groundwater-is still debated despite its importance in regulating aquifer redox status and groundwater As levels. Here, we used the radiocarbon ( 14 C) signature of microbial DNA isolated from groundwater samples to determine the relative importance of surface and sediment-derived OC. Three DNA samples collected from the shallow, high-As aquifer and one sample from the underlying, low-As aquifer were consistently younger than the total sediment carbon, by as much as several thousand years. This difference and the dominance of heterotrophic microorganisms implies that younger, surface-derived OC is advected within the aquifer, albeit more slowly than groundwater, and represents a critical pool of OC for aquifer microbial communities. The vertical profile shows that downward transport of dissolved OC is occurring on anthropogenic timescales, but bomb 14 C-labeled dissolved OC has not yet accumulated in DNA and is not fueling reduction. These results indicate that advected OC controls aquifer redox status and confirm that As release is a natural process that predates human perturbations to groundwater flow. Anthropogenic perturbations, however, could affect groundwater redox conditions and As levels in the future.A quifer redox status is a major factor affecting groundwater composition and its suitability for human consumption. The most egregious example is the dire health impact of elevated levels of arsenic (As) in groundwater drawn with inexpensive handpumped tube wells by more than 100 million villagers across South, Southeast, and East Asia (1, 2). Aquifer redox status is largely controlled by microbial respiration of organic carbon (OC) coupled to the utilization of terminal electron acceptors. Reduction of iron (Fe) oxides containing As coupled with the oxidation of OC is the dominant process causing the accumulation of As in groundwater (1), but there is no consensus on the source of OC that fuels these transformations. Such information is critical to understanding subsurface carbon cycling, redox reactions, and the vulnerability of groundwater aquifers to perturbation.Human perturbations have long been suggested to exacerbate the problem of elevated As in groundwater in several ways. Given the connectivity between contaminated surface waters and aquifers, widespread pumping could redistribute As from the surface to depth (3, 4) or between aquifers (5). This pumping could potentially also deliver reactive OC from ponds and latrines to depth, causing microbial reduction and As release (3, 4). Fluorescent spectra of dissolved organic carbon (DOC), correlations between sedimentary ...