Cyanobacteria, algae, and plants oxidize water to the O 2 we breathe, and consume CO 2 during the synthesis of biomass. Although these vital processes are functionally and structurally well separated in photosynthetic organisms, there is a long-debated role for CO 2 /HCO − 3 in water oxidation. Using membrane-inlet mass spectrometry we demonstrate that HCO − 3 acts as a mobile proton acceptor that helps to transport the protons produced inside of photosystem II by water oxidation out into the chloroplast's lumen, resulting in a light-driven production of O 2 and CO 2 . Depletion of HCO − 3 from the media leads, in the absence of added buffers, to a reversible down-regulation of O 2 production by about 20%. These findings add a previously unidentified component to the regulatory network of oxygenic photosynthesis and conclude the more than 50-y-long quest for the function of CO 2 / HCO − 3 in photosynthetic water oxidation.O xygenic photosynthesis in cyanobacteria, algae, and higher plants leads to the reduction of atmospheric CO 2 to energy-rich carbohydrates. The electrons needed for this process are extracted in a cyclic, light-driven process from water that is split into dioxygen (O 2 ) and protons. This reaction is catalyzed by a penta-μ-oxo bridged tetra-manganese calcium cluster (Mn 4 CaO 5 ) within the oxygen-evolving complex (OEC) of photosystem II (PSII) (1-4). The possible roles of inorganic carbon, C i ðC i = CO 2 ; H 2 CO 3 ; HCO − 3 ; CO 2− 3 Þ, in this process have been a controversial issue ever since Otto Warburg and Günter Krippahl (5) reported in 1958 that oxygen evolution by PSII strictly depends on CO 2 and therefore has to be based on the photolysis of H 2 CO 3 ("Kohlensäure") and not of water. These first experiments were indirect and, as became apparent later, were wrongly interpreted (6-8). Several research groups followed up on these initial results and identified two possible sites of C i interaction within PSII (reviewed in refs. 9-12). Functional and spectroscopic studies showed that HCO − 3 facilitates the reduction of the secondary plastoquinone electron acceptor (Q B ) of PSII by participating in the protonation of Q 2− B . Binding of HCO − 3 (or CO 2− 3 ) to the nonheme Fe between the quinones Q A and Q B was recently confirmed by X-ray crystallography (3,13,14). Despite this functional role at the acceptor side, the very tight binding of HCO − 3 to this site makes it impossible for the activity of PSII to be affected by changing the C i level of the medium; instead inhibitors such as formate need to be added to induce the acceptor-side effect (15). Consequently, the watersplitting electron-donor side of PSII has also been studied intensively (for recent reviews, see refs. 11 and 12). Although a tight binding of C i near the Mn 4 CaO 5 cluster is excluded on the basis of X-ray crystallography (3, 14), FTIR spectroscopy (16), and mass spectrometry (17, 18), the possibility that a weakly bound HCO − 3 affects the activity of PSII at the donor side remains a viable option (reviewed i...