Effects of Photosystem II Herbicides on the Photosynthetic Membranes of the Cyanobacterium Aphanocapsa 6308

The effects of the photosystem II herbicides diuron (3-(3,4-dichlorophenyl)-1,1-dimethylurea) and atrazine (2-chloro-4-ethylamino-6-isopropylamino-s-triazine) on the photosynthetic membranes of a cyanobacterium, Aphanocapsa 6308, were compared to the effects on a higher plant, Spinacia oleracea. The inhibition of photosystem II electron transport by these herbicides was investigated by measuring the photoreduction of the dye 2,6-dichlorophenol-indophenol spectrophotometrically using isolated membranes. The concentration of herbicide that caused 50% inhibition of electron transport (I₅₀ value) in Aphanocapsa membranes for diuron was 6.8 × 10⁻⁹ molar and the I₅₀ value for atrazine was 8.8 × 10⁻⁸ molar. ¹⁴C-labeled diuron and atrazine were used to investigate herbicide binding with calculated binding constants (K) being 8.2 × 10⁻⁸ molar for atrazine and 1.7 × 10⁻⁷ molar for diuron. Competitive binding studies carried out on Aphanocapsa membranes using radiolabeled [¹⁴C]atrazine and unlabeled diuron revealed that diuron competed with atrazine for the herbicide-binding site. Experiments involving the photoaffinity label [¹⁴C]azidoatrazine (2-azido-4-ethylamino-6-isopropylamino-2-triazine) and autoradiography of polyacrylamide gels indicated that the herbicide atrazine binds to a 32-kilodalton protein in Aphanocapsa 6308 cell extracts.     

Cooperation of Photosynthetic Reaction Center of Photosystem II under Weak Light as Shown by Light Intensity-dependence of the Half-effective Dose of Atrazine

The binding constant (K) and number of binding sites (N) of atrazine to isolated photosystem (PS) II membranes were measured with an apparent correlation between N and the activity of oxygen evolution. Upon the addition of an electron acceptor, N became equal to the total number of the population of PS II reaction centers irrespective of having oxygen-evolving activity, about 4 mmol per mole of chlorophyll, with a concomitant decline of K from 1.32 (±0.34) × 10⁷ M^–1 to 4.09 (±0.40) × 10⁶ M^–1 . NH₂OH and NaCl treatments, which inactivate oxygen evolution, affected neither the binding to PS II membranes of the extrinsic 33-kDa protein or of atrazine. The atrazine binding sites that are latent in CaCl₂-treated PS II membranes was partially restored by the reconstitution of the membranes with isolated extrinsic 33-kDa protein. An oxidizing system involving the 33-kDa protein may provide a suitable structure of PS II reaction center complex for atrazine binding. The level of inhibition of oxygen-evolving activity by atrazine under the saturating intensity of light parallels the fraction of the photosystem (PS) II reaction center with the quinone-binding site blocked by atrazine. In contrast, under a rate-limiting intensity of light, percents of remaining oxygen-evolving activity after the addition of atrazine correlated with the 1.33th power of the fraction of atrazine-free binding sites. Inhibition of PS II complexes more than one that bound with atrazine suggests a cooperation between PS II complexes to evolve oxygen under weak light intensity.     

Inhibition of HCO(3) Binding to Photosystem II by Atrazine at a Low-Affinity Herbicide Binding Site

In maize chloroplasts, the ratio of HCO₃⁻ (anion) binding sites to high-affinity atrazine binding sites is unity. In the dark, atrazine noncompetitively inhibits the binding of half of the HCO₃⁻ to the photosystem II (PSII) complexes. The inhibition of binding saturates at 5 micromolar atrazine, little inhibition is seen at 0.5 micromolar atrazine, although the high-affinity herbicide binding sites are nearly filled at this concentration. This means that HCO₃⁻ and atrazine interact noncompetitively at a specific low-affinity herbicide binding site that exists on a portion of the PSII complexes. Light abolishes the inhibitory effects of atrazine on HCO₃⁻ binding. Based on the assumption that there is one high-affinity atrazine binding site per PSII complex, we conclude that there is also only one binding site for HCO₃⁻ with a dissociation constant near 80 micromolar. The location of the HCO₃⁻ binding site, and the low-affinity atrazine binding site, is not known.     

Synthetic quinones influencing herbicide binding and Photosystem II electron transport. The effects of triazine-resistance on quinone binding properties in thylakoid membranes

We have analyzed the binding of synthetic quinones and herbicides which inhibit electron transport at the acceptor side of Photosystem II (PS II) of the photosynthetic electron-transport chain in thylakoid membranes. These data show that quinones and PS II-directed herbicides compete for binding to a common binding environment within a PS II region which functions as the Q⁻ / PQ oxidoreductase. We observed that (1) synthetic quinones cause a parallel inhibition of electron transport and [¹⁴C]herbicide displacement, and (2) herbicide binding is affected both by the fully oxidized and fully reduced form of a quinone. Quinone function and inhibitor binding were also investigated in thylakoids isolated from triazine-resistant weed biotypes. We conclude the following. (1) The affinity of the secondary accepting quinone, B, is decreased in resistant thylakoids. (2) The observation that the equilibrium concentration of reduced Q after transferring one electron to the acceptor side of PS II is increased in resistant as compared to susceptible chloroplasts may be explained both by a decrease in the affinity of PQ for the herbicide / quinone binding environment, and by a decrease of the midpont redox potential of the B / B⁻ couple. (3) The binding environment regulating quinone and herbicide affinity may be divided roughly into two domains; we suggest that the domain regulating quinone head-group binding is little changed in resistant membranes, whereas the domain-regulating quinone side-group binding (and atrazine) is altered. This results in increased inhibitory activity of tetrachloro-p-benzoquinone and phenolic herbicides, which are hypothesized to utilize the quinone head-group domain. The two domains appear to be spatially overlapping because efficient atrazine displacement by tetrachloro-p-benzoquinone is observed.     

Interactions of herbicides and azidoquinones at a Photosystem II binding site in the thylakoid membrane

6-Azido-5-decyl-2,3-dimethoxy-p-benzoquinone (6-azido-Q₀C₁₀) was found to replace the native plastoquinone at B (the second stable electron acceptor to Photosystem II (PS II)). The 6-azido-Q₁₀C₁₀ would accept electrons from the primary electron-accepting quinone, Q, thus allowing electron transport through PS II to the plastoquinone pool in thylakoids. The synthetic azidoquinone also competes with the PS II herbicides ioxynil and atrazine for binding. This observation strongly favors the hypothesis that PS II herbicides block electron transport by replacing the native quinone which acts as the second electron carrier on the reducing side of PS II (termed B). Covalent linkage of 6-azido-Q₀C₁₀ to its binding environment by ultraviolet irradiation greatly reduces herbicide-binding affinity but does not lead to a loss in herbicide-binding sites. We take this as evidence that covalent attachment of 6-azido-Q₀C₁₀ allows some freedom of quinone head-group movement such that the herbicides can enter the binding site. This indicates that the protein determinants which regulate quinone and herbicide binding are very closely related, but not identical. A compound somewhat related to 6-azido-Q₀C₁₀ is 2-azido-3-methoxy-5-geranyl-6-methyl-p-benzoquinone (2-azido-Q₂). This compound was found to be an ineffective competitor with respect to herbicide binding. Thus, interactions with protein-binding determinants are highly dependent on the molecular structure of quinones. The 2-azido-Q₂ was an inhibitor of electron flow in the intersystem portion of the chain.     

Photosystem II Core Phosphorylation Heterogeneity, Differential Herbicide Binding, and Regulation of Electron Transfer in Photosystem II Preparations from Spinach

The effect of photosystem II core phosphorylation on the secondary quinone acceptor of photosystem II (Q_B) domain environment was analyzed by comparative herbicide-binding studies with photosystem II preparations from spinach (Spinacia oleracea L.). It was found that phosphorylation reduces the binding affinity for most photosynthetic herbicides. The binding of synthetic quinones and of the electron acceptor 2,6-dichlorophenolindophenol is also reduced by photosystem II phosphorylation. Four photosystem II core populations isolated from membranes showed different extents of phosphorylation as well as different degrees of affinity for photosynthetic herbicides. These findings support the idea that heterogeneity of photosystem II observed in vivo could be, in part, due to phosphorylation.     

The 16 and 23 kDa extrinsic polypeptides and the associated Ca2+ and Cl- modify atrazine interaction with the photosystem II core complex

The oxygen evolving complex of photosystem II (PS II) contains three extrinsic polypeptides of approximate molecular weights 16, 23 and 33 kDa. These polypeptides are associated with the roles of Cl^-, Ca²⁺ and Mn²⁺ in oxygen evolution. We have shown that selective removal of 16 and 23 kDa polypeptides from the above complex by NaCl washing of PS II enriched membrane fragments renders the PS II core complex more susceptible to the herbicide atrazine. On the other hand, when both native and depleted preparations were resupplied with exogenous Ca²⁺ and Cl^-, we obtained a reduction of atrazine inhibition which was much stronger in the depleted preparations than in the native ones. It is concluded that removal of 16 and 23 kDa polypeptides in general, and disorganization of associated Ca²⁺ and Cl^- in particular, enhances atrazine penetration to its sites of action in the vicinity of the PS II complex. The above could be interpreted if we assume a reduced plastoquinone affinity at the Q_B (secondary plastoquinone electron acceptor) pocket of D1 polypeptide following transmembranous modifications caused by the depletion of these polypeptides.Abbreviations CCCP carbonylcyanide-m-chlorophenylhydrazone - Chl chlorophyll - DCIP 2,6-dichlorophenolindophenol - MES 2-(N-morpholino)ethanesulfonic acid - PMSF phenylmethylsul-phonyfluoride - PS II photosystem II - PAGE polyacrilamide gel electrophoresis     

Identification of tenuazonic acid as a novel type of natural photosystem II inhibitor binding in QB-site of Chlamydomonas reinhardtii

Tenuazonic acid (TeA) is a natural phytotoxin produced by Alternaria alternata, the causal agent of brown leaf spot disease of Eupatorium adenophorum. Results from chlorophyll fluorescence revealed TeA can block electron flow from Q_A to Q_B at photosystem II acceptor side. Based on studies with D1-mutants of Chlamydomonas reinhardtii, the No. 256 amino acid plays a key role in TeA binding to the Q_B-niche. The results of competitive replacement with [¹⁴C]atrazine combined with JIP-test and D1-mutant showed that TeA should be considered as a new type of photosystem II inhibitor because it has a different binding behavior within Q_B-niche from other known photosystem II inhibitors. Bioassay of TeA and its analogues indicated 3-acyl-5-alkyltetramic and even tetramic acid compounds may represent a new structural framework for photosynthetic inhibitors.     

Action of tenuazonic acid,a natural phytotoxin,on photosystem II of spinach

Tenuazonic acid (TeA) is a putative phytotoxin obtained from Alternaria alternata, the organism that can cause brown leaf spot disease of Crofton weed (Eupatorium adenophorum). It is demonstrated here that the tenuazonic acid inhibits the activity of photosystem II (PSII); the I₅₀-value is 48 μg mL^?1. Evidences from chlorophyll fluorescence show that tenuazonic acid interrupts electron transport between Q_A and Q_B on the acceptor side of PSII. It does not have an effect on the antenna pigments, the oxygen-evolving complex (OEC) at the donor side of PSII. On the basis of the fluorescence induction kinetics and competition experiments with [¹⁴C]atrazine, it is shown that tenuazonic acid does not share the same binding environment with atrazine despite their common action target: the Q_B-site. It is concluded that tenuazonic acid is a member of a novel class of PSII inhibitors.     

Effects of hydroxylamine and silicomolybdate on the decay in delayed light emission in the 6–100 μs range after a single 10 ns flash in pea thylakoids

Measurements are reported on μs delayed light emission, following a single 10 ns excitation flash, in Alaska pea thylakoids treated with hydroxylamine (NH₂OH) or with silicomolybdate.

1. In thylakoids treated with 2 mM NH₂OH in the light, or in the dark, the quantum yield of delayed light emission is considerably enhanced. A 10 μs lifetime component of delayed light emission is not significantly changed, whereas a 50–70 μs lifetime component is increased. MnCl₂ and diphenylcarbazide are unable to reverse the above effects of NH₂OH treatment. Thus Mn²⁺ and diphenylcarbazide must not donate electrons directly to reaction center II but on the oxygen-evolution side of the NH₂OH block.
2. When the closed form of photosystem II reaction centers (P₆₈₀Q^-), where P₆₈₀ is the reaction center chlorophyll and Q is a ‘stable’ electron acceptor, is generated by preillumination of NH₂OH-treated thylakoids with diuron present, the μs delayed light emission is inhibited, but a low level residual delayed light emission remains. Possible origins of this emission are discussed. It is believed that the best explanation for residual DLE is the existence of another acceptor besides Q that partakes in charge separation and rapid dissipative recombination when the reaction center is in the P₆₈₀Q^- state.
3. The quantum yield of delayed light emission from ‘closed’ reaction centers (P₆₈₀ ⁺Q^-) that have all charge stabilization reactions (i.e., flow of electrons to P₆₈₀ ⁺ and out of Q^-) blocked by NH₂OH treatment and addition of diuron is 1.1×10^-3 for components measured in a range from 6 to 400 μs and extrapolated to zero time.
4. The addition of silicomolybdate, which accepts electron from Q^-, causes delayed light emission in the μs range to be greatly inhibited.

     

Modification of Herbicide Binding to Photosystem II in Two Biotypes of Senecio vulgaris L

The present study compares the binding and inhibitory activity of two photosystem II inhibitors: 3-(3,4-dichlorophenyl)-1,1-dimethylurea (diuron [DCMU]) and 2-chloro-4-(ethylamine)-6-(isopropyl amine)-S-triazene (atrazine). Chloroplasts isolated from naturally occurring triazine-susceptible and triazine-resistant biotypes of common groundsel (Senecio vulgaris L.) showed the following characteristics. (a) Diuron strongly inhibited photosynthetic electron transport from H₂O to 2,6-dichlorophenolindophenol in both biotypes. Strong inhibition by atrazine was observed only with the susceptible chloroplasts. (b) Hill plots of electron transport inhibition data indicate a noncooperative binding of one inhibitor molecule at the site of action for both diuron and atrazine. (c) Susceptible chloroplasts show a strong diuron and atrazine binding (¹⁴C-radiolabel assays) with binding constants (K) of 1.4 × 10⁻⁸ molar and 4 × 10⁻⁸ molar, respectively. In the resistant chloroplasts the diuron binding was slightly decreased (K = 5 × 10⁻⁸ molar), whereas no specific atrazine binding was detected. (d) In susceptible chloroplasts, competitive binding between radioactively labeled diuron and non-labeled atrazine was observed. This competition was absent in the resistant chloroplasts.     

Cytochrome c reduction by semiquinone radicals can be indirectly inhibited by superoxide dismutase

The inhibition by superoxide dismutase of cytochrome c reduction by a range of semiquinone radicals has been studied. The semiquinones were produced from the parent quinones by reduction with xanthine and xanthine oxidase. Most of the quinones studied were favored over O₂ as the enzyme substrate, and in air as well as N₂, semiquinone radicals rather than superoxide were produced and they caused the cytochrome c reduction. With all but one of the quinones (benzoquinone), cytochrome c reduction in air was inhibited by superoxide dismutase, but the amount of enzyme required for inhibition was up to 100 times greater than that required to inhibit reduction by superoxide. It was highest for the quinones with the highest redox potential. These results demonstrate how superoxide dismutase can inhibit cytochrome c reduction by species other than superoxide. They can be explained by the dismutase displacing the equilibrium: semiquinone + O₂ ? quinone + O₂^? to the right, thereby allowing the forward reaction to out-compete other reactions of the semiquinone. The implication from these findings that superoxide dismutase-inhibitable reduction of cytochrome c may not be a specific test for superoxide production is discussed.     

Electron transfer between exogenous electron donors and reaction center of photosystem 2

Transfer of electrons between artificial electron donors diphenylcarbazide (DPC) and hydroxylamine (NH2OH) and reaction center of manganese-depleted photosystem 2 (PS2) complexes was studied using the direct electrometrical method. For the first time it was shown that reduction of redox-active amino acid tyrosine Y _z ^· by DPC is coupled with generation of transmembrane electric potential difference (δΨ). The amplitude of this phase comprised ～17% of that of the δΨ phase due to electron transfer between Y_Z and the primary quinone acceptor Q_A. This phase is associated with vectorial intraprotein electron transfer between the DPC binding site on the protein-water interface and the tyrosine Y _z ^· . The slowing of ΔΨ decay in the presence of NH₂OH indicates effective electron transfer between the artificial electron donor and reaction center of PS2. It is suggested that NH2OH is able to diffuse through channels with diameter of 2.0–3.0 Å visible in PS2 structure and leading from the protein-water interface to the Mn₄Ca cluster binding site with the concomitant electron donation to Y _z ^· . Because the dielectrically-weighted distance between the NH₂OH binding site and Y _z ^· is not determined, the transfer of electrons from NH₂OH to Y _z ^· could be either electrically silent or contribute negligibly to the observed electrogenicity in comparison with hydrophobic donors.     

Characterization of a Purified Photosystem II-Phycobilisome Particle Preparation from Porphyridium cruentum

Detergent preparations isolated from thylakoids of the red alga Porphyridium cruentum, in a sucrose, phosphate, citrate, magnesium chloride medium consist of phycobilisomes and possess high rates of photosystem II activity. Characterization of these particles shows that the O₂-evolving activity is stable for several hours and the pH optimum is about 6.5 to 7.2. Response of the system to light, electron donors and acceptors, and inhibitors verify that the observed activity, measured both as O₂ evolution and 2,6-dichlorophenol-indophenol reduction, is due to photosystem II. Furthermore, photosystem II is functionally coupled to the phycobilisome in this preparation since green light, absorbed by phycobilisomes of P. cruentum, is effective in promoting both O₂ evolution and 2,6-dichlorophenol-indophenol reduction. Photosystem II activity declines when light with wavelengths shorter than 665 nm is removed. Both 3-(3,4-dichlorophenyl)-1,1-dimethylurea and atrazine inhibit photosystem II activity in this preparation, indicating that the herbicide binding site is a component of the photosystem II-phycobilisome particle.     

Effect of inhibitors,redox state and isoprenoid chain length on the affinity of ubiquinone for the secondary acceptor binding site in the reaction centers of photosynthetic bacteria

Quinone and inhibitor binding to Rhodopseudomonas sphaeroides (R-26 and GA) reaction centers were studied using spectroscopic methods and by direct adsorption of reaction centers onto anion exchange filters in the presence of ¹⁴C-labelled quinone or inhibitor. These measurements show that as secondary acceptor, Q_B, ubiquinone (UQ) is tightly bound in the semiquinone form and loosely bound in the quinone and quinol forms. The quinol is probably more loosely bound than the quinone. o-Phenanthroline and terbutryn, a triazine inhibitor, compete with UQ and with each other for binding to the reaction center. Inhibition by o-phenanthroline of electron transfer from the primary to the secondary quinone acceptor (Q_A to Q_B) occurs via displacement of UQ from the Q_B binding site. Displacement of UQ by terbutryn is apparently accessory to the inhibition of electron transfer. Terbutryn binding is lowered by reduction of Q_B to Q^?_B but is practically unaffected by reduction of Q_A to Q^?_A in the absence of Q_B. UQ-9 and UQ-10 have a 5- to 6-fold higher binding affinity to the Q_B site than does UQ-1, indicating that the long isoprenoid chain facilitates the binding to the Q_B site.     

Dark Ammonium Assimilation Reduces the Plastoquinone Pool of Photosystem II in the Green Alga Selenastrum minutum

The impact of dark NH₄⁺ and NO₃⁻ assimilation on photosynthetic light harvesting capability of the green alga Selenastrum minutum was monitored by chlorophyll a fluorescence analysis. When cells assimilated NH₄⁺, they exhibited a large decline in the variable fluorescence/maximum fluorescence ratio, the fluorescence yield of photosystem II relative to that of photosystem I at 77 kelvin, and O₂ evolution rate. NH₄⁺ assimilation therefore poised the cells in a less efficient state for photosystem II. The analysis of complementary area of fluorescence induction curve and the pattern of fluorescence decay upon microsecond saturating flash, indicators of redox state of plastoquinone (PQ) pool and dark reoxidation of primary quinone electron acceptor (Q_A), respectively, revealed that the PQ pool became reduced during dark NH₄⁺ assimilation. NH₄⁺ assimilation also caused an increase in the NADPH/NADP⁺ ratio due to the NH₄⁺ induced increase in respiratory carbon oxidation. The change in cellular reductant is suggested to be responsible for the reduction of the PQ pool and provide a mechanism by which the metabolic demands of NH₄⁺ assimilation may alter the efficiency of photosynthetic light harvesting. NO₃⁻ assimilation did not cause a reduction in PQ and did not affect the efficiency of light harvesting. These results illustrate the role of cellular metabolism in the modulating photosynthetic processes.     

Light-induced oxidation of the acceptor-side Fe(II) of Photosystem II by exogenous quinones acting through the QB binding site. II. Blockage by inhibitors and their effects on the Fe(III) EPR spectra

Four representative inhibitors of Photosystem II (PS II) Q⁻_A to Q_B electron transfer were shown to bind, at high concentrations, to PS II reaction centers having the acceptor-side non-heme iron in the Fe(III) state. Three of the inhibitors studied, DCMU, o-phenanthroline and dinoseb, modified the EPR spectrum of the Fe(III) relative to that obtained by ferricyanide oxidation in the absence of inhibitor. o-Phenanthroline gave particularly axial symmetry, while DCMU and dinoseb gave more rhombic configurations. The herbicide inhibitor, atrazine and its analogue, terbutryn, had no effect. The dissociation constants for inhibitor binding to reaction centers in the Fe(III) state were measured directly and also estimated from shifts in the midpoint potential of the Fe(III)/Fe(II) couple and were shown to increase by factors of approx. 100, approx. 10 and 10–15 for DCMU (pH 7.5), atrazine (pH 7.0) and o-phenanthroline (pH 7.0), respectively, upon oxidation of the iron. Atrazine and o-phenanthroline, which induce the smallest changes in the midpoint potential of the Fe(III)/Fe(II) couple, were shown to inhibit light-induced oxidation of the Fe(II) by phenyl-p-BQ, described in the preceding paper (Petrouleas, V. and Diner, B.A. (1987) Biochim. Biophys. Acta 893, 126–137). The extent of inhibition was much greater than would be predicted from a simple shift in the midpoint potential for Fe(III)/Fe(II) and we conclude that phenyl-p-BQ and the other quinones, which show light-induced oxidation, act through the Q_B binding site. It is also argued that reduction and oxidation of the iron by ferro- and ferricyanide, respectively, occur through this site. The effects of these inhibitors and of various quinones on the Fe(III) environment are discussed with reference to the known contact points between the protein and o-phenanthroline and terbutryn in the Q_B binding pocket of Rhodopseudomonas viridis reaction centers (Michel, H., Epp, O. and Deisenhofer, J. (1986) EMBO J. 5, 2445–2451). The Fe(III) EPR spectrum is thus a new and sensitive probe of the contact points at which molecules bind to the Q_B binding site.     

Characterization of the Reversible Inactivation of Ankistrodesmus braunii Nitrate Reductase by Hydroxylamine

The photoreversible nature of the regulation of nitrate reductase is one of the most interesting features of this enzyme. As well as other chemicals, NH₂OH reversibly inactivates the reduced form of nitrate reductase from Ankistrodesmus braunii. From the partial activities of the enzyme, only terminal nitrate reductase is affected by NH₂OH. To demonstrate that the terminal activity was readily inactivted by NH₂OH, the necessary reductants of the terminal part of the enzyme had to be cleared of dithionite since this compound reacts chemically with NH₂OH. Photoreduced flavins and electrochemically reduced methyl viologen sustain very effective inactivation of terminal nitrate reductase activity, even if the enzyme was previously deprived of its NADH-dehydrogenase activity. The early inhibition of nitrate reductase by NH₂OH appears to be competitive versus NO₃⁻. Since NO₃⁻, as well as cyanate, carbamyl phosphate and azide (competitive inhibitors of nitrate reductase versus NO₃⁻), protect the enzyme from NH₂OH inactivation, it is suggested that NH₂OH binds to the nitrate active site. The NH₂OH-inactivated enzyme was photoreactivated in the presence of flavins, although slower than when the enzyme was previously inactivated with CN⁻. NH₂OH and NADH concentrations required for full inactivation of nitrate reductase appear to be low enough to potentially consider this inactivation process of physiological significance.     

Photoreductant-induced oxidation of Fe2+ in the electron-acceptor complex of Photosystem II

The ferrous ion associated with the electron acceptors in Photosystem II can be oxidized by the unstable semiquinone form of certain high-potential quinones (phenyl-p-benzoquinone, dimethylbenzoquinone and benzoquinone) which are used as electron acceptors. In a flash sequence, alternating oxidation of the iron by the photoreduced semiquinone on odd-numbered flashes is followed by photoreduction of the iron on even-numbered flashes. These reactions are detected by monitoring EPR signals arising from Fe³⁺. The oxidation of the iron can also occur in the frozen state (−30°C) indicating that the high-potential quinone can occupy the Q_B site. The reaction also takes place when the exogenous quinone is added in the dark to samples in which Q_B is already in the semiquinone form. The inhibitors of electron transfer between Q_A⁻ and Q_B, DCMU and sodium formate, block the photoreductant-induced iron oxidation. It is suggested that the iron oxidation takes place through the Q_B site. This unexpected photochemistry occurs under experimental conditions routinely used in studies of Photosystem II. Some previously reported phenomena can be reinterpreted on the basis of these new data.