Marina A. Kozuleva and Boris N. Ivanov* Photosynthetic Electron Transport lab., Institute of Basic Biological Problems, Pushchino, 142290, Russia *Corrresponding author: E-mail, [email protected]; Fax, +7-496-7330532. (Received November 29, 2015; Accepted February 10, 2016) The review is dedicated to ascertainment of the roles of the electron transfer cofactors of the pigment–protein complex of PSI, ferredoxin (Fd) and ferredoxin-NADP reductase in oxygen reduction in the photosynthetic electron transport chain (PETC) in the light. The data regarding oxygen reduction in other segments of the PETC are briefly analyzed, and it is concluded that their participation in the overall process in the PETC under unstressful conditions should be insignificant. Data concerning the contribution of Fd to the oxygen reduction in the PETC are examined. A set of collateral evidence as well as results of direct measurements of the involvement of Fd in this process in the presence of isolated thylakoids led to the inference that this contribution in vivo is negligible. The increase in oxygen reduction rate in the isolated thylakoids in the presence of either Fd or Fd plus NADP+ under increasing light intensity was attributed to the increase in oxygen reduction executed by the membrane-bound oxygen reductants. Data are presented which imply that a main reductant of the O2 molecule in the terminal reducing segment of the PETC is the electron transfer cofactor of PSI, phylloquinone. The physiological significance of characteristic properties of oxygen reductants in this segment of the PETC is discussed. Keywords: Chloroplast Electron transport Ferredoxin Oxygen reduction Photosystem I Phylloquinone. Abbreviations: A0, primary electron acceptor in PSI; A1, secondary electron acceptor in PSI, phylloquinone; DMF, dimethylformamide; Em, midpoint redox potential; FA and FB, terminal electron acceptors in PSI, FeS clusters; Fd, ferredoxin; FNR, ferredoxin-NADP+ reductase; FX, secondary electron acceptor in PSI, FeS cluster; PETC, photosynthetic electron transport chain; PQ, plastoquinone; PQ and PQH , plastosemiquinone; PQH2, plastohydroquinone, plastoquinol; PhQ, phylloquinone; PhQ , phyllosemiquinone; QA and QB, secondary electron acceptors in PSII; ROS, reactive oxygen species; SOD, superoxide dismutase. Introduction The elaboration of the problem of oxygen reduction in chloroplasts began in 1951 when Alan Mehler observed the appearance of hydrogen peroxide (H2O2) under illumination of isolated chloroplast fragments (Mehler 1951). The term ‘Mehler reaction’ is now used to designate the process of direct oxygen reduction by components of the photosynthetic electron transport chain (PETC). Kozi Asada was one of the first scientists who showed that the superoxide anion radical, O2 , is the primary product of O2 reduction in the PETC (Asada and Kiso 1973, Asada et al. 1974). In Asada’s studies, the characteristics of the Mehler reaction such as Km(O2) and the second-order rate constant (Asada and Nakano 1978, Takahashi and Asada 1982) were first presented, convincing evidence for involvement of PSI cofactors in the process of oxygen reduction (Takahashi and Asada 1988) was obtained and the role of superoxide dismutase (SOD) located near the acceptor side of PSI in a fast conversion of O2 produced there into H2O2 (Ogawa et al. 1995) was stressed. The superoxide anion radical and H2O2 are reactive oxygen species (ROS) capable of negatively affecting the photosynthetic reactions in chloroplasts, and therefore the concentrations of these species are under control there. The above studies and the discovery of thylakoid-bound ascorbate peroxidase in chloroplasts (Miyake and Asada 1992) led to the concept of the ‘water–water cycle’ (Asada 1999, Asada 2000), the term originating from the comprehension that electrons for both oxygen reduction and scavenging of ROS in chloroplasts are derived from water, and the final product of the reactions is water. The physiological functions of the water–water cycle besides ROS scavenging that provides protection from photooxidative damage (Rizhsky et al. 2003) are defense against photoinhibition (Ort and Baker 2002) and participation in ATP production (formerly termed pseudocyclic phosphorylation), additional to that coupled with electron transport to NADP+ (Makino et al. 2002). Data on the magnitude of the Mehler reaction and its contribution to total linear electron transport are presented in numerous research papers, which are analyzed in several reviews (Badger 1985, Robinson 1988, Badger et al. 2000, Ivanov et al. 2012, Ivanov et al. 2014), to which we refer readers. Briefly, the Mehler reaction can account for from 5% to 50–70% of total electron transport in different plant species under various conditions. It may be concluded that the electron outflow from the PETC components to oxygen is conditioned by the structure of the PETC as well as by environmental conditions, and the genotype defines both this structure and its variability under short and prolonged changes of environmental Plant Cell Physiol. 57(7): 1397–1404 (2016) doi:10.1093/pcp/pcw035, Advance Access publication on 24 March 2016, available online at www.pcp.oxfordjournals.org ! The Author 2016. Published by Oxford University Press on behalf of Japanese Society of Plant Physiologists. All rights reserved. For permissions, please email: [email protected] Special Focus Issue – Mini Review The Mechanisms of Oxygen Reduction in the Terminal Reducing Segment of the Chloroplast Photosynthetic Electron Transport Chain M. A. Kozuleva and B. N. Ivanov | Mechanisms of oxygen reduction in chloroplasts conditions such as illumination, temperature, gas composition of the atmosphere, mineral nutrients, the presence of pollutants, and so forth (Ivanov et al. 2014). The Mehler reaction is the limiting crucial point of the water–water cycle (Asada 2000); however, its mechanism, i.e. from which components of the PETC the electrons are principally transferred to O2 molecules, is still under debate. In this review, we will consider in particular the contribution of various components of the terminal reducing segment of the PETC to O2 reduction. Conditions for O2 Reduction in Different Media, and Possible Sites of This Reaction in the PETC The first step of oxygen reduction in the PETC is the transfer of one electron to the O2 molecule, resulting in the generation of the superoxide anion radical, O2 . The midpoint redox potential (Em) of the O2/O2 pair in aqueous media is 160 mV at the normal partial pressure of O2 in ambient air (Asada and Takahashi 1987) while, in the lipid bilayer of the membrane, the Em (O2/O2 ) is close to that in dimethylformamide (DMF; 550 to 600 mV vs. normal hydrogen electrode) (Afanas’ev 1989). The thermodynamic basis is relevant for consideration of sites of reduction of O2 molecules in the PETC because its components are situated in the aqueous media of the lumen and stroma, at membrane boundaries and within the interior of hydrophobic membranes. The components of the PETC, which may be considered as O2 reductants, should possess negative redox potentials thermodynamically sufficient to reduce O2 molecules in the corresponding medium. The possibility of O2 generation by intramembranous components of the PETC was first proposed in the work of Takahashi and Asada (1988), based on the data which showed the delayed appearance of O2 outside thylakoid membranes in response to a 10 ms flash. Recently, using reagents of different lipophilicity, cyclic hydroxylamines producing EPR (electron parmagnetic resonance)-detectable nitroxide radicals after oxidation by O2 , the generation of O2 outside as well as within thylakoid membranes has been directly shown (Kozuleva et al. 2011, Kozuleva et al. 2015). This implied an involvement of several PETC components in the Mehler reaction. Several segments of the PETC are considered as sites of O2 reduction. The data implying the possibility of this process at the acceptor side of PSII were comprehensively reviewed by Pospı́sil (2012). The redox potential of pheophytin, 610 mV, shows that this PSII cofactor could be a reductant of O2 in hydrophobic environments; however, the fast transfer of electrons from reduced pheophytin (200–500 ps) can prevent such a reaction. The redox potential of QA/QA was recently found to be 162 mV (Shibamoto et al. 2010), and this is the most negative value for QA presented in the literature. The Em of QB/ QB was stated to be 45 mV (Crofts et al. 1984). Both these values are not sufficiently negative for plastosemiquinone (PQ ) at these sites to reduce O2 efficiently. Yadav et al. (2014) suggested a role in O2 reduction of PQ , which 1398 might be formed in the recently revealed plastoquinone (PQ)-binding QC site in PSII (Kruk and Strzalka 2001, Hasegawa and Noguchi 2014) after one-electron oxidation of plastoquinol (PQH2) by Cyt b559. It should be stressed, however, that the experimental data demonstrating oxygen reduction in PSII were obtained with PSII-enriched fragments of thylakoid membranes with disturbed native membrane structure and, possibly, with increased water content. In such fragments, the presence of the photochemical generator producing the reduced forms of cofactors with negative redox potentials would inevitably lead to reduction of O2 as the sole available acceptor. So, we must agree with Asada’s statement (Asada 1994) that oxygen reduction at the acceptor side of PSII in intact thylakoids barely occurs. Oxygen reduction in the PQ pool of undamaged thylakoids, in which the oxidation of PQH2 by the Cyt b6f complex was inhibited by the dinitrophenylether of 2-iodo-4-nitrothymol (DNP-INT), was shown (Khorobrykh and Ivanov 2002). An analysis of data obtained in that and subsequent studies (Khorobrykh et al. 2004, Mubarakshina et al. 2006) implied that this reduction is executed by free PQ of the pool (Em = 170 mV) at the membrane–water interface (Mubarakshina and Ivanov 2010). The concentration of free PQ in the membrane as determined by the comproportionation reaction of PQ with PQH2 is low; however, a very high second-order rate constant of the reaction PQ with O2 (108 M 1 s 1) ensured that the calculated oxygen reduction rates in the PQ pool were commensurable with those observed in isolated thylakoids in the absence of the inhibitor (Khorobrykh and Ivanov 2002). It was shown that semiquinone produced via oxidation of quinol at the donor side of the Cyt bc1 complex can be oxidized by O2, generating O2 (Muller et al. 2002). Baniulis et al. (2013) found that the rate of O2 production in the purified Cyt b6f complex was significantly higher than that in the isolated yeast bc1 complex, and they presumed that there was a higher residence time of PQ /PQH2 in the niche near the Rieske protein iron–sulfur cluster in the former. The rate of O2 generation by PQ at that niche would depend on the competition between electron transfer to oxygen and the oxidized low-potential heme of Cyt b6; the latter process is highly favored under conditions of normal PETC operation in vivo. Forquer et al. (2006) proposed that semiquinone would leave the donor niche of the b6f complex in order to react with oxygen. In this case, however, this PQ is incorporated into the PQ pool and can dismutate with another PQ . It is difficult to estimate to what extent oxygen reduction by free PQ of this pool contributes to the total oxygen reduction in vivo during operation of the intact PETC. It could be suggested that stressful conditions can promote the above-mentioned exit of PQ produced at the donor side of the Cyt b6/f complex into the PQ pool, increasing oxygen reduction in this PETC segment. Convincing evidence in favor of PSI as the major site of oxygen reduction in chloroplasts was already obtained at the beginning of elaboration of this problem. In mutants with either a deficiency or absence of PSI, there was negligible electron leakage from the PETC to oxygen (Fork and Heber 1968, Radmer and Ollinger 1980). Discussion of other similar studies conducted Plant Cell Physiol. 57(7): 1397–1404 (2016) doi:10.1093/pcp/pcw035 with undamaged leaves may be found in the reviews by Badger (1985) and Robinson (1988). The common view now is that oxygen reduction in the PETC occurs mainly, if not exclusively, at its terminal reducing segment comprising the PSI complex, ferredoxin (Fd) and ferredoxin-NADP-reductase (FNR). Is it Possible That FNR is Involved in the Reduction of Oxygen In Vivo? In chloroplasts, FNR mediates electron flow from reduced Fd to NADP+. The reduction of NADP+ requires two electrons, while Fd is a one-electron carrier. Thus, FNR provides sequential binding of two molecules of reduced Fd, which donate electrons to the FNR prosthetic group, FAD. In the semiquinone form, FAD in FNR is a good reductant of O2 molecules, with the second-order rate constant of the reaction close to 108 M–1s–1 (Massey 1994). The question of the involvement of FNR in oxygen reduction in chloroplasts in vivo has been repeatedly raised in the literature (Robinson 1988). Isolated FNR added to a thylakoid suspension in either the presence or the absence of Fd increased the rate of oxygen uptake in the light (Goetze and Carpentier 1994). Both the photochemical quenching of Chl fluorescence and the rate of O2 generation were increased as a result of FNR addition to a thylakoid suspension in the absence of Fd (Miyake et al. 1998). In that work, the same effects were observed in response to addition of isolated monodehydroascorbate reductase (MDAR), also an FAD-containing enzyme. The authors assumed that MDAR can play a significant role in oxygen reduction in vivo. The experimental technique in the above studies implies that FB, the terminal cofactor of PSI, can be the immediate electron donor to FNR, providing the oneelectron reduction of FAD to the semiquinone form. However, the reduction of FNR by FB in vivo seems unlikely since FB is located on the PsaC subunit of PSI, which, together with PsaE and PsaD proteins, forms a docking site that was evolutionarily optimized for efficient binding and redox transformation of Fd. Also, in many species, isoforms of FNR are firmly attached to thylakoid membranes, and their withdrawal to the stroma is under physiological control (Hanke and Mulo 2013). This hampers the immediate interaction of FNR with PSI. Another question is whether the membrane-bound FNR can be an effective electron donor to O2 molecules. It is believed that during the catalytic cycle of NADP+ reduction by FNR, NADP+ binding to FNR precedes the binding of reduced Fd (Batie and Kamin 1984). In the absence of NADP+, the electron transfer from reduced Fd to FNR is very slow, while pre-binding of NADP+ greatly accelerates the rate of electron transfer (k = 40–80 s 1 vs. 445 s 1; see Carrillo and Ceccarelli 2003). Moreover, NADP+ is the top-priority electron acceptor from FNR. Thus, oxygen reduction by FNR concurrently with NADP+ reduction can barely proceed. However, under conditions causing deficiency of oxidized pyridine dinucleotide in chloroplasts, the electron transfer from Fd to FNR and then to O2 cannot be excluded. The Role of Ferredoxin in Oxygen Reduction A detailed analysis of available literature data showed that the rate of oxygen uptake in isolated thylakoids with stromal proteins removed is smaller than the rate of the process observed in leaves (Asada 2000). This and some other facts led investigators to propose an involvement of stromal components in oxygen reduction, first of all of Fd. Fd, an electron carrier from PSI to FNR in linear electron flow, is a small, 12 kDa, watersoluble protein, containing an iron–sulfur cluster. In higher plants, the cluster type is [2Fe–2S]. Fd possesses Em equal to 420 mV (Tagawa and Arnon 1968), which is considerably lower than Em (O2/O2 ) in water solutions ( 160 mV). The reduced Fd was shown to be oxidized by oxygen with formation of O2 (Misra and Fridovich 1971). Nevertheless, Fd was found to be a weak oxygen reductant. The rate constant of the reaction of O2 with reduced Fd was found to be as low as 103 M 1 s 1 (Hosein and Palmer 1983, Golbeck and Radmer 1984, Kozuleva et al. 2007), while O2 reduction, e.g. by semiquinones possessing Em (Q/Q ) close to Em (Fd/Fd ), has a second-order rate constant of approximately 109 M 1 s 1 (Wardman 1990). In the work of Asada et al. (1974), the rate of O2 generation, measured in thylakoid suspension as the rate of Cyt c reduction inhibited by SOD, was found to be almost unaffected by Fd addition to thylakoids. The authors concluded that components of PSI rather than Fd are involved in oxygen reduction, and the contribution of Fd to this process is negligible. However, to date, Fd is sometimes considered as the main oxygen reducing agent in chloroplasts in vivo. Indeed, addition of purified Fd to a thylakoid suspension stimulated oxygen reduction when oxygen was the only final acceptor of electrons from PETC components (Allen 1975, Ivanov et al. 1980, Furbank and Badger 1983). The effect was explained to be the result of Fd acting as a mediator between PSI and O2 molecules. In these studies, the rate of oxygen reduction increased with increasing Fd concentration. To achieve rates of oxygen reduction comparable with the maximum rates of electron transport through the PETC, the Fd/Chl ratio in the suspension of isolated thylakoids should be close to 10 mol/mol (Ivanov et al. 1980, Golbeck and Radmer 1984), i.e. approximately three orders of magnitude higher than this ratio in chloroplasts in vivo. The above high Fd concentrations in the thylakoid suspension were obviously necessary to reach a steady concentration of reduced Fd in the light sufficient to provide the transfer of all electrons supplied by the PETC to oxygen. The need for that concentration can be seen by comparing the rate constant of the reaction of reduced Fd with O2 molecules with the rate constant of Fd reduction in the PETC, 106–107 M–1 s–1 (Golbeck and Radmer 1984). It is important that in order to achieve the maximal rates of NADP+ reduction, which are close to the total capacity of PETC, in experiments with isolated thylakoids the Fd/Chl ratio has to be 0.5–1.0 mol/mol (Allen 1975, Red’ko at al. 1982, Furbank and Badger 1983), indicating additionally that Fd reduction by PSI is not a rate-limiting process in oxygen reduction. The above data argued that the transfer of electrons from the PETC through Fd to O2 molecules in thylakoids is an inefficient process. 1399 M. A. Kozuleva and B. N. Ivanov | Mechanisms of oxygen reduction in chloroplasts In the studies of Kozuleva et al. (2007) and Kozuleva and Ivanov (2010), the rates of oxygen reduction by reduced Fd and by the membrane-bound PETC components were experimentally separated for the first time. It was directly shown that, in the absence and in the presence of NADP+, the electrons for oxygen reduction were supplied by both Fd and the membranebound components of the PETC. The relationship of these electron fluxes depended on the Fd concentration and the light intensity. In the presence of only Fd, the fraction of oxygen reduction mediated by Fd varied from 20% to 70%, depending on the Fd concentration. At low Fd concentrations, the stimulation of oxygen reduction by Fd was negligible and this fraction was low (Kozuleva et al. 2007). With increasing total Fd concentration, the steady-state level of the reduced Fd in the light increased, leading to an increase in electron transport from Fd to oxygen as well as its contribution to the overall oxygen reduction (Kozuleva and Ivanov 2010). Gradually increasing the light intensity resulted in the continuing increase in the total rate of oxygen reduction, while the Fd-dependent rate of oxygen reduction exhibited saturation at moderate light intensities. This showed that when transfer of electrons from the reduced Fd to oxygen became limited, the increase in the total rate of oxygen reduction was determined by electron flow to oxygen from the membrane-bound components. The most important question is the contribution of Fd to oxygen reduction occurring simultaneously with NADP+ reduction. The simultaneous occurrence of these processes was discovered by Allen (1975), and then was repeatedly confirmed (Ivanov et al. 1980, Robinson and Gibbs 1982, Furbank and Badger 1983). Addition of NADP+ to a thylakoid suspension containing Fd increased the entire photosynthetic electron transport, i.e. to both NADP+ and O2, first of all as the result of a high rate of NADP+ reduction. The considerable rate of oxygen reduction found under conditions optimal for NADP+ reduction was initially ascribed to the involvement of Fd. However, under such conditions, the concentration of reduced Fd is rather low (Hosler and Yocum 1985, Kozuleva et al. 2007). The Fd contribution to oxygen reduction at Fd concentrations optimal for NADP+ reduction was found to be practically negligible, <7 %, and oxygen reduction is mainly performed by the membrane-bound components of the PETC (Kozuleva and Ivanov 2010). An increase in the light intensity in the presence of NADP+ led to a noticeable increase in the rate of oxygen reduction (Robinson and Gibbs 1982, Furbank and Badger 1983, Kozuleva and Ivanov 2010). The rate of Fd-dependent oxygen reduction was found to be saturated at very low light intensities and remained negligible up to high light intensities (Kozuleva and Ivanov 2010). This revealed that the increase in electron flow to oxygen with increasing light intensity occurred at the expense of the increased oxygen reduction by the membranebound components of the PETC. Thus, direct measurements together with the set of indirect evidence discussed above unequivocally prove that the transfer of electrons from reduced Fd is an unlikely pathway of oxygen reduction in vivo. 1400 Oxygen Reduction in the PSI Pigment–Protein Complex PSI, plastocyanin:ferredoxin oxidoreductase, contains the electron transport chain consisting of electron transfer cofactors P700, A0, A1, FX, FA, FB (Fig. 1). Cofactors between P700 and FX are arranged in two branches, named the A- and B-branches, located on the PsaA/PsaB protein heterodimer along a pseudo-symmetry axis. P700 is a dimer of Chl a molecules. A0 in both branches are also Chl a molecules, which were proposed to be a dimer (Ptushenko et al. 2008) or a monomer (Müller et al. 2010). The lifetime of A0 is around 30 ps, and this makes the electron transfer to oxygen quite improbable despite low redox potential, 1,250 mV (here and below, the Em values are taken from Ptushenko et al. 2008). Phylloquinones (PhQs) occupy two quinone-binding sites A1. These two PhQs differ in Em values, 671 and 844 mV at the A1A and A1B sites, respectively, and their reduced forms differ in their lifetimes: electron transfer from PhQA to FX possessing an Em = 585 mV occurs within approximately 250 ns, while that from PhQB occurs in approximately 20 ns (Santabarbara et al. 2015). FX, FA and FB are [4Fe–4S] clusters. FX is co-ordinated by four cysteine residues, two each from PsaA and PsaB, and thus, besides its function as an electron transfer cofactor, plays a crucial role in PsaA/PsaB heterodimer assembly (Jagannathan et al. 2012). FX transfers electrons to the terminal membrane-bound electron transfer cofactors at the acceptor side of PSI, FA and FB, for 50 ns (Semenov et al. 2006). FA and FB are situated at the PSI subunit PsaC, which protrudes into the stroma. Oxidation of the terminal cofactors by Fd occurs within 500 ns to 1 ms in a pre-formed complex of Fd with PSI and in up to 100 ms in the case of diffusion-limited electron transfer between Fd and PSI in solution (Setif 2006). The Em values of FA/ FA and FB/FB pairs are 479 and 539 mV, respectively (Ptushenko et al. 2008), and they are sufficient for reduction of O2 molecule in water. However, the values of the dielectric constant in the immediate vicinity of these centers are close to 5 (Semenov et al. 2003), which could disable efficient O2 reduction by these cofactors due to positive values of G0 for this reaction (one should take into account the Em value of O2/ O2 in DMF; see above). This estimation is confirmed by low rates of oxygen reduction by both thylakoid membranes (Asada et al. 1974, Khorobrykh et al. 2004) and isolated PSI complexes (Kozuleva et al. 2014), when electron transfer from the terminal PSI cofactors to O2 is the rate-limiting step of the whole electron transport. All other PSI electron transfer cofactors are located in the hydrophobic region of the PsaA/PsaB heterodimer with quite a low permittivity. PSI was proposed as the main site of oxygen reduction in numerous works. However, only a few attempts to establish which PSI cofactor directly reduces O2 molecules were made. Takahashi and Asada (1988) showed that superoxide-dependent protein iodination in isolated thylakoids during the first seconds of illumination occurred exclusively in the PSI proteins; FX was speculated to be the oxygen reductant. Involvement of PhQ in O2 reduction was proposed by Kruk et al. (2003), based on stimulation of oxygen uptake by PhQ addition to the thylakoid membranes Plant Cell Physiol. 57(7): 1397–1404 (2016) doi:10.1093/pcp/pcw035 Fig. 1 Schematic diagram of forward electron transfer in PSI with lifetimes and Em values of the cofactors. Em values of (O2/O2 ) in water and dimethylformamide are shown. Pc, plastocyanin; P700, a dimer of Chl a molecules, the primary electron donor; A0, the primary electron acceptor; PhQ, phylloquinone, a secondary electron acceptor; FX, 4Fe–4S cluster, a secondary electron acceptor; FA and FB, 4Fe–4S clusters, the terminal electron acceptors. containing no quinones after treatment with hexane. The dependence of the rate of oxygen reduction by membrane-bound components on the efficiency of electron withdrawal from PSI permitted Kozuleva et al. (2007) to consider both FX and PhQ as oxygen reductants. It should be noted that they both can reduce O2 in media with a low permittivity. The role of these membrane-bound components of PSI as the main O2 reductants was further explored in Kozuleva and Ivanov (2010). In that study, the unexpected dependence of the O2 reduction rate on the presence of NADP+ was observed in pea isolated thylakoids; addition of NADP+ at high light intensities did not decrease and even increased the oxygen reduction rate relative to the rate observed in the presence of only Fd. This result was ascribed to peculiarities of electron transfer reactions in PSI. Obviously, the reduction of O2 by PhQ and/or FX should increase with an increase in the quasi-steady-state concentration of these cofactors in the reduced state. This concentration depends on the relationship between electron inflow from the donor side of PSI, the electron outflow to downstream cofactors and the charge recombination of their reduced forms with P700+. The latter process is highly stimulated due to electrostatic repulsion when the terminal cofactors, FA/B, become reduced, e.g. the recombination time of P700+A1 is decreased by three orders of magnitude, from 250 ms to 250 ns (Polm and Brettel 1998). When electron withdrawal from FA/B is retarded, the higher stationary negative charge holds there, and the electrostatic effect on PhQ and FX does increase. At high light intensities, in the absence of NADP+, the retardation of electron withdrawal from FA/B could be a result of delay in supply of oxidized Fd due to a low rate of oxidation of reduced Fd by oxygen, while the presence of NADP+ could maintain the lower level of reduced Fd and consequently of FA/B . The average retention of the electrons at FA/B in the presence of only Fd was longer by an order of magnitude than with Fd + NADP+ (Kozuleva and Ivanov 2010), so the electrostatic repulsion in a larger population of PSI could be higher in the absence of NADP+. It is assumed that the sum of rates of forward electron transfer and the recombination from PhQ (or Fx ) in the presence of both Fd and NADP+ is less than in the presence of only Fd; and thus the higher quasi-steadystate concentration of PhQ (or Fx ) and hence the higher rate of O2 reduction by these species should be in the presence of Fd and NADP+. The described increase in oxygen reduction by isolated thylakoids owing to NADP+ addition (Kozuleva and Ivanov 2010) can explain the higher rate of oxygen reduction in intact chloroplasts as compared with ‘naked’ thylakoids, but whether it is inherent only for pea may be ascertained after conducting corresponding studies with other plants. Experiments designed to identify the O2 reductant in PSI were performed with PSI complexes isolated from cyanobacterium Synechocystis sp. PCC 6803 (Kozuleva et al. 2014). Mutants with completely blocked biosynthesis of PhQ are known for this organism (men mutants). These mutants are still able to grow photoautotrophically in low light. It was shown that, in the mutants, PQ occupies the A1 sites of PSI, performing electron transfer from A0 to FX. However, the Em value of PQ/PQ at the A1 sites is about 100 mV more positive than that of PhQ/PhQ (Semenov et al. 2000). This decreases the G0 value for O2 reduction at these sites. It was found that in PSI isolated from the mutant menB, the dependence of oxygen uptake reflecting O2 production on light intensity exhibited saturation behavior already at moderate intensities, while the uptake in PSI from the wild type continued to increase up to notably higher light intensities (Kozuleva et al. 1401 M. A. Kozuleva and B. N. Ivanov | Mechanisms of oxygen reduction in chloroplasts 2014). Oxygen reduction by intermediate electron transfer cofactors in PSI occurred concurrently with such a process at the terminal cofactors, FA/B, but the latter had the same rate in the mutant as in the wild type, since the rate of electron supply to FA/B was shown to be unaffected by the mutation (Kozuleva et al. 2014). Comparison of oxygen reduction in PSI complexes from the wild type and the mutant clearly showed that PhQ is involved in oxygen reduction in PSI, and that its contribution to this process increased with an increase in light intensity. It may be relevant that in the work (Takahashi and Asada 1982), a change in the affinity of oxygen for its reduction by the spinach thylakoids with the change in the actinic light intensity was observed. Data demonstrating that PhQ is a basic reductant of oxygen in the PETC are in good agreement with the evidence of O2 production within the thylakoid membrane (see above). They support the proposition that H2O2 is formed within the membrane in the reaction of PQH2 with intramembrane O2 (Mubarakshina et al. 2006, Mubarakshina and Ivanov 2010). Such a pathway of H2O2 formation, taking into account its signaling function, may be important to explain the repeatedly shown role of the PQ pool redox state as a trigger of acclimation reactions in leaves (Borisova-Mubarakshina et al. 2015). Conclusion Mother Nature arranged the terminal reducing segment of the PETC wisely, providing the presence there of the chain of low potential components performing NADP+ reduction with minimal leakage of electrons to oxygen. The presented data show that Fd cannot significantly contribute to oxygen reduction in vivo. The slow oxidation of reduced Fd by oxygen has evident physiological significance since the reduced Fd is the central chloroplast component donating electrons to numerous metabolic reactions. It is believed that [2Fe–2S] Fds with the clusters shielded by the protein are more tolerant to oxygen than typical bacterial [4Fe–4S] Fds, whose clusters are partially solvent exposed (Jagannathan and Golbeck 2009). Therefore, recruitment of [2Fe–2S] Fds as mobile electron transfer proteins in organisms with oxygenic photosynthesis was proposed to be an evolutionary adaptation for protection against interaction of PSI with oxygen (Jagannathan et al. 2012). In isolated thylakoids, in the absence of natural or artificial electron acceptors, the terminal cofactors of PETC, FA/B, transfer electrons to oxygen as the sole acceptor available. The FA and FB centers, according to their redox potentials and surroundings, do not efficiently reduce O2 molecules, and the rate of such a reduction is low. The low efficiency of oxidation of FA/B by oxygen also has physiological reasons since it enables FA/B to reduce Fd successfully. The evolution of PsaC carrying FA and FB clusters from the bacterial dicluster Fd was proposed to be initiated in order to protect FA and/or FX against oxidative damage by shielding these cofactors by protein (Jagannathan et al. 2012). The linkage of bacterial Fd to the ancestral reaction center also could be designed to prevent electron leakage from 1402 its cofactors to oxygen. Moreover, the switch of Em (FA/FA ) to more positive values providing uphill electron transfer from FA to FB and preferential (90%) residence of electrons on FA was proposed to be an evolutionary adaptation to minimize oxygen reduction by FB in the absence of oxidized Fd (Shinkarev et al. 2000). It was shown that with partial damage of the thylakoid membrane structure, the rate of oxygen reduction greatly increases (Asada and Nakano 1978, Takahashi and Asada 1982, Navari-Izzo et al. 1996). Under stressful conditions in vivo, some impairment of the membrane structure can occur, causing the leakage of electrons from PSI cofactors to oxygen with production of O2 and H2O2 in the stroma, where their increased amount can be the alarm signal. It is widely accepted that the appearance of oxygen in the atmosphere was accompanied by transformation of the type I homodimeric reaction center to a heterodimeric one (Jagannathan and Golbeck 2009, Rutherford et al. 2012). The most conspicuous asymmetry in the electron transfer organization in PSI is the difference in Em values of PhQ at the A1 sites and hence the rates of electron transfer from PhQ to FX in Aand B-branches. Under conditions of retarded electron transfer from the terminal PSI cofactors, the charge recombination occurs in this complex. This could lead to formation of the triplet P700, which in the reaction with O2 molecules in the ground state could produce 1O2, whose reactivity exceeds that of O2 and H2O2. Rutherford et al. (2012) proposed that the smaller energy gap between PhQA and FX than between PhQB and FX promotes charge recombination in the A-branch; and the charge recombination occurring in this branch with the more positive quinone leads to less probable formation of the triplet P700 than charge recombination in the B-branch. We propose that electron flow from PhQ to oxygen can help maintain the forward electron transfer in PSI, thus decreasing charge recombination and 1O2 production (Kozuleva et al. 2014). This is especially relevant under conditions when charge separation takes place in both branches, leading to formation of PhQ at both A1 sites (Santabarbara et al. 2015) and making two PhQ compete for one FX. In the case of retarded electron outflow from PSI, e.g. at high light intensities and saturated NADP+ reduction, oxygen reduction by PhQ may represent an essential mechanism of plants protection against photoinhibition. Funding This study was supported by the Russian Science Foundation [research project # 14-14-00535]. Acknowledgements The authors express their gratitude to Drs. V.V. Klimov and I.I. Proskuryakov for helpful discussion. Disclosures The authors have no conflicts of interest to declare. Plant Cell Physiol. 57(7): 1397–1404 (2016) doi:10.1093/pcp/pcw035 References Afanas’ev, I.B. (1989) Superoxide Ion: Chemistry and Biological Implications. CRC Press, Boca Raton, FL. Allen, J.F. (1975) Oxygen reduction and optimum production of ATP in photosynthesis. Nature 256: 599–600. Asada, K. (1994) Production and action of active oxygen species in photosynthesis tissues. In Causes of Photooxidative Stress and Amelioration of Defense systems in Plants. Edited by Foyer, C.H. and Mullineaux, P.M. pp. 77–104. CRC Press, Boca Raton, FL. Asada, K. (1999) The water–water cycle in chloroplasts: scavenging of active oxygens and dissipation of excess photons. Ann. Rev. Plant Physiol. Plant Mol. Biol. 50: 601–639. Asada, K. (2000) The water–water cycle as alternative photon and electron sinks. Philos. Trans. R. Soc. B: Biol. Sci. 355: 1419–1431. Asada, K. and Kiso, K. (1973). The photo-oxidation of epinephrine by spinach chloroplasts and its inhibition by superoxide dismutase: evidence for the formation of superoxide radicals in chloroplasts. Agric. Biol. Chem. 37: 453–454. Asada, K., Kiso, K. and Yoshikawa, K. (1974) Univalent reduction of molecular oxygen by spinach chloroplasts on illumination. J. Biol. Chem. 249: 2175–2181. Asada, K. and Nakano, Y. (1978) Affinity for oxygen in photoreduction of molecular oxygen and scavenging of hydrogen peroxide in spinach chloroplasts. Photochem. Photobiol. 28: 917–920. Asada, K. and Takahashi, M. (1987) Production and scavenging of active oxygen in photosynthesis. In Photoinhibition. Edited by Kyle, D.J., Osmond, C.B. and Arntzen, C.J. pp. 227–287. Elsevier, Amsterdam, The Netherlands. Badger, M.R. (1985) Photosynthetic oxygen exchange. Annu. Rev. Plant Physiol. 36: 27–53. Badger, M.R., von Caemmerer, S., Ruuska, S. and Nakano, H. (2000) Electron flow to oxygen in higher plants and algae: rates and control of direct photoreduction (Mehler reaction) and rubisco oxygenase. Philos. Trans. R. Soc. B: Biol. Sci. 355: 1433–1446. Baniulis, D., Hasan, S.S., Stofleth, J.T. and Cramer, W.A. (2013) Mechanism of enhanced superoxide production in the cytochrome b6f complex of oxygenic photosynthesis. Biochemistry 52: 8975–8983. Batie, C.J.and Kamin, H. (1984) Ferredoxin:NADP+ oxidoreductase. Equilibria in binary and ternary complexes with NADP+ and ferredoxin. J. Biol. Chem. 259: 8832–8839. Borisova-Mubarakshina, M.M., Ivanov, B.N., Vetoshkina, D.V., Lubimov, V.Y., Fedorchuk, T.P., Naydov, I.A. et al. (2015) Long-term acclimatory response to excess excitation energy: evidence for a role of hydrogen peroxide in the regulation of photosystem II antenna size. J. Exp. Bot. 66: 7151–7164. Carrillo, N. and Ceccarelli, E.A. (2003) Open questions in ferredoxinNADP+ reductase catalytic mechanism. Eur. J. Biochem. 270: 1900–1915. Crofts, A.R., Robinson, H.H. and Snozzi, M. (1984) Reactions of quinols at catalytic sites: a diffusion role in H-transfer. In Advances in Photosynthesis Research. Edited by Sybesma, C. pp. 1.461–1.468. M. Nijhoff/Dr W. Junk Publishers, The Hague. Fork, D.C. and Heber, U.W. (1968) Studies on electron-transport reactions of photosynthesis in plastome mutants of Oenothera. Plant Physiol. 43: 606–612. Forquer I., Covian R., Bowman M.K., Trumpower B.L. and Kramer D.M. (2006) Similar transition states mediate the Q-cycle and superoxide production by the cytochrome bc1 complex. J. Biol. Chem. 281: 38459–38465. Furbank, R. and Badger, M. (1983) Oxygen exchange associated with electron transport and photophosphorylation in spinach thylakoids. Biochim. Biophys. Acta 723: 400–409. Goetze, D.C. and Carpentier, R. (1994) Ferredoxin-NADP+ reductase is the site of oxygen reduction in pseudocyclic electron transport. Can. J. Bot. 72: 256–260. Golbeck, J. and Radmer, R. (1984) Is the rate of oxygen uptake by reduced ferredoxin sufficient to account for photosystem I-mediated O2 reduction? In Advances in Photosynthesis Research. Edited by Sybesma, C. pp. 1.4.561–1.4.564. M. Nijhoff/Dr W. Junk Publishers, The Hague. Hanke, G. and Mulo, P. (2013) Plant type ferredoxins and ferredoxin dependent metabolism. Plant Cell Environ. 36: 1071–1084. Hasegawa, K. and Noguchi, T. (2014) Molecular interaction of the quinone electron acceptor QA, QB and QC in photosystem II as studied by the fragment molecular orbital method. Photosynth. Res. 120: 113–123. Hosein, B. and Palmer G. (1983) The kinetics and mechanism of oxidation of reduced spinach ferredoxin by molecular oxygen and its reduced products. Biochim. Biophys. Acta 723: 383–390. Hosler, J. and Yocum C. (1985) Evidence for two cyclic photophosphorylation reactions concurrent with ferredoxin-catalyzed non-cyclic electron transport. Biochim. Biophys. Acta 808: 21–31. Ivanov, B.N., Khorobrykh, S.A., Kozuleva, M.A. and Borisova-Mubarakshina, M.M. (2014) The role of oxygen and its reactive forms in photosynthesis. In Contemporary Problems of Photosynthesis. Edited by Allakhverdiev, S.I., Rubin, A.B. and Shauvalov, V.A. pp. 407–460. Izhevsk Institute of Computer Science, Moscow–Izhevsk, Russia. Ivanov, B., Kozuleva, M. and Mubarakshina M. (2012) Oxygen metabolism in chloroplast. In Cell Metabolism—Cell Homeostasis and Stress Response. Edited by Bubulya, P. pp. 39–72. InTech (www.intechopen.com). Ivanov, B.N., Red’ko, T.P., Shmeleva, V.L. and Mukhin, E.N. (1980) Participation of ferredoxin in pseudocyclic electron transport in isolated pea chloroplasts. Biokhimiya (Moscow) 45: 1425–1432. English transl. (1981) Biochemistry 45: 1078–1084. Jagannathan, B. and Golbeck, J.H. (2009) Understanding of the binding interface between PsaC and the PsaA/PsaB heterodimer in photosystem I. Biochemistry 48: 5405–5416. Jagannathan, B., Shen, G. and Golbeck, J.H. (2012) The evolution of Type I reaction centers: the response to oxygenic photosynthesis. In Functional Genomics and Evolution of Photosynthetic Systems. Edited by Burnap, R.L. and Vermaas, W.F.J. pp. 285–316. Springer, Dordrecht, The Netherlands. Khorobrykh, S.A. and Ivanov, B.N. (2002) Oxygen reduction in a plastoquinone pool of isolated pea thylakoids. Photosynth. Res. 71: 209–219. Khorobrykh, S., Mubarakshina, M. and Ivanov, B. (2004) Photosystem I is not solely responsible for oxygen reduction in isolated thylakoids. Biochim. Biophys. Acta 1657: 164–167. Kozuleva, M.A. and Ivanov, B.N. (2010) Evaluation of the participation of ferredoxin in oxygen reduction in the photosynthetic electron transport chain of isolated pea thylakoids. Photosynth. Res. 105: 51–61. Kozuleva, M., Klenina, I., Mysin, I., Kirilyuk, I., Opanasenko, V., Proskuryakov, I. and Ivanov, B. (2015) Quantification of superoxide radical production in thylakoid membrane using cyclic hydroxylamine. Free Radic. Biol. Med. 89: 1014–1023. Kozuleva, M., Klenina, I., Proskuryakov, I., Kirilyuk, I. and Ivanov, B. (2011) Production of superoxide in chloroplast thylakoid membranes: ESR study with cyclic hydroxylamines of different lipophilicity. FEBS Lett. 585: 1067–1071. Kozuleva, M.A., Naidov, I.A., Mubarakshina, M.M. and Ivanov, B.N. (2007) Participation of ferredoxin in oxygen reduction by the photosynthetic electron transport chain. Biofizika 52: 650–655. English transl. (2007) Biophysics 52: 393–397. Kozuleva, M.A., Petrova, A.A., Mamedov, M.D., Semenov, A. Yu. and Ivanov, B.N. (2014) O2 reduction by photosystem I involves phylloquinone under steady-state illumination. FEBS Lett. 588: 4364–4368. Kruk, J., Jemiola-Rzeminska, M., Burda, K., Schmid, G. and Strzalka, K. (2003) Scavenging of superoxide generated in photosystem I by plastoquinol and other prenyllipids in thylakoid membranes. Biochemistry 42: 8501–8505. Kruk, J. and Strzalka, K. (2001) Redox changes of cytochrome b559 in the presence of plastoquinones. J. Biol. Chem. 276: 86–91. 1403 M. A. Kozuleva and B. N. Ivanov | Mechanisms of oxygen reduction in chloroplasts Makino, A., Miyake, C. and Yokota, A. (2002) Physiological functions of the water–water cycle (Mehler reaction) and the cyclic electron flow around PSI in rice leaves. Plant Cell Physiol. 43: 1017–1026. Massey V. (1994) Activation of molecular oxygen by flavins and flavoproteins. J.Biol. Chem. 269: 22459–22462. Mehler, A.H. (1951) Studies on reactivity of illuminated chloroplasts. Mechanism of the reduction of oxygen and other Hill reagents. Arch. Biochem. Biophys. 33: 65–77. Misra, H.P. and Fridovich, I. (1971) The generation of superoxide radical during the autoxidation of ferredoxins. J. Biol. Chem. 246: 6886–6890. Miyake C. and Asada K. (1992) Thylakoid-bound ascorbate peroxidase in spinach chloroplasts and photoreduction of its primary oxidation product monodehydroascorbate radicals in thylakoids. Plant Cell Physiol. 33: 541–553. Miyake, C., Schreiber, U., Hormann, H., Sano, S. and Asada, K. (1998) The FAD-enzyme monodehydroascorbate radical reductase mediates photoproduction of superoxide radicals in spinach thylakoid membranes. Plant Cell Physiol. 39: 821–829. Mubarakshina, M.M. and Ivanov, B.N. (2010) The production and scavenging of reactive oxygen species in the plastoquinone pool of chloroplast thylakoid membranes. Physiol. Plant. 140: 103–110. Mubarakshina, M., Khorobrykh S. and Ivanov B. (2006) Oxygen reduction in chloroplast thylakoids results in production of hydrogen peroxide inside the membrane. Biochim. Biophys. Acta 1757: 1496–1503. Müller, M.G., Slavov, C., Luthra, R., Redding, K.E. and Holzwarth, A.R. (2010) Independent initiation of primary electron transfer in the two branches of the photosystem I reaction center. Proc. Natl. Acad. Sci. USA 107: 4123–4128. Muller, F.L., Crofts, A.R. and Kramer, D.M. (2002) Multiple Q-cycle bypass reactions at the Qo site of the cytochrome bc1 complex. Biochemistry 41: 7866–7874. Navari-Izzo, F., Quartacci, M.F. and Sgherri, C.M. (1996) Superoxide generation in relation to dehydration and rehydration. Biochem. Soc. Trans. 24: 447–451. Ogawa, K., Kanematsu, S., Takabe, K. and Asada, K. (1995) Attachment of CuZn-superoxide dismutase to thylakoid membranes at the site of superoxide generation (PSI) in spinach chloroplasts: detection by immuno-gold labelling after rapid freezing and substitution method. Plant Cell Physiol. 36: 565–573. Ort, D.R. and Baker, N.R. (2002) A photoprotective role for O2 as an alternative electron sink in photosynthesis? Curr. Opin. Plant Biol. 5: 193–198. Polm, M. and Brettel, K. (1998) Secondary pair charge recombination in Photosystem I under strongly reducing conditions: temperature dependence and suggested mechanism. Biophys. J. 74: 3173–3181. Pospı́šil, P. (2012) Molecular mechanisms of production and scavenging of reactive oxygen species by photosystem II. Biochim. Biophys. Acta 1817: 218–231. Ptushenko, V.V., Cherepanov, D.A., Krishtalik, L.I. and Semenov, A.Y. (2008) Semi-continuum electrostatic calculations of redox potentials in photosystem I. Photosynth. Res. 97: 55–74. Radmer, R. and Ollinger, O. (1980) Light-driven uptake of oxygen, carbon dioxide, and bicarbonate by the green alga Scenedesmus. Plant Physiol. 65: 723–729. Red’ko, T.P., Shmeleva, V.L., Ivanov, B.N. and Mukhin, E.N. (1982) Relationship between noncyclic and pseudocyclic electron transports in pea chloroplasts as depending on ferredoxin concentration. 1404 Biokhimiya (Moscow) 47: 1695–1699. English transl (1983) Biochemistry 47: 1435–1439. Rizhsky, L., Liang, H. and Mittler, R. (2003) The water–water cycle is essential for chloroplast protection in the absence of stress. J. Biol. Chem. 278: 38921–38925. Robinson, J.M. (1988) Does O2 photoreduction occur within chloroplasts in vivo? Physiol. Plant. 72: 666–680. Robinson, J.M. and Gibbs, M. (1982) Hydrogen peroxide synthesis in isolated spinach chloroplast lamellae. Plant Physiol. 70: 1249–1254. Rutherford, A.W., Osyczka, A. and Rappaport, F. (2012) Back-reactions, short-circuits, leaks and other energy wasteful reactions in biological electron transfer: redox tuning to survive life in O2. FEBS Lett. 586: 603– 616. Santabarbara, S., Bullock, B., Rappaport, F. and Redding, K.E. (2015) Controlling electron transfer between the two cofactor chains of photosystem I by the redox state of one of their components. Biophys. J. 108: 1537–1547. Semenov, A.Y., Vassiliev, I.R., van der Est, A., Mamedov, M.D., Zybailov, B., Shen, G. and Golbeck, J.H. (2000) Recruitment of a Foreign Quinone into the A1 Site of Photosystem I. Altered kinetics of electron transfer in phylloquinone biosynthetic pathway mutants studied by time-resolved optical, EPR, and electrometric techniques. J. Biol. Chem. 275: 23429– 23438. Semenov, A.Y., Mamedov, M.D. and Chamorovsky, S.K. (2003) Photoelectric studies of the transmembrane charge transfer reactions in photosystem I pigment–protein complexes. FEBS Lett. 553: 223–228. Semenov, A.Y., Mamedov, M.D. and Chamorovsky, S.K. (2006) Electrogenic reactions associated with electron transfer in photosystem I. In Photosystem I. The Light-Driven Plastocyanin:Ferredoxin Oxidoreductase. Edited by Golbeck, J.H. pp. 319–338. Springer, Dordrecht, The Netherlands. Sétif, P. (2006) Electron transfer from the bound iron–sulfur clusters to ferredoxin/flavodoxin: kinetic and structural properties of ferredoxin/ flavodoxin reduction by photosystem I. In Photosystem I. The LightDriven Plastocyanin:Ferredoxin Oxidoreductase. Edited by Golbeck, J.H. pp. 439–454. Springer, Doirdrecht, The Netherlands. Shibamoto, T., Kato, Y., Nagao, R., Yamazaki, T., Tomo, T. and Watanabe, T. (2010) Species-dependence of the redox potential of the primary quinone electron acceptor QA in photosystem II verified by spectroelectrochemistry. FEBS Lett. 584: 1526–1530. Shinkarev, V.P., Vassiliev, I.R. and Golbeck, J.H. (2000) A kinetic assessment of the sequence of electron transfer from FX to FA and further to FB in photosystem I: the value of the equilibrium constant between FX and FA. Biophys. J. 78: 363–372. Tagawa, K. and Arnon D.I. (1968) Oxidation-reduction potentials and stoichiometry of electron transfer in ferredoxins. Biochim. Biophys. Acta 153: 602–613. Takahashi, M. and Asada K. (1982) Dependence of oxygen affinity for Mehler reaction on photochemical activity of chloroplast thylakoids. Plant Cell Physiol. 23: 1457–1461. Takahashi, M. and Asada, K. (1988) Superoxide production in aprotic interior of chloroplast thylakoids. Arch. Biochem. Biophys. 267: 714–722. Wardman, P. (1990) Bioreactive activation of quinones: redox properties and thiol reactivity. Free Radic. Res. Commun. 8: 219–229. Yadav, D.K., Prasad, A., Kruk, J. and Pospısil, P. (2014) Evidence for the involvement of loosely bound plastosemiquinones in superoxide anion radical production in Photosystem II. PLoS One 9: e115466.
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