Abstract
In this study, we probe the effects of bicarbonate (hydrogencarbonate), BC, removal from photosystem II in spinach thylakoids by measuring flash-induced oxygen evolution patterns (FIOPs) with a Joliot-type electrode. For this we compared three commonly employed methods: (1) washing in BC-free medium, (2) formate addition, and (3) acetate addition. Washing of the samples with buffers depleted of BC and CO2 by bubbling with argon (Method 1) under our conditions leads to an increase in the double hit parameter of the first flash (β1), while the miss parameter and the overall activity remain unchanged. In contrast, addition of 40–50 mM formate or acetate results in a significant increase in the miss parameter and to an ∼50% (formate) and ∼10% (acetate) inhibition of the overall oxygen evolution activity, but not to an increased β1 parameter. All described effects could be reversed by washing with formate/acetate free buffer and/or addition of 2–10 mM bicarbonate. The redox potential of the water-oxidizing complex (WOC) in samples treated by Method 1 is compared to samples containing 2 mM bicarbonate in two ways: (1) The lifetimes of the S0, S2, and S3 states were measured, and no differences were found between the two sample types. (2) The S1, S0, S−1, and S−2 states were probed by incubation with small concentrations of NH2OH. These experiments displayed a subtle, yet highly reproducible difference in the apparent Si/S−i state distribution which is shown to arise from the interaction of BC with PSII in the already reduced states of the WOC. These data are discussed in detail by also taking into account the CO2 concentrations present in the buffers after argon bubbling and during the measurements. These values were measured by membrane-inlet mass spectrometry (MIMS).
Similar content being viewed by others
Avoid common mistakes on your manuscript.
Introduction
Oxygenic photosynthesis in cyanobacteria, algae, and higher plants created the aerobic atmosphere on earth. These organisms use electrons from water to reduce CO2 to carbohydrates, liberating molecular oxygen (O2) as a side product. Water oxidation is catalyzed by the water-oxidizing complex (WOC) within photosystem II (PSII) and is energetically driven by light-induced charge separations within the reaction center of PSII (Renger and Holzwarth 2005). The heart of the WOC is formed by a metal-oxygen cluster that comprises four manganese ions, one calcium ion, and at least five bridging oxygen’s. The structure of this Mn4O x Ca cluster was recently characterized by polarized EXAFS spectroscopy on PSII single crystals (Yano et al. 2006). In addition, Cl− and HCO −3 have been suggested to be of functional relevance for water splitting (recently reviewed in (Wydrzynski and Satoh 2005)).
Excitations of dark-adapted PSII complexes by short (‘single turn-over’) light flashes result in flash-induced oxygen evolution patterns (FIOPs) with a periodicity of four (Joliot et al. 1969). Kok and coworkers concluded that the WOC cycles during water oxidation through five different redox states, named S i states (i = 0–4), where i is the number of oxidizing equivalents stored within the WOC (Kok et al. 1970). In well dark-adapted samples practically all PSII centers are in the S1 state. The S0 state is slowly (tenth of minutes) oxidized to the S1 state by the oxidized form of tyrosine D, Y oxD , of polypeptide D2 (Messinger and Renger 1993; Styring and Rutherford 1987; Vermaas et al. 1984). The S2 and S3 states are meta-stable and are reduced within seconds to minutes into the S1 state (Isgandarova et al. 2003; Messinger and Renger 1994; Messinger et al. 1993; Shevela et al. 2006a; Vass et al. 1990a; Vass and Styring 1991) by the reduced tyrosine YD (fast phase) and/or by slower donors that include the reduced acceptor side quinone Q −/2−B (slow phase) (Diner 1977; Nugent et al. 1987; Rutherford et al. 1982; Rutherford and Inoue 1984; Vermaas et al. 1984; Vermaas et al. 1988). The S4 state is thought to spontaneously decay under the release of O2 into the S0 state (for review see (Hillier and Messinger 2005)).
The water oxidation cycle does not work ‘perfectly,’ and the damping of FIOPs is accounted for by ‘miss’ (α) and ‘double-hit’ (β) probabilities that are connected with each flash-induced reaction sequence (Forbush et al. 1971; Kok et al. 1970). For simplicity it is often assumed that these parameters are Si state and flash number independent. However, the value of α is expected to depend on the redox equilibria of the donor and acceptor sides of PSII (de Wijn and van Gorkom 2002; Renger and Hanssum 1988; Shinkarev and Wraight 1993; Shinkarev 1996). In case of the β probability, it was shown that it depends (i) on the rate of the Q −A reoxidation (Messinger et al. 1993) and (ii) on the flash profile (Hillier and Messinger 2005; Jursinic 1981).
The Mn oxidation states of the S1 state are Mn4(III,III,IV,IV) (Iuzzolino et al. 1998; Kulik et al. 2005; Messinger et al. 2001b; Yachandra et al. 1993). In agreement with these relatively high-oxidation states of the manganese ions it was shown that the WOC can also be poised in states more reduced than the S0 state (for review see (Debus 1992; Hillier and Messinger 2005). Such treatments usually involve the incubation of PSII samples with small, hydrophilic reductants such as NH2OH, NH2NH2 or NO· (Bouges 1971; Ioannidis et al. 1998; Messinger et al. 1991; Sarrou et al. 2003). The most reduced S −i state that is stable is the S-3 state (Messinger et al. 1997). Indications for the existence of short-lived S-4 and the S-5 states were presented (Messinger et al. 2001a; Messinger et al. 1997).
There are many experimental results that are consistent with the notion that bicarbonate (BC) is required by PSII for maximal activity; however, interpretation of this effect has a history full of controversies (for recent reviews see (Stemler 2002; van Rensen and Klimov 2005)). The problems are caused (i) by several different protocols for BC-depletion and (ii) by the absence (most of the studies) of monitoring of the residual inorganic carbon levels (CO2, HCO −3 (BC) and H2CO3). Typically three different methods were employed for BC-depletion: (1) Dilution of samples into buffers that were depleted of BC by bubbling with CO2-free air, N2 or argon (Klimov et al. 1995a; Klimov et al. 1995b). This method (Method 1) can be combined with brief boiling of the buffer (Govindjee et al. 1997). (2) Incubation of the samples at pH 5.0 which is well below the pK a = 6.3 of BC (Good et al. 1966), induces protonation of BC and subsequent dissociation of H2CO3 into CO2 and water, which facilitates BC removal (Method 2). (3) Addition of chemical analogs of BC, such as formate (Stemler and Radmer 1975) or acetate (Stemler et al. 1974) (see Scheme 1) is thought to replace BC from its binding site(s) in PSII (Method 3). In this study we carefully monitor the inorganic carbon levels in the buffers during sample incubation and under measurement conditions by membrane-inlet mass spectrometry (MIMS).
The first report on BC-effects on the electron flow in chloroplasts (Hill reaction) dates back to the year 1958 (Warburg and Krippahl 1958). In the early 1970s the stimulating effects of BC was thought to arise from interactions of BC with the WOC (Stemler et al. 1974; Stemler and Govindjee 1973) and even different models including BC as substrate for photosynthetic water oxidation were suggested (Metzner 1978; Warburg 1964). The latter suggestions were disproved by mass spectrometric experiments employing 18O-labled HCO −3 or H 182 O (Clausen et al. 2005; Hillier et al. 2006; Radmer and Ollinger 1980). In 1975 it was shown that BC-depletion affects the electron transfer kinetics on the acceptor side of PSII (Wydrzynski and Govindjee 1975). This interpretation became the dominating view (for review see (van Rensen 2002; van Rensen and Klimov 2005; van Rensen et al. 1999), and it is also supported by two recent PSII crystal structures that display BC as a ligand of the non-heme Fe between the two acceptor side quinones QA and QB (Ferreira et al. 2004; Loll et al. 2005).
Starting from 1995 the hypothesis for an additional role of BC at the donor side of PSII was revived by experiments showing that BC is required for both maximal activity and stability of the WOC (Allakhverdiev et al. 1997; Klimov et al. 1995a; Klimov et al. 1995b; Klimov et al. 1997). The stimulating effects of BC ions are especially pronounced during photoactivation (Baranov et al. 2000; Baranov et al. 2004). Electrochemical and EPR characterizations of BC complexes with MnII and MnIII ions show that these ions form electro neutral complexes, and that the dissociation constant (K d ) of the MnIII-BC complex is nearly 10 orders lower than the K d of the MnII–BC complex (Kozlov et al. 2004). It has been suggested that these properties of MnII-BC complexes may facilitate the photo-induced assembly of the inorganic core of the WOC (Dismukes et al. 2001; Kozlov et al. 2004). These results are consistent with several proposals (Klimov and Baranov 2001; van Rensen and Klimov 2005): (1) BC is bound to or is a structural part of the assembled Mn4O x Ca cluster, (2) BC remains bound in the vicinity of Mn4O x Ca cluster or (3) BC is required during photoactivation and then leaves the site.
If BC is a direct ligand to the Mn4O x Ca cluster it can be assumed that its removal will change the redox-potential of the WOC or may affect the accessibility of the WOC to exogenous reductants like NH2OH and NH2NH2. In this study we probe these ideas by a thorough analysis of FIOPs obtained at 2 mM BC and under BC-depleted conditions by studying (i) the life times of the S0, S2, and S3 states and (ii) the reduction rates of the WOC by hydroxylamine.
Materials and methods
Sample preparation
Thylakoid membranes were isolated from market spinach as described previously (Messinger and Renger 1993; Winget et al. 1965). After isolation the thylakoids were frozen in small aliquots in liquid N2 and then stored at −70°C until used. After prolonged storage (several months) thylakoids are enriched in the reduced form of YD (Messinger and Renger 1990; Vass et al. 1990b). Such samples will be referred to as ‘S1YD’-thylakoids. Before the measurements, the thylakoids were thawed in the dark on ice and diluted to [Chl] = 1 mg/mL with MCMM buffer (400 mM mannitol, 20 mM CaCl2, 10 mM MgCl2, and 50–100 mM MES/NaOH at pH 6.5). ‘S1Y oxD ’-thylakoids were obtained from S1YD-thylakoids by excitation with one saturating flash and subsequent 15 min dark-incubation on ice as described earlier (Messinger and Renger 1990).
Bicarbonate/CO2-depletion
BC depletion from thylakoids was carried out as described in (Klimov et al. 1995a; Klimov et al. 1995b) with some modifications. CO2/HCO −3 was removed from the MCMM medium by flushing with argon (BC(−) medium) for 40–60 min. Thylakoids were depleted of CO2/HCO −3 by 50–80-fold dilutions with the BC(−) medium and subsequent dark-incubations on ice for 2–10 h under argon atmosphere. Thereafter the thylakoids were collected by centrifugation and washed at least twice in the BC(−) medium (‘BC(−) thylakoids’).
Treatment of thylakoids with sodium formate
Formate treatment of the S1Y oxD -thylakoids was done according to the method described in (Stemler and Radmer 1975) with some modifications. Samples were treated in the MCMM buffer containing 50 mM NaHCO2 at 20°C and pH 5.0 for 15 min. Then the treated samples were diluted 50-fold in MCMM BC(−) medium (pH 6.4) containing 50 mM NaHCO2. Subsequently the thylakoids were collected by centrifugation, washed once in the same medium and finally resuspended to 1 mg Chl/ml. In reversibility experiments 10 mM NaHCO3 was added to the samples ∼1 min prior to the FIOP measurements, or the samples were washed in formate-free BC(−) buffer.
Treatment of thylakoids with sodium acetate
Acetate treatment of S1Y oxD -thylakoids was performed according to the method described in (Stemler et al. 1974) in MCMM buffer containing 40 mM CH3COONa (30 min at 20°C and pH 5.0 or pH 6.5). In cases, where acetate is removed prior to FIOP measurements, the treated samples were washed twice in a 50-fold excess of MCMM BC(−) medium (pH 6.5). Subsequently the samples were resuspended in BC(−) medium to 1 mg Chl/ml. In order to test the reversibility of the treatments 10 mM BC was added to the acetate-treated samples about ∼1 min before the start of the FIOP measurements.
Treatment of thylakoids with NH2OH
NH2OH-treatment of the samples was done according to the method described in (Messinger et al. 1991, 1997). S1Y oxD -BC(−) thylakoids were prepared as described above to give a final concentration of 2 mg Chl/ml. The reaction was then started by the addition of NH2OH solutions in BC(−) MCMM buffer or MCMM buffer containing 2 mM BC (BC(+) medium). The NH2OH solutions were prepared and adjusted to pH 6.5 shortly before the addition to PSII. The NH2OH incubation was performed in the dark on ice. After the indicated incubation times 10 μl aliquots were taken in very dim green light and rapidly transferred to the bare platinum cathode of the Joliot-type-electrode. In some cases NH2OH was removed from the samples prior to taking the FIOPs. This was done by washing the NH2OH treated sample in a 50-fold excess of MCMM medium (either BC(−) or BC(+)).
FIOP measurements
The FIOPs were measured with a home-built Joliot-type bare platinum electrode (Joliot 1972; Messinger 1993), that keeps the temperature of the electrode constant within ±0.3°C. The measurements were performed at an electrode temperature of 20°C. The samples were kept on the Pt-electrode for about 1 min prior to starting the measurements. The polarization voltage (−0.75 V) was switched on 30 s before excitation with a flash train (2 Hz) of short (∼5 μs half-width) saturating Xenon flashes (EG&G, model PS 302, light pack FY-604). The amplified amperometric signals were recorded with a personal computer. No exogenous electron acceptors were added. For BC-depleted samples only freshly prepared BC(−) buffer (MCMM, pH 6.5) was used as flow buffer, while for control measurements BC(+) MCMH medium was used that contained 2 mM NaHCO3. Since, it was impractical to operate the Joliot electrode inside a glove box, we flushed for BC(−) measurements the airspace above the flow buffer in the reservoir constantly with argon. Tubing between the reservoir and the electrode was kept to a minimum. Direct exposure of the sample to air was only possible during the ∼40 s transfer time, required for the application of the 10 μl aliquots onto the electrode surface and for electrode assembly. For some experiments this transfer was done under an open nitrogen ‘tent’ to further reduce this possible source of CO2 contamination. However, the obtained FIOPs were undistinguishable between the two procedures.
Si lifetime measurements
The S2 and S3 lifetimes were measured by illumination of dark-adapted S1YD-thylakoids with one (S2 formation) or two (S3 formation) preflash(es) and subsequent recording of the O2-yields induced by flash trains (20 flashes at 2 Hz) given at various dark-times (from 0.5 to 90 s) after the respective preflash(es). To observe the kinetics of S0 oxidation to S1 by Y oxD , ‘S1Y oxD ’-thylakoids were excited with three flashes (S0 formation) and after various dark-incubation times (from 0.5 to 60 min) FIOPs were recorded. The polarization voltage was switched on 30 s before the flash train.
FIOPs analysis
The first 16 flashes of each FIOP were analyzed using a spreadsheet program that is based on an extended Kok model which was previously described (Isgandarova et al. 2003; Shevela et al. 2006a). In addition to the normal Kok parameters, this program also includes (i) a high-double-hit probability in the 1st flash (β1), (ii) S−1, S−2 and S−3 states that can be found after reduction with exogenous electron donors (Messinger et al. 1997), and (iii) Si state-dependent miss parameters. This is summarized in Eq. 1:
where, γ i,n = 1−α i- −β n is the S i state and flash number dependent single-hit probability, n is the flash number, and d an activity parameter that compensates for changes in the number of active PSII centers during the flash train (Messinger et al. 1997). In cases where the possibility of a high-double hit in the first flash was analyzed β n equals β1 for the first flash (n = 1) and β n equals β for n > 1 (in addition we applied the restriction β1 ≥ β). The theoretical O2-yield of the nth flash \( (Y^{{fit}}_{n} )\) and the fit quality (fq) were calculated as described previously (Messinger et al. 1991).
For measuring the fast phases of S2 and S3 decay samples with a high content of reduced tyrosine D, YD, were used. The high-reduction level of about 80% was reached by storage of the thylakoids at −80°C for several months (Messinger and Renger 1990; Vass et al. 1990b). The S i state life time data were analyzed by taking into account the fast reduction of S2 and S3 by YD that can occur during the 500 ms dark-times between flashes of a flash train (Isgandarova et al. 2003). Biphasic decay is assumed for the least square analysis of the S2 and S3 state populations. In contrast, the dark-oxidation of S0 to S1 by Y oxD was modeled by a mono exponential decay (Isgandarova et al. 2003).
Membrane-inlet mass spectrometry (MIMS) measurements
The MIMS measurements were performed with an isotope ratio mass spectrometer (ThermoFinnigan DeltaPlus XP) that was connected via a cooling trap (dry ice ethanol) to a home built membrane-inlet cell similar to that described by Messinger and coworkers (Messinger et al. 1995). The volume of the cell is 150 μl and the sample was separated from the vacuum of the mass spectrometer by a silicon membrane (MEM-213) resting on a porous plastic support. For further details on MIMS see (Konermann et al. 2007).
Results
Effect of bicarbonate on the Kok parameters in S1Y oxD -thylakoids
In order to analyze the effects of bicarbonate (BC) on the parameters of the Kok cycle, FIOPs of dark-adapted S1Y oxD -thylakoids were measured after depletion of BC from the PSII sample (Fig. 1a). The BC-depletion of PSII was achieved by repeated washing of the thylakoids with pH 6.5 buffer, which had a reduced BC/CO2 content due to extensive bubbling with argon (‘BC(−) buffer’). Figure 1b displays a FIOP of thylakoids that were treated as above, but to which subsequently 2 mM NaHCO3 was added. For both samples typical period four oscillations with maxima of O2 evolution after the 3rd, 7th, and 11th flashes are observed. This indicates that the overall miss and double-hit parameters are unaffected by our BC depletion, BC(−), procedure. A close inspection of the data shows, however, that the O2-yield induced by the 2nd flash, Y2, is rather large in BC(−) samples (Fig. 1a). Y2 is reversed to normal control levels by addition of 2 mM BC (Fig. 1b). Since both samples were preflashed once prior to the measurement in order to oxidize YD, at least two mechanism may be responsible for the high O2-yield induced by the second flash in BC-depleted samples: (i) the S2 decay is significantly slower in BC(−) samples or (ii) in BC(−) samples the 1st flash is coupled with a high-double-hit probability, β1. High β1 values are known, for example, from ferricyanide treated PSII samples (Jursinic 1981) and high-double hits on every second flash were reported for measurements in the presence of phenyl-para-benzoquinone (PPBQ) (Zimmermann and Rutherford 1986). In both cases the non-heme iron (Fe2+) on the acceptor side of PSII is eventually oxidized by the artificial acceptor to Fe3+, which then allows a fast oxidation of Q −A within the duration of following xenon flash and thus opens PSII for a second turnover within the same flash. Since, the difference in the 2nd flash O2 yields persist even after extended dark-times (several hours) between pre-flash and recording of the FIOPs, explanation (i) appears rather unlikely (see also S2 lifetime measurements below). We, therefore, strongly favor option (ii). It is important to note, however, that our samples do not contain any exogenous electron acceptors.
These qualitative observations are confirmed by a detailed analysis of these FIOPs (see Table 1) employing the extended Kok model described in the experimental section. The fits in Table 1 show that inclusion of the β1 parameter (fit B) leads to a significant improvement of the fit quality for the FIOP obtained with the BC(−) sample; in contrast, the inclusion of this extra parameter does not lead to an improvement of the fit of the FIOP recorded after readdition of bicarbonate (BC(+) sample). We also tested several combinations of S i state-dependent miss parameters. This did not lead to any new insights, and therefore, only the equal miss approach is shown in Table 1.
Our data differ from previous reports (Jursinic and Stemler 1984; Stemler et al. 1974; Stemler and Lavergne 1997). In these earlier publications effects of BC depletion on the miss parameter, but not on β1 were observed (unless ferricyanide was added (Jursinic and Stemler 1984)). A detailed comparison of the BC depletion and measuring conditions shows that the most significant difference between the conditions appear to be the presence of either 100 mM formate (Stemler and Lavergne 1997) or 40 mM acetate (Stemler et al. 1974) during depletion at pH 5.0 and also during the FIOP measurements at pH 6.8. We, therefore, added 50 mM formate (Fig. 2) or 40 mM acetate (Fig. 3) to our buffer and pretreated the samples at pH 5.0 as described in the previous publications (Stemler et al. 1974; Stemler and Radmer 1975). Figures 2a and 3a show that under these conditions, indeed high-miss parameters are observed that could be reduced to almost normal values by addition of 10 mM NaHCO3 (Figs. 2b, 3b, and Table 2). Interestingly, in contrast to our BC depletion procedure neither the addition of formate nor that of acetate leads to an increased β1 parameter (Figs. 2a, 3a, and Table 2). While the increase in the miss parameter is similar for formate and acetate (Table 2), formate leads under our conditions to an inhibition of ∼50% of the PSII centers, while acetate leads only to a decrease of ∼10% (on the basis of the steady state O2 yields). Fits employing S i state-dependent misses gave qualitatively similar results and are, therefore, not presented. These results are in agreement with previous observations (Stemler et al. 1974; Stemler and Lavergne 1997). It should be remarked that we obtained an only slightly smaller increase of the miss parameter if the pH 5.0 treatment was omitted and formate or acetate were added directly to the sample at pH 6.5 (data not shown).
The above experiments demonstrate that the information gathered about the function of bicarbonate in PSII is critically dependent on the choice of the BC depletion procedure. To investigate this further, we washed formate or acetate treated thylakoids with BC(−) buffer (pH 6.5). This procedure removes these additives from the samples, while simultaneously minimizing the rebinding of BC to PSII. The FIOPs obtained under these conditions are shown in Figs. 2c and 3c, respectively. Interestingly, these FIOPs are almost identical to that in Fig. 1a, i.e., they show normal miss parameters and an increased oxygen yield in the second flash. Remarkably, also the formate induced block of PSII centers is fully removed during this washing step. This finding is in agreement with two previous studies (Feyziev et al. 2000; Wiessner et al. 1992). The high β1 value (Figs. 2c, 3c) can be reversed by addition of NaHCO3 (Figs. 2d, 3d).
S0, S2 and S3 lifetime measurements
For testing the effect of bicarbonate depletion on the redox potential of the Mn4O x Ca cluster we explored the effect of bicarbonate depletion on the rates of S2 and S3 state reduction by endogenous electron donors. The expectation is that removal of BC from a putative binding site at the Mn4O x Ca cluster should modify the redox potential of the cluster and thereby, alter the stability of the higher Si states. The S2 and S3 lifetimes were determined in the traditional way by giving one (S2 state) or two (S3 state) preflashes and varying the dark-time to the FIOP measurements. The obtained FIOPs were then deconvoluted into S i state populations taking the back reactions of YD with S2 and S3 into account (for details see (Isgandarova et al. 2003)). The obtained S2 and S3 populations are plotted for BC(+) (closed symbols) and BC(−) thylakoids (open symbols) as a function of dark-time in Fig. 4. Lines represent for both sample types biexponential fits. The two phases in the reduction of S2 and S3 originate from electron donation by YD (fast kinetics) and by the acceptor side of PSII (slow kinetics).
It is clear from Fig. 4 that our BC depletion (method 1) and measuring conditions (see below) do not affect the stability of the S2 and S3 states. Within an estimated fit error of about 10% the derived kinetics for the fast and slow decays of these S i states are found to be independent of the presence or absence of BC (Table 3). Despite the above-discussed significant differences in sample treatment, this result is in agreement with the earlier publication of (Stemler et al. 1974) where the slow S3 state decay was shown to be independent of the BC concentration in a medium containing acetate. It may be remarked, however, that the present data give more direct information, because (i) the complication with acetate is avoided and (ii) the possible mixing of donor and acceptor side effects of BC during the S2 and S3 state decay is avoided by studying the interaction of YD with the Mn4O x Ca cluster.
These lifetime measurements were completed by measuring the kinetics of S0 oxidation to S1 by Y oxD . In this case, three preflashes are used to excite S1Y oxD -thylakoids. Then again the dark-time is varied to the recording of the FIOPs. The results obtained for BC(+) (closed symbols) and BC(−) thylakoids (open symbols) are shown in Fig. 5. Within the fit error of 10% practically no differences exist between the two sample types (Table 3). Therefore, BC does not affect the redox potential of the S0 state under our conditions.
Reduction of the WOC by NH2OH
The BC was shown to be a cofactor during photoactivation of PSII and to form complexes with Mn2+ (Baranov et al. 2004; Dismukes et al. 2001; Kozlov et al. 2004). It is, therefore, possible that BC binds to the Mn4O x Ca cluster in the chemically reduced S −i states, because most of the S -i states contain at least one Mn2+ ion (except S−1, which may contain only Mn3+ ions). Similar to the S i state lifetime measurements above we assume that binding of BC to the Mn4O x Ca cluster in the S -i states would modify the redox potential of the reduced states and/or alter their accessibility for NH2OH, and thereby slow down a possible further reduction.
In a recent report BC was shown to ‘retard’ the shift to the S −i states during the incubation with small concentrations of the two-electron reductant NH2NH2 (Shevela et al. 2006b). In the present study, we employ the one-electron reductant NH2OH as a probe for the reactivity of the Mn4O x Ca cluster, because in this way also the S0 and S−2 states can be studied in more detail. In addition, for more precise Si state deconvolutions, no exogenous acceptors were used (K3[Fe(CN)6] was added in the previous study).
Figure 6 presents original (insets) and normalized FIOPs (symbols) that were obtained with spinach thylakoids after 1 min of dark incubation with the indicated concentrations of NH2OH in BC(−) medium (left) and BC(+) medium (right). The dotted lines show for comparison the respective FIOP of the S1Y oxD thylakoids prior to NH2OH addition. An inspection of the data shows that independent of the presence of BC a progressive shift of the 1st maximum of oxygen evolution toward higher-flash numbers is observed as a function NH2OH concentration. However, the extent of this shift is at all concentrations smaller in the presence of BC samples (right side) as compared to those obtained with BC(−) thylakoids (left side of Fig. 6). This finding is in agreement with a previous report (Shevela et al. 2006b), where a similar observation was made with NH2NH2 as reductant.
Figure 7 displays the calculated normalized S -i state populations as a function of NH2OH concentration in thylakoids after dark-incubation during 5 min in CO2/HCO −3 depleted medium without (a, left side) and after readdition of bicarbonate (b, right side). Again, an apparent retardation in the reduction of all S i states is observed in agreement with (Shevela et al. 2006b). It is important to note that the apparent S i /S −i state distributions after NH2OH incubation result from a complex sequence of reactions: (i) diffusion of NH2OH toward the WOC, (ii) reduction of the Mn4O x Ca cluster, and (iii) the efficiency of light-induced oxidations during the flash train. In addition, back reactions of the formed S −i states with Y oxD (Messinger and Renger 1993) or other electron acceptors need to be considered.
In order to address the question at which point of the above-described chain of events BC modifies the apparent S i /S −i state populations, we compare in Fig. 8 FIOPs that were obtained as follows: (1) BC(−)thylakoids were incubated for 10 min with 0.2 mM NH2OH and then washed and measured in BC(−) medium; (2) BC(+) thylakoids were incubated with NH2OH and then washed and measured in BC(+) medium, and (3) BC(−) thylakoids were incubated with NH2OH, but then washed and measured in BC(+) medium. The effect of the washing was 2-fold: firstly it allows changing the BC concentration after the NH2OH incubation and secondly it stops the reduction process by removing the reductant, thus allowing to study the point of action of BC.
The original FIOPs presented in Fig. 8 (left) reveal that a 10-min incubation of S1Y oxD thylakoids with 0.2 mM NH2OH leads to the first maximum of O2 evolution after the 6th flash, i.e., most centers are shifted into the S−2 state. A comparison of patterns 1 and 2 in Fig. 8 and Table 4 reveals that the subtle, yet highly reproducible difference (see below) in the shift between BC(−) and BC(+) samples can be observed again, despite the fact that NH2OH was removed prior to measuring the FIOPs. FIOP 3 in Fig. 8 was obtained with a sample that was reduced with NH2OH in BC(−) buffer (like FIOP 1, Fig. 8), but measured after washing with BC(+) medium (like FIOP 2, Fig. 8). It is obvious that pattern 3 more closely resembles FIOP 2 than FIOP 1 in Fig. 8. This indicates that BC does not affect the reaction sequence during NH2OH reduction, but leads to an apparent shift of the S i states before or during the measurements. To test, if the differences in apparent S i /S −i state populations are simply the consequence of the effect of BC on the β1 parameter, we included this parameter in our fits that are presented in Table 4. Three different scenarios are tested in Table 4: (A) the β1 parameter is not considered (β1 = β), (B) β1 is fixed to 10% as found for BC(−) in Table 1 and (C) β1 is allowed to vary freely. These fits show that observed differences in S i /S −i state distribution after NH2OH incubation of BC(−) and BC(+) thylakoids do not vanish after including the β1 parameter in the fits. The right side of Fig. 8 displays a summary of three repeats of each experiment. The small error bars show that the experimental error is well below the above-discussed differences.
On the basis of ESEEM measurements it was shown that acetate binds in the vicinity or at Mn4O x Ca cluster (Clemens et al. 2002). We, therefore, tested if acetate slows down the reduction of the Mn by NH2OH. Figure 9 shows that no significant slowing of the reduction of the S1, S0 and S-1 states is observed in presence of 40 mM acetate at pH 6.4. The small differences between the patterns are well explained by the increase in miss parameter caused by acetate addition (compare dashed lines in Fig. 9a, b).
MIMS
In the above experiments BC was depleted from the media by argon bubbling (method 1) and the samples were assayed subsequently on a Joliot-type electrode. These techniques do not allow monitoring the CO2/BC level during the experiment and, despite extreme care, it cannot be excluded that some CO2 may have diffused back into the samples during the quick sample transfer and measurements (total time <2 min). Therefore, the question remains what the actual inorganic carbon levels were during the experiments.
The level of BC-depletion from the media can be determined by monitoring the CO2 level in depleted buffers compared to air-saturated media at given pH. For this 25 μl of these media were injected into the mass spectrometric cell (150 μl volume) that was filled with degassed buffer (pH 6.4). Comparison of trace a (non-depleted buffer) and trace b (argon bubbled buffer) shows that method 1 leads to an about 50-fold reduction of CO2-levels in the buffer. After a 40 s exposure to air, which simulates the application of the sample onto the Joliot electrode, this level rises to about 5-fold below ambient (Fig. 10).
Discussion
Binding of bicarbonate within the WOC
With the BC-depletion levels reached in this study (∼50-times during incubation and ∼5-times during measurements) no evidence was found that BC binds to the Mn4O x Ca cluster. Neither the miss parameter, nor the stabilities of the S0, (S1), S2, and S3 states during the reaction with endogenous electron donors and acceptors were found to be affected by washing thylakoids in BC(−) buffer obtained by extensive bubbling with argon. In addition, BC did not change the rate of reduction of the WOC by the external reductant NH2OH. However, a small, yet reproducible shift in the S i /S −i state distribution occurs that might be related to BC interaction after the reduction occurred or during the light-induced transitions in the flash train. Unfortunately, we are presently unable to provide a conclusive explanation for this latter phenomenon. At any case, the effect appears to be too small to allow the conclusion that BC is bound at or near the Mn4O x Ca cluster.
To further test this question, we examined, whether the BC analog acetate affects the reaction of NH2OH with the Mn4O x Ca cluster. The reasoning behind this experiment is that acetate was shown by ESEEM spectroscopy to bind near or possibly even at the Mn4O x Ca cluster (Clemens et al. 2002). The data of Fig. 9 show that also acetate, at the concentration used in this study (40 mM), does not affect the interaction of NH2OH with the Mn4O x Ca cluster, despite the fact that this concentration is high enough to significantly increase the miss parameter. This suggests that the increased miss parameter is a consequence of the interaction of acetate with the acceptor side, and/or that the acetate (BC) and NH2OH interact at independent sites with the donor side (or WOC).
Although our NH2OH incubations were performed outside the electrode, i.e., at about ∼50-fold decreased BC-levels, they cannot fully exclude very tight BC binding, which might be present if BC were for example a structural component of the WOC.
Bicarbonate binding at the non-heme iron
This study demonstrates for the first time that a clearly increased β1 parameter is found in BC(−) samples. This effect can be suggested to be coupled to the redox state of the non-heme iron on the acceptor side of PSII. The BC binding to the non-heme iron is suggested by crystallography (Ferreira et al. 2004; Loll et al. 2005) and previous studies (involving mostly formate treatments, see below) have clearly established that the ‘BC’ effect on the acceptor side involves binding of formate or acetate at the non-heme iron (for review see (van Rensen 2002; van Rensen and Klimov 2005; van Rensen et al. 1999)). We propose that our BC removal procedure is able to extract the BC molecule bound to the non-heme iron (Fe2+) in a way that it is not replaced by a similar ligand (see below). This appears to alter the redox potential of the non-heme iron so that it can be oxidized to Fe3+ by the ambient redox potential. If xenon flashes of a few μs half-width are used for excitation this situation causes a high-double hit only in the first flash, because Fe3+ accepts after the first flash very rapidly an electron from Q −A and a second turnover can take place in such centers within the same flash. Thereafter, the non-heme iron remains in oxidation state Fe2+ for the rest of the flash train and the double hit returns to normal values (Jursinic 1981).
In previous studies, an altered value of β1 was not found for BC depleted samples (Jursinic and Stemler 1984; Shevela et al. 2006b; Stemler et al. 1974; Stemler and Lavergne 1997). The differences are straight forwardly explained. Shevela and coworkers (Shevela et al. 2006b) used ferricyanide as electron acceptor during the flash experiments that were performed with a highly sensitive-membrane covered (Clark-type) electrode. Therefore, the non-heme iron was oxidized in all samples and no difference was noted between BC(+) and BC(−) thylakoids. In two studies of Stemler BC depletion was achieved by addition of either acetate (Stemler et al. 1974) or formate (Stemler and Lavergne 1997) and in both cases this did not lead to an increase of β1. These earlier observations are confirmed by the experiments presented in Figs. 2 and 3. We propose that in presence of these carboxylic acids BC is replaced at the non-heme iron by acetate/formate, which prevents its oxidation to Fe3+ at ambient redox-potentials. Consistent with this idea it was shown in two previous studies that it is much harder to oxidize the non-heme iron by ferricyanide in presence of formate (Jursinic and Stemler 1984; Radmer and Ollinger 1980). These findings indicate that the redox potential of the non-heme iron dependents on its ligands: it is most easily oxidized to Fe3+ in absence of BC, while formate or acetate appear to stabilizes the Fe2+ oxidation level as compared to the natural BC ligand.
While the above suggestion gives a coherent explanation for the observed data of this study, we have to remark that we neither directly observed BC binding to PSII (the non-heme iron) nor did we obtain direct information about the redox-state of the non-heme iron. Given the fact that the CO2/BC levels very quickly rise from ∼50-fold depletion to a ∼5-fold depletion during sample transfer to the Joliot-electrode, it is also possible that we are unable to observe an increase of the miss parameter similar to that observed with acetate or formate, because of a very rapid (<2 min) rebinding of BC to the non-heme iron during the transfer. This scenario would also be consistent with the above-suggested oxidation of the non-heme iron, because the oxidation of the non-heme iron would in any case occur during the incubation in the sealed vials outside the electrode. We also like to point out that our experiments were performed at a flash frequency of 2 Hz and are therefore unable to detect effects that may be present under rate limiting conditions.
Effects of formate and acetate
Formate and acetate have been added in the past to PSII samples in order to replace BC that may be bound to PSII. This approach is supported by the similar structures of these carboxylic acids as compared to BC (Scheme 1). Consistent with previous studies we find significantly increased miss parameters under these conditions. This raises the question about the mechanistic basis for this effect.
Extensive experimental work by many laboratories has established that there are at least two binding sites for these carboxylic acids within PSII: one at the non-heme iron (Deligiannakis et al. 1994; Diner and Petrouleas 1990; Jajoo et al. 2005; Kühne et al. 1999; Nugent et al. 1992; Wydrzynski and Govindjee 1975; Xiong et al. 1997, 1998) and one between YZ and the Mn4O x Ca cluster (Bock et al. 1988; Clemens et al. 2002; Dorlet et al. 1998, 1999; Feyziev et al. 2000; Force et al. 1997; Govindjee et al. 1997; Jajoo et al. 2005, 2006; Klimov et al. 1995a, b; Kühne et al. 1999; Lakshmi et al. 1999; Lydakis-Simantiris et al. 1998; Maclachlan and Nugent 1993; Mende and Wiessner 1985; Saygin et al. 1986; Szalai and Brudvig 1996a, b; Wincencjusz et al. 1996, 1999). In three further studies also formate binding near YD is reported (Hienerwadel et al. 1996, 2005; Kim and Barry 1998). However, it is unclear if formate and acetate indeed replace BC at both binding sites. While on the basis of the cited literature BC replacement appears to be well-established for the binding site at the non-heme iron, binding within the WOC is often reported to occur in competition with Cl− rather than BC. It was attempted in two previous MIMS studies to quantify the number of bound BC molecules to PSII. While in the first study no evidence was found for CO2 release after formate injection (Stemler 1989), the subsequent report was able to detect the slow release of one CO2 per PSII complex after formate injection at pH 6.5 (Govindjee et al. 1991).
Formate (and acetate) binding to the non-heme iron have been reported to slow the Q −A to Q −B electron transfer, possibly by disrupting the protonation pathway for Q 2−B (Govindjee et al. 1997; van Rensen and Klimov 2005). Binding of acetate (and formate) within the WOC was shown to slow the Y •Z reduction kinetics. Especially the S2Y •Z → S3YZ transition is slowed significantly at room temperature so that the S2Y •Z state can be traped (Bock et al. 1988; Dorlet et al. 1998, 1999; Feyziev et al. 2000; Force et al. 1997; Kühne et al. 1999; Lakshmi et al. 1999; Lydakis-Simantiris et al. 1998; Maclachlan and Nugent 1993; Szalai and Brudvig 1996a, b; Wincencjusz et al. 1996, 1999). Both phenomena can give rise to higher-miss parameters and the current study does not allow deciding, which effect is dominating under our conditions. It also remains to be established, whether the high-miss parameters are caused by the absence of BC or the presence of acetate or formate. Our current data appear to favor the latter, but due to the relatively low-depletion levels during the FIOP measurements they are not fully conclusive in this regard.
MIMS measurements
Our MIMS data show that argon bubbling of buffers leads to a significant reduction of the inorganic carbon levels, in our hands ∼50-fold. They also show that CO2 is diffusing back into the depleted solutions very quickly if small aliquots are handled. This may be one reason for the discrepancies in the literature, and monitoring of the CO2/BC level should be part of any future study.
Conclusion
We show that reducing the BC concentration in the samples 5-fold relative to air saturated buffers does not affect the redox potential of the WOC in PSII as shown by unchanged S0, S2, and S3 life-times. Even at ∼50-fold reduced BC level the rate of reduction of the WOC by NH2OH was unchanged. Therefore, it appears likely that BC, after its probable involvement in the assembly of the Mn4O x Ca cluster, leaves the WOC. Alternatively BC could remain so tightly bound to the WOC that we were unable to remove it by washing with BC/CO2-depleted buffer. This question will be addressed in future MIMS studies. The cause for the high miss parameters in presence of acetate of formate remains to be established.
Abbreviations
- α:
-
Miss parameter
- β:
-
Double hit parameter
- β1 :
-
Double hit parameter of the first flash
- BC:
-
Bicarbonate = hydrogencarbonate
- BC(−):
-
Bicarbonate depleted
- BC(+):
-
Bicarbonate containing
- FIOP:
-
Flash-induced oxygen evolution pattern
- MES:
-
2-(N-morpholino) Ethanesulfonic acid
- MIMS:
-
Membrane-inlet mass spectrometry
- PSII:
-
Photosystem II
- S i states:
-
Oxidation states of the WOC, where i is the number of stored oxidizing equivalents
- WOC:
-
Water oxidizing complex
- Y2 :
-
Oxygen yield induced by the second flash
- YD :
-
Redox-active tyrosine 160 of the D2 polypeptide of PSII
- YZ :
-
Redox-active tyrosine 161 of the D1 polypeptide of PSII
References
Allakhverdiev SI, Yruela I, Picorel R, Klimov VV (1997) Bicarbonate is an essential constituent of the water-oxidizing complex of photosystem II. Proc Natl Acad Sci USA 94:5050–5054
Baranov SV, Ananyev GM, Klimov VV, Dismukes GC (2000) Bicarbonate accelerates assembly of the inorganic core of the water-oxidizing complex in manganese depleted photosystem II: a proposed biogeochemical role for atmospheric carbon dioxide in oxygenic photosynthesis. Biochemistry 39:6060–6065
Baranov SV, Tyryshkin AM, Katz D, Dismukes GC, Ananyev GM, Klimov VV (2004) Bicarbonate is a native cofactor for assembly of the manganese cluster of the photosynthetic water oxidizing complex. Kinetics of reconstitution of O2 evolution by photoactivation. Biochemistry 43:2070–2079
Bock CH, Gerken S, Stehlik D, Witt HT (1988) Time resolved EPR on photosystem II particles after irreversible and reversible inhibition of water cleavage with high concentrations of acetate. FEBS Lett 227:141–146
Bouges B (1971) Action de faibles concentrations d’hydroxylamine sur l’emission d’oxygene des algues chlorella et des chloroplastes d’epinards. Biochim Biophys Acta 936:228–235
Clausen J, Beckmann K, Junge W, Messinger J (2005) Evidence that bicarbonate is not the substrate in photosynthetic oxygen evolution. Plant Physiol 139:1444–1450
Clemens KL, Force DA, Britt RD (2002) Acetate binding at the photosystem II oxygen evolving complex: An S2 state multiline signal ESEEM study. J Am Chem Soc 124:10921–10933
de Wijn R, van Gorkom HJ (2002) S-state dependence of the miss probability in photosystem II. Photosynth Res 72:217–222
Debus RJ (1992) The manganese and calcium ions of photosynthetic oxygen evolution. Biochim Biophys Acta 1102:269–352
Deligiannakis Y, Petrouleas V, Diner BA (1994) Binding of carboxylate anions at the nonheme Fe(II) of PS II. 1. Effects on the Q -a Fe2+ and QaFe3+ EPR spectra and the redox properties of the iron. Biochim Biophys Acta 1188:260–270
Diner BA (1977) Dependence of deactivation reactions of photosystem II on redox state of plastoquinone pool A varied under anaerobic conditions. Equilibria on the acceptor side of photosystem II. Biochim Biophys Acta 460:247–258
Diner BA, Petrouleas V (1990) Formation by NO of nitrosyl adducts of redox components of the photosystem II reaction center. 2. Evidence that HCO -3 CO2 binds to the acceptor-side non-heme iron. Biochim Biophys Acta 1015:141–149
Dismukes GC, Klimov VV, Baranov SV, Kozlov YN, DasGupta J, Tyryshkin A (2001) The origin of atmospheric oxygen on earth: the innovation of oxygenic photosynthesis. Proc Natl Acad Sci USA 98:2170–2175
Dorlet P, Di Valentin M, Babcock GT, McCracken JL (1998) Interaction of Y •Z with its environment in acetate-treated photosystem II membranes and reaction center cores. J Phys Chem B 102:8239–8247
Dorlet P, Boussac A, Rutherford AW, Un S (1999) Multifrequency high-field EPR study of the interaction between the tyrosyl Z radical and the manganese cluster in plant photosystem II. J Phys Chem B 103:10945–10954
Ferreira KN, Iverson TM, Maghlaoui K, Barber J, Iwata S (2004) Architecture of the photosynthetic oxygen-evolving center. Science 303:1831–1838
Feyziev YM, Yoneda D, Yoshii T, Katsuta N, Kawamori A, Watanabe Y (2000) Formate-induced inhibition of the water-oxidizing complex of photosystem II studied by EPR. Biochemistry 39:3848–3855
Forbush B, Kok B, McGloin MP (1971) Cooperation of charges in photosynthetic oxygen evolution. II. Damping of flash yield oscillation, deactivation. Photochem Photobiol 14:307–321
Force DA, Randall DW, Britt RD (1997) Proximity of acetate, manganese, and exchangeable deuterons to tyrosine Y •Z in acetate-inhibited photosystem II membranes: Implications for the direct involvement of Y •Z in water-splitting. Biochemistry 36:12062–12070
Good NE, Winget GD, Winter W, Connolly TN, Izawa S, Singh RMM (1966) Hydrogen ion buffers for biological research. Biochemistry 5:467–477
Govindjee, Weger HG, Turpin DH, van Rensen JJS, Devos OJ, Snel JFH (1991) Formate releases carbon dioxide/bicarbonate from thylakoid membranes - measurements by mass spectroscopy and infrared gas analyzer. Naturwissenschaften 78:168–170
Govindjee, Xu C, van Rensen JJS (1997) On the requirement of bound bicarbonate for photosystem II activity. Z Naturforsch 52:24–32
Hienerwadel R, Boussac A, Breton J, Berthomieu C (1996) Fourier transform infrared difference study of tyrosineD oxidation and plastoquinone QA reduction in photosystem II. Biochemistry 35:15447–15460
Hienerwadel R, Gourion-Arsiquaud S, Ballottari M, Bassi R, Diner BA, Berthomieu C (2005) Formate binding near the redox-active tyrosineD in photosystem II: consequences on the properties of TyrD. Photosynth Res 84:139–144
Hillier W, Messinger J (2005) Mechanism of photosynthetic oxygen production. In: Wydrzynski T, Satoh K (eds) Photosystem II. The light-driven water:plastoquinone oxidoredutase. Advances in photosynthesis and respiration, vol 22. Springer, Dordrecht, pp 567–608
Hillier W, McConnell I, Badger MR, Boussac A, Klimov VV, Dismukes GC, Wydrzynski T (2006) Quantitative assessment of intrinsic carbonic anhydrase activity and the capacity for bicarbonate oxidation in photosystem II. Biochemistry 45:2094–2102
Ioannidis N, Sarrou J, Schansker G, Petrouleas V (1998) NO reversibly reduces the water oxidizing complex of photosystem II through S0 and S1 to the state characterized by the Mn(II)-Mn(III) multiline EPR signal. Biochemistry 37:16445–16451
Isgandarova S, Renger G, Messinger J (2003) Functional differences of photosystem II from Synechococcus elongatus and spinach characterized by flash-induced oxygen evolution patterns. Biochemistry 42:8929–8938
Iuzzolino L, Dittmer J, Dörner W, Meyer-Klaucke W, Dau H (1998) X-ray absorption spectroscopy on layered photosystem II membrane particles suggests manganese centered oxidation of the oxygen evolving complex for the S0-S1, S1-S2, and S2-S3 transitions of the water oxidation cycle. Biochemistry 37:17112–17119
Jajoo A, Bharti S, Kawamori A (2005) Interactions of chloride and formate at the donor and the acceptor side of photosystem II. J Bioenerg Biomembr 37:49–54
Jajoo A, Katsuta N, Kawamori A (2006) An EPR study of the pH dependence of formate effects on Photosystem II. Plant Physiol Biochem 44:186–192
Joliot P, Barbieri G, Chabaud R (1969) Un nouveau modele des centres photochimiques du systeme II. Photochem Photobiol 10:309–329
Joliot P (1972) Modulated light source use with the oxygen electrode. In: San Pietro A (ed) Photosynthesis and nitrogen fixation. Methods of enzymology, vol 24B. Academic Press, New York, pp 123–134
Jursinic P (1981) Investigation of double turnovers in photosystem II charge separation and oxygen evolution with excitation flashes of different duration. Biochim Biophys Acta 635:38–52
Jursinic PA, Stemler A (1984) Effects of bicarbonate depletion on secondary acceptors of photosystem II. Biochim Biophys Acta 764:170–178
Kim SY, Barry BA (1998) Vibrational spectrum associated with the reduction of tyrosyl radical D• in photosystem II: a comparative biochemical and kinetic study. Biochemistry 37:13882–13892
Klimov VV, Allakhverdiev SI, Baranov SV, Feyziev YM (1995a) Effects of bicarbonate and formate on the donor side of photosystem 2. Photosynth Res 46:219–225
Klimov VV, Allakhverdiev SI, Feyziev YM, Baranov SV (1995b) Bicarbonate requirement for the donor side of photosystem II. FEBS Lett 363:251–255
Klimov VV, Hulsebosch RJ, Allakhverdiev SI, Wincencjusz H, van Gorkom HJ, Hoff AJ (1997) Bicarbonate may be required for ligation of manganese in the oxygen-evolving complex of photosystem II. Biochemistry 36:16277–16281
Klimov VV, Baranov SV (2001) Bicarbonate requirement for the water-oxidizing complex of photosystem II. Biochim Biophys Acta 1503:187–196
Kok B, Forbush B, McGloin M (1970) Cooperation of charges in photosynthetic O2 evolution. Photochem Photobiol 11:457–476
Konermann L, Messinger J, Hillier W (2007) Mass spectrometry based methods for studying kinetics and dynamics in biological systems. In: Aartsma T, Matysik J (eds) Biophysical techniques in photosynthesis (Part II). Springer, in press
Kozlov YN, Zharmukhamedov SK, Tikhonov KG, Dasgupta J, Kazakova AA, Dismukes GC, Klimov VV (2004) Oxidation potentials and electron donation to photosystem II of manganese complexes containing bicarbonate and carboxylate ligands. Phys Chem Chem Phys 6:4905–4911
Kühne H, Szalai VA, Brudvig GW (1999) Competitive binding of acetate and chloride in photosystem II. Biochemistry 38:6604–6613
Kulik LV, Epel B, Lubitz W, Messinger J (2005) 55Mn pulse ENDOR at 34 GHz of the S0 and S2 states of the oxygen-evolving complex in photosystem II. J Am Chem Soc 127:2392–2393
Lakshmi KV, Eaton SS, Eaton GR, Brudvig GW (1999) Orientation of the tetranuclear manganese cluster and tyrosine Z in the O2-evolving complex of photosystem II: An EPR study of the S2Y •Z state in oriented acetate-inhibited photosystem II membranes. Biochemistry 38:12758–12767
Loll B, Kern J, Saenger W, Zouni A, Biesiadka J (2005) Towards complete cofactor arrangement in the 3.0 Å resolution structure of photosystem II. Nature 438:1040–1044
Lydakis-Simantiris N, Dorlet P, Ghanotakis DF, Babcock GT (1998) Kinetic and spectroscopic properties of the Y •Z radical in Ca2+- and Cl–depleted photosystem II preparations. Biochemistry 37:6427–6435
Maclachlan DJ, Nugent JHA (1993) Investigation of the S3 electron-paramagnetic-resonance signal from the oxygen-evolving complex of photosystem 2 – effect of inhibition of oxygen evolution by acetate. Biochemistry 32:9772–9780
Mende D, Wiessner W (1985) Bicarbonate in vivo requirement of photosystem II in the green alga Chlamydobotrys stellata. J Plant Physiol 118:259–266
Messinger J (1993) Untersuchungen über die reaktiven Eigenschaften der verschiedenen Redoxzustände der Wasseroxidase Höherer Pflanzen. TU Berlin, Berlin
Messinger J, Renger G (1990) The reactivity of hydrazine with PS II strongly depends on the redox state of the water oxidizing system. FEBS Lett 277:141–146
Messinger J, Renger G (1993) Generation, oxidation by the oxidized form of the tyrosine of polypeptide D2, and possible electronic configuration of the redox States S0, S-1 and S-2 of the water oxidase in isolated spinach thylakoids. Biochemistry 32:9379–9386
Messinger J, Renger G (1994) Analysis of pH-induced modifications of the period four oscillation of the flash induced oxygen evolution reveal distinct structural changes of the photosystem II donor side at characteristic pH values. Biochemistry 33:10896–10905
Messinger J, Wacker U, Renger G (1991) Unusual low reactivity of the water oxidase in the redox state S3 toward exogenous reductants. Analysis of the NH2OH and NH2NH2 induced modifications of flash induced oxygen evolution in isolated spinach thylakoids. Biochemistry 30:7852–7862
Messinger J, Schröder WP, Renger G (1993) Structure-function relations in photosystem II. Effects of temperature and chaotropic agents on the period four oscillation of flash induced oxygen evolution. Biochemistry 32:7658–7668
Messinger J, Badger M, Wydrzynski T (1995) Detection of one slowly exchanging substrate water molecule in the S3 state of photosystem II. Proc Natl Acad Sci USA 92:3209–3213
Messinger J, Seaton G, Wydrzynski T, Wacker U, Renger G (1997) S-3 state of the water oxidase in photosystem II. Biochemistry 36:6862–6873
Messinger J, Robblee JH, Bergmann U, Fernandez C, Glatzel P, Isgandarova S, Hanssum B, Renger G, Cramer SP, Sauer K, Yachandra VK (eds) (2001a) Manganese oxidation states in photosystem II. CSIRO Publishing, Collingwood, Australia
Messinger J, Robblee JH, Bergmann U, Fernandez C, Glatzel P, Visser H, Cinco RM, McFarlane KL, Bellacchio E, Pizarro SA, Cramer SP, Sauer K, Klein MP, Yachandra VK (2001b) Absence of Mn centered oxidation in the S2 to S3 transition: implications for the mechanism of photosynthetic water oxidation. J Am Chem Soc 123:7804–7820
Metzner H (1978) Photosynthetic oxygen evolution. Academic Press, London
Nugent JHA, Demetriou C, Lockett CJ (1987) Electron donation in photosystem II. Biochim Biophys Acta 894:534–542
Nugent JHA, Doetschman DC, Maclachlan DJ (1992) Characterization of the multiple EPR line shapes of iron semiquinones in photosystem 2. Biochemistry 31:2935–2941
Radmer R, Ollinger O (1980) Isotopic composition of photosynthetic O2 flash yields in the presence of H 182 O and HC18O -3 . FEBS Lett 110:57–61
Renger G, Hanssum B (1988) Studies on the deconvolution of flash induced absorption changes into the difference spectra of individual redox steps within the water oxidizing enzyme system. Photosynth Res 16:243–259
Renger G, Holzwarth AR (2005) Primary electron transfer. In: Wydrzynski TJ, Satoh K (eds) Photosystem II. The light-driven water:plastoquinone oxidoreductase. Advances in photosynthesis and respiration, vol 22. Springer, Dordrecht, pp 139–175
Rutherford AW, Inoue Y (1984) Oscillation of delayed luminescence from PS II: recombination of S2Q -B and S3Q -B . FEBS Lett 165:163–170
Rutherford AW, Crofts AR, Inoue Y (1982) Thermoluminescence as a probe of photosystem II photochemistry. The origin of the flash-induced glow peaks. Biochim Biophys Acta 682:457–465
Sarrou J, Isgandarova S, Kern J, Zouni A, Renger G, Lubitz W, Messinger J (2003) Nitric oxide induced formation of the S-2 state in the oxygen evolving complex of photosystem II from Synechococcus elongatus. Biochemistry 42:1016–1023
Saygin Ö, Gerken S, Meyer B, Witt HT (1986) Total recovery of O2 evolution and nanosecond reduction kinetics of chlorophyllaII+ (P680+) after Inhibition of water cleavage with acetate. Photosynth Res 9:71–78
Shevela D, Nöring B, Eckert HJ, Messinger J, Renger G (2006a) Characterization of the water oxidizing complex of photosystem II of the Chl d-containing cyanobacterium Acaryochloris marina via its reactivity towards endogenous electron donors and acceptors. Phys Chem Chem Phys 8:3460–3466
Shevela DN, Khorobrykh AA, Klimov VV (2006b) Effect of bicarbonate on the water-oxidizing complex of photosystem II in the super-reduced S-states. Biochim Biophys Acta 1757:253–261
Shinkarev V, Wraight CA (1993) Oxygen evolution in photosynthesis: from unicycle to bicycle. Proc Natl Acad Sci USA 90:1834–1838
Shinkarev VP (1996) Binary oscillations in the Kok model of oxygen evolution in oxygenic photosynthesis. Photosynth Res 48:411–417
Stemler A (1989) Absence of a formate-induced release of bicarbonate from photosystem 2. Plant Physiol 91:287–290
Stemler AJ (2002) The bicarbonate effect, oxygen evolution, and the shadow of Otto Warburg. Photosynth Res 73:177–183
Stemler A, Govindjee (1973) Bicarbonate ion as a critical factor in photosynthetic oxygen evolution. Plant Physiol 52:119–123
Stemler AJ, Lavergne J (1997) Evidence that formate destabilizes the S-1 state of the oxygen-evolving mechanism in Photosystem II. Photosynth Res 51:83–92
Stemler A, Radmer R (1975) Source of photosynthetic oxygen in bicarbonate-stimulated Hill reaction. Science 190:457–458
Stemler A, Babcock GT, Govindjee (1974) Effect of bicarbonate on photosynthetic oxygen evolution in flashing light in chloroplast fragments. Proc Natl Acad Sci USA 71:4679–4683
Styring S, Rutherford AW (1987) In the oxygen evolving complex of photosystem II the S0 state is oxidized to the S1 State by Y +D (Signal IIslow). Biochemistry 26:2401–2405
Szalai VA, Brudvig GW (1996a) Formation and decay of the S3 EPR signal species in acetate-inhibited photosystem II. Biochemistry 35:1946–1953
Szalai VA, Brudvig GW (1996b) Reversible binding of nitric oxide to tyrosyl radicals in photosystem II. Nitric oxide quenches formation of the S3 EPR signal species in acetate-inhibited photosystem II. Biochemistry 35:15080–15087
van Rensen JJS (2002) Role of bicarbonate at the acceptor side of Photosystem II. Photosynth Res 73:185–192
van Rensen JJS, Klimov VV (2005) Bicarbonate interactions. In: Wydrzynski T, Satoh K (eds) Photosystem II. The light-driven water:plastoquinone oxidoreductase. Advances in photosynthesis and respiration, vol 22. Springer, Dordrecht, pp 329–346
van Rensen JJS, Xu C, Govindjee (1999) Role of bicarbonate in photosystem II, the water-plastoquinone oxido-reductase of plant photosynthesis. Physiol Plant 105:585–592
Vass I, Styring S (1991) pH dependent charge equilibria between tyrosine D and the S states in photosystem II. Estimation of relative midpoint potentials. Biochemistry 30:830–839
Vass I, Deak Z, Hideg E (1990a) Charge equilibrium between the water oxidizing complex and the electron donor tyrosine D in photosystem II. Biochim Biophys Acta 1017:63–69
Vass I, Deak Z, Jegerschold C, Styring S (1990b) The accessory electron-donor tyrosine D of photosystem II is slowly reduced in the dark during low-temperature storage of isolated thylakoids. Biochim Biophys Acta 1018:41–46
Vermaas WEJ, Renger G, Dohnt G (1984) The reduction of the oxygen evolving system in chloroplasts by thylakoid components. Biochim Biophys Acta 764:194–202
Vermaas WFJ, Rutherford AW, Hansson O (1988) Site directed mutagenesis in photosystem II of the cyanobacterium Synechocystis sp. PCC 6803: donor D is a tyrosine residue in the D2 protein. Proc Natl Acad Sci USA 85:8477–8481
Warburg O (1964) Prefactory Chapter. Annu Rev Biochem 33:1–18
Warburg O, Krippahl G (1958) Hill-Reaktionen. Z Naturforsch 13:509–514
Wiessner W, Mende D, Demeter S (1992) Thermoluminescence study of the invivo effects of bicarbonate depletion and acetate formate presence in the 2 algae Chlamydobotrys stellata and Chlamydomonas reinhardtii. Photosynth Res 34:279–285
Wincencjusz H, Allakhverdiev SI, Klimov VV, van Gorkom HJ (1996) Bicarbonate-reversible formate inhibition at the donor side of Photosystem II. Biochim Biophys Acta 1273:1–3
Wincencjusz H, Yocum CF, van Gorkom HJ (1999) Activating anions that replace Cl- in the O2 evolving complex of photosystem II slow the kinetics of the terminal step in water oxidation and destabilize the S2 and S3 states. Biochemistry 38:3719–3725
Winget GD, Izawa S, Good NE (1965) Stoichiometry of photophosphorylation. Biochem Biophys Res Commun 21:438–441
Wydrzynski T, Govindjee (1975) New site of bicarbonate effect in photosystem II of photosynthesis - Evidence from chlorophyll fluorescence transients in spinach-chloroplasts. Biochim Biophys Acta 387:403–408
Wydrzynski T, Satoh K (eds) (2005) Photosystem II. The light-driven water:plastoquinone oxidoreductase. Springer, Dordrecht
Xiong J, Hutchison RS, Sayre RT, Govindjee (1997) Modification of the photosystem II acceptor side function in a D1 mutant (arginine-269-glycine) of Chlamydomonas reinhardtii. Biochim Biophys Acta 1322:60–76
Xiong J, Minagawa J, Crofts A, Govindjee (1998) Loss of inhibition by formate in newly constructed photosystem II D1 mutants, D1-R257E and D1-R257M, of Chlamydomonas reinhardtii. Biochim Biophys Acta 1365:473–491
Yachandra VK, DeRose VJ, Latimer MJ, Mukerji I, Sauer K, Klein MP (1993) Where plants make oxygen: a structural model for the photosynthetic oxygen evolving manganese cluster. Science 260:675–679
Yano J, Kern J, Sauer K, Latimer MJ, Pushkar Y, Biesiadka J, Loll B, Saenger W, Messinger J, Zouni A, Yachandra VK (2006) Where water is oxidized to dioxygen: structure of the photosynthetic Mn4Ca cluster. Science 314:821–825
Zimmermann JL, Rutherford AW (1986) Photoreductant-induced oxidation of Fe2+ in the electron acceptor complex of photosystem II. Biochim Biophys Acta 851:416–423
Acknowledgments
The financial support by the Deutsche Forschungsgemeinschaft (DFG, Me 1629/2–3) and the Max-Planck Gesellschaft is gratefully acknowledged. We thank Katrin Beckmann for her help and advice during the MIMS measurements. DS was initially supported by a fellowship of the Deutsche Akademische Austauschdienst (DAAD). The authors are especially thankful to Govindjee for stimulating this research project by constantly reminding them not to forget about the bicarbonate (formate/acetate) effect on photosystem II.
Author information
Authors and Affiliations
Corresponding author
Rights and permissions
About this article
Cite this article
Shevela, D., Klimov, V. & Messinger, J. Interactions of photosystem II with bicarbonate, formate and acetate. Photosynth Res 94, 247–264 (2007). https://doi.org/10.1007/s11120-007-9200-2
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s11120-007-9200-2