Characterization of four herbicide-resistant mutants of Rhodopseudomonas viridis by genetic analysis, electron paramagnetic resonance, and optical spectroscopy

Herbicides of the triazine class block electron transfer in the photosynthetic reaction centers of purple bacteria and PSII of higher plants. They are thought to act by competing with one of the electron acceptors, the secondary quinone, QB, for its binding site. Several mutants of the purple bacterium Rhodopseudomonas viridis resistant to terbutryn [2-(methylthio)-4-(ethylamino)-6-(tert-butylamino)-s-triazine] have been isolated by their ability to grow photosynthetically in the presence of the herbicide. Sequence analysis of the genes coding for the L and M subunits of the reaction center showed that four different mutants were obtained, two of them being double mutated: T1 (SerL223----Ala and ArgL217----His), T3 (PheL216----Ser and ValM263----Phe), T4 (TyrL222----Phe), and T6 (PheL216----Ser). The residues L223 and L216 are involved in binding of QB, whereas L217 and L222 are not. M263 is part of the binding pocket of the primary quinone, QA. The affinity of the reaction centers for terbutryn and the electron transfer inhibitor o-phenanthroline, determined via the biphasic charge recombination after one flash, is decreased for all mutants. The affinity for ubiquinone 9 is also decreased, except in T1. Characterization by EPR spectroscopy showed that the QB.-Fe2+ signal of T4, having a g = 1.93 peak, is different from the signals obtained with the wild type and the other mutants but very similar to those of Rhodospirillum rubrum and PSII. The results obtained by the combination of these different techniques are discussed with respect to the three-dimensional structure of the wild type and the mode of binding of ubiquinone, terbutryn, and o-phenanthroline as determined by X-ray structure analysis.     

Regulation of photosynthetic electron transport by bicarbonate formate and herbicides in isolated broken and intact chloroplasts

In this paper, we have presented a minireview on the interaction of bicarbonate, formate and herbicides with the thylakoid membranes.The regulation of photosynthetic electron transport by bicarbonate, formate and herbicides is described. Bicarbonate, formate, and many herbicides act between the primary quinone electron acceptor Q_A and the plastoquinone pool. Many herbicides like the ureas, triazines and the phenol-type herbicides act, probably, by the displacement of the secondary quinone electron acceptor Q_B from its binding site on a Q_B-binding protein located at the acceptor side of Photosystem II. Formate appears to be an inhibitor of electron transport; this inhibition can be removed by the addition of bicarbonate. There appears to be an interaction of the herbicides with bicarbonate and/or It has been suggested that both the binding of a herbicide and the absence of bicarbonate may cause a conformational alteration of the environment of the Q_B-binding site. The alteration brought about by a herbicide decreases the affinity for another herbicide or for bicarbonate; the change caused by the absence of bicarbonate decreases the affinity for herbicides. Moreover, this change in conformation causes an inhibition of electron transport. A bicarbonate-effect in isolated intact chloroplasts is demonstrated.Paper presented at the FESPP meeting (Strasbourg, 1984)     

Herbicide binding and thermal stability of photosystem II isolated from Thermosynechococcus elongatus

Binding of herbicides to photosystem II inhibits the electron transfer from Q(A) to Q(B) due to competition of herbicides with plastoquinone bound at the Q(B) site. We investigated herbicide binding to monomeric and dimeric photosystem II core complexes (PSIIcc) isolated from Thermosynechococcus elongatus by a combination of different methods (isothermal titration and differential scanning calorimetry, CD spectroscopy and measurements of the oxygen evolution) yielding binding constants, enthalpies and stoichiometries for various herbicides as well as information regarding stabilization/destabilization of the complex. Herbicide binding to detergent-solubilized PSIIcc can be described by a model of single independent binding sites present on this important membrane protein. Interestingly, binding stoichiometries herbicide:PSIIcc are lower than 1:1 and vary depending on the herbicide under study. Strong binding herbicides such as terbutryn stabilize PSIIcc in thermal unfolding experiments and endothermically binding herbicides like ioxynil probably cause large structural changes accompanied with the binding process as shown by differential scanning calorimetry experiments of the unfolding reaction of PSIIcc monomer in the presence of ioxynil. In addition we studied the occupancy of the Q(B) sites with plastoquinone (PQ9) by measuring flash induced fluorescence relaxation yielding a possible explanation for the deviations of herbicide binding from a 1:1 herbicide/binding site model.     

Herbicide binding and thermal stability of photosystem II isolated from Thermosynechococcus elongatus

Binding of herbicides to photosystem II inhibits the electron transfer from Q_A to Q_B due to competition of herbicides with plastoquinone bound at the Q_B site. We investigated herbicide binding to monomeric and dimeric photosystem II core complexes (PSIIcc) isolated from Thermosynechococcus elongatus by a combination of different methods (isothermal titration and differential scanning calorimetry, CD spectroscopy and measurements of the oxygen evolution) yielding binding constants, enthalpies and stoichiometries for various herbicides as well as information regarding stabilization/destabilization of the complex. Herbicide binding to detergent-solubilized PSIIcc can be described by a model of single independent binding sites present on this important membrane protein. Interestingly, binding stoichiometries herbicide:PSIIcc are lower than 1:1 and vary depending on the herbicide under study. Strong binding herbicides such as terbutryn stabilize PSIIcc in thermal unfolding experiments and endothermically binding herbicides like ioxynil probably cause large structural changes accompanied with the binding process as shown by differential scanning calorimetry experiments of the unfolding reaction of PSIIcc monomer in the presence of ioxynil. In addition we studied the occupancy of the Q_B sites with plastoquinone (PQ9) by measuring flash induced fluorescence relaxation yielding a possible explanation for the deviations of herbicide binding from a 1:1 herbicide/binding site model.     

Mode of action of Photosystem II herbicides studied by thermoluminescence

The mode of action of chemically different herbicides (ureas, pyridazinones, phenylcarbamates, triazines, hydroxyquinolines, hydroxybenzonitriles and dinitrophenols) on photosynthetic electron transport was investigated by measurements of oxygen evolution and thermoluminescence. Depending on the particular herbicide used the thermoluminescence band related to Q (the primary acceptor of Photosystem II) appears at +5, 0 or −14°C. It was shown that these three different peak positions can be ascribed to various redox states of Q, the shifts being due to the binding of herbicides to the chloroplast membrane. Both displacement experiments and additive inhibition of herbicide pairs measured by thermoluminescence and oxygen evolution suggested that the sites of action of these herbicides are on the same protein. However, herbicide treatment of trypsinized chloroplasts showed that there were three different binding sites on the same protein, in agreement with the classification of herbicides into three groups based on thermoluminescence measurements. Our results suggest that the primary and secondary acceptors of Photosystem II (Q and B, respectively) are in close proximity and form a common complex with the herbicide-binding protein within the chloroplast membrane.     

Investigations on the influence of headgroup substitution and isoprene side-chain length in the function of primary and secondary quinones of bacterial reaction centers

The contributions of headgroup and side-chain in the binding and function of the primary (QA) and secondary (QB) quinones of isolated reaction centers (RCs) from Rhodobacter sphaeroides were investigated. Various ubiquinones and structurally similar quinones were reconstituted into RCs depleted of one (1Q-RCs) or both (0Q-RCs) quinones. The influence of partition coefficients on the apparent binding affinities was minimized by expressing dissociation constants in terms of the mole fraction of quinone partitioned into the detergent. It was then apparent that the size of the isoprenyl side-chain was of little consequence in determining the binding affinity or the functional competence of either QA or QB, although an alkyl chain of equivalent size was a poor substitute. The degree of substitution of the headgroup, however, was a sensitive determinant of binding. For both quinone sites, the trisubstituted plastoquinones bond more weakly than the fully substituted ubiquinones. Similarly, for binding to the QA site, duroquinone (tetramethylbenzoquinone) bound much more strongly than trimethylbenzoquinone. The affinity of the QA site for ubiquinones was about 20-times stronger than the QB site, but the QB site is probably not more specific than the QA site. However, QB function depends on a suitable redox free-energy drop from QA as well as binding, and of all the quinones tested only the ubiquinones simultaneously supported full QA and QB activity. Even plastoquinone-A, which fills both roles in Photosystem II, was unable to do so in bacterial RCs, although it did bind. The unique ability of ubiquinones to both bind and provide the appropriate redox span is discussed. The temperature dependence of binding of the isoprenyl ubiquinones at the QA site changed markedly with chain length. For Q-10-Q-7, the binding enthalpy was positive and net binding was entirely driven by entropic factors. For the shorter-chain ubiquinones, Q-6-Q-1, both entropy and enthalpy of binding were favorable. This strong entropy-enthalpy compensation is suggested to arise from antagonistic interactions (anticooperativity) between headgroup and tail binding. For QB function by hydrophobic quinones, the temperature dependence of the micelle properties prevented easy access to thermodynamic parameters. However, for water-soluble Q-0, binding to the QB site was determined to be enthalpically driven.(ABSTRACT TRUNCATED AT 400 WORDS)     

The binding of triazine herbicides to the photosynthetic reaction center of Rhodopseudomonas viridis. Energy minimization studies.

The binding of six herbicides of the triazine family to the photosynthetic reaction center of Rhodopseudomonas viridis was investigated with energy-minimization techniques, in order to correlate experimental with calculated data. The inhibitors were modeled in the active site according to the X-ray structure analysis of the complex formed between the triazine terbutryn (2-ethylamino-4-t-butylamino-6-methylthio-s-triazine) and the reaction center of R. viridis [Michel, H., Epp. O. & Deisenhofer, J. (1986) EMBO J. 5, 2445-2451]. 40 different energy minimizations were carried out with varying cutoff radii, partial charges on inhibitor atoms and dielectric constants, i.e. 10 different combinations of these were tested. The impact of these parameters on the calculated binding and interaction energy was either examined for all protein/triazine complexes or, in the case of the dielectric constant, a smaller sample was used. The calculated energies are dominated by van der Waals interactions, which change by up to 20% when extending the cutoff radius from 0.8 nm to 1.5 nm. The use of uniform or distance-dependent dielectric constant or partial charges on the inhibitor atoms does not severely influence the resulting structures, but shows a great impact on the calculated energies. In the two groups of triazines, each containing three inhibitors with methoxy or methylthio substituents, correlations of biological and calculated data were found quite often, but only once with all six triazines. The energy-minimized structures were compared and analysed. A third hydrogen bond, not seen in the X-ray analysis of the reaction center/tertubryn complex, was found between the t-butylamino moiety of terbutryn (and equivalent moieties in the other triazines) and the carbonyl oxygen of TyrL222.     

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

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

Triazine-resistant Nicotiana mutants from photomixotrophic cell cultures

Summary Triazine-resistant mutants have been isolated in photomixotrophic cell cultures of Nicotiana plumbaginifolia. Triazine herbicides inhibit photosynthesis and cause extensive photodestruction of chloroplasts (bleaching) in sensitive plants. Selection was based on the greening ability of the resistant cells in the presence of 10^-4 M terbutryn, under normal culture conditions, but in a medium containing a low sugar concentration. In the mutant plants, as compared to wild type, two to three orders of magnitude higher concentrations of triazines resulted in inhibition of photosynthetic electron transport and greening. The resistance was inherited maternally.     

Reduction and protonation of the secondary quinone acceptor of Rhodobacter sphaeroides photosynthetic reaction center: kinetic model based on a comparison of wild-type chromatophores with mutants carrying Arg-->Ile substitution at sites 207 and 217 in the L-subunit

After the light-induced charge separation in the photosynthetic reaction center (RC) of Rhodobacter sphaeroides, the electron reaches, via the tightly bound ubiquinone QA, the loosely bound ubiquinone Q(B) After two subsequent flashes of light, Q(B) is reduced to ubiquinol Q(B)H2, with a semiquinone anion Q-(B) formed as an intermediate after the first flash. We studied Q(B)H2 formation in chromatophores from Rb. sphaeroides mutants that carried Arg-->Ile substitution at sites 207 and 217 in the L-subunit. While Arg-L207 is 17 A away from Q(B), Arg-L217 is closer (9 A) and contacts the Q(B)-binding pocket. From the pH dependence of the charge recombination in the RC after the first flash, we estimated deltaG(AB), the free energy difference between the Q-(A)Q(B) and Q(A)Q-(B) states, and pK212, the apparent pK of Glu-L212, a residue that is only 4 A away from Q(B). As expected, the replacement of positively charged arginines by neutral isoleucines destabilized the Q-(B) state in the L217RI mutant to a larger extent than in the L207RI one. Also as expected, pK212 increased by approximately 0.4 pH units in the L207RI mutant. The value of pK212 in the L217RI mutant decreased by 0.3 pH units, contrary to expectations. The rate of the Q-(A)Q-(B)-->Q(A)Q(B)H2 transition upon the second flash, as monitored by electrometry via the accompanying changes in the membrane potential, was two times faster in the L207RI mutant than in the wild-type, but remained essentially unchanged in the L217RI mutant. To rationalize these findings, we developed and analyzed a kinetic model of the Q-(A)Q-(B)-->Q(A)Q(B)H2 transition. The model properly described the available experimental data and provided a set of quantitative kinetic and thermodynamic parameters of the Q(B) turnover. The non-electrostatic, 'chemical' affinity of the QB site to protons proved to be as important for the attracting protons from the bulk, as the appropriate electrostatic potential. The mutation-caused changes in the chemical proton affinity could be estimated from the difference between the experimentally established pK2J2 shifts and the expected changes in the electrostatic potential at Glu-L212, calculable from the X-ray structure of the RC. Based on functional studies, structural data and kinetic modeling, we suggest a mechanistic scheme of the QB turnover. The detachment of the formed ubiquinol from its proximal position next to Glu-L212 is considered as the rate-limiting step of the reaction cycle.     

Mutations that modify or exclude binding of the QA ubiquinone and carotenoid in the reaction center from Rhodobacter sphaeroides

Three single-site mutations have been introduced at positions close to the Q_A ubiquinone in the reaction centre from Rhodobacter sphaeroides. Two of these mutations, Ala M260 to Trp and Ala M248 to Trp, result in a reaction centre that does not support photosynthetic growth of the bacterium, and in which electron transfer to the Q_A ubiquinone is abolished. In the reaction centre with an Ala to Trp mutation at the M260 residue, electron transfer from the primary donor to the acceptor bacteriopheophytin is not affected by the mutation, but electron transfer from the acceptor bacteriopheophytin to Q_A is not observed. The most likely basis for these effects is that the mutation produces a structural change that excludes binding of the Q_A ubiquinone. A third mutation, Leu M215 to Trp, produces a reaction centre that has an impaired capacity for supporting photosynthetic growth. The mutation changes the nature of ubiquinone binding at the Q_A site, and renders the site sensitive to quinone site inhibitors such as o- phenanthroline. Adopting a similar approach, in which a small residue located close to a cofactor is changed to a more bulky residue, we show that the reaction centre can be rendered carotenoid-less by the mutation Gly M71 to Leu.     

Exploring the primary electron acceptor (QA)-site of the bacterial reaction center from Rhodobacter sphaeroides. Binding mode of vitamin K derivatives.

The functional replacement of the primary ubiquinone (QA) in the photosynthetic reaction center (RC) from Rhodobacter sphaeroides with synthetic vitamin K derivatives has provided a powerful tool to investigate the electron transfer mechanism. To investigate the binding mode of these quinones to the QA binding site we have determined the binding free energy and charge recombination rate from QA(-) to D+ (kAD) of 29 different 1,4-naphthoquinone derivatives with systematically altered structures. The most striking result was that none of the eight tested compounds carrying methyl groups in both positions 5 and 8 of the aromatic ring exhibited functional binding. To understand the binding properties of these quinones on a molecular level, the structures of the reaction center-naphthoquinone complexes were predicted with ligand docking calculations. All protein--ligand structures show hydrogen bonds between the carbonyl oxygens of the quinone and AlaM260 and HisM219 as found for the native ubiquinone-10 in the X-ray structure. The center-to-center distance between the naphthoquinones at QA and the native ubiquinone-10 at QB (the secondary electron acceptor) is essentially the same, compared to the native structure. A detailed analysis of the docking calculations reveals that 5,8-disubstitution prohibits binding due to steric clashes of the 5-methyl group with the backbone atoms of AlaM260 and AlaM249. The experimentally determined binding free energies were reproduced with an rmsd of approximately 4 kJ x mol(-1) in most cases providing a valuable tool for the design of new artificial electron acceptors and inhibitors.     

Functioning of quinone acceptors in the reaction center of the green photosynthetic bacterium Chloroflexus aurantiacus

The photosynthetic reaction centers (RC) of the green bacterium Chloroflexus aurantiacus have been investigated by spectral and electrometrical methods. In these reaction centers, the secondary quinone was found to be reconstituted by the addition of ubiquinone-10. The equilibrium constant of electron transfer between primary (QA) and secondary (QB) quinones was much higher than that in RC of purple bacteria. The QB binding to the protein decreased under alkalinization with apparent pK 8.8. The single flash-induced electric responses were about 200 mV. An additional electrogenic phase due to the QB protonation was observed after the second flash in the presence of exogenous electron donors. The magnitude of this phase was 18% of that related to the primary dipole (P+QA-) formation. Since the C. aurantiacus RC lacks H-subunit, this subunit was not an obligatory component for electrogenic QB protonation.     

Replacement of photosynthetic electron transport inhibitors by silicomolybdate

KCN-treated spinach chloroplasts, their photosystem I being ineffective, exhibit a single reaction site for silicomolybdate. Using this heteropolyanion as electron acceptor, photosynthetic oxygen evolution is partially inhibited by ureas, triazines, or phenylpyridazinone herbicides, their inhibitory effect depending on the concentration of silicomolybate. Labelled atrazine attached to isolated chloroplast material is competitively replaced by silicomolybdate in the same manner as e.g. ureas complete with a triazine herbicide. – It is concluded (1) that silicomolybdate is bound and reduced at the herbicide-binding protein, and (2) that the inhibition of silicomolybdate reduction by herbicides such as DCMU is due to loss of reaction sites for silicomolybdate.     

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

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

Characterization of the bacterial population structure in an anaerobic-aerobic activated sludge system on the basis of respiratory quinone profiles.

Bacterial respiratory quinones were used as biomarkers for studying the bacterial population structure, especially the content of Acinetobacter species, in a laboratory-scale anaerobic-aerobic activated sludge system and in the standard aerobic system. All tested sludges contained both ubiquinone and menaquinone, with a molar ratio of about 1:0.5. High-performance liquid chromatography showed that ubiquinone with eight isoprene units (Q-8) was present as the predominant ubiquinone, Q-10 was the second most common type, and Q-9 and other homologs were minor components in the anaerobic-aerobic sludge and the standard aerobic sludge. Bacteriological examination indicated that, in both sludge systems, Q-8-containing bacteria constituted a large proportion of the aerobic heterotrophic bacterial flora, but only a few strains with Q-9 were found. These findings demonstrate that the population of Acinetobacter species, which contain Q-9 as the major quinone, is negligible in those environments. The present results suggest that the introduction of anaerobic conditions into the aerobic batch process has little influence on the bacterial community structure.     

Radical-pair energetics and decay mechanisms in reaction centers containing anthraquinones, naphthoquinones or benzoquinones in place of ubiquinone

In reaction centers from Rhodobacter sphaeroides (formerly called Rhodopseudomonas sphaeroides), light causes an electron-transfer reaction that forms the radical pair state (P+I-, or PF) from the initial excited singlet state (P) of a bacteriochlorophyll dimer (P). Subsequent electron transfer to a quinone (Q) produces the state P+Q-. Back electron transfer can regenerate P from P+Q-, giving rise to 'delayed' fluorescence that decays with approximately the same lifetime as P+Q-. The free-energy difference between P+Q- and P can be determined from the initial amplitude of the delayed fluorescence. In the present work, we extracted the native quinone (ubiquinone) from Rps. sphaeroides reaction centers, and replaced it by various anthraquinones, naphthoquinones, and benzoquinones. We found a rough correlation between the halfwave reduction potential (E1/2) of the quinone used for reconstitution (as measured polarographically in dimethylformamide) and the apparent free energy of the state P+Q- relatively to P. As the E1/2 of the quinone becomes more negative, the standard free-energy gap between P+Q- and P decreases. However, the correlation is quantitatively weak. Apparently, the effective midpoint potentials (Em) of the quinones in situ depend subtly on interactions with the protein environment in the reaction center. Using the value of the Em for ubiquinone determined in native reaction centers as a reference, and the standard free energies determined for P+Q- in reaction centers reconstituted with other quinones, the effective Em values of 12 different quinones in situ are estimated. In native reaction centers, or in reaction centers reconstituted with quinones that give a standard free-energy gap of more than about 0.8 eV between P+Q- and P*, charge recombination from P+Q- to the ground state (PQ) occurs almost exclusively by a temperature-insensitive mechanism, presumably electron tunneling. When reaction centers are reconstituted with quinones that give a free-energy gap between P+Q- and P* of less than 0.8 with quinones that give a free-energy gap between P+Q- and P* of less than 0.8 eV, part or all of the decay proceeds through a thermally accessible intermediate. There is a linear relationship between the log of the rate constant for the decay of P+Q- via the intermediate state and the standard free energy of P+Q-. The higher the free energy, the faster the decay. The kinetic and thermodynamic properties of the intermediate appear not to depend strongly on the quinone used for reconstitution, indicating that the intermediate is probably not simply an activated form of P+Q-.(ABSTRACT TRUNCATED AT 400 WORDS)     

Reaction centers from three herbicide-resistant mutants of Rhodobacter sphaeroides 2.4.1: sequence analysis and preliminary characterization

Many herbicides that inhibit photosynthesis in plants also inhibit photosynthesis in bacteria. We have isolated three mutants of the photosynthetic bacterium Rhodobacter sphaeroides that were selected for increased resistance to the herbicide terbutryne. All three mutants also showed increased resistance to the known electron transfer inhibitor o-phenanthroline. The primary structures of the mutants were determined by recombinant DNA techniques. All mutations were located on the gene coding for the L-subunit resulting in these changes Ile²²⁹ Met, Ser²²³ Pro and Tyr²²² Gly. The mutations of Ser²²³ is analogous to the mutation of Ser²⁶⁴ in the D1 subunit of photosystem II in green plants, strengthening the functional analogy between D1 and the bacterial L-subunit. The changed amino acids of the mutant strains form part of the binding pocket for the secondary quinone, Q _b . This is consistent with the idea that the herbicides are competitive inhibitors for the Q _b binding site. The reaction centers of the mutants were characterized with respect to electron transfer rates, inhibition constants of terbutryne and o-phenanthroline, and binding constants of the quinone UQ₀ and the inhibitors. By correlating these results with the three-dimensional structure obtained from x-ray analysis by Allen et al. (1987a, 1987b), the likely positions of o-phenanthroline and terbutryne were deduced. These correspond to the positions deduced by Michel et al. (1986a) for Rhodopseudomonas viridis.Abbreviations ATP adenosine 5-triphosphate - Bchl bacteriochlorophyll - Bphe bacteriopheophytin - bp basepair - cyt c²⁺ reduced form of cytochrome c - DEAE diethylami-noethyl - EDTA ethylenediamine tetraacetic acid - Fe²⁺ non-heme iron atom - LDAO lauryl dimethylamine oxide - Pipes piperazine-N,N-bis-2-ethane-sulfonic acid - PSII photosystem II - RC reaction center - SDS sodium dodecylsulfate - Tris tris(hydroxy-methyl)aminomethane - UQ₀ 2,3-dimethoxy-5-methyl benzoquinone - UQ₁₀ ubiquinone 50     

Characterization of the adaptation response ofAnacystis nidulans to growth in the presence of sublethal doses of herbicide

Cells of the cyanobacterium,Anacystis nidulans, were cultured in the presence of sublethal doses of the herbicides DCMU [3-(3,4-dichlorophenyl)-1, 1-dimethylurea] and terbutryn (a triazine). The responses observed were characteristic of photosynthetic organisms grown under low light conditions. The contents of the accessory pigment phycocyanin increased in relation to chlorophyll. Moreover, each dose of herbicide was correlated with defined changes in the pigment profile. Data obtained from chlorophyll fluorescence measurements indicated that the additional phycocyanin was functionally integrated into phycobilisomes, probably into newly formed phycobilisomes. The concentration of fatty acids in the total polar lipid fraction (per milligram chlorophyll) was greater in adapted than in control cells; nevertheless, the ratio of unsaturated to saturated fatty acids remained unchanged. Measurable rates of photosynthetic electron transport were similar among herbicide-adapted cultures and controls. These data are consistent with the hypothesis that herbicide treatment impaired electron transport, but that function was restored by the adaptation response. Furthermore, this response is conserved among cyanobacteria and higher plants, indicating that this flexibility is extremely significant to photosynthetic function.     

A similar structure of the herbicide binding site in photosystem II of plants and cyanobacteria is demonstrated by site specific mutagenesis of the psbA gene

Many herbicides inhibit the photosynthetic electron transfer in photosystem II by binding to the polypeptide D1. A point mutation in the chloroplast gene psbA, which leads to a change of the amino acid residue 264 of D1 from serine to glycine, is responsible for atrazine resistance in higher plants. We have changed serine 264 to glycine in Synechococcus PCC7942 and compared its phenotype to a mutant with a serine to alanine shift in the same position. The results show that glycine at position 264 in D1 gives rise to a similar phenotype in cyanobacteria and in higher plants, indicating a similar structure of the binding site for herbicides and for the quinone Q_B in the two systems. A possible mode of binding of phenyl-urea herbicides to D1 is predicted from the difference in herbicidal cross-resistance between glycine and alanine substitutions of serine 264.Abbreviations DCPIP 2,6-dichlorophenolindophenol - I₅₀ concentration of herbicide giving 50% inhibition - K_b binding constant - kb kilobase - MES 2(N-morpholino)ethanesulfonic acid - PS II photosystem II