Chemosphere 75 (2009) 924–928 Contents lists available at ScienceDirect Chemosphere journal homepage: www.elsevier.com/locate/chemosphere Allelopathic mechanism of pyrogallol to Microcystis aeruginosa PCC7806 (Cyanobacteria): From views of gene expression and antioxidant system Jihai Shao a,b,c, Zhongxing Wu a, Gongliang Yu a, Xin Peng a, Renhui Li a,* a Institute of Hydrobiology, Chinese Academy of Sciences, Wuhan 430072, PR China Graduate School of Chinese Academy of Sciences, Beijing 100039, PR China c Resources and Environment College, Hunan Agricultural University, Changsha 410128, PR China b a r t i c l e i n f o Article history: Received 15 October 2008 Received in revised form 12 December 2008 Accepted 2 January 2009 Available online 8 February 2009 Keywords: Pyrogallol Microcystis aeruginosa Allelopathy Mechanism a b s t r a c t Pyrogallol is a potent allelochemical on Microcystis aeruginosa, but its allelopathic mechanism is not fully known. In order to explore this mechanism, gene expressions for prx, mcyB, psbA, recA, grpE, fabZ under pyrogallol stress were studied, and activities of the main antioxidant enzymes were also measured. The results showed that expression of grpE and recA showed no significant change under pyrogallol stress, while psbA and mcyB were up-regulated at 4 mg L1. Both prx and fabZ were upregulated even under exposure to 1 mg L1 pyrogallol concentration. The activities of superoxide dismutase (SOD) and catalase (CAT) were enhanced under pyrogallol stress. Levels of malodialdehyde (MDA) at 2 and 4 mg L1 pyrogallol were significantly higher than those of the controls. It was concluded that oxidant damage is an important mechanism for the allelopathic effect of pyrogallol on M. aeruginosa. Ó 2009 Elsevier Ltd. All rights reserved. 1. Introduction Cyanobacterial blooms are a frequent and worldwide occurrence especially as eutrophication of water supplies increase. Environmental and health problems from these waterblooms have been documented in many regions due to the production of toxins called cyanotoxins (Chorus and Bartram, 1999). The main cyanotoxin group are the hepatotoxic microcystins produced by species and populations of Anabaena (Krishnamurthy et al., 1986), Microcystis (Watanabe et al., 1986), Planktothrix (Laub et al., 2002), and occasionally Nostoc (Sivonen et al., 1990). The toxicity of microcystins is mediated through the inhibition of eukaryotic protein phosphatases 1A and 2A in liver cells (Carmichael, 1995). It is well known that Microcystis is the most important genus responsible for water blooms and production of microcystins (Azevedo et al., 2002). Therefore, controlling growth of harmful Microcystis species in waters is crucial in the management and mitigation of cyanobacteria harmful algae blooms. A variety of methods have been proposed for removing and/or inhibiting cyanobacterial blooms, but most of them were impractical because of high cost or subsequent secondary pollution (Anderson, 1997). Some aquatic plants have been found to * Corresponding author. Tel.: +86 27 68780067; fax: +86 27 68780123. E-mail address: reli@ihb.ac.cn (R. Li). 0045-6535/$ - see front matter Ó 2009 Elsevier Ltd. All rights reserved. doi:10.1016/j.chemosphere.2009.01.021 produce substances inhibiting the growth of harmful cyanobacteria/algae, and some chemicals from these plants, such as eugeniin (Saito et al., 1989), gallic acids, pyrogallol, (+)-catechin, ellagic acid (Nakai et al., 2000), nonanoic acid (Nakai et al., 2005), and ethyl-2-methylacetoacetate (Li and Hu, 2005), have been identified to have algicidal activities. Among these chemicals, pyrogallol was reported to be one of the most inhibitory to Microcystis aeruginosa (EC50, 0.65 mg L1) (Nakai et al., 2000), but the allelopathic mechanism of pyrogallol to Microcystis is not fully known. Previous studies indicated that the inhibitory mechanisms of pyrogallol on Microcystis species may involve interaction among proteins (Spencer et al., 1988), inhibition of alkaline phosphatase (Gross et al., 1996; Dziga et al., 2007), interruption of the electron transfer chain (Leu et al., 2002; Dziga et al., 2007), and oxidant damage from auto-oxidise of polyphenol (Nakai et al., 2001). To date, research on gene expression of Microcystis under various stress conditions has not been done. In our study, we explore the allelopathic mechanism of pyrogallol on gene expression in Microcystis species, as well as antioxidant enzyme activities of M. aeruginosa under pyrogallol stress. Six important genes: synthesis of peroxiredoxin (prx), production of microcystin (mcyB), core protein of photosynthetic processes (psbA), and damage and repair of biological macromolecules (recA, grpE, fabZ) were selected. These results will help elucidate responses of M. aeruginosa under the pyrogallol stress at the gene and protein levels, and eventually provide insight into the allelopathic mechanism of aquatic plants on cyanobacteria and/or algae. J. Shao et al. / Chemosphere 75 (2009) 924–928 925 1989; Bustin, 2000). The induction ratio was calculated using 2DDCt where DDct = (Ct, target gene Ct, 16S rrn) stress (Ct, target gene Ct, 16S rrn) control according to the handbook of ABI Prism 7000 SDS software. 2. Materials and methods 2.1. Strain and culture conditions M. aeruginosa PCC 7806 was originally obtained from the Pasteur Culture Collection of Cyanobacteria in France and kindly provided by the Freshwater Algae Culture Collection of the Chinese Academy of Sciences. The strain was grown in BG11 liquid medium (pH 9) (Rippka et al., 1979), under a 12:12 LD cycle with an intensity of 30 lmol photons s1 m2 provided by cool white fluorescent tubes at 25 ± 1 °C. Pyrogallol (AR) was purchased from Sinopharm Group Chemical Reagent Ltd. (Shanghai, China). Experiments were carried out in 250 mL conical flasks containing 99.9 mL BG11 liquid medium, 100 lL of combined stock pyrogallol solutions and H2O (stock solution of pyrogallol were freshly made up in water prior to use) to obtain pyrogallol concentrations as 0, 1, 2, 4 mg L1 respectively. Each treatment was replicated three times, and the initial cyanobacterial concentration was 5.2 104 cell mL1. All treatments were cultured in the light at 30 lmol photons s1 m2 at 25 ± 1 °C for 12 h. 2.2. RNA extraction M. aeruginosa PCC 7806 cells were harvested, after 12 h exposure to pyrogallol, by centrifuging them at 7000 rpm for 5 min. Pelleted cells were resuspended in Trizol reagent (Invitrogen USA), and homogenized with a mini-beadbeater. Total RNAs were extracted following the Trizol reagent manual (Invitrogen, USA). 2.3. Reverse transcription Total RNAs were digested with RQ1 RNase-free DNase (Promega USA). These DNase treated RNAs were reverse transcripted to cDNA using random primers p(dN)9 and a reverse transcriptase kit (Generay, China). 2.4. Primer design and real-time PCR PCR primers designed for six genes are listed in Table 1, with the 16S rRNA gene as the control. Real-time PCR was performed with 10 lL Master Mix (SYBR Green, TOYOBO, Japan), 0.2 lL (10 pmol lL1) forward primer and reverse primer respectively, 1 lL cDNA, the final volumes were 20 lL. The amplification reactions were performed by an ABI Prism 7000 Sequence Detect System (Applied Biosystems USA) under the following conditions: one cycle at 95 °C for 3 min, followed by 40 cycles of 95 °C for 15 s, 59 °C for 30 s, 72 °C for 30 s. Gene expression data from Real-time PCR were evaluated using Ct value (Livak and Schmittgen, 2001), and the 16S rRNA gene was used as the housekeeping gene to normalize the expression levels of target genes, since the expression of 16S rRNA is stable under the various conditions (Barbu and Dautry, 2.5. Malodialdehyde (MDA), superoxide dismutase (SOD) and catalase (CAT) assays Lipid peroxidation product as malodialdehyde (MDA) was measured spectrophotometrically using the thiobarbituric acid method (Uchimaya and Mihara, 1978). Total SOD activity was determined by nitroblue terazolium (NBT) photoreduction (Beauchamp and Frodovich, 1971), and this enzymic activity was expressed as units of SOD activity per microgram protein, where 1 U of SOD is defined as the amount of enzyme required for 50% inhibition of Cyt c reduction. The assay for antioxidant enzyme-catalase (CAT) activity was based on its ability to decompose H2O2, with the absorbance of supernatant at 240 nm (Choo et al., 2004). 2.6. Statistics Significant differences between control and treated samples were determined using the t- test. Differences were considered to be significant at p < 0.05. 3. Results and discussion 3.1. Gene expression of M. aeruginosa PCC 7806 under pyrogallol stress prx is a gene encoding for peroxiredoxin (Prx), a 25-kDa protein which was first discovered in yeast (Chae et al., 1994), and belongs to the thiol oxidation system. Prx could catalyze the reduction of H2O2, alkyl hydroperoxides, and peroxynitrite, using thioredoxin and other thiol containing reducing agents as electron donors (Wood et al., 2003). As shown in Fig. 1, expression of prx, in response to pyrogallol stress, was found to be up-regulated even at 1 mg L1. The relative normalized expression of prx at pyrogallol concentrations of 2 and 4 mg L1, were 3.6 and 7.2 times of the control. prx plays important biological roles, since peroxiredoxins are highly conserved in eukaryotes and prokaryotes (Kim et al., 1996). Genomic analysis studies have indicated that multigenic families of prx-s exist in cyanobacteria and play important roles in their biological processes (Stork et al., 2005). For example, a mutant of cyanobacterium Anabaena PCC 7120 that fails to synthesize PrxQ-A was found to be highly sensitive to oxidative stress, and this hypersensitivity of the mutant was restored by inducing the Table 1 Primers designed for real-time PCR. Gene name Forward primer (50 -30 ) Reverse primer (50 -30 ) 16S rrn prx psbA mcyB*** recA grpE fabZ GGACGGGTGAGTAACGCGTA* GCGAATTTAGCAGTATCAACACC GGTCAAGARGAAGAAACCTACAAT CCTACCGAGCGCTTGGG TAGTTGACCAGTTAGTGCGTTCTT CGCAAACGCACAGCCAAGGAA TGTTAATTGTGGAATCCATGG CCCATTGCGGAAAATTCCCC** GCGGTGCTGATTTCTTTTTTC GTTG AAACCGTTGAGGTTGAA GAAAATCCCCTAAAGATTCCTGAGT CACTTCAGGATTGCCGTAGGT GTGAATACCCATCTCGCCATC TTGCTTCCCCTTGCATTTT * ** *** Modified according to Urbach et al. (1992). Modified according to Nübel et al. (1997). Kurmayer and Kutzenberger (2003). Fig. 1. Relative normalized expression of prx of M. aeruginosa PCC 7806 under pyrogallol stress. The horizontal axis is the concentrations of pyrogallol in BG11 medium. The error bar is the mean ± standard deviation. * is the p < 0.05 (t-test between control and pyrogallol stress samples). 926 J. Shao et al. / Chemosphere 75 (2009) 924–928 Fig. 2. Relative normalized expression of mcyB of M. aeruginosa PCC 7806 under pyrogallol stress. The horizontal axis is the concentration of pyrogallol in BG11 medium. The error bar is the mean ± standard deviation. * is the p < 0.05 (t-test). expression of the prxQ-A gene in trans (Latifi et al., 2007). The upregulated expression of prx in M. aeruginosa PCC 7806 under pyrogallol stress implied that oxidant damage may be the mechanism for the allelopathy of pyrogallol to Microcystis cells. mcyB is a gene belonging to gene cluster mcyA-J responsible for the synthesis of microcystins in a number of cyanobacterial genera (Pearson and Neilan, 2008). Compared to controls, expression of mcyB at pyrogallol concentrations of 1 and 2 mg L1 showed little variation, but did show a slight up-regulation at 4 mg L1 (Fig. 2). It has been reported that many environmental factors affect the synthesis of microcystins in Microcystis species. Iron deficiency, for instance, resulted in an increase of microcystin-LR content relative to total protein in M. aeruginosa (Beatriz et al., 2006). High light intensity has also been found to increase the transcription of mcyB and mcyD (Kaebernick et al., 2000). To our knowledge, the present study is the first report to demonstrate that pyrogallol could up-regulate the expression of mcyB. Dziga et al. (2007) reported pyrogallol stress could increase microcystin content in the culture medium of M. aeruginosa, and they explained this phenomenon as resulting from the release of this hepatotoxin from dead Microcystis cells. Our results suggested that the up-regulated expression of mcy gene maybe was another reason responsible for the increase of the microcystin contents in the cultural medium of M. aeruginosa beside the release of the microcystin from dead cells. The results also suggested that water safety should be considered when Microcystis forming blooms were planned to be controlled by using pyrogallol or by using aquatic macrophytes with high contents of pyrogallol. To explore whether damages to photosynthetic processes, DNA, protein, and cell membrane occurred under pyrogallol stress, psbA, recA, grpE and fabZ were selected as target genes in this research. psbA encodes D1 protein, a key subunit of Photosystem II (PS II) (Aro et al., 1993). Results of the expression analysis of psbA in response to the pyrogallol stress are shown in Fig. 3. The expression of psbA did not show a significant variation at 1 and 2 mg L1, but the relative normalized expression of psbA at a concentration of Fig. 3. Relative normalized expression of psbA, recA, grpE and fabZ of M. aeruginosa PCC 7806 under pyrogallol stress. ( ) 0, ( ) 1, ( ) 2, ( ) 4 mg L1. The error bar is the mean ± standard deviation. * is the p < 0.05 (t-test). 4 mg L1 pyrogallol was 6.9 times of the control. PS II has been known to be very sensitive to changes in the environment, and the degree of the repair for PS II is determined by the rate of synthesis for the D1 protein de novo (Aro et al., 1993). Photoinhibition would usually not be observed if repairing rate keeps pace with photodamage rate. However, if photodamage rate exceeds repair, then net photoinhibition could be observed (Madhavi et al., 2007). Pyrogallol stress has been found to inhibit the oxygen evolution of M. aeruginosa (Dziga et al., 2007), and it was also shown that the repair rate did not keep up with the damage rate under pyrogallol stress. The synthesis of mature D1 protein involves transcription and translation of psbA and transfer of the precursor (preD1) to the D1. Nishiyama et al. (2004) reported that singlet oxygen molecules could inhibit the repair of PS II by suppressing translation elongation of the D1 protein. As shown in our results, the synthesis of psbA mRNA was up-regulated at a concentration of 4 mg L1, suggesting that the photosynthetic processes in M. aeruginosa PCC7806 had already sensed the pyrogallol stress. The block in elongation of the D1 protein, as described by Nishiyama et al. (2004), probably caused not enough mature D1 to substitute for the damaged ones, which may stimulate cells to transcript more psbA mRNA. Consequently, this may be the reason for the up-regulation of psbA in M. aeruginosa under pyrogallol stress. The expression of recA and grpE showed no significant change under all pyrogallol stress treatments, while that of fabZ was found to be up-regulated even at a concentration of 1 mg L1 pyrogallol. recA is a gene encoding RecA, which forms filaments on the single-stranded DNA. In this activated form, RecA protein functions as a coprotease and stimulates the cleavage of LexA and several other proteins, and then leads to initiation of SOS repairing of DNA (Khil and Camerini-Otero, 2002). Many studies reported that the expression of recA was up-regulated in various environmental stresses such as hydrogen peroxide (Robert and Gu, 2004), 1, 1- dimethylhydrazine (Zavilgelsky et al., 2007) and mitomycin C (Khil and Camerini-Otero, 2002). However, our results showed no obvious up-regulation in expression of recA at pyrogallol concentrations below 4 mg L1. One explanation for this phenomenon is that the damage from pyrogallol on M. aeruginosa PCC 7806 was not severe enough that Microcystis cells initiate SOS repair of DNA since the SOS repair of DNA is an error-prone manner in DNA (Sundin and Weigand, 2007). And this was initiated only under conditions of severe DNA damage. Liu et al. (2007) showed that cell density of toxic M. aeruginosa was only reduced 1.6% after a 2-d exposure to pyrogallol at a concentration of 4.5 mg L1 in BG11 medium, thus reflecting that M. aeruginosa was not severely damaged in concentrations less than 4.5 mg L1. grpE is a gene encoding the heat-shock protein GrpE belonging to DnaK-DnaJ-GrpE chaperone system, and this system has been known to protect proteins against heat-induced protein aggregation. Severe oxidative stress conditions often lead to the expression of molecular chaperones and proteases (VanBogelen et al., 1987). Gawande and Griffiths (2005) reported that grpE promoters of Escherichia coli were up-regulated in oxidative stress, and phenol stress also slightly up-regulated the expression of protein grpE (Santos et al., 2004). Expression of grpE in E. coli was also found to be significantly upregulated under H2O2 stress (Kim et al., 2007). According to our results, the expression of grpE did not significantly change under pyrogallol stress, which implied that the intracellular proteins are not severely denatured from pyrogallol stress at concentrations below 4 mg L1. fabZ belongs to fatty acid biosynthesis (FAS) II, encoding b-hydroxyacyl acyl carrier protein (ACP) dehydratase, which efficiently catalyzes the dehydration of short chain-hydroxyacyl-ACPs and long chain saturated and unsaturated-hydroxyacyl-ACPs (Swarnamukhi et al., 2006). The lipid membranes most susceptible to oxidation are those containing polyunsaturated fatty acids (Floyd, 1990). The up-regulated expression of fabZ obtained J. Shao et al. / Chemosphere 75 (2009) 924–928 Fig. 4. MDA content of M. aeruginosa PCC 7806 under pyrogallol stress. The horizontal axis is the concentrations of pyrogallol in BG11 medium. The error bar is the mean ± standard deviation. * is the p < 0.05 (t-test). in this study suggested that membranes may undergo oxidant damage under the pyrogallol stress. In order to confirm this speculation, the malodialdehyde (MDA) concentration in M. aeruginosa PCC7806 cells under pyrogallol stress were determined, and the results are shown in Fig. 4. Compared with the control, MDA content was significantly higher at concentrations of 2 and 4 mg L1 pyrogallol, demonstrating that the polyunsaturated fatty acids underwent oxidative damage since MDA is the oxidative product of unsaturated fatty acids. In order to maintain the normal function of membranes, more unsaturated fatty acids need to be integrated into membranes, which would cause the obvious up-regulation in expression of fabZ. These findings also supported the hypothesis that oxidant damage is the mechanism for the allelopathy of pyrogallol to Microcystis. As shown in the expression responses of recA, grpE and fabZ under the pyrogallol stress, fabZ was found to be more sensitive than the other two genes, and this difference could be explained in that membranes related to fabZ function are the outer constitutes of cell, and are the first target for oxidative damage. 3.2. Activities of antioxidant enzymes of M. aeruginosa PCC 7806 under pyrogallol stress These results of gene expression demonstrated above suggest that oxidant damage may be an important mechanism for the allelopathy of pyrogallol to Microcystis cells. In order to further confirm this hypothesis, we determined the superoxide dismutase (SOD) and catalase (CAT) of M. aeruginosa PCC7806 under pyrogallol stress. SOD and CAT are representatives for the most important antioxidant enzymes in cells. SOD catalyzes the dismutation of the superoxide radical into H2O2 and O2 (Valentine et al., 1998), and CAT catalyzes the H2O2 into H2O and O2 (Zamocky et al., 2008). By collaboration between these two enzymes, cells could 927 Fig. 6. CAT Activity of M. aeruginosa PCC 7806 under pyrogallol stress. The horizontal axis is the concentrations of pyrogallol in BG11 medium. The error bar is the mean ± standard deviation. * is the p < 0.05 (t-test). eliminate or reduce the toxicity of superoxide radical and H2O2. The activities of SOD and CAT in responding to the pyrogallol stress are shown in Figs. 5 and 6. Compared with controls, the activities of both SOD and CAT were enhanced under pyrogallol stress. It is well known that most environmental stress affect production of active oxygen species in plants and therefore cause oxidative stress (Smirnoff, 1993). Cellular activities of SOD and CAT have always been reported to be elevated under oxidant stress, and nitrogenfixing cyanobacteria have been found to increase both SOD and CAT activities under endosulfan stress (Kumar et al., 2008). Copper stress, could also stimulate activities of SOD and CAT in green alga Pavlova viridis (Li et al., 2006). Therefore, the enhancement of SOD and CAT activities presented in this study suggested that Microcystis cells encountered oxidant stress when exposed to pyrogallol, further supporting the hypothesis that oxidant damage is an important mechanism for the allelopathy of pyrogallol to Microcystis species. 4. Conclusion Results from expression of both prx and fabZ genes, and in SOD and CAT activities support the hypothesis that oxidant damage is an important mechanism for the allelopathic effect of pyrogallol on M. aeruginosa. The expression analyses of psbA, recA, grpE and fabZ indicated that membranes are the first target for the damage of pyrogallol to Microcystis, and the D1 protein in photosynthetic processes is another important target for the damage of pyrogallol to Microcystis. Pyrogallol can up-regulate expression of the microcystin synthesis gene mcyB of M. aeruginosa, suggesting that water safety should be monitored when Microcystis blooms are being controlled using pyrogallol or macrophytes with high contents of pyrogallol. Acknowledgements The present research is supported by the Frontier Research Project of the Chinese Academy of Sciences. References Fig. 5. SOD Activity of M. aeruginosa PCC 7806 under pyrogallol stress. The horizontal axis is the concentrations of pyrogallol in BG11 medium. The error bar is the mean ± standard deviation. * is the p < 0.05 (t-test). Anderson, D.M., 1997. Turning back the harmful red tides. Nature 38, 513–514. Aro, E.M., Virgin, I., Andersson, B., 1993. Photoinhibition of photosystem II. Inactivation, protein damage and turnover. Biochim. Biophys. Acta 1143, 113– 134. Azevedo, S.M.F.O., Carmichael, W.W., Jochimsen, E.M., Rinehart, K.L., Lau, S., Shaw, G.R., Eaglesham, G.K., 2002. Human intoxication by microcystins during renal dialysis treatment in Caruaru, Brazil. Toxicology 181–182, 441–446. Barbu, V., Dautry, F., 1989. Northern blot normalization with a 28S rRNA oligonucleotide probe. Nucleic Acids Res. 17, 7715. 928 J. Shao et al. / Chemosphere 75 (2009) 924–928 Beatriz, M.L., Sevilla, E., Hernandez, J.A., Bes, M.T., Fillat, M.F., Peleato, M.L., 2006. Fur from Microcystis aeruginosa binds in vitro promoter regions of the microcystin biosynthesis gene cluster. Phytochemistry 67, 876–881. Beauchamp, C., Frodovich, I., 1971. Superoxide dismutase: improved assays and an assays applicable acrylamide gels. Anal. Biochem. 44, 276–287. Bustin, S.A., 2000. Absolute quantification of mRNA using real-time reverse transcription polymerase chain reaction assays. J. Mol. Endocrinol. 25, 169–193. Carmichael, W.W., 1995. Toxic Microcystis in the environment. In: Watanabe, M.F., Harada, K., Carmichael, W.W., Fujiki, H. (Eds.), Toxic Microcystis. CRC Press, New York, pp. 1–12. Chae, H.Z., Chung, S.J., Rhee, S.G., 1994. Thioredoxin-dependent peroxide reductase from yeast. J. Biol. Chem. 269, 26768–27670. Choo, K.S., Snoeijs, P., Pedersen, M., 2004. Oxidative stress tolerance in the filamentous green algae Cladophora glomerata and Enteromorpha ahlneriana. J. Exp. Mar. Biol. Ecol. 298, 111–123. Chorus, I., Bartram, J., 1999. Toxic cyanobacteria in water: a guide to their public health consequences, monitoring and management. WHO, E & FN, Spon, London, UK. Dziga, D., Suda, M., Bialczyk, J., Urszula, C.P., Lechowski, Z., 2007. The alteration of Microcystis aeruginosa biomass and dissolved microcystin-LR concentration following exposure to plant-producing phenols. Environ. Toxicol. 22, 341–346. Floyd, R.A., 1990. Role of oxygen free radicals in carcinogenesis and brain ischemia. FASEB 4, 2587–2597. Gawande, P.V., Griffiths, M.W., 2005. Effects of environmental stresses on the activities of the uspA, grpE and rpoS promoters of Escherichia coli O157:H7. Inter. J. Food Microbiol. 99, 91–98. Gross, E.M., Meyer, H., Schilling, G., 1996. Release and ecological impact of algicidal hydrolysable polyphenols in Myriophyllum spicatum. Phytochemistry 41, 133– 138. Kaebernick, M., Neilan, B.A., Börner, T., Dittmann, E., 2000. Light and the transcriptional response of the microcystin biosynthesis gene cluster. Appl. Environ. Microbiol. 66, 3387–3392. Khil, P.P., Camerini-Otero, R.D., 2002. Over 1000 genes are involved in the DNA damage response of Escherichia coli. Mol. Microb. 44, 89–105. Kim, H.K., Kim, S.J., Lee, J.W., Cha, M.K., Kim, I.H., 1996. Identification of promoter in the 50-flanking region of the E. coli thioredoxin-liked thiol peroxidase gene: evidence for the existence of oxygen-related transcriptional regulatory protein Biochem. Biophys. Res. Commun. 221, 641–646. Kim, Y.S., Min, J., Hong, H.N., Park, J.H., Park, K.S., Gua, M.B., 2007. Gene expression analysis and classification of mode of toxicity of polycyclic aromatic hydrocarbons (PAHs) in Escherichia coli. Chemosphere 66, 1243–1248. Krishnamurthy, T., Carmichael, W.W., Sarver, E.W., 1986. Investigations of freshwater cyanobacteria (blue-green algae) toxic peptides. I. Isolation, purification and characterization of peptides from Microcystis aeruginosa and Anabaena flos-aquae. Toxicon 24, 865–873. Kumar, S., Habib, K., Fatma, T., 2008. Endosulfan induced biochemical changes in nitrogen-fixing cyanobacteria. Sci. Total. Environ. 403, 130–138. Kurmayer, R., Kutzenberger, T., 2003. Application of real-time PCR for quantification of microcystin genotypes in a population of the toxic cyanobacterium Microcystis sp. Appl. Environ. Microbiol. 69, 6723–6730. Laub, J., Henriksen, P., Brittain, S.M., 2002. [ADMAdda (5)]-microcystins in Planktothrix agardhii strain PH-123 (cyanobacteria) – importance for monitoring of microcystins in the environment. Environ. Toxicol. 17, 351– 357. Latifi, A., Ruiz, M., Jeanjean, R., Zhang, C.C., 2007. PrxQ-A, a member of the peroxiredoxin Q family, plays a major role in defense against oxidative stress in the cyanobacterium Anabaena sp. strain PCC7120. Free Radical Bio. Med. 42, 424–431. Leu, E., Krieger-Liszkay, A., Goussias, C., Gross, E.M., 2002. Polyphenolic allelochemicals from the aquatic angiosperm Myriophyllum spicatum inhibit photosystem II. Plant Physiol. 130, 2011–2018. Li, F.M., Hu, H.Y., 2005. Isolation and characterization of a novel antialgal allelochemical from Phragmites communis. Appl. Environ. Microbiol. 71, 6545– 6553. Li, M., Hu, C.W., Zhu, Q., 2006. Copper and zinc induction of lipid peroxidation and effects on antioxidant enzyme activities in the microalga Pavlova viridis (Prymnesiophyceae). Chemosphere 62, 565–572. Liu, B.Y., Jiang, P., Zhou, A.E., Tian, J.R., Jiang, S.Y., 2007. Effect of pyrogallol on the growth and pigment content of cyanobacteria-blooming toxic and nontoxic Microcystis aeruginosa. Bull. Environ. Contam. Toxicol. 78, 499–502. Livak, K.J., Schmittgen, T.D., 2001. Analysis of relative gene expression data using real-time quantitative PCR and the 2DDCt method. Method 25, 402–408. Madhavi, K., Hong, J.H., Wang, H.L., Robert, L.B., 2007. Engineered ectopic expression of the psbA gene encoding the photosystem II D1 protein in Synechocystis sp. PCC6803. Photosynth. Res. 92, 315–325. Nakai, S., Inoue, Y., Hosomi, M., Murakami, A., 2000. Myriophyllum spicatumreleasing allelopathic polyphenols inhibiting growth blue-green algae Microcystis aeruginosa. Water Res. 34, 3026–3032. Nakai, S., Yamada, S., Hosomi, M., 2005. Anti-cyanobacterial fatty acids released from Myriophyllum spicatum. Hydrobiologia 543, 71–78. Nakai, S., Inoue, Y., Hosomi, M., 2001. Algal growth inhibition effects and inducement modes by plant-producing phenols. Water Res. 35, 1855–1859. Nishiyama, Y., Allakhverdiev, S.I., Yamamoto, H., Hayashi, H., Murata, N., 2004. Singlet oxygen inhibits the repair of Photosystem II by suppressing translation elongation of the D1 protein in Synechocystis sp. PCC 6803. Biochemistry 43, 11321–11330. Nübel, U., Garcia-Pichel, F., Muyzer, G., 1997. PCR primers to amplify 16S rRNA genes from cyanobacteria. Appl. Environ. Microbiol. 63, 3327–3332. Pearson, L.A., Neilan, B.A., 2008. The molecular genetics of cyanobacterial toxicity as a basis for monitoring water quality and public health risk. Curr. Opin. Biotech 19, 281–288. Rippka, R., Desrulles, J., Waterbury, J.B., Herdman, M., Stanier, R.Y., 1979. Generic assignment, strain histories and properties of pure cultures of cyanobacteria. J. Gen. Microbiol. 11, 1–61. Robert, J.M., Gu, M.B., 2004. Construction and characterization of novel dual stressresponsive bacterial biosensors. Biosens. Bioelectron. 19, 977–985. Saito, K.M., Matsumoto, T.S., Murakoshi, I., 1989. Inhibitory substances from Myriophyllum brasiliense on growth of blue-green algae. J. Nat. Prod. 52, 1221– 1226. Santos, P.M., Benndorf, D., Isabel, S.C., 2004. Insights into Pseudomonas putida KT2440 response to phenol-induced stress by quantitative proteomics. Proteomics 4, 2640–2652. Sivonen, K., Carmichael, W.W., Namikoshi, M., Rinehart, K.L., Dahlem, A.M., Niemela, S.I., 1990. Isolation and characterization of hepatotoxic microcystin homologs from the filamentous freshwater cyanobacterium Nostoc sp. strain 152. Appl. Environ. Microbiol. 56, 2650–2657. Smirnoff, N., 1993. The role of active oxygen in the response of plants to water deficit and desiccation. New Phytol. 125, 27–58. Spencer, C.M., Cai, Y., Martin, R., Gaffney, S.H., Goulding, P.N., Magnolato, D., Lilley, T.H., Haslam, E., 1988. Polyphenol complexation – some thoughts and observations. Phytochemistry 27, 2397–2409. Stork, T., Michel, K.P., Pistorius, E.K., Dietz, K.J., 2005. Bioinformatic analysis of the genomes of the cyanobacteria Synechocystis sp. PCC 6803 and Synechococcus elongatus PCC 7942 for the presence of peroxiredoxins and their transcript regulation under stress. J. Exp. Bot. 422, 3193–3206. Sundin, G.W., Weigand, M.R., 2007. The microbiology of mutability. FEMS Microbiol. Lett. 277, 11–20. Swarnamukhi, P.L., Sharma, S.K., Bajaj, P., Surolia, N., Surolia, A., Suguna, K., 2006. Crystal structure of dimeric FabZ of Plasmodium falciparum reveals conformational switching to active hexamers by peptide flips. FEBS Lett. 580, 2653–2660. Uchimaya, M., Mihara, M., 1978. Determination of malonaldehyde precursor in tissues by thiobarbituric acid test. Anal. Biochem. 86, 271–278. Urbach, E., Robertsin, D., Chisholm, S., 1992. Multiple evolutionary origins of prochlorophytes within the cyanobacterial radiation. Nature 355, 267–270. Valentine, J.S., Wertz, D.L., Lyons, T.J., Liou, L.L., Goto, J.J., Gralla, E.B., 1998. The dark side of dioxygen biochemistry. Curr. Opin. Chem. Biol. 2, 253–262. VanBogelen, R.A., Kelley, P.M., Neidhardt, F.C., 1987. Differential induction of heat shock, SOS, and oxidation stress regulons and accumulation of nucleotides in Escherichia coli. J. Bacteriol. 169, 26–32. Watanabe, M.F., Oishi, S., Watanabe, Y., Watanabe, M., 1986. Strong probability of lethal toxicity in the blue–green alga Microcystis viridis Lemmermann. J. Phycol. 22, 552–556. Wood, Z.A., Schroder, E., Robin, H.J., Poole, L.B., 2003. Structure, mechanism and regulation of peroxiredoxins. Trends Biochem. Sci. 28, 32–40. Zamocky, M., Furtmuller, P.G., Obinger, C., 2008. Evolution of catalases from bacteria to humans. Antioxid. Redox. Sign. 10, 1527–1548. Zavilgelsky, G.B., Kotova, V.Y., Manukhov, I.V., 2007. Action of 1, 1dimethylhydrazine on bacterial cells is determined by hydrogen peroxide. Mutat. Res. 634, 172–176.