FEMS Microbiology Ecology 25 (1998) 171^178 Light causes selection among two phycoerythrin-rich Synechococcus isolates from Lake Constance Christine Postius a; *, Ulrich Kenter b , Alexander Wacker a , Anneliese Ernst a , Peter Boëger a a Lehrstuhl fuër Physiologie und Biochemie der P£anzen, Universitaët Konstanz, D-78457 Konstanz, Germany b Limnologisches Institut, Universitaët Konstanz, D-78434 Konstanz, Germany Received 30 June 1997; revised 27 October 1997; accepted 30 October 1997 Abstract The phycoerythrin (PE)-rich unicellular cyanobacteria Synechococcus spp. strains BO 8808 and BO 9203, from the pelagic zone of Lake Constance, exhibited different responses when cultured under low light and light stress conditions. Under light stress caused by continuous illumination at elevated light intensity, strain BO 8808 ceased growth, the PE/chlorophyll ratio was slowly reduced and the zeaxanthin content was significantly decreased. By contrast, strain BO 9203 grew faster under high light compared to low light intensities. This strain responded to increased light by a rapid reduction of the PE/chlorophyll ratio while the zeaxanthin content remained constant. Both of these alterations may have protecting effects for BO 9203 against light toxicity. In mixtures of both strains, the predominance of the light-tolerant strain BO 9203 was demonstrated by restriction fragment length polymorphism of psbA genes under light stress conditions. Apparently, strain BO 9203, isolated from an algal bloom in the spring, can cope better with high light intensities than strain BO 8808, isolated in the autumn. z 1998 Federation of European Microbiological Societies. Published by Elsevier Science B.V. Keywords : Autotrophic picoplankton; Cyanobacteria ; Phycoerythrin ; Restriction fragment length polymorphism ; Synechococcus ; Zeaxanthin 1. Introduction Cyanobacteria are photoautotrophs which have developed a variety of strategies that enable them to respond adequately to changes in environmental conditions such as light and nutrient £uctuations. With this capability they are able to colonize nearly all ecosystems [1]. In spite of their widespread occur* Corresponding author. Tel.: +49 (7531) 882809; Fax: +49 (7531) 883042; E-mail: [email protected] rence and their signi¢cant contribution to overall primary production of marine and freshwater systems (see [2] for review), unicellular cyanobacteria of the Synechococcus type were observed in Lake Constance for the ¢rst time in 1986 [3]. Since then, their presence as part of the autotrophic picoplankton (APP) and their seasonal variation in numbers, biomass and production has been well documented [4,5]. As in some other prealpine lakes, the APP of this meso-eutrophic lake is dominated by phycoerythrin (PE)-rich cyanobacteria of the Synechococcus type. Over the course of several years we isolated 0168-6496 / 98 / $19.00 ß 1998 Federation of European Microbiological Societies. Published by Elsevier Science B.V. PII S 0 1 6 8 - 6 4 9 6 ( 9 7 ) 0 0 0 9 3 - 7 FEMSEC 878 5-2-98 172 C. Postius et al. / FEMS Microbiology Ecology 25 (1998) 171^178 18 unicellular PE-rich cyanobacterial strains from a single sampling site in the pelagic zone of Lake Constance. DNA characterization by RFLP (restriction fragment length polymorphism) of three psbA genes present in Synechococcus spp. revealed a high genetic diversity among these isolates, as eight of 18 isolates were shown to be genetically di¡erent [6,7]. Although obtained from di¡erent phases of the growth period of the year 1994, the other 10 isolates exhibited identical DNA fragment patterns, demonstrating the persistence of one strain in the pelagic zone during the course of one year [7]. Temporal abundance of genetically distinct strains may be due to di¡erential physiological responses to environmental changes. However, despite high genetic diversity, remarkable physiological di¡erences were only observed between di¡erent pigment types, i.e. when PE- and PC (phycocyanin)-rich isolates were compared under nutrient de¢ciency conditions (C. Postius, unpublished results). Among PE-rich isolates, two strains exhibited special structural features of the outer membrane: one of them had a highly glycosylated surface layer [8], the other one carried a permanent, thick slime layer (C. Postius, unpublished results). When grown under standard dim light culture conditions the other PE-rich strains exhibited no signi¢cant di¡erences in size, shape and composition of major pigments despite their genetic diversity [9]. Cyanobacterial strains may respond di¡erently when exposed to changing light and nutrient conditions [1,10]. Most remarkable is the alteration of the pigment composition, often described for PC-rich cyanobacteria. However, only few reports describe the impact of light on PE-rich unicellular cyanobacteria. In aquatic ecology, cyanobacteria are mainly described as organisms that prefer low light intensities [11]. However, mixing processes in the water column may lead to an exposure to high light intensities which may be lethal to these organisms [12,13]. In natural aquatic systems light intensity changes in various ways and on di¡erent time scales [14,15]. The shortest changes in light regime are caused by waveinduced `£icker e¡ects'. Variations of irradiance due to vertical mixing of the water column include intermediate, variable scales, plus major changes imposed by the diurnal rhythm and actual weather conditions [16]. Longer-term alterations result from seasonal changes and from changes in the trophic situation that a¡ect cell density and therefore light penetration through the water column [17,18]. Accordingly, photoacclimative changes in phytoplankton populations occur on time scales ranging between hours, months or even years, as in the case of eutrophication or oligotrophication situations [19]. Rapid responses to altered light conditions may be achieved by changes in cellular reactions, i.e. changes in pigment composition as often described for cyanobacteria [1,10]. On the other hand, long-term £uctuations of the light regime may lead to varying compositions of the population. The objective of this study was to compare two genetically di¡erent PE-rich Synechococcus strains with respect to growth and pigment composition under standard dim light culture conditions and under a light stress situation caused by continuous illumination at increased light intensity. DNA analysis was performed to demonstrate the selection of the better adapted organism under the two growth conditions in mixed cultures. 2. Materials and methods 2.1. Isolation and culture conditions Samples of Synechococcus spp. strains BO 8808 and BO 9203 (hereafter referred to as BO 8808 and BO 9203) were obtained from the pelagic zone (0^8 m) of the northwestern part of Lake Constance, the ë berlinger See', at the site of maximum depth (147 `U m). BO 8808 was isolated in early autumn of the year 1988 by plating 50 Wl of a mixed water sample from the pelagic zone on modi¢ed BG11 medium [20] solidi¢ed with 1.5% agar (w/v). Single colonies were inoculated in liquid medium and cultivated as described elsewhere [7,21]. Strain BO 9203 was obtained in the spring of 1992 by enrichment upon prolonged maintenance at 20 WE m32 s31 green light. Cyanobacterial cultures were maintained, under shaking, at 23³C in liquid cultures (40 ml) in BG11 medium with lowered nitrate supply (5 mM). The illumination was 10^30 WE m32 s31 for 12 day hours and was reduced to approximately 1 WE m32 s31 for a 12-h dark interval. These conditions are referred to as low or dim light conditions. For exposure to light FEMSEC 878 5-2-98 C. Postius et al. / FEMS Microbiology Ecology 25 (1998) 171^178 173 stress conditions, also referred to as high light conditions, 250-ml cultures were illuminated continuously with 100 WE m32 s31 white light. Mixed cultures, exposed to light stress or dim light, were started with the same inoculum for both strains (¢nal OD750 = 0.1) and maintained at the indicated conditions for approximately 3 weeks. 2.2. Pigment determination by absorption measurements Absorption measurements of whole cells and clear solutions were carried out with a U 2000 spectrophotometer (Hitachi, Tokyo, Japan). In vivo absorption spectra of whole cells were recorded with a UV 3000 double-beam spectrophotometer (Shimadzu, Kyoto, Japan). For chlorophyll a (chl a) determination, cells (1 ml) were extracted with 90% (v/v) methanol for 10 min at 60³C, followed by centrifugation at 10 000Ug for 5 min. The chlorophyll a content was calculated from the absorbance of the methanolic extract at 665 nm [22]. The PE/chl a ratio was estimated by measuring absorption of whole cells at 568 nm for PE content and 668 nm for chl a content, and calculating the ratio from these data. Total carotenoid content was calculated by absorption at 480 nm of whole cells. The L-carotene content was assumed to change proportionally to the chlorophyll a content [23]. The relative zeaxanthin content was calculated from the di¡erence of the total carotenoid and the Lcarotene contents. The data calculated from absorption measurements were validated by the determination of pigments using HPLC analysis. Absorption Fig. 2. Chlorophyll a content of cells (Wg/OD750 ) of Synechococcus spp. strains BO 8808 (a) and BO 9203 (b) at low light and high light conditions. measurements for growth and pigment content were performed in three independent experiments. The data of a typical experiment are presented. 2.3. Fluorimetric measurements After gentle resuspension of cells in an ultrasonic cleaning bath (Labson 200, Bender and Hobein, Germany) £uorescence of pigments of whole cells was measured at room temperature in a 1-cm cuvette using a SM-25 £uorimeter (Kontron, Milan, Italy) with a slit width setting of 10 nm for excitation and emission wavelengths. Fluorescence of pigments and energy transfer between pigments were recorded at the following wavelength settings for excitation (ex) and emission (em): chl a: ex 440 nm, em 680 nm; PE: ex 550 nm, em 575 nm; PE to allophycocyanin/PSII: ex 550 nm, em 665 nm; PC to allophycocyanin/PSII: ex 620 nm, em 665 nm; for spectra of the native pigment complexes, see [24]. 2.4. HPLC analyses Fig. 1. Growth of Synechococcus spp. strains BO 8808 (a) and BO 9203 (b) measured by absorption at 750 nm of cultures growing at low light (a 12/12-h light/dark regime of 10/1 WE m32 s31 ) and high light (100 WE m32 s31 , continuously illuminated) conditions. For HPLC analyses, cultures were ¢ltered on a Whatman GF/F ¢lter and pigments were extracted in 95% acetone/5% water (v/v). Carotenoids were separated by reversed-phase HPLC (Hewlett-Packard Model 1050) using a 250-mm column packed with 5 Wm particles of Licosphere 100 RP 18. The pigments were eluted by a gradient composed of solvent A (70% methanol, 30% H2 O and 0.625% tetraethylammonium acetate; v/v/w) and solvent B (60% methanol and 40% acetone; v/v) with the initial proportion of A:B being 50:50 and the ¢nal proportion FEMSEC 878 5-2-98 174 C. Postius et al. / FEMS Microbiology Ecology 25 (1998) 171^178 light conditions (Fig. 1b). Initially, BO 8808 also grew better at increased light intensities, but 5 days after changing from dim light to high light conditions growth stopped and optical density remained at a constant level (Fig. 1a). 3.2. Changes in pigment contents Fig. 3. Phycoerythrin/chlorophyll a ratio of Synechococcus spp. strains BO 8808 (a) and BO 9203 (b) at low light and high light conditions measured by absorption of whole cells at 568 nm and 668 nm, respectively. 99.5:0.5. Identi¢cation and quanti¢cation of pigments was performed using a Waters diode array detector (Model 991; Waters, Millipore Corporation, Milford, MA). 2.5. DNA preparation and RFLP of psbA genes DNA was isolated from 250 ml of 2^3-week-old cultures. For preparation of DNA from freshly mixed cell cultures, 125 ml of both cultures were adjusted to the same cell density (OD750 =1.0), mixed and immediately harvested for DNA isolation. DNA was isolated as described by Brass et al. [24]. For RFLP analysis the DNA was digested with the restriction endonuclease BamHI and analyzed by Southern blot hybridization (hybridization temperature 50³C) using a probe derived from an internal BstEII fragment of psbA1. This gene, cloned in pDAN1, encodes the D1 protein of photosystem II of Synechococcus sp. PCC 7942 ([25], for further details see references [6,7]). Chlorophyll a content of cells grown under low light conditions decreased slightly after inoculation but recovered after one generation (Fig. 2). Transfer to increased, continuous illumination caused a stronger decline in chl a/OD750 indicating that strains initiated a major photoacclimation process (Figs. 2 and 4). Strain BO 9203 started to recover after one generation as indicated by a slow increase in chl a/OD750 (Fig. 2b) and a net increase of chl a/ml (data not shown). However, in BO 8808 degradation of chlorophyll a continued even after cell growth was arrested (compare Figs. 1a and 2a). After 2 weeks of cultivation under stress conditions BO 8808 exhibited a threefold lower chlorophyll content than BO 9203. Changes in phycobiliprotein content were recorded as the absorption ratio of PE/chl a (Fig. 3a,b). BO 9203 showed a rapid response, starting immediately after the cultures were transferred to the stress situation. The reduction of the PE/chl a ratio of BO 8808 was much slower and less distinct than that of BO 9203. Fluorescence emission intensities of PE (ex 550/em 575) and chlorophyll a (ex 440/em 680) revealed a distinct decrease of the emission of PE for BO 9203 at 100 WE m32 s31 (Fig. 4b), while for BO 8808 this decrease was retarded and less than for BO 3. Results 3.1. Changes in growth The isolates were routinely grown at 10 WE m32 s with dark intervals of 12 h. Under these dim light conditions, growth of BO 9203 was slightly slower than that of BO 8808 (Fig. 1a,b). Under high light conditions (100 WE m32 s31 , continuous illumination), BO 9203 grew faster than under low 31 Fig. 4. Fluorescence emission (arbitrary units) of PE (ex 550/em 575) and chlorophyll a (ex 440/em 680) of Synechococcus spp. strains BO 8808 (a) and BO 9203 (b) at low light and high light conditions. FEMSEC 878 5-2-98 C. Postius et al. / FEMS Microbiology Ecology 25 (1998) 171^178 175 9203 (Fig. 4a). When exposed to high light intensities, the L-carotene content decreased in both strains (data not shown), while the zeaxanthin content showed a di¡erent response in the compared strains (Fig. 5a,b). For BO 9203, the cellular concentration of zeaxanthin increased slightly under dim light but remained constant under high light intensities. On the other hand, the zeaxanthin content of strain BO 8808 remained constant at low light conditions, but decreased continuously at high light intensities, indicating reduction of zeaxanthin under stress conditions for this strain. 3.3. DNA analysis of unialgal and mixed cell cultures by RFLP of psbA genes The isolates BO 8808 and BO 9203 exhibited a distinct restriction fragment pattern when probed with the internal BstEII fragment of the psbAI gene from Synechococcus PCC 7942. This probe recognizes three homologous genes in the PC-rich parent strain represented by three labeled fragments in a BamHI digest. The PE-rich isolates BO 8808 and BO 9203 exhibited characteristic patterns, each consisting of four fragments (Fig. 6). When the DNA was isolated immediately after mixing the isolates, characteristic fragments of both strains were visible. Cultivating mixed cultures for 3 weeks under dim light conditions (30 WE m32 s31 ) caused prevalence of the characteristic fragment pattern of BO 8808. In contrast, RFLP analyses from mixed strains which had been cultivated for 3 weeks under light stress Fig. 6. DNA analysis (RFLP) of pure and mixed cultures of Synechococcus spp. strains BO 8808 and BO 9203. DNA was digested with BamHI and probed with an internal fragment of psbA1 from Synechococcus sp. PCC 7942 as mentioned in Section 2. The position of DNA molecular weight markers (M) is indicated. On top of the gel the source of the DNA (strain numbers) are indicated. Culture conditions under which cells were maintained: lanes 1 and 2: pure cultures cultivated under 10 WE m32 s31 ; lane 3: mixed cultures at the start of cultivation ; lane 4: mixed cultures after 3 weeks under low light ; lane 5: mixed cultures after 3 weeks under light stress. conditions revealed the characteristic pattern of BO 9203, the strain which showed superior growth under these conditions. By these experimental procedures a selection of the ¢ttest strain occurred in mixed cultures, according to the environmental conditions. 4. Discussion Fig. 5. Relative zeaxanthin content of Synechococcus spp. strains BO 8808 (a) and BO 9203 (b) at low light and high light culture conditions. Values represent the di¡erence of total carotenoid content and L-carotene content. Symbols R/S (10 WE m32 s31 ) and O/P (100 WE m32 s31 ) mark the relative pigment contents detected by HPLC analysis of the same data set. This study shows that di¡erent light conditions lead to a selection of di¡erent strains from mixed cultures. The predominance of strain Synechococcus BO 9203 at high light conditions was caused by a higher growth rate induced by increased light intensity, while BO 8808 grew better under low light conditions (Fig. 1). After transfer to high light, both strains initiated an acclimation process during which the amount of photosynthetic membranes was reduced [26]. In BO 9203 loss of chlorophyll a was accompanied by a rapid decomposition of phycobilisomes (Fig. 4b). This destruction of the light-har- FEMSEC 878 5-2-98 176 C. Postius et al. / FEMS Microbiology Ecology 25 (1998) 171^178 vesting system may limit the phototoxic e¡ects of high light. Similar acclimation processes were observed in PC-rich and marine PE-rich Synechococcus isolates [26,27]. On the other hand, in strain BO 8808 delayed reduction of PE may lead to sustained phototoxicity and to progressive destruction of chlorophyll a and other cell components (Figs. 2a and 4a). In particular, the decrease of zeaxanthin under light stress conditions may limit the photoprotective e¡ect of this carotenoid located primarily in the cytoplasmic or outer cell wall membrane [23]. Maintenance of a high zeaxanthin level in strain BO 9203 exposed to light stress situations may be bene¢cial to these cells since zeaxanthin is thought to quench oxygen radicals generated by the photochemically non-productive excitation of chlorophyll molecules [28]. With respect to destruction of PE and maintenance of zeaxanthin, strain BO 9203 resembled the highlight-tolerant marine Synechococcus strain WH 7803 [23,26]. To our knowledge, a dim-light-adjusted Synechococcus strain comparable to strain BO 8808 has not been described before. The apparent light stress experienced by this strain may have been enhanced by other factors. In particular, we did not examine whether the lack of a dark period under high light conditions had an additional adverse e¡ect on this strain. The di¡erent reactions of strains compared under laboratory conditions may be relevant for population dynamics in natural environments. Within a picoplankton community Lindell and Post [29] described a seasonal succession of Prochlorococcus, eukaryotic algae and Synechococcus spp. populations in the Gulf of Aqaba. In the pelagic zone of Lake Constance, Weisse and Kenter [4] studied the succession of APP, dominated by PE-rich Synechococcus spp. Over the course of several years, the abundance of these picocyanobacteria suggested spring and summer populations in this environment. Several possibilities may account for £uctuations in population dynamics of those picocyanobacteria. The presence of di¡erent predators and selective predation may cause a change in the picoplankton population during the growth season [30,31]. The £agellate Paraphysomonas sp., isolated from Lake Constance, was shown to graze selectively on Synechococcus spp. from the same environment [32]. Alternatively, the composition of cyanobacterial populations blooming in spring may depend on strategies of the organisms to survive winter. Those organisms surviving in highest numbers may play an important role as inocula to start the growing season in spring. High levels of viable picocyanobacteria were found in the aphotic bottom sediment of Lake Biwa, which are likely to seed photoautotrophic picoplankton blooms occurring in these waters [33]. In the Baltic Sea even cyanobacteria trapped in the ice interior during winter are thought to be important contributors to the spring cyanobacterial community [34]. However, the survival strategies of APP in Lake Constance are not yet known. Another possibility is that changed environmental conditions may cause dominance of the better adapted organism. In Lake Arcas the contribution and abundance of speci¢c cyanobacterial populations can be explained by the interplay of light regime and presence of sul¢de as the most determinant ecological parameters [35]. In Lake Constance we demonstrated high genetic diversity among Synechococcus strains isolated from a single site, and in several cases even from a single sample [7], suggesting a mixed population. Intermittent light changes, as they occur in natural waters, seem to be tolerated by most of these picocyanobacteria. However, seasonally changing parameters, like incident light, may exert stress upon some species and may result in dominance of those strains that cope better with the altered situation. The light-tolerant strain BO 9203 was isolated from a sample collected in the spring while strain BO 8808, sensitive to high light intensities, was isolated in the autumn [7], when light stress is less likely to occur. However, the assumed seasonal population dynamics, that may be due to a varying light regime, will have to be con¢rmed `in situ' by speci¢c DNA hybridization. Acknowledgments This project was supported by the Deutsche Forschungsgemeinschaft by its Sonderforschungsbereich 248 `Sto¡haushalt des Bodensees'. J. Hirschberg, Jerusalem, supplied the plasmid pDAN1, which is gratefully acknowledged. We thank R. Grimm and C. Gebauer for technical assistance in DNA and HPLC analysis, respectively. FEMSEC 878 5-2-98 C. Postius et al. / FEMS Microbiology Ecology 25 (1998) 171^178 References [1] Tandeau de Marsac, N. and Houmard, J. (1993) Adaptation of cyanobacteria to environmental stimuli: new steps towards molecular mechanisms. FEMS Microbiol. Rev. 104, 119^ 190. [2] Stockner, J.G. and Antia, N.J. (1986) Algal picoplankton from marine and freshwater ecosystems: a multidisciplinary perspective. Can. J. Fish. Aquat. Sci. 43, 2472^2503. [3] Weisse, T. (1988) Dynamics of autotrophic picoplankton in Lake Constance. J. Plankton Res. 10, 1179^1188. [4] Weisse, T. and Kenter, U. (1991) Ecological characteristics of autotrophic picoplankton in a prealpine lake. Int. Rev. Ges. Hydrobiol. 76, 493^504. [5] Weisse, T. and Schweizer, A. (1991) Seasonal and interannual variation of autotrophic picoplankton in a large prealpine lake (Lake Constance). Verh. Int. Limnol. 24, 821^825. [6] Ernst, A., Marschall, P. and Postius, C. (1995) Genetic diversity among Synechococcus spp. (cyanobacteria) isolated from the pelagial of Lake Constance. FEMS Microbiol. Ecol. 17, 197^204. [7] Postius, C., Ernst, A., Kenter, U. and Boëger, P. (1996) Persistence and genetic diversity among strains of phycoerythrin-rich cyanobacteria from the picoplankton of Lake Constance. J. Plankton Res. 18, 1159^1166. [8] Ernst, A., Postius, C. and Boëger, P. (1996) Glycosylated surface proteins re£ect genetic diversity among Synechococcus spp. of Lake Constance. Arch. Hydrobiol. Spec. Issues Adv. Limnol. 48, 1^6. [9] Ernst, A., Sandmann, G., Postius, C., Brass, S., Kenter, U. and Boëger, P. (1992) Cyanobacterial picoplankton from Lake Constance: II. Classi¢cation of isolates by cell morphology and pigmentation composition. Bot. Acta 105, 161^167. [10] Grossman, A.R., Schaefer, M.R., Chiang, G.G. and Collier, J.L. (1994) The responses of cyanobacteria to environmental conditions: Light and nutrients. In: The Molecular Biology of Cyanobacteria (Bryant D.A., Ed.), pp. 641^675. Kluwer Academic, Dordrecht. [11] Van Liere, L. and Walsby, A.E. (1982) Interactions of cyanobacteria with light.In : The Biology of Cyanobacteria (Carr, N.G. and Whitton, B.A., Eds), pp. 9^45. Blackwell, Oxford. [12] Elo¡, J.N., Steinitz, Y. and Shilo, M. (1976) Photooxidation of cyanobacteria in natural conditions. Appl. Environ. Microbiol. 31, 119^126. [13] Falkowski, P.G. (1984) Physiological response of phytoplankton to natural light regimes. J. Plankton Res. 6, 295^ 307. [14] Schubert, H., Matthijs, H.C.P., Mur, L.R. and Schiever, U. (1995) Blooming of cyanobacteria in turbulent water with steep light gradients: The e¡ect of intermittent light and dark periods on the oxygen evolution capacity of Synechocystis sp. PCC 6803. FEMS Microbiol. Ecol. 18, 237^245. [15] Fisher, T., Minnaard, J. and Dubinsky, Z. (1996) Photoacclimation in the marine alga Nannochloropsis sp. (Eustigmatophyte) : a kinetic study. J. Plankton Res. 18, 1797^1818. [16] Preèzelin, B.B., Tilzer, M.M., Scho¢eld, O. and Haese, C. (1991) The control of the production process of phytoplank- [17] [18] [19] [20] [21] [22] [23] [24] [25] [26] [27] [28] [29] [30] [31] 177 ton by the physical structure of the aquatic environment with special reference to its optical properties. Aquat. Sci. 53, 1015^1621. SÖndergaard, M. (1991) Phototrophic picoplankton in temperate lakes: seasonal abundance and importance along a trophic gradient. Int. Rev. Ges. Hydrobiol. 76, 505^522. Callieri, C., Amicucci, E., Bertoni, R. and Voëroës, L. (1996) Fluorometric characterization of two picocyanobacteria strains from lakes of di¡erent underwater light quality. Int. Rev. Ges. Hydrobiol. 81, 13^23. Gaedke, U. and Schweizer, A. (1993) The ¢rst decade of oligotrophication in Lake Constance. I. The response of phytoplankton biomass and cell size. Oecologia 93, 268^275. Rippka, R., Deruelles, J., Waterbury, J.B., Herdman, M. and Stanier, R. (1979) Generic assignments, strain histories and properties of pure cultures of cyanobacteria. J. Gen. Microbiol. 111, 1^61. Ernst, A. (1991) Cyanobacterial picoplankton from Lake Constance : I. Isolation by £uorescence characteristics. J. Plankton Res. 13, 1307^1312. Tandeau de Marsac, N. and Houmard, J. (1988) Complementary adaptation : physiological conditions and action spectra. Methods Enzymol. 167, 318^328. Kana, T.M., Glibert, P.M., Goericke, R. and Welschmeyer, N.A. (1988) Zeaxanthin and L-carotene in Synechococcus WH7803 respond di¡erently to irradiance. Limnol. Oceanogr. 3, 1623^1627. Brass, S., Westermann, M., Ernst, E., Reuter, W., Wehrmeyer, W. and Boëger (1994) Utilization of light for nitrogen ¢xation by a new Synechocystis strain is extended by its low photosynthetic e¤ciency. Appl. Environ. Microbiol. 60, 2575^ 2583. Hirschberg, J., Ohad, N., Pecker, I. and Rahat, A. (1987) Isolation and characterization of herbicide resistant mutants in the cyanobacterium Synechococcus R2. Z. Naturforsch. 42 C, 758^761. Kana, T.M. and Glibert, P.M. (1987) E¡ect of irradiances up to 2000 WE m32 s31 on marine Synechococcus WH7803-II. Photosynthetic responses and mechanisms. Deep-Sea Res. 34, 497^516. Loënneborg, A., Lind, L.K., Kalla, S.R., Gustafsson, P. and ë quist, G. (1985) Acclimation Processes in the light-harvestO ing system of the cyanobacterium Anacystis nidulans following a light shift from white to red light. Plant Physiol. 78, 110^ 114. Demmig-Adams, B. (1990) Carotenoids and photoprotection in plants : A role for the xanthophyll zeaxanthin. Biochim. Biophys. Acta 1020, 1^24. Lindell, D. and Post, A.F. (1995) Ultraphytoplankton succession is triggered by deep winter mixing in the Gulf of Aqaba (Eilat), Red Sea. Limnol. Oceanogr. 40, 1130^1141. Perez, M.T., Dolan, J.R., Rassoulzadegan, F. and Mostajir, B. (1996) Predation on marine picoplankton populations examined with an `add-in' approach. J. Plankton Res. 18, 635^ 641. S|émek, K., Vrba, J., Pernthaler, J., Posch, T., Hartman, P., Nedoma, J. and Psenner, R. (1997) Morphological and com- FEMSEC 878 5-2-98 178 C. Postius et al. / FEMS Microbiology Ecology 25 (1998) 171^178 positional shifts in an experimental bacterial community in£uenced by protists with contrasting feeding modes. Appl. Environ. Microbiol. 63, 587^595. [32] Muëller, H. (1996) Selective feeding of a freshwater chrysomonad, Paraphysomonas sp., on chroococcoid cyanobacteria and nano£agellates. Arch. Hydrobiol. Spec. Issues Adv. Limnol. 48, 63^71. [33] Eguchi, M., Oketa, T., Miyamoto, N., Maeda, H. and Kawai, A. (1996) occurrence of viable phototrophic picoplankton in the aphotic zone of Lake Biwa, Japan. J. Plankton Res. 18, 539^550. [34] Laamanen, M. (1996) Cyanoprokaryotes in the Baltic Sea ice and winter plankton. Arch. Hydrobiol. Suppl. Algol. Stud. 83, 423^433. [35] Camacho, A., Garcia-Pichel, F., Vicente, E. and Castenholz, R.W. (1996) Adaptation to sul¢de and to the underwater light ¢eld in three cyanobacterial isolates from Lake Arcas (Spain). FEMS Microbiol. Ecol. 21, 293^301. FEMSEC 878 5-2-98
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