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Applied and Environmental Microbiology, May 2007, p. 2976-2981, Vol. 73, No. 9
0099-2240/07/$08.00+0 doi:10.1128/AEM.02449-06
Copyright © 2007, American Society for Microbiology. All Rights Reserved.

Plymouth Marine Laboratory, Prospect Place, The Hoe, Plymouth PL1 3DH, United Kingdom,1 School of Biological Sciences, University of Plymouth, Drake Circus, Plymouth PL4 8AA, United Kingdom,2 Bigelow Laboratory for Ocean Sciences, 180 McKown Point Road, P.O. Box 475, W. Boothbay Harbor, Maine 04575-04753
Received 19 October 2006/ Accepted 28 February 2007
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Reef-building corals associate with a diverse array of eukaryotic and prokaryotic microbes. The coral colony has been modeled as a holobiont comprising multispecies mutualisms consisting of the coral animal, endosymbiotic dinoflagellates (zooxanthellae), bacteria, fungi, protozoans, endolithic algae, and other unknown components (27). Disruption of any of these components may cause physiological changes that result in coral disease or death.
Zooxanthellae (genus Symbiodinium) are now known to comprise numerous clades (2). Zooxanthellae form a symbiotic relationship with many Cnidaria species and are by far the best-understood microbial associates of corals, and they have a clearly beneficial relationship with the coral. They release photosynthetic products to their hosts, providing an important source of organic carbon and nitrogen for host metabolism, growth, and reproduction (12, 24, 40). The symbiosis with zooxanthellae is believed to explain the success of reef-building corals in nutrient-poor tropical seas (15). Disruption of the zooxanthella-host symbiosis (bleaching) can lead to expulsion of zooxanthellae from the host and/or a decrease in the amount of the zooxanthella photosynthetic pigment (15, 18). Zooxanthellae have been shown to undergo necrosis, apoptosis, and lysis during bleaching (4, 31). The expulsion of Symbiodinium cells may help corals adapt to changing environmental conditions by allowing symbiont populations to redistribute themselves (3, 10 ). If the symbiont-host relationship is not recovered, the coral does not survive (33). It has been argued that the random mosaic patterns of bleaching are difficult to attribute to the effect of temperature stress alone as neighboring regions of a colony must be exposed to the same conditions (16). One explanation for the patchy spatial distribution of coral bleaching involves localized infections. Bacterial infection by Vibrio sp. has been shown to be responsible for some types of coral bleaching (5, 28, 37). Given the great abundance of viruses in marine systems, in which concentrations reach >108 particles ml1 (6, 44), it is likely that viruses are also involved as agents of coral disease (11), and involvement of viruses in the coral bleaching process must be considered. It has been established that the majority of marine viruses infect bacteria, but viruses that infect eukaryotic algae have also been shown to be abundant in the marine environment (8). Virus-like particles (VLPs) have been found in cells of about 50 different algal species representing nearly all major algal classes (26, 38 ), and evidence suggests that viruses play a significant role in the population dynamics and community composition of marine phytoplankton (8, 22, 29, 32). Despite this, there have been relatively few reports on viruses of dinoflagellates (14, 30, 35) and fewer still on the presence of viruses in zooxanthellae. Previous studies in our laboratory have shown that zooxanthellae and corals produce VLPs when they are exposed to stress and elevated temperatures (11, 42, 43), suggesting that zooxanthellae harbor latent viruses. In order to determine whether VLPs are induced by exposure of the zooxanthellae to UV light, we utilized Symbiodinium sp. cultured in vitro to simplify the complexity found in whole organisms containing symbionts.
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Experimental treatments.
Triplicate exponentially growing cultures (50 ml; approximately 105 cells ml1) were exposed for 2 min in open petri dishes to UV light (254 nm) from a Chromato-Vue transilluminator (model TM-20) which was placed upside down 12 cm above the petri dishes to allow direct radiation. After exposure, the cultures were transferred back into 50-ml flasks and maintained at 26°C with illumination using a cycle consisting of 16 of light and 8 h of darkness. Samples used for enumeration of zooxanthellae and VLPs were collected daily for 1 week. Zooxanthellae were enumerated immediately, and 1-ml aliquots were fixed in 0.5% glutaraldehyde, stored at 4°C for 30 min, snap frozen in liquid nitrogen, and stored at 80°C until they were processed for enumeration of VLPs and bacteria.
Enumeration of zooxanthellae, VLPs, and bacteria by analytical flow cytometry (AFC).
All analyses were performed with a Becton Dickinson FACScan flow cytometer using the Cellquest software. For enumeration of live zooxanthellae, undiluted samples were examined for 2 min using a high flow rate (ca. 50 to 70 µl min1) with the discriminator set on red fluorescence. For enumeration of VLPs and bacteria, counting was performed using fixed samples diluted 1:10 to 1:1,000 in TE buffer (10 mM Tris, 1 mM EDTA; pH 8.0), filtered with a 50-kDa filter using tangential flow filtration (Vivaflow flip flow), and stained for 10 to 15 min at 80°C with a 105 dilution of SYBR green I stain (Molecular Probes). The samples were analyzed for 2 min at a low flow rate (ca. 30 µl min1) with the discriminator set on green fluorescence (23). VLPs and bacteria were enumerated using plots of side scatter (SSC) versus green fluorescence. All 16 zooxanthella strains were screened and exhibited differential sensitivity to UV induction. Strain CCMP 2465 exhibited the strongest response and was therefore utilized for further assessment.
TEM.
Samples potentially containing VLPs were filtered through 0.45-µm filter units (Whatman) with a BD Plastipak sterile 10-ml syringe to remove debris and large cells. Aliquots were fixed in 0.5% glutaraldehyde, stored at 4°C for 30 min, and snap frozen in liquid nitrogen. "Spot" grids were prepared by placing grids onto 15 to 30 µl of a fixed suspension for 30 min. The excess liquid was removed with filter paper, and each preparation was negatively stained with uranyl acetate (2% [wt/vol] in water). For preparation of thin sections, UV-induced zooxanthellae were pelleted by centrifugation at 14,000 rpm in 1.5-ml Eppendorf tubes for 1 min. The pellets were resuspended, washed, and repelleted twice in filtered seawater (pore size, 0.2 µm). Molten agar (2% Fischer agar in distilled H2O; 0.5 ml) was added to each washed pellet and allowed to set; the excess agar was trimmed from the agar plugs. A 4% osmium tetroxide solution was mixed 1:1 with filtered seawater and added to cover the agar plugs. The preparations were left for 1 h at room temperature, and this was followed by two washes in filtered seawater (pore size, 0.2 µm), dehydration with a graded ethanol series, and infiltration with Spurr's resin in preshaped molds. Dried (48 h, 35°C) blocks were mounted and cut into sections that were 70 to 80 nm thick with a Reichert-Jung Ultracut microtome; the sections were floated onto transmission electron microscopy (TEM) grids, stained with 2% uranyl acetate in 70% ethanol (15 min), washed in double-distilled H2O, stained with Reynolds lead citrate for 15 min, and then rinsed in double-distilled H2O. Prepared grids and thin sections were examined with a JEOL 200 CX TEM (magnification, 80 to 600,000) at 160 kV. Photographs were taken at magnifications between x5,000 and x50,000.
Concentration of VLPs.
Zooxanthellae were grown to a density of ca. 105 cells ml1 in 3 liters of ASP-8A medium and exposed to UV light (254 nm) for 2 min in open petri dishes. VLPs were isolated from the growth media 96 h after exposure to UV. Debris, bacteria, and algal cells were removed by filtration though 0.45-µm-pore size, 47-mm-diameter filters (PALL Corp.). VLPs in the supernatant were concentrated by tangential flow filtration (Vivaflow flip flow) with a 50-kDa cutoff to obtain ca. 50 ml. Further concentration to ca. 3 ml was accomplished by ultracentrifugation with a Beckman L8-M at 100,000 x g for 2 h. VLPs were further purified and concentrated on a CsCl gradient prepared with CsCl in TE buffer at densities of 1.0, 1.2, 1.4, and 1.6 g cm3, and the pelleted VLPs were added to the 1.0-g cm3 layer. This preparation was then centrifuged at 100,000 x g for 2 h at 20°C, with the deceleration set at 8. A translucent white band was removed by piercing the ultracentrifuge tube just below the band, which allowed aliquots to be separated. Aliquots were dialyzed (Fisher; diameter, 0.32 mm; 12- to 14-kDa molecular-mass cutoff) overnight against 1 liter of TE buffer at 4°C, and the TE buffer was changed twice in this time. The dialyzed VLP concentrate was stored at 4°C until it was analyzed.
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FIG. 1. AFC analysis of VLPs induced following UV treatment of zooxanthella cultures. (A) AFC analysis of control culture of zooxanthellae, showing bacteria (cultures were nonaxenic). (B) AFC analysis of UV-treated culture (after 96 h), showing a new VLP group with high SSC (indicated by arrow). (C) CsCl gradient of the VLPs with a translucent white band at ca. 1.25 g cm3. (D) AFC analysis of concentrated VLPs taken from the CsCl gradient, showing the presence of the high-SSC VLP group.
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FIG. 2. (A) Growth curves showing numbers of cells of zooxanthella strain CCMP 2465 ml1 in control cultures ( ) and UV-treated cultures (), together with the numbers of the high-SSC VLPs ml1 in the unirradiated control cultures ( ) and the UV-treated cultures ( ). (B) Concentrations of bacteria in the control cultures ( ) and the UV-treated cultures ( ), together with the numbers of bacteriophage particles ml1 (106) in the control cultures ( ) and the UV-treated cultures ( ). The error bars indicate the standard errors for measurements from triplicate cultures.
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Identification of VLPs.
After induction free VLPs in the UV-treated supernatants and concentrates were observed by TEM as long flexible filaments that were 2 to 3 µm long and approximately 30 nm wide (Fig. 3). In VLPs purified by CsCl gradient centrifugation there was an increase in the density of the filamentous VLPs after concentration (3 x 107 VLPs ml1) (Fig. 3B and E). Thin sections of UV-treated zooxanthellae revealed pockets of filamentous VLPs with similar morphology in the cytoplasm on the periphery of zooxanthella cells (Fig. 4); filamentous VLPs were not seen in controls. The incidence of VLPs observed in the thin sections increased markedly between 39 and 46 h postinduction compared to the incidence in noninduced controls (in which no filaments were observed). The presence of intracellular VLPs provides further evidence that the particles observed were actually infecting the zooxanthellae and not the bacteria present in the cultures. Therefore, we designated the new group of VLPs "zooxanthella filamentous virus 1" (ZFV1).
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FIG. 3. TEM images showing the morphology of the new VLP, ZFV1. The filamentous VLP is ca. 2 to 3 µm long. (A, C, D, and F) Images from spot grids containing unconcentrated lysate. Scale bars = 1 µm. (B and E) Images of VLPs concentrated on a CsCl gradient (shown in Fig. 1C). Scale bars = 200 nm.
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FIG. 4. TEM images showing the presence of filamentous VLPs in thin sections of zooxanthellae prepared 39 h (A and B) and 46 h (C and D) after induction with UV light. Scale bars = 3 µm (A), 200 nm (B), 2 µm (C), and 300 nm (D). The box in panel A indicates the area shown in panel B, and the box in panel C indicates the area shown in panel D. Chl, chloroplast; Nu, nucleus; Li, lipid vacuole.
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Implications for the mechanism of coral bleaching.
Wilson et al. (43) first suggested that zooxanthellae may harbor a latent infection, after showing that VLPs were present in zooxanthellae of thermally stressed anemones and that isolated VLPs could reinfect zooxanthellae. Further studies have shown that VLPs are present in three species of tropical coral (11). While the hosts of the numerous VLPs remain unknown, the abundance of VLPs and their close association with corals and the symbiotic zooxanthellae is evident. A variety of VLP forms have been observed, and while most of VLPs the are hexagonal, it is notable that a filamentous VLP (up to 3 µm long) whose morphology is similar to that of ZFV1 has been observed in seawater following exposure of the coral Acropora formosa to heat stress (11). Although in our experiments we utilized nonaxenic cultures, our results clearly indicate that zooxanthellae contain a latent virus that is induced by UV treatment, leading to the lysis of the zooxanthellae. Extrapolation from this virus-host interaction and its effects on zooxanthella viability provides a novel link to the impact of latent infection on symbiotic dinoflagellates and the subsequent disruption of reef ecosystems. If stress-induced viral induction in zooxanthellae occurs in the natural reef environment, the presence of this new group of filamentous VLPs is clearly important.
W.H.W. was supported through the NERC-funded core strategic research program of the Plymouth Marine Laboratory.
Published ahead of print on 9 March 2007. ![]()
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