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Synechococcus, some of which differ genetically and physiologically and display different environmental distribution patterns, are found in high concentrations in coastal waters (Scanlan D J, 2002; Waterbury J B, 1986). It has been estimated that in coastal waters, 80% of Synechococcus cells may encounter infectious cyanophage particles each day (Suttle C A, 1994). Although many Synechococcus isolated from coastal waters are resistant to cyanophages, a large number of cyanophages have been successfully isolated from different coastal environments (Suttle C A, 1994; Waterbury J B, 1993).
Cyanophages are viruses that can infect Synechococcus sp. and other prokaryotic algae. The isolation and characterization of cyanophages infecting marine Synechococcus strains began in the 1990s (Suttle C A, 1993; Waterbury J B, 1993; Wilson W H, 1993). Five marine cyanophages propagated on Synechococcus sp. strain WH7803 were isolated by Waterbury and Valois from different oceanographic areas, including open ocean and coastal waters (Waterbuty J B, 1986; Waterbury J B, 1993). Representatives of all three families of tailed phages were found among the seven Synechococcus phages isolated by Suttle, Chan and Wilson (Suttle C A, 1993; Wilson W H, 1993). The diversity of cyanophages in the environment is substantial, and many new cyanophages have been discovered over the past decade (Prangishvili D, 2006; Suttle C A, 2007; Van Etten J L, 2010). However, metagenomic data show that more than 70% of the genes in the oceanic viral fraction cannot be associated with known viruses, indicating that a substantial amount of viral diversity remains to be identified (Angly F E, 2006; Bench S R, 2007; Suttle C A, 2007).
Cyanophages infecting Synechococcus are ubiquitous in marine environments and are highly abundant in coastal waters, with concentrations of up to 108 cyanophages per liter (Suttle C A, 1993; Suttle C A, 1994; Waterbury J B, 1993). However, no previous reports have documented marine Synechococcus cyanophages in China. The purpose of this study was to isolate a cyanophage-Synechococcus system from the East China Sea; this goal is fundamental for studying phage-host interaction in the Chinese coastal ecosystem.
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Surface seawater samples were collected from the coastal waters of the East China Sea (33°44'38″N, 122°25'44″E) in August 2011 at a depth of 1 m. The water samples for the isolation of cyanophages were concentrated by the ultrafiltration method described by Chen et al. and stored in the dark at 4 ℃ until use(Chen F et al, 1996). The water samples for the isolation of Synechococcus were filtered through a 1.0-mm filter and stored at 15 ℃ until use.
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The filtered samples were enriched with sterilized artificial seawater medium (ASW) and incubated under a constant illumination of approximately 25 μE m-2 s-1 at 20 ℃. After visible growth (based on color and turbidity) was evident in the enrichments, clonal isolates were obtained by repeated cycles (repeated five times) of colony isolation using a serial dilution method described by Throndsen and Rippka (Rippka R, 1988; Throdson J, 1969). The resulting isolate SJ01 was clonal and unialgal.
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Cultures in the exponential to early stationary phase were used for recording in vivo absorption spectra. An aliquot of the culture was transferred to a cuvette, and the in vivo absorption spectrum was measured from 400 to 750 nm using a Scinco S-3100 UV-VIS Spectrophotometer equipped with LabPro Plus Software. The A495/A545 ratio is a measure of the amount of PUB (phycourobilin) relative to that of PEB (phycoerythrin) (Rocap G, 2002). The experiment was performed in triplicate.
Chlorophyll was estimated using a previously described method (Becker W E, 1994). The cells were resuspended in 90% methanol and allowed to stand in the dark for 24 hours (Becker W E, 1994). The suspension was cleared by centrifugation, and chlorophyll was estimated spectrophotometrically using the following equations: Chlorophyll a (μg L-1) = (13.95×A665) - (6.88×A650), and Chlorophyll b (μg L-1) = (24.96×A650) - (7.32×A665)(Rocap G, 2002), where A650 and A665 are the absorbance values of the sample at 650 and 665 nm, respectively. The experiment was performed in triplicate.
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DNA was prepared from exponential-phase culture using a method modified from that described by Tillett and Neilan (Tillett D and Neilan B A, 2000). The extracted DNA (2 μL) was added to a 48 μL PCR mixture containing Taq DNA polymerase assay buffer (50 mmol/L KCl, 20 mmol/L Tris-HCl, pH 8.4), 5.0 mmol/L MgCl2, 200 μmol/L deoxyribonucleoside triphosphate, 0.25 μmol/L each of the primers, and 2.0 U of Taq DNA polymerase (TaKaRa). The PCR primers that were used to amplify the 16S rRNA, ITS, and psbA genes of Synechococcus sp. SJ01 are shown in Table 1. The negative controls contained all of the above reagents, but sterile water was used as the template. The amplification products were verified by electrophoresis and then sequenced.
Species Primer Sequence Source Synechococcus SJ01 16S rRNA 27F1 5′-AGAGTTTGATCMTGGCTCAG-3′ Neilan B A, 1997 409R 5′-TTACAA(C/T)CCAA(G/A)(G/A)(G/A)CCTTCC TCCC-3′ ITS 16S-1247f 5′-CGTACTACAATGCTACGG-3′ Rocap G, 2002 23S-1608r 5′-CYACCTGTGTCGGTTT-3′ psbA psbA-1 5′-AACATCATYTCWGGTGCWGT-3′ Lindell D, 2004 psbA-2 5′-TCGTGCATTACTTCCATACC-3′ Cyanophage S-SJ2 g20 CPS1 5′-GTAG[T/A]ATTTTCTACATTGA[C/T]GTTGG-3′ Sullivan M B, 2008 CPS2 5′-GGTA[G/A]CCAGAAATC[C/T]TC[C/A]AGCAT-3′ psbA psbA-1F 5′-AACATCATYTCWGGTGCWGT-3′ Huang S, 2012 psbA-1R 5′-TCGTGCATTACTTCCATACC-3′ DNApol 90Fa 5′-GAYACIYTIRYIYTITCIMG-3′ Huang S, 2012 355Ra 5′-GGIAYYTGIGCIARRTTIGG-3′ Table 1. Primers used in this study
BLAST searches of the GenBank database (www.ncbi. nlm.nih.gov) were performed to identify closely related sequences. Neighbor-joining (NJ) trees were generated using the MEGA 4.0 program (http://www.megasoftware.net/) for all sequences, which included selected representative sequences from GenBank following alignment using ClustalX2. Bootstrap values were obtained with 1000 resamplings, and clades with bootstrap values greater than 50% were shown on the nodes of the branches.
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Synechococcus phages were isolated with liquid dilution cultures rather than from plaques on solid media because lawn formation is erratic for many strains belonging to Synechococcus marine cluster A (Waterbury J B, 1993). Serial dilutions of the concentrated seawater samples were added to exponentially growing cultures of the host suspended in ASW growth medium in test tubes. The phage-host suspensions were incubated at 20 ℃ for 1 h with occasional agitation to allow the adsorption of the cyanophage. These tubes were incubated in constant illumination (approximately 25 μE m-2 s-1) at 20 ℃ and were monitored daily for cell growth or lysis. The controls contained host cells but no seawater dilutions. The lysis of the host cells was usually observed for up to five weeks. Putative cyanophage lysates obtained by this method were passed through a 0.22 μm pore size filter, and the filtrate was stored at 4 ℃ in the dark. The purified cyanophage filtrates were then obtained with three successive serial dilutions in the liquid medium.
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Phage purification was performed by sucrose density gradient centrifugation as described previously with the following modifications (Vidaver, 1973): both DNA and RNA were digested with 1 μg/mL Dnase Ⅰ and Rnase A (TaKaRa); and five sucrose steps of 20%, 30%, 40%, 50%, and 60% were used. A visible band locating between the 40% and 50% steps was collected and washed to obtain highly purified phage particles.
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An ultra-thin section was used to observe the ultrastructure of Synechococcus sp. SJ01. One milliliter Synechococcus sp. SJ01 was centrifuged at 6000 g for 10 min, and 0.2 mL 2.5% glutaraldehyde was then added to the precipitate for postfixation. Fixation was performed by immersing the sample in 1% osmic acid for 4 h. The sample was then centrifuged at 6000 g for 5 min. PBS was added to the precipitate for washing, and the centrifugation and washing were repeated three times. Dehydration was performed by immersing the sample in 50% to 100% alcohol. The sample was then embedded in Spurr resin (ERL-4206). Ultra-thin sections were stained with uranyl acetate and lead citrate and then observed using a Tecnai G2 TEM.
A total of 20 μL of sucrose density gradient purified phage concentrate was transferred to 200 mesh formvar carbon-coated copper grids and then negatively stained with 2% sodium phosphotungstate (pH 7.0). The grids were viewed using a HITACHI 3H-7000FA TEM.
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To estimate the size of the S-SJ2 genome, DNA was prepared from sucrose density gradient purified phages following the method of Wilson et al (Wilson, 1993). The DNA that was extracted from purified cyanophage was digested with the following restriction endonucleases: Hind Ⅲ, BamH Ⅰ, EcoR Ⅰ, EcoR Ⅴ, Pst Ⅰ, and Dpn Ⅰ. Extracted DNA (2 μL) was added to a 48 μL PCR mixture containing Taq DNA polymerase assay buffer (50 mmol/L KCl, 20 mmol/L Tris-HCl, pH 8.4), 5.0 mmol/L MgCl2, 200 μmol/L deoxyribonucleoside triphosphate, 0.25 μmol/L each of the primers, and 2.0 U of Taq DNA polymerase (TaKaRa). The PCR primers that were used to amplify the g20, psbA, and DNApol genes of cyanophage S-SJ2 are shown in Table 1. Negative controls contained all of the reagents, but sterile water was used as the template. The amplification products were verified by electrophoresis.