2012) In our study the three identified TRFs (TRF_149nt,

2012). In our study the three identified TRFs (TRF_149nt,

TRF_249nt and TRF_270nt) contributed significantly (35%) to the discrimination of station E54 from the other stations. Both TRF_149nt and TRF_270nt were affiliated with Verrucomicrobia, of which iTRF_149nt belonged to Spartobacteriaceae and iTRF_270nt to a 16S rRNA sequence of uncultured Verrucomicrobia (AM040118). The latter 16S rRNA sequence was found in the sediment off Sylt ( Musat et al. 2006). Recently, Verrucomicrobia were observed in the Baltic Sea ( Andersson et al. 2010) and Spartobacteriaceae were found to be quantitatively important in the Baltic Sea at salinities Small molecule library supplier between 5 and 10 ( Herlemann et al. 2011). Verrucomicrobia, which can make a considerable contribution to polysaccharide Sirolimus chemical structure degradation, can also be expected to be associated with phytoplankton ( Martinez-Garcia et al. 2012). Spartobacteria in particular have been directly associated with phytoplankton in the Baltic Sea ( Herlemann et al. 2013). TRF_249nt was identified as

a candidate for Roseobacter. A clone sequence with this TRF was affiliated with the Roseobacter DC5-80-3 branch in the RCA cluster and CARD-FISH showed an abundance of less than 1%. The RCA cluster is widespread in temperate and polar oceans, but constituted less than 0.5% of all bacteria in the Baltic Sea ( Selje et al. 2004). In surface waters, no representative was found at the Landsort Deep station ( Riemann et al. 2008) or in the Baltic Proper ( Herlemann et al. 2011). As its absence was observed in spring (

Riemann et al. 2008) and summer ( Herlemann et al. 2011) and its presence in late summer (our data) and in autumn ( Selje et al. 2004), such differences may be explained by the seasonal dynamics of taxa within the Baltic Sea bacterioplankton communities ( Andersson et al. 2010). Roseobacter was often shown to co-occur with phytoplankton ( Buchan et al. 2005), especially with natural phytoplankton blooms ( O’Sullivan et al. 2004) or in mesocosm studies of Thalassiosira ( Allgaier et al. 2003). It was also shown to be an early surface coloniser in temperate marine waters ( Dang et al. 2008); the DC5-80-3 clade has been linked with the degradation of aromatic compounds ( Buchan et al. 2005). Crump et al. (2004) showed that a shift from a mixture of allochthonous 5-Fluoracil molecular weight communities to a native estuarine community requires bacterial doubling times much shorter than the local water residence time. The doubling time (DT) calculated on the basis of leucine bacterial production and bacterial biomass (all DAPI stained cells) was about 1.7–2.2 days in the Gulf of Gdańsk; a shorter doubling time would probably be based on active cells only. The DT was at least seven times shorter than the residence time in the Gulf of Gdańsk, calculated by Witek et al. (2003). Bacteria in the water at station E54 had enough time to establish a stable community connected with the occurrence of Coscinodiscus sp.

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