Magnetotactic bacteria (MTB) are ubiquitous in aquatic environments, for example marines and lakes. They can form intracellular nanosized magnetite or greigite crystals, known as magnetosomes, which are membrane bound and are generally organized into one or more chains (Schüler, 2008). The net magnetic moment of magnetosome chains can interact with the Earth’s magnetic field and thus navigate MTB along local geomagnetic fields (magnetotaxis) (Faivre & Schüler, 2008). It is widely believed that the magnetotaxis

in conjunction with aerotaxis and other chemotaxis can help MTB to efficiently locate and maintain the most optimal position in vertically stratified sediments or water columns (Frankel et al., 1997; Pan et al., 2009b). All currently known MTB belong to the Proteobacteria and Nitrospira phyla based on the comparison of 16S rRNA genes (Amann et al., 2006). MTB can play important roles in mediating some geochemical Alectinib cost processes, for example iron and sulfur cycling (Simmons & Edwards, 2006). Moreover, fossil magnetosomes preserved in sediments are important natural remanent magnetization carriers (Chang Selleckchem BGB324 & Kirschvink, 1989; Moskowitz et al., 1993; Pan et al., 2005a, b; Kopp & Kirschvink, 2008), and can serve as a potential proxy for paleoenvironmental reconstruction

(Snowball et al., 1999; Snowball et al., 2002; Paasche et al., 2004; Kopp & Kirschvink, 2008). Therefore, understanding the patterns of MTB communities in environments is of great importance. A handful of studies have examined the

diversity and vertical distribution of MTB in a single location and have shown that the majority of MTB are usually close to the oxic–anoxic transition zone in chemically PRKD3 stratified aquatic habitats (Spring et al., 1992, 1993; Bazylinski et al., 1995; Bazylinski & Frankel, 2004; Simmons et al., 2004; Flies et al., 2005a; Pan et al., 2008; Lin & Pan, 2009; Lin et al., 2009). However, due to the lack of detailed studies, the distribution of MTB communities between different locations and their temporal variations remain unclear (Spring et al., 1994; Flies et al., 2005b). Our previous studies revealed that large amounts of MTB (up to 106 cells mL−1) existed in sediments from Lake Miyun near Beijing, China, where the enriched MTB affiliated within both Proteobacteria and Nitrospira phyla (Lin et al., 2008, 2009). In the present study, we used a combination of a cultivation-independent approach and unifrac analysis to investigate the temporal variations of MTB in two freshwater sediment microcosms, which were collected from two separate sites in Lake Miyun, Beijing. The diversity and variation of MTB communities in two microcosms were also compared. The MTB-bearing sediment samples used in this study were collected from two separate sites (MY8 and MY11) in the southern margin of Lake Miyun near Beijing, China (Fig. 1).