Moreover, GDC-0068 solubility dmso viruses can act indirectly on bacterial structure throughout the release of cell debris during lysis activity (enriching the pool of dissolved and particulate organic matter (DOM and POM) and AG-881 cost inorganic nutrients) enhancing in fine growth and production of some bacterial groups [11, 12]. Indeed, whether cells are grazed or lysed can have different

ecological and biogeochemical consequences, as the implications for the matter and energy flow through the microbial web will be very different [13, 14]. Typically, high rates of viral cell lysis may generate a recycling of nutrients and organic matter at the base of the food web and therefore, less carbon and nutrients may reach higher trophic levels, a process referred to as the viral shunt [13, 14]. In contrast, if bacteria are grazed by flagellates, nutrients and energy can reach higher trophic levels via the connection between the microbial loop and the classical food chain [15]. Thus, these processes can significantly influence the production of dissolved organic carbon and the recycling of nutrients [14, 16] and can impact/modify not only bacterial diversity [9, 17] but also the relationship between diversity and ecosystem functioning [18]. A few studies

have investigated the individual effects of flagellates or viruses on bacterial communities in terms of abundance, production and diversity (e.g. [7, 10, 19, 20]). However, their combined effects on bacteria, and the comparison AZD5363 chemical structure between individual and combined effects are still limited [18, 21, 22]. According to these studies, both viral

lysis and protistan bacterivory may act additively to reduce bacterial production and sustain diversity, which could explain the less pronounced blooming species in heterotrophic bacterioplankton than in phytoplankton [22]. However, the opposite effect has also been reported [23]. Moreover, comparisons of the combined effects of viruses and RG7420 order flagellates on the bacterial community according to the trophic status of aquatic systems are scarce and until now, no information has been made available for lacustrine systems. To the best of our knowledge, Zhang et al. [22] are the only authors who have investigated these effects taking into account a trophic range within a coastal ecosystem, and the same trend was highlighted [22]. According to these authors, a shift of predator control mechanisms from flagellates in oligotrophic systems to viruses in eutrophic systems could explain the results. In this study, we collected samples from two peri-alpine lakes (Annecy and Bourget) with substantial differences in their trophic state (oligo- vs. mesotrophic, respectively) and we developed treatments with either individual or combined predators of the bacterial community using a fractionation approach (i.e.