Taxonomy and functional interactions in upper and bottom waters of an oligotrophic high-mountain deep lake (Redon, Pyrenees) unveiled by microbial metagenomics
Graphical abstract
Introduction
High mountain lakes are, in general, highly sensitive systems to external forcing and, in some cases, atmospheric depositions closely connected to large-scale environmental changes can be easily detected (Grimalt et al., 2001; Camarero and Catalan, 2012; Triadó-Margarit et al., 2019). Because of its isolation level and highly diluted nature of high mountain waters, the status of some lake indicators such as water temperature, dissolved geochemical compounds, or plankton composition are very good sensors on the remote effects of human-induced perturbations at the ecosystem scale, making these lakes particularly suitable as long-term ecological research field sites and model systems to unveil diffuse impacts of global change (Adrian et al., 2009). Overall, mountain lakes are considered very appropriate sentinels and recorders of past and present environmental changes (Catalan et al., 2006; Williamson et al., 2009). However, the value of lakes as proper sentinels of climate change is closely related to the level of accurate understanding of internal lake processes (Adrian et al., 2009).
Most mountain lakes are relatively shallow, and water is highly transparent (Catalan et al., 2009). Consequently, the trophogenic zone, where primary production is higher than respiration, extends from the top to the bottom of the water column. Only during winter, when snow accumulates on top of the ice cover and light cannot penetrate, the water column becomes tropholithic and heterotrophic processes dominate over autotrophic. The extent and temporal duration of these tropholithic zones are particularly relevant for the in-lake alkalinity generation by processes that constitute a net consumption of anions (Psenner, 1988). The high-mountain Lake Redon (2240 m a.s.l., Pyrenees, Spain) is an extensively studied freshwater system and a good model for deep glacial dimictic lakes (Catalan et al., 2006). In a deep lake, such as Redon, trophogenic and tropholithic zones coexist during summer stratification, because near the bottom light levels are extremely low. Near the surface and near the bottom, Lake Redon holds two of the extremes of the range of conditions that can be found in high-mountain ecosystems. Lake Redon also has a long water renewal time for a high-mountain lake. The average time is four years, and deep layers are estimated to renew every 15 years (Catalan, 1988). Consequently, the water column dynamics is largely influenced by the internal load of nutrients. During the summer and winter (ice cover) stratifications, there is a progressive accumulation of compounds in the deep layers, coming from sinking material and in situ mineralization or diffusion from the highly organic sediments (Catalan et al., 1992). During autumn and spring mixing periods, the accumulated nutrients are brought to the photic zone and used by aerobic phototrophs producing the peaks of primary production in the lake. In contrast, the top layer has low inputs from the small streams flowing into the lake, which usually dries out at the end of summer, and remains isolated by a thick metalimnion from the more productive bottom layers in these lakes, located between 30 and 45 m depths. Therefore, the deep layers are naturally richer in all kind of organic and inorganic compounds involved in the C, N, P and S cycles (Catalan et al., 1992). Conversely, the high UVR in the top layer (Catalan et al., 2006) may enhance the concentration of some unusual compounds that result from photoreactions (Valentine and Zepp, 1993). In essence, all these conditions provide an excellent case to investigate the main features of an integrated view of the carbon, nitrogen, sulfur and phosphorus cycles and on the biogeochemical interactions with the bacterial and archaeal populations inhabiting the lake.
Metagenomics and in-silico metabolic pathway reconstruction is a way to unveil the complexity of the biogeochemical networks (e.g., Tyson et al. (2004)) and to provide solid foundations for the understanding of the microbiological processes in the environment (e.g., Llorens-Mares et al., 2015; Simon et al., 2009). We applied this approach in Lake Redon for a better understanding of the internal lake processes using two composite samples collected from the near surface and from the near bottom, respectively. We aimed to establish a current framework for some of the microbial biogeochemical processes that may help to support the identification of potential future climate and global change signals in the lake. We analyzed the two ends of the range of conditions found in Lake Redon. We hypothesized a limited dissimilatory sulfur cycle, and an important presence and diversity of nitrogen- and phosphorus-cycling genes in order to overcome the nutrient limitation inherent to these oligotrophic systems. We also expected to find unseen metabolic processes in the lake in both of the studied extremes that the particular conditions of high mountain lakes may favor but have been understudied to date.
Section snippets
Study site, samples collection, and sequencing
Lake Redon is a high-altitude dimictic lake with mixing periods in spring and autumn. Located in the central Pyrenees (42° 38′ 34″ N, 0° 46′ 13″ E, altitude 2240 m a.s.l., maximum depth 73 m, surface 0.24 km2). It has been extensively studied as a model alpine lake (see a review by Catalan et al., 2006 and references therein). Due to its isolation, small catchment area and limited soil and vegetation development, the lake is oligotrophic and atmospheric depositions of reactive nitrogen and
Results
The lake was thermally stratified with a metalimnion spanning from 11 to 26 m and a temperature gradient from 13 to 4 °C. The whole water column was oxygenated, although with a lower oxygen concentration in the bottom layer (Table 1). The concentrations of ammonia (×10), nitrate (×1.4), and bacterial abundance (×1.7) were higher at the bottom than at the top. In the 2 m sample, 90% of the total solar irradiance was measured, and no photons were detected at 60 m depth. Prokaryotes, mostly
Discussion
High-altitude mountain lakes experience extreme physical conditions and low temperatures, high ultraviolet radiation (UVR), ultraoligotrophic conditions, and a marked seasonality with a long ice cover period (Sommaruga, 2001; Catalan et al., 2006). Therefore, microbial life faces extreme conditions combined with low resources in these environments, and planktonic microbes and biogeochemical pathways are difficult to investigate because of the low organism density and activity. Biogeochemical
Acknowledgements
J Caliz, M Sala, X Triadó-Margarit, and L Camarero are acknowledged for field and lab assistance, and ancillary data. We are thankful to the Centre de Recerca d'Alta Muntanya, Universitat de Barcelona, Vielha, for logistic facilities. This research was funded by Grants INTERACTOMA RTI2018-101205-B-I00 to EOC and TRANSFER CGL2016-80124-C2-1-P to JC from the Spanish Office of Science (MICIU/AEI/MINECO) and European funding (ERDF/FEDER).
Declaration of competing interest
The authors declare that they have no conflict of interest.
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