Vertical distribution of the prokaryotic cell size in the Mediterranean Sea
© Springer-Verlag and AWI 2012
Received: 28 July 2011
Accepted: 27 February 2012
Published: 16 March 2012
Distributions of prokaryotic cell size and morphology were studied in different areas of the Mediterranean Sea by using image analysis on samples collected from surface down to bathypelagic layers (max depth 4,900 m) in the Southern Tyrrhenian, Southern Adriatic and Eastern Mediterranean Seas. Distribution of cell size of prokaryotes in marine ecosystem is very often not considered, which makes our study first in the context of prokaryotic ecology. In the deep Mediterranean layers, an usually-not-considered form of carbon sequestration through prokaryotic cells has been highlighted, which is consistent with an increase in cell size with the depth of the water column. A wide range in prokaryotic cell volumes was observed (between 0.045 and 0.566 μm3). Increase in cell size with depth was opposed to cell abundance distribution. Our results from microscopic observations were confirmed by the increasing HNA/LNA ratio (HNA, cells with high nucleic acid content; LNA, cells with low nucleic acid content) along the water column. Implications of our results on the increasing cell size with depth are in the fact that the quantitative estimation of prokaryotic biomass changes along the water column and the amount of carbon sequestered in the deep biota is enhanced.
KeywordsProkaryotic sizes Prokaryotic morphotypes Vertical distribution Cell carbon content Image analysis Mediterranean Sea
Marine microbial biomass and metabolism as well as its role on oceanic C pump are focal points in marine ecology studies. In this frame, prokaryotic biomass quantification (both bacteria and archaea) is a key parameter for the knowledge of food-web functioning and the cycling of organic matter or nutrients in the context of oceanic biogeochemical fluxes (Fukuda et al. 1998; Tanaka and Rassoulzadegan 2002).
The relevant role of prokaryotes in the water column has been recently assessed, and new concepts on the functioning of this community have been developed mainly about the importance of prokaryotes in the dark water column (Arístegui et al. 2009; Nagata et al. 2010; Reinthaler et al. 2006).
Biomass of prokaryotic natural assemblages in aquatic environment is mainly investigated by cell counting—using epifluorescence microscopy or flow cytometry. Then, a conversion factor is applied for transforming cell number into carbon content in order to estimate biomass. The relationship between cell and dry mass has been determined by several methods to establish the appropriate conversion factors, as referred by Pernthaler and Amann (2005), and the most frequently applied conversion factor derives from the assumption that each marine bacterium contains 20 fg of carbon (Ducklow and Carlson 1992; Lee and Fuhrman 1987). Nevertheless, since the cell carbon content varies together with cell volume (Bölter et al. 2002; Fukuda et al. 1998), the use of a constant conversion factor might determine an overestimation or underestimation of the actual standing stock. As a consequence, the determination of size is needed to accurately estimate prokaryote biomass. Size is one of the most relevant ecological traits, and the understanding of the mechanisms controlling size distribution is crucial for revealing the interaction of the prokaryotes with their environment. The importance of prokaryotic cell size has been discussed in-depth by Young (2006), stating the selective biological implication of cell shapes. Among the phenotypic traits of microbial communities, size reflects the complexity of the habitats at microscale and, in some extent, the distribution patterns of different genotypes (Pernthaler and Amann 2005). Specific studies on size distribution and size classification are very rare and, among them, Bölter et al. (1993) is concerned about the methodological comparisons between different data treatments applied to soil bacteria.
Several studies have been carried out on the size spectra of natural population of prokaryotes in aquatic environment (Rassoulzadegan and Sheldon 1986; Posch et al. 2009), but relatively few studies have so far dealt with the cell size and morphotypes in relation with environmental parameters (Jochem 2001; Robarts et al. 1996). This has been done mainly at regional scale (Mahadevaswamy et al. 2008; Zmuda 2005) or in relation with protistan grazing pressure (Pernthaler et al. 1996; Simek et al. 2001).
Recent studies have shown that prokaryotic cell size often increases with depth in the water column (La Ferla et al. 2010; Van Wambeke et al. 2010) even though the interpretation is still unknown. Cell size is the result of the balance between different factors, among which are resource availability, cell growth, frequency of division (Tanaka and Rassoulzadegan 2002), bacteriovory (Pernthaler 2005), viral lysis (Danovaro et al. 2008) and species composition (Jochem 2001). Environmental characteristics, such as hydrostatic pressure (Grossart and Gust 2009), turbulence (Peters et al. 2002), temperature and chemical variables (Kalcheva et al. 2008), also are able constraining cell size variations.
Information on prokaryotic biomass depends on the methodology used for the study. Indeed, epifluorescence microscopy differentiates prokaryotic morphotypes and subpopulations with different sizes and carbon content (Jochem 2001), while the application of flow cytometry distinguishes sub-populations with a different apparent DNA content (Button and Robertson 2001). Differences in the side scatter signal (SSC, related to the size, density and morphology of the cells) and in the relative green fluorescence (related to the nucleic acid content of the cells) allow discriminating two fractions, named HNA cells (cells with high nucleic acid content) and LNA cells (cells with low nucleic acid content) (Gasol and del Giorgio 2000). The HNA cells are generally considered to represent active members of the bacterial community, whereas LNA may be dead or dying cells (Gasol et al. 1999; Lebaron et al. 2002). However, the use of HNA cell abundance as a proxy for the activity in natural systems has been questioned (Bouvier et al. 2007; Moran et al. 2007). As stressed by different studies (Felip et al. 2007; Gasol et al. 1999), using both epifluorescence microscopy and flow cytometry allows us to deeply investigate the distribution patterns of prokaryotic cell volumes.
In coastal and pelagic areas of the Mediterranean Sea (MED), results on prokaryotic volumetric determinations have been already obtained (e.g., La Ferla and Leonardi 2005; Misic et al. 2008; Pedrós-Alió et al. 1999; La Ferla et al. 2010). In the MED, flow cytometry has been used mainly to study phototrophic organisms (Casotti et al. 2003), to analyze prokaryotes of fresh sediments (Amalfitano et al. 2009; Fazi et al. 2008) or to monitor living properties of bacterial cells (Caruso et al. 2010; Scharek and Latasa 2007).
Our general aim is to investigate the prokaryotic cell volume and morphology variations in the MED on a vertical scale as a first step in understanding the microbial structures and their ecological functions in this marine environment. The specific goals of this study are (1) to investigate the size distribution of the prokaryotic cells with depth in different Mediterranean pelagic ecosystems and (2) to understand the relationship between environmental properties and cell size distribution in order to look for the main driving forcing of cell size distribution.
For this purpose, we applied image analysis equipped with epifluorescence microscopy for cell determinations together with flow cytometry analysis along the water column of several stations from the South Tyrrhenian (ST), South Adriatic (SA) and Eastern Mediterranean (EM) Seas.
Materials and methods
Sampling stations, dates, coordinates, bottom depths, sample numbers, names of cruise and projects
41° 50′ N, 17° 45′ E
39° 30′ N, 13° 30′ E
39° 30′ N, 13° 30′ E
40° 36′ N, 14° 08′ E
39° 42′ N, 13° 37′ E
36° 34′ N, 21° 07′ E
35° 39′ N, 26° 10′ E
34° 57′ N, 22° 05′ E
Hydrological parameters and dissolved oxygen
CTD casts are performed using a calibrated Sea Bird Electronics SBE 9/11 PLUS coupled to a Carousel SBE 32 of 12/24 Niskin bottles. The CTD probe is equipped with oxygen, fluorometer and transmissometer sensors. Calibration of temperature and conductivity sensors is performed at the SACLANT Research Center (La Spezia, Italy) before cruises.
Parallel determination of oxygen concentration is carried out at all the sampling depths using the Winkler method (Carpenter 1965) with an automatic endpoint detection burette Metrohm 716 DNS Titrino.
Nutrient concentrations and photosynthetic pigments
Samples for determining nutrient concentrations are collected in 20-mL polyethylene vials and quickly frozen and stored at −20°C. Nutrient concentrations are determined within a few weeks after the end of each cruise, using a hybrid Brän-Luebbe-Technicon AutoAnalyzer following classical methods (Grasshoff 1976) with slight modifications. In brief, flow rates of reagents are reduced, and their concentrations changed to obtain the same quantity of reagents in the mixed flow though reducing the dilution of the sample and thus increasing the sensitivity by a factor of two. All nutrient concentrations are determined using running standards for each batch (in general two or three stations). All samples are analyzed twice, and all the analyses are carried out with the same setup of equipment.
For photosynthetic pigments, 3 L samples are filtered onto Nuclepore filters (47 mm diameter) of 3 μm porosity and onto Nuclepore filters (47 mm diameter) of 0.2 μm porosity, separating the picophytoplankton fraction from the rest of the community (micro- and nano-phytoplankton). Filters are immediately stored in liquid nitrogen for later pigment analysis. High-performance liquid chromatography (HPLC) analyses are performed within 2 weeks of collection according to the protocol described in Dimier et al. (2007). Briefly, pigment filters are extracted in 5 mL 100 % methanol, and 500 mL of 1 mol L1 ammonium acetate is added to the 1 mL pigment extract for five minutes before the analysis in a Hewlett-Packard series 1100 HPLC (Hewlett-Packard, Wilmington, NC, USA). A 3-mm C8 BDS column (ThermoHypersil, Runcorn, UK) is used, and the mobile phase is composed of a two-solvent mixture: A, methanol, aqueous ammonium acetate (70:30), and B, methanol. Pigments are detected at 440 nm, and for each pigment, the absorption spectrum between 400 and 700 nm is done using a photodiode array detector (model DAD series 1100, Hewlett-Packard). Chlorophyll and derivatives also are analyzed by fluorometry (series 1100 fluorometer, Hewlett-Packard), using a 410 nm excitation wavelength and a 665 nm emission wavelength, and quantified using standards from the V.K.I. (Water Quality Institute, Horsholm, Denmark).
Epifluorescent microscopy (Image analysis)
Measurements are taken on an adequate number of cells to obtain a well-representative mean volume due to normal distribution of the data.
Errors during biomass calculation by PA and VOL account for >5 % and ~3 %, respectively, as already estimated by Bölter et al. (2002).
Samples for flow cytometry analysis are preserved by fixation with sterile (0.22 μm) paraformaldehyde 2 % (final concentration) for 15 min and freezing in liquid nitrogen. At the laboratory, samples are stained with Syto13 at 2.5 μM (Gasol and del Giorgio 2000; Andrade et al. 2003). Counts (PAC) are performed in a CyAn ADP flow cytometer (Dako, USA) equipped with a solid-state laser (488 nm, 25 mW) and filter modifications (green FL1 to 515 ± 30 nm and red FL4 to 660 ± 30 nm). For calibration of side scatter and green fluorescence signals, and as an internal standard for cytometric counts, fluorescent latex beads (1.58 μm diameter) are systematically added. Based on optics and fluorescence signals, HNA and LNA cells abundances are also determined (Gasol and del Giorgio 2000).
Data processing and statistical analyses
Data are grouped according to the following depth intervals: >2–200 m (epipelagic layer), >200–1,000 m (mesopelagic layer) and >1,000 m–bottom depth (bathypelagic layer).
Descriptive statistical analysis and Pearson’s correlations are performed with SigmaStat software v3.0, and analysis of variance (ANOVA) is applied to log-transformed VOL data to assess the statistical differences between sampling depths.
Multivariate analysis is performed using the package Primer 6 (Clarke and Gorley 2006). The Shannon index (H′) applied on cell volume and specific morphological form data (cocci, coccobacilli, rods, vibrios and spirillae) is estimated for the different sampling depths. Hierarchical cluster analysis (HCA) is applied to test the similarity (group average linkage method) level of cell size versus depth as well as principal component analysis (PCA) to reduce the environmental variables down to a few components (Jolliffe 2005).
Physical and chemical characteristics of the water samples as minima, maxima, median, mean values and standard deviations
Dissolved oxygen CTD
Dissolved oxygen Winkler
ChlaN + M
Prokaryotic cell volumes (VOL), carbon contents (CCC), abundances (PA), biomass (PB) by image analysis and prokaryotic cell abundances (PAC) and high nucleic acid to low nucleic acid ratios (HNA/LNA) by flow cytometry
fg C cell−1
Cell × 105 ml−1
µg C L−1
Cell × 105 ml−1
CCC dependent on cell volume varies in the range 15–129 fg C cell−1 with a mean value of 57 ± 25 fg C cell−1. Spatial variability of the distribution is high, with differences among the sampled areas (mean values of 39, 51 and 61 fg C cell−1 in SA, ST and EM, respectively, data not shown) and with depth.
On the contrary to cell size, PA presents the highest values in the euphotic layers and thus decreasing with depth (Fig. 3b). PA varies between 0.4 and 28.9 × 105 cells ml−1 with mean value of 4.7 ± 3.1 × 105 cells ml−1. PA is the lower in EM (mean value, 3.1 ± 2.9 × 105 cells ml−1), relative to that in the ST (mean value, 5.2 ± 6.3 × 105 cells ml−1), and in SA (mean value, 6.1 ± 4.2 × 105 cells ml−1).
PB, ranging between 0.9 and 73.1 μg C L−1 (mean value, 16 ± 10 μg C L−1), shows the highest values at surface and seems to be more dependent on PA than VOL. PB is higher in SA (19 ± 8 μg C L−1), than in EM (17 ± 13 μg C L−1) and ST (14 ± 16 μg C L−1). As for PA, PB presents the highest variability in the ST area.
The PAC distribution along the water column varies between 0.18 and 37.87 × 105 cells ml−1, and it significantly correlates to PA (r = 0.32, n = 106, P < 0.01). PAC results underestimated relatively to PA (from image analysis) probably due to the weak fluorescence signal by smaller cells.
The HNA/LNA ratio ranges between 0.09 and 3.69 with the means of 0.64, 1.32 and 1.44 in the epi-, meso- and bathypelagic layers, respectively. These results suggest increasing bacterial sizes and cellular volumes toward deep waters.
Pearson’s coefficient of correlations determined between the cell volumes and depth, cell abundance, biomass, abundance by cytometry, HNA/LNA ratio, nutrients, divinyl-chlorophylla
Cell size in the epipelagic layer is significantly different from the size measured in the mesopelagic layer (P < 0.05) and bathypelagic layers (P < 0.01) (ANOVA, data not shown). Significant variations in cell size occur with depth along the water column and are confirmed by the higher Shannon index found in the deep layers than at the surface (data not shown).
The PCA shows that the first axis explains up to 56 % of the variability determined by the physical–chemical characteristics, mainly density, and NO3 and PO4 levels. The second component, representing 26 % of the variability, is mainly constituted by biological parameters like morphometric (volume) and morphological (mainly coccal forms) ones.
Biomass, calculated on the above morphotypes—taking into account abundance and size—is mainly composed by coccobacilli (37 % of total biomass) and rods (31 %). Cocci account for 20 %, vibrios for 12 % and spirillae for <1 % of the total biomass.
Prokaryotic cell volume distribution along the water column
The calculation of cell volume provides a taxonomic approach for analyzing the ecosystems structure allowing us to better quantify biomass as well as cell heterogeneity in mixed assemblages (Quinones et al. 2003). Moreover, it has been hypothesized that changes in size or shapes or morphology of unicellular bodies, including prokaryotic cells, can be a sensitive indicator of trophic and climatic changes in aquatic ecosystems (Pernthaler and Amann 2005).
Our results show that large cells, with volumes ranging between 0.1 and 0.3 μm3, dominate the total prokaryotic assemblage. The ranges of cell size are generally higher than those previously referred by La Ferla et al. (2010) in different MED areas but similar to those measured by Azzaro et al. (2011) in the South Adriatic Sea and by Misic et al. (2008) in the Tyrrhenian Sea, being the latest estimated by acridine orange direct counts. Cellular sizes measured in our study are also higher than those reported for oceanic areas (Lee and Fuhrman 1987; Pedrós-Alió et al. 1999) even though few data are available since most of the studies dealt with cell size variability measured in laboratory or mesocosm experiments (Heldal et al. 1994). In the Baltic Sea, Blackburn et al. (1998) and Heinanen (1991) determined smaller cell volumes within ranges of 0.023–0.232 and 0.021–0.072 μm3, respectively. Moreover, Heinanen (1991) reported higher cell size during the vernal phytoplankton bloom than in summer, mainly in relation with river discharge. Conversely in our study, seasonal differences in cell size are not detected, probably because a low coastal effect on the studied ecosystems. However, increases in cell size are highlighted over the 3 years.
A synthesis of CCC obtained in Mediterranean and Oceanic seawater samples
Lee and Fuhrman (1987)
20 fg C cell−1
Ducklow and Carlson (1992)
20 fg C cell−1
Christian and Karl (1994)
10–15 fg C cell−1
Pacific (Aloha Station)
Caron et al. (1995)
10–15 fg C cell−1
Fukuda et al. (1998)
12–30 fg C cell−1
Coastal Southern and Pacific Oceans
Gundersen et al. (2002)
4–9 fg C cell−1
La Ferla et al. (2004)
19 fg C cell−1
La Ferla and Leonardi (2005)
6–42 fg C cell−1
La Ferla et al. (2010)
14–22 fg C cell−1
Williams and Carlucci (1976)
10 fg C cell−1
North-Central Pacific Ocean
Becquevort et al. (1998)
15–80 fg C cell−1
Børsheim et al. (1990)
300 fg C µm−3
Roskilde Fjord (Norway)
Bjornsen and Kuparinen (1991)
390 fg C µm−3
Morphotypes distribution along the water column
Each morphotype shows variability in size and abundance along the water column. Our results confirm the existence of different populations along the water column as already assessed by more specific biomolecular techniques in samples of the Tyrrhenian Sea (Tamburini et al. 2009) and North Atlantic (Reinthaler et al. 2006). Coccal forms and coccobacilli are the main contributors of the biomass. The shift of morphotype along the water column is clear, with small coccal form prevailing at surface while great-elongated forms dominate at depth. In the South China Sea, Hu et al. (2011) highlighted a depth partitioning in the prokaryotic community structure and clones libraries of crenarchaeal genes showed two depth-dependent clusters: a “shallow” and a “deep” cluster in the epipelagic and in the meso- and bathypelagic layers, respectively. Morris et al. (2002), in the northwestern Sargasso Sea, reported a numerical shift of small-sized SAR11 (curved rods of less than 1 μm) to larger-sized Archaea along the water column. Moreover, these authors affirmed that in many of the studied environments, SAR11 is the most dominant organism, accounting for an average of 35 % of surface water and 18 % of mesopelagic cell counts in both coastal and open ocean systems. In our case, we cannot exclude the occurrence of this clade, these cells being difficult to properly distinguish in image analysis because of their small size, close to the limit of resolution of light microscopy.
A further approach developed by Posch et al. (2009), using a combination of CARD-FISH and image analysis to discriminate between different morphotypes and their taxonomic affiliation, has shown how this combination is useful to provide the simultaneous analysis of both morphotypes and phylogenetic lineages. Formerly, combination between confocal laser scanning microscopy, allowing determinations of bacterial numbers, volumes and dividing cells by and image analysis, have been successfully applied by Bloem et al. (1995).
Comparison of cell volumes and environmental parameters
Hydrology does not affect cell size variability, as revealed by the lack of significant correlation between cell size and temperature or salinity. This result agrees with the findings of Li and Dickie (1996) asserting that, at large scale, temperature exerts only a direct significant influence on the cell abundance below 14°C, while above 14°C temperature does not affect cell abundance. The high temperature of MED seawater (always ~13°C below the seasonal thermocline down to the bottom and during winter mixing period) relatively to the oceanic ones does not limit the deep microbial growth (Tanaka 2009).
The hydrostatic pressure alone may not be a constraining factor for cell size. Indeed, many prokaryotes are piezophiles and physiologically well adapted to high pressure. Studies in laboratory show that pressure affects cell division but not cell growth (Barlett 2002).
Response of bacteria to pressure seems to be strain dependent as revealed by Grossart and Gust (2009), which showed that selected strains respond individually to pressure exposition with strong physiological response during sinking. A study by Oger and Jebbar (2010) revealed adaptive strategies to high hydrostatic pressures in prokaryotes to maintain appropriate cell turgor and fluid balance.
Turbulence of water column also might affect the distribution of prokaryotes, for instance influencing the grazing pressure that appears to be lower under turbulent conditions (Peters et al. 2002).
Other environmental variables, as nutrients, are responsible for varying bacterial cell size. A coupling between environmental trophic level and composition or size variability of bacterioplankton populations has been observed by Ducklow and Carlson (1992). Vrede et al. (2002) showed that morphology, biomass, size, abundance and C content changed according to nutrient and substrate limitations on growing cultured bacteria. Interestingly, Øvreås et al. (2003) from a mesocosm study showed that a new population of large rod-shaped bacteria is able to develop following the addition of glucose together with inorganic nutrients. These authors hypothesized a shift from a bacterial community dominated by species with high ability to compete for organic carbon source to a community dominated by species with a high ability to compete for mineral nutrients. Cells with the capacity to store glycogen are able to increase their size without a parallel increase in the cellular requirement for the limiting nutrient.
From our results, the hypothesis that fluctuations in nutrient availability influence cell volume is confirmed as revealed by the significant correlation found between cell volume and nutrient concentrations. This can be due to a shift of population according to their efficiency to compete for the available resources throughout the water column. These features suggest a certain degree of bottom-up control (Eiler et al. 2011). Indeed, in the surface layer, cell size covaries with divinyl-chlorophyll a concentration, probably in relation with the fact that this pigment biomarker of Prochloroccus is much higher in the deep-chlorophyll maximum, corresponding to the biomass and nutrient-rich layer (Zaccone et al. 2004).
The inverse correlation between the cell number and size is intriguing. Epipelagic layers are characterized by abundant and small cells, among which coccal forms show the highest relative frequency, while in the deep layers, cell concentration is lower and characterized by greater volumes of rods, coccobacilli and vibrios, and higher presence of rods. Racy et al. (2005) suggest that in high productive conditions (chlorophyll a rich and thus young and labile organic matter availability) the numerical increase of spheroidal cells (cocci and coccobacilli) is favored, due to a more efficient reproductive strategy. This result fits with our higher presence of coccal forms in the surface layer where phytoplankton grows. On the other hand, the hypothesis that abundant and dwarf forms also might use the strategy by getting smaller to increase the surface, especially in oligotrophic environments, cannot be excluded.
Conversely, in the deep layers where phytoplankton is absent and richer in more recalcitrant substrata, cell abundance is lower and the low resources are probably used by cells for optimizing growth, instead of division, which is more expensive in terms of energetic cost (Racy 2004). This hypothesis might be confirmed by the increase in the leucine/thymidine uptake ratios in growing bacterial cells in oceanic environments (Kirchman et al. 1986). Even in reducing cell division due to stressful conditions, cell growth continues. Thanks to this mechanism, the organism is able to increase its surface area, providing itself with greater contact with the medium and so enhancing its capacity to capture the scarce resources from the surroundings. Our study corroborates this hypothesis since the inverse correlation between cell count and size, a sort of microbial phenomenon of “gigantism”.
To our knowledge, studies comparing prokaryotic cell volume and carbon pools are few in marine ecosystems, as in the MED sea where relationships between DOC and POC distributions and microbial community are scarce (La Ferla et al. 2006; Sempéré et al. 2000; Zaccone et al. 2002). Santinelli et al. (2010) hypothesized a different functioning of the microbial loop, mainly linked to the semi-labile fraction of DOC in the deep MED layers. The higher DOC concentration found in the deepest layer relatively to the intermediate layers in the MED may be linked to different cell size dominance in these layers, in relation with different behavior in the metabolic functioning of prokaryotic populations along the water column. Studies on DOC availability to prokaryotic enzymatic activity highlighted different behavior in different areas of MED. The increase in the cell-specific activities with depth was mainly found in the more oligotrophic Eastern basin as well as an active microbial community metabolizing proteinaceous substrates was found in the bathypelagic layer of the Tyrrhenian Sea (Zaccone et al. 2012).
Cell size variations affect the prey–predator relationship. Indeed, size is a relevant factor influencing susceptibility to protistan grazing, with a refuge at the lower and upper ends of the prokaryotic cell size range (Jürgens and Güde 1994). Hence, a relative grazing resistance can be assumed for the so-called ultramicrobacteria and for complex forms such as the filaments and aggregates. Protista primarily feed on particular morphotypes in natural mixed assemblages (Peters et al. 2002), and Arístegui et al. (2009) suggested that heterotrophic nanoflagellates might control prokaryotic abundance in the meso-bathypelagic systems in the same way as in epipelagic water.
The dominant cell volume found in our study ranged between 0.1 and 0.3 μm3, and cell volume distribution appears unclear when compared with the Pernthaler’s diagram on the effect of predation on the microbial community structure (Pernthaler 2005). Indeed, most of the cells are distributed close to the mean size, and the absence of cells volume ranging between 0.08 and 0.119 μm3 suggests a selective predation over these cell dimensions. In different areas as a subarctic estuary, the microbial cell volumes are controlled by predators in summer and by the resources (inorganic nutrients, carbon) available in other periods (Heinanen 1992). Since the impact of bacterial cell volume is less relevant than cell length for feeding efficiency of the heterotrophic nanoflagellate (Matz et al. 2002), the length frequency classes are determined. In our samples, the most frequent length is ranged between 0.4 and 0.8 μm, and the prokaryotic population is mainly distributed far from the mean length value. According to Pernthaler and Amann (2005) in pelagic habitats, heterotrophic flagellates preferably ingest microbial cells within a length range of 1–3 μm, and by consequence smaller cells take advantage of the low grazing rate. Unfortunately, we do not have any data on predation in this study, but cell length frequencies suggest a weak top-down control on the prokaryotic population longer than 1.2 μm. Recent results in the MED from dilution experiments suggested a high effect of potential predation of heterotrophic nanoflagellates on prokaryotic abundance (on average 49.5 %) at 1,500 m depth (Fonda Umani et al. 2010). However, different behaviors of the heterotrophic nanoflagellate grazing pressure on prokaryotes growth rates are observed relatively to the different biogeographic regions, for instance being higher in the western than in the eastern MED basin. In the latter, the prokaryotic growth is higher than mortality. The opposite is observed in the western basin, as in the Tyrrhenian Sea, where heterotrophic nanoflagellates are able to control prey abundance. However, in our samples, noticeable differences between the size and length frequencies are not detected over the three sampled areas.
Finally, a relevant role of high viral abundance occurring in the meso- and bathypelagic waters of MED on cell size distribution could not be excluded mainly in the Eastern basin (Magagnini et al. 2007).
These previous results on nanoflagellates and viruses corroborate our results about the weak top-down control hypothesized in our study.
At a methodological point of view, flow cytometry underestimates cell counts relatively to image analysis probably due to the weak fluorescence signal by smaller cells as already observed by Heldal et al. (1994). The relative contribution of HNA cells to total abundance strongly fluctuates, and the depth-dependent pattern agrees with the increasing cell sizes with depth. Indeed, the shift in dominance from low-DNA to high-DNA cells below the epipelagic layer is probably linked to cell size increase with depth.
The novelty of our study consists in considering cell size as a functional parameter in marine prokaryotic studies. Our results show that a usually-not-considered form of carbon sequestration through the prokaryotic cells exists in the deep MED. Such sequestration can be greater than normally thought, due to consistent increase in cell size in the dark water column. Different factors might affect cell size and morphology distribution, as a probable response to environmental condition variations (both biotic and abiotic) along the water column. Bottom-up and top-down controls on prokaryotic cell size can be hypothesized. Although assessing the prokaryotic size and morphology by microscopy is slow and labor-intensive, our results lead to the thesis that VOL calculation must be locally applied for CCC determination, at least within the different water masses, in order to more correctly calculate biomass concentration.
The authors thank the colleagues at CNR IAMC: F Soraci, A Cosenza, V La Cono for their valuable contribution, as well as G Caruso for her support in statistic. The research was supported by funds of VECTOR—CARPEL project (MIUR-Ministero Italiano dell’Università e Ricerca), STM-Short Term Mobility 2009 (AMMCNT—CNR n. 0051228), RSTL-Ricerca Spontenea a Tema Libero of CNR (cod. 483) and MAMBA project (EU.FP6). AS Cabral was funded by a CNPq Post-doc scholarship, and R Paranhos was funded by CNPq, CAPES and FAPERJ.
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