Skip to main content
Advertisement
Browse Subject Areas
?

Click through the PLOS taxonomy to find articles in your field.

For more information about PLOS Subject Areas, click here.

  • Loading metrics

Sunlight Effects on the Osmotrophic Uptake of DMSP-Sulfur and Leucine by Polar Phytoplankton

  • Clara Ruiz-González ,

    clararg@icm.csic.es

    Affiliation Department of Marine Biology, Institut de Ciències del Mar-CSIC, Barcelona, Spain

  • Martí Galí,

    Affiliation Department of Marine Biology, Institut de Ciències del Mar-CSIC, Barcelona, Spain

  • Eva Sintes,

    Affiliation Department of Marine Biology, Faculty Center of Ecology, University of Vienna, Vienna, Austria

  • Gerhard J. Herndl,

    Affiliation Department of Marine Biology, Faculty Center of Ecology, University of Vienna, Vienna, Austria

  • Josep M. Gasol,

    Affiliation Department of Marine Biology, Institut de Ciències del Mar-CSIC, Barcelona, Spain

  • Rafel Simó

    Affiliation Department of Marine Biology, Institut de Ciències del Mar-CSIC, Barcelona, Spain

Abstract

Even though the uptake and assimilation of organic compounds by phytoplankton has been long recognized, very little is still known about its potential ecological role in natural marine communities and whether it varies depending on the light regimes the algae experience. We combined measurements of size-fractionated assimilation of trace additions of 3H-leucine and 35S-dimethylsulfoniopropionate (DMSP) with microautoradiography to assess the extent and relevance of osmoheterotrophy in summer phytoplankton assemblages from Arctic and Antarctic waters, and the role of solar radiation on it was further investigated by exposing samples to different radiation spectra. Significant assimilation of both substrates occurred in the size fraction containing most phytoplankton (>5 µm), sunlight exposure generally increasing 35S-DMSP-sulfur assimilation and decreasing 3H-leucine assimilation. Microautoradiography revealed that the capacity to take up both organic substrates seemed widespread among different polar algal phyla, particularly in pennate and centric diatoms, and photosynthetic dinoflagellates. Image analysis of the microautoradiograms showed for the first time interspecific variability in the uptakes of 35S-DMSP and 3H-leucine by phytoplankton depending on the solar spectrum. Overall, these results suggest that the role of polar phytoplankton in the utilization of labile dissolved organic matter may be significant under certain conditions and further confirm the relevance of solar radiation in regulating heterotrophy in the pelagic ocean.

Introduction

The ability to take up and utilize dissolved organic matter (DOM) as a source of carbon and energy (hereafter ‘osmoheterotrophy’) was demonstrated for a wide variety of algal cultures more than three decades ago (see refs. in [1], [2], [3]), yet it was initially thought to be ecologically irrelevant due to the inability of the algae to compete with bacteria at the low substrate concentrations found in natural environments [4], [5], [6]. Owing to their high surface to volume ratio and their efficient uptake systems, heterotrophic bacteria are regarded as the most efficient consumers of DOM [5], and consequently, phytoplankton osmoheterotrophy is neglected in most geochemical models of carbon flow [7], [8].

However, some studies have shown that several phytoplankton species do actively take up substrates at low concentrations so that they may, in fact, be competitive with bacteria [9], [10]. Among the organic substrates algae are able to use are pyruvate, acetate, lactate, ethanol, saturated fatty acids, glycolate, glycerol, hexoses, urea, and amino acids (e.g. [11], [12], [13], [14]). More recently, it was discovered that a variety of marine phytoplankton taxa can also take up the ubiquitous algal synthate dimethylsulfoniopropionate (DMSP) [15], [16] and assimilate its sulfur [15], thus influencing the cycling of organic sulfur in the surface ocean. These evidences, together with the phagotrophy described for many algal groups [17], [18], suggest that algae may play a more diverse role in aquatic biogeochemical cycles than just supplying heterotrophs with autotrophically synthesized organic matter. Moreover, while most studies on phytoplankton osmoheterotrophy have focused on algal cultures (which may not be representative of ecologically relevant organisms) and on freshwater or benthic systems, pelagic marine environments have received less attention and very little is known about the role of algal osmoheterotrophy in natural marine communities.

The uptake and assimilation of organic substrates by algae often increase with decreasing light availability [19], [20], although either enhanced uptake under light exposure [21], [22], [23] or no effect of irradiance on uptake rates [24], [25] have also been reported. Studies of algal osmoheterotrophy have commonly exposed cells to artificial light, and although some have considered in situ light conditions, to our knowledge none has specifically assessed the effect of natural solar ultraviolet radiation (UVR, 280–400 nm).

Research on the effects of UVR (and mainly UVB, 280–320 nm) on aquatic food webs has gained increasing attention, and this has been particularly so in the polar regions, where there is evidence that ozone depletion [26], [27] and the ongoing loss of sea-ice [28], [29] are leading to enhanced underwater levels of UVR. In these regions, the continuous darkness during the polar winter, the low irradiance under the sea ice layer and the relatively high concentrations of labile organic nutrients [30], [31] may select for algae with heterotrophic or photoheterotrophic capabilities. As an example, Rivkin and Putt [21] found that Antarctic algae incorporated amino acids and glucose at ambient concentrations and proposed that this ecological trait might supplement light-limited growth during the polar spring and summer as well as support heterotrophic growth throughout the polar winter.

The first aim of this work was to assess the occurrence and relevance of the utilization of dissolved organic compounds in natural marine phytoplankton assemblages during the Arctic and Antarctic summers by tracking the fate of two ubiquitous low-molecular-weight (LMW) dissolved organic compounds: leucine and DMSP. Our second aim was to address the effect of natural solar radiation on the uptake of these compounds by different phytoplankton groups. We combined measurements of size-fractionated radioisotope uptake and assimilation with a microautoradiographic approach to identify the organisms taking up the respective radiolabeled substrate. Image analysis of microautoradiograms allowed to determine group-specific substrate affinities and sensitivities to UVR. This study relates to our previous work on sunlight effects on the assimilation of these substrates by major bacterial groups in the same communities [32].

Methods

Study Area and Sample Collection

The study was carried out on board RV Hespérides during the ATOS I and II cruises to the Arctic and Antarctica (Fig. 1). In July 2007, ATOS I visited the Atlantic sector of the Arctic with a transect from Iceland, parallel to the eastern Greenland current, up to the ice cap edge (ca. 81°N) located north/northwest of Svalbard. In February 2009, ATOS II cruised around the Antarctic Peninsula, from the Weddell Sea (65°S) through the Bransfield Strait and into the Bellingshausen Sea (ca. 69°S). No specific permits were required for the described field studies. In Antarctic waters, the activities conducted met the requirements and protocols of the Antarctic Treaty as reviewed and approved by the Spanish Polar Committee. The locations of study were not privately-owned nor protected beyond the Antarctic Treaty, and the field studies did not involve endangered or protected species.

thumbnail
Figure 1. Map of the stations where different experiments were performed.

(A) Arctic stations, July 2007; (B) Antarctic stations, February 2009. Maps were generated with the Ocean Data View software (http://odv.awi.de).

https://doi.org/10.1371/journal.pone.0045545.g001

Samples for size-fractionated uptake and assimilation measurements and for microautoradiography were collected at 5 m depth (except for station AN2, sampled at 20 m depth, where high abundances of the diatom Pseudonitzschia were found) with a rosette of Niskin bottles mounted on a CTD profiler. Water characteristics of the sampled stations together with the irradiance measurements and time of incubation during experiments are compiled in Table 1.

Experimental Design

We performed a number of experiments (seven for size fractionated assimilation and four for microautoradiography, see below) to assess the impact of natural solar radiation on the heterotrophic activity of polar microalgae. Briefly, water samples were incubated in UVR-transparent quartz bottles amended with trace concentrations of 35S-DMSP (donated by R. P. Kiene, University of South Alabama, Dauphin Island Sea Lab, USA) or 3H-leucine (Amersham) under different light conditions. Bottles were either exposed to the full solar radiation spectrum (PAR+UVR), the full spectrum without UVB (i.e., PAR+UVA, covered with Mylar-D foil) or kept in the dark. Samples were incubated inside a black tank with running seawater to maintain in situ temperature. To simulate the irradiance level of 5 m depth, samples were placed 5 cm under the surface below an optically neutral mesh that reduced surface irradiances by 40%. Samples from station AN2 (20 m depth) were covered with a double neutral mesh that reduced surface irradiances by 60%.

Radiation Measurements

UVR and PAR radiation inside the incubation tank were continuously monitored throughout the incubations with a Biospherical PUV-radiometer 2500. The downwelling cosine irradiance reaching the samples was recorded at a frequency of 5 s−1. The wavelengths measured included one integrated band in the visible (PAR, 400–700 nm, µmol photons cm−2 s−1) and 6 channels within the UVR range (305, 315, 320, 340, 380, 395 nm, in mW cm−2 nm−1). The mean spectral irradiance in the 6 UVR bands was converted to mean UVB and UVA irradiance (mW cm−2) by integrating over the spectrum (sum of trapezoids), between 305–320 nm and 320–395 nm, respectively. Finally, the mean UVB, UVA and PAR irradiance was multiplied by the duration of each experiment in order to obtain the radiation dose (in kJ m−2 for UVB and UVA, and mol photons m−2 for PAR), shown for each experiment in Table 1.

Size Fractionated Assimilation

Samples of 50 ml were incubated for 7 to 12 h in quartz bottles with added trace concentrations of 35S-DMSP (845 Ci mmol−1, 0.8 pM final conc. for Arctic samples and 120–145 Ci mmol−1, 2.5–3 pM final conc. for Antarctic samples) or 3H-leucine (161 Ci mmol−1, 0.5 nM final conc.). Controls were killed with paraformaldehyde (PFA, 1% final conc.) before the addition of the radioactive compound and were exposed to the same conditions as live samples. After exposure, the incorporation of substrate was stopped by overnight PFA-fixation (1% final conc.) at 4°C in the dark, and duplicate or triplicate subsamples of 15–25 ml were filtered through 5 µm pore-sized filters (SMWP, Millipore); the filtrate was subsequently filtered through 0.2 µm pore-sized filters (GNWP, Millipore) and rinsed with 0.2 µm filtered seawater. The fraction collected on 0.2 µm filters was mainly comprised by prokaryotic cells, as revealed by microscopy. With the filtration system off, macromolecules were precipitated by pouring 5 ml of cold 5% trichloroacetic acid (TCA) onto the filters for 5 min. Then, the TCA was removed and the filters were rinsed with Milli-Q water. Radioactivity was determined by placing them into 5 ml of scintillation cocktail (Optimal HiSafe) and counting with a Beckman scintillation counter.

Microautoradiography of Algae

Samples of 50 ml were incubated under the different light treatments with added 35S-DMSP (845 Ci mmol−1, 0.04 nM final conc. for Arctic samples and 145 Ci mmol−1, 0.03 nM final conc. for Antarctic samples) or 3H-leucine (161 Ci mmol−1, 0.5 nM final conc.) for 7 to 12 h. Controls killed with PFA were also run simultaneously with all live incubations. After sunlight exposure, live samples were fixed overnight with PFA (1% final conc.) at 4°C in the dark. Aliquots of 15–20 ml were gently filtered through 5 µm polycarbonate filters (Osmonics, inc.), rinsed with Milli-Q water, air dried and stored at −20°C until processing. Microautoradiography of 35S-DMSP samples from station AN2 could not be performed due to an insufficient amount of the radiolabeled substrate used.

Microautoradiography was carried out as described by Vila-Costa et al. [15]. Filters were developed after 6 d for 3H-leucine and 18 d for 35S-DMSP in Arctic samples, and 20 d for 3H-leucine and 2 mo for 35S-DMSP in Antarctic samples, and stained with 4,6-diamidino-2-phenylindole (DAPI, 1 µg ml−1). Labeled cells were counted under an Olympus BX61 epifluorescence microscope within the major groups showing consistent uptake of any of the substrates. Active and inactive cells were clearly distinguished by the presence or absence of silver grain accumulations denser than the background. Between 30 and 700 cells were considered for obtaining the percentages of active cells. Epifluorescence microscopy combined with scanning electronic microscopy was used to identify the eukaryotic microorganisms present in our samples.

Image Analysis of the Silver Grain Area Surrounding Active Algal Cells

We followed the protocol described by Sintes and Herndl [33] with some modifications for algal images. For each individual cell, three images were acquired: one of the alga stained with DAPI, one of the fluorescence of chlorophyll (both in epifluorescence mode of a Zeiss Axioplan 2 microscope) and a third image of the silver grains by switching to the transmission mode of the microscope. The images were acquired with a digital camera (AxioCam MRc5) mounted on the microscope. Pictures were taken of 20 to 60 cells per phytoplankton group and treatment. Overlapping signals in the DAPI + chlorophyll images and the transmitted light images (silver grains) indicated cells that had assimilated 35S from DMSP or 3H from leucine. Image analyses were conducted with the KS300 3.0 software (Carl Zeiss), which allowed us to record the area of each cell, as well as the silver grain area around it. Several, but not all the algal groups were considered for this analysis. In the Arctic experiments, the five groups analyzed were two pennate diatoms (Pseudonitzschia spp., Navicula spp.), a group of centric diatoms (Thalassiosira spp.), photosynthetic dinoflagellates (mainly Prorocentrum spp., although other species were also included), and the dominant flagellate Phaeocystis sp. From Antarctic waters (Station AN1), Pseudonitzschia spp., three different species of Thalassiosira (spp. A, B and C) with distinct size and chloroplast distribution, and a group of unidentified heterotrophic nanoflagellates were considered. The latter were the only heterotrophic organism analyzed, as they were the ones showing by far the largest 35S-silver grain areas at that station. For background correction, three pictures from each filter were taken of an area containing no cells, and the averaged silver grain area per background area was subtracted from the average silver grain area per cell area measured for each algal group. 3H-leucine samples from station AR3 and AN2 were not analyzed since too few cells were labeled.

Additionally, DAPI-stained bacteria retained onto these filters were counted in order to estimate their contribution to apparent algal substrate uptake. Since many occurred on aggregates, silver grains could not be attributed to individual bacteria, but an estimated mean silver grain area per bacterial cell was obtained by dividing the silver grain area by the number of bacterial cells in the aggregate.

Statistical Analyses

Shapiro-Wilk’s W-test for normality of data and Levene’s test for homogeneity of variance were applied prior to analysis, and either ANOVA or the nonparametric Kruskal-Wallis test was used to address statistically significant differences (p<0.05) in the measured variables. Post hoc analyses (Tukey’s test) were applied for comparison among different light treatments. Correlations between variables were calculated using the Pearson’s correlation coefficient. These statistical analyses were performed using the JMP software (SAS Institute).

Results

Background Information

The waters sampled during the two cruises displayed varying temperature (range −0.73–3.22°C) and salinity values (range 26.9–34.3) depending on the influence of the ice-melting (Table 1). While in Arctic waters there was a prevalence of the flagellate Phaeocystis sp., diatoms were the dominant phytoplankton in Antarctic stations. The four stations selected for microautoradiographic analyses from both cruises displayed elevated phytoplankton abundances typical of summer blooms.

Bulk Assimilation of 3H-leucine and 35S-DMSP by Size-fractionated Plankton

The assimilation of both 3H-leucine and 35S-DMSP by differently sized microorganisms was measured by fractionating the samples through 5 µm and 0.2 µm filters after incubation with these radiotracers under different light spectra. For a general view, the results of the dark incubations are presented in Figure 2. While leucine assimilation by organisms >5 µm was significantly higher than in the size fraction 0.2–5 µm in 8 out of 12 stations (p<0.05, Fig. 2A), assimilation of 35S-DMSP was always significantly lower in the 0.2–5 µm fraction (Fig. 2B), which mainly comprised heterotrophic bacteria.

thumbnail
Figure 2. ‘Algal’ vs. ‘bacterial’ assimilation of 3H-leucine and 35S-DMSP.

Comparison between the percentages of assimilated 3H-leucine (A) and 35S-DMSP (B) of total added substrate by organisms >5 µm (grey bars) and 0.2–5 µm organisms (black bars) measured at different stations (average ± standard errors). All incubations were performed in the dark. Asterisks (*) indicate significant differences between both fractions (ANOVA, p<0.05).

https://doi.org/10.1371/journal.pone.0045545.g002

Sunlight Effects on Substrate Assimilation by Organisms >5 µm

The results of the subset of incubations performed also under PAR and UVR light are presented in Fig. 3. Exposure to the full spectrum of solar radiation (including UVB) caused a significant (Tukey’s test, p<0.05) reduction of 3H-leucine assimilation by organisms >5 µm compared to dark treatments at all stations except AN2 (range 20% to 75% decrease, Fig. 3A). Removal of UVB from the solar spectrum yielded higher assimilation percentages, yet never exceeding those of the dark controls. Interestingly, this variability in UVB-induced inhibition of 3H-leucine uptake was significantly correlated with the measured UVB doses during experiments (Pearson’s r = 0.88 and r = 0.89, p<0.01, n = 7, compared to dark and PAR+UVA (Fig. 4A) treatments, respectively). Conversely, assimilation of 35S-DMSP by organisms >5 µm were consistently stimulated by light exposure (Fig. 3B), showing up to 33% and 45% increases due to PAR+UVA and full sunlight exposure, respectively, compared to the dark control (p<0.05). At three stations (AR5, AR6 and AN2), the full spectrum of solar radiation significantly inhibited the uptake of DMSP compared to PAR+UVA (Fig. 3B) but none of these responses appeared to be directly related to the light doses (Fig. 4B).

thumbnail
Figure 3. Effects of solar radiation on substrate assimilation.

Percentages of assimilated 3H-leucine (A) and 35S-DMSP (B) of total added substrate by organisms >5 µm measured after exposure to the following radiation conditions: PAR+UVA (dashed bars), PAR+UVR (white bars) and darkness (black bars). Values are averages ± standard errors. Letters refer to results with a post hoc Tukey’s test. Different letters indicate significant differences (p<0.05) among treatments.

https://doi.org/10.1371/journal.pone.0045545.g003

thumbnail
Figure 4. UVB doses versus inhibition of substrate incorporation.

Relationships between the UVB-driven changes in the incorporation of (A) 3H-leucine or (B) 35S-DMSP and the UVB doses received by Arctic (black circles) and Antarctic (open circles) samples during each experiment.

https://doi.org/10.1371/journal.pone.0045545.g004

Differential Assimilation of 35S-DMSP and 3H-leucine by Phytoplankton Taxa

Microautoradiography was applied to 5 µm filters from four selected stations (AR3, AR4, AN1 and AN2) to determine which phytoplankton phyla, if any, were responsible for the detected assimilation of leucine and DMSP. We observed that in most stations 35S-DMSP and 3H-leucine uptake was widespread among diverse algal groups (Table 2). Percentages of active cells were obtained combining the three light treatments, since generally it was not the number of active algae, but the size of the silver grain area, which differed significantly among the light treatments. Only some groups displayed significantly different numbers of active cells among treatments (p<0.05), written in bold in Table 2: while Phaeocystis spp. (AR3 and AR4) and photosynthetic dinoflagellates (AR3) exhibited higher numbers of active cells in 35S-DMSP uptake upon dark incubation compared to the light treatments, Pseudonitzschia spp. from stations AR3 and AN1 showed higher uptake after PAR+UVA or both light treatments, respectively (p<0.05). Instead, 3H-leucine uptake by Pseudonitzschia spp. from AN1 was inhibited by light incubation. Estimates of abundances and ranges of cell areas within each group are also indicated in Table 2.

thumbnail
Table 2. Most common microorganisms identified at the different stations.

https://doi.org/10.1371/journal.pone.0045545.t002

At the two Arctic stations (AR3 and AR4) the flagellate Phaeocystis sp. dominated the phytoplankton assemblage (Table 2, see also [34]), co-occurring with both photosynthetic (mainly Prorocentrum spp.) and heterotrophic dinoflagellates (AR3), or pennate and centric diatoms (AR4, where Pseudonitzschia spp. was nearly as abundant as Phaeocystis sp.). Except the dominant Phaeocystis sp., which hardly ever appeared labeled, most of the analyzed groups showed high uptake of either one or both substrates, although the majority exhibited more cells active in 35S-DMSP uptake (Table 2). Clearly defined silver grain areas around cells were found upon incubation with 35S-DMSP, whereas the label for 3H-leucine was generally restricted to fewer Arctic groups.

Some typical 35S-DMSP autoradiograms from the Arctic samples are shown in Fig. 5. Diatoms such as Pseudonitzschia spp. (Fig. 5A) or Navicula (Fig. 5D) appeared intensely labeled. Clusters of well-localized silver grains also occurred in association with single or clumped bacteria that were attached to Phaeocystis mucus and thus were retained on the 5 µm filters (Fig. 5F). In all cases, prokaryotic cells were clearly visible due to DAPI staining and few bacteria adhering to live microalgae were sometimes present. For the enumeration of DMSP- or leucine-positive algae, only those devoid of attached bacteria were counted. Negligible numbers of labeled algal cells (<1%) were found in the killed controls.

thumbnail
Figure 5. Microautoradiograms showing uptake of 35S-DMSP by different planktonic organisms in Arctic samples.

(A) Pseudonitzschia sp.; (B) Protoperidinium sp.; (C) unidentified photosynthetic dinoflagellate; (D) Navicula sp. (E) unlabelled Phaeocystis sp. Black dots surrounding cells indicate uptake of the radioactive substrate by algae. (F) Clusters of well-localized silver grains occurred in association with single or clumped bacteria attached to Phaeocystis mucus and thus retained onto the 5 µm filters. Scale bar represents 10 µm.

https://doi.org/10.1371/journal.pone.0045545.g005

Remarkably, the flagellate Phaeocystis sp., the dominant bloom former and DMSP producer in these waters, was only slightly labeled with 35S in the dark, but the signal was much weaker than that of the other algal groups (Fig. 5E).

The Antarctic stations AN1 and AN2 strongly differed in their phytoplankton composition. While a large number of Thalassiosira-like centric diatoms were found at station AN1, station AN2 was almost completely dominated by Pseudonitzschia spp. (Table 2). Microautoradiography was performed with both 35S-DMSP and 3H-leucine on samples of station AN1, while at station AN2, only 3H-leucine was used. In contrast to what was found for Arctic algae, 35S-DMSP silver grain areas were small for most groups at AN1 except for the heavily labeled small heterotrophic nanoflagellates. The large diatoms (Chaetoceros spp., Eucampia spp., Lithodesmium spp., Corethron spp. and some big Thalassiosira [spp. C and D]) showed clear preference for leucine over DMSP as illustrated by the high numbers of active cells (Table 2) and dense silver grain areas around them. Examples of leucine microautoradiograms of Antarctic algae are shown in Fig. 6. At station AN2, however, most of the radiolabel was associated with heterotrophic bacteria. Barely any of the dominant Pseudonitzschia, but just a few centric diatoms and heterotrophic dinoflagellates seemed to take up leucine.

thumbnail
Figure 6. Microautoradiograms showing uptake of 3H-leucine by different planktonic algae in Antarctic samples.

(A) Unlabelled Thalassiosira sp.B (left) and sp.C (right).; (B) Chaetoceros sp.; (C) Corethron sp.; (D) Eucampia sp. Note that the isotope seems to be specifically incorporated in structures such as chloroplasts (arrows in B and D). Scale bar represents 10 µm. (E and F) Examples of image analysis process. Three cells, shown under transmitted light in the left are digitized and nucleus, cell area and silver grain regions are identified, marked with different colours, and then sized (see Methods). Scale bar represents 10 µm.

https://doi.org/10.1371/journal.pone.0045545.g006

Differential Sensitivity to Solar Radiation among Phytoplankton Groups

Microautoradiograms of 5 µm filters were subjected to image analysis to provide insight into the effects of sunlight on the uptake of these two organic compounds by some common groups of phytoplankton. Unfortunately, neither all groups nor all samples could be analyzed due to size or abundance limitations. In spite of the methodological uncertainties (see Discussion), we found group-specific responses to either substrate or light (Fig. 7). The pennate diatom Pseudonitzschia spp. from the Arctic, the one with the largest silver grain area per cell for 35S-DMSP, showed a significant increase (60% and 72% at Stn. AR3 and AR4, respectively, p<0.05) in the uptake of DMSP when exposed to PAR+UVA as compared to dark and full solar radiation conditions. Interestingly, although microautoradiograms from station AN2 are not available, the 35S-DMSP assimilated by the largest fraction, almost entirely comprised by Pseudonitzschia spp., also exhibited highest DMSP uptake in the PAR+UVA treatment (Fig. 3B). Navicula spp. at station AR4 also showed this pattern. In contrast, both light treatments significantly inhibited their 35S-DMSP uptake at station AR3. Generally, dark conditions seemed to stimulate 35S incorporation in the rest of the algal groups from station AR3 and AR4 (Figs. 7A and 7B), while most organisms from AN1 showed a significant photostimulation of 35S-DMSP uptake caused by both light treatments (Fig. 7C, p<0.05). Small heterotrophic nanoflagellates were also included for comparison since they presented the greatest silver grain areas (Fig. 7C), yet they did not show significantly different areas among light treatments (p>0.05).

thumbnail
Figure 7. Sunlight effects on group-specific assimilation of 3H-leucine and 35S-DMSP.

Average silver grain area per active algal cell in 35S-DMSP or 3H-leucine uptake as measured by image analysis of microautoradiograms (average ± standard error of 20 to 60 single cells) in 5 µm filters. Stn. AR3, AR4 and AN1, 35S-DMSP samples (A, B and C); Stn. AR4 and AN1, 3H-leucine samples (D and E). Samples were incubated under the following radiation conditions: PAR+UVA (dashed bars), PAR+UV (white bars) and darkness (black bars). Note the break in the Y axes in figures C and D. [Ps] Pseudonitzschia spp; [Nav] Navicula spp.; [ThA,B,C] Thalassiosira spp.A, B, C; [Din] Photosynthetic dinoflagellates; [Ph] Phaeocystis spp. [HNf] Heterotrophic nanoflagellates. Letters refer to results with a post hoc Tukey’s test. Different letters indicate significant differences (p<0.05) among treatments.

https://doi.org/10.1371/journal.pone.0045545.g007

The uptake of 3H-leucine by Thalassiosira spp. at station AR4 was negatively affected by full sunlight (Fig. 7D, p<0.05), whereas no significant differences between the light treatments and the dark controls were observed for Pseudonitzschia spp. At station AN1, exposure to sunlight consistently inhibited their activity, but only Thalassiosira (sp. B) showed a clear negative effect of UVB compared to PAR+UVA exposure (Fig. 7E, p<0.05).

Relative Contribution of Algal Groups and Bacteria to Substrate Uptake

The group-specific responses were calculated as the mean silver grain area around each group cells multiplied by the abundance of its active cells, and divided by the total sum of silver grain areas of the groups considered for image analysis. The patterns shown in Fig. 7 imply different relative contributions to total measured silver grain area among stations (Fig. 8A, B) and treatments (Table 3). This summed silver grain area can be considered as a proxy for the total algal uptake of 35S-DMSP or 3H-leucine provided that linearity between silver grain area and bulk incorporation is hold over time (see Discussion).

thumbnail
Figure 8. Estimated contribution of different organisms to total assimilation and biomass.

Average relative contribution of each of the analyzed groups to the total silver grain area (as % of the sum of the silver grain area associated with all the considered groups) for 35S-DMSP (A) or 3H-leucine samples (B). (C) Relative contribution of each of the analyzed groups to total phytoplankton biomass (as % of the sum of cell areas of all the individuals of the considered groups). All estimates are averages of the three treatments.

https://doi.org/10.1371/journal.pone.0045545.g008

thumbnail
Table 3. Relative contribution of the analyzed groups to the total silver grain area after exposure to the different light treatments.

https://doi.org/10.1371/journal.pone.0045545.t003

Additionally, an estimated contribution of each group to total biomass was calculated by multiplying the average cell area by the abundance of each group divided by the total sum of analyzed cell areas (Fig. 8C). Among these groups, Arctic Pseudonitzschia spp. accounted for a significant (stn. AR3) or even dominant (stn. AR4) contribution to total incorporation of 35S-DMSP or 3H-leucine, especially upon light exposure (Figs. 8A, B, Table 3), which was much higher than expected based on their relative abundances (Fig. 8C). Consequently, the contribution of the rest of the groups decreased under PAR+UVA or UVR and PAR +UVA conditions. The less active Pseudonitzschia at AN1 contributed only marginally to the uptake of either substrate (Fig. 8A, Table 3). At the Arctic stations, although the specific uptake of 35S-DMSP by Phaeocystis sp. was low (or totally absent under light incubations), its high abundance resulted in a substantial contribution (∼7–12%) to total uptake in the dark (Figs. 8A, C, Table 3). At station AN1, the low contribution of heterotrophic nanoflagellates to total cell biomass (<2%) contrasted with their high representation among the considered 35S-DMSP- or 3H-leucine-assimilating cells (up to 30% or 10%, respectively, Fig. 8A, B). The highly labeled, large Thalassiosira sp. C cells were responsible for most of the 3H-leucine silver grain area around algae (Fig. 8B), even more so under UVR exposure (Table 3). It must be noted, though, that the presence of heavily labeled large diatoms that could not be quantified for uptake, such as Chaetoceros spp. or Eucampia spp., suggests that the relative contributions of the counted organisms to total 3H-leucine uptake shown in Fig. 8B are most likely overestimates.

Bacterial Contribution to Substrate Assimilation

In an attempt to estimate the contribution of heterotrophic bacteria to the uptake of the >5 µm fraction, we also quantified the silver grain area associated to the filter-retained prokaryotes. In general, their contribution to 35S-DMSP uptake was small (station AR3) to negligible (AR4 and AN1, Table 4, Fig. 8A) compared to that of the considered algal groups together. Conversely, their contribution to 3H-leucine uptake was as high as 79% and 26% at stations AR4 and AN1, respectively (Table 4), yet, as abovementioned, these latter values are overestimates because not all eukaryotic algae could be measured for their silver grain areas.

thumbnail
Table 4. Comparison between the relative contribution of prokaryotic and phytoplankton cells within 5 µm filters.

https://doi.org/10.1371/journal.pone.0045545.t004

Discussion

The osmotrophic uptake of organic compounds is believed to supplement autotrophic energy gain in algae, particularly in deep waters, systems with high allochthonous inputs or polar areas where algae need to survive during the long aphotic winter [1], [21], [22]. However, the spread and importance of DOM uptake by phytoplankton in natural marine communities and how it is influenced by natural radiation conditions still remain unclear. Our results show for the first time a direct effect of natural PAR and UVR levels on the uptake of 3H-leucine and 35S-DMSP by different phytoplankton taxa. Moreover, they provide the second evidence of 35S-DMSP uptake by natural marine eukaryotic phytoplankton assemblages, after Vila-Costa et al. [15].

‘Algal’ Versus ‘bacterial’ Assimilation of 3H-leucine and 35S-DMSP

Across the regions studied, the >5 µm fraction showed a frequent dominance of the assimilation of 3H-leucine and 35S-DMSP. This unexpected finding, which is opposite to the commonly found dominance of the smallest size fractions (mainly bacterioplankton) in the uptake of organic compounds [25], [35], points to a potentially important role of polar eukaryotic phytoplankton as low molecular weight (LMW)-DOM consumers.

The uptake of both leucine and DMSP was initially thought to be specific for heterotrophic bacteria [36], [37], yet several studies have demonstrated that different algal and cyanobacterial species can take up and assimilate either leucine [11], [22] or reduced sulfur from DMSP [15], [38], [39]. Algae are known to use different amino acids as carbon and nitrogen sources or to meet their cellular nitrogen demands, particularly when inorganic nitrogen is scarce [14], [40]. But very little is still known about the magnitude of algal DMSP assimilation in natural communities, its ecophysiological function, and how it influences the cycling of organic sulfur in the surface ocean and whether it can potentially regulate the emissions of volatile sulfur to the atmosphere.

Sunlight Effects on the Bulk Assimilation by Organisms >5 µm

When samples amended with 3H-leucine were incubated under different light treatments, a general decrease in the incorporation by the >5 µm size fraction was observed towards full spectrum conditions. Interestingly, this inhibition was correlated with the UVR doses received by samples during incubations, suggesting that, similarly to what is observed for bacteria [41], the osmotrophic uptake of leucine by phytoplankton is negatively affected by solar radiation. Several experiments have also shown light-driven effects on the uptake of leucine by phytoplankton cells, yet depending on the species tested, either photostimulation or photoinhibition of uptake or consumption were reported [10], [21]. However, none of these experiments considered UVR exposure. On the other hand, the observed changes in 35S-DMSP assimilation are in accordance with the light-driven enhancement of this activity reported elsewhere for diatoms and picophototrophs [15], [38]. Unlike for leucine, the light-driven effects on DMSP assimilation were not related to irradiance levels, suggesting that DMSP-sulfur assimilation may be indirectly influenced by more complex, yet still poorly known, light-driven DMSP production, release and consumption dynamics (e.g. [42], [43]). In particular, the described antioxidant function of DMSP [44] might partially explain the observed light driven increases in its accumulation, yet it remains to be tested whether this function can be attained through the uptake of DMSP besides intracellular production [43].

Widespread Algal Uptake of Organic Compounds by Taxonomic Groups

Whereas size fractionation may lead to inaccurate estimates of phytoplankton DOM-uptake since it does not completely separate algae from bacterial aggregates, attached bacteria, detritus or protozoa, autoradiographic surveys permit the rapid screening of algal populations taking up specific substrates (e.g. [40], [45]). Microautoradiography of 5 µm filters revealed an unexpected widespread capacity to take up both 3H-leucine and 35S-DMSP among a variety of algal phyla, mainly diatoms and photosynthetic dinoflagellates. While many Arctic phytoplankton groups were intensely labeled for 35S, the taxa present at the Antarctic station AN1 displayed lower numbers of active cells with weaker silver grain areas. This high uptake of 35S-DMSP in the Arctic might be related to the high DMSP supply rates released by the blooming Phaeocystis sp. [46] compared to the lower DMSP concentrations found in the sampled Antarctic waters (M. Galí et al., unpublished). Supporting this idea, Vila-Costa et al. [15] found higher numbers of Mediterranean 35S-assimilating diatoms in summer, when DMSP comprised a larger share of total sulfur and carbon fluxes. Accordingly, low- or non-DMSP producing diatoms (e.g. Pseudonitzschia spp.) would consume DMSP released by their high producing phytoplankton counterparts such as Phaeocystis sp. Should DMSP uptake supply energy, carbon or sulfur for growth, a DMSP-rich environment like summer Arctic waters might favor algal species capable of utilizing this substrate.

At the Antarctic station AN1, conversely, weak silver grain areas were usually observed for 35S-DMSP. Instead, great numbers of big diatoms (Chaetoceros spp., Eucampia spp., Thalassiosira spp.) appeared intensely labeled for 3H-leucine uptake. Finally, at station AN2, most of the signal was associated with the bacteria retained on the 5 µm filter and none of the blooming Pseudonitzschia appeared labeled for leucine.

Altogether, our findings highlight the helpfulness of single-cell resolution techniques to avoid misinterpretation of bulk assimilation data, and suggest that the osmotrophic uptake by phytoplankton should be considered when bulk bacterial activity measurements are conducted and interpreted. Since bacterial activity assays are generally performed in the dark, and darkness consistently led to the greatest uptake of 3H-leucine by phytoplankton, bacterial production may be overestimated depending on the abundance and activity of co-occurring phytoplankton.

It is not clear whether microautoradiography reflects actual assimilation (incorporation of the radiolabel into macromolecules) or just uptake. Organic molecules may enter a cell but fail to be metabolized at all, in which case they just accumulate in the cytoplasm [16], [47]. Samples were fixed with PFA after exposure to the radioisotopes, a process believed to cause cells to loose cytoplasm [48], so the fact that the autoradiographic signal remained after fixation points to substantial substrate assimilation. Moreover, the specific labeling patterns observed for some diatoms, which showed silver grains of 3H-leucine specifically associated with structures such as chloroplasts and nucleus, suggests incorporation of the amino acid into cellular macromolecules rather than simple uptake (see arrows in figs. 6B and D).

Inter-group Variability in Algal Responses to Sunlight

In the microautoradiograms of algal samples subjected to image analysis, the differences in the silver grain area around cells were considered to reflect the effects of natural sunlight on the assimilation of these two organic compounds. The previously demonstrated linear relationship between silver grain areas and bulk incorporation of 3H-leucine allows comparison provided that incubation and exposure conditions are kept the same [33]. However, when organisms are very active, this linearity may be lost since after a while silver grain areas become denser but not larger, a fact that cannot be always detected by image analysis. In complex samples like ours, it is possible that some groups displayed higher uptake velocities than others and that this linearity was not maintained over time for all of them. Therefore, our results must be regarded as trends and general patterns, but not as absolute values or incorporation rates. In any case, the lack of linearity would lead to reduced differences among groups or treatments, or a misdetection of the whole range of variation, but not to an artifactual creation of the observed differences.

Quantification of the silver grain areas around cells revealed a variety of group-specific responses to sunlight which further varied depending either on the substrate or the station considered. Taken together, it appeared that natural irradiance levels were significantly influencing the osmoheterotrophic activity of the studied phytoplankton assemblages. However, since a given group responded differently depending on the substrate analyzed (i.e., photostimulation for 35S-DMSP and photoinhibition for 3H-leucine) these results cannot be solely considered as an indication of an inhibitory effect of UVR on the activity of the organism. Besides the potentially differential damage of UVR onto uptake systems [49], several other mechanisms have been proposed for the observed light-driven effects on DOM uptake by phytoplankton. Algal utilization of amino acids has been shown to be most significant in the absence of photosynthesis, e.g., in turbid waters, in dark incubations or at night [10], [50], [51], [52]. It has been suggested that, during the day, the products of photosynthesis and the uptake of nitrate, ammonium or urea restrict the uptake of amino acids by increasing the intracellular amino acid pool [51]. A lower uptake in the light could also be due to dilution of the labeled substrate with newly photosynthesized substrate, or to transport systems under repression by photosynthesis catabolites [6]. Thus, factors other than the light conditions, such as the natural substrate concentration and maybe the past environmental history of the algae affect each species’ ability to assimilate organic substrates.

Our observation that 35S-DMSP uptake by various algal groups is enhanced by light could suggest that the photosynthetic apparatus harvests light and transfers this energy into ATP that is used for supplementary powering the active uptake of DMSP. Alternatively, an increased DMSP release by UVR-stressed algae [43], [44] might activate the uptake systems of their low DMSP-producing counterparts. Finally, the potential use of DMSP as an antioxidant [43] might explain its accumulation under light conditions. In any case, this light-driven algal DMSP uptake (also observed in the size fractionated assimilation) would lead to higher shares in the hitherto overlooked contribution of eukaryotic phytoplankton as a DMSP sink, particularly in the long daylight of the polar summer.

Relative Contribution of Algal Groups and Bacteria to Substrate Uptake

In spite of the aforementioned limitations of the method, image analysis of silver grain and cellular areas allowed a rough estimation of each group’s contribution to the measured substrate uptake. As seen by the different patterns shown by figures 8A, B and C, this contribution was hardly ever related to the group’s contribution to biomass, highlighting a diversity of roles in phytoplankton osmoheterotrophic activity that cannot be predicted from their abundances alone. This, joined to each group’s differential responses to sunlight, suggests that solar radiation may modulate not only the quantity but also the direction of the fluxes of some organic compounds through the different compartments of the microbial food webs.

The silver grain areas associated with 5 µm-retained bacteria were also quantified in order to estimate their contribution to the substrate assimilation regarded as ‘algal’. On average, retained bacteria comprised <4% of the total bacterial abundance in the Arctic waters and 9–16% in the Antarctic stations [32]. Altogether, our results suggest that phytoplankton were responsible for the vast majority of the 35S-DMSP assimilation in the 5 µm fraction, whereas these aggregated or attached bacteria contributed a major proportion of 3H-leucine assimilation (AR3, AR4 and AN2 samples), except at station AN1 where big diatoms labeled for 3H-leucine were abundant. In any case, since not all phytoplankton groups were analyzed, these observations are most likely overestimates of the interfering role of associated bacteria in leucine assimilation by the algal fraction.

It has been proposed that sunlight has the potential to favor picophytoplankton in their competition for DMSP uptake against heterotrophic bacteria, as observed for the Mediterranean cyanobacterium Synechococcus [39]. Since free-living heterotrophic bacteria from the same polar stations mostly showed non-significant or negative light-driven effects in their number of 35S-labelled cells (see Table 4 in [32]), it is likely that the observed photostimulation of certain algal groups would also lead to an increased competition of eukaryotic phytoplankton for total DMSP uptake relative to that of bacteria. In view of the differential responses and substrates affinities, though, this process will be strongly dependent on the identity of the organisms involved.

Our findings confirm a major role of solar radiation on DMSP dynamics in the ocean [53], [54], but they unveil a new mechanistic twist: depending on the microbial consortia, light levels may favor DMSP-sulfur uptake by a fraction of the eukaryotic phytoplankton assemblage, thus diverting DMSP from being further catabolized into volatile DMS. Thus, sunlight simultaneously favors [55] and hampers [this work] DMS production, inhibits microbial DMS consumption and destroys DMS through photolysis [56]. This DMS cycle is a paradigmatic example of how sunlight and biogeochemical processes in the pelagic ocean are so intimately entangled in processes and counter-processes that result in largely buffered dynamics [57].

Part of the radioisotope incorporation by algae could have occurred through bacterivory or phagotrophy. Members of the dinophytes, cryptophytes and haptophytes have been shown to feed on bacteria or other algae [17], [18], [58] whereas diatoms do not. Diatoms, particularly polar species that have to survive long winter darkness, are known for their dark survival potentials [59], [60], [61] with facultative heterotrophy as one of their strategies. Therefore, since diatoms were major contributors to 35S-DMSP uptake in the studied stations (Fig. 8A), an important fraction of the substrate uptake must have occurred by osmoheterotrophy rather than phagotrophy. Yet, uptake by non-diatom ingestion of 35S- or 3H-labeled bacteria or small algae cannot be totally discarded, and bacterivory can also be regulated by light [62], [63]. Small heterototrophic nanoflagellates at station AN1 could have been grazing on bacteria and, interestingly, their responses to light were similar to those of particular bacterial groups from this station labeled for the same substrates (see Figs. 3 and 4 in [32]). Conversely, large hetero- or phototrophic Arctic dinoflagellates such as Protoperidinium spp. (Fig. 5B), Prorocentrum spp. and Leucocryptos marina appeared intensely labeled for 35S-DMSP but not for 3H-leucine. This suggests that either osmotrophic uptake [64] or grazing on other algae, but not bacterivory, was a major source of the 35S label found in these other groups.

Overall, our findings support the notion of a major and widespread heterotrophic activity within phytoplankton assemblages in summer Arctic and Antarctic waters. The use of autoradiography combined with size-fractionated assimilation offers a way to screen mixed phytoplankton populations for heterotrophic potential, revealing distinct affinities and behavioral trends in polar algae with regard to 3H-leucine and 35S-DMSP uptake and solar radiation. Future experiments combining different incubation times with measurements of assimilation and silver grain areas should allow a more quantitative assessment of this phenomenon, a necessary step to introduce algal osmoheterotrophy into elemental budget and numerical simulations of the planktonic food web.

Acknowledgments

We are very grateful to R. Scharek, H. Sarmento, N. Sampedro, M. and J.M. Fortuño for their valuable help with identification of phytoplankton taxa, and to O. Armangué for his very helpful assistance with filter processing. We also thank all scientists, technicians and crew of the R/V Hespérides for their cooperation during both cruises, and specially A. Lana for her assistance during on-deck experiments. We are indebted to R.P. Kiene (University of South Alabama) for kindly providing 35S-DMSP.

Author Contributions

Conceived and designed the experiments: RS CRG JMG. Performed the experiments: CRG MG. Analyzed the data: CRG ES GJH MG. Contributed reagents/materials/analysis tools: RS JMG GJH. Wrote the paper: CRG.

References

  1. 1. Droop MR (1974) Heterotrophy of carbon. In: Stewart WP, editor. Algal Physiology and Biochemistry. Oxford: Blackwell. 530–559.
  2. 2. Neilson AH, Lewin RA (1974) The uptake and utilization of organic carbon by algae: an essay in comparative biochemistry. Phycologia 13: 227–264.
  3. 3. Amblard C (1991) Carbon heterotrophic activity of microalgae and cyanobacteria: ecological significance. Ann Biol-Paris 30: 6–107.
  4. 4. Wright RT, Hobbie JE (1965) The uptake or organic solutes in lake waters. Limnol Oceanogr 10: 22.
  5. 5. Wright RT, Hobbie JE (1966) Use of glucose and acetate by bacteria and algae in aquatic ecosystems. Ecology 47: 447–464.
  6. 6. Hellebust JA (1970) The uptake and utilization of organic substances by marine phytoplankters. In: Hood DW, editor. Symposium on organic substances in natural waters. Inst. Marine Sci. Occassional Publ. No. 1. University of Alaska, Fairbanks. 225–526.
  7. 7. Azam F, Cho BC (1987) Bacterial utilization of organic matter in the sea. In: Fletcher M, editor. Ecology of Microbial Communities. Cambridge, UK: Cambridge University Press. 261–281.
  8. 8. Thingstad TF (2003) Physiological models in the context of microbial food webs. In: Findlay SEG, Sinsabaugh RL, editors. Aquatic Ecosystems: interactivity of dissolved organic matter. San Diego, USA: Academic Press. 383–397.
  9. 9. Kamjunke N, Kohler B, Wannicke N, Tittel J (2008) Algae as competitors for glucose with heterotrophic bacteria. J Phycol 44: 616–623.
  10. 10. Kamjunke N, Tittel J (2008) Utilisation of leucine by several phytoplankton species. Limnologica 38: 360–366.
  11. 11. Parker BC, Bold HC, Deason TR (1961) Facultative heterotrophy in some Chlorococcacean algae. Science 133: 761–763.
  12. 12. Lewin J, Hellebust JA (1976) Heterotrophic nutrition of the marine pennate diatom Nitzschia angularis var. afiinis. Mar Biol 36: 313–320.
  13. 13. Amblard C (1991) Carbon heterotrophic activity of microalgae and cyanobacteria: ecological significance. Ann Biol-Paris 30: 6–107.
  14. 14. Bronk DA, See JH, Bradley P, Killberg L (2007) DON as a source of bioavailable nitrogen for phytoplankton. Biogeosciences 4: 283–296.
  15. 15. Vila-Costa M, Simó R, Harada H, Gasol JM, Slezak D, et al. (2006) Dimethylsulfoniopropionate uptake by marine phytoplankton. Science 314: 652–654.
  16. 16. Spielmeyer A, Gebser B, Pohnert G (2011) Investigations of the uptake of dimethylsulfoniopropionate by phytoplankton. ChemBioChem 12: 2276–2279.
  17. 17. Jones RI (1994) Mixotrophy in planktonic protists as a spectrum of nutritional strategies. Mar Microb Food Webs 8: 87–96.
  18. 18. Raven JA (1997) Phagotrophy in phototrophs. Limnol Oceanogr 42: 198–205.
  19. 19. Hellebust JA (1971) Glucose uptake by Cyclotella cryptica: dark induction and light inactivation of transport system. J Phycol 7: 345–349.
  20. 20. Flynn KJ, Butler I (1986) Nitrogen sorces for the growth of marine microalgae: role of dissolved free amino acids. Mar Ecol-Progr Ser 34: 281–304.
  21. 21. Rivkin RB, Putt M (1987) Heterotrophy and photoheterotrophy by antarctic microalgae light-dependent incorporation of amino acids and glucose. J Phycol 23: 442–452.
  22. 22. Paerl HW, Bebout BM, Joye SB, Marais DJD (1993) Microscale characterization of dissolved organic matter production and uptake in marine microbial mat communities. Limnol Oceanogr 38: 1150–1161.
  23. 23. Bouarab L, Dauta A, Loudiki M (2004) Heterotrophic and mixotrophic growth of Micractinium pusillum Fresenius in the presence of acetate and glucose: effect of light and acetate gradient concentration. Water Res 38: 2706–2712.
  24. 24. Nilsson C, Sundback K (1996) Amino acid uptake in natural microphytobenthic assemblages studied by microautoradiography. Hydrobiologia 332: 119–129.
  25. 25. Znachor P, Nedoma J (2010) Importance of dissolved organic carbon for phytoplankton nutrition in a eutrophic reservoir. J Plankton Res 32: 367–376.
  26. 26. Stamnes K, Slusser J, Bowen M, Booth C, Lucas T (1990) Biologically effective ultraviolet radiation, total ozone abundance, and cloud optical depth at McMurdo station, Antarctica, Setptember 15 1988 through April 15 1989. Geophys Res Lett 17: 2181–2184.
  27. 27. Waibel AE, Peter T, Carslaw KS, Oelhaf H, Wetzel G, et al. (1999) Arctic ozone loss due to denitrification. Science 283: 2064–2069.
  28. 28. Rothrock DA, Yu Y, Maykut GA (1999) Thinning of the Arctic sea-ice cover. Geophys Res Lett 26: 3469–3472.
  29. 29. Parkinson CL (2002) Trends in the length of the Southern Ocean sea-ice season, 1979–99. Ann Glaciol 34: 435–440.
  30. 30. Rich J, Gosselin M, Sherr E, Sherr B, Kirchman DL (1997) High bacterial production, uptake and concentrations of dissolved organic matter in the Central Arctic Ocean. Deep-Sea Research Part Ii-Topical Studies in Oceanography 44: 1645–1663.
  31. 31. Kirchman DL, Meon B, Ducklow HW, Carlson CA, Hansell DA, et al. (2001) Glucose fluxes and concentrations of dissolved combined neutral sugars (polysaccharides) in the Ross Sea and Polar Front Zone, Antarctica. Deep-Sea Research II 48: 4179–4197.
  32. 32. Ruiz-González C, Galí M, Simó R, Gasol JM (2012) Sunlight effects on the DMSP-sulfur and leucine assimilation activities of polar heterotrophic bacterioplankton. Biogeochemistry. Doi: 10.1007/s10533-012-9699-y.
  33. 33. Sintes E, Herndl GJ (2006) Quantifying substrate uptake by individual cells of marine bacterioplankton by catalyzed reporter deposition fluorescence in situ hybridization combined with micro autoradiography. Appl Environ Microb 72: 7022–7028.
  34. 34. Lasternas S, Agustí S (2011) Phytoplankton community structure during the record Arctic ice-melting of summer 2007. Polar Biol 33: 1709–1717.
  35. 35. Azam F, Hodson RE (1977) Size distribution and activity of marine microheterotrophs. Limnol Oceanogr 22: 492–501.
  36. 36. Kirchman D, Knees E, Hodson R (1985) Leucine incorporation and its potential as a measure of protein-synthesis by bacteria in natural aquatic systems. Appl Environ Microb 49: 599–607.
  37. 37. Kiene RP, Linn LJ, Bruton JA (2000) New and important roles for DMSP in marine microbial communities. J Sea Res 43: 209–224.
  38. 38. Malmstrom RR, Kiene RP, Vila M, Kirchman DL (2005) Dimethylsulfoniopropionate (DMSP) assimilation by Synechococcus in the Gulf of Mexico and northwest Atlantic Ocean. Limnol Oceanogr 50: 1924–1931.
  39. 39. Ruiz-González C, Simó R, Vila-Costa M, Sommaruga R, Gasol JM (2012) Sunlight modulates the relative importance of heterotrophic bacteria and picophytoplankton in DMSP-sulphur uptake. ISME J 6: 650–659.
  40. 40. Paerl HW (1991) Ecophysiological and trophic implications of light-stimulated amino acid utilization in marine picoplankton. Appl Environ Microb 57: 473–479.
  41. 41. Aas P, Lyons MM, Pledger R, Mitchell DL, Jeffrey WH (1996) Inhibition of bacterial activities by solar radiation in nearshore waters and the Gulf of Mexico. Aquat Microb Ecol 11: 229–238.
  42. 42. Sakka A, Gosselin M, Levasseur M, Michaud S, Monfort P, et al. (1997) Effects of reduced ultraviolet radiation on aqueous concentrations of dimethylsulfoniopropionate and dimethylsulfide during a microcosm study in the Lower St. Lawrence Estuary. Mar Ecol-Progr Ser 149: 227–238.
  43. 43. Archer SD, Ragni M, Webster R, Airs RL, Geiderb RJ (2010) Dimethyl sulfoniopropionate and dimethyl sulfide production in response to photoinhibition in Emiliania huxleyi. Limnol Oceanogr 55: 1579–1589.
  44. 44. Sunda W, Kieber DJ, Kiene RP, Huntsman S (2002) An antioxidant function for DMSP and DMS in marine algae. Nature 418: 317–320.
  45. 45. Faust MA, Correll DL (1977) Autoradiographic study to detect metabolically active phytoplankton and bacteria in Rhode River estuary. Mar Biol 41: 293–305.
  46. 46. Galí M, Simó R (2010) Occurrence and cycling of dimethylated sulfur compounds in the Arctic during summer receding of the ice edge. Mar Chem 122: 105–117.
  47. 47. Palmer EG, Togasaki RK (1971) Acetate metabolism by an obligate phototrophic strain of Pandorina morum. J Protozool 18: 640–644.
  48. 48. Kiene RP, Linn LJ (1999) Filter type and sampling handling affect determination of organic substrate uptake by bacterioplankton. Aquat Microb Ecol 17: 311–321.
  49. 49. Herndl GJ, Brugger A, Hager S, Kaiser E, Obernosterer I, et al. (1997) Role of ultraviolet-B radiation on bacterioplankton and the availability of dissolved organic matter. Plant Ecol 128: 42–51.
  50. 50. Schell DM (1974) Uptake and regeneration of free amino acids in marine waters of Southeast Alaska. Limnology and Oceanography 19: 260–270.
  51. 51. Flynn KJ, Butler I (1986) Nitrogen sorces for the growth of marine microalgae: role of dissolved free amino acids. Mar Ecol-Progr Ser 34: 281–304.
  52. 52. Tuchman NC, Schollett MA, Rier ST, Geddes P (2006) Differential heterotrophic utilization of organic compounds by diatoms and bacteria under light and dark conditions. Hydrobiologia 561: 167–177.
  53. 53. Simó R, Pedrós-Alió C (1999) Short-term variability in the open ocean cycle of dimethylsulfide. Global Biogeochem Cy 13: 1173–1181.
  54. 54. Toole DA, Siegel DA (2004) Light-driven cycling of dimethylsulfide (DMS) in the Sargasso Sea: Closing the loop. Geophys Res Lett 31.
  55. 55. Galí M, Saló V, Almeda R, Calbet A, Simó R (2011) Stimulation of gross dimethylsulfide (DMS) production by solar radiation. Geophys Res Lett 38.
  56. 56. Toole DA, Slezak D, Kiene RP, Kieber DJ, Siegel DA (2006) Effects of solar radiation on dimethylsulfide cycling in the western Atlantic Ocean. Deep-Sea Res Pt I 53: 136–153.
  57. 57. Simó R (2004) From cells to globe: approaching the dynamics of DMS(P) in the ocean at multiple scales. Can J Fish Aquat Sci 61: 673–684.
  58. 58. Bird DF, Kalff J (1989) Phagotrophic sustenance of a metalimnetic phytoplankton peak. Limnol Oceanogr 34: 155–162.
  59. 59. Antia NJ, Cheng JY (1970) The survival of axenic cultures of marine planktonic algae from prolonged exposure to darkness at 20°C. Phycologia 9: 179–183.
  60. 60. Smayda TJ, Mitchell-Innes B (1974) Dark survival of autotrophic, planktonic marine diatoms. Mar Biol 25: 195–202.
  61. 61. Palmisano AC, Sullivan CW (1982) Physiology of sea ice diatoms. I. Response of three polar diatoms to a simulated summer-winter transition. J Phycol 18: 489–498.
  62. 62. Legrand C, Graneli E, Carlsson P (1998) Induced phagotrophy in the photosynthetic dinoflagellate Heterocapsa triquetra. Aquat Microb Ecol 15: 65–75.
  63. 63. Sommaruga R, Oberleiter A, Psenner R (1996) Effect of UV radiation on the bacterivory of a heterotrophic nanoflagellate. Appl Environ Microb 62: 4395–4400.
  64. 64. Saló V, Simó R, Vila-Costa M, Calbet A (2009) Sulfur assimilation by Oxyrrhis marina feeding on a 35S-DMSP-labelled prey. Environ Microbiol 11: 3063–3072.