Abstract
The globally distributed diazotroph Trichodesmium contributes importantly to nitrogen inputs in the oligotrophic oceans. Sites of dissolved organic matter (DOM) accumulation could promote the mixotrophic nutrition of Trichodesmium when inorganic nutrients are scarce. Nano-scale secondary ion mass spectrometry (nanoSIMS) analyses of individual trichomes sampled in the South Pacific Ocean, showed significant 13C-enrichments after incubation with either 13C-labeled carbohydrates or amino acids. These results suggest that DOM could be directly taken up by Trichodesmium or primarily consumed by heterotrophic epibiont bacteria that ultimately transfer reduced DOM compounds to their host trichomes. Although the addition of carbohydrates or amino acids did not significantly affect bulk N2 fixation rates, N2 fixation was enhanced by amino acids in individual colonies of Trichodesmium. We discuss the ecological advantages of DOM use by Trichodesmium as an alternative to autotrophic nutrition in oligotrophic open ocean waters.
Nitrogen is recognized as the proximate limiting nutrient for primary production in the oceans1. The oceanic nitrogen reservoir is controlled by a balance between fixed nitrogen gains (via dinitrogen -N2- fixation) and losses (denitrification)2. While global nitrogen budget estimations determine that denitrification exceeds N2 fixation considerably3, recent improvements in the 15N2 isotope tracer method used to measure biological N2 fixation have evidenced that formerly published rates could be underestimated by a factor of ~2 to 64,5,6,7,8, and thus could be high enough to balance denitrification on a global basis. However, the variability among N2 fixation rates obtained when using the two different methods (adding 15N2 as a bubble or pre-dissolved in seawater)4,9 can be high7 and at times not significant10,11,12. A mechanistic understanding of which factors determine the degree of discrepancy between the two 15N2 methods is currently lacking. Moreover, marine pelagic N2 fixation had been long attributed to the tropical and subtropical latitudinal bands of the ocean, e.g.13, while other ecological niches such as high latitude waters, oxygen minimum zones and the vast dark realm of the ocean (below the euphotic zone) are now recognized as active N2 fixation sites14,15,16. It is likely that the inclusion of these previously unaccounted for active N2 fixation sites will be more important in equilibrating denitrification and N2 fixation rates than the underestimation of rates due to discrepancies between isotopic tracer methods.
In chronically stratified open ocean regions such as the vast subtropical gyres, primary production depends largely on external fixed nitrogen inputs provided by N2 fixation performed by prokaryotes termed ‘diazotrophs’. Diazotrophic cyanobacteria are photosynthetic prokaryotes (with the exception of the photoheterotrophic Candidatus Atelocyanobacterium thalassa which cannot photosynthesize)17 that thrive in oligotrophic tropical and subtropical waters of the oceans where they provide an important source of fixed nitrogen for other phytoplankton13. Despite being classically regarded as photoautotrophs, some unicellular diazotrophic cyanobacteria like Cyanothece are able to take up dissolved organic matter (DOM) molecules photoheterotrophically18. As well, various filamentous diazotrophic cyanobacteria such as Anabaena bear genes for amino acids transport, which may be used to incorporate amino acids from the in situ DOM pool, or to assimilate amino acids self-produced during diazotrophic growth19.
The filamentous diazotrophic cyanobacterium Trichodesmium is ubiquitous in the tropical and subtropical oceans where it is estimated to contribute 60–80% of global N2 fixation inputs20. Trichodesmium is limited by iron and/or phosphate availability21 which are often scarce in oligotrophic subtropical gyres. The concomitant accumulation of DOM in these oligotrophic gyres22 where Trichodesmium thrives, suggests it could benefit from organic compounds. While most of the marine DOM is composed of refractory molecules that persist in seawater for millennia, labile DOM (degraded within hours or days) accumulates preferentially at the surface ocean as a result of photosynthesis products23. Trichodesmium has been shown to assimilate organic phosphorus compounds such as phosphomonoesters and phosphonates when phosphate is scarce24,25 in an equally efficient manner to phosphate consumption26, although a minimum availability of inorganic nutrients may be needed before Trichodesmium can cleave the carbon-phosphorus bond of phosphonates27. On the other hand, while the uptake of carbon or nitrogen-rich DOM compounds has been studied in cultures of Trichodesmium (e.g. refs 28 and 29), such activity has not been revisited for almost two decades. The extent to which mixotrophic nutrition facilitates the growth and/or N2 fixation in Trichodesmium remains poorly known, particularly for natural colonies. Here we quantify the uptake of carbohydrates and amino acids and their effect on N2 fixation by natural Trichodesmium colonies using nano-scale secondary ion mass spectrometry (nanoSIMS).
Results
Station LDA presented relatively oligotrophic conditions at the surface with inorganic nutrient concentrations below the detection limit (0.02 μM for both nitrate -NO3−- and phosphate -PO43−-; Table S1), but high dissolved organic carbon (DOC; 95.34 ± 2.81 μM) and relatively high chlorophyll a concentrations (0.36 ± 0.05 μg L−1; Table S1) when compared to typical open ocean regional values30. Station LDB was sampled in an elevated chlorophyll a patch (0.83 ± 0.07 μg L−1) and exhibited lower DOC concentrations (70.65 ± 0.09 μM). Bacterial abundance was > 3-fold higher at LDB than at LDA (Table S1).
Bulk N2 fixation rates at LDA were 2.23, 4.61 and 4.10 nmol N L−1 d−1 for the control, carbohydrate and amino acid treatments, respectively. At station LDB, bulk N2 fixation rates were ~9-, 5- and 2-fold higher than at LDA (21.28, 23.44 and 10.79 nmol N L−1 d−1, respectively; Fig. 1a,b). At LDA, the addition of both carbohydrates and amino acids increased bulk N2 fixation but the variability among replicates was high, resulting in non-significant differences (p > 0.05) as observed in previous similar experiments15. No significant enhancement of bulk N2 fixation rates were observed at station LDB for either treatment.
At both stations LDA and LDB, nanoSIMS analyses of individual trichomes (Table S2) revealed significant 13C-enrichments (p < 0.0001) by ~1.7-fold relative to the control upon both carbohydrate and amino acid additions (Fig. 1c,d). These additions also significantly enhanced the 15N-enrichment of Trichodesmium by ~1.2-fold at station LDA (both p < 0.0001), but not at station LDB, where a high degree of variability was observed between filaments (Fig. 1c,d). When comparing both stations, we observed that per-trichome carbon and nitrogen uptake rates were ~2- and 5-fold higher at LDB than at LDA (Fig. 1e,f). NanoSIMS example images of 13C and 15N enriched trichomes in control, carbohydrate and amino acid treatments are shown in Fig. 2a–f, respectively. The addition of both carbohydrate or amino acids enhanced per-trichome nitrogen uptake rates at each station, although increases were only statistically significant for amino acid additions (Fig. 1e,f).
Discussion
We present evidence of carbohydrate and amino acid uptake by natural Trichodesmium colonies in conditions usually regarded as optimal for their autotrophic growth (Table S1). The addition of either carbohydrates or amino acids increased per-trichome N2 fixation rates compared to the control at both LDA and LDB, but only amino acid additions induced statistically significant per-trichome N2 fixation enhancements (Fig. 1e,f). At LDB, the enhancement of per-trichome N2 fixation rates with respect to the control upon the addition of either carbohydrates or amino acids was ~5-fold higher than at LDA, suggesting different DOM degradation patterns at LDB. LDB was located inside a massive chlorophyll patch, which had been drifting eastwards for several months (see chlorophyll a satellite images time lapse, where station LDB is represented by a pink cross; de Verneil, 2015). The persistence of the patch could be maintained by a regular input of inorganic nutrients via wet deposition, which often enhances primary production due to the high nutrient and trace metal content of volcanic ashes in this highly seismic active area of the South Pacific Ocean31. The wet deposition of inorganic nutrients could maintain both photosynthetic and N2 fixation activities while promoting a dynamic production and consumption of DOM. The higher DOM uptake by Trichodesmium at LDB (Fig. 1d,f) suggests that higher in situ DOM availability at LDB compared to LDA, promoted the heterotrophic nutrition of Trichodesmium over growth on inorganic nutrients. DOC standing stocks were lower at LDB than at LDA likely due to a tight coupling between its production and consumption, as suggested by the higher bacterial abundance (Table S1) and production at LDB than at LDA (F. Van Wambeke, personal communication). Alternatively, differences in Trichodesmium DOM uptake between stations LDA and LDB could be influenced by different DOM uptake genetic ability in different Trichodesmium strains32.
Given the high energetic cost of CO2 and N2 fixation in cyanobacteria33,34, the alternative nutrition on DOM is thought to alleviate energy shortages. For example, unicellular cyanobacteria use glycerol as an alternative to CO218, but the use of organic carbon substrates such as carbohydrates by Trichodesmium has seldom been observed and at low rates35. Although the external input of combined nitrogen is thought to preclude N2 fixation in Trichodesmium29,36,37, our results show a significant enhancement of per-trichome N2 fixation rates upon the addition of amino acids, as observed in other sites where heterotrophic diazotrophs predominate, like in mesopelagic waters15,38,39. Amino acids may provide a more readily accessible source of organic carbon than carbohydrates, resulting in a greater enhancement of N2 fixation rates.
DOM utilization likely confers nutritional plasticity to Trichodesmium in oligotrophic environments, reinforcing the obsoleteness of the categorical division of marine microbes into autotrophs or heterotrophs. Although we did not conduct 13C-labeled bicarbonate uptake experiments during this cruise, previous experiments performed in the Southwest Pacific Ocean and in cultures of Trichodesmium IMS101 have shown per trichome bicarbonate uptake rates of ~2–3 × 106 fmol C trichome−1 h−1 40,41, which are in the same order of magnitude as the per trichome carbohydrate uptake rates measured here (~1–9 × 106 fmol C trichome−1 h−1). This suggests that under certain environmental conditions, Trichodesmium may be able to exploit carbon comparably from inorganic and organic carbon sources.
Our results cannot however confirm whether DOM molecules were directly taken up by Trichodesmium, or if they were primarily reduced by epibiont bacteria and then transferred to the trichomes. For example, heterotrophic bacterial epibionts are known to facilitate dissolved organic phosphorus acquisition in Trichodesmium colonies42. Thus, the degree and/or functional diversity of epibiont bacteria colonization among sampling stations could have also influenced DOM uptake rates in our Trichodesmium samples43. We observed bacteria appearing to be attached to trichomes in our samples (Fig. S1), and thus cannot rule out this possibility. Different incubation time span experiments are needed to discern whether DOM passes through bacteria before being taken up by Trichodesmium, or if Trichodesmium assimilates DOM directly. However, such short-term experiments would require a high isotopic enrichment of the source DOM pool, which would likely bias the measured uptake rates.
We present evidence of carbohydrate and amino acid uptake by natural Trichodesmium colonies. Climate change scenarios predict inorganic nutrient limitation and increased DOM retention within the photic zone44, which will likely promote mixotrophy in Trichodesmium. Further studies on Trichodesmium organic versus inorganic nutrient acquisition are thus needed to predict how this important diazotroph will respond to climate alterations.
Methods
We sampled seawater at two stations in the Southwest Pacific (LDA: 19.21°S-164.68°E, LDB: 18.24°S-170.80°W, on 26 February and 15 March 2015, respectively) at depths receiving 50% of surface photosynthetically active radiation (corresponding to 7 and 9 m depth, respectively). The samples were incubated under in situ simulated conditions for 36 h with equimolar quantities of 13C-labeled carbohydrates (sodium pyruvate, sodium acetate and glucose) or amino acids (alanine, leucine and glutamic acid; Sigma-Aldrich, Munich, Germany), added at concentrations of 4 μM C (final concentration for the mix of all three carbohydrates or all three amino acids38). While the real marine DOM pool is molecularly highly complex and mostly refractory, these commercially available compounds were chosen as representative of carbohydrate and small organic acids typically found in marine labile DOM15,38,45. Seawater was distributed into sixteen 4.3 L transparent polycarbonate bottles (Nalgene, Rochester, NY, USA). Four bottles were filtered immediately upon collection (T0), four were amended with the carbohydrate mix, and another four with the amino acids mix. The last four bottles were used as a control without amendments. All bottles were labeled with 6 mL 98.9 atom% 15N2 gas (Cambridge Isotope Laboratories, Tewksbury, MA, USA) to assay N2 fixation simultaneously. Of each quadruplicate set, three bottles were used to estimate bulk N2 fixation rates (expressed as ‘N uptake’) and one bottle was used for nanoSIMS analyses (see Supplementary Information). Mann-Whitney statistical tests were used to test the significance of our results.
Additional Information
How to cite this article: Benavides, M. et al. Dissolved organic matter uptake by Trichodesmium in the Southwest Pacific. Sci. Rep. 7, 41315; doi: 10.1038/srep41315 (2017).
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Supplementary Material
Acknowledgments
This is a contribution of the OUTPACE (Oligotrophy from Ultra-oligoTrophy PACific Experiment) project (https://outpace.mio.univ-amu.fr/) funded by the French research national agency (ANR-14-CE01–0007–01), the LEFE-CyBER program (CNRS-INSU), the GOPS program (IRD) and the CNES. The OUTPACE project was managed by T. Moutin, S. Bonnet and A. Doglioli from the MIO (OSU Institut Pytheas, AMU, Marseille, France). MB was funded by the People Programme (Marie Skłodowska-Curie Actions) of the European Union’s Seventh Framework Programme (FP7/2007-2013) under REA grant agreement number 625185. HB was supported by a PhD scholarship from the French Ministry of Research and Education. SD was funded by the National Science Foundation (OCE-1434916). We thank I. Berman-Frank for her insightful comments to previous versions of this manuscript. We are indebted to M. Pujo-Pay, O. Grosso, S. Helias-Nunige and M. Caffin for DOC, nutrient and Chl a measurements, the technicians at the Laboratoire de Minéralogie & Cosmochimie (MNHN) for their invaluable assistance with nanoSIMS analyses, as well as to L. Guentas and M. Meyer for their help acquiring SEM images. G. Rougier and M. Picheral are warmly thanked for their efficient help in CTD rosette management and data processing. Finally, we thank the crew of the R/V L’Atalante for outstanding shipboard operation.
Footnotes
Author Contributions Conceived and designed the experiments: M.B., S.B., S.D. Performed the experiments: M.B., S.D., H.B. Analyzed the data: M.B., H.B. Contributed reagents/ materials/ analysis tools: P.R., S.D., S.B. Wrote the paper: M.B., S.B., S.D., H.B.
References
- Falkowski P. G. Evolution of the nitrogen cycle and its influence on the biological sequestration of CO2 in the ocean. Nature 387, 272–275 (1997). [Google Scholar]
- Gruber N. & Galloway J. N. An Earth-system perspective of the global nitrogen cycle. Nature 451, 293–296 (2008). [DOI] [PubMed] [Google Scholar]
- Codispoti L. A. An oceanic fixed nitrogen sink exceeding 400 Tg N a−1 vs the concept of homeostasis in the fixed-nitrogen inventory. Biogeosciences 4, 233–253 (2007). [Google Scholar]
- Mohr W., Großkopf T., Wallace D. W. R. & LaRoche J. Methodological Underestimation of Oceanic Nitrogen Fixation Rates. PLOS ONE 5, e12583 (2010). [DOI] [PMC free article] [PubMed] [Google Scholar]
- Großkopf T. et al. Doubling of marine dinitrogen-fixation rates based on direct measurements. Nature 488, 361–364 (2012). [DOI] [PubMed] [Google Scholar]
- Wilson S. T., Böttjer D., Church M. J. & Karl D. M. Comparative Assessment of Nitrogen Fixation Methodologies, Conducted in the Oligotrophic North Pacific Ocean. Appl Environ Microbiol 78, 6516–6523 (2012). [DOI] [PMC free article] [PubMed] [Google Scholar]
- Benavides M. et al. Longitudinal variability of size-fractionated N2 fixation and DON release rates along 24.5°N in the subtropical North Atlantic. J. Geophys. Res. Oceans 118, 3406–3415 (2013). [Google Scholar]
- Böttjer D. et al. Temporal variability of nitrogen fixation and particulate nitrogen export at Station ALOHA. Limnol Oceanogr, doi: 10.1002/lno.10386 (2016). [DOI] [Google Scholar]
- Montoya J. P., Voss M., Kahler P. & Capone D. G. A simple, high-precision, high-sensitivity tracer assay for N2 fixation. Appl Environ Microbiol 62, 986–993 (1996). [DOI] [PMC free article] [PubMed] [Google Scholar]
- Mulholland M. R. et al. Rates of dinitrogen fixation and the abundance of diazotrophs in North American coastal waters between Cape Hatteras and Georges Bank. Limnol. Oceangr. 57, 1067–1083 (2012). [Google Scholar]
- Bonnet S., Baklouti M., Gimenez A., Berthelot H. & Berman-Frank I. Biogeochemical and biological impacts of diazotroph blooms in a low-nutrient, low-chlorophyll ecosystem: synthesis from the VAHINE mesocosm experiment (New Caledonia). Biogeosciences 13, 4461–4479 (2016). [Google Scholar]
- Shiozaki T., Nagata T., Ijichi M. & Furuya K. Nitrogen fixation and the diazotroph community in the temperate coastal region of the northwestern North Pacific. Biogeosciences 12, 4751–4764 (2015). [Google Scholar]
- Karl D. M. et al. Dinitrogen fixation in the world’s oceans. Biogeochemistry 57/58, 47–98 (2002). [Google Scholar]
- Loescher C. R. et al. Facets of diazotrophy in the oxygen minimum zone waters off Peru. ISME J 8, 2180–2192 (2014). [DOI] [PMC free article] [PubMed] [Google Scholar]
- Benavides M. et al. Mesopelagic N2 Fixation Related to Organic Matter Composition in the Solomon and Bismarck Seas (Southwest Pacific). PLOS ONE 10, e0143775 (2015). [DOI] [PMC free article] [PubMed] [Google Scholar]
- Ratten J.-M. et al. Sources of iron and phosphate affect the distribution of diazotrophs in the North Atlantic. Deep-Sea Res Part II 116, 332–341 (2015). [Google Scholar]
- Zehr J. P. et al. Globally distributed uncultivated oceanic N2-fixing cyanobacteria lack oxygenic photosystem II. Science 322, 1110–1112 (2008). [DOI] [PubMed] [Google Scholar]
- Feng X. et al. Mixotrophic and photoheterotrophic metabolism in Cyanothece sp. ATCC 51142 under continuous light. Microbiology 156, 2566–2574 (2010). [DOI] [PubMed] [Google Scholar]
- Montesinos M. L., Herrero A. & Flores E. Amino acid transport systems required for diazotrophic growth in the cyanobacterium Anabaena sp. strain PCC 7120. Journal of Bacteriology 177, 3150–3157 (1995). [DOI] [PMC free article] [PubMed] [Google Scholar]
- Mahaffey C., Michaels A. F. & Capone D. G. The conundrum of marine N2 fixation. Am. J. Sci. 305, 546–595 (2005). [Google Scholar]
- Bergman B., Sandh G., Lin S., Larsson J. & Carpenter E. J. Trichodesmium - a widespread marine cyanobacterium with unusual nitrogen fixation properties. FEMS Microbiol Rev 37, 286–302 (2012). [DOI] [PMC free article] [PubMed] [Google Scholar]
- Hansell D. A., Carlson C. A., Repeta D. J. & Schlitzer R. Dissolved organic matter in the ocean: a controversy stimulates new insights. Oceanography 22, 202–211 (2009). [Google Scholar]
- Moran M. A. et al. Deciphering ocean carbon in a changing world. Proc Natl Acad Sci USA 201514645, doi: 10.1073/pnas.1514645113 (2016). [DOI] [PMC free article] [PubMed] [Google Scholar]
- Dyhrman S. T., Webb E. A., Anderson D. M., Moffett J. W. & Waterbury J. B. Cell-specific detection of phosphorus stress in Trichodesmium from the Western North Atlantic. Limnol Oceanogr 47, 1832–1836 (2002). [Google Scholar]
- Dyhrman S. T. et al. Phosphonate utilization by the globally important marine diazotroph Trichodesmium. Nature 439, 68–71 (2006). [DOI] [PubMed] [Google Scholar]
- Beversdorf L. J., White A. E., Björkman K. M., Letelier R. M. & Karl D. M. Phosphonate metabolism by Trichodesmium IMS101 and the production of greenhouse gases. Limnol Oceanogr 55, 1768–1778 (2010). [Google Scholar]
- del Valle D. A. & Karl D. M. Aerobic production of methane from dissolved water-column methylphosphonate and sinking particles in the North Pacific Subtropical Gyre. Aquat. Microb. Ecol. 73, 93–105 (2014). [Google Scholar]
- Mulholland M. R., Ohki K. & Capone D. G. Nitrogen utilization and metabolism relative to patterns of N2 fixation in cultures of Trichodesmium NIBB1067. J Phycol 35, 977–988 (1999). [Google Scholar]
- Ohki K., Zehr J. P., Falkowski P. G. & Fujita Y. Regulation of nitrogen-fixation by different nitrogen sources in the marine non-heterocystous cyanobacterium Trichodesmium sp. NIBB1067. Arch Microbiol 156, 335–337 (1991). [Google Scholar]
- Aufdenkampe A. K. et al. Biogeochemical controls on new production in the tropical Pacific. Deep-Sea Research II 49, 2619–2648 (2002). [Google Scholar]
- Martino M. et al. Western Pacific atmospheric nutrient deposition fluxes, their impact on surface ocean productivity. Global Biogeochemical Cycles, doi: 10.1002/(ISSN)1944-9224 (2014). [DOI] [Google Scholar]
- Rouco M., Joy-Warren H., McGillicuddy D. J., Waterbury J. J. B. & Dyhrman S. T. Trichodesmium sp. clade distributions in the western North Atlantic Ocean. Limnol Oceanogr 59, 1899–1909 (2014). [Google Scholar]
- Kranz S. A., Gladrow D. W., Nehrke G., Langer G. & Rosta B. Calcium carbonate precipitation induced by the growth of the marine cyanobacteria Trichodesmium. Limnol Oceanogr 55, 2563–2569 (2010). [Google Scholar]
- Holl C. M. & Montoya J. P. Interactions between nitrate uptake and nitrogen fixation in continuous cultures of the marine diazotroph Trichodesmium (Cyanobacteria). J Phycol 41, 1178–1183 (2005). [Google Scholar]
- Paerl H. W., Bebout B. M. & Prufert L. E. Bacterial associations with marine Oscillatoria sp. (Trichodesmium sp.) populations: ecophysiological implications. J Phycol 25, 773–784 (1989). [Google Scholar]
- Mulholland M. R. & Capone D. G. Nitrogen fixation, uptake and metabolism in natural and cultured populations of Trichodesmium spp. Mar Ecol Prog Ser 188, 33–49 (1999). [Google Scholar]
- Fu F.-X. & Bell P. R. F. Factors affecting N2 fixation by the cyanobacterium Trichodesmium sp. GBRTRLI101. FEMS Microbiol Ecol 45, 203–209 (2003). [DOI] [PubMed] [Google Scholar]
- Bonnet S. et al. Aphotic N2 Fixation in the Eastern Tropical South Pacific Ocean. PLOS ONE 8, e81265 (2013). [DOI] [PMC free article] [PubMed] [Google Scholar]
- Rahav E. et al. Dinitrogen fixation in aphotic oxygenated marine environments. FMICB 4, 1–11 (2013). [DOI] [PMC free article] [PubMed] [Google Scholar]
- Berthelot H., Bonnet S., Grosso O., Cornet V. & Barani A. Transfer of diazotroph-derived nitrogen towards non-diazotrophic planktonic communities: a comparative study between Trichodesmium erythraeum, Crocosphaera watsonii and Cyanothece sp. Biogeosciences 13, 4005–4021 (2016). [Google Scholar]
- Bonnet S. et al. Diazotroph derived nitrogen supports diatom growth in the South West Pacific: a quantitative study using nanoSIMS. Limnol Oceanogr, doi: 10.1002/lno.10300 (2016). [DOI] [Google Scholar]
- Van Mooy B. A. S. et al. Quorum sensing control of phosphorus acquisition in Trichodesmium consortia. ISME J 6, 422–429 (2012). [DOI] [PMC free article] [PubMed] [Google Scholar]
- Rouco M., Haley S. T. & Dyhrman S. T. Microbial diversity within the Trichodesmium holobiont. Environ Microbiol, doi: 10.1111/1462-2920.13513 (2016). [DOI] [PubMed] [Google Scholar]
- Passow U. & Carlson C. A. The biological pump in a high CO2 world. Mar Ecol Prog Ser 470, 249–271 (2012). [Google Scholar]
- Dekaezemacker J. et al. Evidence of active dinitrogen fixation in surface waters of the eastern tropical South Pacific during El Niño and La Niña events and evaluation of its potential nutrient controls. Global Biogeochemical Cycles 27, 768–779 (2013). [Google Scholar]
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