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N cycling in the world’s oceans

N cycling in the world’s oceans. Nitrogen. N is an essential nutrient for all living organisms (nucleic acids and amino acids) N has many oxidation states, which makes speciation and redox chemistry very interesting NH 4 + is preferred N nutrient. Non-bioavailable N 2 O 200 Tg N (+1)

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N cycling in the world’s oceans

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  1. N cycling in the world’s oceans

  2. Nitrogen • N is an essential nutrient for all living organisms (nucleic acids and amino acids) • N has many oxidation states, which makes speciation and redox chemistry very interesting • NH4+ is preferred N nutrient

  3. Non-bioavailable N2O 200 Tg N (+1) N2 2.2*107 Tg N (0) Bioavailable/Fixed (oxidation state) NO3- 5.7*105 Tg N (+5) NO2- 500 Tg N (+3) NH4+ 7.0*103 Tg N (-3) Organic N 5.3*105 Tg N (-3) Marine N Libes, 1992

  4. Marine Fixed N Budget Codispoti et al. (2001) Marine Reservoir: 6.3*105 Tg N Sources: 287 Tg N/yr Sinks: 482 Tg N/yr Atmospheric deposition: 86 Tg N/yr N2 fixation: 125 Tg N/yr N2O loss: 6 Tg N/yr Water Column denitrification: 150 Tg N/yr River Input: 76 Tg N/yr Organic N export: 1 Tg N/yr Benthic denitrification: 300 Tg N/yr Sedimentation: 25 Tg N/yr

  5. Fixation N2 Nitrification Mineralization NH4 NO3 Uptake Phytoplankton Grazing Chlorophyll Zooplankton Mortality Large detritus Water column Susp. particles Nitrification N2 NH4 NO3 Denitrification Aerobic mineralization Organic matter Sediment

  6. Nitrogen Cycle http://www.petsforum.com/personal/trevor-jones/nitrogencycle.gif

  7. Organic Matter Oxidation Sequence Morel & Herring, 1993 Respiration ΔG° (kJ/mol) -119 Denitrification -113 MnO2 reduction -96.9 Fe oxide reduction -46.7 Sulfate reduction -20.5 Methanogenesis -17.7

  8. Alternative pathways to N2 Microbially mediated Nitrification Anammox Heterotrophic Denitrification OLAND Nitrogen Fixation Chemical Reactions MnO2 Reduction Mn2+ Oxidation

  9. Marine Fixed N Budget UnbalancedWHY?????????????????????? • N Fixation may have been underestimated Limited data on Trichodesmium and other N fixers; variability in abundances and fixation rates of organisms • Recent estimates of N fixation rates have increased (Gruber and Sarmiento, 1997; Karl et al., 1997) • Denitrification may have been overestimated Stoichiometric and model-based estimates used; limited data on direct denitrification measurements

  10. My research • Denitrification describes the removal of fixed N, mostly NO3-, resulting in the formation of non-biologically available N, primarily N2 gas • Continental shelf sediments are responsible for up to 67% of marine denitrification estimates • Sandy sediments comprise 70% of continental shelves; global estimates of denitrification are mostly based on muddy sediments • Sands contain less organic matter and nutrients, and high oxygen concentrations in overlying water

  11. Benthic primary production (BPP) • Sandy sediments have low organic matter content, substrate for heterotrophic denitrification • BPP supplies reactive organic matter through remineralization • Organisms compete with microbes for nutrients such as NH4+ • Organisms also produce oxygen during photosynthesis • Role of BPP remains unclear

  12. A. Experiment 1 1B 1E 1A 14N14N 15NH4+, 14NO3- 15NO3- 14N15N, 15N15N 1C 1F 1D POM 15N15N 14N15N B. Experiment 2 2E 2A 2B 15N15N 15NO3-, 14NH4+ 14NO3- 14N15N, 14N14N 2C 2F 2D POM 14N14N 14N15N Isotope tracer experiments Possible outcomes of amendment experiments. 1A = Aerobic nitrification of 15NH4+; 1B = Heterotrophic denitrification with 14NO3- and/or 15NO3-; 1C = OLAND with 15NH4+ or partial nitrate reduction to nitrite followed by anammox with 15NH4+; 1D = Same as 1C except with standard nitrate; 1E = Heterotrophic denitrification with standard nitrate; 1F = Assimilation. 2A = Aerobic nitrification of standard ammonium; 2B = Heterotrophic denitrification with 14NO3- and/or 15NO3-; 2C = OLAND with standard ammonium or partial nitrate reduction to nitrite followed by anammox with standard ammonium; 2D = Same as 2C except with 15NO3-; 2E = Heterotrophic denitrification of 15NO3-; 1F = Assimilation

  13. Sampling Sampling

  14. Membrane Inlet Mass Spec. (MIMS)

  15. Results • W27 and Experiment 2 results suggest the presence of denitrification • Experiment 1 results suggest that within the 48-hr timescale of the experiment, no alternative pathway to N2 exists in these sediments

  16. Denitrification Rates • W27 Experiment provided a rate of 21.6 µmole N m-2 d-1 • R4-Experiment 2 provided rates of 22.8 & 23.2 µmole N m-2 d-1 • Rates obtained from other continental shelf studies of denitrification yielded 700-3200 µmole N m-2 d-1 • Other continental shelf sites studied contain higher organic matter content than Georgia sediments • Georgia continental shelf sediments are oxic to at least 1-cm depth, thus inhibiting higher rates of denitrification

  17. Discussion of results • Sandy, continental shelf sediments are potentially important sites of denitrification that may have been overlooked • These environments may have similar rates to current study site and if so, similar techniques can be used to measure such low rates of denitrification • Denitrification was not completely inhibited by low organic matter content or benthic primary production • BPP varies seasonally and spatially, yet denitrification rates were very close between two different stations during different seasons

  18. Future work • Impact of BPP can be explored further by monitoring nutrient and dissolved O2 concentrations and benthic primary production rates (monitored by SABSOON) • Compare rates to Gulf of Mexico shelf denitrification rates (Nov. – Dec. 2004) • Further explore the presence of alternative pathways in salt marsh sediments by using isotope tracers, 15N isotopic analyses, and HgCl2 (Oct. – Nov. 2004)

  19. Future work (cont’d)

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