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11/16/2010

Plankton production is supported by 2 types of nitrogen: The f‐ratio

1) new production supported by external sources of N (e.g. NO ‐ and N ), Assumptions: 3 2 ‐ ‐ 2) recycled or regenerated production, sustained by recycling of N. 1) N2 fixation is low f = (VNO3 )/ (VNO3 + ∑VNR) 2) Steady state system 3) Euphotic zone nitrification is low

Note NR includes regenerated forms of N N uptake (historically thought to include 2 + urea and NH4 ) regenerated Biological + MthMathemati tilcal ditidescription linki ng new NH4 production production and export. At steady state, nitrogen input is balanced by export nitrogen export. ‐ NO3

Under steady state (i.e. nitrate input balanced by export/grazing loss), if export NO ‐ NH + is less than input, accumulates. NO ‐ 2 4 N export This biomass must eventually be exported 3 to keep the system in steady state. ‐Why does this generalization apply to the open sea but not near shore environments?

Determining the f‐ratio

• Incubate seawater in the presence of trace 15 ‐ 15 + 15 NO3 , NH4 , and sometimes N‐urea 15N • Calculate NO3‐, NH4+, and “DON” uptake 15N • What makes this difficu lt for the oligotrop hic 15N ocean?

Net Uptake

15N

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Autonomous sensing of nitrate

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Not all “new” are introduced to the euphotic zone from below…

• Atmospheric deposition (both dry and wet) Johnson et al. (2010) Nature can form an important source of nutrients. • Advection: lateral input of nutrients

• N2 fixation

Assimilation of N by N2 fixation

• N2 fixation is the primary mode of nitrogen introduction to marine and terrestrial .

• N2 fixation converts N2 to NH3; exclusively prokaryotic process • Requires significant energy expensive

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Each annual cycle at HOT and BATS has significant Dissolved At Station ALOHA, N Inorganic Carbon 2 (DIC) drawdown, fixation appears to but not enough contribute ~30‐84% of nitrate is present new production in surface to support growth.

8 NO 6 3‐ from Karl et al. in

4 Fasham, Ocean

(‰) 2 Biogeochemistry

0 N particulate N export N2 15  -2 89 90 91 92 93 94 95 96 97 98 99 00 01 02 03 04 05 06 07 Year

Let’s look at dissimilatory nitrogen transformations

Oxidized N

Energy to be gained in oxidation

Reduced N Global estimate of N2 fixation based on N‐DIC drawdown in NO3‐ depleted warm is equivalent to 0.8 0.3 Pg C yr‐1

(Sarmiento & Gruber, 2006)

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Nitrification Dissimilatory nitrogen transformations - •Biological oxidation of NH3 to NO3 using oxygen as terminal electron acceptor. NH2OH → NO → N2O

+ - - Nitrification: NH4 → NO2 → NO3 •Two step process; ammonia oxidation fllfollowed db by n itititrite oxid idtiation; bthboth reactions yield energy. - - : NO3 → NO2 → NO → N2O → N2 - •NO2 serves as an important intermediate; incomplete nitrification also + Anammox: NO2 + NH4 → N2 + 2H2O yields N2O.

Aerobic regeneration of nitrogen Complete of organic matter

(CH2O)106(NH3)16H3PO4 + 138O2  106CO2 + 122H2O +16HNO3 + H3PO4

+ Degradation of organic N to Multi-step process. First step is the breakdown of amino acids to NH4 ; this process ammonium occurs during is mediated by heterotrophic heterotrophic . Nitrification: 2NH + + 3O  2NO - + 4H+ + 2H O Nitrification is a 2 step 4 2 2 2 predominately mediated by ppyrocess that is mediated by - - chemoautotrophic microbes 2NO2 +O+ O2  2NO3 different groups of (best studied are microbes. The first step These reactions yield energy (but not much…) Nitrosomonas and Nitrobacter) (termed ammonium + oxidation) oxidizes NH4 to - NO2 , and the second step - - converts NO2 to NO3 .

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Recent isolation and cultivation of an abundant archaeal ammonium oxidizer

Archaea 20- 40% of total picoplankton in meso- and bathypelagic waters

0 Let’s look at dissimilatory nitrogen transformations

1000

Oxidized N 2000 Pacific Atlantic Depth (m) 3000

4000 Energy to be 0 1020304050 gained in NO - + NO - (mol L-1) 3 2 oxidation

Reduced N

(Sarmiento & Gruber, 2006)

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Denitrification Anaerobic ammonium oxidation

- - The reduction of NO3 and NO2 to N2 during heterotrophic respiration of (anammox) organic matter. Occurs predominately in anaerobic or suboxic environments. + - • NH4 + NO2  2N2 + 2H2O - C106H175O42N16P + 104 NO3  106CO2 + 60N2 + H3PO4 +138 H2O • Anaerobic ammonium oxidation

• Major source of N gas - - 2 NO3 and NO2 are (along with denitrification) used as terminal electron acceptors during heterotrophic • Anoxic sediments, marine respiration. , and sewage wastewater

• Mediated by Planctomyces

Oxygen concentrations along the 26.9 kg m-3 isopycnal surface (~500 m in the N. Pacific)

High in surface water due to of nutrients.

High organic matter

flux depletes O2 concentrations below the euphotic zone.

Chlorophyll distributions

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Global Nitrogen Budget

Process Nitrogen Flux (TgN yr-1) Sources

Pelagic N fixation 120  50 N input by N2 Losses of N by 2

fixation denitrification Benthic N2 fixation 15  10 Atmosphere N2 N2 N2O River input (DON) 35  10 River input (PON) 45  10 Atmospheric deposition 50  20 TtlSTotal Sources 265  55 Bacterial Nitrification - Organic NO2 degradation NH + - Sinks matter 4 NO3 Organic N export 1 N O 2 Benthic denitrification 180  50 Aerobic Suboxic Water column denitrification 65  20 Denitirifcation N2O Sediment burial 25  10 Bacterial + N O loss to atmosphere 4  2 NH 2 degradation 4 N 2 Total Sinks 275  55 1 Tg = 1012 g

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