the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Riverine nitrogen supply to the global ocean and its limited impact on global marine primary production: a feedback study using an Earth system model
Miriam Tivig
David P. Keller
Andreas Oschlies
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- Final revised paper (published on 01 Oct 2021)
- Supplement to the final revised paper
- Preprint (discussion started on 04 May 2021)
Interactive discussion
Status: closed
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RC1: 'Comment on bg-2021-101', Anonymous Referee #1, 21 May 2021
This is an interesting article exploring the long-term impact of riverine nitrogen inputs on the global ocean nitrogen inventory and associated primary production. The authors show that in simulations that have reached equilibrium, impacts on the global N inventory and primary production are highly limited due to feedbacks on N fixation and denitrification. I appreciated the candidness of the discussion on the modelling approach’s strengths/weaknesses and how the results differ from those previously published in this area. The main discussion that I think might be expanded upon is how indicative simulations that have reached equilibrium are for policy relevant timescales (interannual to decadal). Put another way, how do the authors’ main conclusions change over the course of these 10000-year simulations? Are the implications different for watersheds that are experiencing rapid increases or decreases in nitrogen export at present? Most of my comments and suggestions relate to how the manuscript text could be better structured and the figures could be made much easier to interpret. Subject to these changes, I would be happy to recommend for publication.
Minor comments
L23. “atmospheric” –should probably be dissolved/aqueous.
L26. Aren’t these “model concepts” observationally /experimentally derived? Some reference to the empirical evidence would be useful here. Maybe also its limitations if it’s heavily based on given species (eg Trichodesmium).
L31. concentrations “of” fixed N
L32. “the consumption of O2”- Do you mean the consumption of O2 during remineralisation? If so, be explicit.
L47. The Séférian et al. 2020 reference is perhaps worth citing here as it summarises the inclusion of riverine inputs in recent models.
L51. “real” should probably be realistic or observed.
L59. Maybe clarify what is meant by N export here. Riverine delivery? For many in the ocean biogeochemistry community export is instinctively a vertical flux.
Figure 1. More detail is needed on the tracers in the figure legend.
L100. “atmospheric” –should probably be dissolved/aqueous.
L101. Are they limited by a max NO3 concentration? I know much of this will be in the cited references but more detail is required on N-fixation in the model. Highlight perhaps that most models don’t have explicit diazatrophs and this is an advantage of using uvic. What is the diazatroph PFT based on? How does N-fixation compare to observations where they exist?
L105-110. As with the above comment, some comparison on how denitification in the model compares to observations would be very useful. I think a global map of N-fixation and denitification in the model CTR is required.
L140. It should be made clearer on first use that NEWS etc are simulation names.
Table 1. For clarity I would remove UVic from the simulation names as this is not repeated in the main text. I would also add a CTR row.
L156. “vary a little” – please quantify this
L151. This should really be called a “Results and Discussion” section.
L160. The wording here needs to be clearer. “At smaller scales…globally higher.” This reads like it contradicts L167-168.
Figure 3. Axes are missing labels and units here.
Figure 5. I find it very difficult to see differences between positive and negative anomalies using this colorbar. I suggest changing to something far more distinctive (e.g. red for negative anomalies). The same applies to other figures using this scale.
L175-177. This is difficult to see in Figure 5 maybe cite figure 6 here.
Figure 6. The depths given in the figure don’t match the legend.
L181-183. This sentence is confusing and needs rephrasing.
Figure 7. Label missing from panel c.
L187. typo. “amounts to an increase of only 1.1…”
L209. I’m not sure the language here is accurate. Presumably the model is not explicitly trying to compensate anything. Wouldn’t this be better described as enhanced denitification sinks promoting conditions that favour N-fixers over the other PFT type and consequently global N-fixation rates are higher?
L210-213. The discussion of other literature here before properly explaining your model results is confusing. Where these papers have used the same model this should be clear.
L216. “where NO3 concentrations are substantially reduced relative to the CTL”
Figure 8- See earlier comments on how it would be nice to see global Nfix in the control.
Figure 9. Suggest using different color palettes for mean states and anomalies.
L219-227. The balance between results of the model simulations and the discussion of other literature needs to be more organised. The presentation of discussion before results is quite confusing.
L221-222. This is a bit rushed and therefore confusing. I think more detail is needed here on this mechanism, the difference between the stoichiometry of N-fixation and denitrification and how spatial and temporal coupling is important for the positive feedback to occur.
Table 3. Benthic denitrification appears to be twice the magnitude of that in the water column. This doesn’t seem to be reported and discussed in the manuscript. Does this have implications for models lacking benthic denitrification?
L246. “…and vary little between…”
L251. “smaller scales” is ambiguous. Here and elsewhere I recommend being more specific e.g basin/watershed/coastal scales etc.
L257-259. Differences in spatial patterns between these simulations are difficult to discern it looks more like the magnitude of change is the only difference.
L259. Are these subtropical and tropical regions where N-fixers are predominately confined to?
L297. Maybe “exported again” should be “recycled” here.
L301. And presumably not all the N can be consumed via local primary production due to other constraints.
Table 6. Maybe the increase in NPP per quantity of additional N would be a useful metric to add to this table given each watershed provides different total N delivery.
L325. For clarity I think “inhibiting additional NPP” should be “limiting increases in NPP”.
Section 4. Given the extensive discussion of the Lacroix et al. 2020 paper, I think a few more details are required to compare the studies properly. What was their model resolution, did they have explicit N-fixers and benthic denitrification?
L358. The emphasis here and in the conclusions (L376) doesn’t really match the findings. I would say the feedbacks do much more than “partly compensate” the riverine fluxes. Maybe this would be clearer if you gave the % of added N that is retained in the inventory at equilibrium or some other metric of feedback strength.
L388-389. I’m not sure this “upper limit” conclusion would hold if N fertilisation were targeted spatially and temporally in regions of N limitation. Perhaps this should be toned down a little.
- AC1: 'Reply on RC1', Miriam Tivig, 30 Jul 2021
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RC2: 'Comment on bg-2021-101', Anonymous Referee #2, 17 Jun 2021
Summary:
The manuscript presents an adaptation of an existing EMIC model in which riverine fluxes of nitrogen from the Global NEWS2 dataset are introduced. These new fluxes are used in a number of experiments that investigate the resulting changes in primary production, N2-fixation, and denitrification. A focus of the analysis is the impact on the nitrogen cycle of this change on these balancing processes.
Overall:
The manuscript is generally straightforward to understand. My main criticisms of the current draft would that that:
- the model description has a few gaps that might benefit from filling and improved clarity
- the experimental design involves several highly idealised simulations and it could be clearer which hypotheses are being tested when these are being framed; for instance, rather than use a single experiment that scales river inputs, a suite of scaling runs could instead assess the strength and saturation of feedbacks
- the results are generally clear enough, but there are omissions or odd choices in the results presented; it would be helpful, for instance, to have tables which bring together the major N-cycle processes across the different runs
My recommendation is that the manuscript should be accepted after revision that addresses these major criticisms. I include below a list of more minor comments on the manuscript, and additionally have added some suggestions that the authors may want to consider during revision – these are mostly stylistic, and I leave their adoption up to the authors.
Minor comments:
Pg. 1, ln. 1: I might be inclined to make a distinction between the natural and the anthropogenic nitrogen cycles; we have so radically modified the N-cycle that negative feedbacks may have been swamped; in any case, definitely: make it clear in the abstract whether you consider that you are dealing with the natural or modern N-cycle
Pg. 1, ln. 18: “steady state” - I'm not enough of an expert in riverine supply to be sure, but my first reaction is that the scale of anthropogenic inputs of nitrogen to the ocean must make this assumption questionable. It's an assumption I'm happy to make in my own tangential work for simplicity, but where a study is addressing it head-on, I'd expect something on the anthro perturbation to the N-cycle
Pg. 2, ln. 25: “slowly” - to assist less familiar readers, please expand on why we might expect (or why we know) diazotrophs to be slow-growing
Pg. 2, ln. 29: “most marine organisms” - except diazotrophs, of course
Pg. 2, ln. 32: “consumption of O2” - this statement is perhaps confusing as people will be aware that growth of phytoplankton *produces* oxygen; I know what you mean here, but others might not
Pg. 2, ln. 34: “work together” - do they really "work together"?; might it not be fairer to say that they work independently, but between them the nitrogen cycle is balanced (which it inevitably must be)
Pg. 2, ln. 38: “considered in this study” - it might be useful to indicate the size of the deposition sink so that it's clear why it's ignored here; also, my first thought here was that you didn't want to have to add an additional low importance process, but it looks like someone has already done this for your model; so perhaps be very clear here why you're ignoring it
Pg. 2, ln. 39: “highly” - how high is "highly"? do you have an estimate of how much the riverine flux has been affected by human activities, or is this still highly uncertain?
Pg. 2, ln. 47: “2008” - 2008 doesn't seem very "current"; perhaps reword or find a better example
Pg. 2, ln. 50: “as on” - "as on" -> "*than on* the actual quantity of nitrogen nutrient"
Pg. 2, ln. 55: “long enough” - you should say what you think the relevant time period is; I believe Tyrrell (1999) puts an estimate on this based on input flux and ocean inventory
Pg. 2, ln. 57: “estimations of” -> "estimated"
Pg. 3, ln. 62: “EMICs” - a passing mention of computation cost would help explain the underlying attraction of EMICs
Pg. 3, ln. 75: the rationale for this omission of atmospheric deposition needs to be made very clear; I was previously assuming that you were ignoring it (1) because it was one more process to add (... but Landolfini et al. seem to have already added it to this model), and (2) because it's much less important than riverine input (... but you imply otherwise here); please be clear on the rationale here
Pg. 3, ln. 79: “series of simulations” - it would possibly be helpful if these experiments were given a scientific rationale in addition to their description (e.g. "this experiment simulates increased anthropogenic emissions", "this experiment simulates differential waste water management between geographical regions", etc.)
Pg. 4, Figure 1: this diagram makes it look like PO4 might be added to the ocean as well via a fixed R_N:P parameter; is that right?
Pg. 4, Fig. 1: maybe identify the 7 state variables in the caption to help with clarity
Pg. 4, ln. 97: “updates” - a little expansion on these updates might help readers understand if they are significant
Pg. 4, ln. 97: “prognostic variables” - you don't refer to the variables by the abbreviations used in Figure 1; nor does Figure 1's caption
Pg. 4, ln. 100: “atmospheric” - technically, they're fixing dissolved dinitrogen which is in equilibrium with atmospheric N2
Pg. 5, ln. 105: “benthic denitrification” - this could be described a little more clearly; I *think* you mean that a function based on a more sophisticated benthic sediment model turns receipt of organic matter at the seafloor into oxic and anoxic (with denitification) remineralisation of this matter; is that right?
Pg. 5, ln. 107: “models” - "models" or "model"?; this is a little confusing
Pg. 5, ln. 109: “subgrid” - how "subgrid" is subgrid here?; for instance, do you simply identify the fraction of a cell that is shelf and do calculations based on this basic split, or do you divide each cell into an N x M subcell domain that does the bathymetry better?
Pg. 5, ln. 123: To avoid confusion in readers, perhaps mention that NEWS2 includes no runoff from the Antarctic continent
Pg. 5, ln. 133-135: it sounds like this assumes a constant seasonal cycle in runoff; this is not unreasonable in an EMIC where the hydrological cycle may be in a long-term equilibrium
Pg. 6, ln. 136: can you clarify what happens with riverine P in this model please?; Figure 1 tends to imply there might be a link between riverine N and P; Global NEWS provides both, and the balance of N and P could be important for your model's N2-fixation response
Pg. 6, ln. 145: “bioavailable” - maybe add: "(or rapidly turned over to DIN)"
Pg. 7, Table 1: add control experiment to this table
Pg. 7, ln. 149: “steady state” - it might be nice to see a figure (supplementary?) where the long-term balancing of the N budget took place; for instance, to illustrate the timescales associated with addition and removal processes
Pg. 7, ln. 155: “fairly well” - all runs omit the midwater maximum around 1000 m
Pg. 7, ln. 156: “global average” - what is the global concentration difference?; and what is this as a percentage of total observed inventory?
Pg. 7, ln. 156: “misfit” - this is absolute error, right?
Pg. 7, ln. 167: “not surprising” - well, not *entirely* surprising; it's possible, of course, that adding local sources of N might trigger strong balancing denitrification that could even offset the addition (though this seems unlikely)
Pg. 7, ln. 171: on this point, might it be possible to include some total of suboxic ocean volume (e.g. the volume of below some standard oxygen threshold concentration)?
Pg. 8, Table 2: “+1,12” -> “+1.12”
Pg. 10, Figure 5: normally, delta (or bias) plots are coloured blue (negative) to red (positive) with white in the centre
Pg. 11, Figure 6: why 850m?; from Figure 3b, the largest misfit seems to be at 1000m
Pg. 12, Figure 7: it's obviously not possible to tell how realistic oxygen is here; perhaps compare NEWS and CTR directly to WOA instead?
Pg. 13, ln. 192: surplus "like"
Pg. 13, ln. 193: assuming that N inputs fuel corresponding increases in productivity, it may be worth noting in passing how much production is also enhanced by river N in these regions
Pg. 13, ln. 197: see my earlier remarks about PO4 availability and riverine sources; if riverine P is neglected, this may skews where N2 fixation is favoured; ditto if PO4 is added in strict proportion to DIN
Pg. 14, Figure 8: maybe it would be better to show CTR N2 fixation in addition to the deltas?
Pg. 15, ln. 223: “oxygen concentrations even though higher at the surface” - Is this elevated oxygen due to enhanced production?; typically surface oxygen is boring because it equilibrates quickly to saturation values (with ambient temperature)
Pg. 15: per my remarks for Figure 7, making the model's relationship with observed oxygen clear might be useful
Pg. 17, Table 3: add a column listing the balance at equilibrium?; I make the discrepancy about 0.5 Tg N / y for all of the model experiments; actually, what is this discrepancy?; is it the model just not fully equilibrated?
Pg. 18, Figure 11: if possible, it might be an idea to include a map of observational estimated production; the total of the models here might be OK, but I think the patterns - particularly in the Indian Ocean - might not be; this is important given the amount of analysis that is focused in this region
Pg. 18, Figure 11: surplus colourbar on Figure 11b?
Pg. 19, Table 4: this is a weird, single-column table
Pg. 19, Table 4: these numbers are a bit higher compared to what I'm used to; e.g. the Oregon State University primary production website; there, I find ~40 Pg C / y; the 3 models their site includes are quite divergent, however
Pg. 20, Table 5: this is a very strange way to organise a table; it's a single column when it should be three columns of numbers
Pg. 20, Table 5: also, I might be inclined to include numbers (or deltas) for the other major N-cycle processes, N2-fixation and denitrification
Pg. 20, Table 5: also, why the areal units here?; would it not make more sense to report global totals (i.e. Pg C / y)?
Pg. 24, ln. 352: “increase in marine primary production is small” - this analysis appears not to factor in that total riverine input of N is ~0.2% of the N used in primary production; so, contrary to the point you make here, the changes in NPP found between the simulations appear to actually be quite large; I guess the factor that makes the rivers more important is that they deliver N to shallow ocean areas (= shelves) where they will have a larger impact
Pg. 25, ln. 387: “carbon export” - how is this defined?; e.g. 100 m export?; and does it include or exclude shelf regions where material is not properly exported?
Pg. 25, ln. 387: You might want to consider these changes in light of how much nutrient is being added to the ocean relative to N cycling through production; if my earlier back-of-the-envelope calculations are right, river N is 0.2% of N-cycling through production, but you're finding several percent in NPP change
Pg. 25, ln. 390-392: this paragraph doesn't really say very much; I'd suggest deleting it
Pg. 26, ln. 397: if riverine phosphorus is not included here, does that not skew the model's balance between N2-fixation and denitrification since the N being added is not balanced by P?
Pg. 26, ln. 400: “hdl” - what is this?; could this be put onto Zenodo or something to get a proper DOI?
Pg. 26, ln. 402: I get a 404 error from this link
Style points:
Pg. 8, Figure 3: can you make the lines in the key thicker so it's easier to tell them apart?; also, the choice of colours is rather unhelpful in this regard; also, why are they ordered in this strange way in the key?
Pg. 9, Figure 4: this colour scale looks more like a delta one to me
Pg. 10, Figure 5: it might be better not to stretch the smaller Indian basin to the same size as the other basins here; perhaps just plot the same latitude range on all three panels?
Pg. 15, Figure 9: this colourbar implies negative denitification is possible in the model; is it?
Pg. 16, Figure 10: this colourbar is missing the extreme cyan colour that indicates "out of range" delta concentration
Pg. 23, Figure 13: could you try a clever log scale here?; this plot is otherwise not very informative
Pg. 25, ln. 369: purely as a style point, I would suggest thinning your conclusions section to 5 or 6 bullet-point statements of your findings; this makes it very easy for readers to understand the main findings (and decide whether to read more!)
- AC2: 'Reply on RC2', Miriam Tivig, 30 Jul 2021