the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Estimating lateral nitrogen transfer through the global river network using a land surface model
Abstract. Lateral nitrogen (N) transport from land to oceans through rivers is an important component of the global N cycle. We developed a new model of this system, called ORCHIDEE-NLAT, which simulates the routing of water in rivers, and the pertaining transport of dissolved inorganic N (DIN), dissolved organic N (DON) and particulate organic N (PON) as well as the accompanying biogeochemical processes of decomposition for DON and PON, and denitrification for DIN during the transit from land to oceans through the river network. Evaluation against global observation-based datasets reveal that the model captures both the magnitude and seasonal variations of riverine water discharges and total nitrogen (TN) flows well. The ORCHIDEE-NLAT model was then applied to reconstruct the historical evolution of global TN flows from land to rivers, as well as the denitrification of DIN within the river network. Due to anthropogenic activities (e.g. mineral fertilisers and manure application, sewage water injection in rivers and land use change) and indirect climate and CO2 effects, the TN exports are modelled to increase from 27.1 Tg N yr-1 over 1901–1910 to 40.8 Tg N yr-1 over 2001–2014, with DIN (80 %) contributing most of this increase. The annual mean TN flow and DIN denitrification rates show substantial spatial heterogeneities. The seasonal amplitude of TN flow is of similar magnitude as the large-scale spatial variability. Compared to previously published global aquatic N transfer models (IMAGE-GNM, FrAMES-N, MBM, DLEM and Global NEWS2), our model produces similar global and continental-scale TN exports to the ocean, but shows distinct patterns at finer scale spatial scales (e.g. basin scale). ORCHIDEE-NLAT could also be coupled with other land surface models such as those used in the Nitrogen Model Intercomparison Project (NMIP). Our model provides a full simulation of N transport and reactivity from soils to oceans at an unprecedented spatio-temporal resolution (daily fluxes at 0.5° globally).
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Status: final response (author comments only)
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RC1: 'Comment on esd-2024-29', Zihao Bian, 07 Oct 2024
This study introduced a newly developed offline model of lateral N transfers, called ORCHIDEE-NLAT, within the framework of the land surface model ORCHIDEE. The ORCHIDEE-NLAT was used to simulate historical changes in riverine DON, PON, and DIN exports across the globe. Overall, it is an important work of global riverine N transport model development. The manuscript is well written and the model structure is clearly illustrated. Currently, the accuracy of the model in simulating riverine N exports is actually low, especially at regional scale. I understand it is very challenging to accurately simulate N transfers at the global level, but I still have some suggestions for authors to improve the model in the future.
- The ORCHIDEE-CNP and ORCHIDEE-Clateral are both used to provide the land-to-river inputs. ORCHIDEE-Clateral provides runoff, drainage, DOC, and POC inputs, while ORCHIDEE-CNP provides inputs of DON and DIN leaching from manure. Can ORCHIDEE-CNP provide all these forcing data? Using the outputs of two models may bring uncertainties and make this study complicated. Since runoff and drainage are critical components that determine DIN, DON, and PON fluxes, different water inputs simulated by two versions of land models can bring inconsistencies in water flux information behind N fluxes.
- In the aquatic N module, why not consider the transformation process from PON to DON, and from inorganic N to organic N?
- The residence time method is used to calculate N transport along the river networks. This method is commonly used but very simple and may not be able to accurately capture water transport processes. Authors may consider using hydrological kinetic equations in the future.
- The validation of model results only focuses on TN and NO3. How to validate DON and PON flexes? USGS provides organic N observation. The assumption of a linear relationship between observed TN and NO3 may ignore the variations in organic N.
- The simulated total N fluxes in the 1920s is questionable as authors have already mentioned. What are climate data sources? How about the precipitation change? ORCHIDEE has already been used to simulate lateral C and sediment fluxes, and does the same issue occur in these simulated variables? Better to check it and make it right.
Minor
L64. N leaching into the aquatic environment. LOAC includes land.
L91-93. This is also an issue for LSM.
L157-159. Does ORCHIDEE-CNP have soil organic C pools? It should also have POC outputs.
L166-167. How to separate sewage TN into different N species.
L197. A constant ratio may make the simulated DON less informative and accurate.
L257. What about N deposition into sediment?
Equations 4-11. Not all variables are explained. Please check.
Figure 4. Put the NSE value into the figure.
L507. Can you explain the decrease in PON export?
Figure 7. Better to use mg/L as concentration unit.
L586. Figs.
L625-627. ON inflow is simulated by ORCHIDEE CNP and Clateral, not NLAT. Right?
Figure 11c. Wrong name of NLAT.
L738-741. Another important thing is to improve model structure and data quality.
L863. Doi is invalid.
Citation: https://doi.org/10.5194/esd-2024-29-RC1 - AC2: 'Reply on RC1', Minna Ma, 13 Nov 2024
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RC2: 'Comment on esd-2024-29', Anonymous Referee #2, 10 Oct 2024
- AC1: 'Reply on RC2', Minna Ma, 13 Nov 2024
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