TY - JOUR
T1 - Characterizing Catchment-Scale Nitrogen Legacies and Constraining Their Uncertainties
AU - Sarrazin, Fanny J.
AU - Kumar, Rohini
AU - Basu, Nandita B.
AU - Musolff, Andreas
AU - Weber, Michael
AU - Van Meter, Kimberly J.
AU - Attinger, Sabine
N1 - Funding Information:
Support to Fanny J. Sarrazin was provided by the Reduced Complexity Models project co‐funded by the Helmholtz Association (grant no. ZT‐I‐0010). Fanny J. Sarrazin, Rohini Kumar, Michael Weber and Sabine Attinger acknowledge the Advanced Earth Modelling Capacity (ESM; grant no. ZT‐0003) project funded by the Helmholtz Association. We thank Martin Bach for providing the N surplus data for agricultural areas. We thank Oldrich Rakovec for providing the long‐term mHM simulations. We thank two anonymous referees for their useful suggestions that allowed us to improve the quality of this paper. Open access funding enabled and organized by Projekt DEAL.
Funding Information:
Support to Fanny J. Sarrazin was provided by the Reduced Complexity Models project co-funded by the Helmholtz Association (grant no. ZT-I-0010). Fanny J. Sarrazin, Rohini Kumar, Michael Weber and Sabine Attinger acknowledge the Advanced Earth Modelling Capacity (ESM; grant no. ZT-0003) project funded by the Helmholtz Association. We thank Martin Bach for providing the N surplus data for agricultural areas. We thank Oldrich Rakovec for providing the long-term mHM simulations. We thank two anonymous referees for their useful suggestions that allowed us to improve the quality of this paper. Open access funding enabled and organized by Projekt DEAL.
Publisher Copyright:
© 2022. The Authors.
PY - 2022/4
Y1 - 2022/4
N2 - Improving nitrogen (N) status in European water bodies is a pressing issue. N levels depend not only on current but also past N inputs to the landscape, that have accumulated through time in legacy stores (e.g., soil, groundwater). Catchment-scale N models, that are commonly used to investigate in-stream N levels, rarely examine the magnitude and dynamics of legacy components. This study aims to gain a better understanding of the long-term fate of the N inputs and its uncertainties, using a legacy-driven N model (ELEMeNT) in Germany's largest national river basin (Weser; 38,450 km2) over the period 1960–2015. We estimate the nine model parameters based on a progressive constraining strategy, to assess the value of different observational data sets. We demonstrate that beyond in-stream N loading, soil N content and in-stream N concentration allow to reduce the equifinality in model parameterizations. We find that more than 50% of the N surplus denitrifies (1480–2210 kg ha−1) and the stream export amounts to around 18% (410–640 kg ha−1), leaving behind as much as around 230–780 kg ha−1 of N in the (soil) source zone and 10–105 kg ha−1 in the subsurface. A sensitivity analysis reveals the importance of different factors affecting the residual uncertainties in simulated N legacies, namely hydrologic travel time, denitrification rates, a coefficient characterizing the protection of organic N in source zone and N surplus input. Our study calls for proper consideration of uncertainties in N legacy characterization, and discusses possible avenues to further reduce the equifinality in water quality modeling.
AB - Improving nitrogen (N) status in European water bodies is a pressing issue. N levels depend not only on current but also past N inputs to the landscape, that have accumulated through time in legacy stores (e.g., soil, groundwater). Catchment-scale N models, that are commonly used to investigate in-stream N levels, rarely examine the magnitude and dynamics of legacy components. This study aims to gain a better understanding of the long-term fate of the N inputs and its uncertainties, using a legacy-driven N model (ELEMeNT) in Germany's largest national river basin (Weser; 38,450 km2) over the period 1960–2015. We estimate the nine model parameters based on a progressive constraining strategy, to assess the value of different observational data sets. We demonstrate that beyond in-stream N loading, soil N content and in-stream N concentration allow to reduce the equifinality in model parameterizations. We find that more than 50% of the N surplus denitrifies (1480–2210 kg ha−1) and the stream export amounts to around 18% (410–640 kg ha−1), leaving behind as much as around 230–780 kg ha−1 of N in the (soil) source zone and 10–105 kg ha−1 in the subsurface. A sensitivity analysis reveals the importance of different factors affecting the residual uncertainties in simulated N legacies, namely hydrologic travel time, denitrification rates, a coefficient characterizing the protection of organic N in source zone and N surplus input. Our study calls for proper consideration of uncertainties in N legacy characterization, and discusses possible avenues to further reduce the equifinality in water quality modeling.
UR - http://www.scopus.com/inward/record.url?scp=85130987575&partnerID=8YFLogxK
UR - http://www.scopus.com/inward/citedby.url?scp=85130987575&partnerID=8YFLogxK
U2 - 10.1029/2021WR031587
DO - 10.1029/2021WR031587
M3 - Article
AN - SCOPUS:85130987575
SN - 0043-1397
VL - 58
JO - Water Resources Research
JF - Water Resources Research
IS - 4
M1 - e2021WR031587
ER -