Increased extreme rains intensify erosional nitrogen and phosphorus fluxes to the northern Gulf of Mexico in recent decades

Soil erosion delivers enormous amounts of macro-nutrients including nitrogen (N) and phosphorus (P) from land to rivers, potentially sustaining water column bioavailable nutrient levels for decades. In this study, we represent erosional N and P fluxes in the Energy Exascale Earth System Model (E3SM) and apply the model to the continental United States. We estimate that during 1991–2019 soil erosion delivers 775 Gg yr−1 (1 Gg = 109 g) of particulate N (PN) and 328 Gg yr−1 of particulate P (PP) on average to the drainage basins of the northern Gulf of Mexico, including the Mississippi/Atchafalaya River and other rivers draining to the Texas Gulf and the Eastern Gulf. Our model simulation shows that in these rivers PP is the dominant P constituent and over 55% of P exported by erosion comes from soil P pools that could become bioavailable within decades. More importantly, we find that during 1991–2019 erosional N and P fluxes increase at rates of about 15 Gg N yr−1 and 6 Gg P yr−1, respectively, due to increased extreme rains in the Mississippi/Atchafalaya river basin, and this intensification of erosional N and P fluxes drive the significant increase of riverine PN and PP yields to the northern Gulf of Mexico. With extreme rains projected to increase with warming, erosional nutrient fluxes in the region would likely continue to rise in the future, thus complicating the effort of reducing eutrophication in the inland and coastal waters.

[1]  A. Bouwman,et al.  Modeling Process‐Based Biogeochemical Dynamics in Surface Fresh Waters of Large Watersheds With the IMAGE‐DGNM Framework , 2020, Journal of Advances in Modeling Earth Systems.

[2]  K. Calvin,et al.  The DOE E3SM v1.1 Biogeochemistry Configuration: Description and Simulated Ecosystem‐Climate Responses to Historical Changes in Forcing , 2020, Journal of Advances in Modeling Earth Systems.

[3]  J. Murphy,et al.  Changing suspended sediment in United States rivers and streams: linking sediment trends to changes in land use/cover, hydrology and climate , 2020 .

[4]  J. Ni,et al.  River dam impacts on biogeochemical cycling , 2020, Nature Reviews Earth & Environment.

[5]  Maoyi Huang,et al.  A substantial role of soil erosion in the land carbon sink and its future changes , 2020, Global change biology.

[6]  T. Stuessy Human Influences , 2020, Environmental History of Oceanic Islands.

[7]  V. G. Christensen,et al.  Complex Response of Sediment Phosphorus to Land Use and Management Within a River Network , 2019, Journal of Geophysical Research: Biogeosciences.

[8]  F. Hoffman,et al.  Representing Nitrogen, Phosphorus, and Carbon Interactions in the E3SM Land Model: Development and Global Benchmarking , 2019, Journal of Advances in Modeling Earth Systems.

[9]  Philip W. Jones,et al.  The DOE E3SM Coupled Model Version 1: Overview and Evaluation at Standard Resolution , 2019, Journal of Advances in Modeling Earth Systems.

[10]  Hong S. He,et al.  Precipitation From Persistent Extremes is Increasing in Most Regions and Globally , 2019, Geophysical Research Letters.

[11]  L. Leung,et al.  Modeling Sediment Yield in Land Surface and Earth System Models: Model Comparison, Development, and Evaluation , 2018, Journal of Advances in Modeling Earth Systems.

[12]  J. Murphy,et al.  Suspended-sediment concentrations and loads in the lower Mississippi and Atchafalaya rivers decreased by half between 1980 and 2015 , 2018, Journal of Hydrology.

[13]  P. Ciais,et al.  Global soil organic carbon removal by water erosion under climate change and land use change during AD 1850–2005 , 2018, Biogeosciences.

[14]  J. Six,et al.  Role of Soil Erosion in Biogeochemical Cycling of Essential Elements: Carbon, Nitrogen, and Phosphorus , 2018, Annual Review of Earth and Planetary Sciences.

[15]  N. Basu,et al.  Legacy nitrogen may prevent achievement of water quality goals in the Gulf of Mexico , 2018, Science.

[16]  P. Thornton,et al.  The Impact of Parametric Uncertainties on Biogeochemistry in the E3SM Land Model , 2017 .

[17]  Xuesong Zhang,et al.  A Global Data Analysis for Representing Sediment and Particulate Organic Carbon Yield in Earth System Models , 2017 .

[18]  F. Moatar,et al.  QUAL-NET, a high temporal-resolution eutrophication model for large hydrographic networks , 2017 .

[19]  Thomas S. Bianchi,et al.  Where Carbon Goes When Water Flows: Carbon Cycling across the Aquatic Continuum , 2017 .

[20]  J. Norman,et al.  Nutrient and pesticide data collected from the USGS National Water Quality Network and previous networks, 1963-2016 , 2017 .

[21]  K. Fennel,et al.  Modeling River-Induced Phosphorus Limitation in the Context of Coastal Hypoxia , 2017 .

[22]  E. Tipping,et al.  The C:N:P:S stoichiometry of soil organic matter , 2016, Biogeochemistry.

[23]  C. Koven,et al.  Multiple soil nutrient competition between plants, microbes, and mineral surfaces: model development, parameterization, and example applications in several tropical forests , 2015 .

[24]  Michael Obersteiner,et al.  Human-induced nitrogen–phosphorus imbalances alter natural and managed ecosystems across the globe , 2013, Nature Communications.

[25]  J. Finlay,et al.  Human Influences on Nitrogen Removal in Lakes , 2013, Science.

[26]  Mark S. Wigmosta,et al.  On an improved sub-regional water resources management representation for integration into earth system models , 2013 .

[27]  W. Post,et al.  The role of phosphorus dynamics in tropical forests – a modeling study using CLM-CNP , 2013 .

[28]  Yinghai Ke,et al.  A Physically Based Runoff Routing Model for Land Surface and Earth System Models , 2013 .

[29]  Steven E. Lohrenz,et al.  Acidification of subsurface coastal waters enhanced by eutrophication , 2011 .

[30]  E. Stehfest,et al.  Harmonization of land-use scenarios for the period 1500–2100: 600 years of global gridded annual land-use transitions, wood harvest, and resulting secondary lands , 2011 .

[31]  Carolien Kroeze,et al.  Global river nutrient export: A scenario analysis of past and future trends , 2010 .

[32]  B. Arheimer,et al.  Development and testing of the HYPE (Hydrological Predictions for the Environment) water quality model for different spatial scales , 2010 .

[33]  Michael Obersteiner,et al.  A high-resolution assessment on global nitrogen flows in cropland , 2010, Proceedings of the National Academy of Sciences.

[34]  R. Batalla,et al.  Contribution of the largest events to suspended sediment transport across the USA , 2010 .

[35]  R. H. Meade,et al.  Causes for the decline of suspended‐sediment discharge in the Mississippi River system, 1940–2007 , 2009 .

[36]  C. Gobler,et al.  Eutrophication and Harmful Algal Blooms: A Scientific Consensus. , 2008, Harmful algae.

[37]  J. Poesen,et al.  Spatial scale effects on the effectiveness of organic mulches in reducing soil erosion by water , 2008 .

[38]  D. Montgomery Soil erosion and agricultural sustainability , 2007, Proceedings of the National Academy of Sciences.

[39]  Robert L. Runkel,et al.  Toward a transport‐based analysis of nutrient spiraling and uptake in streams , 2007 .

[40]  D. M. Nelson,et al.  Phosphorus limits phytoplankton growth on the Louisiana shelf during the period of hypoxia formation. , 2006, Environmental science & technology.

[41]  A. Bouwman,et al.  Estimation of global river transport of sediments and associated particulate C, N, and P , 2005 .

[42]  Jan Köhler,et al.  Lake responses to reduced nutrient loading - an analysis of contemporary long-term data from 35 case studies , 2005 .

[43]  Thomas S. Bianchi,et al.  Effect of seasonal sediment storage in the lower Mississippi River on the flux of reactive particulate phosphorus to the Gulf of Mexico , 2004 .

[44]  J. D. Tarpley,et al.  The multi‐institution North American Land Data Assimilation System (NLDAS): Utilizing multiple GCIP products and partners in a continental distributed hydrological modeling system , 2004 .

[45]  M. Allen,et al.  Constraints on future changes in climate and the hydrologic cycle , 2002, Nature.

[46]  John C. Field,et al.  Climate change impacts on U.S. Coastal and Marine Ecosystems , 2002 .

[47]  R. Morgan,et al.  A simple approach to soil loss prediction: a revised Morgan–Morgan–Finney model , 2001 .

[48]  W. Battaglin,et al.  Long‐term changes in concentrations and flux of nitrogen in the Mississippi River Basin, USA , 2001 .

[49]  W. Battaglin,et al.  Nitrogen flux and sources in the Mississippi River Basin. , 2000, The Science of the total environment.

[50]  Stephen L. Johnson,et al.  HYPOXIA IN THE NORTHERN GULF OF MEXICO , 2000 .

[51]  Richard P. Hooper,et al.  Flux and Sources of Nutrients in the Mississippi-Atchafalaya River Basin , 1999 .

[52]  W. Wiseman,et al.  Characterization of Hypoxia: Topic I Report for the Integrated Assessment on Hypoxia in the Gulf of Mexico , 1999 .

[53]  David Pimentel,et al.  Ecology of Soil Erosion in Ecosystems , 1998, Ecosystems.

[54]  S. R. Daniel,et al.  Organic Carbon and Nitrogen Content Associated with Colloids and Suspended Particulates from the Mississippi River and Some of Its Tributaries , 1997 .

[55]  J. Syvitski,et al.  Geomorphic/Tectonic Control of Sediment Discharge to the Ocean: The Importance of Small Mountainous Rivers , 1992, The Journal of Geology.

[56]  P. Froelich Kinetic control of dissolved phosphate in natural rivers and estuaries: A primer on the phosphate buffer mechanism1 , 1988 .

[57]  R. Pocklington,et al.  Seasonal and annual variations in the organic matter contributed by the St Lawrence River to the Gulf of St. Lawrence , 1987 .

[58]  M. Meybeck Carbon, nitrogen, and phosphorus transport by world rivers , 1982 .

[59]  J. Trefry,et al.  Heavy metal inputs to Mississippi Delta sediments , 1980 .