Abstract

Excess deposition (including both wet and dry deposition) of nitrogen and sulfur are detrimental to ecosystems. Recent studies have investigated the spatial patterns and temporal trends of nitrogen and sulfur wet deposition, but few studies have focused on dry deposition due to the scarcity of dry deposition measurements. Here, we use long-term model simulations from the coupled WRF-CMAQ model covering the period from 1990 to 2010 to study changes in spatial distribution as well as temporal trends in total (TDEP), wet (WDEP) and dry deposition (DDEP) of total inorganic nitrogen (TIN) and sulfur (TSO4). We first evaluate the model's performance in simulating WDEP over the U.S. by comparing the model results with observational data from the U.S. National Atmospheric Deposition Program. The coupled model generally underestimates the WDEP of both TIN (including both the oxidized nitrogen deposition-TNO3, and the reduced nitrogen deposition-NHX) and TSO4, with better performance in the eastern U.S. than the western U.S. TDEP of both TIN and TSO4 show significant decreases over the U.S., especially in the east due to the large emission reductions that occurred in that region. The decreasing trends of TIN TDEP are caused by decrease of TNO3, and the increasing trends of TIN deposition over the Great Plains and Tropical Wet Forests regions are caused by increases in NH3 emissions although it should be noted that these increasing trends are not significant. TIN WDEP shows decreasing trends throughout the U.S., except for the Marine West Coast Forest region. TIN DDEP shows significant decreasing trends in the region of Eastern Temperate Forests, Northern Forests, Mediterranean California and Marine West Coast Forest, and significant increasing trends in the region of Tropical Wet Forests, Great Plains and Southern Semi-arid Highlands. For the other three regions (North American Deserts, Temperate Sierras and Northwestern Forested Mountains), the decreasing or increasing trends were not significant. Both the WDEP and DDEP of TSOx have decreases across the U.S., with a larger decreasing trend in the DDEP than that in the WDEP. Across the U.S. during the 1990-2010 period, DDEP of TIN accounted for 58-65% of TDEP of TIN. TDEP of TIN over the U.S. was dominated by deposition of TNO3 during the first decade, which then shifts to reduced nitrogen (NHX) dominance after 2003 resulting from combination of NOx emission reductions and NH3 emission increases. The sulfur DDEP is usually higher than the sulfur WDEP until recent years, as the sulfur DDEP has a larger decreasing trend than WDEP.

Highlights

  • Increased nitrogen and sulfur deposition is detrimental to ecosystems, since it leads to decreased biological diversity (Clark and Tilman, 2008; Clark et al, 2013; Stevens et al, 2004), increased terrestrial and aquatic eutrophication (Bouwman et al, 2002; Bowman et al, 2008; Fisher et al, 2011), and acidification (Greaver et al, 2012; Savva and Berninger, 2010)

  • After performing the annual precipitation adjustment for model simulated Wet deposition (WDEP), we see that the correlation coefficients (R) are slightly improved relative to using the unadjusted WDEP values (Table 1), increasing from 0.89 to 0.92 for TNO3, from 0.77 to 0.81 for NHx, and from 0.92 to 0.94 for total sulfur (TS) (Fig. S3 in the Supplement)

  • By evaluating the model’s performance against observations from the NADP network, we find that the model generally underestimated the WDEP for both the oxidized nitrogen (TNO3) deposition and reduced nitrogen (NHx) deposition across the United States (US)

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Summary

Introduction

Increased nitrogen and sulfur deposition is detrimental to ecosystems, since it leads to decreased biological diversity (Clark and Tilman, 2008; Clark et al, 2013; Stevens et al, 2004), increased terrestrial and aquatic eutrophication (Bouwman et al, 2002; Bowman et al, 2008; Fisher et al, 2011), and acidification (Greaver et al, 2012; Savva and Berninger, 2010). For NH3, 80 % of the total emissions are from livestock manure management and chemical fertilizer in 2005 as estimated from the US National Emission Inventory (Reis et al, 2009), which are not regulated under current legislation and underwent significant increases over the past decades (Xing et al, 2013; Warner et al, 2017) Another possible source of NH3 emissions are vehicles, which may be twice as high as the emission estimates in the current National Emissions Inventory The primary emission source for sulfur deposition is sulfur dioxide (SO2), which mainly originates from fossil-fuel combustion (Smith et al, 2011)

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