5 research outputs found

    Nitrogen Stable Isotope Composition (δ<sup>15</sup>N) of Vehicle-Emitted NO<sub><i>x</i></sub>

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    The nitrogen stable isotope ratio of NO<sub><i>x</i></sub> (δ<sup>15</sup>N-NO<sub><i>x</i></sub>) has been proposed as a regional indicator for NO<sub><i>x</i></sub> source partitioning; however, knowledge of δ<sup>15</sup>N values from various NO<sub><i>x</i></sub> emission sources is limited. This study presents a detailed analysis of δ<sup>15</sup>N-NO<sub><i>x</i></sub> emitted from vehicle exhaust, the largest source of anthropogenic NO<sub><i>x</i></sub>. To accomplish this, NO<sub><i>x</i></sub> was collected from 26 different vehicles, including gasoline and diesel-powered engines, using a modification of a NO<sub><i>x</i></sub> collection method used by the United States Environmental Protection Agency, and δ<sup>15</sup>N-NO<sub><i>x</i></sub> was analyzed. The vehicles sampled in this study emitted δ<sup>15</sup>N-NO<sub><i>x</i></sub> values ranging from −19.1 to 9.8‰ that negatively correlated with the emitted NO<sub><i>x</i></sub> concentrations (8.5 to 286 ppm) and vehicle run time because of kinetic isotope fractionation effects associated with the catalytic reduction of NO<sub><i>x</i></sub>. A model for determining the mass-weighted δ<sup>15</sup>N-NO<sub><i>x</i></sub> from vehicle exhaust was constructed on the basis of average commute times, and the model estimates an average value of −2.5 ± 1.5‰, with slight regional variations. As technology improvements in catalytic converters reduce cold-start emissions in the future, it is likely to increase current δ<sup>15</sup>N-NO<sub><i>x</i></sub> values emitted from vehicles

    Nitrogen Stable Isotope Composition (δ<sup>15</sup>N) of Vehicle-Emitted NO<sub><i>x</i></sub>

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    The nitrogen stable isotope ratio of NO<sub><i>x</i></sub> (δ<sup>15</sup>N-NO<sub><i>x</i></sub>) has been proposed as a regional indicator for NO<sub><i>x</i></sub> source partitioning; however, knowledge of δ<sup>15</sup>N values from various NO<sub><i>x</i></sub> emission sources is limited. This study presents a detailed analysis of δ<sup>15</sup>N-NO<sub><i>x</i></sub> emitted from vehicle exhaust, the largest source of anthropogenic NO<sub><i>x</i></sub>. To accomplish this, NO<sub><i>x</i></sub> was collected from 26 different vehicles, including gasoline and diesel-powered engines, using a modification of a NO<sub><i>x</i></sub> collection method used by the United States Environmental Protection Agency, and δ<sup>15</sup>N-NO<sub><i>x</i></sub> was analyzed. The vehicles sampled in this study emitted δ<sup>15</sup>N-NO<sub><i>x</i></sub> values ranging from −19.1 to 9.8‰ that negatively correlated with the emitted NO<sub><i>x</i></sub> concentrations (8.5 to 286 ppm) and vehicle run time because of kinetic isotope fractionation effects associated with the catalytic reduction of NO<sub><i>x</i></sub>. A model for determining the mass-weighted δ<sup>15</sup>N-NO<sub><i>x</i></sub> from vehicle exhaust was constructed on the basis of average commute times, and the model estimates an average value of −2.5 ± 1.5‰, with slight regional variations. As technology improvements in catalytic converters reduce cold-start emissions in the future, it is likely to increase current δ<sup>15</sup>N-NO<sub><i>x</i></sub> values emitted from vehicles

    Using <sup>15</sup>N, <sup>17</sup>O, and <sup>18</sup>O To Determine Nitrate Sources in the Yellow River, China

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    Many previous studies have used δ<sup>15</sup>N and δ<sup>18</sup>O of nitrate (δ<sup>15</sup>N<sub>NO3</sub> and δ<sup>18</sup>O<sub>NO3</sub>) to determine the nitrate sources in rivers but were subject to substantial uncertainties and limitations, especially associated with evaluating the atmospheric contribution. The Δ<sup>17</sup>O of nitrate (Δ<sup>17</sup>O<sub>NO3</sub>) has been suggested as an unambiguous tracer of atmospheric NO<sub>3</sub><sup>–</sup> and may serve as an additional nitrate source constraint. In the present study, triple nitrate isotopes (δ<sup>15</sup>N<sub>NO3</sub>, Δ<sup>17</sup>O<sub>NO3</sub>, and δ<sup>18</sup>O<sub>NO3</sub>) were used for the first time to assess the sources and sinks of nitrate in the Yellow River (YR) basin, which is the second longest river in China. Results showed that the Δ<sup>17</sup>O<sub>NO3</sub> of the water from the YR ranged from 0‰ to 1.6‰ during two normal-water seasons. This suggested that unprocessed atmospheric nitrate accounted for 0–7% of the total nitrate in the YR. The corrected δ<sup>15</sup>N<sub>NO3</sub> and δ<sup>18</sup>O<sub>NO3</sub> values with atmospheric imprints being removed indicated that the main terrestrial sources of nitrate were sewage/manure effluents in the upstream of the YR and manure/sewage effluents and ammonium/urea-containing fertilizer in the middle and lower reaches which made comparable contributions to the nitrate. In addition, there was a significant positive relationship between δ<sup>15</sup>N<sub>NO3</sub> and δ<sup>18</sup>O<sub>NO3</sub> values of river water (<i>p</i> < 0.01) which may signal the presence of denitrification. This study indicates that the triple nitrate isotope method is useful for assessing the nitrate sources in rivers, especially for the measurements of atmospheric nitrate contribution

    Sources and Transport of Nitrogen in Arid Urban Watersheds

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    Urban watersheds are often sources of nitrogen (N) to downstream systems, contributing to poor water quality. However, it is unknown which components (e.g., land cover and stormwater infrastructure type) of urban watersheds contribute to N export and which may be sites of retention. In this study we investigated which watershed characteristics control N sourcing, biogeochemical processing of nitrate (NO<sub>3</sub><sup>–</sup>) during storms, and the amount of rainfall N that is retained within urban watersheds. We used triple isotopes of NO<sub>3</sub><sup>–</sup> (δ<sup>15</sup>N, δ<sup>18</sup>O, and Δ<sup>17</sup>O) to identify sources and transformations of NO<sub>3</sub><sup>–</sup> during storms from 10 nested arid urban watersheds that varied in stormwater infrastructure type and drainage area. Stormwater infrastructure and land coverretention basins, pipes, and grass coverdictated the sourcing of NO<sub>3</sub><sup>–</sup> in runoff. Urban watersheds were strong sinks or sources of N to stormwater depending on runoff, which in turn was inversely related to retention basin density and positively related to imperviousness and precipitation. Our results suggest that watershed characteristics control the sources and transport of inorganic N in urban stormwater but that retention of inorganic N at the time scale of individual runoff events is controlled by hydrologic, rather than biogeochemical, mechanisms

    Fossil Fuel Combustion-Related Emissions Dominate Atmospheric Ammonia Sources during Severe Haze Episodes: Evidence from <sup>15</sup>N‑Stable Isotope in Size-Resolved Aerosol Ammonium

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    The reduction of ammonia (NH<sub>3</sub>) emissions is urgently needed due to its role in aerosol nucleation and growth causing haze formation during its conversion into ammonium (NH<sub>4</sub><sup>+</sup>). However, the relative contributions of individual NH<sub>3</sub> sources are unclear, and debate remains over whether agricultural emissions dominate atmospheric NH<sub>3</sub> in urban areas. Based on the chemical and isotopic measurements of size-resolved aerosols in urban Beijing, China, we find that the natural abundance of <sup>15</sup>N (expressed using δ<sup>15</sup>N values) of NH<sub>4</sub><sup>+</sup> in fine particles varies with the development of haze episodes, ranging from −37.1‰ to −21.7‰ during clean/dusty days (relative humidity: ∼ 40%), to −13.1‰ to +5.8‰ during hazy days (relative humidity: 70–90%). After accounting for the isotope exchange between NH<sub>3</sub> gas and aerosol NH<sub>4</sub><sup>+</sup>, the δ<sup>15</sup>N value of the initial NH<sub>3</sub> during hazy days is found to be −14.5‰ to −1.6‰, which indicates fossil fuel-based emissions. These emissions contribute 90% of the total NH<sub>3</sub> during hazy days in urban Beijing. This work demonstrates the analysis of δ<sup>15</sup>N values of aerosol NH<sub>4</sub><sup>+</sup> to be a promising new tool for partitioning atmospheric NH<sub>3</sub> sources, providing policy makers with insights into NH<sub>3</sub> emissions and secondary aerosols for regulation in urban environments
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