5 research outputs found
Nitrogen Stable Isotope Composition (δ<sup>15</sup>N) of Vehicle-Emitted NO<sub><i>x</i></sub>
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>
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
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
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 coverî—¸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
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