3 research outputs found
Chemical Method for Nitrogen Isotopic Analysis of Ammonium at Natural Abundance
We report a new chemical method to
determine the <sup>15</sup>N
natural abundance (δ<sup>15</sup>N) for ammonium (NH<sub>4</sub><sup>+</sup>) in freshwater (e.g., precipitation) and soil KCl extract.
This method is based on the isotopic analysis of nitrous oxide (N<sub>2</sub>O). Ammonium is initially oxidized to nitrite (NO<sub>2</sub><sup>–</sup>) by hypobromite (BrO<sup>–</sup>) using
previously established procedures. NO<sub>2</sub><sup>–</sup> is then quantitatively converted into N<sub>2</sub>O by hydroxylamine
(NH<sub>2</sub>OH) under strongly acid conditions. The produced N<sub>2</sub>O is analyzed by a commercially available purge and cryogenic
trap system coupled to an isotope ratio mass spectrometer (PT-IRMS).
On the basis of a typical analysis size of 4 mL, the standard deviation
of δ<sup>15</sup>N measurements is less than 0.3‰ and
often better than 0.1‰ (3 to 5 replicates). Compared to previous
methods, the technique here has several advantages and the potential
to be used as a routine method for <sup>15</sup>N/<sup>14</sup>N analysis
of NH<sub>4</sub><sup>+</sup>: (1) substantially simplified preparation
procedures and reduced preparation time particularly compared to the
methods in which diffusion or distillation is involved since all reactions
occur in the same vial and separation of NH<sub>4</sub><sup>+</sup> from solution is not required; (2) more suitability for low volume
samples including those with low N concentration, having a blank size
of 0.6 to 2 nmol; (3) elimination of the use of extremely toxic reagents
(e.g., HN<sub>3</sub>) and/or the use of specialized denitrifying
bacterial cultures which may be impractical for many laboratories
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
Identifying Ammonia Hotspots in China Using a National Observation Network
The
limited availability of ammonia (NH<sub>3</sub>) measurements
is currently a barrier to understanding the vital role of NH<sub>3</sub> in secondary aerosol formation during haze pollution events and
prevents a full assessment of the atmospheric deposition of reactive
nitrogen. The observational gaps motivated us to design this study
to investigate the spatial distributions and seasonal variations in
atmospheric NH<sub>3</sub> on a national scale in China. On the basis
of a 1-year observational campaign at 53 sites with uniform protocols,
we confirm that abundant concentrations of NH<sub>3</sub> [1 to 23.9
μg m<sup>–3</sup>] were identified in typical agricultural
regions, especially over the North China Plain (NCP). The spatial pattern
of the NH<sub>3</sub> surface concentration was generally similar
to those of the satellite column concentrations as well as a bottom-up
agriculture NH<sub>3</sub> emission inventory. However, the observed NH<sub>3</sub> concentrations at urban and desert sites were comparable
with those from agricultural sites and 2–3 times those of mountainous/forest/grassland/waterbody
sites. We also found that NH<sub>3</sub> deposition fluxes at urban
sites account for only half of the emissions in the NCP, suggesting
the transport of urban NH<sub>3</sub> emissions to downwind areas.
This finding provides policy makers with insights into the potential
mitigation of nonagricultural NH<sub>3</sub> sources in developed
regions