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δ(15)N-stable isotope analysis of NH(x): An overview on analytical measurements, source sampling and its source apportionment

Agricultural sources and non-agricultural emissions contribute to gaseous ammonia (NH(3)) that plays a vital role in severe haze formation. Qualitative and quantitative contributions of these sources to ambient PM(2.5) (particulate matter with an aerodynamic equivalent diameter below 2.5 µm) concent...

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Autores principales: Bhattarai, Noshan, Wang, Shuxiao, Pan, Yuepeng, Xu, Qingcheng, Zhang, Yanlin, Chang, Yunhua, Fang, Yunting
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Higher Education Press 2021
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7982311/
https://www.ncbi.nlm.nih.gov/pubmed/33777477
http://dx.doi.org/10.1007/s11783-021-1414-6
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author Bhattarai, Noshan
Wang, Shuxiao
Pan, Yuepeng
Xu, Qingcheng
Zhang, Yanlin
Chang, Yunhua
Fang, Yunting
author_facet Bhattarai, Noshan
Wang, Shuxiao
Pan, Yuepeng
Xu, Qingcheng
Zhang, Yanlin
Chang, Yunhua
Fang, Yunting
author_sort Bhattarai, Noshan
collection PubMed
description Agricultural sources and non-agricultural emissions contribute to gaseous ammonia (NH(3)) that plays a vital role in severe haze formation. Qualitative and quantitative contributions of these sources to ambient PM(2.5) (particulate matter with an aerodynamic equivalent diameter below 2.5 µm) concentrations remains uncertain. Stable nitrogen isotopic composition (δ(15)N) of NH(3) and NH(4)(+) (δ(15)N(NH(3)) and δ(15)N(NH(4)(+)), respectively) can yield valuable information about its sources and associated processes. This review provides an overview of the recent progress in analytical techniques for δ(15)N(NH(3)) and δ(15)N(NH(4)(+)) measurement, sampling of atmospheric NH(3) and NH(4)(+) in the ambient air and their sources signature (e.g., agricultural vs. fossil fuel), and isotope-based source apportionment of NH(3) in urban atmosphere. This study highlights that collecting sample that are fully representative of emission sources remains a challenge in fingerprinting δ(15)N(NH(3)) values of NH(3) emission sources. Furthermore, isotopic fractionation during NH(3) gas-to-particle conversion under varying ambient field conditions (e.g., relative humidity, particle pH, temperature) remains unclear, which indicates more field and laboratory studies to validate theoretically predicted isotopic fractionation are required. Thus, this study concludes that lack of refined δ(15)N(NH(3)) fingerprints and full understanding of isotopic fractionation during aerosol formation in a laboratory and field conditions is a limitation for isotope-based source apportionment of NH(3). More experimental work (in chamber studies) and theoretical estimations in combinations of field verification are necessary in characterizing isotopic fractionation under various environmental and atmospheric neutralization conditions, which would help to better interpret isotopic data and our understanding on NH(x) (NH(3) + NH(4)(+)) dynamics in the atmosphere. [Image: see text] ELECTRONIC SUPPLEMENTARY MATERIAL: Supplementary material is available in the online version of this article at 10.1007/s11783-021-1414-6 and is accessible for authorized users. Supplementary material includes supplementary tables on summary of recent isotope-based source apportionment studies on ambient NH(3) derived from δ(15)N(NH(3)) values (Table A1); and summary of recent isotope-based source apportionment studies on particulate NH(4)(+) derived from δ(15)N(NH(4)(+)) values (Table A2).
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spelling pubmed-79823112021-03-23 δ(15)N-stable isotope analysis of NH(x): An overview on analytical measurements, source sampling and its source apportionment Bhattarai, Noshan Wang, Shuxiao Pan, Yuepeng Xu, Qingcheng Zhang, Yanlin Chang, Yunhua Fang, Yunting Front Environ Sci Eng Review Article Agricultural sources and non-agricultural emissions contribute to gaseous ammonia (NH(3)) that plays a vital role in severe haze formation. Qualitative and quantitative contributions of these sources to ambient PM(2.5) (particulate matter with an aerodynamic equivalent diameter below 2.5 µm) concentrations remains uncertain. Stable nitrogen isotopic composition (δ(15)N) of NH(3) and NH(4)(+) (δ(15)N(NH(3)) and δ(15)N(NH(4)(+)), respectively) can yield valuable information about its sources and associated processes. This review provides an overview of the recent progress in analytical techniques for δ(15)N(NH(3)) and δ(15)N(NH(4)(+)) measurement, sampling of atmospheric NH(3) and NH(4)(+) in the ambient air and their sources signature (e.g., agricultural vs. fossil fuel), and isotope-based source apportionment of NH(3) in urban atmosphere. This study highlights that collecting sample that are fully representative of emission sources remains a challenge in fingerprinting δ(15)N(NH(3)) values of NH(3) emission sources. Furthermore, isotopic fractionation during NH(3) gas-to-particle conversion under varying ambient field conditions (e.g., relative humidity, particle pH, temperature) remains unclear, which indicates more field and laboratory studies to validate theoretically predicted isotopic fractionation are required. Thus, this study concludes that lack of refined δ(15)N(NH(3)) fingerprints and full understanding of isotopic fractionation during aerosol formation in a laboratory and field conditions is a limitation for isotope-based source apportionment of NH(3). More experimental work (in chamber studies) and theoretical estimations in combinations of field verification are necessary in characterizing isotopic fractionation under various environmental and atmospheric neutralization conditions, which would help to better interpret isotopic data and our understanding on NH(x) (NH(3) + NH(4)(+)) dynamics in the atmosphere. [Image: see text] ELECTRONIC SUPPLEMENTARY MATERIAL: Supplementary material is available in the online version of this article at 10.1007/s11783-021-1414-6 and is accessible for authorized users. Supplementary material includes supplementary tables on summary of recent isotope-based source apportionment studies on ambient NH(3) derived from δ(15)N(NH(3)) values (Table A1); and summary of recent isotope-based source apportionment studies on particulate NH(4)(+) derived from δ(15)N(NH(4)(+)) values (Table A2). Higher Education Press 2021-03-15 2021 /pmc/articles/PMC7982311/ /pubmed/33777477 http://dx.doi.org/10.1007/s11783-021-1414-6 Text en © Higher Education Press 2021 This article is made available via the PMC Open Access Subset for unrestricted research re-use and secondary analysis in any form or by any means with acknowledgement of the original source. These permissions are granted for the duration of the World Health Organization (WHO) declaration of COVID-19 as a global pandemic.
spellingShingle Review Article
Bhattarai, Noshan
Wang, Shuxiao
Pan, Yuepeng
Xu, Qingcheng
Zhang, Yanlin
Chang, Yunhua
Fang, Yunting
δ(15)N-stable isotope analysis of NH(x): An overview on analytical measurements, source sampling and its source apportionment
title δ(15)N-stable isotope analysis of NH(x): An overview on analytical measurements, source sampling and its source apportionment
title_full δ(15)N-stable isotope analysis of NH(x): An overview on analytical measurements, source sampling and its source apportionment
title_fullStr δ(15)N-stable isotope analysis of NH(x): An overview on analytical measurements, source sampling and its source apportionment
title_full_unstemmed δ(15)N-stable isotope analysis of NH(x): An overview on analytical measurements, source sampling and its source apportionment
title_short δ(15)N-stable isotope analysis of NH(x): An overview on analytical measurements, source sampling and its source apportionment
title_sort δ(15)n-stable isotope analysis of nh(x): an overview on analytical measurements, source sampling and its source apportionment
topic Review Article
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7982311/
https://www.ncbi.nlm.nih.gov/pubmed/33777477
http://dx.doi.org/10.1007/s11783-021-1414-6
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