A renewed rise in global HCFC-141b emissions between 2017–2021
<p>Global emissions of the ozone-depleting gas HCFC-141b (1,1-dichloro-1-fluoroethane, CH<span class="inline-formula"><sub>3</sub></span>CCl<span class="inline-formula"><sub>2</sub></span>F) derived from measurements of atmosp...
Main Authors: | , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , |
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Copernicus Publications
2022-07-01
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Series: | Atmospheric Chemistry and Physics |
Online Access: | https://acp.copernicus.org/articles/22/9601/2022/acp-22-9601-2022.pdf |
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author | L. M. Western L. M. Western A. L. Redington A. J. Manning C. M. Trudinger L. Hu L. Hu S. Henne X. Fang L. J. M. Kuijpers C. Theodoridi D. S. Godwin J. Arduini B. Dunse A. Engel P. J. Fraser C. M. Harth P. B. Krummel M. Maione J. Mühle S. O'Doherty H. Park S. Park S. Reimann P. K. Salameh D. Say R. Schmidt T. Schuck C. Siso C. Siso K. M. Stanley I. Vimont I. Vimont M. K. Vollmer D. Young R. G. Prinn R. F. Weiss S. A. Montzka M. Rigby |
author_facet | L. M. Western L. M. Western A. L. Redington A. J. Manning C. M. Trudinger L. Hu L. Hu S. Henne X. Fang L. J. M. Kuijpers C. Theodoridi D. S. Godwin J. Arduini B. Dunse A. Engel P. J. Fraser C. M. Harth P. B. Krummel M. Maione J. Mühle S. O'Doherty H. Park S. Park S. Reimann P. K. Salameh D. Say R. Schmidt T. Schuck C. Siso C. Siso K. M. Stanley I. Vimont I. Vimont M. K. Vollmer D. Young R. G. Prinn R. F. Weiss S. A. Montzka M. Rigby |
author_sort | L. M. Western |
collection | DOAJ |
description | <p>Global emissions of the ozone-depleting gas HCFC-141b (1,1-dichloro-1-fluoroethane, CH<span class="inline-formula"><sub>3</sub></span>CCl<span class="inline-formula"><sub>2</sub></span>F) derived from measurements of atmospheric mole fractions increased between 2017 and 2021 despite a fall in reported production and consumption of HCFC-141b for dispersive uses.
HCFC-141b is a controlled substance under the Montreal Protocol, and its phase-out is currently underway, after a peak in reported consumption and production in developing (Article 5) countries in 2013.
If reported production and consumption are correct, our study suggests that the 2017–2021 rise is due to an increase in emissions from the bank when appliances containing HCFC-141b reach the end of their life, or from production of HCFC-141b not reported for dispersive uses.
Regional emissions have been estimated between 2017–2020 for all regions where measurements have sufficient sensitivity to emissions.
This includes the regions of northwestern Europe, east Asia, the United States and Australia, where emissions decreased by a total of 2.3 <span class="inline-formula">±</span> 4.6 Gg yr<span class="inline-formula"><sup>−1</sup></span>, compared to a mean global increase of 3.0 <span class="inline-formula">±</span> 1.2 Gg yr<span class="inline-formula"><sup>−1</sup></span> over the same period.
Collectively these regions only account for around 30 % of global emissions in 2020.
We are not able to pinpoint the source regions or specific activities responsible for the recent global emission rise.</p> |
first_indexed | 2024-12-10T17:48:54Z |
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issn | 1680-7316 1680-7324 |
language | English |
last_indexed | 2024-12-10T17:48:54Z |
publishDate | 2022-07-01 |
publisher | Copernicus Publications |
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series | Atmospheric Chemistry and Physics |
spelling | doaj.art-e50fa04da87b464688ba8f00d7a5fd192022-12-22T01:39:09ZengCopernicus PublicationsAtmospheric Chemistry and Physics1680-73161680-73242022-07-01229601961610.5194/acp-22-9601-2022A renewed rise in global HCFC-141b emissions between 2017–2021L. M. Western0L. M. Western1A. L. Redington2A. J. Manning3C. M. Trudinger4L. Hu5L. Hu6S. Henne7X. Fang8L. J. M. Kuijpers9C. Theodoridi10D. S. Godwin11J. Arduini12B. Dunse13A. Engel14P. J. Fraser15C. M. Harth16P. B. Krummel17M. Maione18J. Mühle19S. O'Doherty20H. Park21S. Park22S. Reimann23P. K. Salameh24D. Say25R. Schmidt26T. Schuck27C. Siso28C. Siso29K. M. Stanley30I. Vimont31I. Vimont32M. K. Vollmer33D. Young34R. G. Prinn35R. F. Weiss36S. A. Montzka37M. Rigby38Global Monitoring Laboratory, National Oceanic and Atmospheric Administration, Boulder, CO, USASchool of Chemistry, University of Bristol, Bristol, UKHadley Centre, Met Office, Exeter, UKHadley Centre, Met Office, Exeter, UKClimate Science Centre, CSIRO Oceans and Atmosphere, Aspendale, Victoria, AustraliaGlobal Monitoring Laboratory, National Oceanic and Atmospheric Administration, Boulder, CO, USACooperative Institute for Research in Environmental Sciences, University of Colorado, Boulder, CO, USAEmpa, Swiss Federal Laboratories for Materials Science and Technology, Dübendorf, SwitzerlandCollege of Environmental and Resource Sciences, Zhejiang University, Hangzhou, Zhejiang, ChinaA/gent b.v. Consultancy, Venlo, NetherlandsNatural Resources Defense Council, Washington, DC, USAStratospheric Protection Division, Environmental Protection Agency, Washington, DC, USADepartment of Pure and Applied Sciences, University of Urbino, Urbino, ItalyClimate Science Centre, CSIRO Oceans and Atmosphere, Aspendale, Victoria, AustraliaInstitute for Atmospheric and Environmental Science, Goethe University Frankfurt, Frankfurt am Main, GermanyClimate Science Centre, CSIRO Oceans and Atmosphere, Aspendale, Victoria, AustraliaScripps Institution of Oceanography, University of California San Diego, La Jolla, CA, USAClimate Science Centre, CSIRO Oceans and Atmosphere, Aspendale, Victoria, AustraliaDepartment of Pure and Applied Sciences, University of Urbino, Urbino, ItalyScripps Institution of Oceanography, University of California San Diego, La Jolla, CA, USASchool of Chemistry, University of Bristol, Bristol, UKDepartment of Oceanography, Kyungpook National University, Daegu, Republic of KoreaDepartment of Oceanography, Kyungpook National University, Daegu, Republic of KoreaEmpa, Swiss Federal Laboratories for Materials Science and Technology, Dübendorf, SwitzerlandScripps Institution of Oceanography, University of California San Diego, La Jolla, CA, USASchool of Chemistry, University of Bristol, Bristol, UKScripps Institution of Oceanography, University of California San Diego, La Jolla, CA, USAInstitute for Atmospheric and Environmental Science, Goethe University Frankfurt, Frankfurt am Main, GermanyGlobal Monitoring Laboratory, National Oceanic and Atmospheric Administration, Boulder, CO, USACooperative Institute for Research in Environmental Sciences, University of Colorado, Boulder, CO, USAInstitute for Atmospheric and Environmental Science, Goethe University Frankfurt, Frankfurt am Main, GermanyGlobal Monitoring Laboratory, National Oceanic and Atmospheric Administration, Boulder, CO, USACooperative Institute for Research in Environmental Sciences, University of Colorado, Boulder, CO, USAEmpa, Swiss Federal Laboratories for Materials Science and Technology, Dübendorf, SwitzerlandSchool of Chemistry, University of Bristol, Bristol, UKCenter for Global Change Science, Massachusetts Institute of Technology, Cambridge, MA, USAScripps Institution of Oceanography, University of California San Diego, La Jolla, CA, USAGlobal Monitoring Laboratory, National Oceanic and Atmospheric Administration, Boulder, CO, USASchool of Chemistry, University of Bristol, Bristol, UK<p>Global emissions of the ozone-depleting gas HCFC-141b (1,1-dichloro-1-fluoroethane, CH<span class="inline-formula"><sub>3</sub></span>CCl<span class="inline-formula"><sub>2</sub></span>F) derived from measurements of atmospheric mole fractions increased between 2017 and 2021 despite a fall in reported production and consumption of HCFC-141b for dispersive uses. HCFC-141b is a controlled substance under the Montreal Protocol, and its phase-out is currently underway, after a peak in reported consumption and production in developing (Article 5) countries in 2013. If reported production and consumption are correct, our study suggests that the 2017–2021 rise is due to an increase in emissions from the bank when appliances containing HCFC-141b reach the end of their life, or from production of HCFC-141b not reported for dispersive uses. Regional emissions have been estimated between 2017–2020 for all regions where measurements have sufficient sensitivity to emissions. This includes the regions of northwestern Europe, east Asia, the United States and Australia, where emissions decreased by a total of 2.3 <span class="inline-formula">±</span> 4.6 Gg yr<span class="inline-formula"><sup>−1</sup></span>, compared to a mean global increase of 3.0 <span class="inline-formula">±</span> 1.2 Gg yr<span class="inline-formula"><sup>−1</sup></span> over the same period. Collectively these regions only account for around 30 % of global emissions in 2020. We are not able to pinpoint the source regions or specific activities responsible for the recent global emission rise.</p>https://acp.copernicus.org/articles/22/9601/2022/acp-22-9601-2022.pdf |
spellingShingle | L. M. Western L. M. Western A. L. Redington A. J. Manning C. M. Trudinger L. Hu L. Hu S. Henne X. Fang L. J. M. Kuijpers C. Theodoridi D. S. Godwin J. Arduini B. Dunse A. Engel P. J. Fraser C. M. Harth P. B. Krummel M. Maione J. Mühle S. O'Doherty H. Park S. Park S. Reimann P. K. Salameh D. Say R. Schmidt T. Schuck C. Siso C. Siso K. M. Stanley I. Vimont I. Vimont M. K. Vollmer D. Young R. G. Prinn R. F. Weiss S. A. Montzka M. Rigby A renewed rise in global HCFC-141b emissions between 2017–2021 Atmospheric Chemistry and Physics |
title | A renewed rise in global HCFC-141b emissions between 2017–2021 |
title_full | A renewed rise in global HCFC-141b emissions between 2017–2021 |
title_fullStr | A renewed rise in global HCFC-141b emissions between 2017–2021 |
title_full_unstemmed | A renewed rise in global HCFC-141b emissions between 2017–2021 |
title_short | A renewed rise in global HCFC-141b emissions between 2017–2021 |
title_sort | renewed rise in global hcfc 141b emissions between 2017 2021 |
url | https://acp.copernicus.org/articles/22/9601/2022/acp-22-9601-2022.pdf |
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