Methodology for Measurement of Ammonia Emissions from Intensive Pig Farming
Determination of ammonia (NH<sub>3</sub>) emissions for intensive livestock facilities (pork, poultry) is important from both a regulatory and a research point of view. Buildings housing livestock are a large source of ammonia emissions from the agriculture sector. However, measurements...
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2021
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oai:doaj.org-article:c5ffad80eccd4a7493d715bfc582cd632021-11-25T15:58:39ZMethodology for Measurement of Ammonia Emissions from Intensive Pig Farming10.3390/agriculture111110732077-0472https://doaj.org/article/c5ffad80eccd4a7493d715bfc582cd632021-10-01T00:00:00Zhttps://www.mdpi.com/2077-0472/11/11/1073https://doaj.org/toc/2077-0472Determination of ammonia (NH<sub>3</sub>) emissions for intensive livestock facilities (pork, poultry) is important from both a regulatory and a research point of view. Buildings housing livestock are a large source of ammonia emissions from the agriculture sector. However, measurements to determine emissions can be time-consuming and costly. Therefore, it is essential to find a suitable methodology for monitoring NH<sub>3</sub>. The methodology for determining NH<sub>3</sub> emissions is legislatively unified in terms of sampling methodology, including sampling time (24 h), sampling points (input/output), number of sampling days, and their distribution during the year, and to determine only a general calculation of the annual average NH<sub>3</sub> emissions. For this reason, the researchers chose different approaches for the calculation of NH<sub>3</sub> emissions, and these approaches are not unified. Based on accurate monitoring and created models, the authors proposed a methodology for calculation of NH<sub>3</sub> emissions, which divides the 24 h measurement into time windows (30 min), from which the arithmetic mean and standard deviation are determined, and the total emissions for one year is determined. The chosen time windows for the partial calculation are important from the point of view of reflecting the microclimatic conditions inside the stable and the device limits for sampling the NH<sub>3</sub> concentration and airflow.Pavel KrizRadim KunesLubos SmutnyPavel CernyZbynek HavelkaPavel OlsanMaohua XiaoRadim StehlikAntonin DolanPetr BartosMDPI AGarticleInnova 1412NH<sub>3</sub>welfaremicroclimatic conditionslivestockenvironmentAgriculture (General)S1-972ENAgriculture, Vol 11, Iss 1073, p 1073 (2021) |
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Innova 1412 NH<sub>3</sub> welfare microclimatic conditions livestock environment Agriculture (General) S1-972 |
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Innova 1412 NH<sub>3</sub> welfare microclimatic conditions livestock environment Agriculture (General) S1-972 Pavel Kriz Radim Kunes Lubos Smutny Pavel Cerny Zbynek Havelka Pavel Olsan Maohua Xiao Radim Stehlik Antonin Dolan Petr Bartos Methodology for Measurement of Ammonia Emissions from Intensive Pig Farming |
description |
Determination of ammonia (NH<sub>3</sub>) emissions for intensive livestock facilities (pork, poultry) is important from both a regulatory and a research point of view. Buildings housing livestock are a large source of ammonia emissions from the agriculture sector. However, measurements to determine emissions can be time-consuming and costly. Therefore, it is essential to find a suitable methodology for monitoring NH<sub>3</sub>. The methodology for determining NH<sub>3</sub> emissions is legislatively unified in terms of sampling methodology, including sampling time (24 h), sampling points (input/output), number of sampling days, and their distribution during the year, and to determine only a general calculation of the annual average NH<sub>3</sub> emissions. For this reason, the researchers chose different approaches for the calculation of NH<sub>3</sub> emissions, and these approaches are not unified. Based on accurate monitoring and created models, the authors proposed a methodology for calculation of NH<sub>3</sub> emissions, which divides the 24 h measurement into time windows (30 min), from which the arithmetic mean and standard deviation are determined, and the total emissions for one year is determined. The chosen time windows for the partial calculation are important from the point of view of reflecting the microclimatic conditions inside the stable and the device limits for sampling the NH<sub>3</sub> concentration and airflow. |
format |
article |
author |
Pavel Kriz Radim Kunes Lubos Smutny Pavel Cerny Zbynek Havelka Pavel Olsan Maohua Xiao Radim Stehlik Antonin Dolan Petr Bartos |
author_facet |
Pavel Kriz Radim Kunes Lubos Smutny Pavel Cerny Zbynek Havelka Pavel Olsan Maohua Xiao Radim Stehlik Antonin Dolan Petr Bartos |
author_sort |
Pavel Kriz |
title |
Methodology for Measurement of Ammonia Emissions from Intensive Pig Farming |
title_short |
Methodology for Measurement of Ammonia Emissions from Intensive Pig Farming |
title_full |
Methodology for Measurement of Ammonia Emissions from Intensive Pig Farming |
title_fullStr |
Methodology for Measurement of Ammonia Emissions from Intensive Pig Farming |
title_full_unstemmed |
Methodology for Measurement of Ammonia Emissions from Intensive Pig Farming |
title_sort |
methodology for measurement of ammonia emissions from intensive pig farming |
publisher |
MDPI AG |
publishDate |
2021 |
url |
https://doaj.org/article/c5ffad80eccd4a7493d715bfc582cd63 |
work_keys_str_mv |
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1718413405686071296 |