2019
DOI: 10.1051/e3sconf/201910000070
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Influence of the variability of the odour emission rate on its impact range: a case study of the selected industrial source

Abstract: Odour concentration measurements in a chosen industrial source were made in this study using the method of dynamic olfactometry. The two different scenarios considered the variation of the odour emission rate as input for the dispersion model were compared for the period 2017 (before installation of the equipment for gas treatment) and 2018 (after implementation of purifying technologies). In this paper the odour impact range was determined by applying model calculations conducted in the Polish reference dispe… Show more

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Cited by 2 publications
(3 citation statements)
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“…In 2019, Romanik et al [29] presented a comparative analysis, based on the combination of dynamic olfactometry and dispersion modelling, of the emission scenario relevant to an industrial activity before and after the installation of abatement equipment. The results obtained satisfied the twofold purpose of the study of proposing an experimental procedure to assess the odor impact at the sensible receptors and to evaluate the effectiveness of the technical intervention in the reduction of odorous emissions.…”
Section: Examples Of Applicationsmentioning
confidence: 99%
“…In 2019, Romanik et al [29] presented a comparative analysis, based on the combination of dynamic olfactometry and dispersion modelling, of the emission scenario relevant to an industrial activity before and after the installation of abatement equipment. The results obtained satisfied the twofold purpose of the study of proposing an experimental procedure to assess the odor impact at the sensible receptors and to evaluate the effectiveness of the technical intervention in the reduction of odorous emissions.…”
Section: Examples Of Applicationsmentioning
confidence: 99%
“…where S xyz -the concentration of the substance in the air averaged for one hour (µg/m 3 ); E g -maximum emission of gaseous substance (mg/s); σ y -horizontal atmospheric diffusion coefficient (m); σ z -vertical atmospheric diffusion coefficient (m); u-average wind velocity in the layer from the geometric height of the emitter h to the effective height of the emitter H (m/s); y-component of the distance of the emitter from the point for which calculations are made perpendicular to the wind direction (m); z-the height at which the concentration of the substance in the air is calculated (m). The model mentioned above was used, among others, for the assessment of the odour impact of a waste management plant [14], the assessment of the odour impact of a waste composting plant located at the waste management plant [21], the odour assessment of an industrial facility [22], and the odour impact assessment of a sewage treatment plant [19]. Therefore, it was used to assess the olfactory impact of the farm site under study.…”
Section: Modelling Of the Spread Of Odour Pollutantsmentioning
confidence: 99%
“…This project indicated, among others, that the value of the comparative level of the permissible concentration of odours in the air equals 1 ou E /m 3 or the value of the permissible frequency of exceeding the permissible level of 1 ou E /m 3 equals 3% per year. These values are often used in the literature related to the determination of the odour impact of various objects [14,19,21,22]. These values may differ between individual countries depending on the solutions adopted [23].…”
Section: Introductionmentioning
confidence: 99%