Contaminant Dispersion Model In A Water Body - Case Study: Rio Paraibuna

Author(s):  
Guilherme Jahnecke Weymar ◽  
Silvana Garcia ◽  
Daniela Buske ◽  
Igor Furtado ◽  
Hugo Alexandre Soares Guedes
2019 ◽  
Vol 100 ◽  
pp. 00070 ◽  
Author(s):  
Elżbieta Romanik ◽  
Yaroslav Bezyk ◽  
Marcin Pawnuk ◽  
Urszula Miller ◽  
Agnieszka Grzelka

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 dispersion model – OPERAT FB software for the grid size 2 x 2 km. The conducted research shows a significant improvement in the odour impact range of chosen industrial source in year 2018 compared to 2017.


2021 ◽  
Vol 137 (4) ◽  
pp. 98
Author(s):  
V.A. Shaimova ◽  
Yu.V. Nosul ◽  
S.Kh. Kuchkildina ◽  
A.N. Kulikov ◽  
D.S. Maltsev ◽  
...  
Keyword(s):  

2019 ◽  
Vol 38 (1) ◽  
pp. 403-413
Author(s):  
Yubing Gao ◽  
Hainan Gao ◽  
Xingyu Zhang

2020 ◽  
Vol 12 (24) ◽  
pp. 10549
Author(s):  
Marinella Giunta

The road sector is one of the main sources of air emissions in the atmosphere during both construction and operation. The objective of the present paper is a comprehensive evaluation of the impact on air quality during the two main phases of life cycle of roads. In this case study of a motorway project, the emissions of the primary pollutants, CO, NOx, and PM10 are estimated, and the results showed that (i) CO and NOx pollutants released during both phases are comparable, while the emissions of PM10 are more significant in the construction phase; (ii) 85% of PM10 in construction is due to storage, transit on unpaved road, and crushing; (iii) the portals of the tunnel are the sites where there are higher concentrations of pollutants in operation; and (iv) the CO concentrations estimated by the dispersion model are strongly influenced by the topography.


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