The effect of barrier location on characteristics of gas pollutant transfer in the vicinity of highway

2021 ◽  
Vol 28 (3) ◽  
pp. 369-381
Author(s):  
S. A. Lavruk ◽  
S. A. Valger
Keyword(s):  
1996 ◽  
Vol 68 (9) ◽  
pp. 1771-1780 ◽  
Author(s):  
K. Ballschmiter

The relationship between physicochemical properties, environmental distribution and effects of organochlorine compounds as a major class of persistent organic pollutants (POPs) are discussed. The environmental fate of a compound includes its transport and dispersion in the environment as well as its accumulation and transformation in defined environmental compartments. Accumulation and transformation as the result of environmental distribution may have long-term consequences; this is indicated by the ultimate accumulation and long-term bioactivity of several widely spread organochlorines, and is clearly evident in the decomposition of chlorofluorocarbons in the stratosphere.Depending on the order of trophic levelsbiomagnifiaction factors of 10,000 up to 100,000 are encountered for persistentsemivolatile organochlorines such as 4,4'-DDE, PCB congeners or some Toxapheneconstituents. Mammals show intra-species pollutant transfer during thelactation period. While the mother animal is partly depleting its bodyburden, the calve accumulates in a critical period of its life via themilk a concentrated input of persistent organochlorines. A similar depletionphenomenon is also found for fish and crustacean which enrich in the eggsa substantial part of the accumulated body burden of the female.The air skimming of semivolatiles by plantsurfaces leads to surprisingly high levels of pollutants in the uppersoil layers of forests that otherwise would be considered pristine interms of human activities.


2005 ◽  
Vol 39 (14) ◽  
pp. 2661-2672 ◽  
Author(s):  
M SADIKI ◽  
F QUENTEL ◽  
C ELLEOUET ◽  
L STEPHAN ◽  
R OLIER ◽  
...  

2021 ◽  
Vol 1 (5(69)) ◽  
pp. 58-63
Author(s):  
M. Biliaiev ◽  
V. Biliaieva ◽  
O. Berlov ◽  
V. Kozachyna

The problem of air pollution modelling near road which is situated in complex terrain is under consideration. To simulate wind flow pattern in case of complex terrain Navier-Stokes’s equations were used. NavierStokes’s equations were written using Helmholtz variables. Numerical finite difference schemes of splitting were used for numerical integration of Navier-Stokes’s equations. Equation of connective-diffusive pollutant transfer was used to simulate air pollution. Finite difference scheme of splitting was used for numerical integration of convectivediffusive equation of pollutant transfer. Computer code was developed on the basis of created numerical model. The results of a numerical experiment are presented.


2021 ◽  
Vol 8 ◽  
Author(s):  
Kugako Sugimoto ◽  
Hideki Fukuda ◽  
Isao Koike ◽  
Toshi Nagata

Transparent exopolymer particles (TEPs) play important roles in the regulation of carbon and pollutant (microplastics and spilled oils) transport in marine environments; however, the factors controlling TEP dynamics in coastal systems have yet to be fully clarified. A widely used colorimetric method quantifies TEPs as a homogeneous pool, which hampers the examination of internal TEP dynamics. Here, we used the microscopy to elucidate the seasonal dynamics of TEP subgroups and their controlling factors in Sagami Bay, Japan. TEPs were classified into three types: those not associated with other types of particles (Type I), those colonized by multiple types of particles (bacteria, algal cells, and detritus) (Type II), and those densely colonized by only bacterial clusters (Type III). Type II was generally the most dominant TEP component in terms of area, except in February, when Type I contributed substantially to the total TEP area. Type III was less abundant in terms of area but contributed substantially (up to 34%) to the total number of TEPs. The mean diameters were 14.0 ± 2.8 μm, 17.0 ± 5.8 μm, and 7.5 ± 0.9 μm for Type I, Type II, and Type III TEPs, respectively. Type I and Type III TEPs likely represent a transient phase of TEP development toward the formation of Type II, characterized by a high turnover and relatively low abundance in terms of area. The power-law slopes of the distributions of each TEP size, which reflected geometric features of the TEPs at steady state, changed dynamically over the seasons. The abundance of each type of TEP was significantly positively correlated with bacterial abundance, suggesting that bacteria are intimately involved in the regulation of internal TEP dynamics in Sagami Bay. Our results highlight the importance of investigating the internal dynamics of TEPs to improve current understanding of their roles in the regulation of carbon and pollutant transfer in marine environments.


1988 ◽  
Vol 20 (6-7) ◽  
pp. 175-182
Author(s):  
W. R. Parker

The role played by fine cohesive sediment in the transport and recycling of pollutants arises from the often reversible partition of pollutants between the dissolved phase and surface sorbed phase. Adequate prediction requires that a realistic understanding of the physical behaviour of the fine sediment population of an area is coupled with the kinetics of the sorbtion/desorbtion equilibria at crucial stages in the fine sediment transport cycle. This paper examines the physical basis underlying the prediction of fine sediment transport, identifying processes and phenomena which are important in affecting predictions. Parameterisation of source and sink terms are seen to be areas of great uncertainty and model calibration requires the deployment of new, but available, technology.


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