Mass concentration of PM10 and PM2.5 fine-dispersed aerosol fractions in the Eastern Gobi Desert

2013 ◽  
Vol 38 (2) ◽  
pp. 80-87 ◽  
Author(s):  
A. L. Dement’eva ◽  
G. S. Zhamsueva ◽  
A. S. Zayakhanov ◽  
V. V. Tsydypov ◽  
A. A. Ayurzhanaev ◽  
...  
2021 ◽  
Vol 11 (24) ◽  
pp. 11958
Author(s):  
Soo-Min Choi ◽  
Hyo Choi

Multiple statistical prediction modeling of PM10, PM2.5 and PM1 at Gangneung city, Korea, was performed in association with local meteorological parameters (air temperature, wind speed and relative humidity) and PM10 and PM2.5 concentrations of an upwind site in Beijing, China, in the transport route of Chinese yellow dusts which originated from the Gobi Desert and passed through Beijing to the city from 18 March to 27 March 2015. Before and after the dust periods, the PM10, PM2.5 and PM1 concentrations showed as being very high at 09:00 LST (the morning rush hour) by the increasing emitted pollutants from vehicles and flying dust from the road and their maxima occurred at 20:00 to 22:00 LST (the evening departure time) from the additional pollutants from resident heating boilers. During the dust period, these peak trends were not found due to the persistent accumulation of dust in the city from the Gobi Desert through Beijing, China, as shown in real-time COMS-AI satellite images. Multiple correlation coefficients among PM10, PM2.5 and PM1 at Gangneung were in the range of 0.916 to 0.998. Multiple statistical models were devised to predict each PM concentration, and the significant levels through multi-regression analyses were p < 0.001, showing all the coefficients to be significant. The observed and calculated PM concentrations were compared, and new linear regression models were sequentially suggested to reproduce the original observed PM values with improved correlation coefficients, to some extent.


ASJ. ◽  
2021 ◽  
Vol 1 (44) ◽  
pp. 9-14
Author(s):  
G. Fedorovitch

A rational criterion for the hygienic relevance of the surface area of dust settling in the lungs is formulated in the article.  The differential parameters of airborne dust are determined by measuring the mass concentration of particular matter PM10 and PM2.5. A unified model of the behavior of dust in the lungs has been developed. It describes the deposition of particles on the walls of the airways when cleaning the inhaled air and the subsequent removal of settled dust from the lungs.  The adequacy of the model was verified by the compliance with the results of in vivo testing. The phenomenon of dust deposition in the lungs is described. It is typical for periodic dust exposure in the workplace. Dust exposure is acceptable if the surface area of the deposited dust does not exceed the area of the internal surface of the airways. With this approach, the concentration of dust in inhaled air is recomputed into the surface area of dust particles deposited in the lungs. As the initial data, the results of routine measurements of the mass concentration of particulate matter PM10 and PM2.5 are used. Permissible concentration for PM10 close to the WHO Recommendations and adopted in industrialized countries. Permissible concentration for PM2.5 should be a lot stiffer than currently accepted.  In reality, only the pair PM10 and РМ2,5 gives a quantitative characteristic of the danger of dust exposure. It determines the entering to the area of permissible dust exposure. 


Author(s):  
Yongil Lee ◽  
Young-Chul Lee ◽  
Taesung Kim ◽  
Jin Choi ◽  
Duckshin Park

Hazards related to particulate matter (PM) in subway systems necessitate improvement of the air quality. As a first step toward establishing a management strategy, we assessed the physicochemical characteristics of PM in a subway system in Seoul, South Korea. The mean mass of PM10 and PM2.5 concentrations (n = 13) were 213.7 ± 50.4 and 78.4 ± 8.8 µg/m3, with 86.0% and 85.9% of mass concentration. Chemical analysis using a thermal–optical elemental/organic carbon (EC–OC) analyzer, ion chromatography (IC), and inductively coupled plasma (ICP) spectroscopy indicated that the chemical components in the subway tunnel comprised 86.0% and 85.9% mass concentration of PM10 and PM2.5. Fe was the most abundant element in subway tunnels, accounting for higher proportions of PM, and was detected in PM with diameters >94 nm. Fe was present mostly as iron oxides, which were emitted from the wheel–rail–brake and pantograph–catenary wire interfaces. Copper particles were 96–150 nm in diameter and were likely emitted via catenary wire arc discharges. Furthermore, X-ray diffraction analysis (XRD) showed that the PM in subway tunnels was composed of calcium carbonate (CaCO3), quartz (SiO2), and iron oxides (hematite (α-Fe2O3) and maghemite-C (γ-Fe2O3)). Transmission electron microscopy images revealed that the PM in subway tunnels existed as agglomerates of iron oxide particle clusters a few nanometers in diameter, which were presumably generated at the aforementioned interfaces and subsequently attached onto other PM, enabling the growth of aggregates. Our results can help inform the management of PM sources from subway operation.


2005 ◽  
pp. 29
Author(s):  
M. D. Tasi? ◽  
S. F. Rajši? ◽  
V. T. Novakovi? ◽  
Z. R. Miji? ◽  
M. N. Tomaševi?

2018 ◽  
Vol 878 ◽  
pp. 263-268
Author(s):  
G.V. Seimova ◽  
I.V. Stefanenko ◽  
M.S. Kalashnikova

Air pollution is one of the most significant problem and threats to human health worldwide. The most common pollutant is particulate matter (PM). For characteristics of the PM and their health effects, commonly used indicator is the mass concentration of particles with diameters less than 10 microns (PM10) and small dispersed suspended particles with diameter less than 2.5 microns (PM2.5), as such small particles are able to penetrate deep into the respiratory tract of the human body. The concentration of particles PM10 and PM2.5 in the air is subjected of rationing. This problem has been explored in many countries with the aim of possible reducing concentrations of PM10 and PM2.5 in the air.


Atmosphere ◽  
2021 ◽  
Vol 13 (1) ◽  
pp. 21
Author(s):  
Ioana Elisabeta Popovici ◽  
Zhaoze Deng ◽  
Philippe Goloub ◽  
Xiangao Xia ◽  
Hongbin Chen ◽  
...  

We present the mapping at fine spatial scale of aerosol optical properties using a mobile laboratory equipped with LIDAR (Light Detection And Ranging), sun photometer and in situ instruments for performing on-road measurements. The mobile campaign was conducted from 9 May to 19 May 2017 and had the main objective of mapping the distribution of pollutants in the Beijing and North China Plain (NCP) region. The highest AOD (Aerosol Optical Depth) at 440 nm of 1.34 and 1.9 were recorded during two heavy pollution episodes on 18 May and 19 May 2017, respectively. The lowest Planetary Boundary Layer (PBL) heights (0.5–1.5 km) were recorded during the heavy pollution events, correlating with the highest AOD and southern winds. The transport of desert dust from the Gobi Desert was captured during the mobile measurements, impacting Beijing during 9–13 May 2017. Exploring the NCP outside Beijing provided datasets for regions with scarce ground measurements and allowed the mapping of high aerosol concentrations when passing polluted cities in the NCP (Baoding, Tianjin and Tangshan) and along the Binhai New Area. For the first time, we provide mass concentration profiles from the synergy of LIDAR, sun photometer and in situ measurements. The case study along the Binhai New Area revealed mean extinction coefficients of 0.14 ± 0.10 km−1 at 532 nm and a mass concentration of 80 ± 62 μg/m3 in the PBL (<2 km). The highest extinction (0.56 km−1) and mass concentrations (404 μg/m3) were found in the industrial Binhai New Area. The PM10 and PM2.5 fractions of the total mass concentration profiles were separated using the columnar size distribution, derived from the sun photometer measurements. This study offers unique mobile datasets of the aerosol optical properties in the NCP for future applications, such as satellite validation and air quality studies.


2017 ◽  
Vol 2017 (67) ◽  
pp. 31-37
Author(s):  
O. Turos ◽  
◽  
T. Maremukha ◽  
I. Kobzarenko ◽  
A. Petrosian ◽  
...  

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