Mercury, Platinum, Antimony and Other Trace Elements in the Atmospheric Environment of the Urban Area of Mexico City: Use of Ficus benjamina as Biomonitor

Author(s):  
Ofelia Morton-Bermea ◽  
Elizabeth Hernández-Álvarez ◽  
Sara Laura Ordoñez-Godínez ◽  
Isidro Montes-Ávila
2011 ◽  
Vol 86 (5) ◽  
pp. 495-500 ◽  
Author(s):  
Janin Guzmán-Morales ◽  
Ofelia Morton-Bermea ◽  
Elizabeth Hernández-Álvarez ◽  
María Teresa Rodríguez-Salazar ◽  
María Elena García-Arreola ◽  
...  

2013 ◽  
Vol 31 (3) ◽  
pp. 932-936
Author(s):  
Juan J Pérez-Rivero ◽  
Emilio Rendon-Franco ◽  
Mario Pérez-Martínez ◽  
Alejandro Ávalos-Rodríguez ◽  
Rafael Ávila-Flores

2011 ◽  
Vol 11 (8) ◽  
pp. 3789-3809 ◽  
Author(s):  
G. Li ◽  
M. Zavala ◽  
W. Lei ◽  
A. P. Tsimpidi ◽  
V. A. Karydis ◽  
...  

Abstract. Organic aerosol concentrations are simulated using the WRF-CHEM model in Mexico City during the period from 24 to 29 March in association with the MILAGRO-2006 campaign. Two approaches are employed to predict the variation and spatial distribution of the organic aerosol concentrations: (1) a traditional 2-product secondary organic aerosol (SOA) model with non-volatile primary organic aerosols (POA); (2) a non-traditional SOA model including the volatility basis-set modeling method in which primary organic components are assumed to be semi-volatile and photochemically reactive and are distributed in logarithmically spaced volatility bins. The MCMA (Mexico City Metropolitan Area) 2006 official emission inventory is used in simulations and the POA emissions are modified and distributed by volatility based on dilution experiments for the non-traditional SOA model. The model results are compared to the Aerosol Mass Spectrometry (AMS) observations analyzed using the Positive Matrix Factorization (PMF) technique at an urban background site (T0) and a suburban background site (T1) in Mexico City. The traditional SOA model frequently underestimates the observed POA concentrations during rush hours and overestimates the observations in the rest of the time in the city. The model also substantially underestimates the observed SOA concentrations, particularly during daytime, and only produces 21% and 25% of the observed SOA mass in the suburban and urban area, respectively. The non-traditional SOA model performs well in simulating the POA variation, but still overestimates during daytime in the urban area. The SOA simulations are significantly improved in the non-traditional SOA model compared to the traditional SOA model and the SOA production is increased by more than 100% in the city. However, the underestimation during daytime is still salient in the urban area and the non-traditional model also fails to reproduce the high level of SOA concentrations in the suburban area. In the non-traditional SOA model, the aging process of primary organic components considerably decreases the OH levels in simulations and further impacts the SOA formation. If the aging process in the non-traditional model does not have feedback on the OH in the gas-phase chemistry, the SOA production is enhanced by more than 10% compared to the simulations with the OH feedback during daytime, and the gap between the simulations and observations in the urban area is around 3 μg m−3 or 20% on average during late morning and early afternoon, within the uncertainty from the AMS measurements and PMF analysis. In addition, glyoxal and methylglyoxal can contribute up to approximately 10% of the observed SOA mass in the urban area and 4% in the suburban area. Including the non-OH feedback and the contribution of glyoxal and methylglyoxal, the non-traditional SOA model can explain up to 83% of the observed SOA in the urban area, and the underestimation during late morning and early afternoon is reduced to 0.9 μg m−3 or 6% on average. Considering the uncertainties from measurements, emissions, meteorological conditions, aging of semi-volatile and intermediate volatile organic compounds, and contributions from background transport, the non-traditional SOA model is capable of closing the gap in SOA mass between measurements and models.


2009 ◽  
Vol 74 (11) ◽  
pp. 1319-1333 ◽  
Author(s):  
Jasminka Joksic ◽  
Milena Jovasevic-Stojanovic ◽  
Alena Bartonova ◽  
Mirjana Radenkovic ◽  
Karl-Espen Yttri ◽  
...  

Within this study, attempts were made to characterize the coarse and fine particulate aerosol fractions in urban area of Belgrade and define the inorganic chemical composition of the aerosol fractions. For this purpose, daily deposits of PM10, PM2.5 and PM1 aerosol fractions were collected during spring and autumn sampling periods in 2007 and analyzed for the PM mass concentrations, trace elements and secondary ions. The results obtained in the two campaigns showed average daily mass concentrations of 37 and 44 ?g/m3 for PM10, 22 and 23 ?g/m3 for PM2.5 and 15 and 17 ?g/m3 for the finest particulate matter fraction PM1 with the maximums exceeding the limit values set by the EU air quality regulations. A correlation with the gas-phase ambient air pollutants SO2, NO2 and O3 was found and is discussed. The concentrations of trace elements (Mg, Al, K, V, Cr, Mn, Fe, Co, Ni, Cu, Zn, As, Se, Mo, Cd, Sb, Ba, Tl, Pb and Th) and secondary ions (NO3 -, SO4 2-, NH4 +, K+, Ca2+ and Na+) determined in the PM10, PM2.5 and PM1 aerosol fractions showed levels and distributions indicating soil and traffic-related sources as the main pollution sources. This study was conducted as the first step of PM assessment in order to point out main air pollution sources and suggest a remedy strategy specific for this region.


2013 ◽  
Vol 2013 (1) ◽  
pp. 4675
Author(s):  
Cambal Leah ◽  
Sara Gillooly ◽  
Brett Tunno ◽  
Drew Drew Michanowicz ◽  
Daniel Bain ◽  
...  

2007 ◽  
Vol 85 (1) ◽  
pp. 52-63 ◽  
Author(s):  
P.A. Báez ◽  
M.R. García ◽  
B.M. del C. Torres ◽  
H.G. Padilla ◽  
R.D. Belmont ◽  
...  

Grana ◽  
1992 ◽  
Vol 31 (4) ◽  
pp. 315-319 ◽  
Author(s):  
I. Rosas ◽  
C. Calderón ◽  
B. Escamilla ◽  
M. Ulloa

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