Harry M ten Brink

Dr. Harry M ten Brink

orcid

Research Focus & Metrics

Academic Career Length

57Years (1970-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 October 2009 in Atmospheric Environment
Verified
Journal Article
Open access
PMP.S. Monks
P.S. Monks
CGC. Granier
C. Granier
Sandro FuzziSandro Fuzzi
Sandro Fuzzi
ASA. Stohl
A. Stohl
MWM.L. Williams
M.L. Williams
RGR. von Glasow
R. von Glasow
International audienceAir quality transcends all scales with in the atmosphere from the local to the global with handovers and feedbacks at each scale interaction. Air quality has manifold effects on health, ecosystems, heritage and climate. In this review the state of scientific understanding in relation to global and regional air quality is outlined. The review discusses air quality, in terms of emissions, processing and transport of trace gases and aerosols. New insights into the characterization of both natural and anthropogenic emissions are reviewed looking at both natural (e.g. dust and lightning) as well as plant emissions. Trends in anthropogenic emissions both by region and globally are discussed as well as biomass burning emissions. In terms of chemical processing the major air quality elements of ozone, non-methane hydrocarbons, nitrogen oxides and aerosols are covered. A number of topics are presented as a way of integrating the process view into the atmospheric context; these include the atmospheric oxidation efficiency, halogen and HOx chemistry, nighttime chemistry, tropical chemistry, heat waves, megacities, biomass burning and the regional hot spot of the Mediterranean. New findings with respect to the transport of pollutants across the scales are discusse

1 May 2004 in Atmospheric Environment
Verified
Journal Article
Closed access
JPJean-P Putaud
Jean-P Putaud
FRFrank Raes
Frank Raes
RDRita Van Dingenen
Rita Van Dingenen
EBErika Brüggemann
Erika Brüggemann
MFM.-Cristina Facchini
M.-Cristina Facchini
AWAlfred Wiedensohler
Alfred Wiedensohler

1 March 2010 in Atmospheric Environment
Verified
Journal Article
Closed access
JPJ.-P. Putaud
J.-P. Putaud
RDRita Van Dingenen
Rita Van Dingenen
Andrés Alastuey UrósAndrés Alastuey Urós
Andrés Alastuey Urós
HBH. Bauer
H. Bauer
WBW. Birmili
W. Birmili
FRF. Raes
F. Raes

1 December 2004 in Atmospheric Environment
Verified
Journal Article
Closed access
XQXavier Querol
Xavier Querol
Andrés Alastuey UrósAndrés Alastuey Urós
Andrés Alastuey Urós
CRC.R. Ruiz
C.R. Ruiz
Begoña Artíñano Rodríguez De TorresBegoña Artíñano Rodríguez De Torres
Begoña Artíñano Rodríguez De Torres
HHH.C. Hansson
H.C. Hansson
JSJ. Schneider
J. Schneider

1 May 2004 in Atmospheric Environment
Verified
Journal Article
Closed access
RDRita Van Dingenen
Rita Van Dingenen
FRFrank Raes
Frank Raes
JPJean-P Putaud
Jean-P Putaud
UBUrs Baltensperger
Urs Baltensperger
ACAurelie Charron
Aurelie Charron
PWPeter Wåhlin
Peter Wåhlin

15 June 2004 in Atmospheric Chemistry and Physics
Verified
Journal Article
Open access
PDF file
MSM. Schaap
M. Schaap
MLM. van Loon
M. van Loon
HBHarry M ten Brink
Harry M ten Brink
FDF. J. Dentener
F. J. Dentener
PBP. J. H. Builtjes
P. J. H. Builtjes
Nitrate is an important component of (secondary inorganic) fine aerosols in Europe. We present a model simulation for the year 1995 in which we account for the formation of secondary inorganic aerosols including ammonium sulphate and ammonium nitrate, a semi volatile component. For this purpose, the chemistry-transport model LOTOS was extended with a thermodynamic equilibrium module and additional relevant processes to account for secondary aerosol formation and deposition. During winter, fall and especially spring high nitrate levels are projected over north western, central and eastern Europe. During winter nitrate concentrations are highest in Italy, in accordance with observed data. In winter nitric acid, the precursor for aerosol nitrate is formed through heterogeneous reactions on the surface of aerosols. Modelled and observed sulphate concentrations show little seasonal variation. Compared to sulphate levels, appreciable ammonium nitrate concentrations in summer are limited to those areas with high ammonia emissions, e.g. the Netherlands, since high ammonia concentrations are necessary to stabilise this aerosol component at high temperatures. As a consequence of the strong seasonal variation in nitrate levels the AOD depth of nitrate over Europe is especially significant compared to that of sulphate in winter and spring when equal AOD values are calculated over large parts of Europe. Averaged over all stations the model reproduces the measured concentrations for NO3, SO4, NH4, TNO3 (HNO3+NO3), TNH4 (NH3+NH4) and SO2 within 20%. The daily variation is captured well, albeit that the model does not always represent the amplitude of single events. The model underestimates wet deposition which was attributed to the crude representation of cloud processes. Comparison of retrieved and computed aerosol optical depth (AOD) showed that the model underestimates AOD significantly, which was expected due to the lack of carbonaceous aerosols, sea salt and dust in the model. The treatment of ammonia was found to be a major source for uncertainties in the model representation of secondary aerosols. Also, inclusion of sea salt is necessary to properly assess the nitrate and nitric acid levels in marine areas.