PM
10
metal concentrations and source identification using positive matrix
factorization and wind sectoring in a French industrial zone
Laurent Y. Alleman ⁎, Laure Lamaison
1
, Esperanza Perdrix, Antoine Robache
2
, Jean-Claude Galloo
Université Lille Nord de France, F-59000, Lille, France
Ecole des Mines de Douai, Département Chimie et Environnement, 941 rue Charles Bourseul, BP 10838, 59508 Douai cedex, France
article info abstract
Article history:
Received 24 July 2009
Received in revised form 8 February 2010
Accepted 24 February 2010
The elemental composition data of ambient aerosols collected upon selected wind sectors in
the highly industrialised harbour of Dunkirk (France) were interpreted using pollution roses,
elemental ratios, Enrichment Factors (EF), Principal Component Analysis (PCA) and Positive
Matrix Factorization (PMF) receptor model. The objective was to identify the possible sources
of PM10 aerosols, their respective chemical tracers and to determine their relative contribution
at the sampling site.
PM10 particles samples were collected from June 2003 to March 2005 in order to analyse up
to 35 elements (Ag, Al, As, Ba, Bi, Ca, Cd, Ce, Co, Cr, Cs, Cu, Eu, Fe, K, La, Mg, Mn, Mo, Na, Ni, Pb,
Rb, S, Sb, Sc, Si, Sm, Sr, Th, Ti, U, V, Zn and Zr) using Inductively Coupled Plasma (ICP)-Atomic
Emission Spectrometry (AES) and ICP-Mass Spectrometry (MS). A significant effort has been
made on estimating the total uncertainty of each result by regularly analysing blanks, quality
controls and SRM NIST standards. Based on this procedure, a selected set of 24 "robust"
elements was compared to the 35-element matrix in order to evaluate the sturdiness of our
PMF statistical treatment.
Eight source factors were resolved by PCA for all the wind sectors explaining 90% of the total
data variance. The PMF results confirmed that eight physically interpretable factors contributed
to the ambient particulate pollution at the sampling site: crustal dust (11%), marine aerosols
(12%), petrochemistry activities (9.2%), metallurgical sintering plant (8.6%), metallurgical
coke plant (12.6%), ferromanganese plant (6.6%), road transport (15%) and a less clearly
interpretable profile probably associated to dust resuspension (13%). These weighted
contributions against wind direction frequencies demonstrate that industrial sources are the
most important contributors to this site (37%) followed by the natural sources (detrital and
marine sources) (23%) and the road transport (15%).
© 2010 Elsevier B.V. All rights reserved.
Keywords:
Trace element
PM
10
Positive matrix factorization
Source-receptor model
ICP-MS
1. Introduction
Aerosols originate from a variety of natural (soil dust
erosion, sea salt, volcanism, natural forest fires …) and
anthropogenic (industries, transports, biomass burning,
combustion of fossil fuels …) sources. Atmospheric particles
with an aerodynamic diameter smaller than 10 μm (PM
10
)
have been put under scrutiny in the past, being easily inhaled
and deposited within the respiratory system (Pope et al.,
1995). Studies show that PM
10
play a role in the incidence and
severity of respiratory diseases (Pope and Dockery, 1999;
Brunekreef and Holgate, 2002) and have significant associa-
tions with decline in lung function and cardio-vascular
pathologies. As these particles may be harmful to humans,
their assessment level and chemical composition are signifi-
cant from an environmental health perspective. In addition,
Atmospheric Research 96 (2010) 612–625
⁎ Corresponding author. Ecole des Mines de Douai, Département Chimie et
Environnement, 941 rue Charles Bourseul, BP 10838, 59508 Douai cedex,
France.
E-mail address: alleman@ensm-douai.fr (L.Y. Alleman).
1
Present address: Laboratoire Traces Inorganiques, CARSO-LSEHL, 321,
avenue Jean Jaurès, 69007, Lyon, France.
2
Present address: Direction Régionale de l'Industrie, de la Recherche et de
l'Environnement DRIRE Bourgogne, Dijon, France.
0169-8095/$ – see front matter © 2010 Elsevier B.V. All rights reserved.
doi:10.1016/j.atmosres.2010.02.008
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