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Inhalation of ultrafine carbon particles triggers biphasic pro-inflammatory response in the mouse lung

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High levels of particulate matter in ambient air are associated with increased respiratory and cardiovascular health problems. It has been hypothesised that it is the ultrafine particle fraction (diameter <100 nm) that is largely responsible for these effects. To evaluate the associated mechanisms on a molecular level, the current authors applied an expression profiling approach. Healthy mice were exposed to either ultrafine carbon particles (UFCPs; mass concentration 380 microg x m(-3)) or filtered air for 4 and 24 h. Histology of the lungs did not indicate any pathomorphological changes after inhalation. Examination of the bronchoalveolar lavage fluid revealed a small increase in polymorphonuclear cell number (ranging 0.6-1%) after UFCP inhalation, compared with clean air controls, suggesting a minor inflammatory response. However, DNA microarray profile analysis revealed a clearly biphasic response to particle exposure. After 4 h of inhalation, mainly heat shock proteins were induced, whereas after 24 h, different immunomodulatory proteins (osteopontin, galectin-3 and lipocalin-2) were upregulated in alveolar macrophages and septal cells. In conclusion, these data indicate that inhalation of ultrafine carbon particles triggers a biphasic pro-inflammatory process in the lung, involving the activation of macrophages and the upregulation of immunomodulatory proteins.
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Inhalation of ultrafine carbon particles
triggers biphasic pro-inflammatory
response in the mouse lung
E. Andre
´*
,#,+
, T. Stoeger
",+
, S. Takenaka
"
, M. Bahnweg*, B. Ritter
"
, E. Karg
"
,
B. Lentner
"
, C. Reinhard
"
, H. Schulz
"
and M. Wjst
#
ABSTRACT: High levels of particulate matter in ambient air are associated with increased
respiratory and cardiovascular health problems. It has been hypothesised that it is the ultrafine
particle fraction (diameter ,100 nm) that is largely responsible for these effects. To evaluate the
associated mechanisms on a molecular level, the current authors applied an expression profiling
approach.
Healthy mice were exposed to either ultrafine carbon particles (UFCPs; mass concentration 380
mg?m
-3
) or filtered air for 4 and 24 h. Histology of the lungs did not indicate any
pathomorphological changes after inhalation.
Examination of the bronchoalveolar lavage fluid revealed a small increase in polymorpho-
nuclear cell number (ranging 0.6–1%) after UFCP inhalation, compared with clean air controls,
suggesting a minor inflammatory response. However, DNA microarray profile analysis revealed a
clearly biphasic response to particle exposure. After 4 h of inhalation, mainly heat shock proteins
were induced, whereas after 24 h, different immunomodulatory proteins (osteopontin, galectin-3
and lipocalin-2) were upregulated in alveolar macrophages and septal cells.
In conclusion, these data indicate that inhalation of ultrafine carbon particles triggers a biphasic
pro-inflammatory process in the lung, involving the activation of macrophages and the
upregulation of immunomodulatory proteins.
KEYWORDS: Air pollution, alveolar macrophages, cytokines, expression profiling
Epidemiological studies have shown that
increased levels of particulate matter (PM)
in ambient air are associated with aggra-
vation of respiratory diseases and cardiovascular
complications. A strong association has been seen
for respiratory and cardiac deaths, particularly
among elderly people [1–3]. Oxidative stress,
induced by inhaled particles, successively lead-
ing to activation of pro-inflammatory gene
transcription, is one mechanism thought to cause
the adverse health effects of ambient PM. In
particular, alveolar macrophages may be acti-
vated by particles and release cytokines and
reactive oxygen species [4].
Different hypotheses were developed to explain
which particle properties drive the adverse
health effects. These hypotheses deal with the
particle’s charge, its content of transition metals,
and its size and specific surface area. According
to the ‘‘ultrafine hypothesis of particle toxicity’’,
ambient ultrafine particles (UFP), i.e. particles
with a diameter ,100 nm, are the proportion of
particulate air pollution that mainly causes the
adverse health effects [5]. Animal studies indicate
that at high exposure levels ultrafine carbon
particles (UFCPs) and titanium dioxide particles
have a greater toxic potential than fine particles
with a diameter ranging between 0.1–1.0 mm [6,
7]. UFP induce pulmonary inflammation at a
lower mass concentration than larger particles
[8]. Although UFP comprise only 1–8% of the
mass, they present up to 99% of the number of
ambient PM [9]. Due to their small size, UFP are
known to enter the alveolar–capillary barrier [10,
11], translocate from the lung into the blood [12],
and thus have the capability to directly interact
with extrapulmonary organs.
So far, the molecular and cellular events induced
by inhalation of UFP are poorly understood. The
objective of the current study was to identify
genes regulated by the exposure to UFP in order
to elucidate pathways that are activated by these
particles and whose activation possibly leads to
adverse health effects.
AFFILIATIONS
*Ludwig-Maximilians-University,
Institute for Epidemiology,
#
GSF-National Research Center for
Environment and Health, Institute for
Epidemiology, and
"
GSF-National Research Center for
Environment and Health, Institute for
Inhalation Biology, Neuherberg,
Germany.
+
Both authors contributed equally to
this study.
CORRESPONDENCE
T. Stoeger
GSF-National Research Center for
Environment and Health
Institute for Inhalation Biology
Ingolstaedter Landstrasse 1
D-85758 Neuherberg/Munich
Germany
Fax: 49 8931872400
E-mail: tobias.stoeger@gsf.de
Received:
June 16 2005
Accepted after revision:
April 20 2006
SUPPORT STATEMENT
The present study was funded by
grant 01GS0122 from the German
National Genome Network (NGFN),
Bonn, Germany.
European Respiratory Journal
Print ISSN 0903-1936
Online ISSN 1399-3003
EUROPEAN RESPIRATORY JOURNAL VOLUME 28 NUMBER 2 275
Eur Respir J 2006; 28: 275–285
DOI: 10.1183/09031936.06.00071205
CopyrightßERS Journals Ltd 2006
c
Young, healthy BALB/cJ mice that were exposed to UFCPs
were used as a model. The present authors performed DNA
microarray analysis of whole-lung RNA from mice that were
exposed to high levels of UFP for different periods of time.
Among the affected genes, concerted upregulation of genes
encoding for molecules involved in oxidative stress and
macrophage activation were found. The current results are
the first to demonstrate that inhalation of UFCPs leads to
macrophage activation and triggers pro-inflammatory pro-
cesses in healthy mice. Furthermore, the current authors
identified the regulation of soluble immunomodulatory pro-
teins that might serve as a useful marker for inflammatory
processes induced by particle inhalation in further studies.
MATERIALS AND METHODS
Animals
Female BALB/cJ mice, established at The Jackson Laboratory
(Bar Harbor, ME, USA), were shipped to the GSF-National
Research Center for Environment and Health (Neuherberg,
Germany) at 8 weeks of age. The animals were kept at the GSF
in ‘‘isolated ventilated cages’’ (IVC-Racks; BioZone, Ramsgate,
UK) supplied with filtered air in a 12-h light/12-h dark cycle.
Specified pathogen-free status was approved by a health
certificate according to Federation of European Laboratory
Animals Science Association guidelines. Food and water were
available ad libitum. Animals were aged 10–12 weeks when
studied. Eight animals per experimental group were analysed.
Experimental protocols were in accordance with the German
Law on Animal Protection and approved by the Bavarian
Animal Research Authority (approval no. 211-2531-108/99).
Particle generation and whole-body exposure chamber
The set-up of the whole-body exposure system for rodents has
been described previously by KARG et al. [13]. Briefly, the
exposure chamber was supplied with a constant flow of
humidified air (23uC, 46% relative humidity) and loaded with
UFCPs. UFCPs were produced by an improved electric spark
generator (Model GFG 1000; Palas, Karlsruhe, Germany)
operated with ultrapure graphite electrodes in an argon atmos-
phere (,10
-6
impurities) [14]. UFCPs produced by this method
consist of o96% elemental carbon [15]. Particle number
concentration (CPC 3022A; TSI, St. Paul, MN, USA) and size
distribution (EMS 150; Hauke, Gmunden, Austria) were
continuously monitoredat the entrance of the exposure chamber.
Particle number concentration was 8610
6
cm
-3
with a count
median diameter of 49 nm. Mass concentration was measured
gravimetrically by filter sampling. The average UFCP mass
concentration in the exposure chamber was 380 mg?m
-3
.
Experimental groups
Groups of eight mice were exposed to UFCPs or clean air for 4
or 24 h, respectively. After particle or clean air exposure,
bronchoalveolar lavage (BAL) was performed on eight mice
per condition, and blood was taken from the same animals.
Lungs were taken for RNA preparation from an additional
eight animals per experimental condition. Eight further mice
were sacrificed either after exposure to UFCPs or clean air for
24 h and different organs were taken for histological
examinations.
BAL
After exposure, mice were anaesthetised by i.p. injection of a
mixture of xylazine and ketamine, and killed by exsanguina-
tion. BAL was performed by cannulating the trachea and
infusing the lungs 10 times with 1.0 mL of PBS without Ca
2+
and Mg
2+
. The BAL fluid (BALF) from lavage one and two, as
well as those from three to 10 were pooled and centrifuged
(4256gfor 20 min at room temperature). The cell-free super-
natant from lavage one and two was used for the biochemical
measurements. For each animal, the 10 cell pellets were unified
and resuspended in 1 mL of RPMI 1640 Medium (BioChrome,
Berlin, Germany) supplemented with 10% foetal calf serum
(Seromed, Berlin, Germany), and the number of living cells
was determined by the trypan blue exclusion method. The cell
differentials were performed on cytocentrifuge preparations
(May–Gru
¨nwald–Giemsa staining, 26200 cells counted).
Polymorphonuclear leukocytes were used as inflammatory
markers.
Biochemical analyses
Lactate dehydrogenase (LDH) activity was assayed spectro-
photometrically by monitoring the reduction of oxidised
nicotinamide adenine dinucleotide at 366 nm in the presence
of lactate. Total proteins were determined spectrophotomet-
rically at 620 nm applying the BioRad Protein Assay Dye
Reagent (Nr.500-0006; BioRad, Munich, Germany).
RNA purification
Frozen lungs were thawed in lysis buffer (supplied with RNA
isolation kit) and homogenised with a FastPrep FP120 cell
disrupter (BIO101/Savant; Qbiogene, Heidelberg, Germany)
for 40 s. The RNA was isolated by using the RNeasy kit
(Qiagen, Hilden, Germany). A DNase I treatment was
routinely performed. For each experimental condition, RNA
from the lungs of eight animals was prepared.
Microarray analysis
The GeneChip hybridisations were carried out by a service
provider (RZPD; Deutsches Ressourcenzentrum fu
¨r
Genomforschung GmbH, Berlin, Germany). The RNA was
quantified and equal amounts of RNA from eight lungs per
experimental condition were pooled. For sample preparation,
15 mg of total RNA were used. First-strand synthesis was
carried out by a T7-(dT)24 primer and Superscript II reverse
transcriptase (Invitrogen Life Technologies, Karlsruce,
Germany). Second-strand synthesis was performed according
to the Superscript Choice system. Biotin-labelled cRNA was
generated by an in vitro transcription reaction (BioArray
HighYield RNA Transcript Labeling Kit; Enzo, Farmingdale,
NY, USA). The fragmented cRNA was hybridised to the
murine U74Av2 GeneChip (Affymetrix, High Wycombe, UK)
representing 12,500 sequences (functionally characterised
sequences and expressed sequence tag clusters). The washing
procedure was carried out using the GeneChip Fluidics Station
(Affymetrix) according to the manufacturer’s protocol. The
hybridised cRNA was stained with R-phycoerythrin-strepta-
vidin (Molecular Probes, Karlsruhe, Germany) followed by an
antibody amplification procedure with a biotinylated anti-
streptavidin antibody (Vector Laboratories, Burlingame, CA,
USA). The chips were scanned with a GeneArray Scanner
(Hewlett Packard, Bo
¨blingen, Germany). Data were analysed
ULTRAFINE PARTICLE INHALATION IS PRO-INFLAMMATORY E. ANDRE
´ET AL.
276 VOLUME 28 NUMBER 2 EUROPEAN RESPIRATORY JOURNAL
with the Affymetrix Microarray Suite (MAS 5.0) and Microsoft
Excel software. The expression level of a single mRNA was
determined as the average fluorescence intensity among the
intensities obtained by 16-paired (perfect-matched and single
nucleotide-mismatched) probes consisting of 25-mer oligonu-
cleotides. To identify differentially expressed genes, genes that
were scored absent in the test sample (upregulated genes) or
absent in the control sample (downregulated genes) were
excluded. Genes that were differentially expressed between the
two clean air exposure times (4 and 24 h) were only included if
the comparison of the test sample to both control samples
revealed a two-fold or more change. The given fold changes for
genes with a difference call increase or decrease were used.
RT-PCR and real-time RT-PCR
For RT-PCR and real-time RT-PCR, 1 mg of total RNA was used
for the first-strand cDNA reaction using hexamer primer
(Promega Corporation, Mannheim, Germany) and Superscript
II reverse transcriptase (Invitrogen Life Technologies) at 42uC
for 50 min. PCR was performed on aliquots of this reaction in a
total volume of 25 mL. For real-time PCR, the first-strand cDNA
template, primer mix (as for RT-PCR) and SYBR Green PCR
Master Mix (Applied Biosystems) were used in a total volume
of 20 mL. Primers for ribosomal 18S mRNA were used as a
control for each template in every experiment. The reactions
were repeated with independently isolated RNA samples from
a single animal per experimental condition. Expression of
target genes was normalised to ribosomal 18S mRNA and
displayed as fold-change relative to the sample from the
control animals. The experiments were performed with the
ABI Prism 7000 SDS (Applied Biosystems).
In situ hybridisation
In situ hybridisation was performed with a single-stranded
digoxigenin-labelled RNA probe on paraffin-embedded lung
sections as described elsewhere [16]. For each experimental
condition, two mice were analysed. Sense and antisense probes
specific for osteopontin, galectin-3 and lipocalin-2 were
generated by RT-PCR and in vitro transcription.
Histology and immunohistochemistry
Lungs from exposed and control mice were fixed in buffered
formalin at an inflation pressure of 20 cmH
2
O and embedded
in paraffin. Slides from exposed and control lung tissues were
stained with polyclonal antibodies against galactin-3
(Cedarlane Laboratories Ltd, Hornby, Ontario, Canada),
osteopontin (R&D systems, Wiesbaden, Germany) and
lipocalin-2 (R&D systems). After staining with a biotinylated
secondary antibody (Vector laboratories Inc.) and streptavidin-
Vectastain Elite ABC-peroxidase reagents (Vector Laboratories
Inc.), slides were developed with diaminobenzidine (Vector
Laboratories Inc.). Negative controls tissues were stained
without primary antibody.
Analysis of protein secretion
Per assay, 50 mL of cell-free BALF were applied. Mouse-specific
enzyme-linked immunosorbent assays for osteopontin (Assay
Designs, Ann Arbor MI, USA), keratinocyte-derived chemo-
kine (KC), tumour necrosis factor (TNF)-a, interleukin (IL)-10,
IL-12p40 and IL-1b(R&D Systems) were used according to the
manufacturer’s instructions.
Statistical analyses
Values are reported as mean¡SE. ANOVA was used to
establish the statistical significance between the different
experimental groups. Tukey’s honestly significant difference
procedure was applied to differentiate significant differences
between the groups. Differences were considered significant at
p,0.05.
RESULTS
Characteristics of particles
UFCPs showed a monomodal number distribution with a
median particle size (equivalent mobility diameter) of
48.9¡1.8 nm, mean geometric SD of 1.53, and mean number
concentration of 7.7¡0.8610
6
cm
-3
. The average UFCP mass
concentration in the exposure chamber was measured as 380
mg?m
-3
(fig. 1). According to the particle spectra, 92.3% of the
generated particles were classified as ultrafine and 7.7% as
fine. It was estimated that 85% of the deposited mass in rodent
lungs was from UFPs and 15% from fine particles. This
estimation was carried out using the multiple-path particle
deposition model [17], assuming standard breathing condi-
tions. The particle mass distribution needed for this calculation
was derived from the number distribution reported above and
a particle density varying with size, calculated according to
NAUMANN [18].
BALF cell and protein parameters after inhalation of UFCP
After UFCP or clean air inhalation for 4 and 24 h, mice were
sacrificed and BAL was performed to analyse cellular
distribution and protein levels. The total number (0.45¡
0.05610
6
) of lavaged cells was unchanged after UFCP inhala-
tion (fig. 2a). Noticeably, the fraction of polymorphonuclear
cells (PMN) appeared slightly, but not significantly increased
after particle inhalation for 24 h (fig. 2b). The number of
macrophages in BALF was not increased after UFCP inhalation
(fig. 2c). LDH, a marker for cytotoxicity, was not altered, but
total protein concentration in BALF was significantly increased
after 24 h of particle inhalation (fig. 2d). This, together with the
slightly elevated PMN number, points to a very mild
0.01 0.10
Diameter × µm
0.00
0.25
0.50
0.75
1.00
1.25
1.50
1.75
2.00
Differential number density ×107 cm-3
l
l
l
l
l
l
l
l
l
l
l
l
l
l
l
l
ll
l
lll
l
l
l
l
l
l
l
ll
FIGURE 1. Average number size distribution of 77 samples of generated
ultrafine carbon particles (UFCP) in 24 h. UFCPs show a median particle size of
48.9¡1.8 nm and mean number concentration of 7.7¡0.8610
6
cm
-3
.Ofthe
generated particles, 92.3% are classified as ultra-fine (,0.1 mm).
E. ANDRE
´ET AL. ULTRAFINE PARTICLE INHALATION IS PRO-INFLAMMATORY
c
EUROPEAN RESPIRATORY JOURNAL VOLUME 28 NUMBER 2 277
inflammatory response within the lungs after UFCP inhalation
for 24 h.
Changes in gene expression after inhalation of UFCPs for
4h
According to analysis of the hybridisation signals (MAS5.0
software; Affymetrix), between 45.6% (4-h clean air) and 47.2%
(24-h clean air, 24-h UFCP inhalation) of 12,422 transcripts
represented on the chip were detected (detection: p,0.04;
signal: .30).
Among the genes that were significantly expressed (detection
p-value ,0.04; signal .30) and showed significant changes
(p,0.003) according to the Affymetrix MAS5.0 software, the
current authors identified 157 (1.3%) genes that were upregu-
lated after 4 h of inhalation of UFP and 125 (1%) down-
regulated genes. From these genes, seven were induced two-
fold or more, whereas no gene was more than two-fold
downregulated (table 1). Two genes, granzyme A and a 59–39
exonuclease, were 1.8-fold downregulated.
From the two-fold and more upregulated genes, five were heat
shock proteins (hsp; table 1). The highest induction, four-fold,
was detected for hspa1A (the mouse homologue of hsp70), a
hsp described to interact with apoptosis-inducing factor. The
other upregulated genes with chaperone activity were hsp105
(2.6-fold induction), suppression of tumorigenicity-13 (2.2-
fold induction), stress-induced phosphoprotein-1 (two-fold
induction) and osmotic stress protein 94 (two-fold induction).
A 2.2-fold induction was detected for carcinoembryonic
antigen-related cell adhesion molecule-2.
Furthermore, the mRNA for prolyl-4-hydoxylase alpha (I)-
subunit, a key enzyme in the biosynthesis of collagens was
upregulated two-fold. Another eight genes fulfilled the criteria
for an increase of expression (between 1.5-fold and two-fold
induction). Amongst them WEre hsp47 and hsp40 and two
molecules associated with electron transport, cytochrome b-
561 and PFTAIRE protein kinase-1.
Changes in gene expression after inhalation of UFP for 24 h
After UFP inhalation for 24 h, expression of 236 (1.9%) genes
was increased and 307 (2.5%) genes were decreased compared
with the two clean air controls (detection p-value ,0.04; signal
.30; p,0.003) according to the Affymetrix MAS5.0 software.
From these affected genes, 17 were induced and six repressed
two-fold or more (table 1). Noticeably, all two-fold or more
upregulated genes were related to inflammatory processes. In
particular osteopontin, lipocalin-2 (24p3) and galectin-3 have
been implicated to be important mediators of inflammation
and to play a role as an integrated part of the body’s defence
system [19–21].
The highest increase, a 5.4-fold change, was detected for serum
amyloid A3, a major acute-phase response protein secreted by
activated macrophages. A 3.8-fold induction was detected for
0.00
0.10
0.20
0.30
0.40
0.50
0.60a)
Total cell number ×106
0.0
0.2
0.4
0.8
1.0
1.2
1.4
b)
PMN %
0.6
90
91
93
95
96
98
100c)
Macrophages %
92
94
97
99
0
50
100
150
200
250
d)
Protein µg·mL-1
24 h
4 h
24 h4 h
*
FIGURE 2. Results of ultrafine carbon particle (UFCP) inhalation for 4 and 24 h in a) total cell number, b) polymorphonuclear cells (PMN), c) macrophages, and d)
protein in bronchoalveolar lavage fluid. h: control group; &: UFCP exposed subjects. Data are presented as mean¡SE from eight animals. *: p,0.05.
ULTRAFINE PARTICLE INHALATION IS PRO-INFLAMMATORY E. ANDRE
´ET AL.
278 VOLUME 28 NUMBER 2 EUROPEAN RESPIRATORY JOURNAL
the mRNA of the tumour growth factor-bmember activin B.
Although the expression level was comparatively low, a three-
fold increase was detected for prostaglandin-endoperoxide
synthase 1 (cyclooxygenase-1). The mRNA expression of
leucine-rich a-2-glycoprotein was 2.8-fold increased. Tissue
inhibitor of metalloproteinase (TIMP)-1, another factor
involved in extracellular matrix remodelling, appeared 2.4-
fold upregulated. Expression of two protease inhibitors was
2.4-fold and 2.2-fold increased: serine protease inhibitor-2,
representing the homologue of human a-antichymotrypsin
and the protein kinase-120 precursor, a member of the inter-a-
trypsin inhibitor superfamily. Additionally, the later two genes
that are involved in acute phase response and blood coagula-
tion, the mRNA for coagulation factor III (tissue factor), was
2.2-fold upregulated. Another gene involved in coagulation,
thrombospondin-1, an extracellular matrix protein that is
secreted by different cell types, including endothelial cells,
fibroblasts, smooth muscle cells and type II pneumocytes, was
2.4-fold induced by UFCP exposure. A two-fold induction was
detected for keratin complex-1 gene 19, a specific cytoskeletal
component of simple epithelia, including bronchial epithelial
cells. Another 11 genes were less than two-fold but .1.5-fold
induced (data not shown), amongst them the extracellular
matrix proteins tenascin-C and TIMP-2 and the suppressor of
cytokine signalling-3.
Molecules repressed by UFCP inhalation were cytochrome P1-
450, receptor-type protein tyrosine phosphatase, translation
initiation factor-2C, nuclear factor I/C, ryanodine receptor
RyR1 and E-selectin ligand-1. To validate the results of the
microarray experiments, the current authors performed real-
time RT-PCR on lung RNA from single animals (fig. 3). For all
genes examined, the results obtained were confirmed by
microarray hybridisation. The changes were in the same order
of magnitude as detected by expression profiling.
Inhalation of UFP leads to macrophage activation
Several genes, e.g. cytokines and cell adhesion molecules,
which were found to be upregulated in the present expression
TABLE 1 Changes in gene expression after inhalation of ultrafine particles for 4 h and 24 h
Identifier Name/description Gene symbol 4 h 24 h
Fold induction
M12571 Heat shock protein, 1A Hsp1a 4.0
#
1.2
L40406 Heat shock protein, 105 kDa Hsp105 2.6
#
1.1
AF101164 CEA-related cell adhesion molecule-2 Ceacam2 2.2
#
1.3
AW124318 Suppression of tumorigenicity-13 St13 2.2
#
1.0
U27830 Stress-induced phosphoprotein-1 Stip1 2.0
#
1.2
U16162 Prolyl 4-hydroxylase alpha(I)-subunit P4ha1 2.0
#
1.1
U2392 Osmotic stress protein-94 Osp94 2.0
#
0.9
X03505 Serum amyloid A-3 Saa3 1.1 5.4
#
X69620 Inhibin beta-B Inhbb 2.5
"
3.8
#
X13986 Osteopontin, secreted phosphoprotein Spp1 1.1 3.4
#
M34141 Prostaglandin-endoperoxide synthase-1 Ptgs1 1.0 3.0
#
AW230891 Leucine-rich alpha-2-glycoprotein-1 Lrg1 1.4 2.8
#
V00755 Tissue inhibitor of metalloproteinases-1 Timp1 1.3 2.4
#
M64086 Spi2 proteinase inhibitor (spi2/eb4) Serpina3n 1.1 2.4
#
M62470 Thrombospondin-1 Thbs1 3.0
+
2.4
#
X81627 24p3, lipocalin2 Lcn2 1.0 2.4
#
L41352 Amphiregulin Areg 1.2 2.4
#
AV300608 SH2 domain binding protein-1 Sh2bp1 0.8 2.2
#
M26071 Coagulation factor III F3 1.1 2.2
#
AF023919 PK-120 precursor itih-4 0.9 2.2
#
M15131 Interleukin-1bIL1b0.9 2.0
#
M36120 Keratin complex-1, acidic gene-19 Krt1-19 1.0 2.0
#
M35970 Expressed in nonmetastatic cells-1 Nme1 0.8 2.0
#
X16834 Galectin-3, Mac-2 Lgals3 1.0 2.0
#
Fold repression
K02588 Cytochrome P450,1a1 Cyp1a1 1.2 2.6
#
X58289 Protein tyrosine phosphatase, receptor type B Ptprb 1.6 2.4
#
Y07693 Nuclear factor I/C Nfic 1.2 2.4
#
D38216 RyR1 skeletal muscle ryanodine receptor Ryr1 1.0 2.2
#
X84037 E-selectin ligand-1, golgi apparatus protein-1 Glg1 1.4 2.0
#
AI152867 Eukaryotic translation initiation factor-2C Eif2c2 1.6 2.0
#
#
: genes induced or repressed two-fold or more after 4-h or 24-h ultra-fine carbon particle inhalation;
"
: excluded from analysis because absent in test sample (see
Methods section);
+
: excluded from analysis because fold change between clean air controls (4 h and 24 h) two-fold or more.
E. ANDRE
´ET AL. ULTRAFINE PARTICLE INHALATION IS PRO-INFLAMMATORY
c
EUROPEAN RESPIRATORY JOURNAL VOLUME 28 NUMBER 2 279
study, are known to be involved in inflammatory cell
activation. To analyse their expression and cellular distribution
in the lung, exemplary galectin-3, osteopontin and 24p3 were
chosen for in situ hybridisation experiments. Lungs of mice
exposed for 24 h to either UFCP or clean air were compared.
In lungs from clean air control animals, galectin-3 expression
was hard to detect by in situ hybridisation. Only a few single
alveolar epithelial cells were weakly labelled (fig. 4). After
inhalation of UFCP for 24 h, a positive staining of alveolar
macrophages and alveolar epithelial cells was clearly recogni-
sable. No signal was detected after hybridisation with the
galectin-3 sense probe.
In situ hybridisation experiments with an osteopontin-specific
antisense probe on mouse lung revealed positive staining of
alveolar macrophages after 24-h inhalation of UFCP (fig. 4). In
lungs from clean air control mice, after hybridisation with the
sense probe, no staining was detected (fig. 4).
Lipocalin-2 (24p3) expression was detected in alveolar wall
epithelial cells from lungs after 24-h UFCP inhalation (fig. 4).
No staining was seen in lung sections from clean air controls
and after hybridisation with the sense probe.
These results were confirmed by immunohistochemistry. In
alveolar macrophages of control animals, a slight staining was
detected by anti-osteopontin and anti-galectin-3 antibodies.
This signal increased after UFCP particle inhalation (24 h).
Both antibodies revealed a staining in bronchiolar cells.
However, this signal did not increase after UFCP inhalation.
Lipocalin-2 protein expression was detected in lung septal cells
of control animals. This signal was increased after particle
inhalation (fig. 4).
Secretion of osteopontin into BALF after inhalation of
UFCPs
Osteopontin is a secreted protein, which is found in extra-
cellular fluid and serum. To determine whether newly
expressed osteopontin protein is enriched in BALF, an
osteopontin-specific immunoassay with BALF samples from
UFCP- and clean air-exposed mice was performed (fig. 5).
BALF samples from eight animals of each experimental group
were pooled. In clean air control, 18 ng?mL
-1
osteopontin
protein was detected. After UFCP inhalation for 24 h,
osteopontin protein concentration increased to 35 ng?mL
-1
.In
concordance with the current authors’ chip and in situ mRNA
expression data, osteopontin protein is about two-fold
enriched in BALF from animals after 24-h UFCP inhalation.
No increase could be observed after UFCP inhalation for 4 h.
For further characterisation of the inflammatory response to
UFCP exposition, the secretion of cytokines and chemokines,
known as inflammatory markers, into BALF was examined.
KC, the mouse homologue of IL-8, can be detected in BALF by
ELISA. KC protein levels in BALF from control animals and
after 4-h particle inhalation did not differ. After particle
inhalation for 24 h, KC concentration increased significantly
from 9.0¡0.5 to 14.4¡0.8 pg?mL
-1
(fig. 5). TNF-acould not be
detected in BALF. IL-1bshowed a mild but not significant
increase from 1.2¡0.2 to 1.5¡0.2 pg?mL
-1
after 24-h UFCP
inhalation. IL-10 protein levels decreased from 0.7¡0.2 to
0.4¡0.2 pg?mL
-1
, again not statistically significant, while IL-
12p40 increased from 4.1¡0.4 to 5.2¡0.3 pg?mL
-1
.
DISCUSSION
UFP have been identified in epidemiological studies as an
important factor inducing adverse health effects, such as
cardiovascular complications and aggravation of respiratory
diseases [1–3]. In animal experiments, intratracheal instillation
of UFP beyond a certain mass and surface area dose has been
shown to cause acute pulmonary inflammation [22, 23].
Exposures of healthy and asthmatic subjects to 25 mg?m
-3
UFCP did not cause any detectable changes in airway
inflammation [15]; however, they caused alterations in the
expression pattern of adhesion molecules on blood cells,
indicating increased retention of leukocytes in the pulmonary
vascular bed [24]. The present study provides evidence that
inhalation of elemental carbon particles at doses .40-fold
above environmental relevant doses induces mild pro-inflam-
matory processes within 24 h of exposure. Beyond this, a
comprehensive expression profiling approach gives an insight
into early pathways leading to these processes.
Oxidative stress, caused by ambient particles deposited in the
lung, is believed to be the main factor driving inflammatory
and noxious effects [25]. Even though the mechanism of the
generation of oxidative stress is not understood, it appears to
be related to the surface properties and the large particle
surface area of UFP. Thus, cell–particle interactions in the lung
might lead to the activation of pro-inflammatory gene
transcription via the induction of nuclear import of redox-
sensitive transcription factors, such as nuclear factor (NF)-kb
and activator protein-1. Several studies suggest that the
particle-bound nonelemental carbon impurities account for
the surface reactivity of UFP. LIet al. [26] and XIA et al. [27]
observed a direct correlation between oxidative stress and the
organic carbon content of UFP, in particular the polycyclic
aromatic hydrocarbons and quinones. DICK et al. [28] showed
that the property of UFP to cause oxidant damage is related to
their ability to generate surface free radicals. In this process,
transition metals may be involved via Fenton chemistry [29].
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
4.0
Lipocalin-2 Osteopontin Galectin-3
Fold induction
FIGURE 3. Validation of differential gene expression induced by inhalation of
ultrafine carbon particles (UFCPs) by real-time RT-PCR. BALB/cJ mice were
exposed to UFCP for 4 h (h) and 24 h (&). RNA preparation and RT-PCR were
carried out as described in the Materials and Methods section. Data are presented
as the mean of eight samples per experimental group.
ULTRAFINE PARTICLE INHALATION IS PRO-INFLAMMATORY E. ANDRE
´ET AL.
280 VOLUME 28 NUMBER 2 EUROPEAN RESPIRATORY JOURNAL
To mimic ambient conditions, the use of ambient UFP should
be the most realistic exposure. However, apart from problems
of nonreproducibility due to varying compositional changes in
ambient particle samples and the bias arising from sampling
artefacts, the aerosolisation of collected particles at the
ultrafine range is, at present, very problematic. Like
a) b) c)
d) e) f)
g) h) i)
j) k) l)
AM
AS
AM
AS
AS
AS
AM
SC
SC
AM
AS
AM
AM
AS
AS
SC
SC
FIGURE 4. Osteopontin (a, d, g and j), galectin-3 (b, e, h and k) and lipocalin-2 (c, f, i and l) were upregulated after inhalation of ultrafine carbon particles (UFCPs).
Paraffin-embedded lung sections of control animals (a–c) and animals after 24-h UFCP inhalation (d–l) were hybridised to Dig-labelled antisense probes (a–i) or antibodies (j–
l). In situ hybridisation with an osteopontin antisense probe revealed almost no staining in control sections; however, after inhalation, alveolar macrophages (AM) showed a
positive signal (d and g). This result was confirmed by immunohistochemistry with a polyclonal osteopontin antibody (j). According to in situ hybridisation (e and h) and
immunohistochemistry (k), galectin-3 is upregulated after UFCP particle inhalation in AM. Lipocalin-2 expression was not detected in control animals by in situ hybridisation
(c). After particle inhalation, a signal was detected by in situ hybridisation (f and i) and immunohistochemistry (l) in lung septal cells (SC). AS: alveolar space. Scale bar550 mm
(a–f), 25 mm (g–i) and 10 mm (j–l).
E. ANDRE
´ET AL. ULTRAFINE PARTICLE INHALATION IS PRO-INFLAMMATORY
c
EUROPEAN RESPIRATORY JOURNAL VOLUME 28 NUMBER 2 281
combustion-derived UFPs, which represent the major compon-
ent of urban UFPs, the PALAS-generated soot particles (UFCP)
that were used in the present study represent carbonaceous
nanoparticles. Although urban particles contain trace amounts
of organic compounds and metals, the current study focused
on the effects of pure carbon particles.
The essential advantage of laboratory-made UFCPs is the
possibility to produce defined spectra of particle sizes with
similar surface and organic content properties. Thus, UFCPs
are produced with organic mass contributions ,5% [14, 15].
PALAS soot particles are known to have similar physical
properties like freshly generated diesel soot, e.g. an electron
spin resonance-signal characteristic for organic carbon-centred
radicals [30, 31]. This feature might be important for hydroxyl
generation and downstream effects on cellular oxidative stress
[32]. Recently, BECK-SPEIER et al. [31] demonstrated the high
oxidative potential of UFCP in a cell-free system, as well as the
production of the oxidative stress marker 8-isoprostane in
exposed alveolar macrophages.
In the present study, a UFP concentration of 380 mg?m
-3
was
used. This is 10–100-fold higher than ambient levels measured
in polluted urban areas [8]. This mass concentration is in the
range (170–1660 mg?m
-3
) applied in other toxicological studies
identifying only mild inflammatory responses to UFP exposure
[33, 34]. The pro-inflammatory effects described in the current
study could also be detected less pronounced at a lower
particle burden of 180 mg?m
-3
,e.g. the release of osteopontin in
BALF increased 1.5-fold after 24-h inhalation of 180 mg?m
-3
UFCPs. Although this mass concentration is still high in
comparison to ambient UFP measured at urban sites, e.g. in
Munich (Luise-Kiesselbach-Platz, autumn 1998, 8 mg?m
-3
;E.
Karg, GSF-National Research Center for Environment and
Health, Neuherberg, Germany, personal communication), it
should be notified that the particle effects described were
already detectable after acute exposures and have been found
in young and healthy animals. Aged and compromised
animals are expected to have a stronger response to particle
exposure. According to this, ELDER et al. [35] exposed different
groups of healthy and compromised mice to 110 mg?m
-3
UFCP
for 6 h and found significant lung inflammatory response only
in aged, emphysematous animals, but not in healthy mice.
In the present study, overall histology of the lung did not give
any indication for inflammation or pathological changes.
Examination of BALF showed a small increase in PMN cell
number after UFCP inhalation (4.0¡1.2610
3
) compared with
clean air controls (2.6¡0.5610
3
), suggesting a very mild
inflammatory cellular response (fig. 2). This was reinforced
by a moderate but significant increase in BALF protein
concentration after 24 h of UFCP inhalation. These results fit
into a recently published study by FRAMPTON et al. [15] where
healthy and mildly asthmatic volunteers exposed for 2 h to
UFCP (10 mg?m
-3
and 25 mg?m
-3
) did not reveal any significant
effects on pulmonary functions or markers for airway
inflammation.
However, DNA microarray profile analysis already revealed a
remarkable upregulation of mRNA expression after 4 h of UFP
inhalation. Five out of seven significantly induced genes
encode hsp and proteins with chaperone activity. This
induction is transient and no longer detected after UFCP
inhalation for 24 h. Based on their ability to chaperone
antigenic peptides, hsp can elicit specific cellular adaptive
immune responses [36]. These immunmodulatory properties
of hsp are likely to be responsible for the initiation of the
immune response after particle inhalation. The current results
support this hypothesis, as they revealed the subsequent
induction (after 24-h UFP inhalation) of several genes known
to be regulated via the NF-kB signalling pathway. Amongst
them are galectin-3 and lipocalin-2 (24p3), whereas osteopon-
tin has recently been shown to activate NF-kBvia induction of
induced-kB phosphorylation and degradation through inhibi-
tor of NF-kb kinase. Additionally, the current authors noted
transiently increased transcript levels of the alpha (I)-subunit
of prolyl-4-hydoxylase after 4 h of particle inhalation. Prolyl-4-
hydoxylase is a key enzyme in the biosynthesis of collagens.
Collagen synthesis is increased during connective tissue
remodelling that occurs in allergic asthma. In accordance to
the induction of hsp70 by UFCP exposure that is reported in
the present findings, it was recently shown that exposure of
human alveolar epithelial cells to ultrafine carbon black
particles induced hsp70 as a result of oxidative stress [37].
0
5000
10000
15000
20000
25000
30000
35000
40000
a)
OPN pg·mL-1
0
2
4
6
8
12
14
16
18
b)
KC pg·mL-1
10
Control 4 h 24 h
*
FIGURE 5. a) Osteopontin (OPN) and b) keratinocyte-derived chemokine (KC)
concentration in bronchoalveolar lavage fluid (BALF) after particle inhalation.
Osteopontin levels in BALF pools (eight animals per experimental group) and KC
levels in unpooled BALF samples were measured by ELISA. Inhalation of ultrafine
carbon particles (UFCPs) increases osteopontin concentration from 18 ng?mL
-1
(control) to 35 ng?mL
-1
(24-h UFCP). An increase in KC concentration from
9pg?mL
-1
to 15 pg?mL
-1
was measured after 24-h particle inhalation. Data are
presented as the mean¡SE of eight separate experiments. *: p,0.05.
ULTRAFINE PARTICLE INHALATION IS PRO-INFLAMMATORY E. ANDRE
´ET AL.
282 VOLUME 28 NUMBER 2 EUROPEAN RESPIRATORY JOURNAL
The highest induction after UFCP exposure for 24 h was
detected for serum amyloid A (SAA)-3, the predominant SAA
isoform expressed extrahepatically. SAA3 is known to be
secreted by macrophages after lipopolysaccharide (LPS) treat-
ment. The upregulation of SAA3 after particle inhalation
indicates an inflammatory response, although the increase is
not as high as after LPS induction.
According to the current results, osteopontin seems to play a
central role in the induction of pro-inflammatory processes by
UFP inhalation. Osteopontin is a secreted and glycosylated
phosphoprotein that contains the arginine-glycine-aspartic
acid (RGD) integrin-binding domain. Osteopontin protein
has chemokine/cytokine-like properties and is among the
most abundantly expressed proteins in a wide range of lung
diseases, such as fibrosis, sarcoidosis and lung carcinoma [19,
38]. In the present study, in situ hybridisation experiments
revealed upregulation of osteopontin expression in alveolar
macrophages and a two-fold increase of secreted osteopontin
protein was detected by ELISA in BALF after UFP inhalation.
In accordance with the current in situ results, immunohisto-
chemistry revealed osteopontin protein expression in alveolar
macrophages.
Recently, it was shown that osteopontin is implicated in
experimental particle-induced lung disease using a titanium
dioxide exposure model in a rat. Under exposure conditions,
which resulted in fibroproliferative lung disease (long-term
exposures at particle concentrations .10 mg?m
-3
), rats had
significant increases in total lung osteopontin mRNA expres-
sion and increased levels of osteopontin protein in BALF prior
to the development of lesions [40]. Osteopontin is secreted by
activated macrophages, leukocytes and activated T-lympho-
cytes, and is present in extracellular fluid at sites of
inflammation, and in the extracellular matrix of mineralised
tissues. In the immune system, osteopontin plays a role in
chemotaxis, leading to the migration of macrophages and
dendritic cells to sites of inflammation. Osteopontin protein
interacts with a variety of cell surface receptors, including the
avb3, avb1, a41b,a8b1 and a9b1 integrins, as well as CD44.
Binding of osteopontin protein to these cell surface receptors
stimulates cell adhesion, migration, and specific signalling
functions. The major integrin-binding site of osteopontin is the
RGD integrin-binding motif, which is required for the
adherence of many cell types. ASHKAR et al. [39] have
demonstrated a differential regulation of macrophage IL-12
and IL-10 expression by osteopontin, which affects type-1
immunity. Interaction between osteopontin protein and
macrophages is mediated through avb3 integrin and CD44.
The phosphorylation-dependent interaction between osteo-
pontin protein and its integrin receptor stimulates IL-12
expression, whereas the phosphorylation-independent inter-
action with CD44 inhibits IL-10 expression by macrophages. In
the present study, IL-10 protein concentration was slightly
diminished in BALF after UFCP inhalation, as was demon-
strated by ELISA. Moreover, IL-12 concentration was raised
slightly but not significantly after particle inhalation.
To support the current hypothesis that UFP inhalation triggers
inflammatory processes,the expression of other known markers
for inflammation in relation to particle inhalation was examined.
A significant increase of KC protein concentration in BALF
was detected, although the mRNA expression was not
upregulated. KC, a CXC chemokine, is released by activated
macrophages and injured epithelial cells and acts as a
chemoattractant for neutrophils. It has also been implicated
in the accelerated release of neutrophils in response to
inflammation. In the lung, the release of matrix-bound KC
by shedding is important for the migration of neutrophils
from the interstitium to the alveolar space [41].
Lipocalin-2 (24p3, neutrophil gelatinase-associated lipocalin
(NGAL)) is upregulated after 24-h UFP inhalation in epithelial
cells of the alveolar wall. Lipocalins are small secreted proteins
that play a role in diverse biological processes through binding
of small hydrophobic molecules, encompassing retinoids, fatty
acids, prostaglandins and odorants [20]. Lipocalin-2 expression
is induced by different stimuli in diverse tissues and cell lines.
It was identified as a LPS-induced protein secreted by mouse
macrophages [42]. Recently, it was demonstrated that
lipocalin-2 was expressed in bronchial goblet cells as well as
in alveolar type II pneumocytes, and that the expression is
increased in bronchial and alveolar cells of inflamed human
lungs [42]. The increase of lipocalin-2 mRNA expression is
induced by IL-1bvia a NF-kB-dependent pathway in the
human type II pneumocyte-derived cell line A549. No
induction of lipocalin-2 transcript was seen in A549 cells after
stimulation with LPS, TNF-aand IL-6. In the mouse lung,
liocalin-2 was detected by in situ hybridisation in septal cells
after particle inhalation (fig. 4). No hybridisation signal was
detected in bronchial cells and in control animals. It remains to
be investigated in further in vitro experiments if the lipocalin-2
expression in alveolar epithelial cells is upregulated directly by
UFPs that are supposed to enter these cells because of their
small size [11, 43], or if the increased expression and secretion
of a cytokine, such as IL-1b, by alveolar macrophages is
necessary for lipocalin-2 upregulation. Even if the function of
lipocalin-2 is not known, increased serum levels of the human
homologue NGAL have been related to the clinical manifesta-
tion of cardiovascular disease [44]. Recently, a putative
function of this lipocalin as a modulator of the inflammatory
response has been suggested. Under normal circumstances,
granulocytes have a short life span and die by apoptosis. In
many chronic inflammatory responses, such as bronchial
asthma or lung fibrosis, delayed apoptosis of granulocytes
leads to their accumulation at sites of inflammation, where
they cause tissue damage via the release of toxic mediators [45].
Interestingly, osteopontin and lipocalin-2 seem to play a role in
the pathogenesis of atherosclerosis [44, 46]. People suffering
from this cardiovascular disease are one of the groups
considered particularly susceptible to the effects of airborne
particles.
Galectin-3 is a b-galactoside-binding lectin, implicated in
inflammatory responses as well as in cell adhesion. The role
of galectin-3 as an adhesion molecule for neutrophil extra-
vasation during streptococcal pneumonia has been recently
demonstrated [47]. Recently, the contribution of galectin-3 to
phagocytosis by macrophages has been shown [48]. Galectins,
in particular galectin-1 and galectin-3, play a role as regulators
of inflammatory processes. It was demonstrated that alveolar
infection with Streptococcus pneumoniae, but not with Escherichia
coli, induces the production and secretion of galectin-3 by
E. ANDRE
´ET AL. ULTRAFINE PARTICLE INHALATION IS PRO-INFLAMMATORY
c
EUROPEAN RESPIRATORY JOURNAL VOLUME 28 NUMBER 2 283
alveolar macrophages [48]. Accumulation of galectin-3 in the
alveolar space of streptococcus-infected lungs correlates with
the onset of neutrophil extravasation. In vitro assays revealed
the ability of galectin-3 to mediate the adhesion of neutrophils
to endothelial cells. These data suggest that galectin-3 is
implicated in b
2
integrin-independent neutrophil extravasation
induced by S. pneumoniae; however, not in b
2
integrin-
dependent pulmonary infection induced by E. coli. Induction
of galectin-3 expression in alveolar macrophages by UFP
inhalation might maintain neutrophil extravasation in a similar
way.
In conclusion, the current data provide evidence that inhala-
tion of ultrafine carbon particles triggers a biphasic pro-
inflammatory process in the lungs of healthy mice. After a
short exposure to ultrafine particles, heat shock proteins are
transiently upregulated and might be responsible for the
subsequent activation of macrophages. The present study
demonstrates that inhalation of ultrafine carbon particles
induces the upregulation of osteopontin and galectin-3
expression in alveolar macrophages. Osteopontin, galectin-3
and lipocalin-2 are secreted proteins and their regulation might
serve as a useful marker for inflammatory processes induced
by particle inhalation in further studies.
ACKNOWLEDGEMENTS
The authors would like to thank G. Ferron and O. Schmid for
help with the application of the rodent deposition model and
critical reading of the manuscript.
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EUROPEAN RESPIRATORY JOURNAL VOLUME 28 NUMBER 2 285
... exposure to TiO 2 nanoparticle for 1 h daily for 11 days induced pulmonary acute phase response but no hepatic acute phase response 5 days after last exposure day. [11] In the lung tissue, global transcriptional profiling showed that the acute phase gene Saa3 was the most differentially regulated gene, [11,37] but Saa3, Saa1, and Saa2 were all highly expressed in lung tissue following pulmonary exposure to TiO 2 and carbon black nanoparticles as well as multiwalled carbon nanotubes. [13,17,38] Pulmonary Saa3 mRNA expression has been shown to correlate with blood levels of SAA3 following pulmonary exposure to carbon nanotubes [39] and pulmonary Saa3 expression was paralleled by increased blood levels of SAA3 following pulmonary exposure to carbon black, diesel exhaust particles, jet engine particles, and nanofibrillated cellulose. ...
... [43] Instead, inhalation of carbon black and diesel exhaust particles induced a pulmonary acute phase response, [17,44] which for carbon was already detected after 24 h at concentrations of 380 µg m −3 . [37] Hepatic acute phase response has been detected 1 day after pulmonary exposure to multiwalled carbon nanotubes, but the acute phase response had diminished on day 3 post-exposure, in contrast to pulmonary Saa3 levels that remained elevated. [45] Saa1 was the most differentially expressed hepatic acute phase response following airway exposure to TiO 2 [46] and carbon nanotubes [39,47,48] and we use Saa1 mRNA levels as a biomarker of the hepatic acute phase response. ...
... SAA is a macrophage and neutrophil chemoattractant [49] and Saa mRNA levels in lung tissue correlates closely with neutrophil cell numbers in bronchoalveolar lavage fluid across particle type, dose level, time point and pulmonary dosing method (inhalation or instillation) in mice. [17,37,44,45,50] Particleinduced pulmonary inflammation in terms of neutrophil influx has been shown to correlate closely with total surface area of the deposited particles. [8,12,51] Similarly, Saa3 mRNA levels (and hence acute phase response) correlate with the total surface area of the deposited nanoparticles and carbon nanotubes. ...
Article
Inhaled nanoparticles constitute a potential health hazard due to their size‐dependent lung deposition and large surface to mass ratio. Exposure to high levels contributes to the risk of developing respiratory and cardiovascular diseases, as well as of lung cancer. Particle‐induced acute phase response may be an important mechanism of action of particle‐induced cardiovascular disease. Here, the authors review new important scientific evidence showing causal relationships between inhalation of particle and nanomaterials, induction of acute phase response, and risk of cardiovascular disease. Particle‐induced acute phase response provides a means for risk assessment of particle‐induced cardiovascular disease and underscores cardiovascular disease as an occupational disease.
... Plausible mechanisms of UfCP-mediated cardiovascular effects have been addressed in many studies. We have previously shown that exposing young and healthy mice to high number concentrations of CNPs induces local acute inflammatory effects in the lung [31]. Furthermore, we could reproduce the epidemiological findings of PM-related cardiovascular risks in an experimental setting by exposing spontaneously hypertensive rats (SHRs) with ambient dust and CNPs [30,32,33]. ...
... BALB/cJ mice were assessed after 4 h and 24 h inhalation exposure, or 4 h after IAI. Time points were selected based on our previous studies showing that in lungs, CNPs induced a two-phase inflammatory response after 4 or 24 h inhalation [31], whereas the extrapulmonary pro-coagulatory impact in the hepatic microvasculature was detected as early as 2 h after CNP IAI application [34,35]. Therefore, we sought to systematically and independently investigate the two potential modes of action by applying (i) similar CNPs, as used in several of our previous studies [44][45][46][47][48] and (ii) equivalent doses of CNP in mice via inhalation or intra-arterial infusion (IAI) and subsequent comparison of the effects in the lung, blood, and secondary target organs such as heart, aorta, and liver. ...
... Taking into account the results from our previous study on platelet accumulation in the hepatic microvasculature [36] using identical inhalation exposure settings (440 μg/m 3 , mass median diameter 72 nm), we suggest that the extrapulmonary pro-thrombogenic effects represent the most sensitive response to CNP inhalation. These prothrombogenic effects may occur even in absence of any detectable pulmonary or systemic inflammation as previously reported [31,35]. The lack of any signs for extrapulmonary inflammation reported by the Khandoga et al., [35] study might be related to the use of C57BL/6 mice, which are less prone to inflammatory reactions than the BALB/c mice used here. ...
Article
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Background The death toll associated with inhaled ambient particulate matter (PM) is attributed mainly to cardio-vascular rather than pulmonary effects. However, it is unclear whether the key event for cardiovascular impairment is particle translocation from lung to circulation (direct effect) or indirect effects due to pulmonary particle-cell interactions. In this work, we addressed this issue by exposing healthy mice via inhalation and intra-arterial infusion (IAI) to carbon nanoparticles (CNP) as surrogate for soot, a major constituent of (ultrafine) urban PM. Methods Equivalent surface area CNP doses in the blood (30mm² per animal) were applied by IAI or inhalation (lung-deposited dose 10,000mm²; accounting for 0.3% of lung-to-blood CNP translocation). Mice were analyzed for changes in hematology and molecular markers of endothelial/epithelial dysfunction, pro-inflammatory reactions, oxidative stress, and coagulation in lungs and extra-pulmonary organs after CNP inhalation (4 h and 24 h) and CNP infusion (4 h). For methodological reasons, we used two different CNP types (spark-discharge and Printex90), with very similar physicochemical properties [≥98 and ≥95% elemental carbon; 10 and 14 nm primary particle diameter; and 800 and 300 m²/g specific surface area] for inhalation and IAI respectively. Results Mild pulmonary inflammatory responses and significant systemic effects were observed following 4 h and 24 h CNP inhalation. Increased retention of activated leukocytes, secondary thrombocytosis, and pro-inflammatory responses in secondary organs were detected following 4 h and 24 h of CNP inhalation only. Interestingly, among the investigated extra-pulmonary tissues (i.e. aorta, heart, and liver); aorta revealed as the most susceptible extra-pulmonary target following inhalation exposure. Bypassing the lungs by IAI however did not induce any extra-pulmonary effects at 4 h as compared to inhalation. Conclusions Our findings indicate that extra-pulmonary effects due to CNP inhalation are dominated by indirect effects (particle-cell interactions in the lung) rather than direct effects (translocated CNPs) within the first hours after exposure. Hence, CNP translocation may not be the key event inducing early cardiovascular impairment following air pollution episodes. The considerable response detected in the aorta after CNP inhalation warrants more emphasis on this tissue in future studies. Electronic supplementary material The online version of this article (doi:10.1186/s12989-017-0200-x) contains supplementary material, which is available to authorized users.
... Lipocalin-2 (LCN2) is a biologically active protein that binds to specific receptors in neutrophils, macrophages, and epithelial cells, showing antimicrobial effects and activating inflammatory factors [6]. Relevant studies found that LCN2 was significantly upregulated in mouse lung epithelium after exposure to inhalation of ultrafine carbon particles and in human lung tissue with severe inflammation, but some alveolar cells in uninflamed lungs showed weak staining of LCN2 [7,8]. Thus, we concluded that LCN2 may participate in regulating the pathological or inflammatory processes of alveolar epithelial cells, but the probable mechanism affecting that process has not been investigated. ...
... In this study, we first established a BLM-induced lung injury in mice to observe the expression of LCN2 in alveolar epithelial cells. The results confirmed that LCN2 expression mainly focused on the alveolar epithelium and inflammatory cells of lung injury mice ( Figure 1D-E), which was consistent with a previous study on LCN2 expression in chronic lung diseases, demonstrating that LCN2 was significantly upregulated in lung tissue after exposure to damage factors, such as ultrafine carbon particles, pathogens and inflammatory cytokines [7,8,18]. Then, we further evaluated and quantified the expression of LCN2 in alveolar epithelial cells, and LCN2 and Prospc double-positive cells were highly expressed in lung tissue after BLM lung injury (Figure 2). ...
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The impaired proliferative capacity of alveolar epithelial cells after injury is often an important factor causing epithelial repair dysfunction, leading to the occurrence of lung diseases such as idiopathic pulmonary fibrosis (IPF). Lipocalin-2 (LCN2) participates in multiple processes regulating the pathological process of alveolar epithelial cells, but the mechanisms involved are still unclear. We used bleomycin (BLM)-treated mouse model to characterize the expression of LCN2 in the lung fibrosis regions and analyzed the location of LCN2 in alveolar epithelial cells. LCN2 was increased in the alveolar epithelium post-BLM injury, and highly expressed LCN2 was mainly concentrated on alveolar type 2 (AT2) cells in BLM-injured lungs. Moreover, human pulmonary alveolar epithelial cells (HPAEpiCs) were transfected with the LCN2 overexpression plasmid vector in vitro, LCN2-overexpressing HPAEpiCs showed impaired cell viability and cell growth. Recombinant human interleukin 17 (IL-17) protein (rhIL-17) at different concentrations was administered to intervene HPAEpiCs and observe cell viability and cell growth state and to analyze the concentration-dependent effect of IL-17. HPAEpiC intervention with rhIL-17 mildly rescued the impaired cell proliferation induced by LCN2 overexpression, and the effect of IL-17 intervention was partially concentration dependent. The target cells regulated by this process were Pro-surfactant protein C (Prospc) positive alveolar epithelial cells. The results revealed the reversed effect of IL-17 on the impaired proliferative capacity of the alveolar epithelium induced by LCN2 overexpression, providing new clues for the treatment of lung injury diseases.
... These granules mediate local tissue injury which suggests serum NGAL correlation to bronchial asthma severity [15].Similarly Kowsalya et al., 2013 reported that NGAL has been considered a marker of inflammatory processes such as obesity and asthma [16]. Andre et al., 2006 reported that NGAL has been shown to be a proinflammatory molecule that may be considered a marker of inflammatory processes such as asthma [17]. On the contrary, some studies suggested a protective effect for NGAL against airway inflammation and hyper-reactivity as it has anti-apoptotic and antimicrobial effects [18][19][20]. ...
... These granules mediate local tissue injury which suggests serum NGAL correlation to bronchial asthma severity [15].Similarly Kowsalya et al., 2013 reported that NGAL has been considered a marker of inflammatory processes such as obesity and asthma [16]. Andre et al., 2006 reported that NGAL has been shown to be a proinflammatory molecule that may be considered a marker of inflammatory processes such as asthma [17]. On the contrary, some studies suggested a protective effect for NGAL against airway inflammation and hyper-reactivity as it has anti-apoptotic and antimicrobial effects [18][19][20]. ...
Article
Full-text available
Neutrophil gelatinase-associated lipocalin (NGAL) is emerging as a potential biomarker in many medical conditions including asthma. The aim of this study was to assess the role of serum NGAL in Egyptian childhood bronchial asthma. The study included 156 patients and 39 apparently healthy control children. Full clinical examination, pulmonary function tests; CBC, CRP, IgE, liver function tests, and renal function tests, and serum NGAL level were performed. The difference between the studied groups was statistically significant regarding IgE, eosinophils and NGAL (P= 0.001 for each). In addition, the difference between the subgroup with severe persistent asthma and the subgroup with mild intermittent asthma was significant (P=0.001). ROC curve analysis showed that at a cutoff value of 0.884 the sensitivity and specificity of differentiating severe bronchial asthma patients from controls was 82 % and 76 %, respectively. In conclusion, NGAL may represent a potential marker of bronchial asthma in children with severe disease.
... 3−5 Inhalation of soot-like carbonaceous nanoparticles (CNPs) is well-known to induce acute inflammatory (E) Quantification of the morphometric changes measuring mean chord length (MCL) using the CAST method verifies significant alveolar responses, both locally in lungs and systemically in the cardiovascular system of exposed people, 6 as well as in toxicological animal studies. 7,8 Due to their fiber-shape and asbestos homology, some specimen of engineered carbon nanotubes (CNTs) can induce persistent inflammation and even chronic lung injury. 9,10 Based on the central role of inflammation, pulmonary nanoparticle exposure was reported to contribute to the development of CLDs, like asthma, lung fibrosis, and even cancer and in particular COPD. ...
Article
Full-text available
Nanoparticles (NPs) released from engineered materials or combustion processes as well as persistent herpesvirus infection are omnipresent and are associated with chronic lung diseases. Previously, we showed that pulmonary exposure of a single dose of soot-like carbonaceous NPs (CNPs) or fiber-shaped double-walled carbon nanotubes (DWCNTs) induced an increase of lytic virus protein expression in mouse lungs latently infected with murine γ-herpesvirus 68 (MHV-68), with a similar pattern to acute infection suggesting virus reactivation. Here we investigate the effects of a more relevant repeated NP exposure on lung disease development as well as herpesvirus reactivation mechanistically and suggest an avenue for therapeutic prevention. In the MHV-68 mouse model, progressive lung inflammation and emphysema-like injury were detected 1 week after repetitive CNP and DWCNT exposure. NPs reactivated the latent herpesvirus mainly in CD11b+ macrophages in the lungs. In vitro, in persistently MHV-68 infected bone marrow-derived macrophages, ERK1/2, JNK, and p38 MAPK were rapidly activated after CNP and DWCNT exposure, followed by viral gene expression and increased viral titer but without generating a pro-inflammatory signature. Pharmacological inhibition of p38 activation abrogated CNP- but not DWCNT-triggered virus reactivation in vitro, and inhibitor pretreatment of latently infected mice attenuated CNP-exposure-induced pulmonary MHV-68 reactivation. Our findings suggest a crucial contribution of particle-exposure-triggered herpesvirus reactivation for nanomaterial exposure or air pollution related lung emphysema development, and pharmacological p38 inhibition might serve as a protective target to alleviate air pollution related chronic lung disease exacerbations. Because of the required precondition of latent infection described here, the use of single hit models might have severe limitations when assessing the respiratory toxicity of nanoparticle exposure.
... The carbonaceous particles in PM 2.5 may act as vehicles for strong acids like H 2 SO 4 and cause damage to alveolar epithelium with inhalation of PM 2.5 , decreasing resistance to infection and pulmonary dysfunction [42]. Additionally, inhalation of high levels of spherical carbonaceous nanoparticles may induce inflammatory response and reactivates latent virus [43,44]. Through the IVW methods, we found PM 2.5 absorbance was a likely risk factor of COVID-19 hospitalisation and severe respiratory symptoms. ...
Article
Background: Several observational studies reported on the association between particulate matter ≤2.5μm (PM2.5) and its absorbance with coronavirus (COVID-19), but none use Mendelian randomisation (MR). To strengthen the knowledge on causality, we examined the association of PM2.5 and its absorbance with COVID-19 risk using MR. Methods: We selected genome-wide association study (GWAS) integration data from the UK Biobank and IEU Open GWAS Project for two-sample MR analysis. We used inverse variance weighted (IVW) and its multiple random effects and fixed effects alternatives to generally predict the association of PM2.5 and its absorbance with COVID-19, and six methods (MR Egger, weighted median, simple mode, weighted mode, maximum-likelihood and MR-PRESSO) as complementary analyses. Results: MR results suggested that PM2.5 absorbance was associated with COVID-19 infection (odds ratio (OR) = 2.64; 95% confidence interval (CI) = 1.32-5.27, P = 0.006), hospitalisation (OR = 3.52; 95% CI = 1.05-11.75, P = 0.041) and severe respiratory symptoms (OR = 28.74; 95% CI = 4.00-206.32, P = 0.001) in IVW methods. We observed no association between PM2.5 and COVID-19. Conclusions: We found a potential causal association of PM2.5 absorbance with COVID-19 infection, hospitalisation, and severe respiratory symptoms using MR analysis. Prevention and control of air pollution could help delay and halt the negative progression of COVID-19.
... TLR2 has furthermore been proposed to be a functional receptor for the acute phase protein serum amyloid A (SAA) [18]. Different isoforms of SAA exists; in both mice and humans, SAA1 and SAA2 are inducible by inflammatory cytokines [19], but whereas Saa3 is considered a pseudogene in humans, it is the most differentially regulated gene in lung tissue of mice exposed to various types of NMs [20][21][22][23]. Acute phase response is an established risk factor for cardiovascular disease in a prospective epidemiological study [24]. ...
Article
Full-text available
Background Pulmonary exposure to high doses of engineered carbonaceous nanomaterials (NMs) is known to trigger inflammation in the lungs paralleled by an acute phase response. Toll-like receptors (TLRs), particularly TLR2 and TLR4, have recently been discussed as potential NM-sensors, initiating inflammation. Using Tlr2 and Tlr4 knock out (KO) mice, we addressed this hypothesis and compared the pattern of inflammation in lung and acute phase response in lung and liver 24 h after intratracheal instillation of three differently shaped carbonaceous NMs, spherical carbon black (CB), multi-walled carbon nanotubes (CNT), graphene oxide (GO) plates and bacterial lipopolysaccharide (LPS) as positive control. Results The LPS control confirmed a distinct TLR4-dependency as well as a pronounced contribution of TLR2 by reducing the levels of pulmonary inflammation to 30 and 60% of levels in wild type (WT) mice. At the doses chosen, all NM caused comparable neutrophil influxes into the lungs of WT mice, and reduced levels were only detected for GO-exposed Tlr2 KO mice (35%) and for CNT-exposed Tlr4 KO mice (65%). LPS-induced gene expression was strongly TLR4-dependent. CB-induced gene expression was unaffected by TLR status. Both GO and MWCNT-induced Saa1 expression was TLR4-dependent. GO-induced expression of Cxcl2 , Cxcl5 , Saa1 and Saa3 were TLR2-dependent. NM-mediated hepatic acute phase response in terms of liver gene expression of Saa1 and Lcn2 was shown to depend on TLR2 for all three NMs. TLR4, in contrast, was only relevant for the acute phase response caused by CNTs, and as expected by LPS. Conclusion TLR2 and TLR4 signaling was not involved in the acute inflammatory response caused by CB exposure, but contributed considerably to that of GO and CNTs, respectively. The strong involvement of TLR2 in the hepatic acute phase response caused by pulmonary exposure to all three NMs deserves further investigations.
... Both in vitro and in vivo studies on health effects of ambient PM have identified the generation of oxidative stress as one of the major mechanisms by which air pollution particles exert adverse biological effects (Li et al. 1999;Li, Xia, and Nel 2008). Animal experiments, exposing healthy mice to high levels of laboratory-generated CNP by inhalation and instillation have shown local acute inflammatory effects in the lungs Andre 2006). Many studies show that nanoparticles by virtue of their small size can easily penetrate into the deeper part of lung (alveolar compartment) by evading airway mucocillary as well as clearance by macrophages. ...
Article
Full-text available
Carbon nanoparticles (CNP) are generated by incomplete combustion of diesel engines. Several epidemiological studies associated higher susceptibility to particulate matter related adverse respiratory outcomes with preexisting conditions like chronic bronchitis (CB). Therefore, we compared the effect of CNP exposure on primary bronchial epithelial cells (PBEC) developed in air-liquid interface (ALI) models of normal versus CB-like-mucosa. PBEC cultured at ALI represented normal mucosa (PBEC-ALI). To develop CB-like-mucosa (PBEC-ALI/CB), 1 ng/ml interleukin-13 was added to the basal media of PBEC-ALI culturing. PBEC-ALI and PBEC-ALI/CB were exposed to sham or to aerosolized CNP using XposeALI® system. Protein levels of CXCL-8 and MMP-9 were measured in the basal media using ELISA. Transcript expression of pro-inflammatory (CXCL8, IL6, TNF, NFKB), oxidative stress (HMOX1, SOD3, GSTA1, GPx), tissue injury/repair (MMP9/TIMP1) and bronchial cell type markers (MUC5AC, CC10) were assessed using qRT-PCR. Increased secretion of CXCL-8 and MMP-9 markers was detected 24 h post-exposure in both PBEC-ALI and PBEC-ALI/CB with more pronounced effect in the later. Pro-inflammatory and tissue injury markers were increased at both 6 h and 24 h post-exposure in PBEC-ALI/CB. Oxidative stress markers exhibited similar responses at 6 h and 24 h post-exposure in PBEC-ALI/CB. The club cell specific marker CC10 was increased by 300 fold in PBEC-ALI/CB and 20 fold in PBEC-ALI following CNP exposure. Our data indicates an earlier and stronger reaction of pro-inflammatory, oxidative stress and tissue injury markers in PBEC-ALI/CB models compared to PBEC-ALI models following CNP exposure. The findings may provide insight into the plausible mechanisms of higher susceptibility among predisposed individuals to nanoparticle exposure.
Article
Background iodiesel is promoted as a sustainable replacement for commercial diesel. Biodiesel fuel and exhaust properties change depending on the base feedstock oil/fat used during creation. The aims of this study were, for the first time, to compare the exhaust exposure health impacts of a wide range of biodiesels made from different feedstocks and relate these effects with the corresponding exhaust characteristics. Method Primary airway epithelial cells were exposed to diluted exhaust from an engine running on conventional diesel and biodiesel made from Soy, Canola, Waste Cooking Oil, Tallow, Palm and Cottonseed. Exhaust properties and cellular viability and mediator release were analysed post exposure. Results The exhaust physico-chemistry of Tallow biodiesel was the most different to diesel as well as the most toxic, with exposure resulting in significantly decreased cellular viability (95.8±6.5%) and increased release of several immune mediators including IL-6 (+223.11±368.83 pg/mL) and IL-8 (+1516.17±2908.79 pg/mL) above Air controls. In contrast Canola biodiesel was the least toxic with exposure only increasing TNF-α (4.91±8.61). Conclusion This study, which investigated the toxic effects for the largest range of biodiesels, shows that exposure to different exhausts results in a spectrum of toxic effects in vitro when combusted under identical conditions.
Article
The pulmonary fibrosis could be caused by long-term inhalation of carbon black (CB) particles. Studies on the mechanisms of pulmonary fibrosis induced by CB are required to develop the stratagem of prevention and treatment on fibrosis. The RNA-binding protein DiGeorge syndrome critical region gene 8 (DGCR8)-dependent pri-miRNAs processing is regulated by N⁶-methyladenosine (m⁶A) modification, which targets the downstream signal pathway. However, its role in pulmonary fibrosis has not been known clearly. In the present study, rats inhaled CB at dose of 0, 5 or 30 mg/m³ for 28 days, 6 h/day, respectively. The rats inhaled CB at dose of 0 or 30 mg/m³ for 14 days, 28 days and 90 days, respectively. In vitro experiments, the normal human bronchial epithelial cell line (16HBE) was treated with CB (0, 50, 100 and 200 μg/mL) for 24 h. In vitro and vivo study, the levels of fibrosis indicators including α-SMA, vimentin, collagen-I and hydroxyproline in CB treatment groups statistically increased in dose- or time- dependent manners compared with the control. After CB treatment, PI3K-AKT-mTOR pathway was activated and regulated by miRNA-126. We found that both of m⁶A modifications of pri-miRNA-126 and its binding with DGCR8 were decreased after CB treatment, which resulted in the reduction of mature miRNA-126 accompanied by accumulation of unprocessed pri-miRNA-126. This work demonstrated that m⁶A modification of pri-miRNA-126 and its binding with DGCR8 decreases blocked miRNA-126 maturation, and then activated the PI3K/AKT/mTOR pathway, which drove the fibro genesis in the lung after CB exposure.
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Ultrafine carbon, metal, and metal oxide particles were generated with a commercially available spark generator designed for the production of carbon particles. Aerosols with number concentrations up to 10 cm were produced at flow rates up to 150 lpm. Lognormal size distributions with modal diameters in the range of 18–150 nm and geometric standard deviations of about 1.5 were obtained. The chemical composition, size, number concentration, morphology, and surface area of the particles were varied, and the generation of particles with fixed characteristics could be maintained over many hours. The particle characteristics, however, could not be varied independently. For a certain chemical composition only size and number concentration were variable; morphology and surface area were fixed regardless of particle size. The particles grow by coagulation of primary particles formed by nucleation. The coagulated particles can either stick together and maintain their identity or fuse together and lose their identity. Each material used for the generation of ultrafine particles is thus associated with a certain morphology and surface area: silver with a low mass-related BET surface area (20 m g), metal oxides and iridium with a low-to-intermediate BET surface area (50 m g for cadmium oxide, 120 m g for iridium, and 300 m g for ferric oxide), and carbon with a large BET surface area (750 m g). Iridium, on the other hand, has a huge volume-related BET surface area (2800 m cm). It was not possible to generate ultrafine carbon particles without contaminations with the generator. However, these contaminations could be decreased in this study from 25% to 6% by replacing organic components of the generator by pure inorganic components.
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We conducted a series of experiments with ultrafine particles (approximately 20 nm) and larger particles (less than 200 nm) of "nuisance" dusts to evaluate the involvement of alveolar macrophages (AM) in particle-induced lung injury and particle translocation in rats. After intratracheal instillation of both ultrafine particles and larger particles of TiO2, we found a highly increased interstitial access of the ultrafine particles combined with a large acute inflammatory reaction as determined by lung lavage parameters. An additional experiment revealed that intratracheal instillation of phagocytized ultrafine TiO2 particles (inside AM) prevented both the pulmonary inflammatory reaction and the interstitial access of the ultrafine particles. Another experiment showed that the influx of polymorphonuclear cells (PMN) into the alveolar space unexpectedly decreased with higher doses of ultrafine particles, whereas alveolar epithelial permeability (protein leakage) increased. The divergence between PMN influx into the alveolar space and changes in alveolar epithelial permeability implies that they are separate events. Pulmonary inflammatory parameters determined by lung lavage analysis correlated best with the surface area of the retained particles rather than with their mass, volume, or numbers. Because higher doses resulted in an increased interstitialized fraction of particles, we suggest that inflammatory events induced by particles in the interstitial space can modify the inflammation in the alveolar space detectable by lung lavage. Our results demonstrate the dual role of AM for modifying particle-induced lung injury, i.e., both preventing such injury and contributing to it. We conclude that the increased pulmonary toxicity of ultrafine particles is related to their larger surface area and to their increased interstitial access.(ABSTRACT TRUNCATED AT 250 WORDS)
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The association between fine and ultrafine particles and respiratory health was studied in adults with a history of asthma in Erfurt, Eastern Germany. Twenty-seven nonsmoking asthmatics recorded their peak expiratory flow (PEF) and respiratory symptoms daily. The size distribution of ambient particles in the range of 0.01 to 2.5 microm was determined with an aerosol spectrometer during the winter season 1991-1992. Most of the particles (73%) were in the ultrafine fraction (smaller than 0.1 microm in diameter), whereas most of the mass (82%) was attributable to particles in the size range of 0.1 to 0.5 microm. Because these two fractions did not have similar time courses (correlation coefficient r = 0.51), a comparison of their health effects was possible. Both fractions were associated with a decrease of PEF and an increase in cough and feeling ill during the day. Health effects of the 5-d mean of the number of ultrafine particles were larger than those of the mass of the fine particles. In addition, the effects of the number of the ultrafine particles on PEF were stronger than those of particulate matter smaller than 10 microm (PM10). Therefore, the present study suggests that the size distribution of ambient particles helps to elucidate the properties of ambient aerosols responsible for health effects.
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An intensive soot aerosol characterisation campaign was organised in October 1999 at the large aerosol chamber facility AIDA in Karlsruhe, with the participation of scientists from nine Austrian, German, Russian, and Swiss Research Centres and Universities who contributed special equipment and expertise. The main goal was a comprehensive physical and chemical characterisation of soot aerosol from a modern turbo Diesel passenger car equipped with an oxidation catalyst, in comparison with artificial soot aerosol (“Palas” soot) from a commercial spark discharge generator which is often used as a surrogate for combustion soot in laboratory studies. Included were experiments with pure ammonium sulphate aerosol as well as its external mixtures with soot aerosols, and their evolution to partially internal mixtures on time scales up to . Effects of organic coatings on various aerosol properties, generated in situ by heterogeneous nucleation of products from the reaction of α-pinene with ozone were also investigated. The purpose of this paper is to present an overview of the whole campaign. This includes the description of technical and modelling tools, standard procedures, and the presentation of experimental parameters in tabular form, as a common background for a series of companion papers which focus on selected scientific issues. Included is a comparison between Diesel and spark generated soot in terms of their Raman and ESR spectra. The most remarkable difference is the large spin density in spark generated soot, which exceeds that of Diesel soot by an order of magnitude. However, the spin densities in both materials are too small to affect the surface properties of soot aerosols to a significant extent.
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The sectional aerosol behavior code COSIMA simulates the time evolution of the structural, dynamical, and optical properties of airborne agglomerate particles as well as their heterogeneous chemical interactions with reactive trace gases utilizing a formalism based on fractal scaling laws. The modeled processes include diffusion to the walls and sedimentational deposition, Brownian and gravitational coagulation, molecular transport from the gas phase to the accessible particle surface, surface adsorption and reactions, gas phase reactions, and dilution effects due to sampling (e.g. during aerosol chamber experiments). The effect of hydrodynamic interactions and shielding on particle mobility is considered within the framework of the Kirkwood–Riseman theory. Rayleigh–Debye–Gans theory is used to deal with light absorption and scattering. The code is validated against new experimental data on the dynamics of Diesel and graphite spark soot as well as recent theoretical and simulation results. Applying the Kirkwood–Riseman formalism to compute the mobility of fractal like agglomerates significantly enhances coagulation rates as well as wall and depositional loss but does not affect the form of the self preserving size distributions attained in the long time regime if Brownian coagulation dominates the aerosol dynamics.
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Background: Air pollution in cities has been linked to increased rates of mortality and morbidity in developed and developing countries. Although these findings have helped lead to a tightening of air-quality standards, their validity with respect to public health has been questioned. Methods: We assessed the effects of five major outdoor-air pollutants on daily mortality rates in 20 of the largest cities and metropolitan areas in the United States from 1987 to 1994. The pollutants were particulate matter that is less than 10 microm in aerodynamic diameter (PM10), ozone, carbon monoxide, sulfur dioxide, and nitrogen dioxide. We used a two-stage analytic approach that pooled data from multiple locations. Results: After taking into account potential confounding by other pollutants, we found consistent evidence that the level of PM10 is associated with the rate of death from all causes and from cardiovascular and respiratory illnesses. The estimated increase in the relative rate of death from all causes was 0.51 percent (95 percent posterior interval, 0.07 to 0.93 percent) for each increase in the PM10 level of 10 microg per cubic meter. The estimated increase in the relative rate of death from cardiovascular and respiratory causes was 0.68 percent (95 percent posterior interval, 0.20 to 1.16 percent) for each increase in the PM10 level of 10 microg per cubic meter. There was weaker evidence that increases in ozone levels increased the relative rates of death during the summer, when ozone levels are highest, but not during the winter. Levels of the other pollutants were not significantly related to the mortality rate. Conclusions: There is consistent evidence that the levels of fine particulate matter in the air are associated with the risk of death from all causes and from cardiovascular and respiratory illnesses. These findings strengthen the rationale for controlling the levels of respirable particles in outdoor air.