Oscar mejlar över en nyuppgrävd studie från Frankrike, en gedigen doktorsavhandling kommen från en av Dr Alain Géloën´s adepter,Yuri Lima de Albuquerque. Ämnet för avhandlingen är då såklart luftföroreningar och dess påverkan på människa.
Which atmospheric nanoparticles trigger healthdiseases?
Abstract
In 2017 around 5 million people had premature deaths due to air pollution. Our
objectives were to identify which atmospheric nanoparticles cause negative effects on
human health, their mechanisms of action and how to prevent them.
Two types of
particles were tested, naphthalene (anthropogenic origin) and particles from biomass
burning (from both anthropogenic and natural origin).
Three different methodologies
were used: real time cell analysis, a measure of cell proliferation and adhesion;
quantitative phase contrast microscope (Holomonitor, PHI), that gives behavioral and
structural parameters of cells (e.g. area, motility and migration) and bright field real
time microscopy (Cytation, Biotek), for real time cell imaging.
Fresh naphthalene
nanoparticles were more toxic than aged. Glutathione at 1 mM partially restored cell
proliferation. Four by-products of naphthalene nanoparticles were tested on lung cell
model A549: 1.4-naphthoquinone (1.4-NQ); 2-hydroxy-1.4-naphthoquinone (2-OHNQ), phthalic acid (PA) and phthaldialdehyde (OPA).
According to their EC50, 1.4-NQ
showed a toxicity 100 times higher than other compounds. 1.4-NQ and OPA decreased
the optical volume, migration, motility and motility speed of cells. 1.4-NQ increased the
oxidative stress (DHR staining). Addition of glutathione protected the cells against 1,4-
NQ.
The toxicity of particles from different mode of burning wood (flaming (FWS),
smoldering (SWS) and pyrolysis (PWS)) were similarly toxic on A549 cell proliferation.
In conclusion, toxicity of naphthalene nanoparticles depends on 1,4 naphthoquinone
which is mediated through oxidative stress.
Key-words: RTCA, holomonitor, naphthalene, 1,4-naphthoquinone, glutathione,
biomass burning.
Den observante noterar att holomonitor finns med i nyckelordsangivelsen.Det visar sig att forskaren har hela 59 hänvisningar till instrumentet i sin studie.Jag kommer inte att radda upp samtliga av utrymmesmässiga skäl.Värt att notera i samma observation är att HoloMonitors kompis finns med, Agilentas RTCA, Real-Time Cell Analysis.
1 Introduction
In 2017 around 5 million people had premature deaths due to air pollution,
according to the Global Burden of Diseases, Injuries, and Risk Factors Study 2017
(GBD, 2017), an epidemiological study comparing results of 145 countries led by the
researches at the World Health Organization and based at the Institute for Health
Metrics and Evaluation (IHME)/University of Washington.
This number previously cited for air pollution deaths is higher in 2017, for
example, than child malnutrition (3.1 million of deaths) or alcohol related deaths (2.8
million of deaths), or even illegal drugs abuse (585 thousand of deaths).
That is a
growing factor for health problems according to this epidemiological study, when
showing that in the leading causes of premature deaths, Ambient Particulate Matter
(particulates in suspension in air) occupied the 17th position on 1990, then the 13th in
2007 and the 10th on 2017 (GBD, 2017).
In addition, the Global Burden of Diseases, Injuries, and Risk Factors Study
2017 adds a list of the 10 leading risks for premature death, where air pollution is the
only environmental, the others being behavioral or metabolic.
In the 10 leading risks
for premature death in 2007, unsafe water source was the 9th leading cause, being
lowered to 14th by 2017, showing that the world’s population does not share the same
preoccupations about the quality of water and air.
Human activities are the main determinant for intensifying a range of
environmental issues (Wang et al., 2013a). An increasing concentration of people and
economic activities in emerging megacities has been accompanied by a growing in
motor vehicle and factories emissions (Atash, 2007; Zhang et al., 2015a), a
development that has led to rapid increases in energy consumption, exhaust
emissions, and consequently air pollution, especially in developing countries (Tanaka,
2015).
There is no doubt that ambient air pollution, which constitutes an increasing
environmental concern, poses a huge range of negative health implications at local,
regional, and global scales (Grimm et al., 2008), including, but not limited to, higher
instances of cardiorespiratory diseases (lower respiratory infections), cancer (tracheal,bronchus and lung cancer), ischemic heart disease, ischemic stroke, intracerebral
hemorrhage, type 2 diabetes mellitus, among other diseases in urban populations
(Vella et al., 2015; Eze et al., 2015; GBD, 2017; Boudrel et al., 2017; Khilnani & Tiwari,
2018).
These impacts incur real costs for individuals, medical systems, and economies
(Matus et al., 2012).
Air pollution is a worldwide recognized threat to health, since it has been
associated with many diseases, including increased mortality and morbidity rates but
also with ecosystems damage, impacts on the built environment and the climate (EEA,
2017; Landrigan et al., 2018).
Some air pollutants can persist for long periods of time
and accumulate in the environment and food chain, thus affecting humans and animals
via multi-route of exposure (inhalation, dermal, ingestion). According to the European
Environment Agency (EEA), transports, industries, energy, power plants, agriculture,
households and waste management are the economic sectors that contribute the most
to air pollution (EEA, 2017).
So far, several epidemiological studies had affirmed that
air pollutants cause health diseases, diseases which are growing in number every year
and becoming more and more problematic in a world scale. But it still rests unknown:
what are these pollutants and why are they toxic, with the mechanisms of toxicology
still to be studied. To start understanding these questions we first have to identify what
are the toxic compounds produced by pollution.
3 Methods (urval)
3.1.5.1 Single cell lines
The cells were seeded at the amount of 2500 cells per well of 96-wells e-plates
for cell proliferation assay (xCELLigence, RTCA, Agilent, Santa Clara, CA, USA) and
96-wells plates for imaging in Holomonitor (PHI, Boston, MA, USA) and Cytation 3
(Biotek Instruments, Winooski, VT, USA), and 150.000 cells per 0.4µm PET membrane
inserts (Thincert cell culture insert for 12-wells plate, sterile, translucent membrane
(pet) (Greiner Bio-One, Courtaboeuf, France) for Vitrocell experiments, all under
conditions of 5% CO2 and 37°C.
3.3.2 Microscopy
3.3.2.1 Holomonitor
Holomonitor M4 (PHI, Boston, MA, USA) is a label-free imaging microscope that
uses a low power laser to analyze cells for extended periods of time.
From 3D images
collected with the low power laser, Holomonitor allows the study of dose response
assays and kinetic morphology, given by behavioral and structural parameters, such
as area, optical volume, perimeter length, migration, motility, and motility speed (Zhang
& Judson, 2018; Lajkó et al., 2018; Berlin et al., 2021).
Cells were plated in 96-wells plates and were able to proliferate for 48h under control
conditions.
After the addition of treatment (naphthalene by-products or biomass
burning mass wood nanoparticles dissolved in 150 µL culture medium), the plate was
placed in the microscope to initiate the analysis. The plates were covered with six
HoloLids (PHI, Boston, MA, USA), lids specially designed to eliminate image
disturbances caused by condensation inside the cell culture vessel.
For every
experiment, 3 to 5 wells were analyzed for each treatment. Time-lapse changed
according to the experiment: 5 min intervals during 10 h of experiment for naphthalene
by-products and 10 min interval for 10 h for the experiments on burning mass wood
nanoparticles.
After the experiment ended, the data were collected in Excel files for analysis.
Toxicity will be determined by changes on the cell index, parameters of cell
monitored by Holomonitor and results of fluorescence of zombie red (viability of cell
membrane) or DHR (oxidative stress production) when statistically different from
control.
4.2.2. Effects of naphthalene SOA by-products on A549 behavioral and structural
parameters
To determine whether the by-products of naphthalene SOA alter the structure and
behavior of cells, A549 cells were exposed to concentrations corresponding to the
EC50 observed for cell index, i.e., 1,4-NQ (50 µM), 2-OH-NQ, PA and OPA (5 mM).
Cells were monitored by means of the Holomonitor for 10 hours post-exposure to the
chemicals.
As for the cell index assay, the effect of DMSO was also tested with Holomonitor
to observe if the toxic effect induced by the chemicals was not induced by DMSO 0.1%
alone.
Results show that DMSO 0.1% did not affect any of the studied parameters
(area, optical volume, perimeter length, migration, motility, and motility speed).
The results for the toxicity of naphthalene NPs and its by-products were obtained
with real time cell analysis (RTCA). This system uses the cell index, a unit given by the
occupied area of gold-microelectrodes present inside each well of the E-plates.
Cell
index is given by the occupied area of the microelectrodes, which, in its turn, depends
on the number of cells, their size or their adhesion strength. RTCA is proven to be a
good method to study the toxicological effects of nanoparticles and/or chemicals
because cell number is directly related to cell division, thus, critical for epithelium
renewal (Altmann & Enesco, 1967).
However, since RTCA depends on three different
cell characteristics (number, size and adhesion) to establish the cell index, the
determination of which parameter affected the cell index is unknown.
The system does
not show which of the three previously cited characteristics affected the cell index.
Using RTCA alone, it is not possible to determine if the cell number, size or adhesion
were changed.
To complement the results of RTCA and go even further in our
research, we used the Holomonitor microscope.
The four naphthalene NPs by-products, compounds were tested with Holomonitor
at concentrations corresponding to their EC50.
Holomonitor is a quantitative phase
contrast microscope that uses a lower-power laser to analyze cells.
It produces 3D
pictures that are later utilized to obtain the quantification of several parameters, such
as area, perimeter and optical volume (structural parameters) and migration, motility
and motility speed (behavioral parameters), in real time and without any labelling.
Regarding the structural parameters, the area and perimeter of cells were not affected
by 1,4-NQ, but the optical volume was decreased (Figure 35). This indicates a change
in the shape of the cell, where the optical volume would be able to change without
interfering in the area.
The change in the size of the cell can be related to a loss of
local adhesions. Mechanisms linking 1.4-NQ with a decrease in cell adhesion have
never been reported, however one study with furano-1,2-naphthoquinone (Su et al.,
2010) and one study with a naphthoquinone-coumarin hybrid (NPQ-C6) (MartínRodríguez et al., 2019) stated that both quinones suppressed the activation of BCRABL1/STAT5, two proteins connected to cell adhesion.
RTCA or Holomonitor do not
precise the effect on the adhesion of cells, even if a change in it may interfere in the
cell index. Although studies relating 1,4NQ and cell adhesion have not been performed
yet, Wang et al. (2013b) studied the effect of shikonin, another naphthoquinone, on the
cell adhesion of A549 cells. They have found that shikonin at 1.5 µM have decreased
A549 cell adhesion to extracellular matrix by inhibiting integrin β1 expression.
Migration,
motility and motility speed are closely related as parameters of Holomonitor.
The effect on cells of the three other chemicals: 2-OH-NQ, PA and OPA, were also
measured using Holomonitor.
6 Conclusions and perspectives
My thesis brings light to the study of the toxicity of atmospheric nanoparticles and
its effects on the human health.
In conclusion, our study showed that anthropogenic
naphthalene nanoparticles are toxic to in vitro cell lines, using RTCA.
This toxicity is
mainly caused by 1,4-naphthoquinone (EC50 31.8 µM), the most toxic by-product of
naphthalene.
Both naphthalene nanoparticles and 1,4-naphthoquinone have their toxic
effects counteracted by the antioxidant glutathione (at 1 mM for naphthalene
nanoparticles and 2.5 mM for 1,4-naphthoquinone). The effect of glutathione was
tested under two different conditions, either was mixed with naphthoquinone during
one hour before addition on cells, or cells were exposed to glutathione for 15hours and
then removed before the addition of 1,4NQ on cells.
In both case glutathione
antagonized the effect of 1,4NQ arguing for an action through oxidative stress.
Further
analysis with Holomonitor showed that 1,4-naphthoquinone and phthaldialdehyde also
altered in the cells’ behavioral (migration, motility and motility speed) and structural
(optical volume) parameters.
Furthermore, dual anthropogenic-natural particles of
water -soluble biomass burning were also toxic to cells, with EC50 of 188.3 ± 43.3
µg/mL for flaming; 188.7 ± 24.3 µg/mL for smoldering; and 202 ± 20.9 µg/mL for
pyrolysis particles, also affecting the cell’s behavior and structure.
Moreover, the
present study also cleared the way for more toxicological studies, showing that three
real time and label free methods (RTCA, Holomonitor and Cytation) share a perfect
complementarity when assessing the toxicity of chemicals.
Min kommentar
Doktorsavhandlingen avslutas med en referens till Dr Alain Géloën`s studie från april 2021.
Bloggen uppmärksammade den naturligtvis när den offentliggjordes.
Samma rubrik skulle man kunna använda på denna doktorsavhandling.
Tack till Oscar som mejlade över denna doktorsavhandling.
Man sänder även en tacksamhetens tanke till Dr Alain Géloën och hans team för att de studerar ett så osexigt men ack så viktigt område som luftföroreningar och vilken negativ effekt de har på människa.
Jag avslutar som vanligt med Dr Alain Géloën´s väl valda ord.
Mvh the99
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