Comparison of the extraction efficiencies of different leaching
agents for reliable assessment of bio-accessible trace metal fractions in airborne
particulate matter
A. Mukhtar1, 2 and A.Limbeck1
1 Institute of
Chemical Technologies and Analytics, Vienna University of Technology, Vienna,
Austria,
2Division of Science and Technology, University of Education, Lahore,
Pakistan
ch_mazam@hotmail.com
Abstract
In present study, an in-vitro physiologically
based extraction test has been applied for extraction of bio-accessible trace
metal fractions in airborne particulate matter (APM) samples collected from different
urban sites in Austria and Pakistan using the leaching agents H2O, sodium
chloride, ammonium acetate, ammonium citrate, synthetic gastric juice and
artificial lung fluids. Obtained extracts were then measured using an ETV-ICP-OES
procedure which allowed highly sensitive measurement of dissolved analytes even
in the presence of leaching agents. Derived results indicated that the
investigated leaching agents extract different amounts of trace metals. In
general, leaching agents with organic nature yielded comparatively greater extractable
and thus bio-accessible trace metal fractions to that of simple solvents like H2O
or aqueous NaCl solution. With water, only 26.3±4.0% of Cd was found to be
bio-accessible whereas 88.4±24.8 of Cd was obtained as
bio-accessible fraction with the use of synthetic gastric juice. The
concentrations of bio-accessible metal fractions varied from 0.4 ng m-3
(Cd) to 714 ng m-3 (Zn) and 0.3 ng m-3 (Cd) to 190 ng m-3
(Zn) for PM10 samples collected from Karachi (Pakistan) and Graz (Austria)
respectively.
Key words: Bio-accessibility;
trace metals; airborne particulate matter; synthetic body fluids
Introduction
In recent years, many toxicological studies
have implicated metal contents as a possible harmful component of APM
(Prieditis and Adamson, 2002) since they can be absorbed into human tissues during
breathing especially particles with an aerodynamic diameter less than 10
microns (PM10). The toxicity of metal depends upon its species that are
present. Thus, for risk assessment of metal toxicity, it is important to
determine bio-accessible concentrations instead of total metal contents
(Michelozzi et al., 1998).
Particles
in the 2.5- to 10-μm size fraction are in most cases deposited in the tracheal
and the bronchial region after inhalation, from where they are transported
within hours by the so-called mucociliary clearance adoral and are mainly
swallowed. This fraction reaches the gastrointestinal tract (GIT), where it
comes into contact with gastric juice (Hamel et al., 1998). On the other hand
particles less than 1 µm can enter into the alveolar region of lungs where they
interact with the lung fluid (Jianjum et al., 2010 and Song et al., 2011). For
risk assessment of metal toxicity the determination of bio-accessible fractions
is recommended. For this purpose extraction procedures with different leaching
agents such as water, buffer solutions or synthetic body fluids were reported
in literature. Since the chemical composition of these leaching agents is
different it is expected that inconsistent amount of bio-accessible metal
fractions is obtained via the use of applied leaching agents. Therefore, it is
highly needed to evaluate the extraction efficiencies of various commonly used
leaching agents for true estimation of bio-accessible trace metal fractions in
APM.
In
present study, an in-vitro physiologically based extraction test (PBET) was
employed for extraction of APM samples from Graz (Austria) and Karachi
(Pakistan) with the leaching agents water, sodium chloride, ammonium acetate,
ammonium citrate, synthetic gastric juice, artificial lysosomal fluid and
Gamble solution, followed by measurement of resulting extracts using
electrothermal vaporization inductively-coupled plasma atomic emission
spectrometry (ETV-ICP-OES). Derived results were discussed in order to gain
more detailed information about the extraction behavior of the investigated
leaching agents.
Materials
and Methods
Reagents and materials
High purity water was obtained by purifying de-ionized water (reverse
osmosis/ion exchange combination Euro 20 plus, SG Water Systems, Germany) with
an Easypure 2 system (Thermo Barnstead, USA). All used chemicals and reagents
were of analytical reagent grade and were procured from Merck (Darmstadt,
Germany). Pepsin from porcine stomach mucosa (456 units mg−1 solid) was
purchased from Sigma Aldrich (Chemie GmbH, Steinheim, Germany). Certified
multielement standard solutions of In, As, Ba, Cd, Co, Cu, Mn, Ni, Pb and Zn
(1000 mg/L) were purchased from Merck (Darmstadt, Germany) and diluted with 1%
HNO3 (v/v) in order to prepare various working standard solutions. A
1 mol l-1 solution of ammonium acetate was prepared by dissolving
77.0825 g weight in one litre of bi-distilled water and pH of the solution was
maintained at 7. Similarly, 0.1 mol l-1 ammonium citrate solution
was prepared by dissolving 22.619 g in one litre of high purity water and pH of
the solution was maintained at 4.4 with the use of HCl. The synthetic gastric
juice was prepared according to a US Pharmacopeia methodology by dissolving 2 g
NaCl in 50 ml of high purity water followed by addition of 7 ml of conc. HCl in
order to maintain pH of resulting solution at 2-2.5. To this solution, 3.2 g of
pepsin were added, dissolved well and finally the volume was make up to 1 litre
using bi-distilled water. Artificial lysosomal fluid and Gamble solution were
prepared according to Colombo et al., 2008. Indium at level of 1 ppm was also
added to the prepared leaching agents as an internal standard in order to
overcome non-spectral interferences as well as errors related to manual sample
handling steps. The prepared leaching agents were stored in refrigerator at 4°C
until further use.
Instrumentation
An iCAP 6500
series ICP-OES spectrometer (Thermo Scientific, USA) has been used for
simultaneous multielement analysis of As, Ba, Cd, Co, Cu, Mn, Ni, Pb, Zn. For
sample introduction by electrothermal vaporization, an ETV system model 4000A
ETV (Spectral Systems, Fürstenfeldbruck, Germany) was used corresponding in
essence to a longitudinally heated graphite tube furnace. A detailed
description of instrumentation and optimized method parameters can be found in Mukhtar
and Limbeck, 2011.
Collection
of PM10 samples
Sampling of size
segregated APM samples (PM10) was performed at an urban site in Karachi, during
March-April 2009 (20 * 25 cm) using high volume sampler, with an intake volume
of approximately 1223 m3. Whereas sampling at Graz was done during July-August,
2006 (147 * 147 mm) with the help of an automated sampling device (Leckel,
Germany) containing a PM10 pre-separation head, with an intake volume of Graz
samples was 650 m3. Quartz
fiber filters (PALL Life-sciences, Michigan, USA) were used as sampling
substrates.
In-Vitro
physiological based extraction test (PBET) and determination of residual/total
metal contents
For determining
the bio-accessible trace metal fraction present in APM, an in-vitro
physiological based extraction test was performed. For this purpose, aliquots
with a diameter of 10 mm were punched out from each collected PM10 sample. Six
punches from each PM10 sample were taken into pre-cleaned polypropylene tubes
followed by addition of 700 mg of leaching agent. From each sample three
replicates have been prepared with each type of leaching agent. Closed tubes
were treated in an ultrasonic bath (Sonorex TK30, Bandelin, Germany) at 37°C
for 1 h in order to extract soluble trace metal fractions. After cooling down
the sample solutions to room temperature, the derived extracts were centrifuged
(Hettich, Zentrifugen-EBA 20) at 5000 rpm for 10 min for separation of undissolved
material and remaining filter substrate . The supernatant clear sample
solutions were transferred to new 3 ml polypropylene tubes and stored until
further analysis.
The remaining
eight aerosol filter punches (diameter 12 mm) were used for determination of
total trace metal contents. For sample digestion the filter punches were
transferred into pre-cleaned Bernas type Teflon lined bombs followed by
addition of 1 ml conc. HNO3, 1 ml HCl and 50 µl of HClO4. The Teflon lined bombs were then placed in
indigenously developed refractory oven and treated at 130 °C for 1 h in order
to dissolve total metal contents. Finally, the temperature of the refractory
oven was increased to 150 °C and maintained for other 30 min for evaporation of
excessive amount of HNO3 and HCl. After cooling the insoluble filter
material including the small droplet of HClO4 remaining in the
Teflon lined bombs were transferred in new PP tubes and . diluted to a final
mass of approximately 2 g with 1% (v/v) HCl. Simultaneously a defined amount of
In as internal standard was added. After centrifugation the supernatant
solutions were removed and stored in new PP tube at 4°C until ananlysis.
ETV-ICP-OES
Analysis of standard solutions and PM10 samples
Measurement of
standard solution and prepared PM10 extracts was carried out according to Mukhtar
and Limbeck, 2011. Briefly, 40 µl of the prepared extracts/digests were
pipetted into precleaned graphite boats and dried using an IR-lamp. For
analysis, the graphite boats were inserted into the graphite furnace tube of
the ETV system and the furnace program was started by the ICP-OES software and
the emission spectra of the vapor introduced into plasma was measured.
Results
and Discussion
Total metal concentrations in PM10 samples from
Karachi ranged from few ng m-3 to some hundred ng m-3.
The highest concentrations among the measured elements were observed for Zn ranging
from 361 ng m-3 to 918 ng m-3 whereas lowest
concentrations were observed for trace element Cd varying from 1.9 ng m-3
to 4.2 ng m-3. As and Co revealed results below their detection
limits i.e., less than 0.5 ng m-3. These results were found in
accordance to literature findings as reported by Venkataraman et al., 2002, and
Salam et al., 2003 for mega south Asian cities Mumbai and Dhaka respectively. Similar
observations were found for PM 10 samples collected from Graz, with
concentrations of Zn varying from 71 ng m-3 to 300 ng m-3 and
Cd concentrations ranging from 0.9 to 1.5 ng m-3. These findings were
in agreement with the results reported in literature from various sites in
central Europe. For example, Limbeck et al., 2009 have reported concentrations
of Cd and Zn in the order of 0.1 ng m-3 and 200 ng m-3 respectively
in PM10 samples collected from various urban sites in Vienna. The results
indicated clearly that atmosphere of Karachi is significantly more contaminated
with toxic trace elements as compared to Graz.
Bio-accessible fractions were found to be
lower than the corresponding total metal concentrations, indicating that only a
fraction of metal is soluble in various leaching agents. Since
bio-accessibility test has been performed with different leaching agents,
variable amounts of bio-accessible trace metal fractions have been released
which reflect differences in their ionic strength and composition. Therefore a
question arises about the trueness of bio-accessible fractions. It was found
that lowest bio-accessible trace metal fractions were obtained with the use of
water and NaCl as compared to leaching agents with organic composition like
synthetic gastric juice and artificial lysosomal fluid (Figure 1a and 1b).
However, the Gamble solution released comparable quantities of bio-accessible
trace metal fractions to that of water and NaCl. Furthermore, the low leaching
ability of Gamble solution as compared to
Fig. 1 Trace metal
fractions extractable with different leaching agents (%), results are average
of twenty investigated PM10 samples.
synthetic gastric juice and artificial
lysosomal fluid could be explained on the basis that it is neutral (pH˜7),
thus the interaction of Gamble solution with PM10 metal particles is not so aggressive.
In contrast, synthetic gastric juice and artificial lysosomal fluid being having
complex organic nature and acidic pH causes the metals to release easily,
thereby posing serious health risks when trace fractions become part of body
fluid. It can also be deduced from above figure that the metal extracting
behavior of applied leaching agents is quite similar for PM10 samples collected
from two entirely different sites i.e., Graz (Central Europe) and Karachi
(South Asia), indicating that bio-accessibility is element as well as leaching
agent dependent.
Using
synthetic gastric juice for assessment of bio-accessible trace metal fractions concentrations
in PM10 ranging from 0.4 ng m-3 (Cd) to 714 ng m-3 (Zn) were
found in aerosol samples collected in Karachi, whereas bio-accessible trace metal concentrations in PM10
samples from Graz varied from 0.3 ng m-3 (Cd) to 190 ng m-3
(Zn). Comparison of bio-accessible fraction in PM10 samples reported in present
study with literature data is not possible, since current study is carried out
for the first time where an attempt has been made to provide a guideline for
estimation of actual bio-accessible trace metal fractions in APM.
Conclusion
In this study an attempt has been made for
the first time in order to propose a model for the estimation of true
bio-accessible trace metal fractions in APM which could be used as a guideline
for future studies. In present study, an in-vitro PBET was applied for
extraction of bio-accessible metal fractions present in APM using various
leaching agents followed by subsequent measurement of gastric extracts using a
recently developed ETV-ICP-OES procedure. The obtained results indicated severe
differences in the extraction efficiencies of the investigated leaching agents.
Highest bio-accessible trace metal fractions are obtained with the use of synthetic
body fluids, lowest results were observed for water and sodium chloride
solution. Generally it was found that the presence of organic complexing agent
as well as acidic conditions improve the solubility of trace metals
significantly. Therefore, for future studies it is highly recommended to use
synthetic body fluids for estimation of bio-accessible trace metal fractions in
APM, since they enable a more reliable assessment of bio-accessible trace metal
fractions in PM10 than pure inorganic solutions.
Acknowledgements
Azam Mukhtar acknowledges the Higher Education Commission (HEC),
Pakistan and the Austrian Exchange Service (ÖAD) for providing a Ph.D.
scholarship for the period 2007-2011.
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