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http://informahealthcare.com/txmISSN: 1537-6516 (print), 1537-6524 (electronic)
Toxicol Mech Methods, 2013; 23(5): 315–322! 2013 Informa Healthcare USA, Inc. DOI: 10.3109/15376516.2012.755595
RESEARCH ARTICLE
Dispersant affects the cellular influences of single-wall carbonnanotube: the role of CNT as carrier of dispersants
Masanori Horie1, Mayumi Stowe1, Miki Tabei1, Haruhisa Kato2, Ayako Nakamura2, Shigehisa Endoh3,Yasuo Morimoto1, and Katsuhide Fujita3,4
1Institute of Industrial Ecological Sciences, University of Occupational and Environmental Health, Japan, Kitakyushu, Japan, 2National Metrology
Institute of Japan (NMIJ), National Institute of Advanced Industrial Science and Technology (AIST), Tsukuba, Japan, 3Technology Research
Association for Single Wall Carbon Nanotubes (TASC), Tsukuba, Japan, and 4Research Institute of Science for Safety and Sustainability (RISS), AIST,
Tsukuba, Japan
Abstract
The application of carbon nanotube (CNT) as a functional material to engineering and lifesciences is advanced. In order to evaluate the cytotoxicity of CNT in vitro, some chemical andbiological reagents are used for dispersants. In the present study, the cellular influences of sixkinds of chemical or biological reagents used as dispersants were examined. Pluronic F-127,Pluronic F-68, 1,2-dipalmitoyl-sn-glycero-3-phosphocholine (DPPC), pulmonary surfactantpreparation Surfacten� , bovine serum albumin (BSA) and Tween 80 were used in thepreparation of CNT-medium dispersants. The influences of each reagent on cell viability inhuman lung carcinoma A549 cells were small. However, Pluronic F-127, DPPC, Surfacten� andTween 80 induced an increase of intracellular reactive oxygen species (ROS) level. Next, CNT-medium dispersions were prepared, using each reagent as a dispersant and applied to A549cells. The cellular influences depended on the kind of dispersant. Cells exposed to CNTdispersion including Pluronic� F-127, Surfacten� , DPPC and Tween 80 showed LDH release tothe culture supernatant. Induction of intracellular ROS level was observed in cells exposed toCNT dispersion including each reagent except BSA. These results suggest that the adsorbeddispersant reagents on the surface of the CNT affect its cellular influences, particularly theinduction of oxidative stress.
Keywords
Adsorption, carbon nanotube, cell viability,dispersant, oxidative stress
History
Received 10 November 2012Revised 27 November 2012Accepted 30 November 2012Published online 24 January 2013
Introduction
Carbon nanotube (CNT), which is one of the nanocarbons,
has distinctive properties such as nanoscale fiber, lightweight,
electrical conductivity and chemical stability. CNT is applied
for not only industrial uses, such as fuel cells, but also in life
sciences such as nanomedicine. These distinctive physical and
chemical properties of CNT also mean a potential for
distinctive biological properties, including toxicity. The
increased application of CNT to industry and life sciences
makes the evaluation of its biological influences essential for
its effective utilization. Particularly, the evaluation of the
cellular influences of CNT is essential for its application in
life sciences, such as drug delivery systems. In vitro
evaluation of CNT using culture cells is essential in order
to understand the mechanisms of its cellular influence.
Actually, there are many investigations about the cellular
influences of CNT, which suggest that CNT has some
potential cytotoxic activity, particularly the induction of
oxidative stress (Chen et al., 2011; He et al., 2011; Horie
et al., 2012a). For example, an increase in intracellular
reactive oxygen species (ROS) level was shown in
SWCNT-exposed human lung carcinoma A549 cells
(Horie et al., 2012a).
Exposure of epithelial and fibroblast cells to multiwall
carbon nanotube (MWCNT) also induced an increase in
intracellular ROS level (He et al., 2011). The induction of
oxidative stress is one of the important properties in the
cellular influences of nanoparticles, including CNT. MWCNT
induced oxidative stress on lung-derived culture cells, and the
MWCNT differentiated fibroblast to myofibroblast via the
activation of NF-�B, TGFb1 and PDGF (He et al., 2011).
Myofibroblast has a high potency of collagen production, and
it may cause pulmonary fibrosis. On the other hand, the
cellular influences of CNT, particularly the induction of
oxidative stress, are affected by not only ‘‘CNT’’ but also by
the chemical agents used as a dispersant. In order to evaluate
the cellular influences of CNT, the preparation of a stable and
well-dispersed CNT-medium dispersion is very important.
Address for correspondence: Masanori Horie, Institute of IndustrialEcological Sciences, University of Occupational and EnvironmentalHealth, Japan, 1-1 Iseigaoka, Yahata-Nishi, Kitakyushu, Fukuoka807-8555, Japan. Tel: þ81936917466. E-mail: [email protected]
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CNT usually forms large aggregates in a culture medium that
includes large amount of salts and proteins, and an aggregated
CNT accumulates on the cells. Inhomogeneously distributed
CNT aggregates on cells may cause variable cellular
responses. Therefore, some chemicals are used as dispersant
in order to prepare a stable CNT-medium dispersion. For
in vitro examinations, it is necessary that the dispersant have a
low cytotoxicity. In some cases, chemical surfactants such as
Triton X-100 and Tween 80 are used for in vivo examinations
(Kato et al., in press; Morimoto et al., 2012a,b). Since these
chemical surfactants show cytotoxicity via damage to the cell
membrane, using them for in vitro examinations is unsuitable
(Alpatova et al., 2010). Tween 80 induced not only cell
membrane injury but also oxidative stress to cells (Tatsuishi
et al., 2005). Triton X-100 showed chemical interaction to
single-wall carbon nanotube (SWCNT) (Zhang & Zhan,
2007). Low cytotoxicity nonionic surface-active agents such
as Plironic F-127 and Pluronic F-68 are used in many cases of
in vitro examinations (Bardi et al., 2009). Additionally,
dipalmitoylphosphatidylcholine (DPPC), which is a major
phospholipid and pulmonary surfactant preparation, is also
used as a dispersant (Herzog et al., 2009; Mercer et al., 2010;
Wang et al., 2010). The cytotoxicity of these surfactants and
phospholipid are small. On the other hand, these surfactants
adsorb onto the surface of CNT in a stable medium
dispersion. CNT has strong protein adsorption ability (Dutta
et al., 2007). CNT adsorbed culture medium components onto
the surface and induced indirect cellular influences via
medium starvation (Casey et al., 2008). Generally, serum,
which is fetal bovine serum (FBS) in many cases, is added to
cell culture medium to supplement cell growth factors and
nutrients. When CNT is dispersed in a culture medium,
proteins such as bovine serum albumin (BSA) are adsorbed to
the CNT (Dutta et al., 2007). At that time, the adsorbed
proteins function as a dispersant. Even if the cytotoxicity of
the adsorbed proteins and surfactants is small, these adsorbed
‘‘dispersants’’ affect the cellular influences. Albumin-coated
SWCNT inhibited the induction of cyclooxygenase-2 (COX-
2) by lipopolysaccharide, and this anti-inflammatory effect
was decreased by the inhibition of albumin adsorption by
precoating of the SWCNT with Pluronic F-127 (Dutta et al.,
2007). The cytotoxicity of CNT was also decreased by the
adsorption of blood proteins onto the CNT (Ge et al., 2011).
These findings indicate that dispersants affect the cellular
influences induced by CNT. Therefore, the choice of a
dispersant for the preparation of a CNT-medium dispersant
for in vitro examinations is very important. Moreover, an
adsorbed dispersant on the surface of CNT may cause a
locally high concentration exposure of the dispersant to cells.
That is to say, the concentration of the dispersant in a
dispersion cannot reflect the cellular exposure concentration
of the dispersant. However, there is no investigation
comparing the cellular influences of various dispersants in
the same experimental system. In the present study, in order
to accurately evaluate the cellular influences induced by CNT,
the cellular influences of six kinds of dispersants were
examined. First we examined the cellular influences induced
by the dispersant itself, then a CNT-medium dispersion was
prepared using each dispersant, and these cellular influences
were examined.
Materials and methods
Materials
SWCNT was obtained from the National Institute of
Advanced Industrial Science and Technology (AIST,
Tsukuba, Japan). The SWCNT was synthesized by the
water-assisted chemical vapor deposition (so-called super-
growth CVD) method (Hata et al., 2004). SWCNT has a
relatively large diameter (1–3 nm), high carbon purity (above
99.98%) and high specific surface area. In the present study,
six kinds of chemical reagents and biologics were used as
dispersants: Pluronic� F-127, Pluronic� F-68, 1,2-dipalmi-
toyl-sn-glycero-3-phosphocholine (DPPC), BSA, polyox-
yethylene(20) sorbitan monooleate (Tween 80�) and
pulmonary surfactant preparation Surfacten�. We call these
chemical reagents and biologics ‘‘dispersants’’ in the present
study. Pulronic� F-127, Pulronic� F68 and DPPC were
purchased from Sigma-Aldrich Co. (St. Louis, MO). Tween
80� was purchased from Wako Pure Chemical Industries, Ltd
(Osaka, Japan). BSA (fatty acid free) was purchased from
Nacalai Tesque Inc. (Kyoto, Japan). Surfacten� was pur-
chased from Mitsubishi Tanabe Pharma Corporation (Osaka,
Japan). According to its data sheet, Surfacten� was prepared
by lung extract of healthy bovine and it included phospho-
lipids, free fatty acid and triglyceride.
Culture cells
Human lung carcinoma A549 cells were purchased from the
RIKEN BioResource Center (Tsukuba, Ibaraki, Japan). These
cells were cultured in Dulbecco’s modified Eagle medium
(DMEM; Gibco, Invitrogen Corporation, GlandIsland, NY)
supplemented with 10% heat-inactivated FBS (CELLect
GOLD; MP Biomedicals Inc., Solon, OH), 100 units/ml of
penicillin, 100 mg/ml of streptomycin and 250 ng/ml of
amphotericin B (Nacalai Tesque, Kyoto, Japan). In this
study, this DMEM cocktail is called ‘‘DMEM-FBS’’. The
DMEM cultures were placed in a 75-cm2 flask (Nunc; Thermo
Fisher Scientific Inc., Waltham, MA) and incubated at 37 �C in
a 5% CO2 atmosphere. For cell viability assays, the cells were
seeded on a 96-well, 12-well or 6-well multidish
(Nunc; Thermo Fisher Scientific Inc., Waltham, MA) at
2� 105 cells/ml and incubated for 24 h; subsequently, the
culture medium was removed and added to the dispersant
solution or CNT dispersion, and incubated for another 24 h.
Preparation of CNT-medium dispersion
For the preparation of SWCNT-Pluronic� F-127, -Pluronic
F-68, -Tween 80 and -BSA dispersion, 6 mg of SWCNT
powder was weighed in a glass vial and 1 mg/ml of Pluronic�
F-127, Pluronic F-68 and Tween 80 solution, and 10 mg/ml of
BSA solution were added at a concentration of 0.2 mg CNT/
ml dispersant. The SWCNT was predispersed by ultrasonica-
tion for 30 min in an ultrasonic bath (Branson 1510; Branson
Ultrasonics Corporation, Danbury, CT). Then the predis-
persed SWCNT dispersion was transferred to a 1.5-ml
microtube. The SWCNT was dispersed by ultrasonication
for 30 min at 4 �C (10 s ultrasonication and 5 s interval) using
Cosmobio Bioruptor (Cosmo bio Co. Ltd, Tokyo, Japan).
Then the large aggregates were removed by centrifugation at
316 M. Horie et al. Toxicol Mech Methods, 2013; 23(5): 315–322
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7200� g (10 000 rpm) for 10 min. The dispersed CNT in the
supernatant was collected by a filtration by mixed cellulose
ester membrane filter with a pore size of 0.1 mm (Toyo Roshi
Kaisha, Ltd, Tokyo, Japan). The membrane was transferred to a
glass vial and 1 ml of each dispersant was added (1 mg/ml). The
SWCNT on the membrane was dispersed again by ultrasonica-
tion for 30 min in an ultrasonic bath, then the predispersed
SWCNT dispersion was transferred to a 1.5 ml microtube. The
SWCNT was dispersed by ultrasonication for 30 min at 4 �C(10 s ultrasonication and 5 s interval) using a Cosmobio
Bioruptor (UCD-250; Cosmo Bio Co. Ltd, Tokyo, Japan).
The large aggregates were then removed by centrifugation at
7200� g for 10 min. For the preparation of CNT-DPPC and
-Surfacten dispersion, 6 mg of SWCNT powder was weighed in
a glass vial and 1 mg/ml of each dispersant solution was added
at a concentration of 0.2 mg CNT/ml dispersant. The SWCNT
was predispersed by ultrasonication for 30 min in an ultrasonic
bath, then the predispersed SWCNT dispersion was transferred
to a 1.5 ml microtube. The SWCNT was dispersed by
ultrasonication for 30 min at 4 �C using a Cosmobio
Bioruptor, then the large aggregates were removed by
filtrate-used cell strainer (BD Falcon 352235, 380 mesh, BD
Biosciences, San Jose, CA). Then, after centrifugation at 10
000 rpm for 10 min, the precipitated CNT was resuspended to
1 ml of DMEM-FBS and dispersed again by ultrasonication for
30 min at 4 �C using a Cosmobio Bioruptor.
The concentration of CNT in the dispersion was estimated by
absorbance of 600, 700 and 800 nm. The CNT-Tween 80
dispersion, the concentration of which is known, was used for
preparation of a standard curve. Each CNT dispersion was
diluted with DMEM-FBS at a concentration of 10 and 50 mg/ml.
Measurement of mitochondrial activity
For the measurement of mitochondrial activity, cells were
seeded in a 96-well plate at 2� 105 cells/ml. They were
incubated for 24 h and the culture medium was removed.
Subsequently, a dispersant solution or CNT-DMEM disper-
sion was applied and the cells were incubated for a further
24 h. A 3-(4,5-dimethyl-2-thiazolyl)-2,5-diphenyltetrazolium
bromide (MTT) assay was conducted for the determination of
mitochondrial activity. After removing the CNT dispersion,
0.5 mg/ml MTT (Nacalai Tesque, Inc., Kyoto, Japan) medium
solution was added to the cells, and the cells were incubated at
37 �C for 2 h. Isopropyl alcohol containing 40 mM HCl was
added to the culture medium (3:2, by volume), and they were
mixed by a pipette until the formazan was completely
dissolved. The optical density of the formazan was measured
at 570 nm using a VERSA max microplate reader (Molecular
Devices, Sunnyvale, CA). WST-1 assay was performed by a
premix WST-1 cell proliferation assay system (Takara Bio
Inc., Otsu, Japan). After removing the dispersant solution or
CNT-DMEM dispersion, the cells were incubated with a
WST-1 medium solution at 37 �C for 90 min. The WST-1
solution was then transferred to a new 96-well plate. The
optical density of the formazan was measured at 440 nm.
Detection of cell membrane damage
Cell membrane damage was detected by a lactate dehydro-
genase (LDH) assay. Cells were exposed to the dispersant or
CNT dispersion for 24 h and then the culture supernatant was
collected and applied to the LDH assay. Before being applied
to LDH assay, the culture supernatant of the CNT dispersion
was passed through a 0.20 mm membrane filter (Millex,
Millipore Corporation, Billerica, MA). In the LDH assays,
LDH release was measured with tetrazolium salt using a
Cytotoxicity Detection KitPLUS (LDH) (Roche Diagnostics
GmbH, Mannheim, Germany) according to the manufac-
turer’s protocol. The amount of formazan salt formed was
measured at 492 nm using a SpectraMax 190 absorbance
microplate reader (Molecular Devices, LLC, Sunnyvale, CA).
The maximum amount of released LDH was determined by
incubating the cells with a lysis solution provided in the kit.
Cell membrane damage was described as ‘‘cytotoxicity’’.
Cytotoxicity was calculated using the following equation:
Cytotoxicity (%)¼ (experimental value� low control)/(high
control� low control)� 100, where the low control (refers to
spontaneous LDH release) was determined as LDH released
from untreated normal cells, and the high control (refers to the
maximum release of LDH) was determined as LDH released
from cells lysed by surfactant treatment.
Measurement of intracellular ROS level
Intracellular ROS was detected by a 20,70-dichlorofluorescin
diacetate (DCFH-DA) (Sigma-Aldrich, St. Louis, MO).
DCFH-DA was dissolved in DMSO at a concentration of
5 mM as a stock solution and stored at �20 �C; when used in
an experiment, it was diluted 500 times with a serum-free
medium. The cells were seeded at 2� 105 cells/ml in 12-well
multiwall plates and incubated for 24 h at 37 �C, under a 5%
CO2 atmosphere. After the culture medium was removed,
CNT-DMEM dispersion was applied and the cells were
incubated for a further 24 h. The medium was then changed to
a serum-free DMEM that included 10 mM of DCFH-DA, and
it was incubated for 30 min at 37 �C. The cells were then
washed once with PBS, collected by 0.25% trypsinization,
washed once again with PBS and resuspended in 1 ml of PBS.
The cell samples in the PBS were excited with a 488 nm laser
in a iCyt EC800 cell analyzer (Sony Corporation, Tokyo,
Japan) flow cytometry system, and the emission of 20,70-dichlorofluorescein (DCF) was recorded at 525 nm. Data were
collected from at least 5000 gated events.
Real-time polymerase chain reaction
The expression of the target genes was determined by real-
time polymerase chain reaction (PCR). Total RNA was
isolated from cells using an RNeasy mini kit (Qiagen GmbH,
Hilden, Germany). cDNA synthesis was carried out with a
High Capacity cDNA Reverse Transcription kit (Applied
Biosystems, Carlsbad, CA). Real-time-PCR was conducted by
a Step One real-time-PCR system (Applied Biosystems), and
PCR amplification of lung tissues was detected by TaqMan�
gene expression assays (Applied Biosystems). PCR amplifi-
cation was detected with TaqMan� gene expression assay.
Human b-actin gene was used as an endogenous control. The
assay ID of TaqMan� gene expression assay for human
b-actin and heme oxygenase-1 (HO-1) were Hs99999903_m3
and Hs01110250_m1, respectively (Applied Biosystems).
DOI: 10.3109/15376516.2012.755595 Effect of dispersant on cytotoxicity of CNT 317
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The gene expression level was analyzed by the relative
standard curve method.
Statistical analyses
Data are the mean�SD for at least three separate data.
Statistical analyses were done by the analysis of variance
(ANOVA) using the Dunnett or Tukey tests for multiple
comparisons. The calculation method is described in each
figure legend.
Results
Effect of dispersant on mitochondrial activity and cellmembrane damage
Six kinds of ‘‘dispersants’’ were applied to A549 cells, and the
mitochondrial activities were measured by MTT and WST-1
assay after 24 h exposure (Figure 1). In the result of the MTT
assay, formation of the MTT formazan was slightly inhibited at
a concentration of 1.0 mg/ml by each dispersant except BSA.
Because these effects did not show in WST-1 assay, there was
possibility that some dispersants affected the formation or
dissolution of the MTT formazan. There might be little
biological meaning about this observation. Tween 80 also
decreased MTT conversion at a concentration of 0.1 mg/ml.
Compared with the MTT assay, in the result of the WST-1
assay, WST-1 conversion was decreased in only DPPC and
Surfacten� at a concentration of 1.0 mg/ml. Although the
WST-1 conversion was decreased at a high concentration, the
cytotoxicity of the dispersants was small. The formazan
formation was 90–97% at a concentration of 1.0 mg/ml in
both the MTT assay and the WST-1 assay. Only the Surfacten�
decreased cell viability to 69% at a concentration of 1.0 mg/ml
measured by MTT assay. Additionally, cell membrane damage
in cells exposed to the dispersants was measured by LDH
release to the medium. Cell membrane damage was observed
in DPPC, Surfacten� and Tween 80 exposed cells at a
concentration of 1.0 mg/ml. Other dispersants did not injure
the cell membranes.
Effect of dispersant on oxidative stress
Induction of oxidative stress is an important aspect of the
cellular influences of nanoparticles. SWCNT also induced
oxidative stress to culture cells (Horie et al., 2012a); therefore
the potential of induction of oxidative stress by the dispersants
was examined (Figure 2). A549 cells were exposed to each
dispersant for 24 h and intracellular ROS level was measured.
Except for Pluronic� F-68 and BSA, the dispersants increased
intracellular ROS level concentration-dependent. Particularly,
Tween 80 increased intracellular ROS level remarkably. The
intracellular ROS levels in the Tween 80 exposed cells at
concentrations of 0.1 and 1.0 mg/ml were 2.7 and 11 times
higher than in unexposed cells, respectively. The intracellular
ROS levels in Pluronic� F-127, Surfacten� and DPPC
exposed cells at concentrations of 1.0 and 0.1 mg/ml were
2–2.7 and 1.2–1.5 times higher than in unexposed cells,
respectively. These results suggest that oxidative stress is
induced in cells even when the concentration of the dispersant
is 0.1 mg/ml, which does not affect cell viability. On the other
hand, Pluronic� F-68 and BSA did not induce an increase of
intracellular ROS level even at a concentration of 1.0 mg/ml.
The gene expression of HO-1 in dispersants-exposed cells was
also examined. HO-1 is a major stress response enzyme
protein, including to oxidative stress, and has the function of
decreasing oxidative stress. Only Surfacten� and Tween 80
enhanced the gene expression of HO-1.
Effect of CNT dispersion on mitochondrial activity andcell membrane damage
SWCNT-medium dispersions were prepared using each
dispersant. When CNT-medium dispersions were applied to
MTT
WST-1
LDH
0
20
40
60
80
100
120
F-127 F-68 Surfacten DPPC BSA Tween80
0.001
0.01
0.1
1.0
mg/mL
MT
T c
onve
rsio
n (%
of
cont
rol) ** **
**
**
**
0
20
40
60
80
100
120
F-127 F-68 Surfacten DPPC BSA Tween80
0.001
0.01
0.1
1.0
WST
-1 c
onve
rsio
n (%
of
cont
rol)
mg/mL
****
0
10
20
30
40
50
60
F-127 F-68 Surfacten DPPC BSA Tween80
0.001
0.01
0.1
1.0
Cyt
otox
icity
(%)
mg/mL
**
**
**
Figure 1. Cytotoxicity of the dispersant.Cytotoxicity was measured by MTT, WST-1 and LDH assay asmitochondrial activity and cell membrane damage. A549 cells wereexposed to each ‘‘dispersant’’ for 24 h at concentrations of 0.001, 0.01,0.1 and 1.0 mg/ml. The mitochondrial activity was measured by MTTand WST-1 assay. The percentage of mitochondrial activity comparedwith the standardized control was 100%. Cell membrane damage wasdetected by LDH release to the culture medium.**p50.01, *p50.05 (versus control, Dunnett, ANOVA).
318 M. Horie et al. Toxicol Mech Methods, 2013; 23(5): 315–322
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cells, none of the dispersions included aggregates or
precipitations, at least by visual judgment. After the CNT-
medium dispersions were incubated with cells for 24 h, only
the dispersions including Surfacten� and DPPC formed small
aggregates. A549 cells were exposed to CNT-medium
dispersions, including each dispersant, for 24 h and then cell
viabilities were measured by MTT assay and WST-1 assay
(Figure 3). It is reported that the MTT assay is not suitable in
the evaluation of the cytotoxicity of CNT because CNT
inhibits the formation of color by MTT formazan (Worle-
Knirsch et al., 2006). Thus, we also examined the influences
of the dispersant on the measurement of the cell viability of
CNT-dispersion-exposed cells by MTT assay. All the CNT-
medium dispersions decreased MTT conversion to 20–40% as
measured by MTT assay. In many cases, result of MTT assay
is shown as ‘‘cell viability’’. When ‘‘cell viability’’ was
measured by MTT assay, all the CNT-medium dispersions
decreased apparent viability to 60–80%. On the other hand,
when WST-1 assay was conducted, WST-1 conversion was
significantly decreased in the DPPC and Tween 80 disper-
sions at a CNT concentration of 50 mg/ml. LDH release to the
medium was observed in the CNT-dispersion-exposed cells
except in dispersions including Pluronic� F-68 and BSA.
Although a significant release of LDH was observed in cells
exposed to the dispersions including Pluronic� F-127, the cell
membrane damage was very small. The LDH activity in the
culture supernatant at a CNT concentration of 50 mg/ml was
1.9% of total intracellular LDH. The LDH releases of CNT
dispersions including Surfacten� and DPPC-exposed cells
MTT
WST-1
LDH
0
20
40
60
80
100
120
10
50
CNT
μg/mL
MT
T c
onve
rsio
n (%
of
cont
rol)
**
****
****
****
**
********
0
20
40
60
80
100
120
10
50
WST
-1 c
onve
rsio
n (%
of
cont
rol)
μg/mL
CNT
**
0
5
10
15
20
25
30
F-127 F-68 Surfacten DPPC BSA Tween80
F-127 F-68 Surfacten DPPC BSA Tween80
F-127 F-68 Surfacten DPPC BSA Tween80
10
50
CNT
μg/mL
Cyt
otox
icity
(%
)
**
**
****
****
**
Figure 3. Cytotoxicity of the CNT dispersion with various dispersants.Cytotoxicity was measured by MTT, WST-1 and LDH assay asmitochondrial activity and cell membrane damage. A549 cells wereexposed to the CNT-medium dispersion with various dispersants for 24 hat CNT concentrations of 10 and 50mg/ml. The final concentrations ofthe dispersant were approximately 1.0 (BSA) and 0.1 mg/ml (otherdispersants). The mitochondrial activity was measured by MTT andWST-1 assay. The percentage of mitochondrial activity compared withthe standardized control was 100%. Cell membrane damage was detectedby LDH release to the culture medium.**p50.01, *p50.05 (versus control, Dunnett, ANOVA).
Intracellular ROS level
Gene expression of HO-1
0
2
4
6
8
10
12
14
0.01
0.1
1.0
mg/mL
Rel
ativ
e D
CF
fluo
resc
ence
(vs
con
trol
)
**
**
**
*******
**
0
0.5
1
1.5
2
2.5
F-127 F-68 Surfacten DPPC BSA Tween80
F-127 F-68 Surfacten DPPC BSA Tween80
0.1
1.0
mg/mL
Rat
io to
con
trol
(H
O-1
/β-a
ctin
)
**
** **
Figure 2. Influence of the dispersant on the induction of oxidative stress.Intracellular ROS level was detected by the DCFH method.The A549 cells were treated with the dispersant for 24 h. The mediumwas then exchanged with fresh, FBS-free DMEM containing 10mM ofDCFH-DA. After incubation for 30 min, cells were collected andwashed. DCF fluorescence in the cells was measured by flowcytometry. The value of the DCF fluorescence-standardized untreatedcells was 1. mRNA was prepared from the A549 cells which wereexposed to the dispersant for 24 h. Gene expression of HO-1 wasdetected by real-time PCR.**p50.01, *p50.05 (versus control, Dunnett, ANOVA).
DOI: 10.3109/15376516.2012.755595 Effect of dispersant on cytotoxicity of CNT 319
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were 5.3% and 6.8% of total intracellular LDH at a CNT
concentration of 50 mg/ml, respectively. CNT dispersion
including Tween 80 most induced LDH release. The LDH
release of the CNT dispersion including Tween 80-exposed
cells was 25% at a CNT concentration of 50 mg/ml.
Effect of CNT dispersion on oxidative stress
The induction of oxidative stress by CNT-medium dispersions
including each dispersant was examined. Almost all the CNT
dispersions induced an increase in intracellular ROS level
(Figure 4). Only the dispersion including BSA did not cause
an increase in intracellular ROS level. Although the
intracellular ROS level tended to increase in the CNT
dispersion including BSA exposed cells, there was no
statistically significant difference. On the other hand, when
cells were exposed to CNT dispersions including Pluronic�
F-127, Pluronic� F-68 and Surfacten� at a CNT concentration
of 50 mg/ml, the intracellular ROS levels were significantly
increased. The intracellular ROS levels in cells exposed to
these dispersions were 1.5–2 times higher than in unexposed
cells. In cells which were exposed to CNT dispersion
including DPPC at a concentration of 50 mg/ml, the
intracellular ROS level was approximately 6.7 times higher
than that in unexposed cells. The increases of the intracellular
ROS level caused by exposure to a CNT-medium dispersion
were reduced by removal of the CNT from the dispersion. The
CNT-medium dispersions were filtered by a filter whose pore
size was 0.20mm. The concentration of CNT in the filtrate of
50 mg/ml of CNT dispersion was 0–4 mg/ml, except for the
dispersion including Tween 80. These results suggest that an
induction of intracellular ROS level was caused by CNT with
adsorbed dispersant, not an excess of dissolved dispersant. On
the other hand, the CNT dispersion including Tween 80
induced a significant increase of intracellular ROS level at
concentrations of 10 and 50 mg/ml. Compared with unexposed
cells, the relative DCF fluorescence of the CNT dispersion
including Tween 80 at CNT concentrations of 10 and
50 mg/ml were 6 and 11 times higher, respectively.
Moreover, a filtrate of the CNT dispersion, including Tween
80, still showed an induction of intracellular ROS level. The
filtrate of CNT dispersion including Tween 80 at a CNT
concentration of 50 mg/ml still included CNT; the filtrate
included 14.2 mg/ml of CNT. Although the CNT concentration
in the dispersion was decreased by filtration, intracellular
ROS level did not differ between the dispersion and the
filtrate. This result suggests that soluble Tween 80 was
involved in the induction of intracellular ROS level.
Additionally, it also can be considered that adsorbed Tween
80 on the remaining CNT caused induction of intracellular
ROS level. The Gene expression of HO-1 in the CNT-
dispersion-exposed cells was also examined (Figure 4). The
CNT dispersions including Pluronic� F-127, Pluronic� F-68,
Surfacten� and DPPC enhanced the gene expression of HO-1.
On the other hand, exposure to the CNT dispersions including
BSA and Tween 80 did not affect HO-1 gene expression.
Discussion
The six kinds of dispersants used in the present study had a
small influence on cell viability. Even at a concentration of
1.0 mg/ml, the mitochondrial activity was slightly decreased
in only Surfacten� and DPPC. Surfacten�, DPPC and Tween
80 induced membrane damage at a concentration of
1.0 mg/ml. The other dispersions did not injure cell
membranes. At lower concentrations, 0.1 mg/ml or lower,
there was no influence on mitochondrial activity or
membrane damage. The main components of Surfacten� are
phospholipids, free fatty acids and triglyceride. Compared
with other water soluble dispersants, Surfacten� and DPPC
formed micelle in the medium dispersion, and they may have
had higher affinity for the cell membrane. These phospholi-
pids and Tween 80 may injure the cell membrane and lead to
a decrease of mitochondrial activity at a high concentration.
However, basically, the dispersants used in the present study
had only a small effect on mitochondrial activity. On the other
hand, even if the dispersant did not affect mitochondrial
activity at a concentration of 0.1 mg/ml, some dispersants,
such as Pluronic F-127�, Surfacten�, DPPC and Tween
80, induced an increase in intracellular ROS level.
Intracellular ROS level
Gene expression of HO-1
0
2
4
6
8
10
12
14
10 50 10 50 10 50 10 50 10 50 10 50
Dispersion
Filtrate
Rel
ativ
e D
CF
fluo
resc
ence
(vs
con
trol
)
Concentration of CNT in DMEM dispersion and filtrate(μg/ml)
F-127 F-68 Surfacten DPPC BSA Tween 80
**
**
**
****
**
**
**
**
**
Dispersion
Filtrate1.6 4.2 0.0 1.5 0.0 2.1 0.0 0.3 0.4 0.0 2.4 14.2
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
F-127 F-68 Surfacten DPPC BSA Tween80
10
50
μg/mL
Rat
io to
con
trol
(H
O-1
/β-a
ctin
)
CNT**
****
******
****
Figure 4. Influence of the CNT dispersion with various dispersants onthe induction of oxidative stress.Intracellular ROS level was detected by the DCFH method. The A549cells were treated with CNT-medium dispersions with various dis-persants for 24 h at CNT concentrations of 10 and 50mg/ml. The finalconcentrations of the dispersant were approximately 1.0 (BSA) and0.1 mg/ml (other dispersants). The medium was then exchanged withfresh, FBS-free DMEM containing 10mM of DCFH-DA. Afterincubation for 30 min, cells were collected and washed. DCFfluorescence in the cells was measured by flow cytometry. The valueof DCF fluorescence-standardized untreated cells was 1. mRNA wasprepared from the A549 cells which were exposed to the CNT dispersionfor 24 h. Gene expression of HO-1 was detected by real-time PCR.**p50.01, *p50.05 (versus control, Dunnett, ANOVA).
320 M. Horie et al. Toxicol Mech Methods, 2013; 23(5): 315–322
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Additionally, Surfacten� and Tween 80 also induced the gene
expression of HO-1. These results suggest that some
dispersants induce oxidative stress on the cell even if there
is no effect on cell viability. We previously examined
intracellular ROS level in hydrogen peroxide (H2O2)–exposed
A549 cells (Horie et al., 2010). The intracellular ROS level in
the cells that exposed F-127�, Surfacten� and DPPC at
concentration of 1.0 mg/ml was equal to the intracellular ROS
level of the cells that exposed 250 mM of H2O2. Additionally,
exposure of the cells by 1 mM of radical initiator, AIPH, for
24 h, increased gene expression of HO-1 (Horie et al., 2012b).
It was three times higher than unexposed cells. Enhancement
of the gene expression of HO-1 by Surfacten and Tween 80
was lower than that of 1 mM of AIPH.
Next, we examined the cellular influences of CNT-medium
dispersions including each ‘‘dispersant’’. The concentration
of the carry-on dispersant from the stock dispersion to
medium dispersion was estimated to be 0.1 mg/ml or lower.
The influence of the CNT dispersions on cell viability was as
small as that of the dispersants. As previously reported
(Worle-Knirsch et al., 2006), an MTT assay of CNT-
dispersion-exposed cells showed a color-dulling result of
MTT formazan, regardless of the kind of dispersant. These
results indicated that MTT assay is not suitable for the
evaluation of the cellular influences of CNT. The cause of the
color-dulling of MTT formazan is unclear, but CNT is
involved in the phenomenon. It may be caused by adsorption
of MTT formazan to CNT or inhibition of dissolution (Worle-
Knirsch et al., 2006).
Cell membrane damage was observed in CNT-dispersion-
exposed cells. LDH release was seen in cells which were
exposed to CNT dispersions including Surfacten�, DPPC,
Tween 80 and Pluronic� F-127. Surfacten�, DPPC and Tween
80 also induced LDH release themselves without CNT. On the
other hand, although Pluronic� F-127 itself did not induce
cell membrane damage without CNT, the CNT dispersion
including Pluronic� F-127 did induce LDH release.
CNT dispersion also induced an increase in intracellular
ROS level. A dose-dependent induction of intracellular ROS
level was observed in cells which were exposed to the CNT
dispersions including each dispersant except BSA. We
previously reported that a CNT-medium dispersion including
BSA as a dispersant induced a significant increase in
intracellular ROS level after 24 h exposure (Horie et al.,
2012a). At that time, we used the same SWCNT as in the
present study, and the CNT concentration was 57 mg/ml. The
intracellular ROS level in the cells exposed to the CNT
dispersion that included BSA was approximately 1.4 times
higher than in unexposed cells. On the other hand, in the
present study, intracellular ROS level in the cells exposed to
the CNT dispersion that included BSA at a concentration of
50 mg/ml was approximately 1.6 times higher than in
unexposed cells. Although the intracellular ROS level in the
cells exposed to the CNT dispersion that included BSA tended
to increase, there was no significant difference because the
data had great variability.
Induction of intracellular ROS level in CNT-
dispersion-exposed cells was inhibited by the removal of
CNT from the dispersion by filtration. The result suggests
that the induction of intracellular ROS level was caused by
CNT, not by the free-soluble dispersant. However, the
filtrate of the CNT dispersion that included Tween 80 still
included a high concentration of CNT. Therefore, whether
the cause of the induction of intracellular ROS level by the
CNT dispersion including Tween 80 was the remaining CNT
or the soluble Tween 80 was unclear. Moreover, gene
expression of HO-1 was enhanced by exposure to CNT
including some dispersants. Intriguingly, although Tween 80
induced an increase in intracellular ROS level, an enhance-
ment of HO-1 expression was not seen in cells exposed to
the CNT dispersion including Tween 80. The cause of this
observation is unclear. At least, adsorbed Tween 80 on the
CNT did not affect the expression of HO-1. CNT dispersion
including BSA did not enhance the expression of HO-1,
either.
The cellular influences of the CNT dispersions were
different depending on the kind of dispersant. Cellular
influences of CNT dispersion on the induction of oxidative
stress were more remarkable than on cell viability.
Particularly, the lipophilic dispersants, Surfacten� and
DPPC, tended to show larger cellular influences than
hydrophilic dispersants. These dispersants might be adsorbed
on the surface of CNT. Even if the concentration of the free
soluble dispersant is low enough, the dispersant that adsorbs
on the surface of CNT has the possibility of becoming locally
concentrated, leading to cellular influences such as the
induction of oxidative stress. On the other hand, the CNT
dispersions including Pluronic� F-68 and BSA showed no
cellular influences. These results suggest that the cellular
influences of CNT are artificially affected by the dispersant.
There are reports that the dispersion state of CNT influences
the cytotoxic activity of CNT (Raja et al., 2007), and thus the
choice of dispersant is important for the preparation of a
stable and uniform dispersion (Kim et al., 2011; Monteiro-
Riviere et al., 2005). In the present study, the CNT dispersions
did not include any aggregates or precipitates, at least visually
discernable ones. However, the size of the aggregates might
be different depending on the kind of dispersant. Additionally,
the interaction between cells and dispersant-adsorbing CNT
should be considered. Actually, after cellular exposure for
24 h, the CNT dispersions including Surfacten� and DPPC
formed small aggregates. There is a report that CNT adsorbed
lipids of lung surfactant in vivo and the adsorbed lipids affect
the phagocytosis of macrophages (Kapralov et al., 2012).
Protein-adsorbed CNT also decreased its biological activity
(Dutta et al., 2007). It is possible that the size of the
aggregates, which depends on the kind of dispersant, affects
their biological activity.
As there is possibility that some dispersants lead to artificial
results in the evaluation of the biological influences of CNT,
the selection of a dispersant is very important. Especially, the
effect of the adsorbed dispersant on the surface of CNT is
considerable. In in vitro examinations, it is important to
understand the biological activity of the dispersant and select a
suitable dispersant for the experimental purpose.
Declaration of interest
The authors report no conflicts of interest. The authors alone
are responsible for the content and writing of this article.
DOI: 10.3109/15376516.2012.755595 Effect of dispersant on cytotoxicity of CNT 321
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This research was funded by New Energy and Industrial
Technology Development Organization of Japan (NEDO)
Grant ‘‘Innovative carbon nanotubes composite materials
project toward achieving a low-carbon society (P10024)’’.
References
Alpatova AL, Shan W, Babica P, et al. (2010). Single-walled carbonnanotubes dispersed in aqueous media via non-covalent functionaliza-tion: effect of dispersant on the stability, cytotoxicity, and epigenetictoxicity of nanotube suspensions. Water Res 44:505–20.
Bardi G, Vittorio O, Maffei M, et al. (2009). Adipocytes differentiationin the presence of Pluronic F127-coated carbon nanotubes.Nanomedicine 5:378–81.
Casey A, Herzog E, Lyng FM, et al. (2008). Single walled carbonnanotubes induce indirect cytotoxicity by medium depletion in A549lung cells. Toxicol Lett 179:78–84.
Chen B, Liu Y, Song WM, et al. (2011). In vitro evaluation ofcytotoxicity and oxidative stress induced by multiwalled carbonnanotubes in murine RAW 264.7 macrophages and human A549 lungcells. Biomed Environ Sci 24:593–601.
Dutta D, Sundaram SK, Teeguarden JG, et al. (2007). Adsorbed proteinsinfluence the biological activity and molecular targeting of nanoma-terials. Toxicol Sci 100:303–15.
Ge C, Du J, Zhao L, et al. (2011). Binding of blood proteins tocarbon nanotubes reduces cytotoxicity. Proc Natl Acad Sci USA108:16968–73.
Hata K, Futaba DB, Mizuno K, et al. (2004). Water-assisted highlyefficient synthesis of impurity-free single-walled carbon nanotubes.Science 306:1362–4.
He X, Young SH, Schwegler-Berry D, et al. (2011). Multiwalled carbonnanotubes induce a fibrogenic response by stimulating reactiveoxygen species production, activating NF-�B signaling, and promot-ing fibroblast-to-myofibroblast transformation. Chem Res Toxicol24:2237–48.
Herzog E, Byrne HJ, Casey A, et al. (2009). SWCNT suppressinflammatory mediator responses in human lung epithelium in vitro.Toxicol Appl Pharmacol 234:378–90.
Horie M, Komaba LK, Kato H, et al. (2012a). Evaluation of cellularinfluences induced by stable nanodiamond dispersion; the cellularinfluences of nanodiamond are small. Diam Relat Mater 24:15–24.
Horie M, Fukui H, Endoh S, et al. (2012b). Comparison of acuteoxidative stress on rat lung induced by nano and fine-scale, solubleand insoluble metal oxide particles: NiO and TiO2. Inhal Toxicol24:391–400.
Horie M, Nishio K, Kato H, et al. (2010). In vitro evaluation of cellularresponses induced by stable fullerene C60 medium dispersion.J Biochem 148:289–98.
Kapralov AA, Feng WH, Amoscato AA, et al. (2012). Adsorption ofsurfactant lipids by single-walled carbon nanotubes in mouse lungupon pharyngeal aspiration. ACS Nano 6:4147–56.
Kato T, Totsuka Y, Ishino K, et al. Genotoxicity of multi-walled carbonnanotubes in both in vitro and in vivo assay systems. Nanotoxicology(in press).
Kim JS, Song KS, Lee JH, et al. (2011). Evaluation ofbiocompatible dispersants for carbon nanotube toxicity tests. ArchToxicol 85:1499–1508.
Mercer RR, Hubbs AF, Scabilloni JF, et al. (2010). Distribution andpersistence of pleural penetrations by multi-walled carbon nanotubes.Part Fibre Toxicol 7:28.
Monteiro-Riviere NA, Inman AO, Wang YY, Nemanich RJ. (2005).Surfactant effects on carbon nanotube interactions with humankeratinocytes. Nanomedicine 1:293–9.
Morimoto Y, Hirohashi M, Kobayashi N, et al. (2012a). Pulmonarytoxicity of well-dispersed single-wall carbon nanotubes after inhala-tion. Nanotoxicology 6:766–75.
Morimoto Y, Hirohashi M, Ogami A, et al. (2012b). Pulmonary toxicityof well-dispersed multi-wall carbon nanotubes following inhalationand intratracheal instillation. Nanotoxicology 6:587–99.
Raja PM, Connolley J, Ganesan GP, et al. (2007). Impact of carbonnanotube exposure, dosage and aggregation on smooth muscle cells.Toxicol Lett 169:51–63.
Tatsuishi T, Oyama Y, Iwase K, et al. (2005). Polysorbate 80 increasesthe susceptibility to oxidative stress in rat thymocytes. Toxicology207:7–14.
Wang L, Castranova V, Mishra A, et al. (2010). Dispersion of single-walled carbon nanotubes by a natural lung surfactant for pulmonaryin vitro and in vivo toxicity studies. Part Fibre Toxicol 7:31.
Worle-Knirsch JM, Pulskamp K, Krug HF. (2006). Oops they did itagain! Carbon nanotubes hoax scientists in viability assays. Nano Lett6:1261–8.
Zhang ZB, Zhang SL. (2007). Photon-induced selective interactionbetween small-diameter metallic carbon nanotubes and triton X-100.J Am Chem Soc 129:666–71.
322 M. Horie et al. Toxicol Mech Methods, 2013; 23(5): 315–322
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