Sukhyun Kang1, Hyuksu Han2, Kangpyo Lee1, Kang Min Kim1. 1. Korea Institute of Industrial Technology, 137-41 Gwahakdanji-ro, Gangwon-do 25440, Republic of Korea. 2. Department of Energy Engineering, Konkuk University, 120 Neungdong-ro, Gwangjin-gu, Seoul 05029, Republic of Korea.
Abstract
With respect to the detection of Fe3+ ions, graphene quantum dots (GQDs) have limitations for commercialization owing to their high limit of detection (LOD). Here, we report a one-step pulsed laser ablation (PLA) process to fabricate amino-functionalized GQDs (FGQDs) for the efficient detection of Fe3+ using polypyrrole (PPy) both as a precursor (amine N) and as a surfactant and also using graphite as a carbon precursor. Using this method, the amine N groups were easily incorporated into the carbon network of the GQDs. Additionally, compared to pristine GQDs, FGQDs showed smaller particle sizes and narrower size distributions owing to the surface passivation effects of the PPy surfactant. Due to the synergistic effect of surface passivation and incorporation of amine N groups, FGQDs exhibited a sensitive response to Fe3+ ions in the concentration range of 500 nM to 50 μM, which is lower than the quality standards for Fe3+ ions (∼5.36 μM) as suggested by the World Health Organization (WHO). Furthermore, the processing time for synthesizing FGQDs by the PLA process was less than 30 min, thus allowing successful practical applications of GQDs in the sensing field.
With respect to the detection of Fe3+ ions, graphene quantum dots (GQDs) have limitations for commercialization owing to their high limit of detection (LOD). Here, we report a one-step pulsed laser ablation (PLA) process to fabricate amino-functionalized GQDs (FGQDs) for the efficient detection of Fe3+ using polypyrrole (PPy) both as a precursor (amine N) and as a surfactant and also using graphite as a carbon precursor. Using this method, the amine N groups were easily incorporated into the carbon network of the GQDs. Additionally, compared to pristine GQDs, FGQDs showed smaller particle sizes and narrower size distributions owing to the surface passivation effects of the PPy surfactant. Due to the synergistic effect of surface passivation and incorporation of amine N groups, FGQDs exhibited a sensitive response to Fe3+ ions in the concentration range of 500 nM to 50 μM, which is lower than the quality standards for Fe3+ ions (∼5.36 μM) as suggested by the World Health Organization (WHO). Furthermore, the processing time for synthesizing FGQDs by the PLA process was less than 30 min, thus allowing successful practical applications of GQDs in the sensing field.
The
global issue of heavy-metal-ion pollution has attracted significant
attention in the past few decades because of critical problems such
as water pollution and human health.[1,2] Heavy-metal
ions (e.g., Cd2+, Fe3+, Cu2+, Co2+, Ni2+, Al3+, and Ag3+)
can be found in water, and eventually turn more toxic inside the human
body. These heavy-metal ions are nondegradable in nature, leading
to their continuous accumulation in the soil and human body. Therefore,
several studies have been undertaken for the detection of heavy metals
to date.[3−6]Among these heavy-metal ions, Fe3+-ion sensing
is important
because the deficiency or abundance of Fe3+ can cause serious
diseases, such as anemia, Parkinson’s syndrome, Alzheimer’s,
and even cancer.[7,8] Several fluorescence probes such
as organic fluorescent dyes, polymer nanodots, and semiconductor quantum
dots have been widely studied for the detection of Fe3+ ions.[9−12] However, they suffer from certain disadvantages such as poor water
solubility, low photostability, and high toxicity, which limits their
reliable application in real sample assays.Recently, graphene
quantum dots (GQDs) have emerged as a potential
new platform as fluorescent probes for the detection of Fe3+ ions because of their low toxicity, high water solubility, and photostability.[13−17] However, the GQDs exhibit a low limit of detection (LOD) for the
Fe3+ ions owing to the limited number of surface active
sites.[18−20] To overcome these issues, several studies have been
performed to enhance the active sites on the GQDs. For instance, functionalized
GQDs with amino groups (e.g., amine N) provide abundant active sites,
which lead to superior detection performance of Fe3+ ions.[21] In addition, narrower size distribution and
smaller size of GQDs were obtained by the effect of surface passivation
using a surfactant (i.e., PPy), resulting in an increased specific
surface area.[22] Owing to the large number
of active sites due to the increasing specific surface area of the
GQDs, the detection performance for Fe3+ ions was enhanced.
Consequently, the effect of surface passivation and functionalization
of GQDs with amine N groups can lead to an improvement in the active
sites, which may play a key role in the enhancement of the Fe3+ detection limit.[23]Recently,
several studies have reported the synthesis of FGQDs
by chemical oxidation, electrochemical preparation, and hydrothermal
methods.[24−26] However, these methods are usually performed under
strongly acidic conditions, which require a prolonged washing step.
Furthermore, for the surface passivation and functionalization of
GQDs, multiple synthesis processes such as heat treatment and deep
coating are required, which are costly and time-consuming.[27,28] Therefore, it is necessary to develop a one-step synthetic method.Pulsed laser ablation (PLA) is an alternative method for the synthesis
of FGQDs. Previous studies have reported the successful preparation
of functionalized GQDs with the incorporation of heteroatoms (e.g.,
N, S) via a one-step PLA process.[29−33] Additionally, lauryl dimethylaminoacetic acid betaine
(LDA) was employed as a surfactant for the surface passivation of
Tb3Al5O12:Ce3+ nanoparticles
during the PLA process, which resulted in narrower size distribution
and smaller size of nanoparticles.[34] In
addition, compared to chemical methods, the PLA process is simple
and chemically clean because it does not require postprocessing steps.[35] Therefore, the PLA is a potential method for
the synthesis of FGQDs.Here, we report a one-step strategy
to fabricate FGQDs by PLA process
using PPy both as a precursor (i.e., amine N) and surfactant. The
effect of surface passivation using PPy during the PLA process enables
narrower size distribution and smaller size of the FGQDs. X-ray photoelectron
spectroscopy (XPS) revealed that functionalized GQDs doped with amine
N can be achieved by the addition of PPy. In addition to these features
of the prepared FGQDs, we have also demonstrated highly sensitive
and selective fluorescence of the FGQDs for the detection of Fe3+ ions.
Results and Discussion
Figure shows the
transmission electron microscopy (TEM) and high-resolution TEM (HR-TEM)
images of the pristine GQDs (GQDs, Figure a,e), FGQDs with 0.5 mol % PPy (F0.5GQDs, Figure b,f), 1.0 mol % PPy
(F1.0GQDs, Figure c,g), and 1.5 mol % PPy (F1.5GQDs, Figure d,h). Compared to GQDs, the FGQDs exhibited
narrower size distributions and smaller sizes, as shown in Figures a–d and S1. The size distribution of the GQDs and the
three types of FGQDs were fitted by a Gaussian curve with a 95% confidence
interval. Average diameters of 5.0 ± 1.5 and 3.5 ± 0.5 nm
were obtained for the GQDs and the three types of FGQDs, respectively,
by counting more than 200 of the GQDs. This indicates that the particle
size distribution of the GQDs can be controlled by the addition of
PPy as a surfactant. Figure e–h shows the HR-TEM images of the GQDs and the three
types of FGQDs. According to the fast Fourier transform (FFT) patterns
(left insets, Figure e–h), it is clear that the GQDs and three types of FGQDs are
crystallized in the pristine graphene structure. In addition, the
right insets of Figure e–h show a lattice spacing of approximately 0.24 nm, which
is in good agreement with the (1120) lattice planes of graphene.[24,25] The atomic force microscopy (AFM) results are shown in Figure S2. Statistical analysis revealed that
more than 93% of the GQDs and three types of FGQDs have a thickness
of less than 1.9 nm, corresponding to three to four graphene layers.
This result indicates that the pristine GQDs and three types of FGQDs
have a few layers, which is similar to that reported in previous studies.[24,29]
Figure 1
TEM
images of GQDs (a), F0.5-GQDs (b), F1.0-GQDs (c), and F1.5-GQDs
(d). HR-TEM images of GQDs (e), F0.5-GQDs (f), F1.0-GQDs (g), and
F1.5-GQDs (h). Corresponding fast Fourier transformation (FFT) patterns
(left insets). Lattice spacing of GQDs and the three types of FGQDs
(right insets)
TEM
images of GQDs (a), F0.5-GQDs (b), F1.0-GQDs (c), and F1.5-GQDs
(d). HR-TEM images of GQDs (e), F0.5-GQDs (f), F1.0-GQDs (g), and
F1.5-GQDs (h). Corresponding fast Fourier transformation (FFT) patterns
(left insets). Lattice spacing of GQDs and the three types of FGQDs
(right insets)We investigated the chemical composition
of the three types of
FGQDs using X-ray photoelectron spectroscopy (XPS). Figure a shows the C 1s peaks of the
three types of FGQDs. The carbon peak can be deconvoluted into four
peaks centered at 284.5, 285.7, 286.3, and 287.7 eV, which represent
C–C/C=C, hydroxyl, C–N/C=N, and carboxyl
groups, respectively. The N 1s spectra of the three types of FGQDs
exhibited three types of configurations for C–N bonding (pyridinic,
pyrrolic, and graphitic), as shown in Figure b.[31] In addition,
we confirmed that the amine N peak located at 399 eV was present in
the XPS profiles of the three types of FGQDs.[36] Furthermore, it was observed that as the PPy concentration was increased
from 0.5 to 1.5 mol %, the C–N/C=N and amine-N concentrations
also gradually increased. In other words, the above-mentioned functional
groups (i.e., C–N, amine-N) in the carbon structure are dependent
on the PPy concentration, which indicates that the tuning of the chemical
composition is controllable in FGQDs.
Figure 2
XPS profiles of the FGQDs (a) C1s and
(b) N1s peaks.
XPS profiles of the FGQDs (a) C1s and
(b) N1s peaks.A possible mechanism for the transformation
of graphite flakes
to the FGQDs is shown in Figure . Generally, when a pulse laser is injected into a
target (i.e., graphite flakes), extremely harsh environments, such
as high temperature and high pressure, are formed owing to multiphoton
absorption ionization.[35] Subsequently,
the plasma plume and cavitation bubble occur in the synthesis area
during the PLA process, which leads to partial decomposition of the
graphite flakes, ethanol, and PPy, resulting in C, H, O, and N precursors.[31] Finally, the formation of each precursor (C,
H, O, and N) occurs in the synthesis area because of their high surface
energy, resulting in the formation of FGQDs. In addition, the aggregation
of FGQDs may be suppressed by the addition of PPy owing to the effect
of surface passivation. Generally, PPy has a positive charge, whereas
FGQDs possess negative polarity because of the abundance of oxygen-rich
functional groups, such as hydroxyl and carboxyl groups, on the surface
of the FGQDs.[37,38] Thus, the PPy surrounds the FGQDs
and forms passivation layers, as shown in Figure . It is noted that the surface of FGQDs may
be locally passivated by PPy because of the ultrafast pressure and
temperature changes during the PLA process, which may not be sufficiently
passivated. These layers can suppress the aggregation of GQDs, resulting
in a narrower particle size distribution and smaller size. These results
are in good agreement with the HR-TEM images shown in Figure .
Figure 3
Schematic illustration
of the possible mechanism for the transformation
of graphite flakes to FGQDs by the PLA process.
Figure 4
Schematic
diagram showing the surface passivation of the PPy/GQDs
Schematic illustration
of the possible mechanism for the transformation
of graphite flakes to FGQDs by the PLA process.Schematic
diagram showing the surface passivation of the PPy/GQDsThe optical properties of the GQDs and three types of FGQDs
were
investigated by photoluminescence (PL), UV–visible (UV–vis),
and photoluminescence excitation (PLE) spectroscopy. Figure a shows the PL properties of
the GQDs and three types of FGQDs. The three types of FGQDs exhibited
stronger PL intensities than that of the GQDs, with quantum yields
(QYs) calculated at 0.8, 1.84, 2.34, and 1.52% for the GQDs, F0.5GQDs,
F1.0GQDs, and F1.5GQDs, respectively. The PL spectra showed that the
peak intensity gradually increased with an increase in the PPy concentration
up to 1.0 mol %. However, the peak intensity and QY decreased as the
PPy concentration exceeded 1.0 mol %. This phenomenon may be occurring
owing to the excessive heteroatoms (i.e., N in this work) blocking
the passivated surface defects.[39] In addition,
the three types of FGQDs showed excitation-dependent PL spectra similar
to that reported in previous studies (Figure S3).[32,40] The PLE spectra of the three types of FGQDs
are different from that of the GQDs, as shown in Figure b. The PLE spectra of FGQDs
exhibited two clear peaks at 260 and 360 nm, which implies that the
N-related group (e.g., amine N) leads to an enhanced electron density
in the intrinsic state of GQDs.[31] The UV–vis
spectra exhibit absorption bands at 210, 260, and ∼360 nm,
as shown in Figure c. Typically, the UV–vis absorption bands at 210 and 260 nm
are assigned to the π–π* transition of C–C/C=C
of the sp2 domain in the carbon structure, and the shoulder
peak at ∼360 nm corresponds to the n–π*
transition of C=O. Compared to GQDs, the three types of FGQDs
exhibited stronger UV–vis peaks at 210 and 260 nm (π–π*
transition), indicating the high density of the carbon framework formed.
In addition, the absorption site at ∼360 nm in the oxygen-containing
groups also increased after the incorporation of amine N, which may
be related to the n−π* transition of C=O and also
to the amine N group. Thus, the strong electron affinity and superior
optical properties of the FGQDs could be useful for the development
of metal-ion sensors.[19,20]
Figure 5
Optical properties of GQDs, F0.5-GQDs,
F1.0-GQDs, and F1.5-GQDs.
(a) PL properties under 360 nm excitation, (b) PLE spectrum, and (c)
UV–vis spectrum.
Optical properties of GQDs, F0.5-GQDs,
F1.0-GQDs, and F1.5-GQDs.
(a) PL properties under 360 nm excitation, (b) PLE spectrum, and (c)
UV–vis spectrum.To explore the fluorescence
sensing application of FGQDs, we performed
PL analysis in the presence of various biologically and environmentally
relevant metal ions (50 μM), such as Ni2+, Fe3+, K+, Al3+, Zn+2, Mn2+, Ag+, Cd2+, Ca2+, and Mg2+. The fluorescence intensity ratio of the FGQDs was analyzed
by adding various metal ions. According to Figure a, the PL intensity of F1.0GQDs showed the
strongest quenching effect in the presence of Fe3+ ions,
whereas negligible PL quenching was observed in the presence of the
other metal ions. Compared to the other cations, the electron-deficient
Fe3+ ions have a higher binding affinity toward electron-rich
groups and can easily interact with electron-donating groups such
as amino groups (e.g., amine N) on the surface of the FGQDs.[41] Additionally, the FGQDs showed narrower size
distributions and smaller particle sizes by surface passivation, which
provided abundant active sites.[21,36] Consequently, the adsorption
of Fe3+ ions onto the FGQDs was accelerated by both surface
passivation and functionalization effects, resulting in high fluorescence
quenching. The concentration-dependent fluorescence of F1.0GQDs with
different concentrations of Fe3+ ions was investigated
for the detection of the Fe3+ ions (Figure b). The PL intensity of the F1.0GQDs decreased
as the concentration of Fe3+ ions increased from 500 nM
to 50 μM. Compared to the GQDs and N-doped GQDs (without amine
N groups; see the Experimental Section), the
F1.0-GQDs showed more sensitivity toward the detection of the Fe3+ ions at a concentration of 5 μM, as shown in Figure c. Although the N
concentrations of the N-doped GQDs (4.1%) and F1.0GQDs (3.8%) were
similar, the limit of detection (LOD) was significantly reduced by
the incorporation of the amine N group (Figures , 6c, and S4 and S5). The LOD of the FGQDs is much lower
than the water quality standards (i.e., ∼5.3 μM) for
Fe3+ ions suggested by the World Health Organization (WHO).
The Fe3+ sensing properties of the FGQDs were compared
with those of the recently reported GQDs, as shown in Table . The FGQDs prepared in this
study showed superior Fe3+ detection performance and ultrafast
synthesis process compared to those of GQDs (Table ). Therefore, the FGQDs synthesized by the
PLA process with PPy could be suitable sensing materials with high
sensitivity and selectivity for the detection of Fe3+ ions.
Figure 6
(a) Fluorescence
intensity of aqueous F1.0-GQDs solution in the
presence of 50 μM concentration of the different metal ions
at λex = 360 nm. F0 and F are the fluorescence intensities of the F1.0-GQDs before
and after interaction with Fe3+ ions, respectively. (Insets:
Photographs of the aqueous FGQDs containing 50 μM of the different
metal ions in daylight (top) and under UV light (bottom, λex = 360 nm)). (b) Fluorescence spectra of the F1.0-GQDs with
different concentrations of Fe3+. (c) Dependence of (F0 – F)/F0 on Fe3+ concentration.
Table 1
Comparison of Fe3+ Sensing
Properties of the FGQDs with Those of Recently Reported GQDs
materials
technique
in detail
detection
limit (μM)
processing
time (h)
ref
FGQDs
PLA process using PPy precursors
0.5
<1 h
this work
GQDs
hydrothermal/modified hummer’s
method
1.1
>24 h
(42)
N-doped GQDs
ammonia through hydrothermal
method
1
> 24 h
(43)
GQDs
chemical oxidation
60
>26 h
(44)
N-doped
GQDs
microwave synthesis
100
>27 h
(45)
GQDs
electrochemical synthesis
7.22
>72 h
(46)
Graphitic
GQDs
electrochemical
synthesis
2
>96 h
(47)
N-doped GQDs
hydrothermal method
0.5
>12 h
(48)
N-doped/amino-functional
GQDs
chemical oxidation
0.5
>24 h
(21)
(a) Fluorescence
intensity of aqueous F1.0-GQDs solution in the
presence of 50 μM concentration of the different metal ions
at λex = 360 nm. F0 and F are the fluorescence intensities of the F1.0-GQDs before
and after interaction with Fe3+ ions, respectively. (Insets:
Photographs of the aqueous FGQDs containing 50 μM of the different
metal ions in daylight (top) and under UV light (bottom, λex = 360 nm)). (b) Fluorescence spectra of the F1.0-GQDs with
different concentrations of Fe3+. (c) Dependence of (F0 – F)/F0 on Fe3+ concentration.
Conclusions
In summary, we successfully
demonstrated that surface-passivated
and functionalized GQDs with amine N can be achieved via the PLA process
using PPy as both the precursor (amine N) and surfactant agent simultaneously.
The FGQDs showed smaller particle sizes and narrower size distributions
than those of the GQDs owing to the effect of surface passivation
produced by a surfactant (PPy). In addition, the XPS results revealed
that the FGQDs were functionalized by PPy, which led to the incorporation
of the amine N. Owing to the synergistic effect of surface passivation
and functionalization, the FGQDs demonstrated highly efficient and
sensitive detection ability toward Fe3+ ions with a low
LOD of 500 nM. We also proposed a possible mechanism for the formation
of the FGQDs based on the plasma plume, cavitation bubble model, and
polarity difference between the GQDs and PPy. We believe that our
strategy is a one-step method for surface passivation and functionalization
of GQDs by the PLA process, allowing successful practical applications,
particularly in the field of heavy-metal-ion sensing.
Experimental Section
Preparation of FGQDs and
N-Doped GQDs
Graphite flakes were purchased from HQ Graphene
(Groningen, The Netherlands),
while polypyrrole (PPy) and high-purity ethanol (>99.99%) were
purchased
from Sigma-Aldrich (St. Louis, Missouri). FGQDs were synthesized by
the facile PLA process from graphite flakes in high-purity ethanol
with PPy. Typically, 500 mg of graphite flakes were dispersed in 200
mL of high-purity ethanol and PPy with different concentrations (0,
0.5, 1.0, and 1.5 mol %). The pulsed laser ablation was injected into
the graphite solution for 30 min at room temperature (about 25–28
°C) in air using a Q-Switched Nd:YAG laser system. The graphite
solution was injected by a horizontal pulsed laser beam (355 nm wavelength
and third harmonic) at a repetition rate of 10 Hz. The pulse laser
width was 10 nm, and the ablation power was 1 J. After completion
of the PLA process, the FGQD suspension was dried overnight at 80
°C under vacuum condition. N-doped GQDs were also prepared by
the PLA process. Typically, 500 mg of graphite flakes and 1.5 mol
% diethylenetriamine (DETA) were dispersed in 200 mL of high-purity
ethanol. Thereafter, the same pulsed laser experimental conditions
as those set up for the synthesis of the FGQDs were employed.
Characterization
High-resolution
transmission electron microscopy (HR-TEM) images of the FGQD samples
were captured using a JEM-2100F transmission electron microscope equipped
with a field emission gun (200 kV; JEOL). XPS profiles were recorded
for both the samples using a VG ESCALAB 220i-XL system (Thermo Fisher
Scientific, Waltham). XPS and high-resolution scans were performed
at pass energies of 100 and 20 eV, respectively, and at an X-ray beam
size of approximately 100 μm. FGQD samples for XPS measurement
were prepared on a silicon substrate by the spin-coating method with
the rotation speed adjusted to 2000 rpm. The samples were dried overnight
in a vacuum oven at 80 °C prior to the measurements. Room-temperature
PL spectra were recorded using a PL spectrophotometer (FluoroMax Plus
fitted with 150 W xenon arc lamp, HORIBA, Kyoto, Japan) in the wavelength
range of 300–800 nm. The PL emission spectra were recorded
at excitation wavelengths of 400, 450, and 500 nm. The above experimental
details are as per our previously published work.[31]
Fe3+ Detection
All measurements
were prepared for FGQD solution with a concentration of 0.05 mg/ml
in phosphate-buffered saline (PBS) at pH = 7.4. All metal cations
(Ni2+, Fe3+, K+, Al3+,
Zn2+, Mn2+, Ag+, Cd2+,
Ca2+, Mg2+) dissolved in deionized water. These
solutions were mixed with 1 mL of GQD solution for 5 min, and then
the optical properties of the samples were investigated by photoluminescence
(PL) under 360 nm. The detection sensitivity for Fe3+ ion
was assessed by monitoring the PL intensity of FGQD solutions containing
different concentrations of Fe3+.
Authors: Shoujun Zhu; Qingnan Meng; Lei Wang; Junhu Zhang; Yubin Song; Han Jin; Kai Zhang; Hongchen Sun; Haiyu Wang; Bai Yang Journal: Angew Chem Int Ed Engl Date: 2013-02-28 Impact factor: 15.336
Authors: Sung Wook Mhin; Jeong Ho Ryu; Kang Min Kim; Gyeong Seon Park; Han Wool Ryu; Kwang Bo Shim; Takeshi Sasaki; Naoto Koshizaki Journal: Nanoscale Res Lett Date: 2009-05-15 Impact factor: 4.703