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Degradation of Graphene by Hydrogen Peroxide

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Graphene, the 2D carbon nanomaterial, is suitable for diverse applications, ranging from electronics and telecommunication, to energy and healthcare. Despite its tremendous technological and commercial prospects, its interactions with biological and environmental constituents still require thorough examination. Here, we report that pristine multilayered graphene degrades in the presence of the naturally occurring, ubiquitous compound hydrogen peroxide (H 2 O 2 ) at physiologically and environmentally relevant concentrations (1–10 000 × 10 −6 M ) at various time points (0–25 h).
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and >1 × 10
3 M cause necrosis.
[ 22 ] Thus, given the widespread
presence of H
2 O 2 in the body and environment, and the future
impact graphene may have on human health and environment,
systematic studies need to be performed to investigate the direct
chemical interaction between H
2 O 2 and graphene. As a fi rst
step, in this communication, we examine the effects of H
2 O 2
on multilayered pristine graphene at physiologically and envi-
ronmentally relevant concentrations (1–10 000 × 10
6 M ). [ 19,22,23 ]
Pristine multilayered graphene deposited on nickel wafer
(wafer size = 1 cm × 1 cm, Graphene Supermarket, Calverton,
NY, USA) or directly onto TEM grids was placed in petri dishes
and treated with H
2 O 2 solution at concentrations of 1 × 10
6 ,
100 × 10
6 , or 10 000 × 10
6 M ( n = 4 per group). Graphene incu-
bated with distilled water (DI) served as the control. As H
2 O 2
solutions gradually deteriorate,
[ 22 ] the solutions were aspirated
out every hour and exchanged with fresh solutions. The experi-
ments were terminated after 10 or 25 h. At these time points,
solutions were completely removed, and graphene substrates
were air-dried. Graphene samples before (time t = 0 h) and after
H
2 O 2 treatment (time t = 10 and 25 h) were examined with
transmission electron microscopy (TEM), atomic force micros-
copy (AFM), and confocal Raman spectroscopy (laser excitation
of 532 nm).
Figure 1 shows representative TEM images of graphene-
coated TEM grids incubated with various concentrations of
H
2 O 2 for 10 h. Figure 1 A shows the control graphene sheet
incubated with DI water with no holes or defects, and has
the basic hexagonal lattice of graphene, possessing 0.142 nm
carbon–carbon bond length, occupying 0.17 nm
2 area. [ 24 ]
Compared with the control group (Figure 1 A), graphene
with 1 × 10
6 M H 2 O 2 treatment after 5 h showed the pres-
ence of randomly distributed small holes as seen in Figure 1 B
(arrows point to few representative holes). The diameter dis-
tribution of holes on graphene was measured by analyzing
multiple ( n = 20) TEM images. Incubation of graphene with
1 × 10
6 M H 2 O 2 for 10 h resulted in the formation of holes
ranging from 1 to 15 nm diameter (representing an area
up to 175 nm
2 ). Thus, these visible holes indicate a “cluster
effect,” i.e., the holes, or defect sites are generated initially by
random attack of H
2 O 2 followed by progressive attraction of
more H
2 O 2 to destroy carbon–carbon bonds around the ini-
tial defect sites. This effect is dependent on the concentration
of H
2 O 2 , and enhanced by higher concentrations of H
2 O 2 .
Upon treatment with 100 × 10
6 M H 2 O 2 , formation of larger-
sized holes (10–15 nm) was observed (Figure 1 C). Addition-
ally, Figure 1 C also shows formation of lighter (few graphene
layers) and darker regions (multiple graphene layers) indi-
cating the degradation of multilayered graphene. Figure 1 D
shows graphene after incubation with 10 000 × 10
6 M H 2 O 2 .
Large-defect sites (10–30 nm) and few graphene layers were
observed corresponding to the degradation of majority of the
graphene sheets.
W. Xing, G. Lalwani, Prof. B. Sitharaman
Department of Biomedical Engineering
Stony Brook University
Stony Brook , New York 11794–5281, USA
E-mail: balaji.sitharaman@stonybrook.edu
Dr. I. Rusakova
Texas Center for Superconductivity
and Advanced Materials
University of Houston Science Center
Houston, Texas 77004–5002 , USA
DOI: 10.1002/ppsc.201300318
Degradation of Graphene by Hydrogen Peroxide
WeiLiang Xing , Gaurav Lalwani , Irene Rusakova , and Balaji Sitharaman *
Graphene, the 2D carbon nanomaterial, is suitable for diverse
applications, ranging from electronics and telecommunication,
to energy and healthcare. Despite its tremendous technological
and commercial prospects, its interactions with biological and
environmental constituents still require thorough examination.
Here, we report that pristine multilayered graphene degrades in
the presence of the naturally occurring, ubiquitous compound
hydrogen peroxide (H
2 O 2 ) at physiologically and environmen-
tally relevant concentrations (1–10 000 × 10
6 M ) at various time
points (0–25 h).
Graphene, a 2D sheet comprised of sp
2 -hybridized carbon
possessing exciting electrical, mechanical, thermal, and optical
properties,
[ 1 ] has been investigated as enabling components in
fuel cells,
[ 2,3 ] sensors, [ 2,4 ] photocatalysis, [ 5 ] electronics, [ 6 ] compos-
ites,
[ 7 ] electrical and optical biosensors,
[ 8 ] drug delivery,
[ 9 ] tissue
engineering,
[ 10,11 ] and imaging probes.
[ 12 ] Recent reports predict
that graphene may overtake carbon nanotubes in commercial
applications.
[ 13 ] The development of potential graphene-based
commercial technologies for applications in material and bio-
medical sciences has raised concerns about its short-term and
long-term effects on human health and the environment,
[ 14 ]
and leads to multiple investigations to assess and evaluate these
effects.
[ 15 ]
An important attribute to be examined while investigating
graphene's effect on human health and environment is its
bio- and environmental-degradation properties. Several studies
have investigated the biodegradation of carbon nanotubes,
[ 16,17 ]
wherein enzymes such as horseradish peroxidase (HRP) and
human myeloperoxidase (hMPO) were employed to catalyze
oxidative degradation of these nanomaterials. A recent study
has used a similar strategy on graphene oxide, and exploits the
catalytic activity of HRP enzyme.
[ 18 ] H 2 O 2 is a component of
this degradation process.
H 2 O 2 is a naturally occurring, ubiquitous compound and a
strong oxidizing agent, found in rain and surface water, and
biota.
[ 19,20 ] Its concentration in natural water sources has been
determined to be 1–7 × 10
3 M . [ 19,21 ] In normal living cells,
diverse cellular pathways synthesize H
2 O 2 in tightly regulated
concentrations varying between 1 × 10
9 and 700 × 10
9 M . H 2 O 2
steady-state concentrations >1 × 10
6 M cause oxidative stress,
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AFM was performed (using a previously described proce-
dure)
[ 11 ] to assess the surface topography of graphene sheets
before and after H
2 O 2 treatment. Samples were incubated
with DI water and 10 000 × 10
6 M H 2 O 2 for 25 h. Pristine
graphene sheets ( Figure 2 A,C,E) appeared smooth, without
any topographical defects. Randomly distributed holes in
graphene sheets were observed after incubation with H
2 O 2
(Figure 2 B,D,E). The diameter of holes ranged from 5.3 to
13.5 nm. Compared with the height of single graphene sheet
(0.34 nm),
[ 18 ] the depth of the holes (9.4–13.5 nm, inset
Figure 2 D) was greater by several folds suggesting the attack of
H
2 O 2 on the inner layers of graphene. Once superfi cial defect
sites are generated, H
2 O 2 may pass through these defect sites
attacking the underlying C–C bonds, and accelerating the deg-
radation of graphene at higher concentrations of H
2 O 2 .
Raman spectroscopy was used to characterize the graphene
samples before and after treatment with H
2 O 2 at every time
point ( Figure 3 ). The ratio of D-band and G-band intensities
( I D / I G ) at all-time points before and after H
2 O 2 treatment are tab-
ulated in Table 1 . The D band indicating the degree of disorder
in sp
2 -hydridized carbon system was observed between 1335 and
1350 cm
1 , and the G band, indicating stretching of graphitic
carbon, was observed between 1570 and 1580 cm
1 . [ 25 ] Table 1
shows decrease in the intensity of D and G bands for all groups
treated with various concentration of H
2 O 2 for 25 h, suggesting
a gradual structural degradation of graphene.
[ 26 ] For groups
treated with 1 × 10
6 and 100 × 10
6 M H 2 O 2 , the I D / I G ratio
increased within 10 h of incubation, and decreased at later time
points. Increase in I D / I G ratio during initial time points can be
attributed to increase in the number of defects on graphene, and
is consistent with previous reports on enzymatic degradation of
graphene.
[ 17,18,26 ] The decrease in I D / I G ratio at later time points
can be attributed to disintegration of the multiple layers of gra-
phene due to progressive increase in the defect sizes, exposing
the underlying pristine graphene layers.
[ 26 ] The Raman spectra
from these underlying pristine graphene layers would have an
intense G band, reducing the I D / I G ratio. For the group treated
with 10 000 × 10
6 M H 2 O 2 , I D / I G ratio progressively decreased
at all time points, unlike 1 × 10
6 and 100 × 10
6 M H 2 O 2 treat-
ment groups, which showed an initial increase in the I D / I G ratio
within the fi rst 10 h. After 25 h, both D and G bands almost dis-
appeared for the 10 000 × 10
6 M H 2 O 2 treatment group.
G band, a characteristic of layered graphene, was observed
at 2750 cm
1 for all treatment groups.
[ 27 ] The intensity of
G band increased during the fi rst 10 h of H
2 O 2 treatment,
decreased, and became negligible at later time points. The
G band became progressively narrow and down shifted at
increasing time points. Several reports have shown the rela-
tion of G band with the number of layers of graphene in which
wider, higher intensity, and an upshift of G band corresponds
to increasing number of graphene layers.
[ 25,27,28 ] In this study,
as the degradation progressed, decrease in the width, intensity,
and downshift of G band corresponds to progressive, layer-
by-layer degradation of graphene. A layer-by-layer degradation
phenomenon was observed during degradation of multiwalled
carbon nanotubes by HRP.
[ 17,29 ] Furthermore, differences in G
band peak intensity and width between various H
2 O 2 treatment
groups imply the dependence of graphene degradation rate on
Figure 1. Representative TEM images of multilayered graphene treated with A) deionized water, B) 1 × 10
6 M H 2 O 2 , C) 100 × 10
6 M H 2 O 2 , and
D) 10 000 × 10
6 M H 2 O 2 for 10 h. Arrows in (B) indicate the formation of holes on graphene sheets, and arrows in (C) indicate the formation of lighter
(few graphene layers) and darker regions (multiple graphene layers) suggesting the degradation of multilayered graphene. It should be noted that the
arrows in (B–D) only point to a few representative holes.
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the concentration of hydrogen peroxide, i.e., graphene treated
with 1 × 10
6 M H 2 O 2 may degrade at a slower rate compared to
treatment with 10 000 × 10
6 M H 2 O 2 .
The above results taken together clearly indicate the deg-
radation of multilayered pristine graphene at a wide range of
H
2 O 2 concentrations found in living systems and environment.
Previous studies report that metal ions such as nickel (Ni), iron
(Fe), and copper (Cu) can catalyze the degradation of H
2 O 2 to
form reactive hydroxyl radicals via the Haber–Weiss reaction.
[ 30 ]
Ni, Fe, or Cu-based substrates or catalysts are used for graphene
Figure 2. Representative AFM images of multilayered graphene on Ni wafer. A,C,E) are topographical scans of pristine graphene samples (incubated
with DI water) and B,D,E) are graphene after 25 h of H
2 O 2 treatment (10 000 × 10
6 M). Insets in images C and D correspond to the line height profi le.
Images E and F are 3D representations of images C and D, respectively.
Part. Part. Syst. Charact. 2014, 31, 745–750
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synthesis using the chemical vapor deposition method.
[ 31 ] Thus,
in this study, the presence of trace amounts of Ni used during
the CVD synthesis of the graphene may be catalyzing the deg-
radation of graphene during H
2 O 2 treatment. The results also
indicate that rate of degradation of graphene is dependent
on H
2 O 2 exposure concentration; increase in concentration
accelerates graphene’s degradation. The visible holes indicate a
“cluster effect,” i.e., the holes, or defect sites are generated ini-
tially by random attack of H
2 O 2 followed by progressive attrac-
tion of more H
2 O 2 to destroy the carbon–carbon bond around
initial defect sites. Furthermore, reaction temperature may also
infl uence the degradation rate. Additional studies are necessary
Figure 3. Representative Raman spectra of graphene treated with A) 10 000 × 10
6 M H 2 O 2 , B) 100 × 10
6 M H 2 O 2 , and C) 1 × 10
6 M H 2 O 2 for a period
of 0, 10, and 25 h. Decrease in the D and G band intensities can be observed after 25 h. Figures D–F show the corresponding I D / I G intensity ratio at
every time point .
Part. Part. Syst. Charact. 2014, 31, 745–750
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Table 1. I D / I G ratio of multilayered graphene samples before and after
incubation with H
2 O 2 for 25 h.
H
2 O 2 incubation
concentration
I D / I G
ratio
Before incubation After incubation (25 h)
10 000 × 10
6 M 0.2312 0.1706
100 × 10
6 M 0.2312 0.1519
1 × 10
6 M 0.2312 0.1499
Received: September 25, 2013
Revised: December 12, 2013
Published online: February 24, 2014
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2 O 2 -
mediated degradation of graphene (interplay of H
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enzymes such as HRP and hMPO on the degradation of single-
and multiwalled carbon nanotubes.
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to strong acids and oxidants prior to enzymatic degradation.
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these bio-organisms but is ubiquitous in eukaryotic cells,
[ 22 ]
and natural resources (fresh and sea water).
[ 32 ] Our results
strongly suggest that alternative degradation mechanism in the
presence H
2 O 2 at physiologically and environmentally relevant
concentrations (1–10 000 × 10
6 M ) could initiate and degrade
single- and multilayered pristine graphene. The limitations of
the above study are: (1) while concentrations of H
2 O 2 mimic
those found in physiological and environmental conditions, the
controlled experimental conditions allow all the available H
2 O 2
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2 O 2 were
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layered sheets of pristine graphene. Thus, this study only pro-
vides insights into the surface degradation effect of H
2 O 2 . Bulk
degradation on macroscopic amount of graphene aggregates in
the presence of H
2 O 2 still needs to be determined.
Acknowledgements
This work was supported by the National Institutes of Health (grants no.
1DP2OD007394–01).
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Part. Part. Syst. Charact. 2014, 31, 745–750
... Previous research indicated that environmentally relevant concentrations of GFNs are in the range of 0.001 to more than 10 mgL − 1 (Ali et al., 2023;Pires et al., 2022;Xing et al., 2014). To the best of the authors' knowledge, no study has evaluated the effects of all three GFNs together at an environmentally relevant dose, despite prior research demonstrating the harmful effects of each GFNs individually at a variety of concentrations. ...
... Several studies have been performed on removing carbon nanomaterials from the environment. The degradation of carbon nanomaterials, such as photodegradation in the presence of UV light, and chemical degradation in the presence of chemicals such as hydrogen peroxide, hypochlorous acid, and Fenton [21][22][23] . The biodegradation of carbon nanomaterials is another considerable removal mechanism. ...
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... 3D graphene materials exhibit longterm stability in ambient air and maintain their properties over time. Given that these materials are primarily composed of graphene, they share comparable sensitivities to external factors as their 2D graphene counterparts [29][30][31][32]. ...
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... When these highly oxidative species (OH˙, H˙, OOH˙) are produced in electrochemical systems, either electrochemically or chemically, they immediately affect the catalysts, electrodes, -derived radicals, which did not provide sufficient information regarding the chemical structural changes in the material. 44 It is evident that a substantial knowledge gap exists on the H 2 O 2 -driven performance changes and material degradation process of graphene-based catalysts for electrochemical systems. ...
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... Besides toxicity, the rate at which graphene degrades in vivo is of paramount importance. Given the widespread presence of H 2 O 2 , a strong oxidizing agent, in the body and environment, the rate of degradation of graphene was found to depend on H 2 O 2 concentration [69]. In addition, holes or defect sites were first generated by random attack of H 2 O 2 , followed by a progressive destruction of carboncarbon bonds of graphene around the initial defect sites. ...
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... Given the toxicity of accumulated graphene, it is important for graphene nanoparticles to be excreted from the body. Hydrolytic and enzymatic degradation with enzymes such as myeloperoxidase, horseradish peroxidase, and lignin peroxidase have been found to be effective in degrading GO, especially in the presence of low concentrations of hydrogen peroxide [197][198][199][200]. Neutrophils and macrophages have also been reported to cause the degradation of graphene, which indicates the importance of the immune system in mediating the effects of graphene in the body. ...
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This study investigated the degradation of graphene oxide (GO) by the white-rot fungus Phanerochaete chrysosporium . Axenic fungal suspensions were inoculated in malt extract glucose medium enriched with various concentrations of...
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In this work, graphene nanoribbons and nanoplatelets were investigated as contrast agents for photoacoustic and thermoacoustic tomography (PAT and TAT). We show that oxidized single- and multi-walled graphene oxide nanoribbons (O-SWGNRs, O-MWGNRs) exhibit approximately 5–10 fold signal enhancement for PAT in comparison to blood at the wavelength of 755 nm, and approximately 10–28% signal enhancement for TAT in comparison to deionized (DI) water at 3 GHz. Oxidized graphite microparticles (O-GMPs) and exfoliated graphene oxide nanoplatelets (O-GNPs) show no significant signal enhancement for PAT, and approximately 12–29% signal enhancement for TAT. These results indicate that O-GNRs show promise as multi-modal PAT and TAT contrast agents, and that O-GNPs are suitable contrast agents for TAT.
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We report the synthesis and characterization of a novel carbon nanostructure-based magnetic resonance imaging contrast agent (MRI CA); graphene nanoplatelets intercalated with manganese (Mn(2+)) ions, functionalized with dextran (GNP-Dex); and the in vitro assessment of its essential preclinical physicochemical properties: osmolality, viscosity, partition coefficient, protein binding, thermostability, histamine release, and relaxivity. The results indicate that, at concentrations between 0.1 and 100.0 mg/mL, the GNP-Dex formulations are hydrophilic, highly soluble, and stable in deionized water, as well as iso-osmolar (upon addition of mannitol) and iso-viscous to blood. At potential steady-state equilibrium concentrations in blood (0.1-10.0 mg/mL), the thermostability, protein-binding, and histamine-release studies indicate that the GNP-Dex formulations are thermally stable (with no Mn(2+) ion dissociation), do not allow non-specific protein adsorption, and elicit negligible allergic response. The r 1 relaxivity of GNP-Dex was 92 mM(-1)s(-1) (per-Mn(2+) ion, 22 MHz proton Larmor frequency); ~20- to 30-fold greater than that of clinical gadolinium (Gd(3+))- and Mn(2+)-based MRI CAs. The results open avenues for preclinical in vivo safety and efficacy studies with GNP-Dex toward its development as a clinical MRI CA.
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This study investigates the efficacy of two-dimensional (2D) carbon and inorganic nanostructures as reinforcing agents for cross-linked composites of the biodegradable and biocompatible polymer polypropylene fumarate (PPF) as a function of nanostructure concentration. PPF composites were reinforced using various 2D nanostructures: single- and multiwalled graphene oxide nanoribbons (SWGONRs, MWGONRs), graphene oxide nanoplatelets (GONPs), and molybdenum disulfide nanoplatelets (MSNPs) at 0.01-0.2 weight% concentrations. Cross-linked PPF was used as the baseline control, and PPF composites reinforced with single- or multiwalled carbon nanotubes (SWCNTs, MWCNTs) were used as positive controls. Compression and flexural testing show a significant enhancement (i.e., compressive modulus = 35-108%, compressive yield strength = 26-93%, flexural modulus = 15-53%, and flexural yield strength = 101-262% greater than the baseline control) in the mechanical properties of the 2D-reinforced PPF nanocomposites. MSNP nanocomposites consistently showed the highest values among the experimental or control groups in all the mechanical measurements. In general, the inorganic nanoparticle MSNP showed a better or equivalent mechanical reinforcement compared to carbon nanomaterials, and 2D nanostructures (GONPs, MSNPs) are better reinforcing agents compared to one-dimensional (1D) nanostructures (e.g., SWCNTs). The results also indicated that the extent of mechanical reinforcement is closely dependent on the nanostructure morphology and follows the trend nanoplatelets > nanoribbons > nanotubes. Transmission electron microscopy of the cross-linked nanocomposites indicated good dispersion of nanomaterials in the polymer matrix without the use of a surfactant. The sol-fraction analysis showed significant changes in the polymer cross-linking in the presence of MSNP (0.01-0.2 wt %) and higher loading concentrations of GONP and MWGONR (0.1-0.2 wt %). The analysis of surface area and aspect ratio of the nanostructures taken together with the above results indicated differences in nanostructure architecture (2D vs 1D nanostructures), and the chemical compositions (inorganic vs carbon nanostructures), number of functional groups, and structural defects for the 2D nanostructures may be key properties that affect the mechanical properties of 2D nanostructure-reinforced PPF nanocomposites and the reason for the enhanced mechanical properties compared to the controls.
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The latest addition to the nanocarbon family, graphene, has been proclaimed to be the material of the century. Its peculiar band structure, extraordinary thermal and electronic conductance and room temperature quantum Hall effect have all been used for various applications in diverse fields ranging from catalysis to electronics. The difficulty to synthesize graphene in bulk quantities was a limiting factor of it being utilized in several fields. Advent of chemical processes and self-assembly approaches for the synthesis of graphene analogues have opened-up new avenues for graphene based materials. The high surface area and rich abundance of functional groups present make chemically synthesized graphene (generally known as graphene oxide (GO) and reduced graphene oxide (RGO) or chemically converted graphene) an attracting candidate in biotechnology and environmental remediation. By functionalizing graphene with specific molecules, the properties of graphene can be tuned to suite applications such as sensing, drug delivery or cellular imaging. Graphene with its high surface area can act as a good adsorbent for pollutant removal. Graphene either alone or in combination with other materials can be used for the degradation or removal of a large variety of contaminants through several methods. In this review some of the relevant efforts undertaken to utilize graphene in biology, sensing and water purification are described. Most recent efforts have been given precedence over older works, although certain specific important examples of the past are also mentioned.
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The Raman spectra of crystalline graphite, graphite damaged by ion-etching, and structurally disordered pyrolytic and glassy carbons were examined as a function of excitation wavelength λ over the range 488.0 to 647.1 nm. The bands located at 1360, 2720 and 2950 cm 1 with λ = 488.0 nm undergo a progressive red-shift as λ increases, while the positions of the other major bands (1580 and 1620 cm 1) are invariant. The significance of these observations is briefly discussed.
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Herein, a new nanocomposite consisting of up-conversion (UC) material (YF3:Yb3+,Tm3+), TiO2 (P25) and graphene (GR) has been prepared and shown to be an advanced sunlight activated photocatalyst. During the facile hydrothermal method, the reduction of graphene oxide and loading of YF3:Yb3+,Tm3+ and P25 were achieved simultaneously, and the functionalities of each part were integrated together. The as-prepared ternary UC–P25–GR nanocomposite photocatalyst exhibited great adsorptivity of dyes, a significantly extended light absorption range, efficient charge separation properties and superior durability. Indeed, the photocatalytic activity of this novel ternary nanocomposite under sunlight was improved compared with those of P25–GR nanocomposites and bare P25. Overall, this work could provide new insights into the fabrication of ternary composites as high performance photocatalysts and facilitate their application in environmental protection issues.
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Development of biocompatible surface coating is critical to engineer various functional nanomaterials for biomedical applications. Here, we present a new surface chemistry of graphene by covalently conjugating graphene oxide (GO) with dextran (DEX), a biocompatible polymer widely used for surface coating of biomaterials. Compared with GO, the graphene–dextran (GO–DEX) conjugate shows reduced sheet sizes, increased thickness and significantly improved stability in physiological solutions. Cellular experiments uncover that DEX coating on GO offers remarkably reduced cell toxicity. We further label GO–DEX with a radioactive isotope, 125I, for in vivo tracking in animal studies. It is found that GO–DEX accumulates in the reticuloendothelial system (RES) including liver and spleen after intravenous injection, and importantly, shows obvious clearance from the mouse body within a week without causing noticeable short-term toxicity to the treated animals. Our results suggest that this DEX coating method on GO may potentially be useful to the further development of novel graphene-based bioconjugates for various biomedical applications.
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Graphene oxide (GO) and reduced graphene oxide (RGO) have important applications in the development of new electrode and photocatalyst architectures. Gold nanoparticles (Au NP) are employed as catalyst to assist generation of hydroxyl radicals (OH•) in a UV-peroxide system and further promote the oxidation of RGO. The oxidation of RGO is marked by pores and wrinkles within the 2-D network. Nanosecond flash photolysis used in conjunction with competition kinetics to elucidate the oxidative mechanism and calculate rate constants for the Au NP-catalyzed and direct reaction between RGO and OH• radicals. Through Au NP-mediated oxidation reaction it is possible to tune the properties of RGO through the degree of oxidation and/or functional group selectivity in addition to the nanoporous and wrinkle facets. The ability of Au NP to catalyze the photolytic decomposition of H2O2 as well as the OH• radical-induced oxidation of RGO raises new issues concerning graphene stability in energy conversion and storage (photocatalysis, fuel cells, Li-ion batteries, etc). Understanding RGO oxidation by free radicals will aid in maintaining the long-term stability of RGO-based functional composites where intimate contact with radical species is inevitable.
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Graphene quantum dots offer a new approach to quantum nanoelectronics.