Subscriber access provided by UNIVERSITY OF TOLEDO LIBRARIES
Article
Thermal modification of molybdenum disulfide surface for tremendous improvement of Hg2+ adsorption from aqueous solution Feifei Jia, Chang Liu, Bingqiao Yang, Xian Zhang, Hao Yi, Jiaming Ni, and Shaoxian Song ACS Sustainable Chem. Eng., Just Accepted Manuscript • DOI: 10.1021/ acssuschemeng.8b01412 • Publication Date (Web): 21 May 2018 Downloaded from http://pubs.acs.org on May 22, 2018
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
1
Thermal modification of molybdenum disulfide
2
surface for tremendous improvement of Hg2+
3
adsorption from aqueous solution
4 5
Feifei Jia1, Chang Liu1, Bingqiao Yang2, Xian Zhang1, Hao Yi1, Jiaming Ni1,
6
Shaoxian Song1,3,4 ∗
7 8
1
9
Technology, Luoshi Road 122, Wuhan, Hubei, 430070, China
School of Resources and Environmental Engineering, Wuhan University of
10
2
11
Wuhan, Hubei, 430073, China
12
3
13
University of Technology, Luoshi Road 122, Wuhan, Hubei, 430070, China
14
4
15
Vanadium Resources, Wuhan University of Technology, Luoshi Road 122, Wuhan,
16
Hubei, 430070, China
Xingfa Mining School, Wuhan Institute of Technology, Xiongchu Avenue 693,
Hubei Key Laboratory of Mineral Resources Processing and Environment, Wuhan
Hubei Provincial Collaborative Innovation Center for High Efficient Utilization of
17
∗
Corresponding author. Tel: +862787212127. E-mail:
[email protected] ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
18
Abstract
19
The adsorption of Hg2+ on thermally modified molybdenum disulfide was
20
explored in this work. The XPS and HRTEM results revealed that thermal treatment
21
led to partial oxidation of MoS2 to MoO3 and a creation of edge defects on the surface
22
of molybdenum disulfide. The DFT calculation indicated that the oxidative etchings
23
were terminated with oxygen atoms, and both the vacancy and perfect surface could
24
be oxidized during thermal treatment. The batch tests indicated that thermal treatment
25
enabled the surface of molybdenum disulfide highly reactive as Hg2+ adsorbent. The
26
adsorption rate and capacity on 500oC heated molybdenum disulfide was 17.6 times
27
faster and 11 folds higher compared to that of molybdenum disulfide without thermal
28
modification. The tremendous enhancement on Hg2+ adsorption was significantly
29
related to the oxidation of molybdenum disulfide and the increase of atom activity on
30
the surface. The oxidation could provide O active sites to strongly adsorb Hg through
31
the formation of Hg-O complex, while the increased activity greatly improved the
32
affinity of Hg to molybdenum disulfide. This work suggests that thermal modification
33
is an efficient method to increase the removal capacity of heavy metals on
34
molybdenum disulfide.
35
Keywords: molybdenum disulfide; Hg2+ adsorption; thermal modification; oxidation
36 37
Introduction
38
Molybdenum disulfide (MoS2), a typical layered transition metal dichalcogenite,
39
has attracted tremendous research interest in the past few years due to its prominent
ACS Paragon Plus Environment
Page 2 of 31
Page 3 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
40
mechanical and optoelectronic properties that completely different from its bulk
41
molybdenite phase.1 By virtue of the direct band gap and high mobility value,
42
molybdenum disulfide possesses enormous potentials in electronics, chemical sensors,
43
biomedical, catalysis, and energy-related fields.2–5 Furthermore, the latest researches
44
show that molybdenum disulfide has substantial potentials in environmental
45
applications because of its huge surface-to-volume ratio and strong adsorption
46
capacity.6–8
47
Among the advances of molybdenum disulfide in environmental fields, the
48
application in contaminant adsorption, especially the removal of heavy metals from
49
water, is critically discussed.9 It was reported that the Hg2+ adsorption capacity of
50
molybdenum disulfide resulted from a natural molybdenite was 305 mg/g.10 The
51
porous MoS2 aerogel exhibited a 1527 mg/g Hg2+ uptake capacity and decreased the
52
Hg2+ level in contaminated water from 10 mg/L to 0.11 µg/L within a few minutes.11
53
Molybdenum disulfide nanosheets with widened interlayer spacing reached an
54
extremely high Hg2+ adsorption capacity (2587 mg/g), which was even higher than the
55
theoretically predicted value (2506 mg/g) on the assumption of a 1:1 stoichiometric
56
S/Hg ratio, as well as fast adsorption kinetics and excellent Hg2+ selectivity.12 In
57
addition, molybdenum disulfide also presents enormous advantages as adsorbent for
58
the removal of other heavy metal ions such as Pb2+, Co2+, Cd2+.8,13,14 The superb
59
uptake capacity of molybdenum disulfide to heavy metals was mainly attributed to the
60
strong complexation between the exposed (001) planes of molybdenum disulfide and
61
the heavy metal ions.
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
62
Our previous work demonstrated that the (001) basal surface of natural
63
molybdenum disulfide were chemically reactive for the heavy metals, nonetheless it
64
exhibited far lower Hg2+ uptake capacity than the synthesized molybdenum
65
disulfide.15 In my view, the surface property of molybdenum disulfide might be of
66
significant importance in the adsorption of Hg2+, however, no profound investigation
67
has concerned on this topic.
68
In this work, an attempt was made to study the role of surface property of
69
molybdenum disulfide in its Hg2+ adsorption. The surface of molybdenum disulfide
70
was modified through a simple thermal treatment. The surface property after thermal
71
treatment was studied by transmission electron microscopy (TEM), X-ray
72
photoelectron spectroscopy (XPS), Raman spectroscopy, as well as a theoretical
73
density functional theory (DFT) calculation. The Hg2+ adsorption performance was
74
investigated through AFM observation, adsorption thermodynamics and kinetics
75
experiments. The mechanism of the enhanced Hg2+ adsorption on molybdenum
76
disulfide was interpreted through XPS determination. The object was to obtain a clear
77
understanding in the effect, as well as the influence mechanism, of surface property of
78
molybdenum disulfide on its adsorption to heavy metals, furthermore to give a precise
79
guidance for the preparation of molybdenum disulfide as superb adsorbent.
80 81
Experimental section
82
Materials
83
Natural molybdenite collected from the Wuzhou mine, Guangxi province, China,
ACS Paragon Plus Environment
Page 4 of 31
Page 5 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
84
was used in this work for the preparation of molybdenum disulfide. X-ray diffraction
85
pattern (XRD) indicated the high purity of the sample (shown in Fig. S1). The
86
thermogravimetry analysis (TGA) and differential thermal analysis (DTA) of
87
molybdenite were given in Fig. S2. At temperature below 460oC, no obvious weight
88
loss was observed, indicating no obvious change of composition. After that, the
89
weight decreased with the increase of temperature and reached a plateau at around
90
680oC, during which the sharp decrease occurred at 550oC. The approximate 10% of
91
the weight loss in this range might be ascribed to the oxidation of MoS2. The dramatic
92
decrease of the weight loss at temperature higher than 750oC was probably resulted
93
from the composition of sample.
94
Mercuric nitrate (Hg(NO3)2·H2O) purchased from Shanghai Zhanyun Chemical
95
Co., Ltd (China), nitric acid and sodium hydroxide purchased from Sinopharm
96
Chemical Reagent Co., Ltd (China) were of analytical grade. Milli-Q water with a
97
resistivity of 18.2 MΩ·cm was used in all the experiments.
98 99 100
Methods Preparation of molybdenum disulfide nanosheets
101
Molybdenum disulfide nanosheets were prepared with an ultrasound assisted
102
electrochemical exfoliation method, during which bulk molybdenite was positioned as
103
a cathode electrode. The details of the preparation procedure were given in our
104
previous work.8 The obtained molybdenum disulfide nanosheet was named as M in
105
this study.
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
106
Page 6 of 31
Thermal modification of molybdenum disulfide
107
The surface property of molybdenum disulfide was modified through a simple
108
thermal treatment. 10 grams of molybdenum disulfide nanosheets were first placed in
109
an agate crucible, followed by putting the crucible in a muffle furnace (Vulcan 3-550).
110
The samples were thermally treated from room temperature to a given value (400oC
111
and 500oC) with a heating rate of 10oC/min and the set temperature was kept constant
112
for 2 h. After cooling down, the samples were washed with deionized water and
113
filtrated
114
(4,5-dihydroxy-1,3-benzenedisulfonic acid disodium salt). Molybdenum disulfide
115
nanosheets subsequent to 400oC and 500oC thermal treatment were named as M-400
116
and M-500, respectively.
until
no
MoO42-
was
detected
in
the
filtrate
with
tiron
117 118
AFM study on Hg2+ adsorption on bulk molybdenum disulfide
119
One drop of 100 µg/L Hg2+ solution prepared with Hg(NO3)2·H2O and deionized
120
water was firstly placed on the surface of bulk molybdenum disulfide with and
121
without thermal treatment for a desired time. After that the surface was washed with
122
deionized water for several times to remove the un-adsorbed Hg2+ and dried in air.
123
The surface morphology was then observed using AFM. Subsequently, the sample
124
was further adsorbed with Hg2+ and the surface morphology of the sample was
125
recorded with AFM.
126 127
Routine experimental of Hg2+ adsorption on molybdenum disulfide nanosheets
ACS Paragon Plus Environment
Page 7 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
128
Batch experiments were conducted to study the adsorption of Hg2+ on
129
molybdenum disulfide before and after thermal treatment. Firstly, a given amount of
130
adsorbent was added into Hg(NO3)2·H2O solution with desired Hg2+ concentration
131
and pH. The suspension was then shaken in a water bath shaker for predetermined
132
time intervals at room temperature and shaking rate of 150 rpm. After that, 5 ml
133
suspension was filtered with 0.22 µm filter membrane, during which the first 2 ml
134
filtrate was discarded and another 3 ml was collected for the chemical analysis of
135
Hg2+. For the adsorption kinetic experiment, 50 mg molybdenum disulfide nanosheets
136
were added into 1 L 50 mg/L Hg2+ solution and adsorbed for different time intervals
137
(0-400 min). For the adsorption isotherm experiments, 10 mg of the adsorbent was
138
added into 150 ml Hg2+ solution with concentration of 25-200 mg/L. The pH of
139
solutions were maintained at 6.0±0.1 in the adsorption kinetics and isotherm
140
experiments. While, 10 mg of the adsorbent was added into 160 ml 50 mg/L Hg2+
141
solution with pH ranging from 1 to 6 when studying the pH effect on the adsorption.
142
Mercury adsorption capacity is estimated by the following expression:
143
q = V0 (C0 - C) / m
(1)
144
where q is the adsorption capacity of the adsorbent, mg/g; C0 and C represent the Hg2+
145
concentration before and after adsorption, respectively, mg/L; V0 is the solution
146
volume, L; m is the mass of the adsorbent, g.
147 148 149
Computational methods The DFT calculations were used to interpret the defect formation on MoS2, as
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 8 of 31
150
well as the stable structure of defective MoS2. The MoS2 structures were subjected to
151
periodic boundary condition with a supercell geometry. 2.0 nm vacuum space was
152
constructed to eliminate the interaction between the adjacent MoS2 layers. All the
153
computations were performed using all-electron DFT with a double numerical basis
154
set plus dynamic polarization function (DNP), as implemented in the Dmol3 module.
155
The Perdew-Burke-Ernzerhof (PBE) of Generalized Gradient Approximation (GGA)
156
was applied as exchange correlation function. In relaxation, a Monkhorst-Pack k-point
157
mesh of 2×1×1 was chosen for the structure optimization. The adsorption energy,
158
Ead, of O2 adsorbed on molybdenum disulfide, is defined as
Ead = EM +O2 − EM − EO2
159
(2)
160
where EM+O is the total energy of molybdenum disulfide with adsorbed O2, EM and
161
EO correspond to the energy of molybdenum disulfide and of the isolated O2 molecule,
162
respectively. The oxidation energy is described by the equation as follows:16,17
2
2
∆E = Eoxidized − E pristine − xµo + yµs
163
(3)
164
where Eoxidized and Epristine are the energies of the oxidized and pristine MoS2; µo and µs
165
are the reference chemical potentials of O and S atoms, x and y are the numbers of
166
added O and removed S atoms, respectively. For the experimental condition
167
performed at 500oC and one bar, the value of µo and µs are -0.75 and -2.64 eV,
168
respectively, calculated from the gas-phase O2 molecule and α-phase of solid sulfur
169
(S8).
170 171
Measurements
ACS Paragon Plus Environment
Page 9 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
172
Bruker MultiMode 8 AFM was used for the observation of surface morphology
173
and thickness of molybdenum disulfide, as well as Hg2+ adsorption on bulk
174
molybdenite. The measurement was performed in PeakForce mode with
175
ScanAsyst-Air silicon nitride probe (nominal tip radius of 2 nm) on V-shaped
176
cantilever (resonance frequency fo=70 kHz, spring constant k=0.4 N/m, dimensions of
177
115 µm×25 µm×650 nm), during which the images were captured with 512 pixels and
178
automatically optimized scan parameters (setpoint, feedback response, and scan rate).
179
The obtained images were analyzed with NanoScope Analysis 1.5 software, in which
180
the images were flattened in second order without further process.
181
Raman spectra were obtained from INVIA Raman microscope with a 514 nm Ar
182
laser (Renishaw, UK). The concentration of Hg2+ was detected using a contrAA700
183
continuum source atomic absorption spectrometer (Jena, Germany). The HRTEM
184
images were observed by using a Tecnai G2 F30 S-TWIN transmission electron
185
microscope (FEI, United States). XPS analysis was performed with an ESCALB
186
250Xi photoelectron spectrometer using Al Kα radiation (Thermo-Fisher Scientific,
187
US).
188 189
Results and discussion
190
Characterization of molybdenum disulfide before thermal modification
191
A representative AFM image of mica surface with deposition of molybdenum
192
disulfide nanosheets was shown in Fig. 1a. The lateral size of these nanosheets ranged
193
from dozens of nanometers to hundreds of nanometers. The similar height color
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
194
indicated the uniform thickness of these nanosheets. The inset figure displayed the
195
height of the corresponding cross-section profile of the molybdenum disulfide
196
nanosheet marked with the line. The step height from the substrate to the nanosheet
197
was around 1.3 nm, which was almost double of the step height measured from AFM
198
for a monolayer S–Mo–S structure (0.7 nm),18 therefore the marked nanosheet might
199
be bilayer molybdenum disulfide. To make further efforts on the presentation of
200
thickness distribution, 200 nanosheets were randomly selected and the result was
201
given in Fig. 1b. It showed that no nanosheets with step height less than 0.8 nm were
202
detected, suggesting that few molybdenum disulfide nanosheets presented as a single
203
layer. It could be observed that most of the nanosheets had thickness ranging from 0.9
204
nm to 1.6 nm, demonstrating that the majority of the sheets belonged to bilayer
205
molybdenum disulfide.
206 207
Fig. 1. AFM characterization of molybdenum disulfide, (a) representative AFM image, the inset
208
figure is the corresponding height cross-section profile of the nanosheet marked with a line, (b)
209
histogram of the thickness distribution of molybdenum disulfide nanosheets.
210 211
A representative TEM image of molybdenum disulfide before thermal treatment
212
was shown in Fig. 4a. The good transparency to visible light indicated the thin
ACS Paragon Plus Environment
Page 10 of 31
Page 11 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
213
thickness of molybdenum disulfide. However, no individual thin nanosheets were
214
observed and most of the sheets existed in the form of stacking, which was probably
215
because that the individual sheets were not stopped by the copper grid during the
216
preparation of TEM sample due to their small lateral size.
217 218
Characterization of molybdenum disulfide after thermal modification
219
XPS was performed to determine the chemical composition on the surface of
220
molybdenum disulfide. The wide-scan XPS spectra of molybdenum disulfide before
221
and after thermal treatment were presented in Fig. 2a. The O peaks at around 531 eV
222
and 975 eV became clear on the thermally treated molybdenum disulfide and their
223
intensity increased with the increase of treating temperature, suggesting that oxidation
224
occurred on molybdenum disulfide during thermal treatment. Fig. 2b displayed the
225
Mo3d spectra of molybdenum disulfide before and after being thermally treated. There
226
were two characteristic peaks of MoS2 at 229 eV [Mo3d5/2], 232 eV [Mo3d3/2] and a S2s
227
peak at 226 eV on M. After being thermally treated at 400oC, the intensity of MoS2
228
[Mo3d5/2] and S2s peaks reduced and a new peak at 235 eV corresponded to MoO3
229
clearly appeared, indicating the partial transformation of MoS2 to MoO3. The decrease
230
in MoS2 [Mo3d5/2], S2s peaks and the increase in MoO3 peak became more remarkable
231
on M-500, demonstrating a further oxidation of MoS2 to MoO3 when increasing the
232
thermal treating temperature to 500oC.
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
233 234 235
Fig. 2. XPS spectra of molybdenum disulfide nanosheets before and after thermal modification (a) wide-scan XPS spectra, (b) high-resolution Mo3d spectra.
236
237 238 239
Fig. 3. Raman spectra of molybdenum disulfide nanosheets before and after thermal treatment.
240
Fig. 3 showed the Raman spectra of molybdenum disulfide nanosheets before
241
and after thermal treatment, where the characteristic in-plane E12g mode and
242
out-of-plane A1g mode of molybdenum disulfide were observed. No obvious Raman
243
shift occurred on the peaks of M-400, indicating that the thickness of molybdenum
244
disulfide nanosheets did not change after 400oC thermal treatment. While, a slight
245
reduction of the frequency differences between the E12g and A1g modes was observed
ACS Paragon Plus Environment
Page 12 of 31
Page 13 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
246
on M-500, suggesting the tiny thinning of molybdenum disulfide layers.19 In addition,
247
a minor decreasing in the intensity of A1g mode occurred on M-500, which might be
248
caused by a slight oxidation of molybdenum disulfide during the 500oC
249
modification.20
250 251
Fig. 4. HRTEM images of molybdenum disulfide (a) without thermal treatment, (b) thermally
252
treated at 400oC, (c) thermally treated at 500oC.
253 254
Fig. 4 showed the HRTEM images of molybdenum disulfide before and after
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
255
thermal treatment. Although small sheets stacking on big sheets were observed,
256
individual sheet had homogeneous transparency, indicating that molybdenum
257
disulfide without thermal treatment was of high crystallinity (Fig. 4a). While after
258
being thermally treated at 400oC, the transparency differed in different regions on the
259
sheet, suggesting that the crystallinity might be reduced in the thermal treatment (Fig.
260
4b). Small defects with dimension of several nanometers were observed on M-400 as
261
pointed out by the arrows in Fig. 4b. As a comparison, lots of etching with dozens of
262
or even hundreds of nanometers in size appeared on molybdenum disulfide sheets
263
after 500oC thermal treatment (Fig. 4c), being clear evident for the presence of defects
264
on M-500. In addition, more defects were observed on M-500 than that on M-400.
265
The results indicated that both the size and the density of defects would increase if
266
molybdenum disulfide was thermally treated at higher temperature, which was highly
267
consistent with the previous work.21,22
268 269
Formation of defects and oxidation of MoS2
270
Partial oxidation and defects were observed on molybdenum disulfide during
271
thermal treatment based on the results of XPS, Raman spectra, and HRTEM. Here
272
DFT calculation was performed to interpret the formation of defects and occurance of
273
oxidation during thermal treatment. The configuration before the O2 adsorption on
274
defective molybdenum disulfide was presented in Fig. 5a and 5b. The O2 was placed
275
above the S vacancy with the O-O bond being vertical to the (001) basal plane of
276
MoS2. It should be mentioned that MoS2 structure with one single S missing was built
ACS Paragon Plus Environment
Page 14 of 31
Page 15 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
277
because one S vacancy was the predominate defect existed on MoS2 due to the lowest
278
defect formation energy.23,24 After the geometric structure optimization and transition
279
state search, one oxygen atom located in the S vacancy site and was bound with three
280
Mo atoms, and another oxygen atom was bound with one S atom near the S vacancy
281
(Fig. 5d and 5e). The optimized structure was in good agreement with other
282
research.23 The calculated adsorption energy of O2 on defective MoS2 was -3.07 eV,
283
indicating that the oxidation of MoS2 was thermodynamically favorable. In addition,
284
the low adsorption energy, which was in the range of typical covalent bond energy,
285
demonstrated a chemisorption for O2 on the surface of defective MoS2. Fig. 5d and 5e
286
also showed that the bond length between O(1) and adjacent Mo was even shorter than
287
that between S and adjacent Mo, which gave another strong evidence for the chemical
288
reaction of O(1) and Mo. The electron density map shown in Fig. 5c displayed that no
289
overlap of electron cloud was being observed between O and Mo or S before the
290
adsorption of O2, while obvious overlaps between O(1) and Mo atoms, O(2) and S atom
291
were observed after the adsorption (Fig. 5f), strongly proving the formation of
292
molybdenum oxide and sulfur oxide. While these formed oxides would evaporate
293
when the surrounding temperature was high, leaving bigger vacancy.21,25,26 If more O2
294
were incorporated into the system, more molybdenum oxide and sulfur oxide would
295
emerge on the structure of MoS2, and those oxides would disappear as well under
296
thermal treatment. In this way, the etching pits enlarged and large defects formed.
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
297 298
Fig. 5. Configurations and electron density maps of MoS2 before and after the reaction with O2.
299
Fig. 5a, 5b and 5c are the top, side view of configuration and electron density map before O2
300
adsorption, respectively, while Fig. 5d, 5e and 5f are the corresponding results after O2 adsorption.
301
The blue, yellow and red balls indicate Mo, S and O atoms, respectively.
302 303
In order to illustrate the terminals of the defects, the structure energy of 50% and
304
100% edge oxidized MoS2 (shown in Fig. 6b and 6c, respectively) was calculated in
305
comparison with the energy of pristine structure with fully S saturated edge (Fig. 6a).
306
The oxidation energy per unit length for 50% and 100% edge oxidized MoS2 were
307
-1.10 and -2.11 eV/Å, respectively, calculated from Eq. (3). The negative values
308
suggested that the oxidized structure of MoS2 were more thermodynamically stable
309
than the pristine structure. And MoS2 with fully oxidized edge was the most stable
310
structure compared to the other two structures because of the lowest energy. The
311
results demonstrated that most of defects might terminate with oxygen atoms when no
312
more thermal energy was input.
ACS Paragon Plus Environment
Page 16 of 31
Page 17 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
313 314
Fig. 6. MoS2 configurations with different oxygen contents on the edge, 100% S (a), 50% O (b),
315
100% O (c). The blue, yellow and red balls indicate Mo, S and O atoms, respectively.
316 317
The oxidation of MoS2 on the basal plane was investigated through calculating
318
the energy of MoS2 structure with two S atoms on the basal plane substituted by two
319
O atoms. The oxygen substitution energy was calculated according to Eq. (3), where
320
the Eoxidized and Epristine were energies of MoS2 after geometric structure optimization
321
as shown in Fig. 7b and 100% O edge oxidized MoS2 as shown in Fig. 6c,
322
respectively. The calculated oxygen substitution energy was -0.36 eV/Å,
323
demonstrating that oxidation could also proceed on the basal plane of MoS2 at high
324
temperature and air atmosphere. In addition, the distance between O and Mo was
325
shorter than that between S and Mo, and the structure of MoS2 had slight modification
326
after optimization, further proving that Mo on the basal plane preferred to bind with O
327
other than S. However, due to the low activity of the basal atoms, oxidation of perfect
328
surface might lag behind that of the edge and vacancy sites.
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
329 330
Fig. 7. MoS2 configurations with two S atoms on the basal plane substituted by two O atoms
331
before (a) and after (b) geometric structure optimization. The blue, yellow and red balls indicate
332
Mo, S and O atoms, respectively.
333 334
Adsorption of Hg2+on molybdenum disulfide nanosheets before and after thermal
335
modification
336
The batch experimental results of Hg2+ adsorption kinetics on molybdenum
337
disulfide nanosheets before and after thermal modification were shown in Fig. 8a. The
338
adsorption increased fastly at initial times until it reached a plateau for the three
339
molybdenum disulfide nanosheets adsorbents. It can been seen that M exhibited the
340
lowest adsorption capacity at 50 mg/L initial Hg2+ concentration. After being treated
341
at 400oC, molybdenum disulfide nanosheets showed an enhanced Hg2+ adsorption
342
capacity, which was almost twice than that of M. While, the Hg2+ adsorption of
343
M-500 dramatically increased to 630 mg/g. These results indicated that thermal
344
treatment of molybdenum disulfide nanosheets significantly improved its Hg2+
345
adsorption capacity. A pseudo-first-order kinetic
346
pseudo-second-order kinetic model (Eq. S2) were used to fit the experimental data for
ACS Paragon Plus Environment
model (Eq. S1) and a
Page 18 of 31
Page 19 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
347
a further investigation of the adsorption mechanism. The fitting results are presented
348
in Fig. 8a and Table S1. The higher correlation coefficient of R22 indicated that the
349
Hg2+ adsorption on all the three molybdenum disulfide adsorbents was well-described
350
by the pseudo-second-order kinetic model, which was based on the assumption that
351
the rate-limiting step might be chemical sorption or chemisorption involving valence
352
forces through sharing or exchange of electrons between adsorbent and adsorbate.27
353
The fitting results demonstrated that chemical interaction might exist between Hg2+
354
and all the molybdenum disulfide adsorbents.
355
The initial adsorption rate, which was defined as the adsorbed Hg2+ per gram of
356
the adsorbent per unit time on the adsorbent in the first 5 min, was used to evaluate
357
the effect of thermal modification on the adsorption kinetics of Hg2+ on molybdenum
358
disulfide nanosheets (Fig. 8b). The adsorption rate of M-500 was 11.27 mg·g-1·min-1,
359
which was 17.6 and 5.3 times faster than that of M and M-400, respectively, further
360
proving the dramatical effect of thermal modification on the Hg2+ removal with
361
molybdenum disulfide nanosheets as adsorbent.
362 363
Fig. 8. Adsorption kinetics of Hg2+ on molybdenum disulfide nanosheets before and after thermal
364
treatment, (a) adsorption capacity as a function of time, (b) adsorption rate in the first 5 min. The
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
365
initial Hg2+ concentration and pH of the solution was 50 mg/L and 6, respectively.
366 367
The adsorption isotherms of Hg2+ on molybdenum disulfide nanosheets before
368
and after thermal modification at temperature of 30oC and pH of 6 were illustrated in
369
Fig. 9. The adsorption capacity increased with the increase of Hg2+ concentration until
370
it reached an equilibrium. The adsorption isotherm indicated an enormous adsorption
371
capacity of molybdenum disulfide nanosheets subsequent to thermal treatment. A 750
372
mg/g Hg2+ uptake capacity was obtained on M-500 at a Hg2+ equilibrium
373
concentration of around 110 mg/L, which was approximately 11 and 2.5 times higher
374
than that of M and M-400. These results indicated a better Hg2+ affinity on M-500
375
than on the other two adsorbents, which might be highly related to the modified
376
surface property of molybdenum disulfide during thermal treatment. It should be
377
mentioned that although a lower Hg2+ adsorption capacity was obtained on M, it was
378
still much higher than the traditional adsorbents (activated carbon, modified clay, etc.)
379
reported in other literatures.28,29
380 381
Fig. 9. Adsorption isotherm of Hg2+ on molybdenum disulfide nanosheets before and after thermal
382
treatment.
ACS Paragon Plus Environment
Page 20 of 31
Page 21 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
383
The adsorptions of Hg2+ on molybdenum disulfide nanosheets with and without
384
thermal treatment at pH range of 1-6 were illustrated in Fig. 10. All the three
385
adsorbents had low Hg2+ adsorption capacity at pH of 1, which might be because that
386
the presence of excess H+ in the solution would compete with Hg2+ for the active sites,
387
resulting in a low adsorption capacity. The adsorption capacity increased slightly with
388
the increase of pH for both M and M-400. While, the Hg2+ uptake capacity had a
389
dramatic enhancement on M-500 when increasing the pH of the solution to 2 and then
390
kept an equilibrium at higher pH values. Fig. 10 clearly suggested that thermal
391
modification enabled molybdenum disulfide to achieve a high Hg2+ affinity in a wide
392
pH range.
393 394
Fig. 10. Hg2+ adsorption on molybdenum disulfide nanosheets before and after thermal treatment
395
as a function of pH.
396 397
AFM observation of Hg2+ adsorption on bulk molybdenite
398
Due to the small size of exfoliated molybdenum disulfide, it is difficult to
399
observe the Hg2+ adsorption on its surface visually. To resolve this problem, bulk
400
molybdenite with large surface was chosen in this work to perform the Hg2+
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
401
adsorption on it and observed with AFM in order to give a better understanding on the
402
Hg2+ adsorption on molybdenum disulfide nanosheets. Bulk molybdenite had an
403
atomic smooth surface before thermal modification (Fig. 11a). After being exposed to
404
100 µg/L Hg2+ solution for 1 min, slight substances, which were confirmed to be Hg2+
405
in our previous work,10,15 were captured on the surface. The above results
406
demonstrated that the surface of molybdenite had chemical reactivity for the
407
adsorption of Hg2+. However, the adsorption of Hg2+ on molybdenite increased slowly
408
with the increase of adsorption time and less than half of the surface was occupied by
409
Hg2+ after 5 min adsorption, which indicated that the activity of the surface for Hg2+
410
was not strong. Fig. 11b illustrated the images of 500oC thermally modified
411
molybdenite with Hg2+ adsorption at different times, respectively. Lots of edge defects
412
were clearly detected on the sample before adsorption, further confirming the
413
existence of defects after being thermally treated. It was noticed that plenty of large
414
defects existed on bulk molybdenite, while only few defects with dimension of dozens
415
of nanometers were observed on molybdenum disulfide nanosheets at the same
416
thermal treatment condition (Fig. 4c). It was because that the oxidative etching was
417
greatly affected by the number of MoS2 layers and the pit sizes increased with the
418
increase of MoS2 layers.21 Plenty of Hg2+ distributed on the surface of thermally
419
treated molybdenite after 1 min adsorption, the density of which was similar with that
420
on 5 min Hg2+ adsorbed molybdenite. This indicated that thermal modification
421
accelerated the adsorption of Hg2+ on molybdenite. As the time increased, the Hg2+
422
adsorption on thermally treated molybdenite increased dramatically. The surface was
ACS Paragon Plus Environment
Page 22 of 31
Page 23 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
423
almost fully occupied by abundant Hg2+ within only 5 min. The defects on the surface
424
of molybdenite became obscure subsequent to 5 min Hg2+ adsorption, further
425
indicating the great Hg2+ adsorption capacity on thermally modified molybdenite.
426
These phenomena revealed that molybdenite was much more capable of capturing
427
Hg2+ after thermal modification. Due to the similar surface property of molybdenum
428
disulfide nanosheets and bulk molybdenite, it might be inferred that the surface of
429
molybdenum disulfide nanosheet was greatly activated during thermal treatment,
430
which was therefore bringing a significant enhancement on the Hg2+ adsorption.
431 432
Fig. 11. AFM images of Hg2+ adsorption on bulk molybdenite without (a) and (b) with thermal
433
modification at different times.
434 435
Origin of the enhanced Hg2+ adsorption on molybdenum disulfide after thermal
436
modification
437
XPS was performed to investigate the mechanism of Hg2+ adsorption on
438
molybdenum disulfide with and without thermal treatment. Compared with the
439
wide-scan XPS spectra of molybdenum disulfide before adsorption, new Hg peaks
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
440
appeared at around 101 eV, 106 eV, 360 eV, 380 eV, and 578 eV (Fig. 12a), which
441
gave a clear evidence for the Hg adsorption on molybdenum disulfide. Fig. 12b
442
compared the Hg4f5/2 and Hg4f7/2 spectra on the three adsorbents. Both of Hg4f peaks
443
were deconvoluted into two peaks, among which the doublet at 100 eV and 104 eV
444
could be assigned to Hg-S, while the other doublet at 101 eV and 105 eV might be
445
Hg-O. This revealed that both the intrinsic S and oxidation-resulted O served as the
446
binding sites for the immobilization of Hg on molybdenum disulfide. By comparing
447
the area proportion of Hg-O and Hg-S peaks, it could be obtained that S sites made a
448
bigger contribution than O sites on M for the adsorption of Hg, while the contribution
449
of the two sites were comparable to each other on M-400, and O sites even became
450
more important in the Hg adsorption on M-500. This phenomenon suggested the
451
significant role of oxidation of molybdenum disulfide in its Hg adsorption. In addition,
452
it was interesting to find out that although the content of S (30.7%) was higher than
453
that of O (20.6%) in 500oC thermally treated molybdenum disulfide, the chemisorbed
454
Hg2+ mainly presented in the form of Hg-O instead of Hg-S, which meant that O had a
455
better affinity than S in the chemisorption of Hg2+. No characteristic peak of Hg0 was
456
found in the range from 99 eV to 100 eV, indicating that no oxidation-reduction
457
reaction occurred on Hg2+ during the adsorption on molybdenum disulfide.30
458
ACS Paragon Plus Environment
Page 24 of 31
Page 25 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
459 460 461
Fig. 12. XPS spectra of molybdenum disulfide nanosheets with and without thermal treatment after Hg2+ adsorption (a) wide-scan XPS spectra, (b) high-resolution Hg4f spectra.
462 463
Conclusions
464
(1) Thermal treatment resulted in a partial oxidation of MoS2 to MoO3 and an
465
emergence of edge defects on the surface of molybdenum disulfide. The oxidation
466
and defects increased with the increase of thermal treatment temperature. DFT
467
calculation indicated that the oxidative etchings were terminated with oxygen
468
atoms, and both the vacancy and basal plane could be oxidized during thermal
469
treatment.
470
(2) The removal capacity of Hg2+ on molybdenum disulfide was significantly
471
enhanced after thermal modification. Molybdenum disulfide subsequent to 500oC
472
thermal treatment reached 17.6 times faster on the adsorption rate and 11 times
473
higher on the adsorption capacity than molybdenum disulfide without
474
modification. The pH effect results revealed that thermally modified molybdenum
475
disulfide exhibited a higher Hg2+ adsorption than that without thermal treatment in
476
all the pH values.
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
477
(3) Thermal treatment enabled molybdenum disulfide achieve a tremendous
478
enhancement on the Hg2+ adsorption, which might be greatly related to the higher
479
activity of the adsorbent surface and the formation of molybdenum oxide in
480
thermal treatment. XPS revealed that molybdenum oxide could strongly bind Hg2+
481
through the formation of Hg-O complexation.
482
(4) The tremendous enhancement of Hg2+ adsorption on molybdenum disulfide after
483
thermal treatment suggests that thermal modification is an efficient method for
484
molybdenum disulfide to increase its removal capacity of heavy metals.
485 486 487 488
Supporting Information X-ray diffraction (XRD) pattern, thermogravimetry analysis (TGA) and differential thermal analysis (DTA) of natural molybdenite.
489 490
Acknowledgements
491
The financial supports for this work from the National Natural Science
492
Foundation of China (51704220, 51674183 and 51704212), Natural Science
493
Foundation of Hubei Province (2017CFB280), and China Postdoctoral Science
494
Foundation (2016M600621) were gratefully acknowledged.
495 496 497
Conflict of Interest The authors declare no competing financial interest.
498
ACS Paragon Plus Environment
Page 26 of 31
Page 27 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
499
References
500
(1)
photoluminescence in monolayer MoS2. Nano Lett. 2010, 10, 1271–1275.
501 502
(2)
(3)
Sundaram, R.S.; Engel, M.; Lombardo, A.; Krupke, R.; Ferrari, A.C.; Steiner, M. Electroluminescence in single layer MoS2. Nano Lett. 2013, 13, 1416–1421.
505 506
Mak, K.F.; Lee, C.; Hone, J.; Shan, J.; Heinz, T.F. Atomically thin MoS2: a new direct-gap semiconductor. Phys. Rev. Lett. 2010, 105, 2–5.
503 504
Splendiani, A.; Sun, L.; Zhang, Y.; Li, T.; Kim, J.; Chim, C.Y.; Galli, G.; Wang, F. Emerging
(4)
Kim, S.; Konar, A.; Hwang, W.; Lee, J.H.; Lee, J.; Yang, J.; Jung, C.; Kim, H.; Yoo, J.; Chio,
507
J.; Jin, Y. W.; Lee, S. Y; Jena, D.; Choi, W.; Kim, K. High-mobility and low-power thin-film
508
transistors based on multilayer MoS2 crystals. Nat. Commun. 2012, 3, 1011–1017.
509
(5)
Liu, C.; Wang, L.; Tang, Y.; Luo, S.; Liu, Y.; Zhang, S.; Zeng, Y.; Xu, Y. Vertical single or
510
few-layer MoS2 nanosheets rooting into TiO2 nanofibers for highly efficient photocatalytic
511
hydrogen evolution. Applied Catal. B, Environ. 2015, 164, 1–9.
512
(6)
Commun. 2013, 49, 10718–10720.
513 514
Sun, L.; Huang, H.; Peng, X. Laminar MoS2 membranes for molecule separation. Chem.
(7)
Zhao, H.; Yang, G.; Gao, X.; Pang, C. H.; Kingman, S. W.; Wu, T. Hg0 capture over
515
CoMoS/γ-Al2O3 with MoS2 nanosheets at low temperatures. Environ. Sci. Technol. 2015, 50,
516
1056–1064.
517
(8)
adsorbent for high-efficient Pb(II) removal from water. Appl. Mater. Today 2017, 9, 220–228.
518 519 520
Liu, C.; Jia, F.; Wang, Q.; Yang, B.; Song, S. Two-dimensional molybdenum disulfide as
(9)
Wang, Z.; Mi, B. Environmental applications of 2D molybdenum disulfide (MoS2) nanosheets. Environ. Sci. Technol. 2017, 51, 8229–8244.
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
521
(10)
adsorbent for removing Hg2+ from water. ACS Sustainable Chem. Eng. 2017, 5, 7410–7419.
522 523
Jia, F., Wang, Q., Wu, J., Li, Y., Song, S. Two-dimensional molybdenum disulfide as a superb
(11)
Zhi, L.; Zuo, W.; Chen, F.; Wang, B. 3D MoS2 composition aerogels as chemosensors and
524
adsorbents for colorimetric detection and high-capacity adsorption of Hg2+. ACS Sustainable
525
Chem. Eng. 2016, 4, 3398–3408.
526
(12)
Ai, K.; Ruan, C.; Shen, M.; Lu, L. MoS2 nanosheets with widened interlayer spacing for
527
high-efficiency removal of mercury in aquatic systems. Adv. Funct. Mater. 2016, 26, 5542–
528
5549.
529
(13)
Aghagoli, M. J.; Beyki, M. H.; Shemirani, F. Application of dahlia-like molybdenum disulfide
530
nanosheets for solid phase extraction of Co(II) in vegetable and water samples. Food Chem.
531
2017, 223, 8–15.
532
(14)
Wang, J.; Zhang, W.; Yue, X.; Yang, Q.; Liu, F.; Wang, Y.; Zhang, D.; Li, Z.; Wang, J.
533
One-pot synthesis of multifunctional magnetic ferrite-MoS2-carbon dots nanohybrid adsorbent
534
for efficient Pb(II) removal. J. Mater. Chem. A 2016, 4, 3893–3900.
535
(15)
disulfide in aqueous solutions. Phys. Chem. Chem. Phys. 2017, 19, 3837–3844.
536 537
(16)
Santosh, K. C.; Longo, R. C.; Wallace, R. M.; Cho, K. Surface oxidation energetics and kinetics on MoS2 monolayer. J. Appl. Phys. 2015, 117, 135301−135308.
538 539
Jia, F.; Zhang X.; Song, S. AFM study on the adsorption of Hg2+ on natural molybdenum
(17)
Santosh, K. C.; Longo, R. C.; Addou, R.; Wallace, R. M.; Cho, K. Impact of intrinsic
540
atomic defects on the electronic structure of MoS2 monolayers. Nanotechnology 2014, 25,
541
375703−375708.
542
(18)
Splendiani, A.; Sun, L.; Zhang, Y.; Li, T.; Kim, J.; Chim, C. Y.; Galli, G.; Wang, F. Emerging
ACS Paragon Plus Environment
Page 28 of 31
Page 29 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
photoluminescence in monolayer MoS2. Nano Lett. 2010, 10, 1271–1275.
543 544
(19)
single- and few-layer MoS2. ACS Nano 2010, 4 (5), 2695–2700.
545 546
Lee, C.; Yan, H.; Brus, L. E.; Heinz, T. F.; Hone, J.; Ryu, S. Anomalous lattice vibrations of
(20)
Balendhran, S.; Ou, J. Z.; Bhaskaran, M.; Sriram, S.; Ippolito, S.; Vasic, Z.; Kats, E.;
547
Bhargava, S.; Zhuiykov, S.; Kalantarzadeh, K. Atomically thin layers of MoS2 via a two
548
step thermal evaporation-exfoliation method, Nanoscale 2012, 4, 461–466.
549
(21)
Zhou, H.; Yu, F.; Liu, Y.; Zou, X.; Cong, C.; et al. Thickness-dependent patterning of MoS2
550
sheets with well-oriented triangular pits by heating in air. Nano Research 2013, 6,
551
703−711.
552
(22)
atomically thin MoS2. J. Phys. Chem. C 2013, 117, 25643−25649.
553 554
Yamamoto, M.; Einstein, T. L.; Fuhrer, M. S.; Cullen, W. G. Anisotropic etching of
(23)
Zhao, B.; Shang, C.; Qi, N.; Chen Z. Y.; Chen, Z. Q. Stability of defects in monolayer MoS2
555
and their interaction with O2 molecule: A first-principles study. Applied Surface Science
556
2017, 412, 385−393.
557
(24)
Paul, J. F.; Payen, E. Vacancy formation on MoS2 hydrodesulfurization catalyst: DFT study of the mechanism. J. Phys. Chem. B. 2003, 107, 4057−4064.
558 559
(25) Najmaei, S.; Yuan, J.; Zhang, J.; Ajayan, P.; Lou, J. Synthesis and defect investigation of
560
two-dimensional molybdenum disulfide atomic layers. Acc. Chem. Res. 2015, 48, 31−40.
561
(26) Hong, J.; Hu, Z.; Probert, M.; Li, K.; Lv, D.; et al. Exploring atomic defects in molybdenum disulphide monolayers. Nat. Commun. 2015, 6, 6293−6300.
562 563 564
(27)
Ho, Y. S.; McKay, G. The kinetics of sorption of divalent metal ions onto sphagnum moss peat. Water Res. 2000, 34 (3), 735−742.
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
565
(28)
Krishnan, K. A.; Anirudhan, T. S. Removal of mercury(II) from aqueous solutions and
566
chlor-alkali industry effluent by steam activated and sulphurised activated carbons prepared
567
from bagasse pith: kinetics and equilibrium studies. J. Hazard. Mater. 2002, 92, 161–183.
568
(29)
Manohar, D. M.; Krishnan, K. A.; Anirudhan, T. S. Removal of mercury(II) from aqueous
569
solutions and chlor-alkali industry wastewater using 2-mercaptobenzimidazole-clay. Water
570
Research 2002, 36, 1609–1619.
571 572
(30)
Behra, P.; Bonnissel-Gissinger, P.; Alnot, M.; Revel, R.; Ehrhardt, J. J. XPS and XAS study of the sorption of Hg(II) onto pyrite. Langmuir 2001, 17 (13), 3970−3979.
573
ACS Paragon Plus Environment
Page 30 of 31
Page 31 of 31 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
574
For Table of Contents Use Only
575
576 577 578
TOC/Abstract Graphic Synopsis
579
Molybdenum disulfide achieves a tremendous enhancement on Hg2+ adsorption after
580
thermal treatment, mading it an excellent adsorbent for the sustainable reuse of
581
mercury contaminated water.
ACS Paragon Plus Environment