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Materials and Interfaces
Selective Adsorption of Dimethyl Disulfide on AcidTreated CuYH@silicalite-1 Core-Shell Structure: Methyl tert-Butyl Ether as Competition Components Chao Yang, Xuan Meng, Dezhi Yi, Zhiming Ma, Naiwang Liu, and Li Shi Ind. Eng. Chem. Res., Just Accepted Manuscript • DOI: 10.1021/acs.iecr.9b03079 • Publication Date (Web): 27 Aug 2019 Downloaded from pubs.acs.org on August 30, 2019
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1
Selective Adsorption of Dimethyl Disulfide on Acid-Treated
2
CuYH@silicalite-1 Core-Shell Structure: Methyl tert-Butyl Ether as
3
Competition Components
4
Chao Yang, Xuan Meng, Dezhi Yi, Zhiming Ma, Naiwang Liu, Li Shi*
5
State Key Laboratory of Chemical Engineering,
6
East China University of Science and Technology, Shanghai 200237, China
7
E-mail:
[email protected] 8
Abstract: To selectively adsorb dimethyl disulfide (DMDS) from its competition
9
components, such as methyl tert-butyl ether (MTBE), the shell layer of silicalite-1
10
crystals was synthesized on commercial Y zeolite crystal surface (CuYH@silicalite-1
11
core@shell structured composites) with a mass composition of tetraethyl orthosilicate/
12
tetrapropylammonium hydroxide/ ethanol/ H2O/ CuYH=20g (0.096 mol):19g (0.0234
13
mol):17g (0.369 mol):87g (4.829 mol):5g. CuYH zeolites were acquired by ion
14
exchanging Cu2+ with HCl treated NaY (noted as NaYH). Results showed that by the
15
dealuminzation of HCl, the ratio of Si/Al for NaY zeolites had been dramatically
16
increased, providing NaYH a favourable condition for the growing of silicalite-1
17
coatings; and many vacancies left by the dissolved Al also enlarged the out surface
18
area of NaYH to provide more load locations for silicalite-1 crystals. Among all these
19
synthesized adsorbents, the core@shell YH-CuCl2 displayed a best DMDS adsorption
20
of about 34.585 mgs/gadsorbent in MTBE solution and a 100% desulfurization rate for
21
about 3 h. Also, the process of synthesizing CuYH@silicalite-1 core@shell composites
22
and their shape-selective adsorption were detailed.
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Key words: Dimethyl disulfide; Shape-selective adsorption desulfurization; Methyl
24
tert-butyl ether; CuYH@silicalite-1 core@shell composites; Dealuminzation.
25
1. Introduction
26
The environmental pollution derived from sulfur containing fuel due to the sulfur
27
oxide emissions has focused more and more attentions. To this end, since the year
28
2009, sulfur content in gasoline has been limited to less than 10 ppmw.1-3 Many
29
effective measures have been taken to reduce the sulfur in gasoline and diesel fuels as
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well as their modifying additives, such as Methyl tert-butyl ether (MTBE), which
31
possesses considerable octane-enhancing property. However, during the production
32
process (reaction of isobutene and methanol), the C4 stream (the main source of
33
isobutene) contains many sulfur compounds, such as DMS (dimethyl sulfide) and
34
DMDS (dimethyl disulfide; about 45 ppm in MTBE)4, 5. The molecular structures of
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DMDS as well as MTBE are illustrated in Scheme. 1. Recently, the desulfurization for
36
MTBE are primarily distillation desulfurization, hydrodesulfurization, and adsorption
37
desulfurization.6-9 By comparison, distillation is always accompanied by huge energy
38
consumption and hydrodesulfurization always requires a harsh operating condition
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under high temperature and pressure. For deep desulfurization, the adsorption
40
desulfurization has been considered the promising technology due to its mild
41
condition of atmospheric temperature, low pressure, low energy consumption and
42
simple operation.10, 11
43 44
Scheme. 1. Molecular structural formula of DMDS and MTBE
45
Adsorption desulfurization had been extensively studied on numerous kinds of
46
adsorbents such as modified composite oxide, activated carbons (ACs), mesoporous
47
silica, metal-organic frameworks (MOF) and zeolite,12-14 among which zeolites had
48
displayed wide application in chemical industry based on their high porosity of
49
microporous or mesoporous silica-alumina crystalline frameworks, large surface areas,
50
thermal stability, and form selectivity.15,
51
well organized nanopores and nanochannels had exhibited tremendous supports for
52
desulfurizing organic sulfur compounds especially DMDS.17 By NaY, NaX, Hβ
53
zeolites, Wakita et al.18 discussed removing DMS from the city gas and found the sites
54
for adsorption on NaY were relied on Na+ with a adsorption capacity of sulfur for 1.1
55
mmols/gadsorbents. Lv et al.19 discussed the adsorption desulfurization (DMDS) in
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liquefied petroleum gas on modified NaY adsorbents, and revealed with 5 wt% Ag2O,
57
NaY displayed the best sulfur capacity 87.86 gs/gadsorbents by the adsorption ability and
58
selectivity of S-Ag(I) interaction. Yi et al.20 also studied exchanging NaY with Ni2+,
16
Actually, different kinds of zeolites with
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Cu2+etc. on desulfurizing DMDS in n-octane and found that S-M bonds were the keys
60
in desulfurization. Lee et al.4 investigated desulfurizing DMDS in C4 hydrocarbon
61
mixtures with β zeolites and claimed that Cu(I) ion-exchanged zeolites showed high
62
DMDS capacity of 8.70 mgs/gadsorbents. Nevertheless, when adsorbing DMDS in MTBE,
63
there would be a fierce competition between them on π-complexation adsorbents,
64
which had been detailedly described in the previous studies;21-23 and Yang10,
65
claimed the adsorption capacity of sulfur on π-complexation adsorbents decreased
66
sharply in the present of MTBE. To solve the competitive adsorption, by using
67
modified ZSM-5 zeolites, Zhao et al.25 had tried to adsorb DMDS from MTBE; and
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acknowledged the pore structure and acidity both played key roles in adsorption
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process and reached a not too optimistic adsorption capacity of 8.24 mgs/gadsorbents.
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Therefore, new strategies on selectively adsorbing DMDS from MTBE are attractive.
24
had
71 72
Scheme. 2. Structure of (a) silicalite-1 and (b) NaY
73
In consideration of the fact that Y zeolite had been proved a promising material
74
in adsorption extensively owing to its high solid acidity, crystalline microporous
75
properties, and 3D pores (tetrahedral framework structures);26-28 in addition, their
76
activity and stability could be further improved by steaming, ion-exchange, and
77
treatment with acid or base.15,
78
structured composite with NaY, whose structure were shown in Scheme. 2, and CuY
79
as the core, silicalite-1 as the shell to remove DMDS in MTBE solution and obtain an
80
adsorption capacity of sulfur on NaY@silicalite-1 and CuY@silicalite-1 to be 20.711
81
and 32.882 mgs/gadsorbent, respectively.21, 22 In present study, we are trying a new way in
82
synthesizing core@shell composites by the dealuminization of HCl on Y zeolite to
83
obtain a better growth environment for silicalite-1 shell. Dealuminization is an
16, 29
Previously, we have applied a core@shell
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efficient method to increase the ratio of Si/Al by transferring framework Al into
85
extra-framework position and then being washed away.15,
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USY zeolite with citric acid and obtained improved Si/Al ratio Y zeolite with smaller
87
unit cell parameters. Qiao et al.35, by malic acid and nitric acid treatment, studied the
88
modified USY zeolites; and found the aluminum removed by coordination reaction of
89
MA could create extensive secondary pores while NA could only remove alumina of
90
extra-framework. In most of these studies, the nature of framework and
91
extra-framework aluminum was characterized on a
92
determining the Al coordination with high resolution.15 Besides, the adsorbents
93
synthesized in this study were also investigated by SEM, TEM, BET, XRD, FT-IR,
94
ICP-OES, and EDS measurements. Also, the selective adsorption on these core@shell
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structured composites was also analyzed according to these characterization.
96
2. Experimental
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2.1. Materials.
30-33
Liu et al.34 modified
Al MAS solid-state NMR by
27
98
NaY zeolites (Si/Al, 2.4) were obtained from Wenzhou Catalyst Plant. 12 mol/L
99
hydrochloric acid (HCl) and analytically pure CuCl2, Cu(NO3)2, CuSO4, EtOH
100
(ethanol), TEOS (tetra ethyl orthosilicate), and 25% TPAOH (tetrapropylammonium
101
hydroxide) solution were purchased from Tansoole (Shanghai). All water used in the
102
experiments was deionized.
103
2.2. Acid treatment on NaY.
104
With a solid to liquid of 1g NaY : 30 mL HCl solution, NaY were put into 0.5
105
mol/L HCl(aq) prepared by diluting 12 mol/L HCl solution in a volumetric flask; after
106
a full mix with stirring for half an hour at 25 °C, then the mixtures were separated by
107
distinct methods to collect NaYH: filtration (filter paper, aperture: 15-20 μm), and
108
centrifugation (rotation speed: 6000 r/min); NaYH were finally collected after a
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thorough washing and drying.
110
2.3. Preparation of core (CuYH), shell (silicalite-1) and core@shell structures
111
2.3.1. Core zeolites (CuYH).
112
CuYH were obtained by ion exchanging NaYH with Cu2+ (CuCl2 , Cu(NO3)2, as
113
well as CuSO4 ): by solid to liquid ratio of 1 g: 20 ml, NaYH (in powder) were added
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into 0.5 mol/L Cu2+ solution in water bath (90 °C); after a day and night stirring, the
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mixtures were separated by filtration, washed, dried, and finally calcined at 450°C for
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6h. These modified NaYH were marked as YH-CuCl2, YH-Cu(NO3)2 and YH-CuSO4.
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2.3.2. core@shell structures (CuYH as the core).
118 119
In this research, by sol-gel coating process, (TPAOH as the template)36, the CuYH@silicalite-1 were prepared as follow:
120
Firstly, the precursor solution was prepared, including TEOS, TPAOH, EtOH,
121
and water at a mass ratio of TEOS/ TPAOH/ EtOH/ H2O=20 g:19 g:17 g:87 g (0.096:
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0.0234: 0.369: 4.829 mol). To sufficiently hydrolyze TEOS into water, TEOS was
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dropwise added and kept stirring for 2 h; then 5 g CuYH (power) was added; by
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continuous stirring for another 0.5 h, a homogeneous suspension was formed. Then it
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was transferred into an hydrothermal autoclave to synthesize the core@shell
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structures at 180 °C for 24 h; the products were obtained by filtration, then washed,
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dried, and calcined at 550 °C for 6 h. The synthesized core@shell structures were
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marked as CSYH-CuCl2, CSYH-Cu(NO3)2 and CSYH-CuSO4, respectively.
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2.3.3 Silicalite-1 and core@shell structures (NaYH as the core).
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Silicalite-1 crystals were synthesized at the same mass ratio of TEOS, TPAOH, EtOH, and H2O (20:19:17:87 g) only without adding CuYH. NaYH core@shell structures were synthesized in the same method by adding
133
NaYH instead of CuYH, marked as CSNaYH.
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2.4. DMDS adsorption (shape selective adsorption) experiments
135
2.4.1. adsorption test in static state.
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The adsorption capacity of sulfur on each adsorbent was obtained by static
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adsorption, performed in a 30 ml airtight container by putting 0.2 g adsorbents into 20
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mL MTBE solution (sulfur content: 748.52 mg/L). After standing for 24 h at room
139
temperature, the sulfur concentration after the static tests was analyzed by a TS-3000
140
fluorescence sulfur tester. The adsorption capacity of sulfur on each adsorbent was
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calculated by the following equation:
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Sulfur adsorption capacity (mgs/gadsorbent) = (748.52- Ct)×0.02/0.2;
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(Ct (mg/L) was the sulfur concentration after static tests)
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2.4.2. Adsorption test in dynamic state.
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To acquire the adsorption desulfurization rate, each sample was loaded in a bed
146
flow reactor (operating condition: weight hourly space velocity: 5 h-1, 0.1 MPa and
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25 °C). In a quartz column (length, 250 mm; internal diameter, 6 mm), about 0.89 g
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adsorbents (size, 20-40 mesh) were loaded intermediately; and the spaces up and
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down were filled with quartz sands. MTBE solution (DMDS sulfur content: 286.13
150
mg/L) was pumped into the quartz column at a flow rate of 6 mL/h by a double
151
plunger microscale pump. The sulfur content of export solution was analyzed in real
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time every half an hour.
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2.5. Characterization for adsorbent samples.
154 155
SEM and TEM photographs were achieved on a Hitachi S-3400 microscope (15 KV; magnification,1-20 K) and a JEM-2100 (200 KV; magnification, 2-1500 K).
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N2 adsorption-desorption was performed via a JW-BK200C instrument. At
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-196 °C, 150 mg of samples were analyzed to acquire surface area, mesoporous and
158
microporous volume.
159 160 161 162 163
XRD was used to analyze the crystal structures of different samples via a D8 Advance polycrystalline diffractometer (40 KV, 100 mA; 10° to 75°; step, 0.02°). By a Magna-IR550 spectrometer (Nicolet Company), the FT-IR spectra were collected by mixing the powder sample with KBr (mass ratio, 1:100). The solid-state
Al magic-angle spinning (MAS) nuclear magnetic resonance
27
164
(NMR) spectra (27Al MAS NMR) were obtained on a Bruker MSL-300 spectrometer
165
(frequency, 104.34 MHz; delay time,10 ms).
166
EDS and ICP-OES data were collected on a TEAMEDS and an Agilent 725
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ICP-OES, respectively, to analyze the element content of superficial and total Si, Al
168
Na and Cu in different adsorbents after HCl treatment and core@shell experiments
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(mainly the variety of Si/Al and Al/Na).
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3. Results and discussion
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3.1. 27Al MAS NMR spectra.
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NaY NaYH
100
172 173
80
60
40
20
Chemical shift (ppm)
0
-20
Figure. 1. 27Al MAS NMR spectra of NaY and NaYH.
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Before and after acid treatment, the changes of Al environments (the chemical
175
state of Al atoms) in NaY zeolite was presented via a 27Al MAS NMR in Figure. 1.
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Two types of Al chemical state in NaY zeolites were observed: tetrahedral coordinated
177
framework Al (65 ppm) and octahedral coordinated extra-framework Al (3 ppm).37 As
178
could be seen, for NaY zeolite, the most signal occurred at around 65 ppm; and almost
179
no obvious signal at 3 ppm was detected, indicating that in NaY zeolite, almost all the
180
Al species were located in framework, providing NaY zeolite a good crystallinity as
181
shown in XRD patterns (Figure. 2). However, after acid treatment, the signal intensity
182
at 65 ppm had dropped dramatically, which suggested that most of the framework Al
183
(about 90%) had disappeared, attributing to the dealuminization effect of HCl on
184
framework Al. In addition, the signal observed at 3 ppm stated clearly that the
185
disappeared framework Al was converted into extra-framework Al; nevertheless,
186
owing to the adequate washing process, only a little extra-framework Al remained,
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leading to a weak signal at 3 ppm.
188
there was a strong dealuminization effect on NaY zeolite; and, of course, the
189
crystallinity of NaY zeolite after acidic treatment would be severely declined, which
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was also consistent with XRD patterns. Meanwhile, the disappeared framework Al
191
would also provide the the NaY zeolite more vacancies especially the surface portion.
Al MAS NMR spectra showed that, for HCl,
27
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192
3.2. XRD spectra of adsorbents. 20.3° 15.6° 18.6°
(6) (5)
MFI 26.3° (11)
MFI (10)
(4)
Intensity (a.u.)
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MFI
(3)
(9)
MFI
(2)
(8)
18.6° * 15.6° *
10
15
* 22.1° 26.3° * 20.3° * 20
25
30
MFI (1)
(7) 35 10
15
20
25
30
35
193
2θ (degrees)
194 195 196
Figure. 2. XRD analysis of adsorbents: (1) NaY, (2) NaYH, (3) YH-CuCl2, (4) YH-Cu(NO3)2, (5) YH-CuSO4, (6) NaYH after 2h acid treatment (7) silicalite-1, (8) CSNaYH, (9) CSYH-CuCl2, (10) CSYH-Cu(NO3)2, (11) CSYH-CuSO4.
197
XRD analysis displayed the variations on the mineralogical structure of NaY
198
zeolites after acid treatment, Cu2+ modification, and core@shell experiment. The
199
peaks at 2θ=15.6°, 18.6°, 20.3°, 22.1°, 23.6°, 26.3° and 27.0° were confirmed as the
200
feature peaks of NaY zeolites;20 dipping in 0.5 mol/L HCl for 30 min and Cu2+ ion
201
exchange made the most characteristic peaks of NaY zeolites unchanged. However,
202
Figure. 2 (2)-(5) also suggested that the crystallinity of NaY decreased drastically;
203
besides the framework defects caused by Cu2+ modifying process, the dealuminization
204
effect of HCl played the most important role as depicted on 27Al MAS NMR spectra
205
(about 90% framework Al disappeared). To demonstrate this dealuminization effect of
206
HCl, we further dipped NaY zeolites in 0.5 mol/L HCl for 2 h. As was shown in
207
Figure. 2 (6), all the characteristic peaks on NaY zeolite had vanished, indicating that,
208
at this point, NaY owned no obvious crystal structures with only some amorphous
209
SiO2 and little amorphous Al2O3.
210
After these acid treated zeolites being coated by silicalite-1 crystals, the same
211
peaks of NaY zeolites at 2θ=15.6°, 18.6°, 20.3°, and 26.3° were also presented on
212
CSNaYH and CSCuYH. However, the intensity of their peaks were decreased, due to
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the coating process and the weak shielding effects of mesoporous shells on X-rays.26
214
Combined with the XRD spectra of NaYH and silicalite-1 crystals (Figure. 2 (7)), both
215
the peaks of NaY and silicalite-1 zeolites were observed on the core@shell structured
216
NaYH and CuYH (Figure. 2 (8)-(11)), especially the MFI-type peaks at 2θ=22-25°,
217
indicating silicalite-1 had been successfully coated on NaYH and CuYH.38
218
3.3. Mass increasement of NaYH and NaYH/CuYH after core@shell experiments.
14 12
in theory after filtration after centrifugation
in theory after filtration after centrifugation
mass gain (%)
mass gain (g)
140 120
10
100
8
80
6 4
5g NaY
60
4.33 4.41
40
2
20
0
219 220 221
160
Mass gain (%)
16
Mass gain (g)
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Industrial & Engineering Chemistry Research
NaYH
CSNaYH
CSYH CuCl2
CSYH Cu(NO3)2
CSYH CuSO4
0
Figure. 3. Mass increasement of NaY after HCl treatment and NaYH/CuYH after core@shell experiments (in theory: assuming that silicalite-1 was entirely coated around the core zeolites).
222
We have previously confirmed that HCl had a strong dealuminization effect on
223
NaY zeolite; and in order to determine this dealuminization effect more intuitively,
224
the mass variation of NaY before and after acid treatment were measured and shown
225
in Figure. 3. NaYH and the core@shell composites were collected from the mixtures
226
by two different methods in this experiment: filtration and centrifugation. Obviously,
227
there was a slight difference between filtration and centrifugation on NaYH; that was
228
because during the dealuminization process, partial NaY particle was broken into
229
smaller one ( 0.4, no
258
clear hysteresis loop or notable plateau was observed, guaranteeing NaY a
259
microporous property.39 After acid treatment, owing to the dealuminization effect of
260
HCl, some micropores in NaY zeolites were enlarged and finally presented the
261
mesoporous properties. As could be seen, NaYH and CuYH owned microporous as
262
well as mesoporous.
263
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250
3
200 175
266
320 280 240
125
200
100 75
160
50
120
25
80
0.00
0.25
0.50
0.75
1.00
0.00
0.25
0.50
0.75
1.00
P/P0 Figure. 4. Adsorption and desorption isotherms of N2 on adsorbents (shifted along y-axis). Table. 1. BET analysis of NaY, NaYH, CuYH, silicalite-1, as well as core@shell structures. Adsorbents NaY Silicalite-1 NaYH YH-CuCl2 YH-Cu(NO3)2 YH-CuSO4 CSNaYH CSYH-CuCl2 CSYH-Cu(NO3)2 CSYH-CuSO4
267 268
Silicalite-1 CSNaYH CSYH-CuCl2 CSYH-Cu(NO3)2 CSYH-CuSO4
360
150
0
264 265
400
NaY NaYH YH-CuCl2 YH-Cu(NO3)2 YH-CuSO4
225
Volume adsorbed (cm /g)
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
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1S
t
2S
micro
3S
meso
4V
t
5V mic
6D
a
7D
mic
(m2/g)
(m2/g)
(m2/g)
(cm3/g)
(cm3/g)
(nm)
(nm)
786.27 489.21 263.32 233.65 225.67 214.53 386.54 368.88 342.49 322.85
754.24 471.68 173.95 149.44 144.26 142.85 347.86 339.37 313.72 294.31
32.02 17.54 89.37 84.21 81.41 71.68 38.68 29.51 28.77 28.54
0.38 0.35 0.19 0.19 0.18 0.17 0.29 0.29 0.27 0.27
0.29 0.20 0.15 0.14 0.12 0.12 0.23 0.22 0.19 0.18
1.81 2.06 3.13 3.16 3.23 3.22 2.31 2.03 2.14 2.19
0.84 0.65 0.84 0.84 0.84 0.85 0.82 0.82 0.83 0.84
1: total surface area; 2: microporous surface area; 3: mesoporous surface area; 4: total pore volume; 5: pore volume of micropores; 6: average aperture; 7: pore size of micropores.
269
Table. 1 and Figure. 5 made further efforts to represent the structural properties
270
of these zeolites, such as St (the total surface area), Smicro, Smeso (micropores and
271
mesopores surface area), Vt (total pore volume), as well as the aperture distributions.
272
Compared with the parent NaY zeolites, the St of NaYH had sharply decreased by as
273
more as 66.5%. Meanwhile, the Smicro decreased by more than 77%; and in contrast,
274
the Smeso increased by 1.8 times, indicating that the dealuminization of HCl played a
275
great effect on the structure of NaY zeolites by removing framework Al. Besides,
276
owing to the collapsed structure, the Vt and Vmic of NaYH decreased, and the Da was
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enlarged. The BJH pore size distributions showed in Figure. 5 also demonstrated the
278
increased mesopores. After a further modification by Cu2+, compared to NaYH, the
279
structural properties of CuYH did not put up a much difference with only a slight
280
decrease in St, Smicro, Smeso Vt, Vmic and a minor increase in Da. Silicalite-1 shell
281
owned microporous as well as mesoporous according to Figure. 4. The surface area of
282
micropores in silicalite-1 occupied a leading position of total surface area (about 96%);
283
and what made silicalite-1 chosen as the shell basically depended on its microporous
284
aperture (about 0.65 nm), compared to NaY, NaYH, and CuYH (0.84, 0.84, and ~0.85
285
nm), which guaranteed silicalite-1 a shape selective capacity. When adsorbents were
286
coated with silicalite-1 shell, the adsorbates with a molecular size more than 0.65 nm
287
would be held back outside; thereby, the shape selective adsorption separation of
288
substances with different molecular sizes could be realized. NaY Silicalite-1 NaYH YH-CuCl2 YH-Cu(NO3)2 YH-CuSO4 CSNaYH CSYH-CuCl2 CSYH-Cu(NO3)2 CSYH-CuSO4
0.035
1.00
0.030
3 -1 -1 dV/dD (cm g nm )
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
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290
0.020 0.015
0.50
0.010 0.005
0.25
0.00
289
0.025
0.75
0.000 2
0
2
4
4 6 Aperture (nm)
6
8
8
10
Figure. 5. Distributions for aperture of different adsorbents (BJH method).
291
However, owing to the dealuminization effect of HCl, on the one hand, the total
292
pore volume of NaYH decreased from 0.38 to 0.19 cm3/g, which was bound to affect
293
the sulfur (DMDS) storage capacity. On the other hand, large amount of disappeared
294
framework Al made more Si elements exposure to the outside surface, and these
295
exposed Si would played an key role in growing silicalite-1 shell. Generally, at the
296
cost of a decreased pore volume, a more uniform and compact shell was achieved
297
(Figure. 6 and 7), providing NaYH and CuYH a higher degree on shape selective
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property to realize the removal of DMDS from MTBE.
299
3.5. SEM and TEM pictures for NaY, NaYH, CuYH and core@shell structures. (b)
(a)
2 um
(c)
1 um
(d)
0.5 um
um
0.5 um
300 301
Figure. 6. SEM pictures for (a) NaY, (b) NaYH, (c) CSNaYH, (d) CSYH-CuCl2.
(a)
(b)
100 nm
(c)
100 nm
~100 nm
(d) ~30 nm
302 303
100 nm
~30 nm
50 nm
Figure. 7. TEM pictures for (a) NaY, (b) YH-CuCl2, (c) CSNaYH, (d) CSYH-CuCl2.
304
After HCl treatment, Figure. 6 (b) exhibited a slightly damaged morphology of
305
NaYH zeolites, suggesting that the dealuminization effect could keep the original
306
skeleton of NaY basically unchanged compared with the regular shape of parent NaY
307
zeolites (Figure. 6 (a) and Figure. 7 (a)); in addition, after dealuminization, the surface
308
of NaY zeolite was no longer flat, leading to an improved outer surface area and more
309
silicon being exposed. After being coated, as shown in Figure. 6 (c and d), a clear
310
cladding structure could be observed that NaYH was enclosed by many fine
311
silicalite-1 crystalline grains which could be more intuitively showed up by TEM
312
pictures (Figure. 7 (c and d)); the thickness of the shell was of about 30-100 nm. Even
313
being homogeneously ion exchanged by Cu2+ (CuCl2) (Figure. 7 (b)), a clear and
314
smooth silicalite-1 shell could be still formed around the CuYH zeolite (Figure. 7 (d)).
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3.6. Analysis of element distribution on different adsorbents.
316
Table. 2 and Figure. S2 revealed the dealuminization effect of HCl more
317
intuitively by displaying the element content and distribution (mainly Si and Al ) of
318
NaY and the acid treated adsorbents. According to the ICP data, the molar ratio of
319
Si/Al was 2.41; while EDS data displayed a relatively larger deviation to be 2.48; that
320
was because the EDS detected only the surface element distribution of the sample,
321
while the ICP-OES analyzed the Si/Al ratio in the whole adsorbent by completely
322
dissolving the sample into aqueous solution.
323
Table. 2. Variety of Si, Al and Na element after acid treatment and core@shell experiment (ICP). Samples NaY NaYH YH-CuCl2 CSY-CuCl2 CSYH-CuCl2
324
Si
Al
★
★
28.3 35.7 36.8 30.8 42.9
11.3 4.6 4.5 8.5 2.1
Na
Si/Al
Al/Na
9.5 4 1.2 2.9 0.6
2.41 7.48 7.89 3.49 19.70
1.01 0.98 3.2 2.5 3
★
The unit of Si, Al, Na was mg/g.
★
325
After being treated by HCl, the Si/Al of NaYH was obviously increased by as
326
much as about twice from 2.41 to 7.48, indicating that abundant Al in NaY zeolites
327
were dissolved and removed after acid treatment. And massive loss of Al would
328
inevitably, on one hand, leave many vacancies around the surface enlarging the out
329
surface area of NaYH zeolites and providing more load locations for silicalite-1 shell;
330
on the other hand, expose more Si elements on the surface, which was the crystal
331
cores of silicalite-1 shell. After being ion-exchanged by CuCl2, the Si/Al of CuYH
332
remained almost the same (7.89, ICP; 8.12, EDS) compared to NaYH (7.48, ICP; 7.94,
333
EDS). while after the coating process, the Si/Al ratio of the corresponding core@shell
334
structures increased from 2.41 (2.48, EDS) to 3.49 (3.56, EDS) and 7.48 (7.94, EDS)
335
to 19.70 (21.48, EDS), respectively. Compared CSY-CuCl2 with CSYH-CuCl2, more
336
Si were detected in CSYH-CuCl2, indicating that HCl treatment could improve the
337
coating by providing more loading positions and crystal nucleus for silicalite-1.
338
In addition, the ratio of Al/Na was also detected and calculated in Table. 2. Na+
339
as the equilibrium charge, it was basically equivalent to the negative charge of
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framework Al in NaY and NaYH zeolite (Al/Na=1.01 and 0.98). As the Na+ being ion
341
exchanged by Cu2+, the loss of Na+ in YH-CuCl2 led to an increased Al/Na ratio to be
342
3.2. After been coated with silicalite-1 shell, the ratio of Al/Na was slightly reduced,
343
which may be attribute to the continuous ion exchange between Na+ and superfluous
344
Cu2+ adsorbed by NaY during core@shell experiment.
345
3.7. Cu2+ loading amount in different adsorbents.
346
Table. 3. Cu2+ amount (ICP) loaded in CuYH and corresponding core@shell structures. Cu2+
Concentration (aq, mol/L)
CuYH zeolite (mg/g)
core@shell composites (mg/g)
CuCl2 Cu(NO3)2 CuSO4
0.5 0.5 0.5
4.3 3.6 1.8
4.1 3.1 1.6
347
Many researches had proved that, as the adsorptive center, Cu2+ could adsorb
348
DMDS by π-complexation.40, 41 Thus, the loading amount of Cu2+ on zeolites would
349
directly affect the quantity of sulfur adsorbed. Via an Agilent 725 ICP-OES, the Cu2+
350
loading amount in NaYH zeolites were displayed in Table. 3. After an ion exchange
351
process in different Cu2+ solution (1 g: 20 ml, 0.5 mol/L Cu2+, 90 °C, 24 h), the Cu2+
352
amount loaded from CuCl2 showed the maximum in both CuYH and its core@shell
353
composites to be 4.3 and 4.1 mg Cu2+/g adsorbents. Actually, in order to complete ion
354
exchange between Cu2+ and Na+, Cu2+ should enter into the channel of NaYH zeolites
355
and reach the point where Na+ stood. However, to maintain the electroneutrality of the
356
solution, the anions (Cl-, NO3-, SO42-) were bound to follow and keep close to Cu2+ to
357
enter into the channel at the same time; thus, the molecular size of anions would play
358
a decisive role by limiting whether Cu2+ could enter the channels; in other words, if
359
the molecular size of anions were larger than some channels which were smaller than
360
the size of Cu2+, at this time, it would still be difficult for Cu2+ to get into smoothly.
361
From this point of view, owing to the fact that the molecular size of Cl-, NO3-, SO42-
362
increased in turn, the Cu2+ loading amount in NaYH zeolites would decrease
363
successively, which was in according with the results shown in Table. 3. In addition,
364
during the coating process (180 °C, 24 h) of synthesizing the CuYH@silicalite-1, a
365
fraction of the loaded Cu2+ in CuYH would be leached out, leading to a slight
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366
decreased Cu2+ loading amount in the corresponding core@shell composites. After
367
Cu2+ being loaded in NaYH zeolites, and used as adsorbents to remove DMDS from
368
MTBE, the Cu-O bonds could also be formed, which was easier to form than Cu-S,
369
lead to the fierce competition between DMDS and MTBE on NaYH and CuYH.
370
3.8. Analysis of FT-IR spectra on adsorbents. 1108
(a) (b)
1008
C-O-C
(c) (d) (e)
1230 C-S
(f) (g) (h) (i) (j)
2000
1619 H-OH
1800
1600
1400
1200
1000
800
600
-1
wave numbers (cm )
371 372 373 374
Figure. 8. The FT-IR spectra of different adsorbents after adsorbing DMDS in MTBE: (a) NaY, (b) NaYH, (c) YH-CuCl2, (d) YH-Cu(NO3)2, (e) YH-CuSO4, (f) silicalite-1, (g) CSNaYH, (h) CSYH-CuCl2, (i) CSYH-Cu(NO3)2, (j) CSYH-CuSO4.
375
After adsorbing DMDS, the FT-IR spectra of adsorbents were displayed in
376
Figure. 8. The bonds at 1619 cm-1 were confirmed as the -OH vibration of water
377
adsorbed in adsorbents;42 1230 cm-1 was the C-S stretching vibration; 1108 and 1008
378
cm-1 were the C-O-C stretching vibration. Owing to the fierce competition between
379
DMDS and MTBE, in MTBE solution, MTBE was much more easier to be adsorbed
380
than DMDS; Figure. 8 (a)-(e) exactly proved that no bonds were located at 1230 cm-1,
381
indicating little DMDS being adsorbed on NaY, NaYH or CuYH. As to silicalite-1
382
crystals, both C-S and C-O-C were recorded, suggesting that both DMDS and MTBE
383
were absorbed. After NaYH or CuYH being enclosed and coated by the shell, the C-S
384
bond could always be recorded (Figure. 8 (g-j)), suggesting that these synthesized
385
core@shell composites could adsorb DMDS in MTBE solution. However, these
386
detected C-S bonds was not enough to further confirm whether the core@shell
387
composites could selectively adsorb DMDS from MTBE, because there was difficulty
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388
in distinguishing if the C-S bonds came from the DMDS adsorbed on silicalite-1 shell
389
or the core zeolites. To test and verify the shape-selection characteristic of the
390
synthesized core@shell structured composites, the active adsorption data was
391
collected by both static and dynamic activity tests.
392
3.9. Desulfurization performances on core@shell zeolites.
393
3.9.1. Analysis on static active data in static state. As shown in Figure. 9, in the MTBE solution with a raw DMDS concentration of
395
748.52 mg/L, by static adsorption tests, the adsorption capacities of DMDS on
396
different adsorbents were collected. Obviously, a great difference could be observed
397
between adsorbents with and without silicalite-1 shell. After adsorption, as could be
398
seen, those adsorbents with no silicalite-1 coatings (NaY, NaYH and CuYH) showed a
399
negative desulfurization by adsorbing the solvent (MTBE) instead of the solute
400
(DMDS); because of the intense competition effect between DMDS and MTBE on
401
these adsorbents32; owing to a much larger quantity of MTBE than DMDS, on these
402
adsorbents, MTBE was preferentially adsorbed, leading to an increased sulfur content,
403
which was higher than 748.52 mg/L (Figure. 9 a, c-f).
Raw material sulfur concentration:748.52
1000
800 789.92 742.34 779.72
831.83 823.02
34.585
26.921
517.52 402.67
400
435.81
0
0.618 -4.14
a
20
479.31 10
0
0
30
23.127
785.22
600
40
31.271
748.52
200
404 405 406 407
mgs/gadsorbent
mg/L
1200
b
-3.12
c
-8.331 -7.45
d
e
-3.67
f
Sulfur adsorbtion capacity (mgs/gadsorbent)
394
After adsorbtion (mg/L)
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
Industrial & Engineering Chemistry Research
-10
g
h
i
j
Figure. 9. Adsorption capacity of sulfur on different adsorbents in desulfurizing DMDS from MTBE: (a) NaY, (b) NaYH, (c) silicalite-1, (d) YH-CuCl2, (e) YH-Cu(NO3)2, (f) YH-CuSO4, (g) CSNaYH, (h) CSYH-CuCl2, (i) CSYH-Cu(NO3)2, (j) CSYH-CuSO4.
408
The adsorption capacities of sulfur on CSNaYH, CSYH-CuCl2, CSYH-Cu(NO3)2,
409
and CSYH-CuSO4 were also calculated and displayed in Figure. 9 g-j. After coating
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410
silicalite-1, a significant capacity (23.127, 34.585, 31.271, and 26.921mgs/gadsorbents) in
411
desulfurization of DMDS from MTBE was obtained, which was far greater than that
412
of silicalite-1 alone as the adsorbent (0.618 mgs/gadsorbents), proving the remarkable role
413
of silicalite-1 shell in selective adsorbing DMDS from MTBE. And compared Figure.
414
9 d (YH-CuCl2) with h (CSYH-CuCl2), based on silicalite-1 shell, the adsorption
415
capacity of sulfur demonstrated a wide range of improvements from -8.331 to 34.585
416
mgs/gadsorbents, which further expounded and proved that after being coated by
417
silicalite-1 crystals, the synthesized core@shell composites owned the capacity to
418
selectively adsorb DMDS from MTBE by preventing MTBE from migrating into the
419
adsorbents (shape selective function of silicalite-1 shell), while letting through only
420
DMDS and adsorbing DMDS inside the adsorbents (adsorption and storage function
421
of the core zeolites).
422
Also, considering the effect the raw material sulfur (DMDS) concentration on the
423
sulfur adsorption capacities of the synthesized core@shell composites, the sulfur
424
adsorption capacity and desulfurization rate of CSYH-CuCl2 in different DMDS
425
concentration of MTBE solution was conducted. As shown in Table S1, the DMDS
426
concentration in MTBE solution was quantified from 268.71 to 856.47 mg/L. With
427
the increase of DMDS concentration, the sulfur adsorption capacity of CSYH-CuCl2
428
was in a uptrend. However, when the concentration of DMDS was more than 451.3
429
mg/L, the sulfur adsorption capacity of CSYH-CuCl2 was kept at 34.162 or so. And as
430
the concentration of DMDS was 268.71 mg/L, the DMDS was adsorbed of only
431
97.2%, owing to the diffusion limitation of static test itself.
432
3.9.2. Analysis on active data in dynamic state.
433
To further evaluate the practical application potential of these core@shell
434
structured adsorbents in desulfurizing DMDS from MTBE, they were pressed and
435
broken into particles, then loaded in a quartz column reactor to collect the dynamic
436
active data every half an hour as shown in Figure. 10. As could be seen, the
437
desulfurization curve of silicalite-1 also confirmed it could selectively adsorb DMDS
438
from MTBE in a small degree. Overall, as the time going on, the desulfurization of all
439
the adsorbents displayed a downside; however, bounded by the desulfurization curve
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440
of silicalite-1, adsorbents with and without core@shell structures showed a significant
441
distinction in desulfurization rate. 100
Desulfurization rate of DMDS(%)
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
Industrial & Engineering Chemistry Research
442 443 444 445
80
a b c d e f g h i j
60 40 20 0 -20 0
1
2
3
4
Time (h) Figure. 10. Desulfurization rate of adsorbents: (a) NaY, (b) NaYH, (c) silicalite-1, (d) YH-CuCl2, (e) YH-Cu(NO3)2, (f) YH-CuSO4, (g) CSNaYH,(h) CSYH-CuCl2, (i) CSYH-Cu(NO3)2, (j) CSYH-CuSO4.
446
Due to the competitive adsorption of DMDS and MTBE, NaY, NaYH as well as
447
CuYH zeolites displayed very poor desulfurization rate throughout the tests, indicating
448
there was no desulfurization capacity in adsorbing DMDS from MTBE on these
449
adsorbents, which was consistent with the static active data analysis. On the contrary,
450
the adsorbents with core@shell structure, such as CSYH-CuCl2, CSYH-Cu(NO3)2, and
451
CSYH-CuSO4, showed a remarkably improved desulfurization rate by 100%
452
desulfurization for about 2.5 h; CSNaYH could also keep this desulfurization level for
453
about 1.5 h. among these core@shell composites, CSYH-CuCl2 showed the best
454
performance by desulfurizing DMDS at 80% level for at least 4.5 hours. And the
455
active life of these core@shell adsorbents would quickly diminish after about 3-3.5 h.
456
3.10. Analysis on desulfurization mechanism.
457
Figure. 11 intuitively presented the dealuminization effect, the silicalite-1 shell
458
growth and the selective adsorption process of DMDS. The NaY core owned 18
459
four-membered rings, 4 six-membered rings and 4 twelve-membered rings in a unit
460
cell with an aperture of about 0.9 nm in main channel. As depicted in Figure. 11, there
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461
were three positions (NaⅠ, NaⅡ, NaⅢ) for Na+ to balance the skeleton negative
462
charge in Y zeolite; when ion exchange Na+ with Cu2+, NaⅡand NaⅢ would be
463
exchanged preferentially than NaⅠwhich was in the center of hexagonal prism cage.
464
After being ion exchanged by Cu2+, owing to its divalent valence state, the adsorbed
465
or bound water in Y zeolite would form hydrated ions with Cu2+ (Cu(H2O)2+) or
466
dissociate into H+ and Cu(H2O)+ and then exist steadily as CuY.
: Si
NaY:
: Al
Si/Al = 2.4
silicalite-1 crystal
467 468 469 470
Figure. 11. The dealuminization of HCl and the silicalite-1 shell growth on CuYH as well as the selective desulfurization mechanism of adsorbing DMDS from MTBE on CuYH@silicalite-1.
471
The Si/Al (molar ratio) of NaY zeolite used in this study was 2.4. After being
472
acid treated the Si/Al had been significantly increased as discussed in element
473
distribution analysis (section 3.6), manifesting as the framework Al being transferred
474
into the extra-framework Al and then removed, leaving many hydroxyl nests (or
475
cavities). when this dealuminized NaY or CuY was coated with silicalite-1 by
476
hydrothermal methods, new silicon sources (from TEOS) would be admitted by the
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Industrial & Engineering Chemistry Research
477
hydroxyl nests and extensively grow along the surface to finally form a complete shell,
478
whose maximum aperture was about 0.65 nm.
479
Except for the competition, the different size of MTBE (0.74 nm) and DMDS
480
(0.37 nm) had made it possible in shape selective desulfurization.43,
481
synthesized core@shell composites were used to adsorb DMDS in MTBE solution,
482
both DMDS and MTBE would contact the silicalite-1 shell preferentially; by virtue of
483
small size, DMDS could diffuse and pass rapidly through silicalite-1 shell, leaving the
484
larger sized and branched structured MTBE being shut out. By metal-S bonds DMDS
485
could be fixed and stored inside the core zeolites; with the continuation of adsorption,
486
the concentration of DMDS would constantly decline and eventually disappeared to
487
achieve the purpose of shape selective desulfurization.
488
4. Conclusion
44
When these
489
At the cost of a decreased surface area, acid treatment had been proved a
490
significant mean to increase the Si/Al ratio of NaY zeolite by the dealuminization
491
effect of HCl from 2.48 to 7.94 (EDS data), which was quite beneficial for the
492
growing of silicalite-1 shell for the sake of more Si elements being exposed on NaY
493
surface to act as the crystal cores of silicalite-1 shell; in addition, the loss of Al after
494
acid treatment would inevitably leave many vacancies around the surface enlarging
495
the out surface area of NaYH zeolites and providing more load locations for
496
silicalite-1 shell as well. After core@shell process, the notable increased Si/Al in
497
corresponding core@shell composites further demonstrated the remarkable role of
498
acid treatment in coating process. As the core, depending on forming the Cu-S bonds
499
within DMDS and Cu2+, CuYH displayed a larger adsorption capacity of sulfur than
500
both NaY and NaYH in storing DMDS. Relying on silicalite-1 shell (shape selectivity)
501
and CuYH core (adsorption and storage centers), CuYH@silicalite-1 displayed a great
502
advantage on desulfurization of DMDS at the present of MTBE; CSYH-CuCl2 had
503
possessed the best adsorption capacity of sulfur to be 34.585 mgs/gadsorbent and 100%
504
desulfurization could be realized and kept for as long as 3 h. After 4.5 hours, more
505
than 80% desulfurization rate was still achieved.
506
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507
Associated Content
508
The X-ray diffraction patterns of silicalite-1 and small particles that filtered out
509
after filtration (Figure S1); EDS analysis of (a) NaY, (b) NaYH, (c) YH-CuCl2, (d)
510
CSY-CuCl2, and (e) CSYH-CuCl2 (Figure S2); as well as the sulfur adsorption
511
capacity and desulfurization rate of CSYH-CuCl2 in different DMDS concentration of
512
MTBE solution (Table S1) were provided in the Supporting Information file.
513
Acknowledgments
514
Project financially supported by the National Science Foundation for Young
515
Scientists of China (No. 21706065); the Open Project of State Key Laboratory of
516
Chemical Engineering (SKL-ChE-18C02); China Postdoctoral Science Foundation
517
(NO.2017M621389), Shanghai Sailing Program (NO.18YF1406300), and Explore
518
and Research Foundation for Youth Scholars of Ministry of Education of China (NO.
519
222201814011).
520
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TOC graphic
: Si
NaY:
: Al
Si/Al = 2.4
silicalite-1 crystal
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