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Study on the Pyrolysis Characteristics of a Typical Low Rank Coal with Hydrothermal Pretreatment Hui Chang, Zhuangzhuang Zhang, Luyao Qiang, Ting Gao, Tingwei Lan, Ming Sun, Long Xu, and Xiaoxun Ma Energy Fuels, Just Accepted Manuscript • DOI: 10.1021/acs.energyfuels.8b04312 • Publication Date (Web): 01 Apr 2019 Downloaded from http://pubs.acs.org on April 2, 2019
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Energy & Fuels
1
Study on the Pyrolysis Characteristics of a Typical Low Rank Coal with
2
Hydrothermal Pretreatment
3 4
Hui Chang, Zhuangzhuang Zhang, Luyao Qiang, Ting Gao, Tingwei Lan, Ming Sun, Long Xu, Xiaoxun Ma
5
School of Chemical Engineering, Northwest University, International Scientific and
6
Technological Cooperation Base of the Ministry of Science and Technology (MOST)
7
for Clean Utilization of Hydrocarbon Resources, Chemical Engineering Research
8
Center of the Ministry of Education (MOE) for Advanced Use Technology of Shanbei
9
Energy, Shaanxi Research Center of Engineering Technology for Clean Coal
10
Conversion, Collaborative Innovation Center for Development of Energy and
11
Chemical Industry in Northern Shaanxi, Xi'an, 710069, PR China
12
ABSTRACT: Coal pyrolysis characteristics are closely related to its structure and
13
composition, and revealing the relationship between them is essential for deep
14
understanding the pyrolysis mechanism. Therefore, in this work, Shendong coal
15
(SDC) was treated by hydrothermal pretreatment (HTP) to change its structure and
16
composition, and the influence of the changes on pyrolysis characteristics were
17
investigated. The changes in physicochemical structure and composition of treated
18
coal samples were characterized by N2 isothermal adsorption, Fourier transform
19
infrared (FTIR) spectroscopy,
20
diffraction (XRD), and inductively coupled plasma optical emission spectrometry
21
(ICP-OES). The pyrolysis experiments of raw and treated coal samples were carried
13C
nuclear magnetic resonance (NMR), X-ray
Corresponding author. E-mail address:
[email protected] 1
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22
out in a fluidized bed reactor. Then, the pyrolysis product distribution, the gas
23
composition, the tar chemical composition and properties, and the char gasification
24
behaviors were comprehensively studied. The experimental results showed that the
25
HTP was effective in surface area and pore volume increases, oxygen removal and
26
transfer, hydrogen radical introduction, and water soluble inorganic metals removal
27
for SDC. Correspondingly, the distribution and composition of pyrolysis products of
28
treated coal samples changed. The pyrolysis gas quality was improved with more
29
formations of H2 and CH4. The tar yield and N-hexane insoluble component
30
increased. More oxygen was enriched in macromolecular tar instead of gas and char
31
products, enhancing the char gasification activity. In addition, the structure-activity
32
relationship between the changes in coal structure and composition and the pyrolysis
33
characteristics was revealed in this work.
34
KEYWORDS: Hydrothermal pretreatment; Structure; Coal pyrolysis; Product
35
distribution; Pyrolysis mechanism
36
1. INTRODUCTION
37
Though efforts have been made to transform energy structure and reduce carbon
38
dioxide emission, the proportion of coal in China’s energy consumption is still up to
39
60.4 % in 2017.1 Low rank coals are and will be a master energy source in the
40
foreseeable future due to its abundance in China. The efficient and clean utilization of
41
low rank coals is imminent. Coal pyrolysis has attracted widespread attentions in
42
recent years since it is the initial step in gasification, liquefaction, coking, and
43
combustion process.2,3 Middle or low temperature pyrolysis is the most optimum 2
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method for low rank coals utilization, obtaining fuel gases, semi-coke, liquid fuels,
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and other high value-added chemicals.4 Considerable studies have shown that the coal
46
pyrolysis characteristics are influenced by the coal types and operating conditions,
47
such as pyrolysis final temperatures, reaction atmospheres, heating rates, residence
48
times, and different reactor types.5-9 Basically, the coal pyrolysis characteristics are
49
principally governed by its structure and composition, and a good knowledge of the
50
relationship between them is essential for deep understanding the pyrolysis
51
mechanism. Pretreatment is confirmed to be a promising method for causing changes
52
in physicochemical structure and composition of low rank coals,10-13 which
53
correspondingly influences the thermal conversion behaviors.
54
So far, several pretreatments for low rank coals have been adopted,10 mainly
55
including organic solvent thermal pretreatment, thermal pretreatment, and
56
hydrothermal pretreatment (HTP). Organic solvent thermal pretreatment was effective
57
in dewatering and deoxygenation of brown coals,11,12 which advanced the
58
hydro-liquefaction reactivity, but reduced the pyrolysis reactivity. Thermal
59
pretreatment was effective in deoxygenation but increased the cross-linking degree of
60
brown coals, resulting in the decrease of pyrolysis reactivity.11
61
HTP is another widely used pretreatment method for low rank coals.13 Compared
62
to organic solvent pretreatments, the hydrothermal pretreatment is simpler, and the
63
separation of water from coal sample is easier. After HTP, water can be removed in
64
the liquid form irreversibly due to the decomposition of oxygen-containing functional
65
groups. Zhundong coal was effectively upgraded with the increases in surface area 3
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66
and pore volume under 300 oC.14 Amounts of carboxyl, alcoholic hydroxyl, ether, and
67
carbonyl groups decreased in coal, whereas no obvious changes in phenolic hydroxyl
68
groups were observed owing to its high bonding energy.15,16 Some heavy metals, such
69
as Hg, Se, and As, can also be removed by the strong solubility of sub-critical
70
water.17,18 The HTP greatly improved the coal combustion characteristics, especially
71
above 250 oC of the pretreatment temperatures.19 The slurrying ability and rheological
72
behaviors of low rank coals were also enhanced,20 as well as the liquefaction
73
behaviors, particularly at the pretreatment temperature of 250 oC.21,22
74
Previous studies mainly focused on how the HTP changed the physicochemical
75
structure and composition of low rank coals,13-18 and further enhanced the coal
76
slurrying ability, liquefaction and combustion behaviors.19-22 A few investigations
77
have focused on the effect of HTP on coal pyrolysis characteristics. Ge et al.
78
researched the effect of HTP on pyrolysis characteristics of low rank coals by
79
TG-FTIR and found that the pyrolysis activity declined but more phenol and CH4
80
were formed.23 Liu et al. found that the tar yield of treated coal samples increased,24
81
while higher pretreatment temperatures (> 260
82
decreasing.25,26 However, the investigation on the relationship between the coal
83
pyrolysis characteristics and the changes in its structure and composition caused by
84
HTP was insufficiently conducted.
oC)
resulted in the tar yield
85
In this work, a comprehensive study of the effect of HTP on Shendong coal
86
(SDC) pyrolysis characteristics was conducted. The HTP of SDC at different
87
pretreatment temperatures and water to coal (W/C) ratios was performed from 4
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200-300 oC. The changes in physicochemical structure and composition of treated
89
coal samples were characterized by BET, FTIR, 13C NMR, XRD, and ICP-OES. The
90
pyrolysis experiments of SDC and treated coal samples were carried out at 600 oC in a
91
fluidized bed reactor. Then, the pyrolysis product distribution, the gases composition,
92
the tar properties, and the char gasification reactivity were analyzed in detail. Element
93
analyzer, synchronous UV-fluorescence spectroscopy, and GC-MS were employed to
94
characterize the tar properties. Additionally, the char gasification reactivity was
95
evaluated. Finally, the structure-activity relationship between the changes in structure
96
and composition and the pyrolysis characteristics was discussed.
97
2. EXPERIMENTAL METHODS
98
2.1. Experimental Materials
99
Shendong coal (SDC), a typical low rank coal, from China was crushed and
100
ground to 40-100 μm, vacuum dried at 105 oC for 12 h and sealed in cabinet filled
101
with N2.
102
The HTP was performed in a sealed autoclave (500 mL). In each run, 30 g SDC
103
and 90 mL deionized water were placed in the autoclave, and purged with 1.0 MPa of
104
N2 (purity, >0.9999) for three times to remove air residues. Then, the pressure was
105
reduced to 0.1 MPa of N2. Subsequently, the reactor was heated at a rate of 3.5 oC/min
106
and a stirring rate of 300 r/min, from ambient temperature to designed temperature
107
(200, 220, 240, 260, and 300 oC), holding for 1 h, respectively. After the autoclave
108
cooling down to ambient temperature, the residues were separated by using filtration
109
method, dried in a vacuum oven at 105 oC for 12 h, and preserved in cabinet filled 5
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with N2. All treated coals were marked with HTP-200, HTP-220, HTP-240, HTP-260,
111
and HTP-300, respectively, based on the pretreatment temperatures. Different water
112
to coal ratios (W/C, volume of deionized water to mass of coal, mL/g) at 240 oC were
113
performed.
114
2.2. Pyrolysis Experiment
115
Pyrolysis experiments were implemented in a powder-particle fluidized bed
116
reactor (in Figure 1), with silica sand (180-360 nm) as the bed material. The minimum
117
fluidization velocity and carrying velocity of bed material were 0.17 and 2.84 m/s,
118
respectively. The particle size of feedstock was 40-100 nm, with the calculated
119
carrying velocity of 0.16 m/s. Then, 0.20 m/s was designed as the operating
120
superficial gas velocity, and the fluidizing bed height was 13.5 cm. Briefly, 4.00±0.05
121
g of the sample pyrolyzed at 600 oC. N2 gas was employed as pyrolysis atmosphere,
122
consisting of feeding gas and fluidizing gas, with a flow rate of 1.20 L/min and 0.6
123
L/min, respectively. When the specified temperature was reached, the coal sample
124
was carried by feeding gas entering into the reactor. Then, the volatiles and char were
125
carried out of reactor and passed through a cyclone, after which the char was gathered
126
in collecting bottles. Then, the tar was collected via cold traps (alcohol condensation
127
bath at -40 oC). Followed by, the uncondensed gases were quantitatively monitored by
128
a GC device (Agilent Micro 3000), equipped with two conductivity (TCD) detectors,
129
a capillary column (PLOT-Q), and 5A molecular sieve, and the gas yield was
130
calculated by difference. To ensure that the results are accurate, all pyrolysis
131
experiments were repeated more than three times and the experimental results were 6
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132 133
Energy & Fuels
repeatable and deterministic. The coal pyrolysis products yields were obtained by the formulas (1)-(4) below. 𝑚𝑡𝑎𝑟 𝑎𝑛𝑑 𝑤𝑎𝑡𝑒𝑟 ― 𝐶𝑤 × 𝑚𝑙
(1)
134
𝑊𝑡𝑎𝑟 =
135
𝑊𝑤𝑎𝑡𝑒𝑟 =
136
𝑊𝑐ℎ𝑎𝑟 = 𝑚𝑐𝑜𝑎𝑙 × 100%
(3)
137
𝑊𝑔𝑎𝑠 = (1 ― 𝑊𝑡𝑎𝑟 ― 𝑊𝑤𝑎𝑡𝑒𝑟 ― 𝑊𝑐ℎ𝑎𝑟) × 100%
(4)
138
where mtar and water is the mass of liquid product, g; ml, is the mass of dichloromethane
139
solution of liquid product, g; cw is the water content of dichloromethane solution, g,
140
which was measured by micro-moisture meter based on K-F Coulomb Method; mcoal
141
and mchar are the mass of coal and char on dry and ash-free basis, respectively, g.
𝑚𝑐𝑜𝑎𝑙 𝐶𝑤 × 𝑚𝑙 𝑚𝑐𝑜𝑎𝑙
× 100%
(2)
× 100%
𝑚𝑐ℎ𝑎𝑟
5
7
5
6 9
11 12
10
4
Gas
8
3
3
F
2
Agilent Micro 3000
2
1
F P
13
N2
P
1.Valve of N2 2.Pressure meter 3.Gas mass flowmeter 4.Coal feeding device 5. Temperature controller 6.Pyrolysis furnace 7. Heat tracing belt
142 143 144 145 146 147
8.Powder-particle fluidized bed 9.Cyclone separator 10.Semi coke bottle 11.Condensation collecting bottle 12.Wet flowmeter 13.GC analyzer
Figure 1. The scheme of powder-particle fluidized bed equipment for pyrolysis. 2.3. Analysis Method The ultimate and proximate analysis of each sample were measured by SDTGA5000a (Sundy Ltd., China) and EL-Ⅲ analyzer (Vario Ltd., Germany). The minerals in coal samples were analyzed by A D/MAX-3C diffractometer 7
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148
(Rigaku Ltd., Japan) with Cu Ka radiation from 5o to 70o, with a step size of 0.02o.
149
The ICP-OES (PerkinElmer Company, America) was applied to determine the content
150
of designated metals.
151
The pore structure parameters of each sample were determined by ASAP2460
152
physisorption apparatus (Micromeritics Ltd., America). Brunauer–Emmet–Teller
153
(BET) equations and Barrett–Joyner–Halenda (BJH) method were respectively used
154
to determine the specific surface area and the pore volume of each sample.
155
Main organic functional groups of each sample were detected by Vertex 70
156
infrared spectrum analyzer (Bruker Company, Germany) and solid-static
157
DP/MAS NMR spectrometer (Bruker AVANCE III 600, Germany).
13C
NMR
158
The composition of tar samples was analyzed by Shimadzu GC-MS-QP 2010
159
Plus equipment. The flow rate was 1.0 mL/min, with a split ratio of 10:1. The oven
160
temperature program was set as follows: began at 40 oC for 4 min, heated to 70 oC at
161
4 oC/min (holding for 2 min), heated to 200 oC at 10 oC/min (holding for 3 min), and
162
finally heated to 300 oC at 4 oC/min (holding for 5 min). The injection and ion-source
163
temperatures were set at 300 and 230oC respectively. The mass spectrometer was set
164
in the electron ionization (EI) mode at 70 eV with m/z from 50 to 500. The
165
compounds were identified in the light of NIST08 and NIST08s library datas via
166
probability matching method. The relative content of compounds was calculated using
167
the peak area normalization method.
168
The aromatic ring condensation degree of tar samples was examined by
169
Synchronous UV-fluorescence spectroscopy (RF-5301) with the initial excitation 8
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170
wavelength of 220 nm, and the synchronous emission spectra was within 300~700
171
nm.
172
The char gasification was performed in a fixed bed reactor coupled with infrared
173
gas analyzer (SIELINS Ltd., China). 300 mg of each sample was placed in the silicon
174
tube and heated from 30 to 900 oC at a heating rate of 30 oC/min, holding for 90 min
175
at 900 oC. The gasification agent CO2 and carrier gas N2 were at a flow rate of 30
176
mL/min and 40 mL/min, respectively. Then, the CO, CO2, H2, and CH4 were detected
177
by infrared gas analyzer. The char gasification yield was obtained by the formula (5)27
178
as follows:
179
W𝑔𝑎𝑠𝑖𝑓𝑖𝑐𝑎𝑡𝑖𝑜𝑛 𝑦𝑖𝑒𝑙𝑑 =
180
where mchar and mresidue are the mass of the char sample and residue after gasification,
181
respectively, g; 𝑀𝑎𝑑 and 𝐴𝑎𝑑 are the moisture and ash content of char sample on the
182
air dry base, g.
𝑚𝑐ℎ𝑎𝑟 ― 𝑚𝑟𝑒𝑠𝑖𝑑𝑢𝑒
(5)
𝑚𝑐ℎ𝑎𝑟 × (1 ― 𝑀𝑎𝑑 ― 𝐴𝑎𝑑)
The gasification reactivity was evaluated by the formula (6)28 as follows:
183
0.5
(6)
184
R𝑖 = 𝜏0.5
185
where 𝜏0.5 is the time that the fixed carbon conversion in char samples reached 50 %,
186
min.
187
3. RESULTS AND DISCUSSION
188
3.1. Influence of HTP on Coal Composition
189 190 191
9
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Table 1. Proximate and ultimate analyses of SDC and treated coal samples.
192
Samples
SDC
HTP-200
HTP-220
HTP-240
W/C ratio
0:1
3:1
3:1
1:1
2:1
3:1
HTP-260
HTP-300
4:1
3:1
3:1
Proximate analysis (wt%) Mad
15.3
7.1
7.5
7.6
8.1
7.8
7.48
6.6
6.2
Ad
9.5
7.8
7.5
7.7
7.6
7.58
7.58
7.3
7.1
Vdaf
35.6
35.4
35.4
35.1
35.1
35.1
35.1
34.6
34.2
FCdaf*
64.4
64.6
64.6
64.7
64.8
64.9
64.9
65.5
65.8
Ultimate analysis (wt%, daf) C
77.8
78.9
79.3
79.2
79.3
79.2
79.4
79.5
79.9
H
4.7
4.8
4.9
5.0
4.9
5.0
4.9
4.8
4.9
N
1.0
1.3
1.2
1.2
1.1
1.2
1.2
1.2
1.2
S
0.4
0.7
0.6
0.6
0.6
0.7
0.6
0.6
0.5
O*
16.1
14.3
14.0
14.0
14.1
13.9
13.9
13.9
13.5
Atomic ratio and calorific value
193
*:
AO/C
0.16
0.14
0.13
0.13
0.13
0.13
0.13
0.13
0.13
AH/C
0.73
0.72
0.75
0.76
0.74
0.76
0.74
0.73
0.73
Qb,ad(MJ/kg)
27.3
30.6
30.6
30.5
30.4
30.5
30.7
31.0
31.2
By difference.
194
The proximate and ultimate analyses of samples are shown in Table 1.
195
Obviously, SDC had higher moisture and oxygen contents. After HTP, the calorific
196
value increased from 27.33 MJ/kg of SDC to 31.19 MJ/kg of HTP-300. The oxygen
197
to carbon (O/C) ratio decreased, while the hydrogen to carbon (H/C) ratios of
198
HTP-220 and HTP-240 increased. Thus indicated that the HTP decomposed the
199
oxygen-containing functional groups and introduced hydrogen radical to coal matrix
200
with decreasing cross-linking degree.11,29 The volatile matter content changed slightly 10
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201
below 260 oC of the pretreatment temperatures and decreased obviously above 260
202
oC,
203
HTP.13,30 The solid yields (dry and ash-free base) after the HTP were 98.8 %
204
(HTP-200), 98.5 % (HTP-220), 97.7 % (HTP-240), 97.3 % (HTP-260), and 96.4 %
205
(HTP-300), respectively. And the hydrogen content of HTP-240 was the highest.
206
Therefore, 240
207
pretreatments of different W/C ratios at 240 oC were conducted and no obvious
208
discrepancy was observed on the composition of treated coal samples, especially
209
above 3:1. Hence, the W/C ratio in this paper was mainly based on 3:1.
due to the cleavage of aliphatic hydrocarbons side chains above 260 oC by
oC
was the optimum pretreatment temperature. Additionally,
c b
a
b a
a:quartz, b:kaolinite, c:muscovite, d:siderite, e:xanthophyllite
c d ea a
a a ab
Intensity (a.u.)
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
Energy & Fuels
a
SDC HTP-200 HTP-220 HTP-240 HTP-260 HTP-300
10
210 211
20
30
40 50 2 (°)
60
70
80
90
Figure 2. XRD spectra of SDC and treated coal samples.
212
The ash content of treated coal samples decreased due to the dissolution of the
213
minerals by HTP.14,31-33 As the XRD spectra displayed in Figure 2, the intensities of
214
kaolinite, muscovite, and siderite peak in treated coal samples decreased,
215
corresponding to the composition of designated metals in each sample (in Table 2).
216
Therefore, the cross-linking points between carboxyl and AAEM species in treated
217
coal samples declined.34,35 Furthermore, the concentration of Hg also decreased, from
218
8.2 × 10-3 mg/gcoal,daf (SDC) to 0.1 × 10-3 mg/gcoal,daf (HTP-300), as well as As from 11
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23.1 × 10-3 mg/gcoal,daf (SDC) to 10.7 × 10-3 mg/gcoal,daf (HTP-300).
220
Table 2. Composition of designated metals in SDC and treated coal samples by
221
ICP-OES. Content (mg/gcoal,daf)
Samples
Content ( × 10 ―3mg/gcoal,daf )
Na
K
Mg
Ca
Fe
Al
Hg
As
SDC
1.5
1.9
0.5
7.4
3.8
8.7
8.2
23.1
HTP-200
1.1
1.3
0.5
6.6
3.7
7.7
5.6
22.7
HTP-220
0.8
1.1
0.4
5.9
2.9
7.5
4.5
22.0
HTP-240
0.9
1.3
0.5
6.4
3.2
7.3
2.6
19.9
HTP-260
0.5
1.0
0.4
5.4
3.0
6.2
1.4
15.7
HTP-300
0.6
1.1
0.4
5.7
3.0
6.3
0.1
10.7
Table 3. Composition of released gases during HTP.
222
Composition( × 10-3mmol/gcoal,daf)
Samples H2
CH4
CO
CO2
C2+C3
HTP-200
0.06
0.02
1.39
8.82
0.01
HTP-220
0.06
0.04
1.67
10.13
0.01
HTP-240
0.06
0.04
1.82
10.76
0.02
HTP-260
0.07
0.08
2.16
11.74
0.02
HTP-300
0.09
0.09
2.71
12.89
0.04
223
Table 3 shows the composition of released gases during HTP. With the rising of
224
pretreatment temperatures, the CO2 relative evolution increased from 8.82 × 10-3
225
mmol/gcoal,daf (HTP-200) to 12.89 × 10-3 mmol/gcoal,daf (HTP-300), due to the cleavage
226
of carboxyl functional groups. The fracture of methoxy and aldehyde functional
227
groups weakly bonded to the matrix led to the increase of CO relative evolution from
228
1.39 × 10-3 mmol/gcoal,daf (HTP-200) to 2.71 × 10-3 mmol/gcoal,daf (HTP-300).35 In 12
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229
addition, the relative evolution of C1~C3 increased along with the rising of
230
pretreatment temperatures because of the thermal rupture of weak covalent bonds,
231
such as aliphatic side chains and bridges.
232
3.2. Influence of HTP on Coal Structure
233
Table 4. Specific surface area and pore structure parameters of coal samples. Surface Area
Pore Volume
Average Pore Diameter
(m2/g)
(cm3/g)
(nm)
SDC
2.01
9.91 × 10-3
19.73
HTP-200
3.81
8.84 × 10-3
9.30
HTP-240
7.31
1.20 × 10-2
6.58
HTP-300
7.81
1.22 × 10-2
6.33
Samples
234
The specific surface area and the pore structure parameters of coal samples are
235
shown in Table 4. The surface area and pore volume of treated coal samples increased
236
with the rising of pretreatment temperatures, whereas the average pore diameters
237
sharply decreased. According to the pore size distribution of the SDC and treated coal
238
samples (in Figure S1 and S2), smaller mesopores in the treated coals were evolved
239
probably from hitherto closed pores and micropores, and more distribution peaks
240
appeared from 2 to 20 nm compared with SDC. This could be attributed to gases
241
evolution during HTP caused by the cleavage of oxygen-containing functional groups
242
and aliphatic hydrocarbon side chains. The disintegration of macropore was attributed
243
to the shrinkage forces caused by the hydrothermal treatment.
244
The FTIR analysis of all samples are depicted in Figure 3. Each infrared
245
spectrum can be divided into four sections as reported in previous literatures:37-39
246
3600-3000 cm-1 (-OH groups stretching vibration), 3000-2800 cm-1 (aliphatic C-H 13
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247
groups stretching vibration), 1800-1000 cm-1 (oxygen-containing functional groups
248
stretching vibration) and 900-700 cm-1 (aromatic C-H groups out-of-plane bending
249
vibration). Taking SDC as an instance, the curve-fitted FTIR spectra of four sections
250
by Gaussian method with PeakFit® (Version 4.12) were exhibited in Figure 4. The
251
same method was adopted for treated coal samples, which was not showed here.
HTP
Absorbance (a.u.)
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 14 of 30
252 253
-2 0 0
SDC HTP
-2 2 HTP 0 -2 H TP 40 -2 6 0 HTP -3 0 0
4000 3500 3000 2500 2000 1500 1000 -1 Wavenumbers (cm )
500
Figure 3. Infrared spectra of SDC and treated coal samples.
254
Several parameters19,24,38,39 related to different functional groups were calculated
255
via the areas of FTIR spectra fitted peaks. The ratio of I1 (3000-2800 cm-1 / 1613
256
cm-1) represents the relative abundance of aliphatic bonds. The CH2/CH3 (2921 cm-1 /
257
2959 cm-1) ratio measures the length or branching degree of aliphatic side chains and
258
bridge bonds. The ratio of I2 (1700-1640 cm-1 / 1630-1500 cm-1) corresponds to the
259
carbonyl or carbonyl groups to aromatic carbon groups. The ratios of I3 (1310 cm-1 +
260
1178 cm-1 + 1150 cm-1 / 1613 cm-1) and I4 (1231 cm-1/1613 cm-1) refer to the richness
261
of phenolic hydroxyl and aryl ethers, respectively. The ratio of I5 (873 cm-1 + 849
262
cm-1 + 818 cm-1 / 873 cm-1 + 849 cm-1 + 818 cm-1 + 799 cm-1 + 776 cm-1 + 751 cm-1)
263
is related to the substitution degree of aromatic ring system. Thus, the chemical
264
structural parameters of coal samples derived from FTIR analysis are presented in 14
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265
Table 5. 0.05
Experimental curve Fitted curve Fitted peak
(a) -OH
(b) Aliphatic CH
0.032
Absorbance
Absorbance
0.04 0.03 0.02
0.05 0.04
3500
3400 3300 3200 -1 Wavenumber (cm )
(c) O-containing
3100
Experimental curve Fitted curve FItted peak
0.016
0.0032
2950 2900 2850 -1 Wavenumber (cm )
(d) Aromatic CH
2800
Experimental curve Fitted curve Fitted peak
0.0024
0.03 0.02
0.0016
0.0008
0.01
267
0.024
0.000 3000
3000
Absorbance
0.00 3600
266
Experimental curve Fitted curve Fitted peak
0.008
0.01
Absorbance
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
Energy & Fuels
0.00 1800 1700 1600 1500 1400 1300 1200 1100 1000 -1 Wavenumber (cm )
0.0000 900 880 860 840 820 800 780 760 740 720 700 -1 Wavenumber (cm )
268
Figure 4. Curve fittings of SDC infrared spectrum in different wavenumber bands, (a)
269
3600-3000 cm-1, (b) 3000-2800 cm-1, (c) 1800-1000 cm-1, (d) 900-700 cm-1.
270
As shown in Table 5, the values of I1, CH2/CH3, and I5 for treated coal samples
271
decreased, due to the cleavage of weak covalent aliphatic side chains, as well as
272
longer aliphatic side chains cracking into shorter ones during HTP. All those can be
273
responsible for the gases release of C1~C3. The I2 ratio of treated coal samples
274
decreased, further indicating that the carbonyl and carboxyl groups were decomposed
275
with the evolution of CO2 and CO by HTP. With the addition of water, abundant
276
hydroxyl and hydrogen radicals are possibly cross-linked to the benzene or phenoxy
277
of matrix to generate phenolic hydroxyl groups during HTP.40 Correspondingly, the
278
value of I3 increased from 1.15 (SDC) to 1.30 (HTP-300). However, the ratio of I4 15
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279
decreased from 0.52 (SDC) to 0.46 (HTP-300). The aryl ethers are not easily
280
decomposed at low temperatures.41 It can be speculated that some aryl ether oxygen
281
transferred to phenolic hydroxyl oxygen by aryl ether hydrolysis reactions during
282
HTP. Table 5. Parameters derived from FTIR analysis of SDC and treated coal samples. I3
I4
I5
CH2/CH3
SDC
0.93
0.41
1.15
0.52
0.43
2.92
HTP-200
0.81
0.39
1.21
0.51
0.40
2.83
HTP-220
0.78
0.40
1.19
0.48
0.39
2.76
HTP-240
0.76
0.38
1.29
0.47
0.34
2.62
HTP-260
0.71
0.35
1.29
0.45
0.33
2.51
HTP-300
0.65
0.35
1.30
0.46
0.31
2.49
Aro C
O-alk
Alk C
I2
COO
I1
0.65
1.33 0.17
1.0
1.91
3.61
0.53
1.10 0.20
1.0
1.67
2.56
C=O
Samples
O-aro
283
Intensity (a.u.)
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 16 of 30
SDC
HTP-240
200
284 285
150 100 50 Chemical shift (ppm)
0
Figure 5. Solid-state 13C NMR spectra of SDC and treated coal samples.
286
Figure 5 shows the 13C NMR spectra of SDC and HTP-240. The spectrums can
287
be divided into six sections,15,42 nonpolar alkyls (alk C, 0-50 ppm), O-alkyls (O-alk,
288
50-90 ppm), aromatics (aro C, 90-150 ppm), aromatic C-O (O-aro, 150-165 ppm),
289
carboxyls (COO, 165-190 ppm), and carbonyls (C=O, 190-220 ppm). As based on the
290
area of aromatics at 90-150 ppm, the ratios of alk C to aro C, COO to aro C, C=O to
291
aro C, and O-alk to aro C for HTP-240 decreased, indicating that the cleavage of 16
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292
some weak aliphatic bonds, carbonyl and carboxyl groups occurred during HTP, as
293
well as aliphatic alcoholic hydroxyl and methoxy. Additionally, the ratio of O-aro to
294
aro C for HTP-240 was significantly higher than that of SDC, suggesting that more
295
phenolic hydroxyl oxygen were formed during HTP.
296
3.3. Influence of HTP on Coal Pyrolysis Table 6. Pyrolysis products distribution of SDC and treated coal samples.
297
Yield %)
(wt
SDC
HTP-200
HTP-220
HTP-240
HTP-260
HTP-300
W/C ratio
--
3:1
3:1
1:1
2:1
3:1
4:1
3:1
3:1
Tar
9.2
9.9
10.1
10.2
10.4
10.5
10.5
9.9
9.7
Char
68.4
70.3
70.6
70.7
71.0
71.3
71.3
72.7
73.7
Gas
19.6
17.1
16.5
16.5
16.1
15.7
15.7
14.8
14.2
Water
3.0
2.7
2.8
2.6
2.5
2.5
2.5
2.6
2.4
298
The pyrolysis products yields are given in Table 6. Both pyrolysis gas and water
299
yields decreased, while the char yield increased with the rising of pretreatment
300
temperatures. The tar yield increased first and then decreased. The products yields of
301
treated coal samples under different W/C ratios were basically the same. Thence,
302
pretreatment temperature is the main influencing factor for HTP.43
303
3.3.1. Gas Products
304
The composition of gas products is shown in Table 7. The CO2 and CO of treated
305
coal samples decreased with the rising of pretreatment temperatures, due to the
306
decomposition of carboxyl, aldehyde groups and methoxy during HTP. And, part of
307
CO was achieved by the fracture of aryl ethers at higher temperatures during pyrolysis
308
process.36 Some aryl ether oxygen transferred to phenolic hydroxyl oxygen during 17
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Page 18 of 30
309
HTP, resulting in the CO evolution decrease during pyrolysis process. Secondly, the
310
absence of water soluble inorganic metals suppressed the tar precursors cracking into
311
small molecular gases in pyrolysis.44 The H2 formation of HTP-240, HTP-260, and
312
HTP-300 increased, which was attributed to the reduction of hydrogen radical
313
consumption during pyrolysis process.45 The hydrogen radical was introduced and
314
longer aliphatic side chains were cracked to short ones during HTP, resulting in the
315
increase of CH4 but decrease of C2~C3 for treated coal samples, compared to that of
316
SDC. However, with the rising pretreatment temperatures, more CH4 was evolved
317
during HTP, leading to the decrease of CH4 (HTP-260, and HTP-300) during
318
pyrolysis.
319
Table 7. Composition of gas products of SDC and treated coal samples. Composition (mmol/gcoal,daf)
Samples
320
H2
CO
CO2
CH4
C2H4
C2H6
C3H6
C3H8
SDC
0.63
1.36
0.72
1.35
0.29
0.10
0.16
0.03
HTP-200
0.59
1.22
0.50
1.43
0.26
0.10
0.10
0.03
HTP-220
0.61
1.04
0.44
1.43
0.25
0.10
0.09
0.03
HTP-240
0.65
0.92
0.43
1.47
0.16
0.09
0.08
0.03
HTP-260
0.66
0.87
0.42
1.40
0.15
0.09
0.07
0.03
HTP-300
0.70
0.82
0.40
1.39
0.14
0.08
0.06
0.03
3.3.2. Tar Products
321
The tar yield and composition are principally governed by coal structure and
322
composition. Its generation consists of the formation and rearrangement of free
323
radical fragments. As reported in previous studies,46-48 the formation of tar precursors
324
was hindered by the existence of AAEM metals due to their cross-linking effects. The 18
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325
AAEM metals in treated coal samples were efficiently removed and hydrogen radical
326
was introduced, which are beneficial to the formation and stabilization of free radical
327
fragments in time during pyrolysis process. Moreover, the increase of smaller
328
mesopores (2-20 nm) in treated coal samples reduced the mass transfer resistance for
329
volatiles evolution (e.g., the molecular diameter of naphthalene is 0.8 nm). Hence, the
330
tar yield increased from 9.2 % (SDC) to 10.5 % (HTP-240). Conversely, the higher
331
pretreatment temperatures promoted the cleavage of weak covalent bonds, leading to
332
lower tar yield of 9.7 % (HTP-300).
50
Tar compositions (area %)
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
Energy & Fuels
40
334
HTP-200 HTP-240 HTP-300
30
20
10
0
333
SDC HTP-220 HTP-260
s s s s atics -ring Ar. -ring Ar. PAH mpound mpound mpound 2 1 Aliph co co r co olic ated Othe Phen Oxygen
Figure 6. Composition of tar products of SDC and treated coal samples.
335
The classification composition of tar samples by GC-MS analyses (peak area
336
normalization method) is given in Figure 6. Obviously, the relative content of
337
phenolic compounds in tar of treated coal samples was higher than that of SDC.
338
Firstly, according to the FTIR analyses, more phenolic hydroxyl groups were
339
generated in treated coal samples. Secondly, the removal of water soluble organic
340
metals inhibited the conversion of macromolecular phenolic compounds to small
341
molecules.49-51 More phenolic compounds were produced in tar samples.
342
Correspondingly, the relative content of monocyclic aromatic hydrocarbons 19
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343
decreased. The relative content of polycyclic aromatic hydrocarbons in tar decreased
344
from 42.1 % of SDC to the average content 30.5 % of treated coal samples. There was
345
a slight decrease in the relative content of aliphatic hydrocarbons from 18.4 % of SD
346
to 14.5 % of HTP-300, due to the fracture of aliphatic side chains by HTP.29 HTP-300
HTP-260 Normalized intensity
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 20 of 30
HTP-240
HTP-220
HTP-200
SDC
300
347 348
400 500 600 Wavelength (nm)
700
Figure 7. Normalized UV-F spectra of tar products from SDC and treated coals.
349
The normalized UV-F spectra of tar samples is presented in Figure 7, where the
350
wavelength of the peak shifts from 487 nm of SDC tar to 515 nm of HTP-300 tar.
351
This observation strongly suggested that much more macromolecular tar compounds
352
were generated from macromolecules of treated coal samples.52 In addition, there was
353
no obvious difference among tar composition of treated coal samples, and the tar
354
samples of SDC and HTP-240 were selected for further analysis below.
355
As shown in Table 8, the oxygen content of SDC tar is lower than that of
356
HTP-240 tar, as well as the nitrogen and sulfur contents, indicating that HTP was
357
advantageous for heteroatoms evolution in pyrolysis. Moreover, the O/C and H/C 20
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358
ratios of HTP-240 tar increased slightly, which corresponded to the fact that HTP
359
promoted more oxygen enrichment in tar and reduced hydrogen consumption to form
360
water.45,53
361
Table 8. Proximate and ultimate analysis of char and tar from SDC and HTP-240
362
coals. Proximate analysis (wt%)
Ultimate analysis (wt%, daf)
Atomic ratio
Samples Mad
Ad
Vdaf
FCdaf*
C
H
N
S
O*
AO/C
AH/C
SDC
3.7
10.0
20.8
79.2
84.3
3.3
1.5
0.4
10.5
0.09
0.46
HTP-240
3.2
7.7
19.0
81.0
86.5
2.9
1.4
0.3
8.9
0.08
0.40
SDC
--
--
--
--
81.2
7.8
0.9
0.3
9.8
0.09
1.15
HTP-240
--
--
--
--
79.7
7.7
1.1
0.3
11.2
0.11
1.17
Char
Tar
363
by difference.
*:
50
Tar compositions (area %)
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
Energy & Fuels
40 30 20 10 0
364 365
SDC HTP-240
s s s s atics -ring Ar. -ring Ar. PAH mpound mpound mpound 1 2 Aliph co co r co olic ated Othe Phen Oxygen
Figure 8. Composition of N-hexane soluble tar from SDC and HTP-240 coals.
366
The N-hexane extraction rate of SDC tar was 37.7 %, markedly higher than 25.9
367
% of HTP-240 tar, indicating that more macromolecules were formed in tar of treated
368
coal samples. The composition of N-hexane soluble tar samples was analyzed by
369
GC-MS, as depicted in Figure 8. The oxygen-containing compounds content in
370
HTP-240 N-hexane soluble tar decreased. Yet, oxygen content in HPT-240 tar was
371
higher than that in SDC tar. It further suggested that more oxygenated 21
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372
macromolecules were formed in tar of treated coal samples.
373
3.3.3. Water Products
374
The pyrolysis water is produced owing to the existence of oxygen-containing
375
functional groups.45 The HTP was beneficial to the removal of aliphatic alcohol
376
hydroxyl beforehand, and more oxygen was enriched in tar. Thus, the water yield
377
decreased from 3.0 % of SDC to 2.4 % of HTP-300.
378
3.3.4. Char Products
379
Some gas components were released during HTP, as shown in Table 3. The
380
higher the pretreatment temperatures, the more gases evolved from coal matrix,
381
resulting in the increase of char yields, from 68.4 % of SDC to 71.3 % of HTP-300.
382
Furthermore, the HTP promoted oxygen enrichment in tar instead of char, as well as
383
nitrogen and sulfur. The average pore diameter of SDC char was 9.39 nm, lower than
384
15.74 nm of HTP-240 char. More macropores were formed in HTP-240 char. The
385
micropore specific surface area of HTP-240 char (1.17 m2/g) was higher than that of
386
SD char (0.25 m2/g).
387
Figure 9 shows the char gasification yield and product distributions. As depicted
388
in Figure 9(a), the char gasification yield from treated coal samples obviously
389
increased. There was no obvious difference in CH4 and H2 evolutions among all char
390
samples, as given in Figure 9(b) and 9(c).
391
Figure 9(d) displays the CO evolution curve during char gasification process. Its
392
evolution began from 600 oC to 900 oC, and reached the maximum at 900 oC. No
393
obvious difference of CO evolution occurred before 700 oC for all samples, verifying 22
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Page 23 of 30
394
that the easily decomposable oxygen was fully volatized during pyrolysis process.
395
The hydroxyl groups with high bonding energy and aryl ethers in the residual char
396
links were responsible for the release of CO above 700 oC.36 However, the oxygen
397
content and O/C ratio of HTP-240 char was 8.94 % and 0.078, lower than that of
398
10.29 % and 0.091 of SDC char, respectively. When the gasification temperature was
399
above 700 oC, the CO formation rate and evolution volume for treated coal samples
400
were obviously higher than that of SDC during gasification process. Thus, the CO
401
was generated by the reactions between CO2 and the chars.36 The 𝑅𝑆𝐷 𝑐ℎ𝑎𝑟 was
402
0.0094, and the 𝑅𝐻𝑇𝑃 ― 240 𝑐ℎ𝑎𝑟 was 0.0104. Therefore, the char gasification reactivity
403
of treated coal samples was enhanced. The higher micropores surface area of chars
404
from treated coal samples increased the gasification reacativity, leading to higher CO
405
evolution. Additionally, lower oxygen and sulfur contents in chars also enhanced
406
gasification reactivity. 4
(a) CH4 distribution (mL/g char )
100 Gasification yields (wt.%)
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
Energy & Fuels
90
80
70
60
SDCHTP-200HTP-220HTP-240HTP-260HTP-300
(b)
3 SDC HTP-200 HTP-220 HTP-240 HTP-260 HTP-300
2 1 0 300 600 900 Temperature (C)
407
900C
23
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30 60 Time (min)
90
Energy & Fuels
408
50
900C CO distribution (mL/g char )
20 (c) H2 distribution (mL/g char )
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
15 SDC HTP-200 HTP-220 HTP-240 HTP-260 HTP-300
10 5 0 300 600 900 Temperature (C)
30 60 Time (min)
90
Page 24 of 30
(d)
900C SDC HTP-200 HTP-220 HTP-240 HTP-260 HTP-300
40 30 20 10 0
300 600 900 Temperature (C)
30 60 Time (min)
90
409
Figure 9. Gasification yield and gas evolution of char samples, (a) gasification yield,
410
(b) CH4 evolution, (c) H2 evolution, (d) CO evolution.
411
3.4. Possible Mechanism of Coal Pyrolysis with HTP
412
The coal pyrolysis characteristics are closely related to its structure and
413
composition. And the coal pyrolysis mechanism was revised in the previous
414
literature.54 The possible mechanisms during the process of HTP and pyrolysis of
415
treated coal samples were proposed in this work. After HTP, the water soluble
416
inorganic metals and some oxygen-containing functional groups in SDC were
417
removed, and the cross-linking points of carboxyl and AAEM species decreased.
418
Then, the formation of smaller mesopores (2-20 nm) increased from hitherto closed
419
pores and micropores. Moreover, the hydroxyl and hydrogen radicals were introduced
420
into the treated coal samples. The aromatic carboxyl groups first cracked to CO2 and
421
aryl radicals, and then reacted with the hydroxyl radical to form phenolic hydroxyl
422
groups. The aryl methyl ethers first cracked to methyl and aryl ether radicals, and then
423
reacted with hydrogen radical respectively to form CH4 and phenolic hydroxyl
424
groups. Correspondingly, more phenolic radicals and macromolecular tar precursors
425
were formed during pyrolysis process. Meanwhile, the absence of water soluble 24
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Energy & Fuels
426
inorganic metals inhibited the deoxygenation of tar precursors. Thus, the tar yield
427
increased with more phenolic compounds, as well as the N-hexane insoluble
428
component, but the CO and CO2 evolution decreased. The pyrolysis water yields
429
decreased, while the formation of H2 and CH4 increased. More oxygen was enriched
430
in macromolecular tar instead of gas and char products. Additionally, the char
431
gasification yield and reactivity were enhanced. The schematic diagram of the
432
mechanism of coal pyrolysis with HTP was shown in Figure 10.
433 434 435
Figure 10. Schematic diagram of the mechanism of coal pyrolysis with HTP. CONCLUSION
436
The physicochemical structure and composition of SDC were changed by HTP,
437
resulting in the differences in pyrolysis characteristics between SDC and treated coal
438
samples.
439
1. After HTP, the smaller mesopores (2-20 nm) increased from hitherto closed
440
pores
and
micropores,
the
water
soluble
inorganic
441
oxygen-containing functional groups were removed, and the cross-linking degree of
442
coal matrix was reduced. 25
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metals
and
some
Energy & Fuels 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
443
2. The pyrolysis gas yield decreased by the significant reduction in CO and CO2.
444
More H2 and CH4 were formed due to the oxygen removal and hydrogen radical
445
introduction. The tar yield increased because of the more tar precursor formations and
446
the lower mass transfer resistance during pyrolysis. The tar N-hexane extraction rate
447
decreased and more oxygen was enriched in macromolecular tar compounds, which
448
can be attributed to the inhibition of deoxygenation of tar precursors. The water yield
449
decreased due to the removal of aliphatic alcohol hydroxyl beforehand and the oxygen
450
enrichment in tar. Additionally, the oxygen and sulfur contents decreased and more
451
macropores were formed in char samples, improving the char gasification activity.
452
3. The experimental results and mechanism analysis from this work indicated
453
that the hydrogen radical and hydroxyl radical were introduced in treated coal
454
samples, and more phenolic hydroxyl groups were formed by aromatic carboxyl
455
hydrolysis reactions and aryl ether hydrolysis reactions. More evolution of smaller
456
mesopores from the hitherto closed pores and micropores facilitated the escape of
457
volatiles. The absence of water soluble inorganic metals promoted the formation of tar
458
precursors and inhibited the cracking of tar precursors. The decomposition of
459
oxygen-containing functional groups and the introduction of hydrogen radical
460
beforehand improved the gas quality.
461
AUTHOR INFORMATION
462
Corresponding Author
463
* Tel: +86-13772424852. E-mail address:
[email protected] 26
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Energy & Fuels
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Notes
465
The authors declare no competing financial interest.
466
ACKNOWLEGEMENTS
467
This work was supported by the National Natural Science Foundation of China (NO.
468
21536009), and Science and Technology Plan Projects of Shaanxi Province
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(2017ZDCXL-GY-10-03).
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REFERENCES
471
(1) BP Statistical Review of World Energy. 2018 (Accessed 20 June 2018), https://www.
472
bp.com/en/global/corporate/energy-economics.html.
473
(2) Qian, W.; Xie, Q.; Huang, Y. Y.; Dang, J. T.; Sun, K. D.; Yang, Q.; Wang, J. C. Combustion
474
characteristics of semicokes derived from pyrolysis of low rank bituminous coal. Int. J. Min. Sci.
475
Technol. 2012, 22(5), 645-650.
476
(3) Xu, Y.; Zhang, Y. F.; Wang, Y.; Zhang, G. J.; Chen, L. Gas evolution characteristics of lignite during
477
low-temperature pyrolysis. J. Anal. Appl. Pyrolysis 2013, 104, 625-631.
478
(4) Xu, Y.; Zhang, Y. F.; Zhang, G. J.; Guo, Y. F. Low temperature pyrolysates distribution and kinetics
479
of Zhaotong lignite. Energy Convers. Manage. 2016, 114, 11-19.
480
(5) Li, W.; Zhu, Y. M.; Liu, Y. Gas evolution and isotopic fractionations during pyrolysis on coals of
481
different ranks. Int. J. Coal Geo. 2018, 188, 136-144.
482
(6) Valdés, C. F.; Chejne, F. Fast pyrolysis of coal particles in a novel hot plate reactor: Implications of
483
the reaction atmosphere on the reactivity and char chemical structure. J. Anal. Appl. Pyrolysis 2018,
484
130, 43-51.
485
(7) Duan, W. J.; Yu, Q. B.; Xie, H. Q.; Qin, Q. Pyrolysis of coal by solid heat carrier-experimental study
486
and kinetic modeling. Energy 2017, 135, 317-326.
487
(8) Tian, B.; Qiao, Y. Y.; Tian, Y. Y.; Liu, Q. Investigation on the effect of particle size and heating rate
488
on pyrolysis characteristics of a bituminous coal by TG–FTIR. J. Anal. Appl. Pyrolysis 2016, 121,
489
376-386.
490
(9) Zhang, H. R.; Bai, J.; Kong, L. X.; Li, X. M.; Bai, Z. Q.; Li, W. Behavior of Minerals in Typical Shanxi
491
Coking Coal during Pyrolysis. Energy Fuels 2015, 29, (11), 6912-6919.
492
(10) Rao, Z. H.; Zhao, Y. M.; Huang, C. L.; Duan, C. L.; He, J. F. Recent developments in drying and
493
dewatering for low rank coals. Progress in Energy and Combustion Science 2015, 46, 1-11.
494
(11) Yan, J. C.; Bai, Z. Q.; Hao, P.; Bai, J.; Li, W. Comparative study of low-temperature pyrolysis and
495
solvent treatment on upgrading and hydro-liquefaction of brown coal. Fuel 2017, 199, 598-605.
496
(12) Yan, J. C.; Bai, Z. Q.; Bai, J.; Guo, Z. X.; Li, W. Effects of organic solvent treatment on the chemical
497
structure and pyrolysis reactivity of brown coal. Fuel 2014, 128, 39-45.
498
(13) Yu, J. D.; Jiang, C. Y.; Guan, Q. Q.; Gu, J. J.; Ning, P.; Miao, R. R.; Chen, Q. L.; Zhang, J. M.
499
Conversion of low-grade coals in sub-and supercritical water: A review. Fuel 2018, 217, 275-284.
500
(14) Zhang, X. P.; Zhang, C.; Tan, P.; Li, X.; Fang, Q. Y.; Chen, G. Effects of hydrothermal upgrading on 27
ACS Paragon Plus Environment
Energy & Fuels 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
501
the physicochemical structure and gasification characteristics of Zhundong coal. Fuel Process. Technol.
502
2018, 172, 200-208.
503
(15) Liu, J. Z.; Wu, J. H.; Zhu, J. F.; Wang, Z. H.; Zhou, J. H.; Cen, K. F. Removal of oxygen functional
504
groups in lignite by hydrothermal dewatering: An experimental and DFT study. Fuel 2016, 178, 85-92.
505
(16) Wu, J. H.; Liu, J. Z.; Zhang, X.; Wang, Z. H.; Zhou, J. H.; Cen, K. F. Chemical and structural changes
506
in XiMeng lignite and its carbon migration during hydrothermal dewatering. Fuel 2015, 148, 139-144.
507
(17) Xiang, F. P.; He, Y.; Kumar, S.; Wang, Z. H.; Liu, L. L.; Huang, Z. Y.; Liu, J. Z.; Cen, K. F. Influence of
508
hydrothermal dewatering on trace element transfer in Yimin coal. Appl. Therm. Eng. 2017, 117,
509
675-681.
510
(18) Wang, B. F.; Li, W.; Li, B. Q.; Wang, G. Study on the fate of As, Hg and Pb in Yima coal via
511
sub-critical water extraction. Fuel 2007, 86, (12-13), 1822-1830.
512
(19) Ge, L. C.; Zhang, Y. W.; Xu, C.; Wang, Z. H.; Zhou, J. H.; Cen, K. F. Influence of the hydrothermal
513
dewatering on the combustion characteristics of Chinese low-rank coals. Appl. Therm. Eng. 2015, 90,
514
174-181.
515
(20) Fu, J. M.; Wang, J. Enhanced slurryability and rheological behaviors of two low-rank coals by
516
thermal and hydrothermal pretreatments. Powder Technol. 2014, 266, 183-190.
517
(21) Wang, Z. C.; Shui, H. F.; Pei, Z. N.; Gao, J. S. Study on the hydrothermal treatment of Shenhua
518
coal. Fuel 2008, 87, (4-5), 527-533.
519
(22) Shi, L.; Wang, X. L.; Zhang, S. Y.; Wu, X. H.; Yuan, L.; Tang, Z. C. A new in-situ pyrolytic
520
time-of-flight mass spectrometer instrument for study on coal pyrolysis. J. Anal. Appl. Pyrolysis 2016,
521
117, 347-353.
522
(23) Ge, L. C.; Feng, H. C.; Xu, C.; Zhang, Y. W.; Wang, Z. H. Effect of hydrothermal dewatering on the
523
pyrolysis characteristics of Chinese low-rank coals. Appl. Therm. Eng. 2018, 141, 70-78.
524
(24) Liu, P.; Wang, L. L.; Zhou, Y.; Pan, T. Y.; Lu, X. L.; Zhang, D. Effect of hydrothermal treatment on
525
the structure and pyrolysis product distribution of Xiaolongtan lignite. Fuel 2016, 164, 110-118.
526
(25) Zhang, D. X.; Liu, P.; Lu, X. L.; Wang, L. L.; Pan, T. Y. Upgrading of low rank coal by hydrothermal
527
treatment: Coal tar yield during pyrolysis. Fuel Process. Technol. 2016, 141, 117-122.
528
(26) Zeng, C.; Favas, G.; Wu H. W.; Chaffee, A. L.; Hayashi, J.; Li, C. Z. Effects of Pretreatment in Steam
529
on the Pyrolysis Behavior of Loy Yang Brown Coal. Energy Fuels 2006, 20, 281-286.
530
(27) Cetin, E.; Gupta, R.; Moghtaderi, B. Effect of pyrolysis pressure and heating rate on radiata pine
531
char structure and apparent gasification reactivity. Fuel 2005, 84, 1328-1334.
532
(28) Ding, L.; Zhou, Z. J.; Guo Q. H.; Huo, W.; Yu, G. S. Catalytic effects of Na2CO3 additive on coal
533
pyrolysis and gasification. Fuel 2015, 142, 134-144.
534
(29) Siskin, M.; Katritzky, A. R. A review of the reactivity of organic compounds with
535
oxygen-containing functionality in superheated water. J. Anal. Appl. Pyrolysis 2000, 54, 193-214.
536
(30) Guo, Y.; Wang, S. Z.; Xu, D. H.; Gong, Y. M.; Ma, H. H.; Tang, X. Y. Review of catalytic supercritical
537
water gasification for hydrogen production from biomass. Renew. and Sustain. Energy Rev. 2010,
538
14(1), 334-343.
539
(31) Favas, G.; Jackson, W. R. Hydrothermal dewatering of lower rank coals. 2. Effects of coal
540
characteristics for a range of Australian and international coals. Fuel 2003, 82, 59-69.
541
(32) Liao, J. J.; Fei, Y.; Marshall, M.; Chaffee, A. L.; Chang, L. P. Hydrothermal dewatering of a Chinese
542
lignite and properties of the solid products. Fuel 2016, 180, 473-480.
543
(33) Jiang, L.; Hu, S.; Wang, Y.; Su, S.; Sun, L. S.; Xu, B. Y.; He, L. M.; Xiang, J. Catalytic effects of
544
inherent alkali and alkaline earth metallic species on steam gasification of biomass. Int. J. Hydrogen 28
ACS Paragon Plus Environment
Page 28 of 30
Page 29 of 30 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
Energy & Fuels
545
Energy 2015, 40, (45), 15460-15469.
546
(34) Liu, L. L.; Kumar, S.; Wang, Z. H.; He, Y.; Liu, J. Z.; Cen, K. F. Catalytic effect of metal chlorides on
547
coal pyrolysis and gasification part I. Combined TG-FTIR study for coal pyrolysis. Thermochim. Acta
548
2017, 655, 331-336.
549
(35) Zhao, D.; Liu, H.; Jiang, L. X.; Ge, J. W.; Xu, L. F.; Cao, Q. X. Investigation into the Relationship
550
between Oxygen-Containing Groups and the Release of Na and Cl during Preoxidation and Pyrolysis of
551
Na-Enriched Zhundong Coal. Energy Fuels 2017, 31, (11), 11939-11946.
552
(36) Liu, J. X; Jiang, X. M.; Shen, J.; Zhang, H. Pyrolysis of superfine pulverized coal. Part 2.
553
Mechanisms of carbon monoxide formation. Energy Convers. Manage. 2014, 87, 1039-1049.
554
(37) Ibarra, J.; Munoz, E.; Mloiner, R. FTIR study of the evolution of coal structure during the
555
coalification process. Org. Geochem. 1996, 24, 725-735.
556
(38) Song, H. J.; Liu, G. R.; Zhang, J. Z.; Wu, J. H. Pyrolysis characteristics and kinetics of low rank coals
557
by TG-FTIR method. Fuel Process. Technol. 2017, 156, 454-460.
558
(39) Zhao, Y.; Qiu, P. H.; Chen, G.; Pei, J. T.; Sun, S. Z.; Liu, L.; Liu, H. P. Selective enrichment of
559
chemical structure during first grinding of Zhundong coal and its effect on pyrolysis reactivity. Fuel
560
2017, 189, 46-56.
561
(40) Siskin, M.; Brons, G.; Vaughn, S. N. Aqueous organic chemistry. 3. Aquathermolysis: reactivity of
562
ethers and esters. Energy Fuels 1990, 4, 488-492.
563
(41) Ye, C. P.; Huang, H. J.; Li, X. H.; Li, W. Y.; Feng, J. The oxygen evolution during pyrolysis of
564
HunlunBuir lignite under different heating modes. Fuel 2017, 207, 85-92.
565
(42) Liu, M.; Li, J.; Duan, Y. F. Effects of solvent thermal treatment on the functional groups
566
transformation and pyrolysis kinetics of Indonesian lignite. Energy Convers. Manage. 2015, 103,
567
66-72.
568
(43) Favas, G.; Jackson, W. R. Hydrothermal dewatering of lower rank coals. 1. Effects of process
569
conditions on the properties of dried product. Fuel 2003, 82, (1), 53-57.
570
(44) Liu, H.; Xu, L. F.; Zhao, D.; Cao, Q. X.; Gao, J. H.; Wu, S. H. Effects of alkali and alkaline-earth
571
metals and retention time on the generation of tar during coal pyrolysis in a horizontal fixed-bed
572
reactor. Fuel Process. Technol. 2018, 179, 399-406.
573
(45) Atesok, G.; Boylu, F.; Sirkeci, A. A.; Dincer, H. The effect of coal properties on the viscosity of
574
coal–water slurries. Fuel 2002, 81, 1855-1858.
575
(46) Xu, S. Q.; Zhou, Z. J.; Xiong, J.; Yu, G. S.; Wang, F. C. Effects of alkaline metal on coal gasification
576
at pyrolysis and gasification phases. Fuel 2011, 90, (5), 1723-1730.
577
(47) Zhang, F.; Xu, D. P.; Wang, Y.; Wang, Y. G.; Gao, Y.; Popa, T.; Fan, M. H. Catalytic CO2 gasification
578
of a Powder River Basin coal. Fuel Process. Technol. 2015, 130, 107-116.
579
(48) Ding, L.; Zhou, Z. J.; Guo, Q. H.; Lin, S. J.; Yu, G. S. Gas evolution characteristics during pyrolysis
580
and catalytic pyrolysis of coals by TG–MS and in a high-frequency furnace. Fuel 2015, 154, 222-232.
581
(49) Zhang, F.; Xu, D. P.; Wang, Y. G.; Argyle, M. D.; Fan, M. H. CO2 gasification of Powder River Basin
582
coal catalyzed by a cost-effective and environmentally friendly iron catalyst. Appl. Energy 2015, 145,
583
295-305.
584
(50) Zhang, Z. Z.; Chang, H.; Gao, T.; Lan, T. W.; Zhang, J. B.; Sun, M.; Xu, L.; Ma, X. X. Catalytic upgrading of coal pyrolysis volatiles over metal-loaded HZSM-5 catalysts in a fluidized bed reactor. J. Anal. Appl. Pyrolysis 2018, https://doi.org/10.1016/j.jaap.2019.01.005. (51) Zhang, Y. Q.; Pan, D. F.; Qu, X.; Liang, P. Secondary Catalytic Effect of Circulating Ash on the Primary Volatiles from Slow and Fast Pyrolysis of Coal. Energy Fuels 2018, 32, (2), 1328-1335.
585 586 587 588
29
ACS Paragon Plus Environment
Energy & Fuels 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
589
(52) Zeng, C.; Wu, H. W.; Hayashi, J.; Li, C. Z. Effects of thermal pretreatment in helium on the
590
pyrolysis behaviour of Loy Yang brown coal. Fuel 2005, 1586-1592.
591
(53) Suuberg, E. M.; Lee, D. Y.; Larsen, J. W. Temperature dependence of crosslinking processes in
592
pyrolysing coals. Fuel 1985, 64, (12), 1668-1671.
593
(54) Liu, Z. Y. Advancement in coal chemistry: structure and reactivity. Scientia Sinica Chimica 2014,
594
44, (9), 1431-1438.
30
ACS Paragon Plus Environment
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