Journal Pre-proof Pore distribution characteristics of various rank coals matrix and their influences on gas adsorption Jiwei Yan, Zhaoping Meng, Kun Zhang, Huifang Yao, Haijin Hao PII:
S0920-4105(20)30135-2
DOI:
https://doi.org/10.1016/j.petrol.2020.107041
Reference:
PETROL 107041
To appear in:
Journal of Petroleum Science and Engineering
Received Date: 30 March 2019 Revised Date:
21 November 2019
Accepted Date: 5 February 2020
Please cite this article as: Yan, J., Meng, Z., Zhang, K., Yao, H., Hao, H., Pore distribution characteristics of various rank coals matrix and their influences on gas adsorption, Journal of Petroleum Science and Engineering (2020), doi: https://doi.org/10.1016/j.petrol.2020.107041. This is a PDF file of an article that has undergone enhancements after acceptance, such as the addition of a cover page and metadata, and formatting for readability, but it is not yet the definitive version of record. This version will undergo additional copyediting, typesetting and review before it is published in its final form, but we are providing this version to give early visibility of the article. Please note that, during the production process, errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain. © 2020 Published by Elsevier B.V.
1
Pore distribution characteristics of various rank coals matrix and
2
their influences on gas adsorption
3
Jiwei Yana, Zhaoping Menga,b,∗, Kun Zhanga, Huifang Yaoc, and Haijin Hao
4 5 6 7 8 9
b
a
College of Geosciences and Surveying Engineering, China University of Mining and Technology
(Beijing), Beijing, 100083, PR China b
State Key Laboratory of Coal and CBM Co-mining, Shanxi Jincheng Anthracite Mining Group
Company, Ltd., Jincheng 048000, PR China c
Department of Earth Science and Engineering, Taiyuan University of Technology, Taiyuan
030024, PR China
10
Abstract: Methane is primarily stored in coal matrix pores and pore size
11
distribution has an important effect on gas adsorption/desorption. Investigation of the
12
relationship between pore size distribution and adsorption performance of coal is of
13
significance for the understanding of the evolution of coalbed methane reservoirs. In
14
this study, a series of laboratory experiments (nitrogen, carbon dioxide and methane
15
adsorption) were carried out to determine the pore size distribution and adsorption
16
capacity of coal samples of various coal ranks. The relationship between pore size
17
distribution, Langmuir volume and the metamorphic degree of coals were established.
18
The factors influencing methane adsorption of coals were also analyzed. The results
19
show that the matrix pores are mainly cylindrical, thin bottleneck-, ink bottleneck-
20
and parallel plate-shaped. With the increase in coal rank, both the total pore volume
21
and the specific surface area initially decrease and then increase. Matrix pores,
22
including micro-, transitional- and mesopores, show a similar asymmetric U-shaped
23
trend in the pore volume and the specific surface area with an increase in coal rank.
24
The percentages by volume and by specific surface area increase for the micropores
25
and declines for the transitional pores and mesopores. In the low-pressure zone,
26
micro- and transitional pores play a dominant role in methane adsorption; however, in
27
the high-pressure zone, the influence of mesopores on methane adsorption is
28 29
pronounced. Key words: various rank coals, pore size distribution, controlling mechanism,
30
methane adsorption
31
1 Introduction
32
Coal experiences a complex evolution processes after its formation, which
33
results in great heterogeneity and complexity in coal structure (Meng et al., 2015;
34
Mishra et al., 2018; Xu et al., 2019; Zhao et al., 2019). The pore size distribution in
35
the coal matrix has an important influence on gas adsorption, desorption and
36
migration. Therefore, it is essential to identify the evolutionary characteristics of coal
37
matrix pore structure and their influences on gas adsorption (Bustin et al., 2016; Meng
38
and Li, 2017; Meng et al., 2016). Fluid invasion and radiation methods are widely
39
used to determine the pore size distribution (PSD) of coals. The fluid invasion
40
methods, such as mercury intrusion porosimetry (MIP) and low-temperature nitrogen
41
adsorption (LT-NA), can provide information about pore morphology and
42
connectivity (Peng et al., 2017; Rijfkogel et al., 2019). The radiation method can
43
reveal the spatial distribution characteristics of pores within the coal (Clarkson et al.,
44
2013). For example, both microfocus X-ray computed tomography (Micro-CT) and
45
focused ion beam scanning electron microscopy (FIB-SEM) can characterize the PSD
46
of coal matrix in two-dimensional plane and in three-dimensional space (Karimpouli
47
et al., 2017; Liu et al., 2017a); small angle X-ray scattering (SAXS) and small angle
48
neutron scattering (SANS) can determine the volume percentages of different types of
49
pores in coal (Melnichenko et al., 2012; Nakagawa et al., 2000; Okolo et al., 2015).
50
Atomic force microscopy (AFM) is a powerful tool for the characterization of
51
macromolecular structure and 3-D spatial structure of coal (Liu et al., 2019a,b Pan et
52
al., 2015b). The above-mentioned characterization methods provide insight into the
53
pore structure of coals. However, a single technology cannot characterize the
54
full-scale pore structure, and it is necessary to combine various methods to study
55
coals' pore characteristics.
56
According to the pore classification method proposed by Hodot (1966), coal
57
matrix pores can be divided into four categories: micropores (pore diameter d≤10nm),
58
transitional
59
macropores (d>1000nm). Previous studies have found that the proportion of macro-
60
and mesopores is relatively large for low-rank coals, while the proportion of
61
transitional pores and micropores is relatively large for medium- and high-rank coals.
62
The total pore volume and specific surface area (SSA) show a U-shaped variation law
63
with the increase in coal rank (Pan et al., 2015a). For the coals in the eastern margin
64
of Ordos, with the increase in coal rank, the proportion of micropores first decreases
65
and then increases and the proportion of transitional pores follows an opposite trend
66
(Chen et al., 2015). Pores less than 5nm in diameter contribute significantly to the
67
SSA, while the pores greater than 10nm in diameter make a major contribution to the
68
pore volume for the high-rank coals in the Sichuan Basin (Shan et al., 2015). The
69
fractures in low-rank coals are short and irregular while they are well-developed and
70
regular in high-rank coals (Chen et al., 2015), which, to some extent, results in an
71
increase in the total pore volume of high-rank coals.
pores
(10nm
mesopores
(100nm
and
72
The coal macerals (vitrinite, inertinite and exinite) also affect the pore size
73
distribution. The SSA, volume, and diameter of pores are generally higher in the
74
inertinite than in the vitrinite (Berbesi et al., 2009; Shan et al., 2015), while Teng et al.
75
(2017) concluded that vitrinite was more porous than inertinite in the Illinois Basin
76
(U.S.) coal. The macerals vary in the different coal regions and basins (Sakurovs et al.,
77
2018). The coal macerals are key factors that influence the behavior of CH4 adsorption.
78
Many studies have shown that vitrinite has a significant effect on the CH4 sorption
79
capacity (Bustin and Clarkson, 1998; Dutta et al., 2011; Moore, 2012). Kiani et al.
80
(2018) held that inertinite contains a large number of pores with a diameter of 8-50nm
81
and has significant influence on the rate of gas sorption, but the maximum adsorption
82
capacity of coals is basically independent of inertinite content. Clarkson and Bustin
83
(2000) conducted isothermal adsorption experiments on CH4 and CO2 and found that
84
the coal with the highest adsorption capacity does not have the highest content of
85
vitrinite nor inertinite, and vitrinite and inertinite coexist in the studied coal.
86
CH4 adsorption capacity greatly depends on the degree of coal metamorphism
87
and PSD characteristics (Naveen et al., 2018). Low-rank coals always exhibit a weak
88
methanogenic capacity and a weak methane adsorption capacity. The methanogenic
89
capacity increases gradually from lignite to anthracite (Scott, 2002). The bituminous
90
coals, high-rank bituminous coals and anthracite coals always have a relatively high
91
cumulative gas production and a high adsorption capacity. The pores <2nm in coals
92
provide a large amount of SSA and play a dominant role in gas adsorption at low
93
pressure, and there is a positive correlation between gas content and pore (<2nm)
94
volume (Mastalerz et al., 2008). With the rise of gas pressure, the transitional-, meso-
95
and macropores tend to have an important influence on gas adsorption. Thus,
96
exploring the PSD characteristics is helpful to understanding the behavior of gas
97
adsorption in various rank coals.
98
At present, the following questions need to be further explored about coal pore
99
structure: systematical analysis of the morphology and evolution mechanism of pores
100
of various rank coals; the influence and controlling mechanism of different pore
101
structures on CH4 adsorption, especially the distribution and evolution characteristics
102
of micropores and their influences on gas adsorption. In this work, low temperature
103
N2 and CO2 adsorption experiments were carried out to determine the pore structure
104
parameters of various rank coals. Methane isotherm adsorption tests were carried out
105
and correlations between adsorption capacity, pore size distribution and Ro,max
106
(maximum vitrinite reflectance with oil) with various rank coals were explored.
107
Finally, the influences of pore morphology and distribution characteristics on CH4
108
adsorption capacity were elucidated, and the evolution characteristics of micropores
109
(in the range of 1.4-10nm in diameter) and transitional- pores and their effects on CH4
110
adsorption were analyzed, and the relationship between pore size distribution and
111
Ro,max was established. The outcomes help the understanding of gas flow and
112
adsorption behaviors in coal mines, and it can also provide a reference for the CBM
113
well drainage.
114
2 Materials and methods
115
2.1 Description of coal samples
116
According to the degree of coal metamorphism (Ro,max, following ISO
117
7404–5:2009),
118
(Ro,max=0.65%-2.0%) and high-rank coals (Ro,max>2.0%) (ISO 11760-2005; Zhang et
119
al., 2018). In this research, coal samples were collected from eastern Yunnan and
120
Inner Mongolia (low-rank coals, Ro,max=0.23%-0.57%), the northern Qinshui Basin
121
and the eastern Ordos Basin (medium-rank coals, Ro,max=0.69%-1.80%) and the
122
southern Qinshui Basin (high-rank coals, Ro,max=2.16%-3.45%) in China. The results
123
of proximate analysis (following ISO 17246: 2010 and ISO 17247-2013) and
124
petrographical determination (following ISO 7404-1:2016) of the coal samples are
125
listed in Table 1. The results indicate that the contents by volume for vitrinite,
126
inertinite and exinite are in the range of 54.1-95.02%, 0.48-22.68% and 0-10.8%,
127
respectively. The exinite largely disappears when Ro,max>1.1%. The mineral content is
128
approximately 5%, except for Baode No.8 coal sample (with a high mineral content of
129
22.60%).
130
2.2 Experimental methods
coals
can
be
divided
into
low-
(Ro,max<0.65%),
medium-
131
Many technologies have been used to determine the PSD of coals, such as MIP
132
(Okolo et al., 2015), LT-NA (Labani et al., 2013), CO2 adsorption (Song et al., 2017),
133
Micro-CT (Ramandi et al., 2016), SEM or FIB-SEM (Gaboreau et al., 2016), AFM
134
(Misra et al., 2019), nuclear magnetic resonance (NMR) (Yao et al., 2010). The
135
principles and the range of apertures tested by different methods are quite different
136
(Fig.1). N2 and CO2 adsorption methods are convenient and effective and are widely
137
used for the determination of PSD.
138
The low temperature nitrogen adsorption (LT-NA) experiments were carried out
139
with the TriStar II3020M automatic multi-station SSA and pore size analyzer made by
140
Micromeritics Instrument, USA. The samples were broken to 40-60 mesh in size, with
141
a weight of 2-3 g for each sample was used for this experiment. Samples were ground
142
and carefully sieved to avoid damaging matrix pores. Because the size of coal
143
particles is three orders of magnitude larger than the pore size of coal matrix, the
144
influence of the coal sample preparation process on the pore structure of coal matrix is
145
insignificant and can be neglected. Before the LT-NA experiments, all samples were
146
dried in a vacuum oven at 378.15K for 24 hours. After vacuum degassing, the samples
147
were placed in the analyzer. Temperature of the container was kept constant with
148
liquid nitrogen (77.15K). The adsorption-desorption experiments were started
149
according to the preset pressure. The adsorption-desorption quantities under different
150
pressures were obtained. The multipoint Brunauer-Emmett-Teller (BET) (Brunauer et
151
al., 1938) and the Barrett-Joyner-Halenda (BJH) methods were used to calculate SSA
152
and pore volume by the instrument software, respectively. The test range in pore
153
aperture is between 1.7nm and 300nm (Li and Meng, 2016).
154
The experimental instrument and procedure of CO2 adsorption experiment are
155
the same as those of the LT-NA experiment. These two experiments were carried out
156
with the same samples. While the experimental temperature for CO2 adsorption was
157
set to 273.15K. The instrument automatically carries out the adsorption experiment
158
and calculates the parameters of PSD by the D-A method according to preset pressure
159
conditions. The aperture measured by CO2 adsorption falls in the range of <2nm
160
(Gaucher et al., 2011).
161
The isothermal adsorption experiment is carried out using the ISO-300
162
isothermal adsorption-desorption apparatus made by Terra Tek Company, USA. The
163
experimental procedure and the apparatus have been described in detail (Zhang et al.,
164
2011). According to the national standard GB/T 19560-2008 (Experimental method of
165
high-pressure isothermal adsorption to coal), the coal samples are broken into
166
particles of 60-80 mesh (0.25-0.18mm). The weight of each sample used for the
167
experiment was 100-120g. Moisture equilibration of the coal samples was performed
168
according to the national standard and then the sample was quickly placed into the
169
sample cell. Sample containers are placed in a humidity-balanced dryer. A sufficient
170
amount of solution, supersaturated with potassium sulfate, is placed at the bottom of
171
the dryer. The weight of the coal sample is measured every 24 hours until the weight
172
variation does not exceed 2%. Helium gas is used to calibrate the volumes of the
173
sample and reference cells and check the system for any leaks. The system
174
temperature is equal to 303.15K, similar to the reservoir temperature. The maximum
175
equilibrium pressure is ~8MPa. Seven pressure points were measured in the
176
isothermal adsorption experiment for each sample. When the gas pressure in the
177
sample cylinder remains unchanged for over 12 hours, the adsorption equilibrium is
178
considered to be reached. Then the isothermal adsorption experiment steps to the next
179
pressure point.
180
3 Results
181
3.1 The low temperature N2 adsorption experiment
182
Experimental results of LT-NA are shown in Fig.2 and Table 2. The adsorption
183
and desorption curves of various rank coals are significantly different (Fig.2a-f).
184
According to the morphological characteristics of the adsorption and desorption
185
curves, the relative pressure can be divided into three zones: low-pressure zone
186
(p/p0<0.1), medium-pressure zone (p/p0=0.1-0.9) and high-pressure zone (p/p0>0.9).
187
For some low-rank coals, the adsorption capacity increases slowly with
188
increasing pressure in low-pressure zone (Fig.2a), indicating that the micropores are
189
poorly interconnected. While for other low-rank coals, the adsorption capacity
190
increases rapidly with increasing pressure in the low-pressure zone (Fig.2b), meaning
191
that the micropores are well developed and interconnected. This difference in gas
192
adsorption is mainly related to the formation environment of the coal and the
193
coal-forming materials (e.g., coal petrographic composition, moisture content) (Fu et
194
al., 2017). The above results show that the micropore distribution of low-rank coal
195
varies in different regions, and the micropores mainly exist in the coal
196
macromolecules and are closely related to the degree of coal metamorphism (Song et
197
al., 2017) and the morphology of these micropores is mainly cylindrical. The
198
adsorption capacity of the BZDB coal samples hardly rises with increasing pressure in
199
the medium-pressure zone (Fig.2a), indicating that the transitional pores have poor
200
interconnectivity and there are many fine bottleneck-shaped transitional pores. In
201
contrast, the adsorption capacity of SCH2 increases significantly with increasing
202
pressure and there is an obvious hysteresis loop in the desorption curve (Fig.2b),
203
indicating that there are some ink bottle-shaped pores in this coal sample. The
204
adsorption capacity increases rapidly with increasing pressure in the high-pressure
205
zone, and capillary condensation effects mainly occur in the mesopores in this stage.
206
Most of the adsorption/desorption isotherms overlap in the high-pressure zone, which
207
means that mesopores are well-developed with a good interconnectivity and are
208
mainly composed of parallel plate-shaped pores or wedge-shaped pores with one side
209
closed.
210
In the low-pressure zone, the adsorption capacity of medium-rank coals is
211
generally greater than that of low-rank coals, meaning that the quantity of micropores
212
in medium-rank coals increases with increasing metamorphism. The adsorption
213
capacity increases relatively slowly with increasing pressure in the medium-pressure
214
zone (Fig.2c, d), reflecting that the pore interconnectivity is very poor at this scale.
215
For some samples the desorption curves have an obvious hysteresis loop, indicating
216
that there are many fine or ink bottleneck-like pores in these coals. Some desorption
217
curves almost have no hysteresis loops in this region, indicating that there are many
218
cylindrical pores with one end closed. The N2 adsorption capacity increases rapidly in
219
the high-pressure zone, capillary condensation mainly occurs in the mesopores, and
220
the desorption curve has no hysteresis loops, indicating that the pores are primarily
221
wedge-shaped pores with one end closed.
222
For high-rank coals, nitrogen adsorption increases rapidly with increasing
223
pressure in the low-pressure zone, and the desorption curve has an obvious hysteresis
224
loop (Fig.2e, f), indicating that gas desorption from micropores is relatively difficult.
225
The micropores in high-rank coals are mainly cylinder-shaped metamorphic pores.
226
The adsorption capacity rises relatively slowly in the medium-pressure zone,
227
indicating that the transitional pores are poorly interconnected. The adsorption
228
capacity increases significantly in the high-pressure zone, and the corresponding
229
desorption curve has a large hysteresis loop, indicating that the mesopores are
230
partially interconnected fine bottleneck-shaped pores, and that the nitrogen molecules
231
are difficult to desorb from these pores due to capillarity.
232
In summary, low-rank coals contain more cylindrical or wedge-shaped pores
233
with one side closed, medium-rank coals contain more wedge-shaped pores, and
234
high-rank coals contain a large number of cylindrical- or fine bottleneck-shaped
235
pores.
236
3.2 Carbon dioxide adsorption experiment
237
The CO2 adsorption isotherm curves (Fig.3) belong to Type I as characterized by
238
IUPAC (Sing et al., 1984), which reveals the gas adsorption characteristics of the
239
pores with 1.4-1.6nm in diameter. The parameters of CO2 adsorption isotherm and
240
pores with size 1.4-1.6nm show similar variation laws while the adsorption capacity
241
varies greatly in various rank coals (Table 3). The SSA and volume of pores with size
242
1.4-1.6nm can be arranged in a descending order: high-rank coals > low-rank coals >
243
medium-rank coals, respectively. The adsorption isotherms of CO2 and N2 are
244
significantly different from each other for the coal samples, which means that the
245
adsorption mechanism and the pore size range measured by CO2 and N2 adsorption
246
methods are different. The adsorption capacity of CO2 in pores with size 1.4-1.6nm
247
are much higher than that of N2 in pores with size 1.7-300nm, and the SSA of pores
248
with size 1.4-1.6nm are very high. The main reasons include that the diameter of CO2
249
molecule is relatively small and the molecules can easily enter the pores with size
250
1.4-1.6nm and/or that the CO2 molecules have a strong affinity to the pore surface of
251
coal so that much more CO2 can be adsorbed (Okolo et al., 2015; Song et al., 2017).
252
3.3 Experimental results of CH4 adsorption
253 254
CH4 adsorption in coal can be described by a Langmuir adsorption model (Langmuir, 1918):
V=
255
PVL P + PL
1
256
where V is the adsorbed gas amount per unit mass of coal, cm3/g; VL is the
257
Langmuir volume of coal, cm3/g; P is the CH4 pressure, MPa; PL is the Langmuir
258
pressure, MPa. The CH4 adsorption capacities of 12 coal samples are presented in
259
Table 3. CH4 adsorption isotherms of various rank coals (Fig.4) show that: the VL
260
values of low-, medium- and high-rank coals are 11.17~17.83cm3/g, 11.81~
261
27.25cm3/g, and 28.49~52.63cm3/g, respectively. The PL values of low-, medium- and
262
high-rank coals are 3.84~9.78MPa, 1.14~3.25MPa, and 2.05~4.64MPa, respectively.
263
Generally, with the increase in coal rank, VL increases and PL first decreases and then
264
increases. The adsorption amount increases rapidly with increasing pressure at a
265
pressure of less than 3MPa and thereafter increases slowly. Within the initial stage of
266
adsorption isotherms, the coal contains abundant adsorption spaces and the pore
267
surface has a strong adsorption force to CH4. Therefore, the CH4 molecules can be
268
adsorbed easily as the adsorption pressure increases, and as the adsorption saturation
269
rises and the available adsorption space decreases in the coal matrix, and the
270
cumulative adsorption quantity increases slowly with further increasing pressure.
271
4 Discussion
272
As the degree of coalification rises, both the pore structure and the
273
methane-generated quantity vary. Pore evolution is one of the key factors that
274
influence the CH4 adsorption of coals.
275 276
4.1 Variation of pore structure in various rank coals 4.1.1 Variation characteristics of pore volume with metamorphism degree
277
Both the total pore volume and the micro-, transitional- and mesopores volumes
278
first decrease and then increase as the coal rank increases, and they decrease rapidly at
279
Ro,max<1.5% and then increase slowly at Ro,max>1.5% (Fig.5a,c,e,g). The relationship
280
between pore volume, SSA and Ro,max can be generalized as follows: y = Ae
281 282
BRo ,max
(2)
where y is the pore volume or specific surface area; A and B are the regression
283
coefficients; Ro,max is the maximum vitrinite reflectance. The detailed results are
284
shown in Figs 5 and 7.
285
A large number of thermogenic pores are produced in the process of thermal
286
metamorphism. This phenomenon is especially obvious in medium- and high-rank
287
coals (Wang et al., 2014), leading to an increase in micropore volume (Fig.5b, h). The
288
volume of pores with size 10-100nm and 100-300nm decreases significantly at
289
Ro,max<1.5% and then increases slowly (Fig.5c, e); the volume percentage of pores
290
with size 10-100nm decreases gradually (Fig.5d) and that of pores with size
291
100-300nm decreases rapidly (Fig.5f). It is possibly due to the variation of pressure
292
and coal composition during coalification. Cai et al. (2018) presented that the coal
293
matrix compressibility decreases more rapidly for low-rank coals than for the
294
medium- and high-rank coals due to mechanical compaction, dehydration and
295
degassing during coalification, with the wetting effect of water molecules on coals
296
seeming to weaken the link between coal particles. The pores >2nm are sensitive to
297
compaction induced by effective stress changes in the coal matrix, whereas the pores
298
<2nm are less effected. The content of moisture and porosity of pores >2nm in
299
low-rank coals are higher than those in the medium- and high-rank coals (Cai et al.
300
2018). Therefore, the influence of pressure on pore and bulk volumes is stronger for
301
low-rank coals than for medium- and high-rank coals. On the other hand, previous
302
research revealed that there are a large number of pores >2nm in inertinite (Giffin et
303
al., 2013). Inertinite content declines quickly in low- and medium-rank coals, which
304
can account for the rapid decrease in mesopore volume in the low- and medium-rank
305
coals.
306
The results of CO2 adsorption experiments show that the volumes of pore with
307
size 1.4-1.6nm of low-, medium- and high-rank coals are in the range of
308
0.051~0.058cm3/g, 0.022~0.042cm3/g and 0.039~0.083cm3/g, respectively. The
309
volumes of pore with size 1.4-1.6nm first decrease and then increase with an
310
inflection point near Ro,max=1.5%. While the volumes of pore with size 1.4-1.6nm of
311
low- and medium-rank coals changes slowly with increasing Ro,max and that of the
312
high-rank coals increases quickly. There are good correlations between the volumes,
313
SSAs of pore with size 1.4-1.6nm and Ro,max (Fig.5h, Fig.7h). The number of aliphatic
314
structures decreases and the number of aromatic structures increases during
315
coalification, resulting in the continuous variation of the coal macromolecules and the
316
evolution of pores <2nm (Liu et al., 2018). Based on thermal simulation and natural
317
metamorphism of coal, Liu et al. (2017b, 2018) found that the volume of pore <2nm
318
decreases to the lowest value near Ro,max=1.4% and then increases with the rise of
319
Ro,max, which is in accordance with our experimental results. The development of
320
pores <2nm is mainly controlled by the aliphatic parts of the chemical structure before
321
Ro,max<1.4%, and by aromatic rings when Ro,max=1.4%~4.0%, and the number of
322
micropore rises with the increasing aromatic carbon content.
323
The macromolecular structure model of the Xiaolongtan coal sample (Fig.6a) has
324
a large quantity of small molecular substances (-CH3, -OH or CH3-O-CH3) and they
325
are the active structures in the experiment of low-temperature oxidation (Meng et al.,
326
2017). The small molecular substances are sensitive to temperature and stress, leading
327
to a rapid change in the pore structure of low-rank coals during the evolution process.
328
For the medium-rank Malan8 coal sample, the macromolecular structure model
329
contains many cyclohexanes and benzenes (Fig.6b) (Si, 2014). The breaking off of
330
small molecular functional groups (-CH3, -OH, -COOH) and the condensation of the
331
aromatic cluster structure leads to the decrease of pores <2nm. For high-rank coals,
332
more methyl groups are lost because of the pervasive conversion from hydroaromatic
333
methyl structure to aromatic rings (Ahamed et al., 2019; Liu et al., 2019c), and the
334
proportion of C=C groups and C=O groups rises with the rise of coal rank (Sonibare
335
et al., 2010; He et al., 2019). The significant increase in aromatic cluster size results in
336
an increase in the volume of pore <2nm (Cao et al., 2013). The macromolecular
337
structure of the Chengzhuang coal (Ro.max=3.21%) comprises 2-5 polycyclic aromatic
338
hydrocarbons and the structural arrangement becomes relatively regular, with only a
339
few small molecular substances (-CH3, -OH) (Fig.6c) (Xiang et al., 2013). At the
340
same time, a large number of thermogenic pores are produced at high temperatures.
341
The above factors result in the rapid increase in micropore volume in high-rank coals.
342 343
4.1.2 Variation characteristics of pore specific surface area with metamorphism degree
344
The SSA of micro-, transitional- and mesopores, total SSA(BET) decline with
345
increasing Ro,max at Ro,max<1.5% and rise at Ro,max>1.5% (Fig.7a,c,e,g,h). It’s clear that
346
the SSA is greater for pores with size 1.4-1.6nm than for pores with a diameter of
347
1.7-300nm (Fig.7h). There is a non-linear relationship between the pore SSA and
348
Ro,max, and the regression coefficients are obtained on the basis of Eq.2 (Fig.7). The
349
SSA percentage of pores with size 1.7-10nm increases nonlinearly as Ro,max increases
350
(Fig.7b), while the SSA percentage of pores with size 10-100nm and 100-300nm
351
decrease nonlinearly with increasing Ro,max (Fig.7d, f). The SSAs of low- and
352
high-rank coals change quickly while that of the medium-rank coals changes slowly.
353
The mechanical strength and metamorphism of low-rank coals are low and sensitive
354
to pressure and temperature. Thus, the mechanical compaction and dehydration have a
355
great influence on the pore structure, resulting in SSA that varies quickly. The number
356
of small molecular functional groups (-CH3, -OH, CH3-O-CH3 and -COOH) in
357
high-rank coals decreases, and the number of aromatic cyclic structures with abundant
358
pores <2nm increases, causing a sharp increase in the SSA of BET and D-A (Wei et
359
al., 2019). The effects of compaction and thermal evolution on pore structure of
360
medium-rank coals are relatively strong, resulting in SSAs that are smaller for
361
medium-rank coals than for low- and high-rank coals.
362
4.1.3 Variation of pore diameter with metamorphism degree
363
For the LT-NA and CO2 adsorption experiments, the average pore diameter of the
364
coal matrix was calculated by BJH and D-A methods, respectively (Fig.8a, b). The
365
average pore diameter measured by LT-NA is mainly in the range of 10-60nm and the
366
variation range is relatively large. The size of micropores measured by CO2
367
adsorption is in the range of 1.49-1.59nm, which is much smaller than that measured
368
by LT-NA adsorption. The average pore diameter decreases rapidly with increasing
369
coalification degree in the lignite stage, and it changes relatively slowly with
370
increasing coal metamorphism for bituminous coals, and increases gradually for the
371
anthracite coals. The variation rule of both SSA and pore volume with metamorphism
372
degree is similar to that of average aperture with metamorphism degree.
373
The PSD of coal is closely related to the evolution of macromolecular structure
374
of coal during coalification. For the low-rank coals within the first stage of
375
coalification, the coal structure is relatively loose, and the content of primary pores is
376
high; therefore, the low-rank coals contain more meso- and transitional pores than the
377
medium- and high-rank coals. Compaction and dehydration have an effect on PSD
378
during coalification; therefore, the average pore diameter declines rapidly with
379
increasing coalification. During the transition from the first to the second stage of
380
coalification (Ro,max=0.6~1.2%) (Liu et al., 2010), the geological process promotes the
381
aromatization of coals and the coal structure becomes compact and the pore volume
382
declines as coalification continues. Particularly, the decrease of the meso- and
383
transitional pore number leads to the decrease of the average pore diameter for
384
medium-rank coals. The high-rank coals contain a large number of gas pores formed
385
by the action of high temperature. To some extent, the generation of endogenetic
386
fractures in the process of coalification also lead to an increasing trend in the average
387
pore diameter. In general, the condensed aromatic rings and the gradual regularity of
388
the molecular arrangement of coal lead to an increase in micropore quantity (Chen,
389
2001). Therefore, the content of micropores in high-rank coals further increases with
390
the average pore diameter displaying a slowly increasing trend.
391 392
4.2 Effect of pore structure on gas adsorption 4.2.1 Adsorption properties of various rank coals
393
Fig.9 shows that the VL increases linearly with the increasing coal rank for all
394
samples (R2=0.85). The adsorption capacity of CH4 is closely related to the physical
395
and chemical properties of coal, which is mainly controlled by coal composition and
396
structure. During the evolution process from low-, via medium- to high-rank coals,
397
the content of aromatic carbon in coal rises (Fig.6), and the vitrinite in coal increases
398
while inertinite and exinite decreases (Table 1), and the CH4 adsorption capacity also
399
increases. The -COOH and -OH show weak affinity to CH4 in low-rank coals, while
400
-CH3 and C=C functional groups in medium- and high-rank coals have a significant
401
influence on CH4 adsorption (Merkel et al., 2015). The influence of coal maceral of
402
various rank coals on methane adsorption is mainly manifested in the following
403
aspects: The methane adsorption capacities of various coal macerals can be arranged
404
in a descending order: vitrinite > inertinite > exinite (Beamish and Crosdale, 1998;
405
Karacan, 2003; Moore, 2012). It is verified that the vitrinite has a strong adsorption
406
force on methane molecules, and there are a large number of micropores and a big
407
SSA in vitrinite, which leads to a strong adsorption force on methane molecules.
408
Therefore, the methane adsorption capacity of coals increases with increasing vitrinite
409
content (Bustin and Clarkson, 1998). Inertinite contains a lot of irregular macropores,
410
and the distance between macropore walls can be relatively large, which results in
411
inertinite having a relatively low methane adsorption capacity and the methane
412
adsorption capacity of coal displays a decreasing trend with increasing inertinite
413
content (Chen, 2001; Lamberson and Bustin, 1993; Moore, 2012). Exinite is rare in
414
coals and it contains less pores and therefore it has no obvious influences on CH4
415
adsorption capacity of coals (Crosdale et al., 1998; Harris and Yust, 1979).
416
In terms of the results of previous studies (Merkel et al., 2015; Zhang et al.,
417
2011), the adsorption capacity of CH4 varies by coal rank. At Ro,max<1.5%, the total
418
pore volume of coal is relatively large, whereas the volume proportion of micropores
419
is small and the gas adsorption capacity of coal is relatively weak. When
420
Ro,max=1.5-3.45%, the coal is mainly composed of vitrinite and contains a large
421
quantity of micropores and is favorable for gas adsorption (Fig.10).
422
4.2.2 Effect of pore structure on CH4 adsorption
423
The relationship between the pore structure parameters and the adsorption
424
capacity of various rank coals shows that, there is a positive correlation between SSA,
425
volume of pores with 1.4-1.6nm in diameter and VL, respectively (Fig.11a, b). There is
426
also a linear correlation between the SSA percentage, pore volume percentage of
427
pores with a diameter of 1.7-100nm and VL (Fig.11c, d), while the total SSA (BET)
428
and the total pore volume (BJH) of low- and medium-rank coals are non-linearly
429
correlated with the VL (Fig.11e, f). Comparing the above relationships, it can be seen
430
that the SSA and volume of pores with size 1.4-1.6nm and 1.7-100nm in coal have an
431
important controlling effect on the CH4 adsorption capacity. The smaller the pore size
432
in the coal the larger the SSA and the higher the CH4 adsorption potential.
433
In the initial stage, the adsorption amount increases quickly with increasing
434
pressure, which is mainly controlled by the presence of relatively small pores, such as
435
micro- or transitional pores. The micropores have a greater SSA and provide a major
436
space for CH4 adsorption (Gensterblum et al., 2013; Li et al., 2018), the filling of
437
micro- and transitional pores is basically completed with the increase of gas pressure,
438
while the CH4 molecules in the meso- and macropores are adsorbed on the pore wall
439
surface under a strong equilibrium pressure (Wang et al., 2015). The influences of the
440
meso- and macropores on methane adsorption capacity of coal increase continuously
441
with increasing pressure. Fig.11e, f shows that, for some samples, the SSA and pore
442
volume are large, but the VL is relatively small. These coals are low- and medium-rank
443
coals, which indicates that for low- and medium-rank coals, the adsorption capacity is
444
not only affected by PSD, but also by other factors, such as, the coal composition
445
and/or coal rank. The molecular structure of low- and medium-rank coals contains
446
more hydrogen- and oxygen-bearing functional groups which have a relatively weak
447
adsorption force on methane molecules. The simulations on the coal molecular
448
structure and CH4 adsorption also show that the presence of moisture, results in a
449
decline in the adsorption capacity of CH4 (Zhang et al., 2014).
450
The pore volume and SSA affect the adsorption capacity, which is closely related
451
to the polycondensation of coal molecular structure during coalification. In the
452
process of coalification, the chemical reactions of dehydrogenation and deoxidation
453
continue and the number of aromatic ring structures increase continuously as well
454
(Fig.12a-c). The number of relatively large intergranular pores in coal decreases, but
455
the number of micropores increases (Fig.12d). These micropores result in a strong
456
methane adsorption capacity of coal. That is, the VL increases with the rise of the
457
Ro,max (Harris and Yust, 1979; Meng and Li, 2016).
458
5 Conclusion
459
N2, CO2 and CH4 adsorption experiments were carried out with various rank
460
coals, and the PSD characteristics and their effects on the CH4 adsorption capacity of
461
coals were investigated. The main conclusions are as follows:
462
(1) The coal matrix mainly contains cylindrical, thin bottle neck-shaped, ink
463
bottle-shaped, and parallel plate-shaped pores. The micropores in low- and
464
medium-rank coals are mainly cylindrical pores with one end closed. The meso- and
465
transitional pores are well interconnected and are primarily parallel plate pores with
466
one end closed. The high-rank coals mainly contain a large number of micropores
467
which are primarily cylindrical pores, the meso- and transitional pores in high-rank
468
coals are mainly open parallel plate pores.
469
(2) The distribution of total pore volume and SSA follow a similar exponential
470
law as the rise of coal metamorphic degree. The average pore diameter of coal matrix
471
first decreases and then increases with the rise of coal rank, with an inflection point
472
nearly at Ro,max=1.5%. The volume and SSA of micro-, transitional- and mesopores
473
have the similar variation law (asymmetric ‘‘U” shape) with Ro,max. Both SSA
474
percentage and pore volume percentage of micropores increase continuously, while
475
those of the transitional- and mesopores vary inversely with increasing Ro, max.
476
(3) The adsorption capacity of CH4 increases as the coal rank increases. There
477
are linear relationships between VL and Ro,max less than 3.5%, the SSA and the volume
478
of pores with a diameter of 1.4-1.6nm, SSA percentage and pore volume percentage
479
of pores of 1.7-100nm in diameter.
480
(4) Both the coal rank and PSD have an important influence on the CH4
481
adsorption. At pressures smaller than 3 MPa, the CH4 adsorption capacity is mainly
482
controlled by micropores and transitional pores. At pressure greater than 3 MPa, the
483
mesopores have an important influence on the adsorption capacity.
484
Acknowledgments
485
This work was financially supported by the Shanxi Province Science and
486
Technology Major Project (Grants 20191102001 and 20181101013), the National
487
Science and Technology Major Project of the Ministry of Science and Technology of
488
China
489
2016ZX05065). The authors thank the reviewers and the editor for their constructive
490
comments.
491
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Wei, Q., Li, X., Zhang, J., Hu, B., Zhu, W., Liang, W., Sun, K., 2019. Full-size pore
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structure characterization of deep-buried coals and its impact on methane
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adsorption capacity: A case study of the Shihezi Formation coals from the Panji
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Deep Area in Huainan Coalfield, Southern North China. J. Petrol. Sci. Eng. 173,
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975-989.
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Xiang, J., Zeng, F., Bin, L., Zhang, L., Li, M., Liang H., 2013. Construction of
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macromolecular structural model of anthracite from Chengzhuang coal mine and
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its molecular simulation. J. Fuel Chem. Techn. 41(4), 391-400.
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Xu, X., Meng, Z., Wang, Y., 2019. Experimental comparisons of multiscale pore
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structures between primary and disturbed coals and their effects on adsorption
691
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692
Yao, Y., Liu, D., Che, Y., Tang, D., Tang, S., Huang, W., 2010. Petrophysical
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characterization of coals by low-field nuclear magnetic resonance (NMR). Fuel
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Zhang, D., Cui, Y., Liu, B., Li, S., Song, W., Lin, W., 2011. Supercritical Pure
696
Methane and CO2 Adsorption on Various Rank Coals of China: Experiments and
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Modeling. Energy Fuels 25, 1891-1899.
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Zhang, M., Fu, X., Wang, H., 2018. Analysis of physical properties and influencing
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Zhang, J., Clennell, M.B., Dewhurst, D.N., Liu, K., 2014. Combined Monte Carlo and
702
molecular dynamics simulation of methane adsorption on dry and moist coal.
703
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704
Zhao, J., Tang, D., Qin, Y., Xu, H., 2019. Fractal characterization of pore structure for
705
coal macrolithotypes in the Hancheng area, southeastern Ordos Basin, China. J.
706
Petrol. Sci. Eng. 178, 666–677.
707
Zhao, Y., Liu, S., Elsworth, D., Jiang, Y., Jie, Z., 2014. Pore Structure
708
Characterization of Coal by Synchrotron Small-Angle X-ray Scattering and
709
Transmission Electron Microscopy. Energy Fuels 28(6), 3704–3711.
710
711 712 713
Fig.1 Comparison of pore size measured by different methods (Modified from Zhao et al., 2014).
adsorption desorption
1.5 1 0.5 0
0.2 0.4 0.6 0.8 Relative Pressure (P/P 0) (a)BZDB (Ro,max=0.43%)
adsorption desorption
8 6 4 2
1
adsorption desorption
1.5 1.0 0.5 0.0
1.2
0.2 0.4 0.6 0.8 Relative Pressure (P/P 0) (c)BD2 (Ro,max=0.77%)
0.6 0.4 0.2 0.0 0.2 0.4 0.6 0.8 Relative Pressure (P/P 0) (e)YC3 (Ro,max=2.57%)
1
0.2 0.4 0.6 0.8 Relative Pressure (P/P 0) (b)SCH2 (Ro,max=0.23%)
1
adsorption desorption
0.4 0.3 0.2 0.1 0.0 0
0.8
0
0.5
1
adsorption desorption
1.0
0
Adsorption volume (cm3/g)
Adsorption volume (cm3/g)
2.0
0
Adsorption volume (cm3/g)
10
0
0
715
Adsorption volume (cm3/g)
2
Adsorption volume (cm3/g)
Adsorption volume (cm3/g)
714
1.4
0.2 0.4 0.6 0.8 Relative Pressure (P/P 0) (d)DQ8-1 (Ro,max=1.8%)
1
adsorption desorption
1.2 1.0 0.8 0.6 0.4 0.2 0.0 0
0.2 0.4 0.6 0.8 Relative Pressure (P/P0) (f)SH3-1 (Ro,max=2.91%)
Fig.2 Low-temperature nitrogen adsorption-desorption curves.
1
716 Ro,max=0.47 Ro,max=0.77 Ro,max=1.56 Ro,max=2.57
Adsorption volume (cm3/g)
35 30
Ro,max=0.57 Ro,max=1.10 Ro,max=1.80 Ro,max=2.67
Ro,max=0.69 Ro,max=1.47 Ro,max=2.16 Ro,max=2.91
25 20 15 10 5 0 0
717 718
0.01 0.02 Relative pressure (p/p0)
0.03
Fig.3 CO2 adsorption isotherms in coal.
0.04
35
Ro,max=0.47% Ro,max=0.77% Ro,max=0.57% Ro,max=0.69% Ro,max=1.10% Ro,max=1.47% Ro,max=1.56% Ro,max=1.80% Ro,max=2.16% Ro,max=2.57% Ro,max=2.67% Ro,max=2.91%
Adsorption volume(cm3 /g)
30 25 20 15 10 5 0 0
719 720 721
2
4
6 Pressure(MPa)
8
Fig.4 Adsorption capacity of CH4 in various rank coals.
10
722 Ro,max<1.5%
4
Ro,max>1.5%
3 2 y = 0.7757e-1.687x R² = 0.12
1
y = 0.0205e0.9715x R² = 0.40
0 0
1
2
3
60
Percentage of micropores (1.7-10nm) volume (%)
Micropores (1.7-10nm) volume (×10-3 cm3 /g)
5
50 40 30 20 10 0
4
0
1
Ro,max(%)
Ro,max>1.5%
6 y = 0.0393e1.0051x R² = 0.75
4
y = 7.0883e-2.379x R² = 0.55
2 0 0
1
2 Ro,max(%)
3
Percentage of transitional (10-100nm) pores volume (%)
Transitional pores (10100nm) volume (×10-3 cm3 /g)
Ro,max<1.5%
40 30 20 10 0
4
0
1
Percentage of mesopores (100-300n m) volume (%)
Mesopores (100-300nm) volume (×10-3 cm3 /g)
Ro,max<1.5% Ro,max>1.5%
5 4 y = 5.3017e-2.392x R² = 0.59
2
y = 0.0506e0.6691x R² = 0.46
1 0 1
2
3
50 40 30 20 10 0
4
0
Micropores (1.4-1.6nm) volume (×10-2 cm3 /g)
Total pore volume (BJH) (×10-3 cm3 /g)
Ro,max<1.5% Ro,max>1.5%
15 14.52e-2.388x
y= R² = 0.55
y = 0.092e0.9886x R² = 0.84
5 0 2
Ro,max(%) (g)
1
2 Ro,max(%)
3
4
(f)
(e)
20
1
2 Ro,max(%)
60
Ro,max(%)
723 724 725 726
4
50
(d)
6
0
3
60
(c)
7
10
4
70
8
0
3
(b)
(a)
10
3
2 Ro,max(%)
3
4
10
Ro,max<1.5%
8
Ro,max>1.5% y = 7.4692e-0.95x R² = 0.75
6 4
y = 0.9511e0.7409x R² = 0.84
2 0 0
1
2
3
Ro,max(%) (h)
Fig.5 The variation of volume of (a) micropores (1.7-10nm), (b) percentage of micropores (1.7-10nm), (c) transitional pores, (d) percentage of transitional pores, (e) mesopores (100-300nm), (f) percentage of mesopores (100-300nm), (g) total pores (1.7-300nm) tested by low-temperature nitrogen adsorption, (h) micropores (1.4-1.6nm) tested by CO2 versus rank for all coals
727 728
investigated.
729 730
(a)
731 732
(b)
733 734 735 736
(c) Fig.6 Macromolecular structure of various rank coal, (a)xiaolongtan (adopted from Meng et al., 2017); (b)Malan8 (adopted from Si, 2014); (c)Chengzhuang (adopted from Xiang et al., 2013).
737 100
Ro,max<1.5% Ro,max>1.5%
y = 0.0222e0.9974x R² = 0.43 y = 0.5266e-1.338x R² = 0.08
0
1
2
3
4
Percentage of micropores (1.7-10nm) specific surface area (%)
Micropores (1.7-10nm) specific surface area (m2 /g)
4.0 3.5 3.0 2.5 2.0 1.5 1.0 0.5 0.0
80 60 40 20 0 0
Ro,max(%)
1
Ro,max<1.5%
1.2
Ro,max>1.5%
1.0 0.8 y = 0.9118e-2.359x R² = 0.48 y = 0.0049e1.0567x R² = 0.82
0.6 0.4 0.2 0.0 0
1 2 Ro,max(%) (c)
3
0
y = 0.1297e-2.334x R² = 0.53
0.05
y = 0.0015e0.6014x R² = 0.41
0.00 1
2 Ro,max(%)
3
Percentage of mesopores (100-300n m) specific surface area (%)
Mesopores (100-300nm) specific surface area (m2 /g)
0.10
0
10 5 0 0
4
7 6
y = 0.0047e2.0658x R² = 0.94
5 4
y = 2.0668e-1.685x R² = 0.24
1
250
2 Ro,max(%) (g)
2 Ro,max(%)
3
4
Ro,max<1.5% Ro,max>1.5% y = 25.356e0.7375x R² = 0.85
200 150 100 50
y = 187.32e-0.908x R² = 0.76
0
0 1
1
(f)
Ro,max<1.5% Ro,max>1.5%
Micropores (1.4-1.6nm) specific surface area (m2 /g)
Total pore specific surface area (BET) (m2 /g)
4
15
(e)
738 739 740 741 742
2 3 Ro,max(%)
(d)
Ro,max>1.5%
0.15
0
1
20 Ro,max<1.5%
2
4
80 70 60 50 40 30 20 10 0
4
0.20
3
3
(b)
1.4
Percentage of transitional (10-100nm) pores specific surface area (%)
Transitional pores (10100nm) specific surface area (m2 /g)
(a)
2 Ro,max(%)
3
4
0
1
2 Ro,max(%)
3
(h)
Fig.7 The variation of specific surface area of (a) micropores (1.7-10nm), (b) percentage of micropores (1.7-10nm), (c) transitional pores, (d) percentage of transitional pores, (e) mesopores (100-300nm), (f) percentage of mesopores (100-300nm), (g) total pores tested by low-temperature nitrogen adsorption (BET), (h) micropores (1.4-1.6nm) tested by CO2 adsorption (D-A) versus rank for all coals investigated.
70
Average micropores (1.41.6nm) diameter (nm)
Average pore diameter tested by N2 adsorption (nm)
743 60 y = 5.52x 2 - 25.675x + 41.152 R² = 0.36
50 40 30 20 10 0
1.60 1.58
y = 0.0242x2 - 0.0989x + 1.6047 R² = 0.43
1.56 1.54 1.52 1.50 1.48
0
1
2
3
4
0
1
Ro,max(%)
(a)
2 Ro,max(%)
3
(b)
744
Fig.8 The variation of (a) average pore diameter (BJH) tested by low-temperature nitrogen
745
adsorption, (b) micropores (1.4-1.6nm) (D-A) tested by CO2 adsorption versus rank for all coals
746
investigated.
747
Langmuir volume (cm3 /g)
50 y = 13.04 x + 2.15 R² = 0.85
40 30 20 10 0 0
748 749
1
2 Ro,max(%)
3
Fig.9 The Langmuir volume of various rank coals.
4
35
16
30
14 12
25
10
20
8
15
6
Total pore volume
10
4
5
2
0
0 0
750 751
×10-3 cm3 /g
18
Langmuir volume
Total pore volume
Langmuir volume(cm3 /g)
40
0.5
1
1.5
2
2.5
3
3.5
Ro,max(%)
Fig.10 The variation of Langmuir volume and total pore volume versus Ro,max.
60 y = 0.21x - 0.08 R² = 0.67
50 40 30 20 10 0 0
Langmuir volume (cm3 /g)
Langmuir volume (cm3 /g)
752
50 100 150 200 250 Micropores (1.4-1.6nm) specific surface area (D-A) (m2 /g)
60 y = 535.24x + 0.68 R² = 0.64
50 40 30 20 10
0 0.00 0.02 0.04 0.06 0.08 0.10 Micropores (1.4-1.6nm) volume (DA) (cm3 /g) (b)
50
y = 3.43x - 304.83 R² = 0.50
40 30 20 10 0 90
92 94 96 98 100 Percentage of specific surface area (BET) with 1.7-100n m in diameter (%)
Langmuir volume (cm3 /g)
60
60
cm3 /g)
Langmuir volume (cm3 /g)
(a)
60
y = 0.97x - 42.12 R² = 0.51
50 40 30 20 10 0 50
60
Langmuir volume
40
Low-rank coals Medium-rank coals High-rank coals Fitting of High-rank coals
50
30 20
(d)
y = 7.70x + 32.0 R² = 0.41
10 0 0 1 2 3 4 5 6 2 Specific surface area (BET) (m /g) (e)
753 754 755 756 757
Langmuir volume
(cm3 /g)
(c)
60 70 80 90 Percentage of volume (BJH) with 1.7-100nm in diameter(%)
50 40 30 20
Low-rank coals Medium-rank coals High-rank coals Fitting of High-rank coals y = 15202x + 24.38 R² = 0.67
10 0 0.000
0.005 0.010 0.015 0.020 Pore volume (BJH) (cm3 /g) (f)
Fig.11 The variation of (a) micropore (1.4-1.6nm) specific surface area (D-A), (b) micropore (1.4-1.6nm) volume (D-A), (c) percentage of specific surface area (BET) with 1.7-100nm in diameter, (d) percentage of volume (BJH) with 1.7-100nm in diameter, (e) total specific surface area (BET), (f) total pore volume (BJH) versus Langmuir volume for all coals investigated.
758 759
Fig.12 Schematic diagram of the evolution of pore structure in coal.
760
Table 1 Proximate analysis and petrographical data of coals. Proximate analysis
761 762 763
No.
Sample information
Ro,max(%)
1
Ha’erwusu No.6(HEWS6)
2 3
Coal composition
Mad (%)
Aad (%)
Vad (%)
V(%)
I(%)
E(%)
M(%)
0.47
3.71
8.03
33.24
57.6
22
10.8
9.5
Shendong 5-2(SD5-2) Shichaohe No.1(SCH1)
0.57 0.29
4.52 26.41
3.49 5.01
29.38 33.91
76.26 81
20.43 17
1.167 0
2.15 2
4
Shichaohe No.2(SCH2)
0.23
25.02
20.46
30.52
80.2
15
0.2
4.6
5 6
Buzhaodongbang(BZDB) Xiaolongtan No.1(XLT1)
0.43 0.23
29.3 34.45
5.19 7.14
35.58 31.42
80.8 83
17.2 12
0.4 2
1.6 3
7 8 9 10 11 12 13
Puyang No.1(PY1) Shanxincun No.1(SXC1) Baode No.2(BD2) Baode No.8(BD8) Malan No.8(ML8) Malan No.2(ML2) Dongqu No.8-1(DQ8-1)
0.32 0.36 0.77 0.69 1.47 1.1 1.80
20.24 47.95 3.65 2.47 0.69 0.86 0.82
9.61 15.83 8.40 5.49 10.71 7.71 8.03
34.19 24.05 32.77 35.81 17.56 24.21 14.18
84.2 80.6 83.27 54.1 74.39 91.04 88.52
12.4 16 6.57 16.5 22.68 3.87 6.42
0.4 0.1 3.59 6.7 0 0 0
3 3.3 6.58 22.60 2.93 5.09 5.06
14 15
Dongqu No.2(DQ2) Dongqu No.8-2(DQ8-2)
1.56
0.80 0.89
9.12 2.97
15.66 13.67
87.54
4.55
0
7.91
16 17
Zhaozhuang No.3(ZZ3) Shihe No.3(SH3-1)
2.16 2.91
0.89 1.92
10.63 8.62
10.68 6.25
87.92 94.3
5.941 0.475
0 0
6.14 5.23
18 19
Changping No.3(CP3) Yuecheng No.3(YC3)
2.67 2.57
1.12 1.88
8.09 10.96
8.61 6.41
94.93 95.02
0.48 0.657
0 0
4.59 4.22
20
Shihe No.3-2(SH3-2)
3.45
0.71
13.39
12.01
Note: Mad, Aad and Vad are the moisture, ash and volatile matter content on air-dried basis, respectively; V, I, E, M represent the content of vitrinite, inertinite, exinite and mineral, respectively.
764
Table 2 The pore parameters tested by low-temperature nitrogen adsorption for coal samples. BET (m2/g)
Avd(nm)
Vt(cm3/g)
HEWS6 SD5-2 SCH1
2.2101 4.9558 0.3711
31.847 15.756 45.484
SCH2
5.8303
BZDB XLT1
Samples
765 766 767 768 769
Percentage of pore volume (%)
Percentage of SSA (%)
V1
V2
V3
S1
S2
S3
0.015629 0.016776 0.002656
7.07 21.96 2.30
50.96 43.40 52.45
41.97 34.64 45.25
33.62 72.27 13.32
56.75 23.60 74.93
9.63 4.13 11.75
11.180
0.014169
28.35
52.34
19.31
75.62
23.07
1.32
0.2670
61.086
0.002722
1.10
42.30
56.61
12.60
68.01
19.39
0.3042
52.200
0.002993
2.11
43.86
54.03
24.61
59.89
15.51
PY1
2.5319
15.097
0.007381
21.66
53.13
25.20
66.73
31.02
2.25
SXC1
1.0653
30.217
0.008007
6.96
41.81
51.24
56.61
32.45
10.94
BD2
0.9263
15.203
0.002826
21.00
58.02
20.98
63.09
34.90
2.01
BD8 ML8
0.4957 0.5169
24.337 14.910
0.002120 0.000483
10.37 16.09
58.83 43.80
30.79 40.10
42.73 75.69
52.41 20.60
4.86 3.70
ML2 DQ8-1
0.2279 0.0986
29.663 16.426
0.000439 0.000664
5.54 14.53
52.27 50.86
42.19 34.61
45.26 68.08
46.50 28.19
8.24 3.73
DQ2
0.2003
19.493
0.000495
11.47
48.03
40.50
65.44
29.49
5.07
DQ8-2 ZZ3 SH3-1 CP3
0.1509 0.2133 2.2343 1.2956
36.676 9.650 5.895 10.924
0.002786 0.000537 0.001676 0.000830
4.56 29.87 55.91 27.41
55.49 41.37 31.61 49.07
39.95 28.76 12.48 23.52
32.89 84.56 91.81 78.27
59.21 13.61 7.74 20.17
7.89 1.83 0.45 1.56
YC3 SH3-2
1.2298 5.3582
6.500 25.231
0.001482 0.003414
48.27 5.57
34.69 62.71
17.04 31.72
90.25 45.47
9.10 49.91
0.65 4.62
Avd-average pore diameter (BJH) (nm); Vt-total pore (1.7-300nm) volume (cm3/g); V1-micropores (1.7-10nm) volume; V2- transitional pores volume; V3-mesopores (100-300nm) volume; S1-micropores (1.7-10nm) specific surface area; S2-transitional pores specific surface area; S3- mesopores (100-300nm) specific surface area.
770
Table 3 Calculation parameters of CO2 and CH4 adsorption. Samples
771 772
CO2 adsorption
CH4 adsorption
SD-A
VD-A
Avds
VL
PL
HEWS6
129.03
0.051
1.59
11.17
3.84
SD5-2
146.35
0.058
1.58
17.83
9.78
BD2
86.83
0.033
1.51
11.81
3.25
BD8
78.66
0.030
1.51
12.5
3.21
ML8
57.33
0.022
1.51
18.55
1.98
ML2
59.09
0.023
1.54
17.42
2.14
DQ8-1
109.44
0.042
1.53
27.25
2.03
DQ2
74.82
0.028
1.50
18.45
1.14
ZZ3
104.36
0.039
1.49
28.49
2.05
SH3-1
199.44
0.074
1.49
44.05
4.32
CP3
169.96
0.065
1.53
41.15
2.96
YC3
217.91
0.083
1.53
52.63
4.64
SD-A-amicropores (1.4-1.6nm) specific surface area, m2/g; VD-A-micropores (1.4-1.6nm) volume, cm³/g; Avds-Average diameter of micropores (1.4-1.6nm), nm; VL- Langmuir volume, cm3/g; PL-Langmuir pressure, MPa.
Highlights 1.Variation of pore parameters of coal matrix with coal rank are analyzed quantitatively. 2.Volume and SSA of pores initially decrease and then increase with increasing Ro,max. 3.Influence of different-type pores on gas adsorption capacity is analyzed. 4.Methane adsorption is controlled by micro-, transitional- and mesopores successively.
The author contributions are as follows: Jiwei Yan: Collection and assembly of data, writing the article, N2, CO2 adsorption experiments. Zhaoping Meng: Research concept and design, data analysis and interpretation. Kun Zhang: Critical revision of the article. Huifang Yao: Collection samples. Haijin Hao: CH4 adsorption experiment.
Declaration of interests ☒ The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper. ☐The authors declare the following financial interests/personal relationships which may be considered as potential competing interests:
No conflict of interest.