Article
Subscriber access provided by RYERSON UNIVERSITY
Pyrolysis and Combustion Enhance Recovery of Gas for Two China Shale Rocks Wei Chen, Yafeng Lei, Yilin Chen, and Jiafeng Sun Energy Fuels, Just Accepted Manuscript • DOI: 10.1021/acs.energyfuels.6b02274 • Publication Date (Web): 27 Oct 2016 Downloaded from http://pubs.acs.org on November 1, 2016
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
Energy & Fuels is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 23
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
1 2 3 4 5 6 7 8 9
Energy & Fuels
Pyrolysis and Combustion Enhance Recovery of Gas for Two China Shale Rocks Wei Chena,*, Yafeng Leib,Yilin Chen c, Jiafeng Sund a School of Energy, Soochow University, China b General Electrical Company, Houston, TX 77041, USA c School of Resource and Geosciences, China University of Mining and Technology, Xuzhou 211116, China d Department of Mechanical Engineering, Texas A&M University, College Station, TX77843, USA
10 11 12 13 14
Corresponding Author:
15
Professor: Wei Chen
16
School of Energy,
17 18 19 20
Soochow University, China Suzhou 215006, China Email:
[email protected] 21 22 23 24 25 26 27 28
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
29
Abstract
30
Due to the low matrix permeability of shale formation in China, the extraction of shale gases
31
from the rocks become difficult. Recently, combustion and other thermal treatment methods
32
were employed to remove organic matters from the shale to increase rock's permeability. In
33
this study, geothermal properties of two shale samples were tested and analyzed. It was found
34
that shale 1# has a higher methane adsorption capacity, reflectance, and porosity than that of
35
shale 2#. Since the shale has low permeability, the two samples were heated up in a TGA
36
instrument in inert (N2 and helium) and un-inert environments (air and CO2) to increase shale
37
permeability by removing the organic matters. From TGA weight loss curves, it was found
38
that the weight loss rates were high in helium environment compared to CO2 and air since
39
helium has higher thermal conductivity which can promote organic matter cracking. However,
40
organic matters were not oxidized with air and some of them were still remained inside the
41
samples at the end of experiments. As a result, pure air may not be a suitable combustion agent
42
to burn the organic matters. Furthermore, the experiment reveal that carrying gases with high
43
thermal conductivity was beneficial for the organic matter cracking.
44
Key Words: Shale, Permeability, Thermal conductivity, Combustion, Organic matter
45
Acronyms
46
BET
Brunauer–Emmett–Teller
47
FC
Fixed carbon
48
Ro
The vitrinite-like macerals reflectance
49
TC
Thermal conductivity
50
TGA
Thermogravimetric analysis
51
TOC
Total organic carbon
ACS Paragon Plus Environment
Page 2 of 23
Page 3 of 23
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
52
Energy & Fuels
VM
Volatile matter
53 54
1. Introduction
55
With the increase of energy demand, shale gas has attracted increasing attentions. Shale gas/oil
56
was considered to be a cleaner and efficient energy to replace other conventional fuels such as
57
coal for power generation. As an unconventional fuel, shale gas was produced from
58
organic-rich shale. With the development of horizontal drilling and hydraulic fracturing
59
technology, shale gas has become more economical to produce around the world, especially in
60
USA[1]. According to Perry et al, the total geological reveres of shale gas reservoirs are
61
estimated to be approximately 456.24 x1012 m3 globally[2]. China has an abundant of different
62
types of shales. These shales include not only organic-rich Paleozoic marine shale but also
63
Mesozoic and Cenozoic continental shales. These shales contain large amount of gas reserve
64
and it was estimated that the total geological reserves of shale gas reservoirs of china is around
65
134 X1012 m3[3]. However, large scale shale gas exploration is the primary challenge due to
66
the low porosity and low permeability of shale formation.
67
Normally, a shale gas reservoir is a source rock which retains hydrocarbons over geologic
68
times. It comprises total organic carbon (TOC) stored inside the matrix[4]. Gas storage in the
69
shale is generally categorized into three groups[5]: (1) a free gas state in pores and fractures;
70
(2) an adsorbed state on the surface or inside organic matter and minerals; and (3) a dissolved
71
state in organic matter and water. For group (1), gas is adsorbed in micropores because of
72
large specific surface area and great adsorption potential in narrow pores[6]. Pore structure is
73
the key factor influencing the occurrence of shale gas and gas storage capacity[7]. However,
74
due to extremely low matrix permeability, clusters of mineral-filled “natural” fractures, and an
75
organic-rich deposition, extraction of the shale gas becomes difficult [8]. Heat treatment
76
would be one of the methods to improve permeability. Jamaluddin et al found that thermal
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
77
treatment can increase permeability in tight gas reservoirs by vaporizing the capillarily
78
blocked water, dehydrating the clay-bound water, destroying the clay lattice and creating
79
thermally induced microfractures[9]. Different technologies such as electrical heater, high
80
temperature steam, and microwave heating were employed in oil and gas industry to extract
81
oil and gas[10]. When shale rocks get hot, the absorbed gases such as methane obtain energy
82
from the injected steam or hot water and leave the rocks. Thus, a large amount of gases can be
83
produced and collected from the shale. According to Fourier’s law, the amount of heat flow to
84
the shale could be determined using the product of thermal conductivity and the temperature
85
gradient. Different types of rocks, sandstones, mudstones, shales, marls, and lime stones, were
86
analyzed to define the relationships between thermal conductivity and other physical
87
properties of rocks[11] . The sandstones, with a large effective porosity typically ranging
88
between 16% and 30%, have bulk thermal conductivities ranging between 2.1 and 3.9
89
W/m/K[12]. Rock thermal conductivity is one of the most important parameters to affect shale
90
gas extraction and its value strongly depends on mineral composition. It increases with
91
augmenting content of minerals of high thermal conductivity mineral such as quartz, and
92
decreases with the increase of low conductivity minerals such as clay minerals[11].
93
In addition to mineral composition, pressures, temperature, porosity and water saturation
94
would affect the rock thermal conductivity. Li et al found that thermal conductivity of the
95
rocks increases with increase of pressure ,but decreases with rising of temperature[13].
96
Gornov et al conducted “optical scanning” of core samples using “λ-profile” method to
97
determine the rock thermal conductivity and found that the thermal conductivity of the
98
regional rocks depends on mineral composition, structure, and texture[14]. Roy et al
99
investigated the effect of water saturation on rock thermal conductivity measurements and
100
found that thermal conductivity of porous rocks under water-saturated state is greater than that
101
under dry state [15]. Popov et al used experimental methods to find the relationship between
ACS Paragon Plus Environment
Page 4 of 23
Page 5 of 23
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
102
permeability, electrical and thermal conductivity[16].
103
In addition to thermal conductivity, the permeability of gas shale is also affected by the
104
organic rich deposition (kerogen) [17, 18].
105
hydraulic fracturing , research aiming at alternative permeability enhancement methods such
106
as combustion were considered to be one possible method to remove the organic matters such
107
as kerogen, portion of naturally occurring organic matter [4] . However, few studies have been
108
conducted using different carrying gases to remove organic matters during combustion and
109
pyrolysis processes to investigate the effect of thermal treatment methods on the shale
110
property changes .
111
The main objective of this study is to study thermal and geochemical properties of two
112
Chinese shales and explore the mechanics of shale combustion and pyrolysis behaviors under
113
different gas environments. The thermal conductivity, pore size, and methane adsorption
114
capacity of the two samples were investigated. Moreover, helium, CO2 and air were employed
115
as carrying gas to remove the organic matters of shale rocks to enhance the permeability.
116
Furthermore, the weight loss process and weight loss rate characteristics obtained from TGA
117
experiment were studied to investigate the effect of heating rates and purging gases properties
118
on organic matter liberation behaviors.
119
2. Properties of Shale Samples
120
2.1 Geochemical properties of shale samples
121
These shale samples were collected from two different drilling holes at ShangGu basin,
122
Shanxi province, China. The samples obtained from this area have a cylinder shape and gray
123
color (Figure 1).
Due to the potential environmental impact of
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
124 125
Figure 1. Illustration of shale 1# and 2#
126
Shale 1# and 2# were buried at depth of 609 and 35 meters, respectively. Before the TGA tests,
127
the raw samples were crushed and screened to small particles with different size. The samples
128
of particles were sent to Jiangsu Coal Research Laboratory for different physical and chemical
129
analyses. In order to explore the shale properties such as thermal properties, proximate and
130
ultimate analyses were conducted as shown in Table 1. Similar to other fossil fuels, proximate
131
analysis provides the composition of the shale in terms of moisture, volatile matter (VM),
132
fixed carbon (FC), mineral matter and ash [17]. It also provided organic matter mass
133
percentage of the shale samples. Table 1 lists the proximate and ultimate analysis results of the
134
two shale samples.
135 136 137 138 139 140
ACS Paragon Plus Environment
Page 6 of 23
Page 7 of 23
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
141
Energy & Fuels
Table 1. Proximate and ultimate analysis shale 1# 0.4 88.08 9.66 2.22 4.63 6.19 0.67 0.13 0.26 1755.50
Moisture Ash VM FC Carbon Oxygen Hydrogen Nitrogen Sulfur HHV (kJ/kg)
shale 2# 0.7 89.09 8.11 2.71 6.24 3.09 0.72 0.16 0.63 2764.08
Dry, Ash Free Moisture Ash VM FC Carbon Oxygen Hydrogen Nitrogen Sulfur HHV (kJ/kg)
0.00 0.00 81.31 18.69 39.00 52.08 5.61 1.10 2.21 14757.13
0.00 0.00 74.77 25.23 57.57 28.50 6.64 1.50 5.79 25498.21
Chemical formula
CH1.7105O1.0024N0.0242S0.0212
CH1.3715O0.3716N0.0223S0.0377
142 143
In addition to proximate and ultimate analysis, the thermal maturity was an important
144
parameter to evaluate the gas self-generation and storage capacity, i.e., gas sorption capacity
145
[19].Thus, understanding of the thermal maturity of the shale samples would be the first step
146
to explore the gas adsorption mechanisms. Table 2 provides the geochemical characteristics
147
analysis of two samples including exinite, vitrine, and inertinite weight percentage as well as
148
the vitrinite-like macerals reflectance (Ro).
149
Table 2. Geochemical characteristics of the shale samples Sample No.
Exinite(%) Vitrinite (%)
shale 1# shale 2#
54 68
18 14
Inertinite(%)
Ro (%)
28 18
1.92 1.85
150
ACS Paragon Plus Environment
Organic Matter type Ⅱ Ⅱ
Energy & Fuels
151
2.2 Shale Pore Size Analysis
152
Pore system of the shale samples was analyzed by nitrogen adsorption. Measurements were
153
conducted in a Surface Area and Pore Size Analyzer (V-Sorb 2800TP) according to Rock
154
surface area and pore size distribution measurement method: static nitrogen adsorption
155
capacity (SY/T 6154-1995). Pore Size Analyzer used the standard static volumetric method to
156
measure the amount of adsorbed gas. In order to removal of bound water and capillary water
157
adsorbed in the clays, about 200-300 mg of the small sized samples were outgassed at 383 K
158
for 5 hours at a vacuum environment (10 µm Hg). Nitrogen with purity of 99.999% was used
159
as an adsorbent at 77 K, and adsorption–desorption isotherms were obtained at relative
160
pressures (p/p0) between 0.01 and 1. Figure 2 gives the adsorption and desorption process of
161
the two samples under liquid nitrogen environments. Under the similar condition, shale 1# has
162
larger adsorption capacity than that of shale 2#.
Absorption-shale 1#
Desorption-shale 1#
Absorption-shale 2#
Desorption shale 2#
8
Absorption (ml/g,STP)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 8 of 23
7 6 5 4 3 2 1 0 0
163
0.2
0.4
0.6
0.8
1
Relative pressure (P/P0)
164
Figure 2. Liquid nitrogen adsorption and desorption curves of shale samples
165
Figure 3 gives the pore size distribution of the shale 1# and Shale 2#. It was found that shale
ACS Paragon Plus Environment
Page 9 of 23
166
1# has more small size pores than shale 2# (< 9 nm) while shale 2# has more large size pores (>
167
10 nm). According to the test, the porosity of the shale 1# and shale 2# is 3.12% and 2.56%,
168
respectively.
169
Pore size distribution shale 1# shale 2#
1.20E-03
Pore Volume (ml/g)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
1.00E-03 8.00E-04 6.00E-04 4.00E-04 2.00E-04 0.00E+00 193.4
98.4
41
24.7
12.6
8.1
5.8
4.5
3.5
2.8
2.3
Pore size(nm)
170 171
Figure 3. Pore size distribution of the shale samples
172
2.3 High-pressure Methane Sorption Experiments
173
The sorption of hydrocarbon gases (mostly methane) in shales not only provides gas-storage
174
capacity but also the “free-gas” capacity in the pore system[20]. In order to investigate the
175
sorption and desorption behavior of shale samples, high-pressure sorption experiments of
176
methane were performed by the volumetric method. The methane sorption capacity of the
177
shale samples was determined by a high-pressure volumetric sorption apparatus (IS-300). All
178
methane isothermal adsorptions were measured at 25 ± 0.1 °C. The adsorption data were then
179
fitted to the Langmuir equation as shown in Equation (1)[21].
180 181
V=
VL P PL + P
(1)
ACS Paragon Plus Environment
Energy & Fuels
182
where V is the volume of adsorbed gas per unit volume of the shale sample at pressure P, VL
183
is the Langmuir volume, P is the gas pressure, and PL is the Langmuir pressure, or the pressure
184
at which half the Langmuir volume of gas is adsorbed. It was found from Figure 4 that with
185
the increase of pressure P, the adsorption capacity of both samples increased. Furthermore,
186
sample 1 has higher methane adsorption capacity than that of sample 2. shale 1#
shale 2#
3.5 3 2.5 Absorptiopn (CM 3/g)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 10 of 23
2 1.5 1 0.5 0 0
2
187
4
6 Pressure (Mpa)
8
10
12
188 189
Figure 4. CH4 adsorption of shale 1# and 2#
190
2.4 Thermal Conductivity Test
191
The thermal conductivity of shale rocks is an important property for determining the amount
192
of heat to extract the methane gas from rock. Typical techniques for the measurement of rock
193
thermal conductivity include the divided-bar steady-state technique, the needle-probe transient
194
method and the optical scanning method[12]. In this study, the hot-wire method (instrument
195
XIATECH TC3000) was employed to experimentally determine the thermal conductivity (TC)
196
of shale samples. The shale samples were embedded in a hot wire and heated with a constant
ACS Paragon Plus Environment
Page 11 of 23
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
197
electric heating power. The TC of the samples could be determined through the
198
temperature-increment rate with the temperature change obtained over time (Figure 5). The
199
experiments were repeated five times and average values were obtained for each sample.
200 201
Figure 5. Hot wire method of temperature change rate with time of shale 1#
202
2.5 TGA Test of Shale Sample
203
In order to study the effect of thermal treatment methods such as combustion and pyrolysis on
204
the shale rock permeability, thermal gravimetric and differential thermal analyses on shale
205
samples were conducted using a TGA-DTA (TA SDT Q600). In each experiment, about 10-12
206
mg samples were heated in a ceramic pan at a rate of 20 oC/min from ambient temperature to
207
1000 oC in different gas environments. The mass loss of the samples (m) as a function of
208
temperature (T) was recorded for the trace. Figure 6a gives the shale 1 # sample weight loss
209
processes under different purge gas environments, and Figure 6b gives the sample weight loss
210
processes of Shale 2 # under different heating rate conditions using helium as the purging gas.
211
Both shales have low moisture (less than 1%) and volatile matter (8% for shale 1# and 9% for
212
shale 2#). Moreover, both shale rocks share the same weight loss trend. The main weight loss
213
process was occurred between the temperature 300 to 600 oC, which corresponding to organic
ACS Paragon Plus Environment
Energy & Fuels
214
matter decomposition and cracking of heavy hydrocarbons. With the temperature inccreasing
215
further (above 600 oC), the weight of the shale decreased slightly which may be due to the
216
dissociation of clay materials and the carbonate minerals components of the shale samples[22].
217
Moreover, it was observed that it was easier for samples to lose weight when helium was used
218
as purge gas, followed by air and then CO2. This is because helium has significantly higher
219
thermal conductivity (0.16 w/m2) while the thermal conductivities of air and CO2 are around
220
0.02 w/m2. Sample lost more weight under helium condition since more heat flux could
221
penetrate into the shale samples which resulted in quickly breakdown of the bonds among the
222
hydrocarbons of the shale samples. It was interesting that samples were not oxidized by air
223
since similar weight percentage remained at the end of the experiment.
224
According to the TGA manufacturer, the uncertainty of the temperature is 0.1% of the
225
measured value. The uncertainty of lignite weight is 0.1 mg.
226
He
Air
CO2
100 99 98 97
Weight %
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 12 of 23
96 95 94 93 92 91 0
227 228 229
100
200
300
400
Temperature
500
600
700
800
(oC)
Figure 6a. Weight loss process of shale1# under different purge gas conditions at heat rate 10 o C/min
ACS Paragon Plus Environment
Page 13 of 23
5 oC/min
100
10 oC/min
20 oC/min
99 98
Weight %
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
97 96 95 94 93 92 91 0
200
400
600
800
1000
Temperature (oC)
230 231
Figure 6b. Weight loss process of shale2# under helium conditions at different heat rates
232
3 Results and Discussion
233
3.1 Fuel Properties
234
It can be found from Table 1 that both shale samples have very high ash content (>88%) and
235
low moisture content (600 oC), weight loss rate did not significantly increase
308
for air. More weight was supposed to lose if organic matters were oxidized by oxygen under
309
high temperature. However, the percentages of weight were similar at the end of experiments
310
under air and CO2 condition (Figure 6a), which means some organic matter such as fixed
311
carbon did not oxidize and remained inside the samples. This may be due to the fact that
312
organic matters were covered by the minerals and muds or the small pores were blocked
313
which prevent the air to contact with organic matters. Thus, simply using air as oxidizer to
314
burn the organic matter of shale rocks may not be an effective method to improve the
315
permeability. More experiments including pure oxygen combustion will be conducted in the
316
near future to explore the reason behind this. Helium
Air
CO2
1 0.9 0.8 0.7
wt%/Min
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
0.6 0.5 0.4 0.3 0.2 0.1 0 0
200
400
Temperature
317
600
800
(oC)
318
Figure 8. Weight loss rate process of shale 1# in different environment at heating rate 20
319
o
320
Figure 9 gives the weight loss rate curves of shale 1# under different heating rates with air
321
as carrying gas. It is not surprising that the maximum weight loss rate (the peak point)
C/min
ACS Paragon Plus Environment
Energy & Fuels
322
increased with the increase of the heating rates. Moreover, the maximum weight loss rate (the
323
peak point) switched to higher temperature. For example, the maximum weight loss rate was
324
almost 1wt%/min at 520 ⁰C with heating rate 20 oC/min, while it was only 0.3 wt%/min at 420
325
o
326
helped the organic matters to liberate from the shale samples.
C with heating rate 5 oC/min. Thus, higher heating rate promoted the weight loss rate and
5 oC/min
10 oC/min
20 oC/min
1 0.8
wt%/min
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 18 of 23
0.6 0.4 0.2 0 0
327
200
400
600
800
1000
Temperaure (oC)
328 329 330 331
Figure 9. Weight loss rate curves of shale 1# under different heating rates with air as carrying gas
332
rate 5 oC/min using helium as carrying gas. These two curves exhibit the similar weight loss
333
trend. The weight loss rate started increasing when temperature was above 300 oC and the
334
quick organic releasing zone was between temperature 330 oC-500 oC. Moreover, shale 2# has
335
a higher release rate when temperature was below 420 oC while shale 1# lost more organic
336
matters above temperature 420 oC since shale 1 # has a higher activation energy.
Figure 10 gives the comparison of the weight loss rate curves of shale 1# and 2# at heating
337
ACS Paragon Plus Environment
Page 19 of 23
Shale 1#
Shale 2#
0.25
wt%/min
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
0.2
0.15
0.1
0.05
0 0
200
400
600
Temperature
338
800
1000
(oC)
339
Figure 10. Weight loss rate of shale 1# and 2# at 5 oC/min under helium environment
340
4. Conclusions
341
In the study, geothermal properties of two shale samples were tested. Combustion and
342
pyrolysis were employed to remove their organic matters to increase their permeability of the
343
shale samples. Following are the conclusions for this study:
344
(1) The total organic content of the shale samples is around 10% and hydrocarbon generating
345
potential of these two shale samples is high. Moreover, the Ro of shale 1# and 2# are 1.92
346
and 1.85 respectively and these two shales are thermally matured and located in the peak
347
gas window.
348 349
(2) The mean activation energy of shale 1 # and 2# are 235, 000 kJ/kmol and 205,600 kJ/kmol, respectively. It was easier for shale 2# to lose organic matters when it was heated up.
350
(3) The TC of shale 1# and shale 2# are 1.39 and 1.54 KJ/(m2·s·K) respectively and shale 1#
351
has higher porosity than that of shale 2#. Moreover, shale 1# (with higher Ro) has larger
352
specific surface area and greater adsorption potential in narrow pores, and higher methanol
353
adsorption capacity.
354
(4) When air, CO2 and helium were employed as purging gas to remove the organic matter
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
355
and to increase their permeability of the two samples, both samples had the same weight
356
loss behaviors. It was found the weight loss rate peaks occurred at temperature between
357
330 oC and 500 oC due to the organic matter decomposition and cracking. It was easier for
358
the samples to lose weight when helium was used as purge gas since helium has higher
359
thermal conductivity, followed by air and then CO2.
360
(5) There is no significant departure between the weight loss rate curves of CO2 and air.
361
Simply using air as oxidizer to burn the organic matters of shale rocks may not be an
362
effective method to improve the permeability. Higher heating rate could promote the
363
weight loss rate.
364
Acknowledgements
365
The authors wish to acknowledge the financial support by “National Natural Science
366
Foundation of China-41602169”
367 368
References
369
[1]
S. Gai, H. Liu, S. He, S. Mo, S. Chen, R. Liu, et al., "Shale reservoir characteristics
370
and exploration potential in the target: A case study in the Longmaxi Formation from
371
the southern Sichuan Basin of China," Journal of Natural Gas Science and
372
Engineering, vol. 31, pp. 86-97, 2016.
373
[2]
Shale," Working Document of the NPC Global Oil and Gas Study, 2007.
374 375
K. Perry and J. Lee, "Unconventional Gas Reservoirs-Tight Gas, Coal Seams, and
[3]
Ministry of Land and Resources of the People's Republic of China (MLR), " The
376
Nation Survey and Evaluation of Shale Gas Resource and Favorable Area Selection,"
377
2012.
378
[4]
G. Chapiro and J. Bruining, "Combustion enhance recovery of shale gas," Journal of
ACS Paragon Plus Environment
Page 20 of 23
Page 21 of 23
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
Petroleum Science and Engineering, vol. 127, pp. 179-189, 2015.
379 380
[5]
M. Sun, B. Yu, Q. Hu, S. Chen, W. Xia, and R. Ye, "Nanoscale pore characteristics of
381
the Lower Cambrian Niutitang Formation Shale: A case study from Well Yuke #1 in
382
the Southeast of Chongqing, China," International Journal of Coal Geology, vol.
383
154–155, pp. 16-29, 2016.
384
[6]
F. Yang, Z. Ning, R. Zhang, H. Zhao, and B. M. Krooss, "Investigations on the
385
methane sorption capacity of marine shales from Sichuan Basin, China," International
386
Journal of Coal Geology, vol. 146, pp. 104-117, 2015.
387
[7]
D. J. K. Ross and R. Marc Bustin, "The importance of shale composition and pore
388
structure upon gas storage potential of shale gas reservoirs," Marine and Petroleum
389
Geology, vol. 26, pp. 916-927, 2009.
390
[8]
X. Zhang, C. , D, F. Deimbacher, M. Crick, and A. Harikesavanallur, "Sensitivity
391
studies of horizontal wells with hydraulic fractures in shale gas reservoirs,"
392
International Petroleum Technology Conference, 2009.
393
[9]
A. K. M. Jamaluddin, D. B. Bermion, F. B. Thomas, and T. Y. Ma, "Application of
394
heattreatment to enhance permeability in tight gas reservoirs," Journal of Canadian
395
Petroleum Technology vol. 11, pp. 98-01, 2000.
396
[10]
H. Wang, R. Rezaee, and A. Saeedi, "Preliminary study of improving reservoir quality
397
of tight gas sands in the near wellbore region by microwave heating," Journal of
398
Natural Gas Science and Engineering, vol. 32, pp. 395–406, 2016.
399 400
[11]
I. Gąsior and A. Przelaskowska, "Estimating Thermal Conductivity from Core and Well Log Data," Acta Geophysica, vol. 62, pp. 785-801, 2014.
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
401
[12]
in the Northeast German Basin," Chemie derErde,, vol. 70, pp. 13–22, 2010.
402 403
S. Fuchs and A. Forster, "Rock thermal conductivity of Mesozoic geothermal aquifers
[13]
Y. Zheng, H. Li, and Z. Gong, "Geothermal study at the Wenchuan earthquake Fault
404
Scientific Drilling project-hole 1 (WFSD-1): Borehole temperature, thermal
405
conductivity, and well log data," Journal of Asian Earth Sciences, vol. 117, pp. 23-32,
406
2016.
407
[14]
P. Y. Gornov, "Relationship of the thermal conductivity of rocks in the Komsomol’sk
408
ore district (Khabarovsk Territory) with minerageny and metasomatism," Russian
409
Geology and Geophysics, vol. 56, pp. 493-499, 2015.
410
[15]
measurements," Tectonophysics, vol. 626, pp. 137-143, 2014.
411 412
P. Nagaraju and S. Roy, "Effect of water saturation on rock thermal conductivity
[16]
Y. Popov, V. Teatychnyi, R. Romushkevich, D. Korobkov, and J. Pohl, "Interrelations
413
between thermal conductivity and other physical properties of rocks: experimental
414
data," Pure appl.geophys, vol. 160, pp. 1137-1161, 2003.
415
[17]
heterogeneities," SPE J, vol. 17, pp. 1002–1011, 2012.
416 417
[18]
[19]
422
F. Hao, H. Zou, and Y. Lu, "Mechanisms of shale gas storage: Implications for shale gas exploration in China," AAPG Bulletin, vol. 97, pp. 1325-1346, 2013.
420 421
E.Fathi and I.Y.Akkutlu, "Lattice Boltzmann method for simulation o fshale gas transport in kerogen," SPE J, vol. 18, pp. 27-37, 2012.
418 419
I. Y. Akkutlu and E. Fathi, "Multiscale gas transport in shales with loca lkerogen
[20]
M. Gasparik, Y. Gensterblum, A. Ghanizadeh, P. Weniger, and B. M. Krooss, "High-Pressure/High-Temperature Methane-Sorption Measurements on Carbonaceous
ACS Paragon Plus Environment
Page 22 of 23
Page 23 of 23
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
423
Shales by the Manometric Method: Experimental and Data-Evaluation Considerations
424
for Improved Accuracy," SPE Journal, vol. 20, pp. 790 - 809, 2015.
425
[21]
J. Am. Chem, vol. 40, pp. 1361-1403, 1918.
426 427
I. Langmuir, "The adsorption of gases on plane surfaces of glass, mica and platinum,"
[22]
M. O. J. Azzam, Z. Al-Ghazawi, and A. Al-Otoom, "Incorporation of Jordanian oil
428
shale in hot mix asphalt," Journal of Cleaner Production vol. 112, pp. 2259-2277,
429
2016.
430
[23]
national laboratory report vol. ORNL/TM-10499, 1987.
431 432
T.M.Gilliam and I.L.Morgan, "Shale : measurement of thermal properties " Oak ridge
[24]
A. Hartmann, V. Rath, and C. Clauser, "Thermal conductivity from core and well log
433
data," International Journal of Rock Mechanics & Mining Sciences, vol. 42, pp.
434
1042–1055, 2005.
435
[25]
D. M. Jarvie, R. J. Hill, T. E. Ruble, and R. M. Pollastro, "Unconventional shale-gas
436
systems: The Mississippian Barnett Shale of north-central Texas as one model for
437
thermogenic shale-gas assessment," AAPG Bulletin, vol. 91, pp. 475-499, 2007.
438
[26]
J. F. Yan, Y. P. Men, Y. Y. Sun, Q. Yu, W. Liu, H. Q. Zhang, et al., "Geochemical and
439
geological characteristics of the Lower Cambrian shales in the middle–upper Yangtze
440
area of South China and their implication for the shale gas exploration," Marine and
441
Petroleum Geology, vol. 70, pp. 1-13, 2016.
442
[27]
L. Pan, F. Dai, G. Li, and S. Liu, "A TGA/DTA-MS investigation to the influence of
443
process conditions on the pyrolysis of Jimsar oil shale," Energy, vol. 86, pp. 749-757,
444
2015.
ACS Paragon Plus Environment