To better understand how supercritical carbon dioxide (CO2) enhances shale gas production, it is necessary to study the interaction of supercritical CO2 with shale and its impact on shale microstructure. The different mechanisms by which supercritical CO2 changes the shale pore structure were studied by X-ray diffraction analyses, scanning electron microscopy (SEM), nuclear magnetic resonance spectroscopy, and low-pressure nitrogen gas adsorption tests on shale samples before and after treatment with different pressures and gases (CO2 and Ar). The results showed that after treatment with CO2, the mineral content of shale changed significantly, and in particular, the proportions of calcite and dolomite decreased. The mineral content of shale changed the most after treatment with supercritical CO2, and the microscopic pores were most observable by SEM. In a gaseous CO2 environment, the effect of CO2 adsorption on shale pores is greater than the effects of gas pressure and dissolution reactions. However, in a supercritical CO2 environment, the changes in shale pore structures are mainly controlled by extraction and dissolution reactions. When shale is exposed to supercritical CO2, the fractal dimensions of adsorption pores and seepage pores decrease, indicating that the specific surface area and roughness of adsorption pores decrease. This implies that the adsorption capacity decreases, and that the complexity of the seepage pores declines, which is conducive for gas migration.
To better understand how supercritical carbon dioxide (CO2) enhances shale gas production, it is necessary to study the interaction of supercritical CO2 with shale and its impact on shale microstructure. The different mechanisms by which supercritical CO2 changes the shale pore structure were studied by X-ray diffraction analyses, scanning electron microscopy (SEM), nuclear magnetic resonance spectroscopy, and low-pressure nitrogengas adsorption tests on shale samples before and after treatment with different pressures and gases (CO2 and Ar). The results showed that after treatment with CO2, the mineral content of shale changed significantly, and in particular, the proportions of calcite and dolomite decreased. The mineral content of shale changed the most after treatment with supercritical CO2, and the microscopic pores were most observable by SEM. In a gaseous CO2 environment, the effect of CO2 adsorption on shale pores is greater than the effects of gas pressure and dissolution reactions. However, in a supercritical CO2 environment, the changes in shale pore structures are mainly controlled by extraction and dissolution reactions. When shale is exposed to supercritical CO2, the fractal dimensions of adsorption pores and seepage pores decrease, indicating that the specific surface area and roughness of adsorption pores decrease. This implies that the adsorption capacity decreases, and that the complexity of the seepage pores declines, which is conducive for gas migration.
Shale gas reservoirs contain
spontaneously generated natural gas
stored within shale rocks of low porosity and low permeability,[1−3] where methane (CH4) exists mainly as free gas and adsorbed
gas.[4,5] Horizontal well fracturing is currently
the main technique used for shale gas production.[6−9] However, because of the very high
water consumption involved in this process,[10−12] which is typically
in the range of 15,000–30,000 tons of water per shale gas well,[13] its application is severely limited in regions
with water scarcity.[8,14] As an alternative, supercritical
CO2 can be used as a new anhydrous fracturing fluid to
extract shale gas.[15−21] It has the characteristics of a low-viscosity gas and a high-density
liquid, with superior fluidity, permeability, and transmissivity.[21] Further, CO2 is more easily adsorbed
than CH4[22−25] by shale rock, which is not only a source of CH4 but
also a gas reservoir. Studies have shown that using supercritical
CO2 to extract shale gas can not only improve the recovery
rate of shale gas but also effectively store CO2 underground,
which alleviates the greenhouse effect.[26−33]When CO2 is injected into a shale gas reservoir,
shale
is exposed to supercritical CO2 at high temperature and
pressure. On the one hand, this causes supercritical CO2 to react with carbonates and clay minerals within the reservoir,[34−37] resulting in changes in mineral contents; on the other hand, a large
amount of injected CO2 increases the pore pressure and
changes the pore structure of shale.[38,39] Microscopic
pores adsorb gas and are channels for gas migration; thus, the study
of the effect of supercritical CO2 on shale microstructure
is of much significance for the efficient production of shale gas
and CO2 storage. At present, several test methods are used
to analyze the interaction between supercritical CO2 and
the shale microstructure, such as X-ray diffraction (XRD), scanning
electron microscopy (SEM), nuclear magnetic resonance (NMR), and low-pressure
nitrogengas adsorption (N2GA).[40−43] Some studies have shown that
supercritical CO2 can extract water molecules from minerals
to form carbonic acid and dissolve carbonate minerals.[44] Lyu et al.[45,46] found that
new pores appeared on the surfaces of shale slices after being saturated
with sub-/super-critical CO2, and an increase in carbon
content confirmed a chemical reaction between CO2 and shale.
Ao et al.[47] found that supercritical CO2 causes strain because of swelling and that high CO2 pressure causes shale deformation; however, deformation also occurs
at low pressure, mainly because of CO2 adsorption. Yin
et al.[48] observed that after treatment
with supercritical CO2, the proportions of clay minerals,
calcite, and dolomite in shale decreased, and the primary macropores
and microcracks in shale were narrowed because of swelling induced
by CO2 adsorption. Lu et al.[38] found that after CO2 saturation, shale porosity and volume
of macropores increased, but the volume of micropores and mesopores
decreased, and that the effect of gaseous CO2 on the pore
structure of shale was weaker than that of supercritical CO2. Jiang et al.[49] noted that original pores
and pre-existing fractures in shale could be eroded because of the
effect of dissolution by supercritical CO2, and new pores
could form. Zhou et al.[50] remarked that
dissolution due to supercritical CO2 led to a reduction
in the number of shale micropores, and that the effect of swelling
transformed macropores into mesopores; also, supercritical CO2 could decrease the surface roughness of shale pores and the
complexity of pore structures.Although several studies have
been conducted on the effect of supercritical
CO2 treatment on shale microstructures, the factors that
affect these changes differ and have not been adequately studied.
In addition to differences in shale specimens and experimental conditions,
the mechanisms of microstructure changes are important and have not
yet been well-understood. For example, it is unclear whether CO2 pressure or mineral dissolution has a greater effect on porosity.
To explore the different mechanisms by which supercritical CO2 changes shale microscopic structure, several methods including
XRD, SEM, NMR, N2GA, and fractal theory were used in this
study to determine the effects of different gas and pressure conditions
on the shale microstructure. The results and significance for improving
shale gas recovery are discussed in this paper.
Methodology
Specimen Preparation
Shale for this
study was obtained from the Fuling area of the Sichuan Basin in China,
which is currently the largest shale gas producing area in China,
and the shale has an average total organic carbon content of 3.47%
and a vitrinite reflectance (R0) of 2.56%.[48,51] The shale was processed into standard cylindrical specimens with
a diameter of 50 mm and a length of 25 mm (Figure ). The parallelism of the end faces of each
cylindrical specimen was not greater than 0.01 mm, and the vertical
deviation was not greater than 0.05°. To eliminate experimental
errors caused by differences among the specimens, an NMR analysis
was conducted to select specimens with the closest pore characteristics
and thus maximize the reliability of the test results (Figure ). To meet different experimental
requirements, some select shale samples were crushed, and the powder
was mixed evenly. Powder finer than 200 mesh was used for XRD, powder
in range of 20–60 mesh was used for N2GA tests,
and cuboid samples of size less than 8 mm × 8 mm × 3 mm
were used for SEM tests. All processed shale samples were wrapped
and sealed with a plastic wrap to prevent moisture and contamination.
Figure 1
Shale
samples: (a) φ 50 mm × 25 mm cylindrical specimens;
(b) powder samples; and (c) cuboid samples.
Figure 2
Initial
transverse relaxation times T2 of shale
specimens.
Shale
samples: (a) φ 50 mm × 25 mm cylindrical specimens;
(b) powder samples; and (c) cuboid samples.Initial
transverse relaxation times T2 of shale
specimens.
Experimental
Procedure
Experiments
with the shale samples were conducted in a high-pressure reactor system
designed at our facility (Figure a). It consists of a high-pressure vessel with a maximum
working pressure of 32 MPa, a Teledyne ISCO 260D syringe pump (Teledyne,
Thousand Oaks, CA, USA) with a maximum working pressure of 51.7 MPa
and a flow rate range of 0.001–107 mL/min, and a thermostatic
water bath with a fluctuation of less than 0.1 °C. The experimental
temperature was set at 60 °C to simulate real reservoir environment,
and the exposure time was set to be 10 days, as per the time required
for the interaction between shale and CO2 to reach equilibrium.[48] Argon (Ar) gas has also been used in these experiments.
Being an inert gas, Ar does not react with shale and can thus be used
to isolate the effect of pressure from a gas on the pores in shale,
as opposed to the effects of CO2, which not only include
pressure from the gas, but also adsorption, dissolution, extraction,
and other factors. To study the mechanisms by which supercritical
CO2 changes the shale pore structure, the exposure conditions
(Table ) of shale
to gas treatments were set as follows: untreated sample (reference
group), 4 MPa Ar, 16 MPa Ar, 4 MPa CO2 (gaseous state),
and 16 MPa CO2 (supercritical state). Before each experiment,
the shale sample chamber was subjected to vacuum for at least 2 h
to avoid the experimental error caused by air.
Experimental Scheme of Shale Exposed
to Different Gas Conditions
specimen
groups
gas
pressure
(MPa)
temperature
(°C)
time (d)
state
A
untreated
B
Ar
4
60
10
gaseous
C
Ar
16
gaseous
D
CO2
4
gaseous
E
CO2
16
supercritical
Experiment apparatus:
(a) high-pressure reactor system; (b) “JSM6610LV”
scanning electron microscope; (c) “MacroMR12-150H-I”
NMR core analysis system; and (d) Micromeritics ASAP 2020 system.An “X-Max20/W500X”
X-ray diffractometer (Co Kα
radiation, 40 kV, 40 mA) was used for the XRD analysis of the 200
mesh shale powder to determine the change in the mineral content of
shale before and after exposure. The micromorphology of shale was
observed using a “JSM6610LV” scanning electron microscope
(JEOL, Japan). The aperture distribution of shale was tested by a
“MacroMR12-150H-I” low-field NMR core analysis system
(Niumag Analytical Instrument Corp., China). The NMR analysis is based
on the principle of using the hydrogen-containing fluid in pores to
determine the pore structure of rocks.[52] Therefore, it was necessary to fully saturate the shale specimens
with water before performing an NMR analysis. The N2 adsorption–desorption
isotherms were obtained at a temperature of −196 °C at
a relative pressure (p/p0) range of 0.01–0.99 using a Micromeritics ASAP 2020 system.
Results and Discussion
XRD and
SEM
Table and Figure show
the results for the mineral content in shale
under different treatment conditions. It can be seen that the shale
was mainly composed of quartz, dolomite, and calcite. The mineral
content of shale did not change appreciably because of treatment with
Ar, but did change significantly after treatment with CO2. The change in the mineral content of shale after treatment with
CO2 is likely due to the chemical reactions of minerals
in the CO2-water system (eqs and 2). The dissolution of calcite
(CaCO3) in acid solution occurs before that of dolomite
(CaMg(CO3)2) (eqs and 4), while quartz (SiO2) is stable and remains almost undissolved. Therefore, it
is believed that the change in the proportion of calcite indicates
the degree of dissolution, and the change in the proportion of quartz
indicates the degree of the overall chemical reaction. The calcite
content is the lowest, and the quartz content is the highest after
treatment with 16 MPa CO2, indicating that when shale is
exposed to supercritical CO2, the dissolution of calcite
and the overall chemical reaction between shale minerals and the CO2–water system are the strongest compared to other conditions.
This is because supercritical CO2 can extract bound water
from clay minerals (TCCM), which increases the amount of CO2 in aqueous solution. The pH of the acid solution decreases, that
is, the acidity increases, with an increase in the pressure of CO2.[53] Compared with a 4 MPa CO2 environment, the 16 MPa CO2 environment has a
higher acidity, which results in a sudden decrease in calcite content
and a sudden increase in quartz content.
Table 2
XRD Resultsa
mineral content (%)
treatment
conditions
quartz
dolomite
calcite
TCCM
feldspar
pyrite
hematite
untreated
42.7
30
16.2
9.3
0.8
0.5
0.5
4 MPa Ar
42.6
30.1
16.2
9.2
0.9
0.6
0.4
16 MPa Ar
42.7
29.8
16.3
9.3
0.9
0.5
0.5
4 MPa CO2
43.3
30.2
15.1
9.8
0.8
0.4
0.4
16 MPa CO2
45.5
30.1
12.4
10.4
0.6
0.5
0.5
TCCM represents
clay minerals such
as kaolinite, illite, and montmorillonite.
Figure 4
Mineral content of shale
under different treatment conditions.
Mineral content of shale
under different treatment conditions.TCCM represents
clay minerals such
as kaolinite, illite, and montmorillonite.The microscopic morphologies (Figure ) of shale samples under different treatment
conditions show that compared with untreated and other treatment conditions,
the pores on the shale surface seem to develop the most because of
the dissolution of minerals when shale is exposed to a 16 MPa CO2 environment.
Figure 5
1000× magnification of the microscopic morphology
of different
shale surfaces.
1000× magnification of the microscopic morphology
of different
shale surfaces.
NMR Analysis
of Aperture Distribution
The aperture distribution of shale
specimens was obtained from the
distribution of the transverse relaxation time T2.[54,55] The pore size has a positive correlation
with the transverse relaxation time. The relationship between pore
size and transverse relaxation time can be expressed by eq as follows[56,57]where T2 is the
transverse relaxation time, ms; Fs represents
the shape factor of the pore; ρ is the relaxation strength of
the transverse surface, nm/ms; r is the pore size,
nm. For this study, Fs = 2 and ρ
= 10 nm/ms.[38,43,58]The aperture distribution of shale before and after exposure
is shown in Figure . Before the tests were conducted, specimens with almost identical T2 curves were identified and selected for testing.
Hence, the T2 curves for untreated shale
in Figure are identical.
It can be seen that the aperture distributions of shale samples show
a bimodal distribution, with two peaks located in the pore size ranges
of 1–250 nm (main peak) and 250–2000 nm (secondary peak).
After treatment with 4 MPa Ar, the aperture distribution curve shows
a slight shift to the left. Because Ar does not react with shale,
the overall decrease in pore size for this condition is likely caused
by the compression of shale pores because of the pressure of the gas.
After treatment with 16 MPa Ar, the decrease in pore size corresponding
to the main peak is more apparent, indicating that the increase in
gas pressure causes a greater compression of shale pores. Also, some
microcracks occur in shale because of the higher pressure of the Argas at 16 MPa; hence, the pore component corresponding to the secondary
peak increases. It has been shown that when CO2 is adsorbed
on a shale surface, it causes an expansion and deformation of shale
and a reduction in pore size.[59−61] It can also be seen from Figure c that after treatment
with 4 MPa CO2, the main peak decreases, while the secondary
peak increases because of the dissolution of minerals such as calcite.
In addition to adsorption and the dissolution reactions with shale
minerals, supercritical CO2 also has the unique ability
to extract organic matter, resulting in an increase in pore size and
forming an acidic environment with higher solubility. Compared with
other treatment conditions, when shale is exposed to a 16 MPa CO2 environment, the magnitudes of both the main peak and the
secondary peak increase significantly, which indicates that the extraction
reaction of supercritical CO2 has a greater effect on shale
pore size than other factors.
Figure 6
Aperture distributions of shale under different
treatment conditions:
(a) 4 MPa Ar; (b) 16 MPa Ar; (c) 4 MPa CO2; and (d) 16
MPa CO2.
Aperture distributions of shale under different
treatment conditions:
(a) 4 MPa Ar; (b) 16 MPa Ar; (c) 4 MPa CO2; and (d) 16
MPa CO2.
Porosity
and Average Pore Size
To
further reveal the effect of different mechanisms on shale pores,
a cumulative porosity diagram (Figure ) was plotted based on NMR data. As seen in this figure,
the porosity of untreated shale was 3.46%, and after the treatments
with 4 MPa Ar, 16 MPa Ar, and 4 MPa CO2, the porosity had
decreased in all cases, and the increments were −0.06, −0.15,
and −0.25%, respectively. However, after being exposed to 16
MPa CO2, the porosity of shale increased from 3.46 to 3.63%,
which represents an increase of 0.17%. Combining the data of Figures b and 7, it can be inferred that although a high gas pressure induces
microcracks in shale, the porosity of shale decreases, indicating
that the impact of gas pressure on shale pores is mainly compressive,
regardless of the magnitude of the pressure. According to Table and Figure , it is seen that after treatment
with 4 MPa CO2, the gas pressure causes a reduction in
shale porosity of 0.06%, and the combined effect of CO2 adsorption and mineral dissolution causes the porosity to decrease
by 0.19%. In general, the effect of CO2 adsorption on shale
porosity is opposite to that of mineral dissolution, that is, adsorption-induced
expansion reduces porosity, and dissolution increases porosity. Therefore,
it can be concluded that in a gaseous CO2 environment,
the adsorption of CO2 has a greater effect on shale pores
than gas pressure and dissolution reactions. By comparing the change
in shale porosity after treatments with 16 MPa Ar and 16 MPa CO2, it is found that after treatment with 16 MPa Ar, the shale
porosity decreases by 0.15%, while after treatment with 16 MPa CO2, the shale porosity increases by 0.17%. The increase in porosity
in the latter case is because the effects of the extraction and dissolution
reactions of supercritical CO2 can not only overcome the
effects of compression caused by gas pressure but also the compressive
effects of CO2 adsorption; this indicates that after treatment
with supercritical CO2, the change in shale porosity is
mainly controlled by extraction and dissolution reactions. Consistent
with the above effects on shale porosity, the average pore size of
shale decreases after treatment with 4 MPa Ar, 16 MPa Ar, and 4 MPa
CO2, but increases after treatment with 16 MPa CO2 (Figure ).
Figure 7
Cumulative
porosity vs T2.
Table 3
Porosity and the Factors Affecting
Porosity
treatment
conditions
porosity/%
increment/%
factors affecting
porosity
untreated
3.46
4 MPa Ar
3.40
–0.06
low gas pressure
16 MPa Ar
3.31
–0.15
high gas pressure
4 MPa CO2
3.21
–0.25
low gas pressure + adsorption + dissolution
16 MPa CO2
3.63
0.17
high gas pressure + adsorption + dissolution + extraction
Figure 8
Schematic
diagram of shale porosity and the factors affecting porosity.
Figure 9
Average pore size of shale specimens.
Cumulative
porosity vs T2.Schematic
diagram of shale porosity and the factors affecting porosity.Average pore size of shale specimens.
Fractal Dimensions of T2 Spectra
According to the International
Union of
Pure and Applied Chemistry (IUPAC) classification of pore sizes,[62] pores of sizes 0–2 nm are defined as
micropores, pores of sizes 2–50 nm are defined as mesopores,
and pores larger than 50 nm are defined as macropores. Adsorption
in rocks mainly occurs in micropores and mesopores, while macropores
are the main channels for gas migration. Therefore, according to the T2 curves obtained from NMR tests, T2 = 2.5 ms (corresponding to a pore size of 50 nm) is
chosen as the demarcation point, and the fractal dimensions of shale
adsorption pores and seepage pores are calculated using eq .[63−66]Figure and Table present the results of the calculations of fractal
dimensions. D obtained
from adsorption pores represents the fractal dimension of the pore
area, which reflects the roughness and heterogeneity of the surface
of shale adsorption pores, and its value is typically between 1 and
2. D obtained from
seepage pores is the fractal dimension of pore volume, which reflects
the complexity of the flow channel of shale seepage pores, and its
value is typically between 2 and 3. It can be seen from Table that both adsorption pores
and seepage pores show a good fitting effect and that the fitting
coefficient of adsorption pores is higher than that of seepage pores,
indicating that adsorption pores have more fractal characteristics
than seepage pores. Figure shows the variation of fractal dimensions of shale pores
for different treatment conditions. For adsorption pores, D increases after treatment
with 4 MPa Ar, 16 MPa Ar, and 4 MPa CO2, and the maximum
value appears for the 16 MPa Ar environment, while D decreases only in the case of treatment
with 16 MPa CO2, indicating that supercritical CO2 decreases the specific surface area and roughness of adsorption
pores, which may weaken the adsorption capacity of shale. For seepage
pores, there are no obvious changes in D after treatment with 4 MPa Ar, 16 MPa Ar, and 4
MPa CO2. However, after treatment with 16 MPa CO2, D decreases significantly,
indicating that in a supercritical CO2 environment, the
complexity of shale seepage pores declines, which is conducive for
gas migration.where D represents the fractal
dimension of pores; Sv represents the
pore volume component occupied in the wetting phase; T2 is the relaxation time, ms; T2max represents the maximum relaxation time constant, corresponding to
the capillary pressure. Besides the NMR method, it is worth pointing
out that fractal theory has been effectively applied to natural porous
media from different perspectives. Cai and Yu[67] introduced fractal to modify the classical Lucas–Washburn
equation, and the proposed fractal time exponent model presented a
theoretical insight to the effect of tortuosity on capillary flow.
Xia et al.[68] employed three fractal structural
parameters, fractal dimension, lacunarity and succolarity, to characterize
scale-invariant complexity, heterogeneity, and anisotropy of rock
microstructures, respectively.
Figure 10
Plots of ln(Sv) vs ln(T2) from NMR testing data under
different treatment conditions:
(a) untreated; (b) 4 MPa Ar; (c) 16 MPa Ar; (d) 4 MPa CO2; and (e) 16 MPa CO2.
Table 4
Fractal Dimension of Shale Samples
from NMRa
region 1 (T2 < 2.5 ms)
region 2 (2.5 ms ≤ T2 < 100 ms)
treatment
conditions
fitting equation
DN1
R2
fitting equation
DN2
R2
untreated
y = 1.797x – 1.902
1.203
0.89555
y = 0.056x – 0.215
2.944
0.67133
4 MPa Ar
y = 1.793x – 0.981
1.207
0.89045
y = 0.046x – 0.178
2.954
0.70342
16 MPa Ar
y = 1.718x – 0.905
1.282
0.87899
y = 0.048x – 2.952
2.952
0.85493
4 MPa CO2
y = 1.755x – 1.099
1.245
0.89046
y = 0.056x – 0.220
2.944
0.74793
16 MPa CO2
y = 1.845x – 1.537
1.155
0.90366
y = 0.091x – 0.353
2.909
0.681
T2 is
the transverse relaxation time obtained from the NMR test.
Figure 11
Variation
of fractal dimensions of shale pores.
Plots of ln(Sv) vs ln(T2) from NMR testing data under
different treatment conditions:
(a) untreated; (b) 4 MPa Ar; (c) 16 MPa Ar; (d) 4 MPa CO2; and (e) 16 MPa CO2.Variation
of fractal dimensions of shale pores.T2 is
the transverse relaxation time obtained from the NMR test.
N2 Adsorption–Desorption
Isotherms
The N2 adsorption–desorption
isotherms of shale samples under different treatment conditions are
shown in Figure , where the shapes of the isotherms are found to be similar. When
the relative pressure p/p0 is in the range of p/p0 = 0–0.45, the adsorption isotherms rise slowly with relative
pressure, and the main type of adsorption is the monolayer adsorption
of N2, or microporous filling. When p/p0 reaches 0.45, the monolayer adsorption of
N2 is considered complete. When p/p0 exceeds 0.45, the adsorption isotherms continue
to rise with relative pressure, the slope increases gradually, and
the adsorption transforms from monolayer adsorption to multilayer
adsorption. Also, when p/p0 is more than 0.45, the isotherms of desorption show hysteresis loops
because of capillary condensation. Also, compared with other treatment
conditions, the volume of adsorption in shale samples, that is, the
adsorption capacity, significantly decreases after treatment with
16 MPa CO2. Figure shows the specific surface area of shale measured
by N2 adsorption. It can be seen that the specific surface
area of shale decreases significantly after supercritical CO2 treatment.
Figure 12
Adsorption and desorption curves of shale specimens under
different
treatment conditions: (a) 4 MPa Ar; (b) 16 MPa Ar; (c) 4 MPa CO2; and (d) 16 MPa CO2.
Figure 13
Specific
surface area of shale specimens.
Adsorption and desorption curves of shale specimens under
different
treatment conditions: (a) 4 MPa Ar; (b) 16 MPa Ar; (c) 4 MPa CO2; and (d) 16 MPa CO2.Specific
surface area of shale specimens.
Conclusions
To explore the different mechanisms
by which supercritical CO2 changes the shale pore structure,
this study uses shale specimens
from the Sichuan Basin, China, and utilizes several methods such as
XRD, SEM, NMR, N2GA, and fractal theory to analyze and
compare the changes in shale pore structures under different gases
and pressures. An analysis of XRD results showed that almost no changes
in shale mineral content occurred after treatment with Ar, while the
mineral content changed significantly after treatment with CO2. The mineral content changed the most, particularly in the
proportions of calcite and dolomite in shale, which decreased, after
exposure to supercritical CO2; these conditions also resulted
in the highest number of microscopic pores, as observed by SEM. The
NMR test results revealed that gas pressure caused compression of
shale pores. In a gaseous CO2 environment, the effect of
CO2 adsorption on shale pores was found to be greater than
the effects of gas pressure and dissolution reactions. In a supercritical
CO2 environment, changes in the structures of shale pores
were mainly controlled by the extraction and dissolution reactions
of supercritical CO2. The results of N2GA tests
and fractal dimensions of T2 spectra showed that adsorption
pores have more fractal characteristics than seepage pores. After
treatment with 16 MPa CO2, the fractal dimensions of the
adsorption pores and seepage pores both decreased, indicating that
when shale is exposed to supercritical CO2, the specific
surface area and roughness of the adsorption pores decrease, the adsorption
capacity is weakened, and the complexity of the seepage pores declines,
which is conducive for gas migration. Therefore, when supercritical
CO2 is used to extract shale gas, it reduces the adsorption
capacity of shale for CH4 and promotes the conversion of
adsorbed gas to free gas, thereby improving shale gas production.