Next Article in Journal
Optimal Operation of Network-Connected Combined Heat and Powers for Customer Profit Maximization
Next Article in Special Issue
A Review of CO2-Enhanced Oil Recovery with a Simulated Sensitivity Analysis
Previous Article in Journal
High Stable, Transparent and Conductive ZnO/Ag/ZnO Nanofilm Electrodes on Rigid/Flexible Substrates
Previous Article in Special Issue
Cathode Assessment for Maximizing Current Generation in Microbial Fuel Cells Utilizing Bioethanol Effluent as Substrate
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Effect of Coal Rank on Various Fluid Saturations Creating Mechanical Property Alterations Using Australian Coals

by
Mandadige Samintha Anne Perera
*,
Ashani Savinda Ranathunga
and
Pathegama Gamage Ranjith
Deep Earth Energy Laboratory, Department of Civil Engineering, Monash University, Building 60, Melbourne, Victoria 3800, Australia
*
Author to whom correspondence should be addressed.
Energies 2016, 9(6), 440; https://doi.org/10.3390/en9060440
Submission received: 13 April 2016 / Revised: 26 May 2016 / Accepted: 1 June 2016 / Published: 8 June 2016
(This article belongs to the Collection Bioenergy and Biofuel)

Abstract

:
During CO2 sequestration in deep coal seams, the coal mass may be subjected to various fluid (CO2, N2, etc.) saturations. Therefore, in order to maintain the long-term integrity of the process, it is necessary to identify the mechanical responses of preferable coal seams for various fluid saturations. To date, many studies have focused on the CO2 saturation effect on coal mass strength and less consideration has been given to the influence of other saturation mediums. Hence, this study aims to investigate coal’s mechanical responses to water and N2 saturations compared to CO2 saturation and to determine the effect of coal-rank. A series of unconfined compressive strength (UCS) tests was conducted on Australian brown and black coal samples saturated with water and N2 at various saturation pressures. An advanced acoustic emission (AE) system was utilized to identify the changes in crack propagation behaviors under each condition. According to the results, both CO2 and water act similarly with coal by enhancing the ductile properties of the coal mass and this mechanical weakening is greater for high-rank coal. Conversely, N2 saturation slightly enhances coal strength and delays crack propagation in coal and this strength enhancement can be improved by increasing the N2 saturation pressure.

1. Introduction

The process of enhanced coal bed methane (ECBM) recovery is being implemented and tested as a viable option to store and reduce the amount of anthropogenic carbon dioxide (CO2) in the Earth’s atmosphere, as well as for the recovery of useful coal bed methane (CH4) gas [1,2,3,4,5,6,7]. Overall, the ECBM process involves introducing CO2 through injecting wells into deep coal seams and this CO2 then acts as a displacing gas, which allows the already adsorbed CH4 to be desorbed from the coal matrix. Finally, CH4 is obtained through a recovery well and used to produce energy in a cost-effective and environmentally friendly way.
However, according to previous studies [1,2,3,6,8,9,10,11,12], this CO2-ECBM process leads to CO2 adsorption-induced coal matrix alterations, which in turn affect its hydro-mechanical properties. Particularly in the geomechanical respect, the coal mass becomes weaker with the substitution of existing adsorbate CH4 with the highly chemically potential CO2 [13,14]. According to Perera et al. [15], Ranathunga et al. [16] and Vishal et al. [17], the inherent brittleness of the coal mass becomes ductile with the plasticization effect of coal with the adsorption of CO2, and this phenomena is higher for super-critical CO2 (beyond the critical temperature of CO2-31.8 °C and the critical pressure of CO2-7.38 MPa). Generally, potential CO2-ECBM reservoirs are located deep underground, where CO2 is in its super-critical state [2]. Hence, the strength reduction may be hazardous for the overall stability of coal reservoirs, mainly in regard to the cap rock’s stability [18]. Table 1 provides a summary of previous studies on the identification of the geomechanical responses of different coal types under various CO2 adsorption conditions. Those studies show that the coal mass is weakened by CO2 adsorption and the effect is relatively higher for super-critical CO2 for any type of coal. For instance, Australian brown coal shows 20.92% and 23.84% of unconfined compressive strength (UCS) and Young’s modulus reduction for sub-critical CO2 saturation at 6 MPa and 57.32% and 41.14% UCS and Young’s modulus reduction for super-critical CO2 saturation at 8 MPa respectively [16]. For Australian black coal, when the CO2 saturation pressure increased from 6 MPa (sub-critical) to 8 MPa (super-critical), the UCS reduction was increased from 56.67% to 77.58% and the Young’s modulus reduction was increased from 42.23% to 70.27% [15]. This is because the higher adsorption potential of super-critical CO2 results in greater coal matrix alterations, causing greater strength reductions in the coal structure.
Interestingly, although both low and high rank coal samples behave similarly under CO2 saturation, low rank coal exhibits a comparatively lower strength reduction compared to high rank coal (see Table 1). According to Table 1, the average reduction of UCS is around 29% for the tested Australian brown coal and that of the tested Australian black coal is around 61%. Further, the Young’s modulus of the tested Australian brown coal exhibits around 26% average reduction, while the tested Australian black coal shows an average reduction of around 47%. In addition, for 3 MPa CO2 saturation, the tested Australian brown coal shows a UCS reduction of 9.21% and Young’s modulus reduction of 20.18%, while the tested Indian black coal shows 17.6% and 26.2% reductions in UCS and Young’s modulus, respectively (see Table 1). The reason is the naturally existing well-developed cleat system in high rank coal that acts as a locus for CO2 movement, permitting a greater matrix alteration compared to low rank coal with a less-developed cleat system.
It is also important to study the geomechanical behavior of the coal mass under other saturation mediums such as water and nitrogen (N2). Moisture in a rock mass is known to affect the strength of rock by reducing its surface energy [19] and consequently softening the bond structure. Hence, it is vital to identify how different types of coals behave under the effect of moisture. In the case of N2 saturation, researchers [3,20,21,22,23] have found that N2 has the ability to recover CO2 adsorption-induced coal matrix alteration, which eventually enhances the hydraulic properties of the coal matrix. Perera, Ranjith and Peter [24] have investigated the behavior of N2 and CO2 saturation on low-rank brown coal and observed around 2% increase in strength and Young’s modulus for 3 MPa N2 saturation. This is quite a low pore pressure condition and it is important to see this effect under much greater pore pressure conditions for possible field application. Regarding the rank effect, although there have been some studies to date [16,25] on the effect of CO2 saturation on different ranks of coal, none of them has considered the rank-dependent mechanical behavior of coal mass under N2 saturation, particularly under high saturation pressure conditions. Therefore, it is interesting to investigate how coal mechanical property alterations vary under high N2 saturation conditions and the rank effect on them, which will in turn enable more reliable applications for field projects. This study therefore intends to fill this gap by determining the effect of water and N2 saturation on the strength of low rank coal (lignite) and high rank coal (bituminous). The main objective of the present study is to distinguish the effects of water and N2 saturation on the mechanical properties of different coal ranks.

2. Methodology

2.1. Samples Used for Testing

Brown coal (lignite) samples acquired from the Hazelwood mine in the Latrobe Valley, Victoria, Australia from approximately 50–75 m depth (from the ground level) were employed to represent low rank coal, while black coal (bituminous) samples collected from the Appin coal mine in the Southern Sydney basin, Australia from approximately 400 m depth (from the ground level) were utilized to represent high rank coal for this study. Both types of coal were obtained immediately after mining and therefore had been subjected to minimal environmental effects such as dusting, water evaporation or sunlight. The samples used for the present study were the same specimens obtained from the same coal blocks used by Perera, Ranjith and Viete [15] (black coal) and Ranathunga et al. [16] (brown coal) and the water content of the blocks was checked before coring new samples to ensure that the coal blocks were not subjected to any moisture loss. The physical properties of the samples used are shown in Table 2. Samples of 38 mm in diameter and 76 mm in height were used for testing purposes and the samples were maintained in a fog room wrapped in plastic wraps (after coring from the coal blocks) before being used for the saturations to preserve natural conditions. The detailed methodology adopted to prepare the samples is discussed in Ranathunga, Perera, Ranjith and Bui [16].

2.2. Samples Preparation for Testing

The procedures implemented for water and N2 saturations are explained in the following sections.

2.2.1. Water Saturation

Three coal samples from each rank were saturated in water for approximately three weeks to allow full water saturation. The samples were placed in vacuum chambers (Figure 1a) and the weight of the coal samples was recorded before placing them into the saturation chamber. The weight was then checked over time for around three weeks until the weight reached a steady state. The samples were then wrapped well with plastic wraps and stored in the fog room for another two weeks to allow an equal distribution of moisture throughout the sample before testing.

2.2.2. N2 Saturation

During the study by Perera, Ranjith and Viete [15], the black coal samples were saturated under two different N2 pressures (8 and 16 MPa) using a high pressure tri-axial test rig (see Figure 1b) to compare the observations of CO2 saturated samples. Unlike CO2, N2 is a comparatively inert gas, which does not cause any significant coal matrix re-arrangement through chemical interactions with the coal mass [23,26]. For this study, brown coal samples were saturated under three different saturation pressures (2, 6 and 8 MPa) using a similar procedure to that reported in Perera, Ranjith and Viete [15]. Further, black coal samples were saturated under two other different saturation pressures (2 and 6 MPa) additional to those used in the study of Perera, Ranjith and Viete [15] for comparison purposes. Here the samples were saturated under 35 °C temperature to provide similar conditions to those used for CO2 saturation in Ranathunga, Perera, Ranjith and Bui [16] and Perera, Ranjith and Viete [15]. It should be noted that upon the completion of each saturation, the pressure cell was depressurized gradually at a quite slow rate of around 0.02 MPa/min to avoid any possible damage to the coal mass caused by the sudden pressure release.

2.3. Experimental Procedure

The following sections summarize the experimental methodology adopted for the testing.

2.3.1. Unconfined Compressive Strength (UCS) Tests

A series of UCS tests was performed on the coal samples using the Shimadzu compression machine available in the Deep Earth Energy Research Laboratory (DEERL) at Monash University. A displacement rate of 0.1 mm/min [27] was applied for the uniaxial compressive tests of the coal samples and the corresponding load and displacement were recorded.

2.3.2. Acoustic Emission (AE) Tests

An advanced acoustic emission (AE) system was used to observe the fracture propagation patterns of the tested brown and black coal samples during the UCS testing. Two AE sensors attached at either side of the specimen were used to capture the acoustic counts during the load application. These AE data were used to characterize the crack propagation stages and to obtain the stress threshold values for each condition.

2.3.3. Scanning Electron Microscopy (SEM) Analysis

High-resolution SEM images were also taken of the coal samples under unsaturated, water-saturated, N2-saturated and CO2-saturated conditions. The scanning was carried out with 4.5 spot size under 15 kV voltage while maintaining a low vacuum mode using the FEI Quanta 3D FEG FIB machine located at the Monash Centre for Electron Microscopy (MCEM), thus providing a fixed resolution of 2 microns for the qualitative analysis of all images. The complete procedure adopted for SEM analysis is detailed in Ranathunga, Perera, Ranjith and Bui [16].

3. Experimental Results and Discussion

Axial stress-strains and AE responses were tested for brown and black coal samples under different fluid saturation conditions. The highest UCS values were used to represent the different test conditions for discussion purposes, as the variation of experimental values was minimal. In addition, SEM images were also incorporated to show the micro-structural changes in the coal matrix under different fluid saturations. The following sections discuss and compare how the different coal types behave under the saturation of various fluids.

3.1. Effect of Coal Rank on Water Saturation Effect on Geomechanical Properties in Coal

Figure 2 shows the variation of axial stress with axial strain for water-saturated brown and black coal samples. According to Figure 2 and Table 3, brown coal exhibits a UCS value of 2.04 MPa and a Young’s modulus value of 35.46 MPa after water saturation, which represent around a 14.64% reduction of UCS and a 16.21% reduction of Young’s modulus compared to the unsaturated brown coal samples. Black coal exhibits a UCS of 21.01 MPa and Young’s modulus of 2.24 GPa after water saturation (refer Table 3), which represents around 36.33% reduction in UCS and a 39.46% reduction in Young’s modulus compared to the unsaturated black coal samples. Both black and brown coal show a similar behavior for water saturation; there is a considerable reduction in their mechanical properties with water saturation. The major reason for this water saturation-induced strength reduction is the softening of the rock mass bond structure [19] and the ability of moisture inside the rock mass to decrease the surface energy [28]. Furthermore, moisture in a rock mass can cause its toughness to be increased [29], by enhancing the ductile behavior, resulting in a lower Young’s modulus.
Interestingly, compared to brown coal, black coal has around 2.5 times higher reduction in both UCS and Young’s modulus. This significant mechanical property weakening in black coal has also been observed by Vishal, Ranjith and Singh [17] for Indian black coal (around 25.5% UCS reduction and 37.8% Young’s modulus reduction upon water saturation). This is possibly due to the fact that black coal has more fractures and a well-developed cleat system that allow more intake of moisture into the coal mass. The water molecules can dissolve in the material and can be drawn to the tips of the fractures, causing more stress towards the fracture tips, resulting in their expansion [28]. Hence, black coal exhibits a higher strength reduction than brown coal, which has fewer fractures and under-developed cleats. These observations can be further confirmed by comparing the SEM images of unsaturated and water-saturated coal samples (see Table 4). Here, compared to unsaturated samples, both brown and black coals show altered micro structures after water saturation and these alterations are clearly greater in black coal.
Figure 3 compares the AE counts with axial stress for brown and black coals with and without water saturation. As shown in Figure 3, the unsaturated samples exhibit clear fracture propagation behavior with all the three main stages under load application compared to the water-saturated samples. A crack closure (CC) region can first be observed without any strain energy release. A stable crack propagation (SC) region can then be witnessed, at which crack propagation is initiated (crack initiation stress-σci), releasing strain energy linearly without damaging the sample. Unstable crack propagation (UC) can finally be seen, which starts at the crack damage point (σcd) and progresses until the sample fails (UCS) with an exponential increment in strain energy released.
However, in water-saturated coal samples, these three stages are not clearly visible. Brown coal (see Figure 3a) portrays only crack closure and then sample failure without any stable or unstable crack propagation. As discussed previously, moisture intake into the rock mass causes the fracture tips of the specimen to be weakened, which may result in failure without any crack propagation. However, stable and unstable crack propagation can be observed for water-saturated black coal before it undergoes failure. The reason may be the softer and weaker properties of brown coal compared to black coal that cause it to fail rapidly, with water saturation creating a softening effect.
After water saturation, the brown coal samples were observed to have a very soft and bulgy appearance compared to the water-saturated black coal samples. Further, the water-saturated brown coal had a bulging failure and black coal exhibited a failure along the major and minor cleats (see Table 4). This is possibly because, due to the well-developed cleat system in high rank black coal compared to brown coal, water molecules have more possibility to move through these cleat systems and weaken the coal mass along them in black coal. In the case of brown coal, which has only a poorly developed cleat system, water molecules slowly diffuse into the whole rock matrix, weakening the coal matrix. Black coal shows more rapid crack propagation after water saturation, probably because the weaker cleat system allows fractures to easily propagate through the system. For example, the crack initiation stress for the unsaturated sample is 26.7 MPa while it is 6.74 MPa for the water-saturated sample. Furthermore, the crack damage occurred at 30.5 MPa for the unsaturated sample and at 17.15 MPa for the water-saturated sample (see Figure 3b). In summary, water saturation causes a strength reduction in any coal regardless of rank. However, high rank coal exhibits a greater strength reduction than low rank coal with water saturation, mainly due to the mature fracture network, which easily attracts water molecules. In addition, water saturation causes a direct failure in low rank brown coal (without fracture propagation) compared to high rank coal, which exhibits more rapid fracture propagation after water saturation compared to its dry condition.

3.2. Rank Effect on N2 Saturation-Created Geomechanical Alterations in Coal

The effects of N2 saturation on brown and black coal’s mechanical properties were then investigated and the results are shown in Figure 4 and Table 3. According to Figure 4, unlike in water saturation, N2 saturation causes a slight increment in coal strength for both brown and black coal, and the strength gain is increased by increasing N2 saturation pressure. The reason may be the ability of N2 to push the existing moisture from the coal mass. This was evident by the calculated weight variation in the N2-saturated samples, which was reduced by around 5% to 19% during the saturation period. As mentioned in the previous section, moisture in a coal mass causes its structure to be weakened, and the removal of moisture from the rock mass should therefore cause a strength gain.
Further, according to Table 3, the Young’s modulus of both brown coal and black coal slightly increase after N2 saturation, and this is also related to the moisture removing potential of the N2 molecules. As described earlier, the existence of water causes the ductile properties of the coal mass to improve. Therefore, the removal of water should improve the brittle behavior, which is proven by the observed Young’s modulus increment in both brown and black coal after N2 saturation. Further, at higher N2 saturation pressures, the amount of N2 molecules that enter the coal mass is higher. Therefore, the removal of moisture from the sample is also higher, which causes greater strength gains. Apart from this moisture release, N2 injection may also cause the release of some adsorbed phase gases such as methane and CO2 from the coal matrix [22]. The adsorption of any of these coal seam gases (CH4, CO2) causes the coal matrix to swell and injecting N2 causes these swelled areas to recover to some extent. Coal swelling causes its strength to be reduced, and therefore even the partial recovery of swelling by injecting N2 should contribute to the enhancement of the strength of the coal mass.
The aim of this study is to identify the effect of coal rank on these coal mass mechanical property alterations under various fluid injections. According to Figure 4, the N2 saturation-created strength gain in brown coal samples is greater than the strength gain in black coal after N2 saturation (see Figure 4). For example, the UCS shows a 1.216 positive gradient for brown coal and a 0.338 positive gradient for black coal with N2 saturation pressure, while Young’s modulus shows a 0.801 and 0.424 positive gradient with N2 saturation pressure for brown and black coals, respectively. This is mainly related to the available moisture in black and brown coals. According to Table 2, the moisture content in brown coal (average 62%) is much higher than in black coal (average 3%). The amount of moisture removed from the coal mass by introducing N2 is therefore higher in brown coal, and this should cause a greater strength gain in brown coal than in black coal. According to the SEM images of 8 MPa N2 saturated brown and black coal samples (see Table 4), brown coal exhibits a clearer micro pore structure compared to black coal after water saturation, probably due to the water removed from the pore space. The SEM image of N2 saturated black coal shows some open pore spaces compared to the unsaturated black coal, possibly due to the moisture removed from the coal matrix. This proves the strength gains observed for N2 saturated black and brown coal.
The AE analysis data for N2 saturation, unlike water saturation, shows considerable delays in crack initiation to crack damage (stable crack propagation) for both high and low rank coals (see Table 4). For instance, 8 MPa N2 saturation caused the stable crack propagation in brown coal to increase from around 0.41 MPa to 0.6 MPa and in black coal from around 2.68 MPa to 3.8 MPa. This may be due to the lower water content in the N2 saturated sample. An increase of surface energy may take place with the water removal from the N2 saturated coal samples, eventually causing a delay in crack propagation. Interestingly, a comparison of the stress threshold values of N2 saturated brown and black coal shows that both display very similar behavior, as shown by the UCS and Young’s modulus results, which show an increment with increasing N2 saturation pressure, and a greater increment for brown coal compared to black coal. The previously mentioned moisture removal rate is the reason for this observation, further confirming the ability of N2 to cause strength gain in the coal mass. Hence, it can be concluded that N2 has the ability to slightly enhance the strength properties of coal and this ability is higher for low rank coal.

3.3. How Significant is Water and N2 Saturation on Coal Strength Compared to That of CO2

Coal generally has a mixture of pore fluid, composed of water, N2, CO2 and CH4 and their composition can be changed with various applications such as CO2 sequestration and N2 injection for ECBM recovery. It is therefore necessary to have comprehensive knowledge of the relative effect created by each component. Particularly in the case of CO2 sequestration, knowledge of the effects of other fluid saturations compared to CO2 saturation is necessary to have an overall idea of coal mass strength in this process. In addition, such a comparative study is essential for various ranked coals to determine the effects of these processes on coal seam. In this respect, Perera et al. [24] conducted a series of strength tests to compare the influence of water and N2 saturation with that of CO2 saturation. However, they conducted this series of strength tests on coal samples saturated under only very low pressure conditions (up to 3 MPa). These are far from the real situation in the field, in which quite high injection pressures of CO2 and N2 are used and the natural water is under very high pore fluid pressures. Therefore, the conduct of a comparative study with greater and more realistic saturation pressures is necessary to understand field conditions, while also incorporating other possible influences such as the CO2 phase effect. Further, a study of different ranked coal is necessary to identify how these influences vary from seam to seam or with coal maturity. This section therefore compares the findings of the present study with those of previous studies on the effect of CO2 saturation on low ranked brown coal [16] and high-ranked black coal [15].

3.3.1. Comparison of Variation of Coal’s Mechanical Properties

Figure 5 compares the UCS and Young’s modulus of CO2 and N2 saturated brown and black coals. According to this figure, there is a clear strength reduction with CO2 adsorption and in contrast a strength gain with N2 adsorption regardless of rank, and both types of strength property alterations are enhanced with increasing saturation pressure. However, when comparing brown and black coals, greater reductions in UCS and Young’s modulus with CO2 saturation in black coal can be seen, due to its well-defined cleat system. In contrast, a lower strength gain under N2 saturation in black coal can be seen due to the previously described lower moisture content of high rank coal. The influence of N2 and CO2 saturation on coal mechanical properties varies greatly under high saturation pressure conditions. For example, the CO2 adsorption-induced strength reduction in both black and brown coals is significantly enhanced after around 8 MPa, with the phase variation of CO2 from sub- to more chemically reactive super-critical conditions (see Figure 5). This change cannot be seen in N2 saturation with increasing pressure (a more linear variation with saturation pressure can be seen), because the N2 phase does not change under such conditions (for N2 the critical temperature is −146.8 °C and the critical pressure is 3.39 MPa) [23]. This is particularly important for field projects, in which coal seams are under very high saturation pressures and temperatures, and completely different responses to CO2 and N2 injections into the seam should be expected.
Now if the water saturation and CO2 saturation effect on coal strength are compared, quite similar behavior can be observed, as both cause the coal mechanical properties to be weaken, with black coal being subjected to more weakening than brown coal due to its cleat system. However, how the water saturation effect varies with saturation pressure could not be tested in the present study. This would give important information on the pressure effect on water softening and warrants future research.

3.3.2. Comparison of Fracture Propagation

Figure 6 shows the variation of normalized stress threshold values and Table 5 displays the respective stress threshold values for brown and black coal saturated with CO2 [15] and N2 [16]. Here, the values have been normalized by dividing each stress value by the respective stress threshold value under unsaturated condition. According to the AE data, (see Figure 6 and Table 5), unlike in N2 saturation, CO2 saturation causes quicker crack initiation and crack damage in both high and low rank coals, probably due to the reduced surface energy with CO2 adsorption [24]. For instance, at around 4 MPa CO2 saturation, there is around 0.74 MPa normalized crack initiation stress for brown coal and around 0.51 MPa crack initiation stress for black coal (around 4.5 MPa saturation pressure in black coal). Further, when comparing the stress threshold values in CO2 saturated brown and black coal, both display very similar behavior in terms of UCS and Young’s modulus (see Table 5), and a reducing stress threshold trend with increasing CO2 saturation pressure, the reduction being greater for black coal than brown coal (see Figure 6). The well-developed cleat system in black coal compared to brown coal might be the reason for this observation. Further, for super-critical CO2 saturations, black coal exhibits crack propagation without any crack initiation (see Figure 6a), probably due to the enhanced ductile behavior of samples under super-critical CO2 adsorption, which causes higher plasticization in the coal mass. In addition, crack propagation in N2 saturation also displays a similar behavior with the variation of strength parameters, which shows an increment in stress threshold with increasing N2 saturation pressure, the increment being greater for brown coal due to greater moisture removal. Based on these crack propagation changes which occur with CO2 and N2 saturations, the use of N2 to recover the CO2 adsorption-induced coal matrix alteration appears to be an effective option.
In relation to crack propagation in water- and CO2-saturated samples, both show more rapid crack propagation (see Table 5) compared to N2 saturation, and particularly in water-saturated sampled, crack initiation is not even visible (see Figure 6 and Table 5). In the case of CO2 saturation, CO2 adsorption-induced coal matrix swelling causes a strain layer to be generated between the adsorbed CO2 and the fracture/cleat face [9,11]. Hence, with lower axial load applications, this weak layer possibly starts to break, causing rapid crack propagation [30]. During water saturation, the water (H2O) molecules react with mineral/macerals and also create hydrogen bonds with the existing moisture in the coal mass [17], which results in structural rearrangements. Further, an expansion of fracture tips may occur due to the water molecule-induced internal stress increment [24], therefore initiating an early failure without any visible crack propagation.

4. Conclusions and Suggestions for Future Research

4.1. Conclusions Drawn from the Present Study

The influence of coal rank on various fluid saturation-induced coal mechanical properties changes was studied using low rank (Australian brown coal) and high rank (Australian black coal) coal samples. The following conclusions can be drawn:
  • Water saturation causes a significant strength reduction in coal regardless of rank, because the moisture penetrating into the coal mass causes its fractures to expand, decreasing the surface energy of the coal mass, and eventually causing the strength to be reduced.
  • This strength reduction is enhanced with increasing coal rank due to the well-developed cleats in mature coal which offer more loci for moisture to stay in the coal mass.
  • The enhanced ductile nature of coal upon water adsorption delays crack initiation, regardless of rank. It is therefore necessary to have a lot of low injection pressure for coal seams with a greater degree of water saturation in terms of safety.
  • In contrast to water saturation, N2 saturation slightly enhances coal strength, regardless of rank, and this increment increases with increasing N2 saturation pressures. This is possibly due to the ability of N2 to partially recover the coal seam gas (methane, CO2) adsorbed swelled areas and push out the adsorbed water from the coal mass.
  • N2 saturation significantly slows crack initiation and propagation in coal regardless of rank. This is a favorable feature in terms of long-term stability in coal seams and can be used to strengthen weak seams after CO2 injection.
  • The strength gain created by N2 saturation reduces with increasing rank, probably due to the lower level of moisture stored in high rank coal.
  • The variation of mechanical properties of coal upon CO2 and N2 saturations shows quite different responses to increasing saturation pressure, as the CO2 phase condition may change from sub- to super-critical under greater pressures. In contrast, N2 does not undergo such phase change with increasing pressure, due to its much lower critical conditions.
  • The present study was conducted under 35 °C temperature (N2 saturation) up to 8 MPa saturation pressure, which represents a pore pressure condition of an approximately 800 m deep coal seam [31]. As the study was conducted in an unconfined environment, the observed strength variations are expected to be lower in a confined environment under field conditions, because the confinement causes greater effective stress in the field, leading to a shrunken pore structure in coal seams with reduced gas flow performance through them.

4.2. Suggestions for Furture Research

  • Methane is one of the major components in coal seam gas that plays an important role in the overall mechanical response of the coal mass. Hence, to understand the overall influence of coal seam gas on coal’s mechanical properties, future research is needed on methane saturation under various pressures for different rank coals.
  • It is recommended to conduct further research on coal mass mechanical behavior under confinements for different saturation conditions to represent the real case scenarios existing in the field, where the coal mass has been exposed to lithostatic pressure conditions.
  • The water saturation effect of the present study was conducted under atmospheric pressure conditions due to the unavailability of the necessary laboratory facilities. However, it is essential to investigate the water saturation effect under different pressure conditions, so that it can be clearly compared with the different pressure effects of N2 and CO2. This is a future research option.
  • As found in the present study, coal mass mechanical behavior under various saturations varies with different coal types. However, the results of this study need to be generalized by testing various ranked coal samples taken from various coal basins around the world. Future experimentation is therefore recommended using a wider range of coal specimens taken from different basins in the world with diverse cleat structures and mineral compositions, in order to obtain better insight into the observed strength variations.

Acknowledgments

The authors wish to express their appreciation for the funding provided by the Australian Research Council (DE130100124) and the use of facilities in the Monash Centre of Electron Microscopy (MCEM).

Author Contributions

Ashani Savinda Ranathunga performed the experiments, analyzed the data, and prepared the draft manuscript. Mandadige Samintha Anne Perera mentored the experimental program and reviewed the draft. Ranjith Pathegama Gamage reviewed the final paper and made important suggestions and recommendations for paper revision.

Conflicts of Interest

The authors declare no conflict of interest.

Abbreviations

The following abbreviations are used in this manuscript:
AE
Acoustic emission
CC
Crack closure
CH4
Methane
CO2
Carbon dioxide
db
Dry basis
E
Young’s modulus
ECBM
Enhanced coal bed methane recovery
MCEM
Monash Center of Electron Microscopy
N2
Nitrogen
SC
Stable crack propagation
SEM
Scanning electron microscopy
UC
Unstable crack propagation
UCS
Unconfined compressive strength
wb
Wet basis
σcd
Crack damage stress
σci
Crack initiation stress

References

  1. Perera, M.S.A.; Ranjith, P.G. Carbon dioxide sequestration effects on coal’s hydro-mechanical properties: A review. Int. J. Energ. Res. 2012, 36, 1015–1031. [Google Scholar] [CrossRef]
  2. Ranathunga, A.S.; Perera, M.S.A.; Ranjith, P.G. Deep coal seams as a greener energy source: A review. J. Geophys. Eng. 2014, 11, 063001. [Google Scholar] [CrossRef]
  3. Vishal, V.; Singh, T.N. A laboratory investigation of permeability of coal to supercritical CO2. Geotech. Geol. Eng. 2015, 33, 1009–1016. [Google Scholar] [CrossRef]
  4. Xie, J.; Gao, M.; Yu, B.; Zhang, R.; Jin, W. Coal permeability model on the effect of gas extraction within effective influence zone. Geomech. Geophys. Geo-Energy Geo-Resources 2015, 1, 15–27. [Google Scholar] [CrossRef]
  5. Gale, J. Geological storage of CO2: What do we know, where are the gaps and what more needs to be done? Energy 2004, 29, 1329–1338. [Google Scholar] [CrossRef]
  6. Zhang, Y.; Gong, B.; Li, J.; Li, H. Discrete fracture modeling of 3D heterogeneous enhanced coalbed methane recovery with prismatic meshing. Energies 2015, 8, 6153–6176. [Google Scholar] [CrossRef]
  7. Hu, G.; Xu, J.; Zhang, F.; Zhao, C.; Qin, W.; Zhu, Y. Coal and coalbed methane co-extraction technology based on the ground movement in the yangquan coalfield, China. Energies 2015, 8, 6881–6897. [Google Scholar] [CrossRef]
  8. Aziz, N.I.; Ming-Li, W. The effect of sorbed gas on the strength of coal – an experimental study. Geotech. Geol. Eng. 1999, 17, 387–402. [Google Scholar] [CrossRef]
  9. Jasinge, D. An investigation of the effect of carbon dioxide sequestration on the behaviour of brown coal. Ph.D. Thesis, Monash University, Melbourne, Australia, 2010. [Google Scholar]
  10. Viete, D.R.; Ranjith, P.G. The effect of CO2 on the geomechanical and permeability behaviour of brown coal: Implications for coal seam CO2 sequestration. Int. J. Coal Geol. 2006, 66, 204–216. [Google Scholar] [CrossRef]
  11. White, C.M.; Smith, D.H.; Jones, K.L.; Goodman, A.L.; Jikich, S.A.; LaCount, R.B.; DuBose, S.B.; Ozdemir, E.; Morsi, B.I.; Schroeder, K.T. Sequestration of carbon dioxide in coal with enhanced coalbed methane recovery: A review. Energ. Fuel 2005, 19, 659–724. [Google Scholar] [CrossRef]
  12. Pan, Z.; Connell, L.D.; Camilleri, M. Laboratory characterisation of coal reservoir permeability for primary and enhanced coalbed methane recovery. Int. J. Coal Geol. 2010, 82, 252–261. [Google Scholar] [CrossRef]
  13. Gibbs, J.W. On the equilibrium of heterogeneous substances. Am. J. Sci. 1878, 16, 441–458. [Google Scholar] [CrossRef]
  14. Griffith, A.A. The phenomena of rupture and flow in solids. Phil. Trans. R. Soc. Lond. Ser. A 1921, 221, 163–198. [Google Scholar] [CrossRef]
  15. Perera, M.S.A.; Ranjith, P.G.; Viete, D.R. Effects of gaseous and super-critical carbon dioxide saturation on the mechanical properties of bituminous coal from the southern sydney basin. Appl. Energy 2013, 110, 73–81. [Google Scholar] [CrossRef]
  16. Ranathunga, A.S.; Perera, M.S.A.; Ranjith, P.G.; Bui, H. Super-critical CO2 saturation-induced mechanical property alterations in low rank coal: An experimental study. J. Supercrit. Fluids 2016, 109, 134–140. [Google Scholar] [CrossRef]
  17. Vishal, V.; Ranjith, P.; Singh, T. An experimental investigation on behaviour of coal under fluid saturation, using acoustic emission. J. Nat. Gas Sci. Eng. 2015, 22, 428–436. [Google Scholar] [CrossRef]
  18. Ates, Y.; Barron, K. The effect of gas sorption on the strength of coal. Min. Sci. Technol. 1988, 6, 291–300. [Google Scholar] [CrossRef]
  19. Brady, B.; Brown, E. Rock Mechanics: For Underground Mining, 3rd ed.; Springer: Dordrecht, The Netherlands, 2004. [Google Scholar]
  20. Jasinge, D.; Ranjith, P.; Choi, X.; Fernando, J. Investigation of the influence of coal swelling on permeability characteristics using natural brown coal and reconstituted brown coal specimens. Energy 2012, 39, 303–309. [Google Scholar] [CrossRef]
  21. Kiyama, T.; Nishimoto, S.; Fujioka, M.; Xue, Z.; Ishijima, Y.; Pan, Z.; Connell, L.D. Coal swelling strain and permeability change with injecting liquid/supercritical CO2 and N2 at stress-constrained conditions. Int. J. Coal Geol. 2011, 85, 56–64. [Google Scholar] [CrossRef]
  22. Perera, M.S.A.; Ranjith, P.G.; Choi, S.K.; Airey, D. The effects of sub-critical and super-critical carbon dioxide adsorption-induced coal matrix swelling on the permeability of naturally fractured black coal. Energy 2011, 36, 6442–6450. [Google Scholar] [CrossRef]
  23. Ranathunga, A.S.; Perera, M.S.A.; Ranjith, P.G.; Ju, Y.; Vishal, V.; De Silva, P. A macro-scale experimental study of sub-and super-critical CO2 flow behaviour in victorian brown coal. Fuel 2015, 158, 864–873. [Google Scholar] [CrossRef]
  24. Perera, M.S.A.; Ranjith, P.G.; Peter, M. Effects of saturation medium and pressure on strength parameters of Latrobe Valley brown coal: Carbon dioxide, water and nitrogen saturations. Energy 2012, 36, 6941–6947. [Google Scholar] [CrossRef]
  25. Ranjith, P.G.; Perera, M.S.A. Effects of cleat performance on strength reduction of coal in CO2 sequestration. Energy 2012, 45, 1069–1075. [Google Scholar] [CrossRef]
  26. Perera, M.S.A.; Ranjith, P.G.; Airey, D.W.; Choi, S.K. Sub- and super-critical carbon dioxide flow behavior in naturally fractured black coal: An experimental study. Fuel 2011, 90, 3390–3397. [Google Scholar] [CrossRef]
  27. ASTM D7012. Standard Test Method for Compressive Strength and Elastic Moduli of Intact Rock Core Specimens un-der Varying States of Stress and Temperatures; ASTM International: West Conshohocken, PA, USA, 2004. [Google Scholar]
  28. Vutukuri, V.S.; Lama, R.D.; Saluja, S.S. Handbook on Mechanical Properties of Rocks: Testing Techniques and Results; Trans Tech Publications: Bay Village, OH, USA, 1978; pp. 105–115. [Google Scholar]
  29. Kuvaev, N.; Panchenko, D. Effect of moisture on the dynamic strength of brown coals. J. Min. Sci. 1975, 11, 220–222. [Google Scholar] [CrossRef]
  30. Ranjith, P.G.; Jasinge, D.; Choi, S.K.; Mehic, M. The effect of CO2 saturation on mechanical properties of Australian black coal using acoustic emission. Fuel 2010, 89, 2110–2117. [Google Scholar] [CrossRef]
  31. Oldenburg, C.M. Geologic carbon sequestration: CO2 transport in depleted gas reservoirs. In Gas Transport in Porous Media; Springer: Dordrecht, The Netherlands, 2006; pp. 419–426. [Google Scholar]
Figure 1. Coal samples in (a) water saturation chamber and (b) N2 saturation chamber.
Figure 1. Coal samples in (a) water saturation chamber and (b) N2 saturation chamber.
Energies 09 00440 g001
Figure 2. Axial stress vs. axial strain curves for brown coal and black coal during water saturation.
Figure 2. Axial stress vs. axial strain curves for brown coal and black coal during water saturation.
Energies 09 00440 g002
Figure 3. Cumulative acoustic counts versus axial stress for unsaturated and water saturated (a) brown coal and (b) black coal samples (Here CC-Crack closure, SC-Stable crack propagation and UC-Unstable crack propagation).
Figure 3. Cumulative acoustic counts versus axial stress for unsaturated and water saturated (a) brown coal and (b) black coal samples (Here CC-Crack closure, SC-Stable crack propagation and UC-Unstable crack propagation).
Energies 09 00440 g003
Figure 4. (a) Compressive strength (UCS) and (b) Young’s modulus (E) increment during N2 saturation for brown and black coal.
Figure 4. (a) Compressive strength (UCS) and (b) Young’s modulus (E) increment during N2 saturation for brown and black coal.
Energies 09 00440 g004
Figure 5. Comparison of (a) UCS and (b) Young’s modulus variation with CO2 [15,16] and N2 saturation of brown coal and black coal.
Figure 5. Comparison of (a) UCS and (b) Young’s modulus variation with CO2 [15,16] and N2 saturation of brown coal and black coal.
Energies 09 00440 g005
Figure 6. Variation of normalized stress threshold values: (a) crack initiation stress, (b) crack damage stress, and (c) failure stress during different CO2 saturations for brown coal and black coal; and (d) crack initiation stress, (e) crack damage stress, and (f) failure stress during different N2 saturations for brown coal and black coal (here the stress threshold values were normalized by dividing by the respective stress threshold value for unsaturated sample).
Figure 6. Variation of normalized stress threshold values: (a) crack initiation stress, (b) crack damage stress, and (c) failure stress during different CO2 saturations for brown coal and black coal; and (d) crack initiation stress, (e) crack damage stress, and (f) failure stress during different N2 saturations for brown coal and black coal (here the stress threshold values were normalized by dividing by the respective stress threshold value for unsaturated sample).
Energies 09 00440 g006
Table 1. Geomechanical responses of different coal types under various CO2 saturation conditions.
Table 1. Geomechanical responses of different coal types under various CO2 saturation conditions.
Temperature (°C)Pressure (MPa)CO2 Phase ConditionCoal TypeCoal RankUCS (MPa)ΔUCS (%)E (MPa)ΔE (%)Reference
350-Lignite 1Low2.40-41.60-[16]
330-Bituminous 2High33.00-3700-[15]
Room temperature0-Bituminous 3High15.29-5340-[17]
Room temperature1GasLignite 1Low2.342.0940.324.73[16]
352GasLignite 1Low2.255.8635.0817.11[16]
353GasLignite 1Low2.179.2133.7820.18[16]
Room temperature4GasBituminous 3High12.6217.60394026.20[17]
354GasLignite 1Low2.1510.0433.6520.49[16]
334.5GasBituminous 2High15.8052.12230037.84[15]
356GasLignite 1Low1.8920.9232.2323.84[16]
336GasBituminous 2High14.3056.67213042.43[15]
358Super criticalLignite 1Low1.0257.3224.9141.14[16]
338Super criticalBituminous 2High7.4077.58110070.27[15]
3510Super criticalLignite 1Low0.9361.0923.4244.69[16]
3312Super criticalBituminous 2High7.3077.88116068.65[15]
3316Super criticalBituminous 2High13.9557.64157057.58[15]
1 Australian brown coal; 2 Australian black coal; 3 Indian black coal.
Table 2. Physical properties of Victorian brown coal and Southern Sydney basin bituminous coal used for the study.
Table 2. Physical properties of Victorian brown coal and Southern Sydney basin bituminous coal used for the study.
Physical PropertyBrown Coal [16]Black Coal [15]
Coal density (g/cm3)1.04–1.11.4–1.9
Moisture content (% wb) 157–661–5
Fixed carbon (% db) 14860–71
Ash yield (% db) 11.76–12
Volatile matter content (% db) 150.310–25
Vitrinite reflectance (%)0.0–0.4 21.1–1.5 2
1 wb-wet basis, db-dry basis; 2 From Silva [24].
Table 3. Unconfined compressive strength (UCS) and Young’s modulus (E) values obtained under various saturation conditions for brown coal and black coal.
Table 3. Unconfined compressive strength (UCS) and Young’s modulus (E) values obtained under various saturation conditions for brown coal and black coal.
Saturation FluidPressure (MPa)Brown CoalBlack Coal
UCS (MPa)ΔUCS (%) 3E (MPa)ΔE (%) 3UCS (MPa)ΔUCS (%) 3E (GPa)ΔE (%) 3
Unsaturated-2.39 1-42.32 1-31.01 2-3.52 2-
-2.34 1-39.32 1-33.00 2-3.70 2-
-2.36 1-42.16 1-----
Water-2.07−14.6435.46−16.2121.01−36.332.24−39.46
-2.01 35.17 20.89 2.14
-2.05 35.28 20.94 2.20
N222.431.5842.520.4733.391.183.710.27
22.39 41.97 32.17 3.54
62.515.0543.081.8033.762.303.761.62
62.48 43.01 32.89 3.64
82.577.5644.284.6334.01 23.063.80 22.70
82.54 44.16 33.20 2 3.71 2
16----35.11 26.393.91 25.68
16 33.30 2 3.71 2
1 From Ranathunga, Perera, Ranjith and Bui [16]; 2 From Perera, Ranjith and Viete [15]; 3 The sample with the highest UCS value was taken to calculate the UCS and E variations.
Table 4. Appearance of the brown and black coal samples under different fluid saturations before and after failure.
Table 4. Appearance of the brown and black coal samples under different fluid saturations before and after failure.
Coal TypeSample Appearance Under Different Test ConditionsSEM Images 3Average Pore Size
Natural samples
Brown coal Energies 09 00440 i001 Energies 09 00440 i002 Energies 09 00440 i003~0.9 μm
Before failure 1After failure 1
Black coal Energies 09 00440 i004 Energies 09 00440 i005 Energies 09 00440 i006~0.43 μm
Before failure 2After failure 2
Water-saturated samples
Brown coal Energies 09 00440 i007 Energies 09 00440 i008 Energies 09 00440 i009~0.34 μm
Before failureAfter failure
Black coal Energies 09 00440 i010 Energies 09 00440 i011 Energies 09 00440 i012~0.12 μm
Before failureAfter failure
N2 saturated samples
Brown coal Energies 09 00440 i013 Energies 09 00440 i014 Energies 09 00440 i015~0.62 μm
After saturation in 8 MPa N2After saturation in 8 MPa N22
Black coal Energies 09 00440 i016 Energies 09 00440 i017 Energies 09 00440 i018~0.23 μm
After failureAfter failure 2
1 From Ranathunga, Perera, Ranjith and Bui [16]; 2 From Perera, Ranjith and Viete [15]; 3 viewed under a magnification of 17,500×, a working distance of 10 mm and a voltage of 15 kV.
Table 5. Stress threshold values obtained under various saturation conditions for brown coal and black coal.
Table 5. Stress threshold values obtained under various saturation conditions for brown coal and black coal.
Saturation FluidSaturation Pressure (MPa)Brown CoalBlack Coal
Crack Initiation Stress (σci, MPa)Crack Damage Stress (σcd, MPa)UCS (MPa)Crack Initiation Stress (σci, MPa)Crack Damage Stress (σcd, MPa)UCS (MPa)
Unsaturated-1.01 11.42 12.39 126.70 230.50 233.00 2
Water---2.06-17.1520.94
N221.141.572.4327.1029.3833.39
61.241.792.5127.5330.4333.76
81.321.922.5728.10 231.90 234.01 2
16---30.14 232.16 235.11 2
1 From Ranathunga, Perera, Ranjith and Bui [16]; 2 From Perera, Ranjith and Viete [15].

Share and Cite

MDPI and ACS Style

Perera, M.S.A.; Ranathunga, A.S.; Ranjith, P.G. Effect of Coal Rank on Various Fluid Saturations Creating Mechanical Property Alterations Using Australian Coals. Energies 2016, 9, 440. https://doi.org/10.3390/en9060440

AMA Style

Perera MSA, Ranathunga AS, Ranjith PG. Effect of Coal Rank on Various Fluid Saturations Creating Mechanical Property Alterations Using Australian Coals. Energies. 2016; 9(6):440. https://doi.org/10.3390/en9060440

Chicago/Turabian Style

Perera, Mandadige Samintha Anne, Ashani Savinda Ranathunga, and Pathegama Gamage Ranjith. 2016. "Effect of Coal Rank on Various Fluid Saturations Creating Mechanical Property Alterations Using Australian Coals" Energies 9, no. 6: 440. https://doi.org/10.3390/en9060440

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop