Mechanistic insights across curing regimes for enzymatic and biopolymer-optimized reinforcement in rock masses
Abstract
Biocementation is an innovative and sustainable technique for reinforcing weak and weathered rock masses in natural and engineered geological settings, and yet, the influence of curing temperature on the mechanical behavior of treated rock masses has not yet been constrained. Biocementations, like enzyme-induced calcite precipitation (EICP) and biopolymers (BP), have gained prominence for enhancing rock properties, particularly to support underground infrastructure. This study systematically investigates how curing regimes affect the mechanical (elastic and inelastic) behavior and reinforcement performance of rock masses for underground engineered applications using EICP and a novel technique, biopolymer-modified enzymatic precipitation (BP-EICP). Results demonstrate that BP-EICP can significantly enhance bulk stiffness (E) by +187% and uniaxial compressive strength (UCS) by +210%, while EICP alone yields comparable improvements (E: +178%; UCS: +216%). Curing temperature plays a critical role in biomineralization, with lower temperature curing producing greater reinforcement in BP-EICP-treated specimens (E: +192%; UCS: +220%) compared to higher curing temperature (E: +178%; UCS: +199%). The modulus ratio (MR) suggests that curing temperature has a minimal effect on stiffness ratios, whereas the biocementation type has a more pronounced impact, with the EICP-treated specimens yielding a 20% decrease in MR, versus a 13% reduction with BP-EICP. Failure modes in biocemented specimens become more complex with increased curing regimes and enzyme activity, showing transitions between axial and shear failure. This work provides new insights into the role of curing temperature and biocementation type in modifying the mechanical behavior of rock masses subjected to stress conditions, with implications for the stability and design of underground natural and built infrastructure.
Highlights
This study investigates how curing regimes influence the behavior of biocemented underground rock masses.
Biopolymer-modified enzymatic precipitation boosts stiffness (+187%) and strength (+210%) in treated rock specimens.
Biocementation curing at low temperatures yields greater rock reinforcement than high-temperature curing.
Biopolymer addition enhances temperature sensitivity in biocementation performance.
Modulus ratio is more affected by biocementation type than by curing temperature in biocemented rocks.
1 INTRODUCTION
Enhancing the properties of weak and fractured rock masses in and around infrastructure in deep underground environments through biocementations has become increasingly vital for improving their mechanical performance for various engineered applications, including near-wellbore cementation (Kolawole et al., 2023; Newell & Carey, 2012), soil reinforcement for erosion mitigation (Almajed et al., 2020; Dagliya et al., 2023), strength enhancement for structural stability (Almajed et al., 2019; Arab et al., 2024; Chandra & Ravi, 2020; Cui et al., 2020, 2024; Refaei et al., 2020; Song et al., 2020), and permeability reduction for effective groundwater flow management (Ashraf et al., 2017; Gao et al., 2019; Hataf & Baharifard, 2019; Kirkland et al., 2020; Lemboye et al., 2021). Traditional methods, such as the use of Portland cement, are widely used but are harmful to the environment due to the high carbon dioxide emissions associated with their production (Chaturvedi & Ochsendorf, 2004; Habert, 2014; Mishra et al., 2022; Mohamad et al., 2021). As a result, sustainable alternatives like enzyme-induced calcite precipitation (EICP) are gaining traction for enhancing the properties of rocks and soils (Alotaibi et al., 2022; Cui et al., 2020; Kumar et al., 2023; Ngoma & Kolawole, 2024). EICP leverages biologically mediated reactions to precipitate calcite within the pore spaces of granular materials, thereby improving their bulk mechanical properties in an eco-friendly manner.
Over the past two decades, several studies have investigated biologically induced techniques for the improvement of underground soils and rocks (Kolawole & Assaad, 2023; Kolawole et al., 2021, 2022; Mortensen & DeJong, 2011; Ngoma & Kolawole, 2024; Ngoma, Kolawole, & Lu, 2024; Ngoma, Kolawole, Olorode, et al., 2024; Xie, Cheng, et al., 2023), and EICP has emerged as one of the most popular explored methods. Several studies have shown that EICP biocementation can change the properties of soils by reducing permeability (Lemboye et al., 2021; Park & Choi, 2021) and increasing the shear strength and uniaxial compressive strength (UCS) of the soil (Li et al., 2024; Xue et al., 2024). To further improve the action of enzyme-induced biocementations, recent advancements have involved the use of the EICP method coupled with biopolymers, such as sodium alginate [SA] (Almajed et al., 2020; Arab et al., 2024; Chandra & Ravi, 2020; Dagliya et al., 2023; Refaei et al., 2020). For instance, SA-modified EICP has been used to stabilize desert sand against wind-induced erosion (Almajed et al., 2020; Dagliya et al., 2023), which has facilitated the development of natural bio-cemented sandstone suitable for use as bricks (Arab et al., 2024). The integration of EICP with biopolymers has also been used for the improvement of critical soil properties such as shear strength (Chandra & Ravi, 2020; Cui et al., 2024; Refaei et al., 2020), UCS (Arab et al., 2024; Refaei et al., 2020), and permeability (Almajed et al., 2020; Baig et al., 2024; Lemboye et al., 2021). Other applications of SA-modified EICP extend to the consolidation of sand produced during oil and gas extraction (Albenayyan et al., 2023; Baig et al., 2024) and the immobilization of copper in soils from wastewater discharged in copper mining and smelting operations (Xie, Cheng, et al., 2023). Although numerous studies have explored the impact of EICP and biopolymer in soils, only a few have examined their potential in consolidated geomaterials (Barrufet et al., 1992; Elyasi Gomari et al., 2021; Ngoma & Kolawole, 2024; Ngoma, Kolawole, & Lu, 2024; Ngoma, Kolawole, Olorode et al., 2024). For instance, Ngoma and Kolawole (2024) investigated the impact of EICP on the mechanical behavior of rocks, while Ngoma and Kolawole (2024) explored the depth of enzymic penetration in rock masses. For biopolymers, Barrufet et al. (1992) used a modified starch biopolymer to alter the hydraulic properties of rocks (−67% reduction). In another study, Elyasi Gomari et al. (2021) found that synthetic polymer polyacrylamide (PAM) and biopolymer Xanthan gum (XG) reduced rock hydraulic properties by −36% and −18%, respectively. However, in addition to the scarce literature on the influence of biopolymers in rocks, to date, no study has explored the impact of SA biopolymer in rocks. This gap is notable because Lemboye et al. (2021) revealed that SA outperformed other biopolymers such as guar gum in improving soil properties, suggesting that it may have greater impact in rock masses compared to other biocementation approaches. Consequently, this work uses SA as the selected biopolymer for engineered rock mass modification. Furthermore, no research has investigated the action and potential of the combined effect of biopolymer (SA) and enzymes (EICP) in rocks, to understand if it will yield the same improvement as that reported in soils.
Studies have also shown that curing temperature may significantly influence the effect of EICP, with optimal results achieved at specific temperatures (Wang et al., 2022; Xue et al., 2024; Zhang et al., 2022). For instance, Xue et al. (2024) investigated the feasibility and efficiency of treating soils using EICP cured at a low temperature of 4°C and at room temperature (21°C). This low curing temperature minimized surface clogging during the same treatment cycles compared to room-temperature curing, due to reduced urease activity. Although the UCS results indicated a slight reduction in strength at low temperatures, an improvement in bio-clogging was observed. Another investigation explored the effects of EICP on soil and found that urease activity remained stable at temperatures below 65°C (Wang et al., 2022). However, at temperatures exceeding 65°C, urease activity diminished with increasing temperature, affecting the mineral precipitation produced (Wang et al., 2022). Wu et al. (2022) demonstrated the potential of EICP to solidify soil for wind erosion prevention and reported that increasing curing temperatures from 15 to 45°C can enhance the mechanical properties of the soil. Similarly, the efficiency of calcite precipitation improved with increasing temperature from 30 to 50°C (Park & Choi, 2021). Another work examined urease reactions with cementation solutions containing varying concentrations of urea and calcium ions at different temperatures to determine the calcium carbonate production rates (Zhang et al., 2022). Using scanning electron microscopy (SEM) and image processing, it was reported that increased urease activity and higher temperatures might have led to higher calcite production rate and larger crystal sizes of calcium carbonate (Zhang et al., 2022). Finally, a recent study focused on addressing the challenge of solidification inhomogeneity caused by high urease activity at elevated temperatures by using garlic extract, a urease inhibitor, at temperatures ranging from 35 to 55°C. The addition of an extract reduced urease activity and improved the homogeneity of solidified soil (Wang et al., 2023).
Despite the growing body of literature, limited research has focused on understanding the effects of EICP on underground rocks, and no studies have explored the combined influence of biopolymers and EICP on rock properties. Moreover, given that rocks can be located deep underground within the subsurface interval, they are subjected to varying temperatures and conditions. Therefore, it is imperative to investigate how EICP and biopolymer-modified EICP (BP-EICP) may influence rock behavior subjected to distinct curing regimes to fully understand their potential and applications.
To address these knowledge gaps, this study aims to explore three fundamental questions: (a) What is the potential of the use of innovative biopolymer-modified enzymatic induced calcite precipitation (BP-EICP) in reinforcing weak rock masses for underground engineering applications? (b) How do biocementation-induced modifications influence the elastic and inelastic behavior of enzymatic (EICP) and biopolymer-optimized (BP-EICP) biocemented rock masses? (c) How do distinct curing regimes (low vs. high temperature) influence the mechanical characteristics of rock masses treated with EICP and BP-EICP? To investigate these questions, we use weak sandstone rock mass commonly found in the underground natural and built environments as an analog for this study, and conduct a suite of tests on biocement-treated and untreated rock specimens that are subjected to unconfined compressive loading conditions.
2 METHODOLOGY
This study adopts a systematic methodology to evaluate the effects of enzymatic and biopolymer-modified biocementations in rocks. The process begins with the preparation and polishing of sandstone rock specimens, followed by the preparation of biocementation treatments.
The specimens are then immersed in cultured biocementation solutions for 3 days and thereafter cured at two distinct temperatures (31 and 45°C). A curing temperature of 31°C was selected, as it is within the commonly reported range for optimum urease activity (Arab, Omar, et al., 2021; Ngoma & Kolawole, 2024), whereas a temperature of 45°C was used to evaluate the effect of an elevated curing temperature on enzyme and biopolymer activity. After the curing phase, the rock specimens are dried in ambient conditions for 3 days. After drying the specimens, uniaxial compression tests are conducted, and the resulting stress–strain curves are obtained and analyzed to examine the mechanical response of the rocks due to the enzymatic and biopolymer-modified biocementations. Figure 1 summarizes the approach used in this study.
2.1 Rock specimens
The analogous inherently heterogeneous granular material used for this study is Berea Sandstone from a sandstone formation in the United States, and this variation of Berea sandstone is from a horizontally layered heterogeneous poroelastic formation with high porosity. The sandstone block was sourced from a subsurface interval of 524 m (1720 ft) with a porosity range of 18%–21% and a permeability range of 80–120 mD. The rock was then prepared into cylindrical cores with a diameter-to-height ratio of 1:2, following the recommended procedures in the International Society for Rock Mechanics [ISRM] (Bieniawski & Bernede, 1979) and American Society for Testing and Materials [ASTM] (ASTM, 2019) standards. Specifically, the cylindrical core specimens are 7.6 cm in height and 3.8 cm in diameter, as shown in Figure 2. The core specimens are divided into groups, as outlined in Table 1, with group A being the untreated control specimens, group B representing the EICP-treated specimens, and group C corresponding to the BP-EICP-treated specimens.
| Sample ID | Treatment period (day) | Sample type | Rock type | Bio-cementation treatment | Curing temperature (°C) | Group |
|---|---|---|---|---|---|---|
| S1 | 0 | Core | Sandstone | No Treatment | N/A | A |
| S2 | 0 | Core | Sandstone | No Treatment | N/A | |
| S3 | 3 | Core | Sandstone | EICP | 31 | B |
| S4 | 3 | Core | Sandstone | EICP | 31 | |
| S5 | 3 | Core | Sandstone | EICP | 45 | |
| S6 | 3 | Core | Sandstone | EICP | 45 | |
| S7 | 3 | Core | Sandstone | Biopolymer + EICP (BP-EICP) | 31 | C |
| S8 | 3 | Core | Sandstone | Biopolymer + EICP (BP-EICP) | 31 | |
| S9 | 3 | Core | Sandstone | Biopolymer + EICP (BP-EICP) | 45 | |
| S10 | 3 | Core | Sandstone | Biopolymer + EICP (BP-EICP) | 45 |
Abbreviation: EICP, enzyme-induced calcite precipitation.
2.2 Biocementation treatment
2.2.1 EICP
The urease enzyme used in this study was purchased from Millipore Sigma, with a specific activity of 50 000–100 000 units/g solid. For EICP treatment, first, a cementation solution is prepared containing a 300 mM equimolar solution of urea and calcium chloride, followed by preparation of a second solution of 0.3 g/L of urease. The cementation solution and urease are pre-mixed immediately before the specimens are immersed in the solution to prevent premature chemical reactions. Fresh urease-cementation solution is then replaced every day for 3 days (Table 2).
| Media | Composition | Quantity |
|---|---|---|
| Cementation solution (pH = 7) | Urea (mM) | 300 |
| Calcium chloride (mM) | 300 | |
| Urease (g/L) | 0.3 |
Abbreviation: EICP, enzyme-induced calcite precipitation.
2.2.2 SA for biopolymer-modified EICP (BP-EICP)
SA (NaC6H7O6) is a natural hydrophilic polysaccharide derived from the cell walls of marine brown algae (Maiti & Kumari, 2016; Santos, 2017). SA is composed of (1–4) linked β-d-mannuronic acid (M units) and α-l-guluronic acid (G units) (Arab et al., 2024; Maiti & Kumari, 2016; Santos, 2017). Studies have shown that the G-blocks of alginate form strong intermolecular crosslinking, also called an egg-box structure, with calcium ions (Figure 3; Maiti & Kumari, 2016; Santos, 2017). For example, when SA is mixed with CaCl2, the monovalent ions in SA (i.e., Na+) are exchanged for divalent ions in CaCl2 (i.e., Ca2+). This reaction transforms the solution from a low-viscosity solution to a gel structure, which consequently enhances the mechanical properties of alginate gels (Maiti & Kumari, 2016; Santos, 2017). The SA used in this work had a reported viscosity of 5–40 cP (1% solution, 25°C) and an estimated molecular weight range of 12 000–40 000 Da. The batch-specific guluronic/mannuronic (G/M) ratio of the SA was reported by the manufacturer (Millipore Sigma-aldrich) to be approximately 1.56. In this study, the SA (biopolymer) used was 1.2% of the average mass of the sandstone rock specimens (in this case, 2 g of SA). The SA is then mixed with the EICP solution before immersion of the rock mass.
2.3 Uniaxial compression test
For uniaxial compression tests, we utilized the GCTS RMS-101 Rock Mechanics Testing System to obtain the stress–strain curves of all 10 core specimens. The testing procedure followed the recommended ISRM standard (Bieniawski & Bernede, 1979), and for the testing program, we maintained a consistent loading rate of 0.5 MPa/s for all the core specimens. The stress–strain curve data from this test are used to characterize the mechanical and loading responses of the specimens with and without EICP and BP-EICP biocementations.
3 RESULTS
A visual assessment of specimens, as shown in Figure 4, was conducted to evaluate the effects of EICP and BP-EICP treatments on the rocks. Figure 4a presents the core specimens before EICP biocementation, whereas Figure 4b,c shows the specimens after EICP treatment at 31 and 45°C, respectively. Similarly, Figure 4d displays the specimens before BP-EICP biocementation, with Figure 4e,f showing the specimens after BP-EICP treatment at 31 and 45°C, respectively. In Figure 4b,c, calcite precipitation is visible around the core specimens for both curing temperatures. However, specimens cured at 31°C show a fully covered top surface (Figure 4b), whereas the specimens cured at 45°C show only partial calcite depositions around the surface rock specimen (Figure 4c). In Figure 4e,f, BP-EICP-treated specimens show prominent calcium alginate gel deposited around the surface of the core specimens, with only minimal calcite precipitation observed.
The mechanical properties of the pre- and post-treatment rock specimens were measured using a suite of uniaxial compression tests. From these tests, the stress–strain curves of the specimens were recorded, as presented in Figure 5. The stress–strain relationship consists of the elastic phase, the yield phase, and failure, with the UCS of the specimens being recorded at the peak of the stress–strain curve, whereas the E is estimated from the linear portion of the curve. The UCS and E of the non-treated and treated specimens are recorded in Table 3. The pre-treatment UCS values of the rock are 8.6 MPa (specimen S1) and 18.7 MPa (specimen S2), whereas the post-EICP treatment UCS values after 3 days are 42.9 MPa (specimen S3), 42.2 MPa (specimen S4), 42.7 MPa (specimen S5), and 44.1 MPa (specimen S6). Post-BP-EICP treatment UCS values for specimens S7, S8, S9, and S10 after 3 days are 46.9, 40.3, 40.9, and 40.5 MPa, respectively.
| Sample ID | Bio-cementation treatment | Curing temperature (°C) | UCS (MPa) | Young's modulus – E (GPa) |
|---|---|---|---|---|
| S1 | No treatment | N/A | 8.6 | 1.5 |
| S2 | No treatment | N/A | 18.7 | 2.3 |
| S3 | EICP | 31 | 42.9 | 5.3 |
| S4 | EICP | 31 | 42.2 | 4.7 |
| S5 | EICP | 45 | 42.7 | 5.3 |
| S6 | EICP | 45 | 44.1 | 4.6 |
| S7 | BP-EICP | 31 | 46.9 | 5.5 |
| S8 | BP-EICP | 31 | 40.3 | 5.3 |
| S9 | BP-EICP | 45 | 40.9 | 5.3 |
| S10 | BP-EICP | 45 | 40.5 | 5.0 |
Abbreviation: EICP, enzyme-induced calcite precipitation.
Young's modulus (Eavg), using the average method, was also estimated, and the results show that the pre-treatment E values are 1.5 GPa (specimen S1) and 2.3 GPa (specimen S2), whereas the post-EICP E values after 3 days of treatment are 5.3 GPa (specimen S3), 4.7 GPa (specimen S4), 5.3 GPa (specimen S5), and 4.6 GPa (specimen S6). Post BP-EICP treatment E values for specimens S7, S8, S9, and S10 after 3 days are 5.5, 5.3, 5.3, and 5.0 GPa, respectively. Further, we estimated additional values of Young's modulus using the secant (Esec) and tangent methods (Etan), which will be discussed in the next section.
4 DISCUSSION
4.1 Potential of BP-EICP and EICP biocementations
The potential of biopolymer-modified EICP in rocks has not been previously explored. The results presented in this study demonstrate that both BP-EICP and EICP biocementations can significantly enhance the mechanical properties of rock (Figure 6). Analyses of the results (Figure 7) show up to a 216% increase in UCS with EICP biocementation and up to a 210% increase with BP-EICP, confirming the effectiveness of both approaches in improving rock strength. Additionally, untreated rocks are less brittle, as shown by their gradual stress–strain response and greater inelastic deformation (Figure 7), whereas EICP- and BP-EICP-treated rocks are more brittle, as they show more abrupt failure.
The observed strength improvement in EICP-biocemented rocks can be attributed to the precipitation of calcite (CaCO₃) within rock pore spaces and in BP-EICP-biocemented rocks, the increased strength can be attributed to the combined effect of calcite mineral precipitation (CaCO₃) and dehydrated calcium alginate gel (C12H14CaO12) formation (Figure 6). In BP-EICP, calcium ions facilitate gelation by replacing monovalent sodium ions in SA, thereby triggering transformation from a low-viscosity solution to a gel-like structure. However, this gelation process may compete with the urease enzyme for calcium ions during the biomineralization reactions (Yuryev et al., 1979; Figure 4), which is why BP-EICP biocementation induced slightly lower mechanical strength in rocks than EICP (Figure 7). Additionally, previous reports suggest that urea can slow the gelation process (Ustunol et al., 1992; Yuryev et al., 1979). Furthermore, unlike studies on biocementation in soils, where biopolymers can be pre-mixed with soil grains before introducing the cementation solution (Arab, Omar et al., 2021), such pre-mixing is not feasible in rocks, which may have slightly influenced the overall effectiveness of BP-EICP biocementation in rocks.
Despite these observations, BP-EICP had a greater effect on the average rock stiffness (E:
4.2 Curing temperature control on changes in rock mechanical responses: EICP versus BP-EICP
Analyses of the stress–strain curves (Figure 5) in this study reveal that the mechanical behavior of rocks varies significantly depending on the biocementation method used (EICP vs. BP-EICP) and the curing temperature (31°C vs. 45°C). Since biocementation is aimed at the long-term enhancement of rock properties for engineering applications, it is crucial to assess both the elastic and inelastic behavior at varying temperatures. In this work, the evaluated elastic properties are Young's modulus (E) and the modulus ratio (MR), which will characterize the stiffness and deformation response of biocemented rocks. To assess the effect of biocementation on the inelastic (permanent deformation) behavior of rocks, the UCS and the consequent failure modes of the biocemented rocks were analyzed.
4.2.1 Elastic mechanical response
To estimate Young's modulus of rocks, the International Society of Rock Mechanics (ISRM) suggests three methods (Bell & Lindsay, 1999; Małkowski et al., 2018): (a) tangent Young's modulus [Etan] (slope at a fixed percentage of the UCS), (b) average Young's modulus [Eavg] (slope of the straight-line part of the stress–strain curve), and (c) secant Young's modulus [Esec] (slope of the line from the origin to a fixed percentage of the UCS). Małkowski et al. (2018) suggested that the tangent modulus (when calculated within a 30%–70% range of peak stress) and the average modulus are the most reliable methods, while the secant modulus is a less reliable method, as it incorporates pore compaction and microcrack effects. Therefore, this work first examines both proposed methods (tangent and average modulus) to estimate Young's modulus of biocemented rocks and then evaluates which method is most suitable for biocemented rocks. To determine the best method for determining Young's modulus of rocks, the coefficient of determination (R2) between UCS and E can be utilized (Małkowski et al., 2018; Ocak, 2008), with a high R2 indicating a better method determination.
The estimated Young's modulus using the secant (Esec) and tangent methods (Etan) was further analyzed and compared with Young's modulus obtained from the average method (Eavg). Figure 9 shows the relationship between the average Young's modulus (Eavg) and UCS (Figure 8a), and the relationship between the tangent Young's modulus (Etan) and UCS (Figure 8b). The results show that Eavg and Etan have R² values of 0.94 and 0.97, respectively. Because the difference in R² between the two methods is insignificant (0.03), this study used Eavg for the analysis of the elastic properties of biocemented rocks. Since biocementation involves complex biogeochemical processes that are highly dependent on multiple factors that cannot be assumed or generalized, in the case of biocemented rocks, it is important to utilize a method that accounts for these variables by using the entire recorded stress–strain data. The tangent method, which assumes linearity at the 30%–70% range of peak stress without considering the entire data set, may lead to generalizations that do not fully capture the elastic response of biocemented rocks. In contrast, the average method incorporates the complete linear stress–strain record, which is necessary for accurate analysis of such complex biogeochemical interactions in rocks.
Using the Eavg method, it was found that the EICP-biocemented rocks cured at a lower temperature showed a 169% increase in stiffness (E), while those cured at 45°C showed a 165% increase (Figure 10a,b). Similarly, the BP-EICP-biocemented rocks cured at a lower temperature demonstrated a 192% increase in stiffness, whereas those cured at 45°C showed a 178% increase (Figure 10a,c). These results align with our initial hypothesis for this work, as previous studies had suggested that high-temperature curing limits crystal growth, which in turn restricts biocementation. Conversely, curing at lower temperatures promotes the formation of larger, well-defined crystals (Cashman, 1993; Marsh, 1981; Mullin, 2001; Myerson, 2002), which can enhance biocementation and improve stiffness in granular media. However, temperature differences had a greater impact on BP-EICP biocementation than on EICP biocementation. In EICP-biocemented rocks, the stiffness improvement at a lower temperature was only 4% greater than that at a higher temperature, suggesting that temperature may not have a significant influence on this change. However, in BP-EICP, low-temperature curing resulted in a 16% greater improvement in rock stiffness compared to high-temperature curing. This discrepancy suggests that low temperature alone is insufficient for large biocement crystal formation, and thus, factors such as urease activity (Chen et al., 2024; Myerson, 2002; Zhang et al., 2022) and in the case of our current study, the presence of biopolymer gel, increased the ability of rocks to resist deformation under compressional stress. This suggests that the biopolymer (calcium alginate gel) in BP-EICP contributed to stiffness retention under varying temperature conditions.
Young's modulus (E) and UCS are essential parameters that are typically applied independently in the analysis of underground stability (Aladejare et al., 2021; Kahraman et al., 2003; Lü et al., 2012). The ratio of UCS to E defines the MR, which is widely used in rock mass estimations and the derivation of rock mass deformation modulus when direct field testing is not feasible (Hoek & Diederichs, 2005; Ocak, 2008; Palchik, 2010). Studies have shown that ignoring the UCS–E correlation can undermine geotechnical reliability, leading to over- or underestimation of rock engineering assessments (Aladejare et al., 2021; Wang & Aladejare, 2016). Therefore, this study also examined the change in the modulus ratio due to biocementation. Previous research has emphasized that the use of the MR of rocks is project-specific (Aladejare et al., 2021) and that there is a positive correlation between UCS and E of rocks (Karakus et al., 2005; Palchik, 2010; Sonmez et al., 2004, 2005). Yet, there has been an overgeneralized use of MR of rocks with the assumption that increasing modulus ratio implies an increase in both E and UCS (Palchik, 2010), which ultimately suggests a more desired rock characteristic in rock engineering applications. However, biologically induced reactions introduce cementitious materials that increase rock strength (Gao et al., 2019; Kolawole et al., 2021; Ngoma & Kolawole, 2024; Ngoma, Kolawole, Lu, 2024; Ngoma, Kolawole, Olorode et al., 2024), relative to untreated rocks, and this can yield a lower value of stiffness to UCS ratio (MR) in such biocemented rocks. Therefore, the generalized application of MR is not applicable in the case of biocemented rocks, which do not obey simplistic MR assumptions. Additionally, even though rocks with high UCS are generally stiffer (higher E), exceptions occur due to mineral composition, porosity, and microfractures, which can weaken or strengthen this relationship.
Table 4 shows that the MR of biocemented rocks decreases after biocementation, with EICP-treated rocks showing the greatest reduction. For EICP-biocemented rocks, MR declined from 145 to 117 at a lower temperature (31°C) and to 114 at a higher temperature (45°C). Similarly, BP-EICP-biocemented rocks showed a decrease in MR from 145 to 125 at lower temperatures and 127 at higher temperatures (Table 4). These results indicate that curing temperature has minimal influence on MR, whereas the type of biocementation method (EICP vs. BP-EICP) has a more significant impact. Specifically, MR decreased by 20% in EICP-biocemented rocks, compared to a 13% reduction in BP-EICP-biocemented rocks, highlighting the greater effect of EICP in altering the relationship between stiffness and strength. Therefore, we can conclude that although biocementation enhances both the strength (UCS) and the stiffness (E) of rock masses (Figures 6 and 7), the relationship between them (MR = E/UCS) does not follow a fixed trend. This means that while both UCS and E increase, they may not do so at the same rate. As a result, the modulus ratio can either increase or decrease depending on how much each parameter changes relative to the other. This variability highlights the complex interaction between strength and stiffness in biocemented rocks, which is influenced again by critical factors, which are biocementation distribution, inherent porosity, and microstructural changes.
| Rock Specimen | Bio-cementation treatment | Curing temperature (°C) | Modulus ratio (MR) | Average MR |
|---|---|---|---|---|
| S1 | No treatment | N/A | 169 | 145 |
| S2 | No treatment | N/A | 121 | |
| S3 | EICP | 31 | 123 | 117 |
| S4 | EICP | 31 | 112 | |
| S5 | EICP | 45 | 125 | 114 |
| S6 | EICP | 45 | 103 | |
| S7 | BP-EICP | 31 | 118 | 125 |
| S8 | BP-EICP | 31 | 133 | |
| S9 | BP-EICP | 45 | 130 | 127 |
| S10 | BP-EICP | 45 | 124 |
Abbreviations: BP-EICP, biopolymer-modified EICP; EICP, enzyme-induced calcite precipitation.
4.2.2 Inelastic mechanical response
Comparisons of the peak strength of sandstone rocks before and after bio-reinforcement indicate that the EICP-biocemented rocks cured at a lower temperature (31°C) showed a +213% increase in strength, whereas those cured at a higher temperature of 45°C showed a +220% increase in strength (Figure 11a,b). This contradicts our elastic response hypothesis, as crystallization dynamics and previous studies have suggested that rapid cooling at higher temperatures limits crystal growth and lower temperatures promote the precipitation of larger, more well-defined crystals (Cashman, 1993; Marsh, 1981; Mullin, 2001; Myerson, 2002). However, Myerson (2002) emphasizes that low temperature alone is insufficient for large crystal formation; slow cooling, urealytic activity, and the quantity of biocementation (Chen et al., 2024; Wang et al., 2024; Zhang et al., 2022) are also essential factors that control biocementation in rock masses. Unlike previous studies (Ngoma & Kolawole, 2024; Ngoma, Kolawole, Olorode et al., 2024), the current work utilized a lower urease concentration relative to previous EICP treatments (0.3 g/L vs. 2 g/L), which may explain why the rock masses cured at 31°C showed a marginally lower increase in strength (+213%) compared to the rocks cured with biocementation at 45°C (+220%), thus contradicting assumptions that lower temperature curing would yield more substantial improvement in biocemented rocks. Therefore, we can infer that in this case, temperature effects were negligible on the inelastic rock property changes due to biocementations. Nevertheless, despite using a relatively lower urease concentration in this study for biocementation in rocks, the results demonstrate that this quantity was still sufficient (up to +216% UCS and +170% E) to significantly enhance rock properties, even surpassing improvements reported in previous studies that utilized large urease amounts for EICP (Ngoma & Kolawole, 2024; Wang et al., 2024). This suggests that the higher pore volume of the rocks in this study provided more void space for effective biocementation. Consequently, other studies may have used more urease enzyme than necessary, especially given that our results indicate better reinforcement with a lower enzyme concentration. Therefore, urease enzyme dosage should be optimized based on the specific rock type and its inherent porosity to maximize efficiency in rock bio-mediated processes for biocementation.
It is also important to note that studies have often presented contradictory findings regarding the impact of temperature on geomaterials, with some suggesting that higher temperatures enhance urease activity, leading to improved biocementation (Park & Choi, 2021; Wang et al., 2022; Zhang et al., 2022), and others propose that lower temperatures (Xue et al., 2024) and urease inhibitors (Wang et al., 2023) are necessary to slow enzyme activity, which can reduce surface clogging and promote uniform precipitation within geomaterials, and lead to better biocementation overall. Additionally, these studies define high and low temperatures differently, with some considering values from 4 to 31°C as low temperatures, while others classify temperatures above 65°C as high. This shows the complex interplay between temperature and urease activity, suggesting that future work on biocementation in rocks should aim to identify an optimal balance (between temperature and urease activity) where precipitations can effectively penetrate the rock pores without prematurely clogging pores, ensuring better enhancement.
For the inelastic response of BP-EICP-biocemented rocks, the crystallization dynamics hypothesis holds, as rocks cured at a lower temperature (31°C) demonstrated a higher increase in strength (+219%) compared to those cured at 45°C (+199%) (Figure 11a,c). In this case, despite the lower urease concentration, the presence of SA biopolymer ensured more strength improvement in BP-EICP. The addition of biopolymer in the biocementation likely compensated for the limited urease, as its gelation process is temperature-dependent. At lower temperatures, calcium ion diffusion occurs gradually, forming a more structured and homogeneous gel, which enhances mechanical strength (Jeong et al., 2020). Conversely, at higher temperatures, gelation occurs more rapidly, leading to a less uniform, weaker gel. Additionally, higher temperatures reduce alginate viscosity, affecting crosslinking efficiency (Jeong et al., 2020). Therefore, unlike EICP-biocemented rocks, where the temperature effect is negligible, the BP-EICP-biocemented rocks were affected by temperature, and the presence of both urease enzyme and SA biopolymer played an important role in maintaining their peak strength.
The inelastic failure mode of rocks under compressive stress was also examined (Figure 12). These failure modes depend on the rock's internal structure and pre-existing weaknesses, due to the tendency of rocks to fail along the path of least resistance (weakest plane). Rocks under uniaxial compression typically fail through axial splitting or shear failure mode (Chakraborty et al., 2019; Fakhimi & Hemami, 2017; Fjær et al., 2021). Studies have shown that these failure modes are closely related to the strength (UCS) of the rock (Chakraborty et al., 2019; Hajiabdolmajid & Kaiser, 2003; Xie et al., 2024; Yagiz, 2008), because UCS determines a rock's ability to withstand axial stress before failure, and the failure mode describes how the material ultimately breaks under stress. Specifically, rocks with relatively higher UCS show minimal plastic deformation upon failure, typically failing through axial splitting due to their limited ability to accumulate large strain (Chakraborty et al., 2019; Xie et al., 2024). However, rocks with lower UCS often show shear failure, where material displacement occurs along the weakest planes (Chakraborty et al., 2019; Xie et al., 2024).
In this study, EICP-biocemented rocks cured at 31°C failed in the shear mode (Figure 12a), despite showing an increase in strength (UCS). This indicates that crystalline calcite reinforcement alone (without biopolymer gel) was insufficient to fully seal pre-existing microfractures. In contrast, BP-EICP-biocemented rocks cured at a lower temperature (31°C) recorded the highest increase in UCS (Figure 11a) and failed in the axial splitting mode (Figure 12c). This suggests that the combination of calcite precipitate and biopolymer gel provided stronger reinforcement, reducing the likelihood of shear deformation. We can therefore infer that with the addition of biopolymers (like in BP-EICP), additional urease enzyme, or extended biocementation treatment, the weakest zones (with discontinuities, cavities, and openings) in the rock masses can be more effectively biocemented, potentially shifting the failure mode from shearing to axial splitting. At higher curing temperature (45°C), both BP-EICP- and EICP-biocemented rocks showed a mix of shear and axial failure (Figure 12b,d), suggesting that calcite and calcium alginate gel precipitation do not always guarantee maximum biocementation of microfractures at this temperature. Moreover, it is important to note that since the specific sandstone rocks (Berea sandstone) analyzed in this work are heterogeneous, the presence of laminations and the distribution of microfractures in the rock may have varied among specimens, resulting in the observation of different failure patterns after biocementation. In some rocks, complete sealing of the pore network and microfractures may have occurred, while other rocks still retained fewer localized weak zones, leading to a mix of shear and axial failures after biocementation. A previous study (Wang et al., 2024) reported a complete shift from shear failure before biocementation to tensile failure after EICP treatment; however, our findings on enzymatic and biopolymer-modified biocemented rocks contradict this trend. A key distinction is that the results reported by Wang et al. (2024) may have been influenced by the artificially induced fractures during the rock specimen preparation in that study, which aligned parallel to the rock's longitudinal axis, thereby creating a pre-determined failure mode of axial splitting. However, our findings in this current work suggest that failure modes in biocemented rocks are more complex and can vary between axial and shear failure depending on the curing temperature, urease activity, rock heterogeneity, and biocementation type.
Although this work offers valuable first insights on the potential effect of biopolymer-modified EICP on the mechanical response of weak rock masses under varying curing regimes, there are a few limitations that should be addressed to further improve on this technique as follows: (i) the number of tested specimens could be increased and (ii) a wider temperature range could be considered for curing regime studies. Despite the constraints, the results show that EICP and BP-EICP can significantly influence rock behavior and improve the strength under controlled curing regimes. This knowledge provides a baseline understanding for future work to further explore the influence of biocementations on different rocks mass types under field-specific conditions. Additionally, the applicability of this work may be extended beyond the rock mass type used in this study, as previous studies (Ngoma, Kolawole, & Lu, 2024; Ngoma, Kolawole, Olorode et al., 2024) have shown that the effectiveness of biocementation also depends on the inherent porosity, mineralogy, and bedding orientation of rocks. These findings suggest that extending BP-EICP to other lithologies is feasible and will require careful consideration of mineralogical compatibility and pore structure.
5 CONCLUSIONS
1.
Mechanical enhancement: BP-EICP significantly improved both the bulk stiffness (↑187%) and the UCS (↑210%) of treated rock masses, whereas EICP alone showed comparable enhancements (↑178% E; ↑216% UCS), confirming the effectiveness of both biocementation techniques.
b.
Temperature sensitivity in BP-EICP: For BP-EICP, lower curing temperatures led to greater mechanical improvements (↑192% E; ↑220% UCS) compared to those cured at higher temperatures (↑178% E; ↑199% UCS), highlighting the temperature sensitivity of the biopolymer-enhanced process.
c.
Temperature effects in EICP: While EICP also showed substantial mechanical gains, the influence of curing temperature was minimal (E: ↑169% at low vs. ↑165% at high; UCS: ↑213% at low vs. ↑219% at high), suggesting that the biopolymer component in BP-EICP plays a more dominant role in temperature-dependent performance.
d.
Modulus Ratio: Both EICP and BP-EICP treatments resulted in a reduction in the modulus ratio, with minimal influence from curing temperature. However, the type of biocementation had a more pronounced effect, with EICP leading to a 20% decrease in MR, while BP-EICP induced a 13% reduction, indicating that biocementation chemistry more strongly influences stiffness alteration than thermal conditions.
e.
Rock failure modes: Failure mechanisms varied with treatment type and curing temperature; EICP-treated rocks cured at lower temperatures predominantly failed due to shearing. While those with high-temperature curing showed a mix of axial splitting and shearing, BP-EICP-treated rocks primarily failed through axial splitting, especially under low-temperature curing, highlighting the influence of biopolymer on fracture behavior.
Additionally, this study proposes the use of the average Young's modulus (Eavg) as a more reliable metric for evaluating stiffness in biocemented rock masses than the tangent modulus (Etan), particularly under varying curing conditions. The observed failure modes underscore the complex interplay between curing temperature, urease activity, material heterogeneity, and biomediation type. Overall, this work underscores the importance of curing temperature, biocementation type, and rock heterogeneity in determining the mechanical performance and failure behavior of biocemented rock masses. These findings contribute to a new understanding of how to optimize biocementation strategies for enhancing the stability of rock masses in deep underground applications in natural and built environments.
ACKNOWLEDGMENTS
This work was supported by the Faculty Development and Research Internal Grant awarded by the Newark College of Engineering (NCE), New Jersey Institute of Technology (NJIT), USA, to Oladoyin Kolawole.
CONFLICT OF INTEREST STATEMENT
The authors declare no conflicts of interest.
Biography
Oladoyin Kolawole is an assistant professor of Geomechanics and Geotechnical Engineering in the Department of Civil and Environmental Engineering at the New Jersey Institute of Technology (NJIT), USA, and also the faculty coordinator for the Geosystems Minor program at NJIT. He is the director of the Geomechanics for Geo-Engineering and Sustainability (GGES) Lab. He received his PhD in Petroleum Engineering with specialization in Geomechanics from Texas Tech University, USA. His interest lies in experimental and computational studies to fundamentally understand and predict the multiscale mechanical behavior and physical attributes of rocks and soils to address problems related to natural and built infrastructure, geosystems, energy, and hazard mitigation. He is a recipient of the 2022 Future Leader Award and the 2021 Distinguished Service Award from the American Rock Mechanics Association (ARMA). He is a member of the Committee on Geological and Geotechnical Engineering (COGGE) at the U.S. National Academies. He has authored and co-authored several peer-reviewed journal articles and conference papers on geomechanics and geotechnical engineering. He is an Editorial Board Member of Springer Nature's Discover Civil Engineering journal and volunteers as a peer reviewer for reputable rock mechanics and geotechnical engineering journals.
附件【Deep Underground Science and Engineering - 2026 - Ngoma - Mechanistic insights across curing regimes for enzymatic and.pdf】