Acta Geotechnica (2021) 16:481–489 https://doi.org/10.1007/s11440-020-01043-2 (0123456789().,-volV)(0123456789(). ,- volV) RESEARCH PAPER One-phase-low-pH enzyme induced carbonate precipitation (EICP) method for soil improvement Ming-Juan Cui1 • Han-Jiang Lai1 • Tung Hoang1 • Jian Chu1 Received: 25 March 2020 / Accepted: 18 July 2020 / Published online: 29 July 2020 Ó Springer-Verlag GmbH Germany, part of Springer Nature 2020 Abstract Enzyme induced carbonate precipitation (EICP) is an emerging soil improvement method using free urease enzyme for urea hydrolysis. This method has advantages over the commonly used microbially induced carbonate precipitation (MICP) process as it does not involve issues related to bio-safety. However, in terms of efficiency of calcium carbonate production, EICP is considered lower than that of MICP. In this paper, a high efficiency EICP method is proposed. The key of this new method is to adopt a one-phase injection of low pH solution strategy. In this so-called one-phase-low-pH method, EICP solution consisting of a mixture of urease solution of pH = 6.5, urea and calcium chloride is injected into soil. The test results have shown that the one-phase-low-pH method can improve significantly the calcium conversion efficiency and the uniformity of calcium carbonate distribution in the sand samples as compared with the conventional two-phase EICP method. Furthermore, the unconfined compressive strength of sand treated using the one-phase-low-pH method is much higher than that using the two-phase method and the one-phase-low-pH method is also simpler and more efficient as it involves less number of injections. Keywords Bacteria Calcium conversion efficiency Soil improvement Strength Urease 1 Introduction Biocementation is emerging to be a new soil improvement method. This method relies mainly on the production of calcium carbonate in soil as the cementing material to cement the soil particles together to increase the shear resistance [42] and fill in the pores to reduce the permeability of soil. There are mainly two approaches for the calcium carbonate production via urea hydrolysis: a) microbially induced carbonate precipitation (MICP) with urease-producing bacteria [1, 2, 22, 28, 36, 40, 46, 47]; and b) enzyme induced carbonate precipitation (EICP) using free urease enzyme [4, 15, 18, 19, 21, 31, 33, 37, 41, 45]. Compared with the MICP method, the EICP method is free from issues related to bio-safety and oxygen availability and can be used for soil with finer particles [21, 24, 45]. & Jian Chu [email protected] 1 School of Civil and Environmental Engineering, Nanyang Technological University, 10 Blk N1, 50 Nanyang Ave., Singapore 639798, Singapore In the previous studies, there are mainly two methods used for EICP treatment: (a) pre-mixing method [3, 4, 35, 39, 49]; and (b) percolation method [17, 20, 21, 32–34]. The pre-mixing method was conducted by mixing urease powder or EICP solution (mixture of urease, calcium and urea) with soil and then putting the mixed soil into a sampling mould. This method is difficult to be used for treating soil in situ [49]. The percolation method was conducted by injecting urease solution and cementation solution either one solution after another [21] or both solutions simultaneously [3]. The former is called a two-phase method and the later a one-phase method. Hoang et al. [21] reported that the amount of precipitated calcium carbonate of EICP-treated sand was only about half that of MICP for the same number of treatments. The calcium conversion efficiency of EICP treatment reported in the literature was generally low. Almajed et al. [3] reported that the calcium conversion efficiency of EICP was about 70–95% after 7 days of curing using cementation solution containing 0.67 M calcium and 1.0 M urea. Thus, more treatments are required for EICP than for MICP to precipitate the same amount of calcium carbonate. The 123 482 Acta Geotechnica (2021) 16:481–489 EICP based soil improvement methods can be much improved if the efficiency of the calcium carbonate production in EICP can be increased. In this paper, a one-phase-low-pH method was adopted to improve the efficiency of calcium carbonate production in the EICP process. To verify the effectiveness of the onephase-low-pH method hereafter, a comparative study between sand columns treated using one-phase-low-pH and two-phase methods was conducted. The data obtained from this study were also compared with published data using EICP-based method. The scanning electron microscopy (SEM) images were examined to reveal the microscopic difference between the EICP- and MICP-treated sand. one-phase-low-pH MICP or EICP method is as follows: (1) preparing MICP (or EICP) solution by mixing the bacterial solution (pH = 6.5) [or urease solution (pH = 6.5)] with CS (2.0 M) and distilled water using a volume ratio of bacterial (or urease) solution: CS: distilled water = 0.3: 0.5: 0.2 to achieve a CS final concentration of 1.0 M; (2) injecting MICP (or EICP) solution into a sand column immediately and incubating the sand at room temperature (25 ± 1 °C) for 24 h; and (3) repeating the above steps until achieving the required number of treatments. For comparison, the twophase method was also used to treat sand columns using either EICP or MICP by injecting one pore volume of bacterial (or urease) solution, followed by injecting the same volume of CS of 1.0 M after 6 h of fixation time for bacteria (or urease). 2 Materials and methods 2.3 Properties tests 2.1 Materials In this study, Sporosarcina pasteurii (OD600 = 3.6 ± 0.3, urease activity UA = 20 ± 1 U/mL) was used for MICP treatment and urease (UA = 40 ± 1 U/mL) extracted from bacteria via ultrasonication was used for EICP treatment. 750 Watt ultrasonic processor (VCX 750) with 20 kHz in frequency was used in this study to extract urease from bacteria through the ‘‘run-cool’’ cycle. During the extraction, the temperature of bacterial solution was kept lower than 35 °C. The soil used was clean Ottawa 20–30 sand (Gs = 2.65, D50 = 0.72 mm, Cu = 1.2, emax = 0.742 and emin = 0.502). Equal mole of CaCl2 and urea were used as cementation solution which will be termed as CS hereafter. Titration method was adopted to measure the calcium concentration of the effluent after each treatment using a standard solution of EDTA (ethylenediaminetetraacetic acid) [9]. After completing the EICP or MICP treatment, all samples were flushed by distilled water at least 5 cycles to remove the residual substances. The samples were then saturated and used for unconfined compression (UC) tests to measure the unconfined compressive strength under a loading rate of 1.0 mm/min [5]. After the UC test, all fractions of the tested sample were collected and dried in an oven with a temperature of 105 °C. The acid dissolving method [12, 44] was adopted to determine the Calcium Carbonate Content (CCC) of each sample. Scanning electron microscopy (SEM) tests were also conducted. 2.2 Sand specimen treatment The test program is summarised in Table 1. Poly vinyl chloride (PVC) tube was used as the mould to prepare sand specimens of 50 mm in diameter and 100 mm in height. All tests were triplicated for repeatability. The one-phase-lowpH injection method [7] was adopted in this study for both MICP and EICP treatment. Hydrochloric acid (HCl) with a concentration of 2.0 M was used to adjust the pH of bacterial or urease solution. The procedure for the application of the 3 Results and discussion 3.1 Comparison of one-phase-low-pH and twophase method Figure 1 shows the results of EICP and MICP treatment for sand using either one-phase-low-pH or two-phase methods. It can be seen that the Calcium Conversion Efficiency Table 1 Sand column treatment test details Test Injection method Bacteria volume ratio VRa MICP-2b Two-phase 1.0 EICP-2 MICP-1 Urease volume ratio VR Calcium concentration, M Number of treatments, N 1.0 1, 2, 3, 4 1.0 1, 2, 3, 4 1.0 One-phase-low-pH EICP-1 a 0.3 0.3 The bacteria or urease volume ratio VR is the ratio of the injected bacteria or urease to the pore volume of sand column MICP-2 or EICP-2 refers two-phase MICP or EICP method and MICP-1 or EICP-1 one-phase-low-pH MICP or EICP method b 123 Acta Geotechnica (2021) 16:481–489 (CCE) (Fig. 1a), which is the ratio of calcium consumed to total calcium supplied for each treatment, and Calcium Carbonate Content (CCC) (Fig. 1b) of sand treated by EICP and MICP using the one-phase-low-pH method were higher than that using the two-phase method. However, the amount of bacteria or urease for each injection using twophase method is greater than that using one-phase-low-pH method. The low CCE and CCC for the two-phase method are possibly due to the fact that most of the injected bacteria or urease would be flushed out during the CS injection. In general, there are three mechanisms for the bacteria or urease to be retained in soil: (1) the adsorption capacity of bacteria or urease; (2) the filtration capacity of soil; and (3) the retention ability of other media such as the precipitated calcium carbonate. The adsorption capacity of bacterial cells or urease enzymes depends on its own characteristics. The bacterial cells are considered as negatively charged [50] and thus will be attracted to the soil 483 particle surface. The filter capacity of soil relies on its physical properties of the soil (e.g., grain sizes and particle gradation) and the sizes of bacterial cells. Soil with smaller particle sizes and good gradation has a better filter capacity. The larger bacterial cells are more likely to be trapped in soil. For the one-phase-low-pH method, all three mechanisms will contribute to the retention of bacterial cells or urease enzymes. For the two-phase method, the bacterial cells or urease enzymes are retained through the first two mechanisms during the injection of bacterial or urease solution. However, during the injection for CS, the seepage force causes the flushing out of some bacterial cells or urease enzymes. Moreover, for the tests using the two-phase method, the CCE for the EICP treatment (Test EICP-2) is much lower than that for the MICP treatment (Test MICP-2). However, when the one-phase-low-pH method is used, the CCE are high for both the EICP treatment (Test EICP-1) and MICP treatment (Test MICP-1). The possible reason for the low Fig. 1 Comparison of EICP and MICP treatments of sand using either the two-phase or the one-phase-low-pH method: a calcium conversion efficiency (CCE) versus number of treatments; b calcium carbonate content (CCC) versus number of treatments; c calcium carbonate content (CCC) in each test after 4 treatments; and d unconfined compressive strength versus number of treatments 123 484 Acta Geotechnica (2021) 16:481–489 Fig. 2 Comparison of Calcium carbonate content (CCC) in sand treated by EICP and MICP using the one-phase-low-pH method: a CCC versus number of treatments; and b CCC distribution at different positions within a treated sand column Fig. 3 Comparison of the relationship between unconfined compressive strength and calcium carbonate content for EICP- and MICPtreated sand columns using one-phase-low-pH method CCE for the two-phase method using the EICP treatment is that more (or higher proportion of) urease would be flushed out of the sand column during the CS injection. This can be explained by the following two reasons: (1) the attachment of urease to sand grains is weaker than bacterial cells and (2) the sizes of urease are smaller than the sizes of bacterial cells and thus the retention for urease is lower. The CCC distribution of EICP- and MICP-treated sand using either one-phase-low-pH or two-phase methods is shown in Fig. 1c. It can be seen that the CCC distribution of EICP and MICP treatment using one-phase-low-pH method is uniform, but non-uniform for the two-phase method. The CCC at the top (i.e., the region close to injection point) of the sand column is the lowest for both EICP and MICP treatment using two-phase method. The different distribution patterns of calcium carbonate for both methods indicate that the onephase-low-pH method contributes to improve the uniformity 123 of calcium carbonate distribution. Thus, the unconfined compressive strength of sand column treated by EICP and MICP using the one-phase-low-pH method is higher than that using the two-phase method (Fig. 1d). In conclusion, the higher CCE and more uniform distribution of calcium carbonate obtained from tests using the one-phase-low-pH method produce higher unconfined compressive strength compared with the two-phase method for both the MICP and EICP treatments. However, it has to be pointed out that not all the one-phase methods will work. This is because MICP (or EICP) will take place as soon as the bacterial (or urease) solution is mixed with the CS solution. This will cause clogging at the injection side and prevent the transmission of the CS solution in the soil, resulting in non-uniform of calcium carbonate distribution [19, 26, 27, 48]. However, this difficulty can be overcome by using low pH (6.5) bacterial or urease solutions as suggested by Cheng et al. [7] or using low activity bacterial solution as demonstrated by Chu and Wen [11]. 3.2 Comparison of EICP and MICP treatment using the one-phase-low-pH method Figure 2a shows a comparison of the CCC obtained after each of EICP and MICP treatment of sand columns using the one-phase-low-pH method in different number of treatments. The CCC obtained in both treatments are almost identical. It can be seen that the CCC increases with the increase in the number of treatments for both the EICP- and MICP-treated sand. The calcium in the effluent of each EICP and MICP treatment were ignorable, meaning that the injected calcium solution for each treatment could be converted to calcium carbonate almost completely after 24 h incubation via the one- Acta Geotechnica (2021) 16:481–489 485 Fig. 4 Comparison of SEM images of sand treated by EICP and MICP using the one-phase-low-pH method: a EICP-1 at CCC= 2.4% after one treatment; b MICP-1 at CCC= 2.3% after one treatment; c EICP-1 at CCC= 4.4% after two treatments; d MICP-1 at CCC= 4.3% after two treatments; e EICP-1 at = 8.4% after four treatments; f MICP-1 = 8.7% after four treatments phase-low-pH method. Moreover, the distribution of CCC in EICP- and MICP-treated sand columns is similar and uniform (Fig. 2b). The unconfined compressive strength (quc) of EICP- and MICP-treated sand columns is plotted versus calcium carbonate content (CCC) in Fig. 3. As expected, quc increases with increasing in CCC for both. However, quc obtained from the EICP treatment is greater than that from the MICP treatment for the same CCC. Similar observations have also been reported by Almajed et al. [4] and Hoang et al. [21]. One explanation for the above difference in the quc versus CCC relationships was given by Hoang et al. [21] as the difference in the deposition location of the precipitated calcium carbonate. However, this deposition difference is not significant in the current study. SEM images of both the EICP- and MICP-treated sand using the one-phase-low-pH method at different CCC are compared in Fig. 4. It can be seen that the calcium carbonate crystals were formed on sand particles in both cases. Two major differences have been observed from the SEM images. Firstly, the morphology of the calcium carbonate crystals formed in the 123 486 Acta Geotechnica (2021) 16:481–489 Fig. 5 Comparison of one-phase-low-pH EICP with published EICP treatments for sand: a relationship between calcium carbonate content (CCC) and number of treatments N; and b relationship between unconfined compressive strength quc and CCC; c relationship between unconfined compressive strength quc and number of treatments N two different treatments is different. For EICP treatment, mainly rhombic calcium carbonate crystals are observed (Fig. 4a, c, e), whereas for MICP treatment, both rhombic and spherical calcium carbonate crystals dominate (Fig. 4b, d, or f). Both types of calcium carbonate crystals have been observed by other researchers [1, 8, 14, 23, 29, 38]. By examining the crystals in Fig. 4a more closely, it can be seen that each rhombic crystal consists of a number of smaller cubic or prismatic shaped calcium carbonate crystals, suggesting the rhombic crystals were more closely related to calcite as also pointed by Declet et al. [13]. Gebauer et al. [16] have reported that calcite is a more stable polymorph of calcium carbonate and likely possesses a higher binding strength in the clusters than other types. Khodadadi et al. [25] also reported that the less stable calcium carbonate mineral phases may not be as effective at improving the mechanical properties of the soil. Furthermore, the surface of the spherical crystals is smooth and thus its contribution to interlocking might not be as high as the rhombic type of crystals. 123 Secondly, the sizes of calcium carbonate crystals are also different. The sizes of the calcium carbonate crystals induced by EICP are smaller than that by MICP at the similar CCC, as shown by a comparison of Fig. 4c with Fig. 4d, which is consistent with the finding of Nafisi et al. [30]. The difference in the sizes of the crystals is related to the sizes of bacterial cells or urease enzymes and the crystallisation rate of calcium carbonate. As the sizes of bacterial cell (within the range of 500–3000 nm [43]) are much bigger than those of urease enzyme (about 12 nm [6]), the calcium carbonate crystals formed with bacterial cells as nuclei [10] in MICP are much bigger than those with urease enzyme as nuclei in EICP. In terms of crystallisation rate, as the urea hydrolysis rate in EICP is quicker, but shorter than that in MICP, the crystallisation rate of calcium carbonate by EICP treatment would be faster and the duration would be shorter than that of MICP. Consequently, the calcium carbonate crystals formed during each EICP treatment (Fig. 4c) would be smaller. If the same amount of calcium carbonate content (CCC) is Acta Geotechnica (2021) 16:481–489 487 Table 2 Summary of the published EICP methods Urease Treatment method Treatment solution Treatment intervals Samples for UC test References Jack bean Percolation method. Add EICP solution from top of sand column EICP solution: 0.67 M CaCl2, 1.0 M urea, 3 g/ L enzyme 7 days Oven-dried at 50 °C Almajed et al. [3] 3 days Oven-dried at 40 °C Almajed et al. [4] Premixing method. Mix sand with EICP solution Selfextracted from bacteria Circulated-percolation process including 4 steps: (1) circulated percolation of urease (3 h); (2) drain off the pore volume urease; (3) circulated percolation of CS (9–12 h); (4) flush with deionized water (2 h), then drain off all liquid (10 h) Urease: 25.4 mM urea/ min; CS: 0.3 M CaCl2, 0.3 M urea 24–27 h Oven-dried at 50 °C for 48 h Hoang et al. [20, 21] Jack bean Inject EICP solution through the injection tube preembedded in sand EICP solution: 1.0 M CaCl2, 1.0 M urea, 15 g/L urease 24 h Wet Neupane et al. [33] Selfextracted from jack bean Pre-mixing method including 4 steps: (1) mixing jack bean extract with urea (3 days); (2) adding calcium to yield calcite solution: (3) mixing sand with calcite solution and compacting into mould; (4) air curing – 3 days Wet Park et al. [37] Jack bean Pre-mixing method including 3 steps: (1) pluviating sand into mould after well-mixing with urease powder; (2) evacuating and applying 50 kPa confining pressure on sand sample; (3) injecting CS solution CS: (1) 0.5 M CaCl2, 0.5 M urea; (2) 1.0 M CaCl2, 1.0 M urea 24 h Dry Yasuhara et al. [49] achieved in each EICP and MICP treatment, then the number of calcium carbonate crystals will be more. In other words, there will be more contact points for cementation in EICP than those in MICP for the same CCC. As biocementation of calcium carbonate between the adjacent soil particles contributes to enhance the strength and stiffness properties of soil [22], the more cementation points of calcium carbonate will produce higher strength for EICP. In summary, the difference in strength enhancement of sand treated by EICP and MICP could also be explained by the differences in the properties of the calcium carbonate crystals and the number and sizes of the crystals. 3.3 Comparison of one-phase-low-pH EICP with published EICP treatment methods The calcium carbonate content (CCC) and unconfined compressive strength (quc) versus number of treatments obtained from the one-phase-low-pH EICP method in this study is compared with those from the published EICP methods [3, 4, 20, 21, 33, 37, 49], as shown in Fig. 5. Information about the published EICP methods is summarised in Table 2. It can be seen from Fig. 5a that the calcium carbonate production in this study is higher compared with three others under the same number of treatments [3, 4, 20, 21, 49]. Figure 5b shows that the quc obtained from this study is similar to the results of Almajed et al. [3, 4] and Hoang et al. [20, 21], but higher than the cases in the published studies [33, 37, 49] under the same CCC. As the number of treatments required is less in the one-phase-lowpH EICP method to achieve the same CCC, it implies that for the same number of treatments, the quc will be higher. This is indeed the case as shown in Fig. 5c. However, it needs to be pointed out that quc is also affected by other factors such as concentration of bacterial or cementation solutions used and thus the data in Fig. 5b and c are scattered. 4 Conclusions In this paper, a one-phase-low-pH EICP method was proposed to improve the efficiency of calcium carbonate production for EICP. In this method, the EICP-solution consisting of a mixture of low pH urease solution (pH = 6.5) and cementation solution (calcium chloride and urea) is injected together into soil. The following conclusions can be drawn from this study: 1. A higher calcium conversion efficiency and more uniform distribution of calcium carbonate in the soil specimens treated was achieved using the one-phaselow-pH EICP method compared with that using a twophase method, and thus producing higher unconfined compressive strength. 2. When the one-phase-low-pH method is adopted, the efficiency of calcium carbonate production for EICP and MICP is almost the same. The injected calcium of 123 488 each treatment could be converted almost completely to calcium carbonate after 24 h incubation. The unconfined compressive strength of the sand column with EICP treatment is greater than that of MICP treatment for the same calcium carbonate content. This can be explained by the differences in the types of calcium carbonate crystals and the sizes of the crystals. 3. Compared with the published EICP treatment methods, the one-phase-low-pH method proposed in this study is more effective as it results in a higher shear strength and simpler as the number of injections is reduced by half given the other conditions the same. Acknowledgements The authors would like to thank Dr Xiaoniu YU of Nanyang Technological University, Singapore, for the discussion with him. The financial supports provided through Grant No. MOE2015-T2-2-142 by the Ministry of Education, Singapore, and the Grant No. SMI-2018-MA-02 by the Singapore Maritime Institute are gratefully acknowledged. The first two authors would also like to thank the support by the National Natural Science Foundation of China (NSFC) (No. 51708243) and the China Postdoctoral Science Foundation (Nos. 2016M600595, 2018M632862 and 2018T110769) for the early stage of their research. References 1. Al Qabany A, Soga K, Santamarina C (2012) Factors affecting efficiency of microbially induced calcite precipitation. J Geotech Geoenviron Eng 138(8):992–1001 2. Al Qabany A, Soga K (2013) Effect of chemical treatment used in MICP on engineering properties of cemented soils. Géotechnique 63(4):331–339 3. Almajed A, Khodadadi TH, Kavazanjian E Jr (2018) Baseline investigation on enzyme-induced calcium carbonate precipitation. J Geotech Geoenviron Eng 144(11):04018081. https://doi. org/10.1061/(ASCE)GT.1943-5606.0001973 4. Almajed A, Khodadadi TH, Kavazanjian E Jr, Hamdan N (2019) Enzyme induced biocementated sand with high strength at low carbonate content. Sci Rep 9(1135):1–7. https://doi.org/10.1038/ s41598-018-38361-1 5. ASTM (American Society for Testing and Materials) D2166 (2013) Standard test method for unconfined compressive strength of cohesive soil. ASTM International, West Conshohocken 6. Blakely RL, Zerner B (1984) Jack bean urease: the first nickel enzyme. J Mol Catal 23:263–292 7. Cheng L, Shahin MA, Chu J (2019) Soil bio-cementation using a new one-phase low-pH injection method. Acta Geotech 14:615–626 8. Cheng L, Shahin MA, Mujah D (2016) Influence of key environmental conditions on microbially induced cementation for soil stabilization. J Geotech Geoenviron Eng 143(1):04016083 9. Choi SG, Park SS, Wu SF, Chu J (2017) Methods for calcium carbonate content measurement of biocemented soils. J Mater Civ Eng 29(11):06017015 10. Chu J, Ivanov V, Naeimi M, Stabnikov V, Liu HL (2014) Optimization of calcium-based bioclogging and biocementation of sand. Acta Geotech 9:277–285 11. Chu J, Wen ZY (2015) Proof of concept: biocement for road repair. In: Trans project reports 129 123 Acta Geotechnica (2021) 16:481–489 12. Cui MJ, Zheng JJ, Zhang RJ, Lai HJ, Zhang J (2017) Influence of cementation level on the strength behaviour of bio-cemented sand. Acta Geotech 12(5):971–986 13. Declet A, Reyes E, Suárez OM (2016) Calcium carbonate precipitation: a review of the carbonate crystallization process and applications in bioinspired composites. Rev Adv Mater Sci 44:87–107 14. Fujita Y, Ferris FG, Lawson RD, Colwell FS, Smith RW (2000) Subscribed content calcium carbonate precipitation by ureolytic subsurface bacteria. Geomicrobiol J 17(4):305–318 15. Gao YF, He J, Tang XY, Chu J (2019) Calcium carbonate precipitation catalyzed by soybean urease as an improvement method for fine-grained soil. Soils Found. https://doi.org/10.1016/ j.sandf.2019.03.014 16. Gebauer D, Völkel A, Cölfen H (2008) Stable prenucleation calcium carbonate clusters. Science 322(5909):1819–1822 17. Handley-Sidhu S, Sham E, Cuthbert MO, Nougarol S, Mantle M, Johns ML, Macaskie LE, Renshaw JC (2013) Kinetics of urease mediated calcite precipitation and permeability reduction of porous media evidenced by magnetic resonance imaging. Int J Environ Sci Technol 10(5):881–890 18. Hamdan N, Kavazanjian E Jr (2016) Enzyme-induced carbonate mineral precipitation for fugitive dust control. Géotechnique 66(7):546–555 19. He J, Gao YF, Gu ZX, Chu J, Wang LY (2020) Characterization of crude bacterial urease for CaCO3 precipitation and cementation of silty sand. J Mater Civ Eng 32(5):04020071 20. Hoang T, Alleman J, Cetin B, Choi SG (2020) Engineering properties of biocementation coarse- and fine-grained sand catalyzed by bacterial cells and bacterial enzyme. J Mater Civ Eng 32(4):04020030 21. Hoang T, Alleman J, Cetin B, Ikuma K, Choi SG (2019) Sand and silty-sand soil stabilization using bacterial enzyme—induced calcite precipitation (BEICP). Can Geotech J 56:808–822 22. Ivanov V, Chu J (2008) Applications of microorganisms to geotechnical engineering for bioclogging and biocementation of soil in situ. Rev Environ Sci Biotechnol 7(2):139–153 23. Ismail MA, Joer HA, Randolph MF, Meritt A (2002) Cementation of porous materials using calcite. Géotechnique 52(5):313–324 24. Jiang NJ, Yoshioka H, Yamamoto K, Soga K (2016) Ureolytic activities of a urease-producing bacterium and purified urease enzyme in the anoxic condition: implication for subseafloor sand production control by microbially induced carbonate precipitation (MICP). Ecol Eng 90:96–104 25. Khodadadi TH, Kavazanjian E, Bilsel H (2017) Mineralogy of calcium carbonate in MICP-treated soil using soaking and injection treatment methods. Geotech Front 2017:195–201 26. Mahawish A, Bouazza A, Gates WP (2018) Effect of particle size distribution on the bio-cementation of coarse aggregates. Acta Geotech 13(4):1019–1025 27. Martin KK, Khodadadi TH, Kavazanjian E Jr (2020) Enzymeinduced carbonate precipitation: scale-up of bio-cemented soil columns. Geo-Congress 2020:96–103 28. Martinez BC, Dejong JT, Ginn TR, Montoya BM, Barkouki TH, Hunt C, Tanyu B, Major D (2013) Experimental optimization of microbial-induced carbonate precipitation for soil improvement. J Geotech Geoenviron Eng 139:587–598 29. Mujah D, Cheng L, Shahin MA (2019) Microstructural and geomechanical study on biocemented sand for optimization of MICP process. J Mater Civ Eng 31(4):04019025 30. Nafisi A, Safavizadeh S, Montoya BM (2019) Influence of microbe and enzyme-induced treatments on cemented sand shear response. J Geotech Geoenviron Eng 145(9):06019008 31. Nam IH, Chon CM, Jung KY, Choi SG, Choi H, Park SS (2015) Calcite precipitation by ureolytic plant (Canavalia ensiformis) Acta Geotechnica (2021) 16:481–489 extracts as effective biomaterials. KSCE J Civ Eng 19(6):1620–1625 32. Nemati M, Voordouw G (2003) Modification of porous media permeability, using calcium carbonate produced enzymatically in situ. Enzyme Microb Technol 33(5):635–642 33. Neupane D, Yasuhara H, Kinoshita N, Ando Y (2015) Distribution of mineralized carbonate and its quantification method in enzyme mediated calcite precipitation technique. Soils Found 55(2):447–457 34. Neupane D, Yasuhara H, Kinoshita N, Unno T (2013) Applicability of enzymatic calcium carbonate precipitation as a soilstrengthening technique. J Geotech Geoenviron Eng 139(12):2201–2211 35. Oliveira PJV, Freitas LD, Carmona JPSF (2017) Effect of soil type on the enzymatic calcium carbonate precipitation process used for soil improvement. J Mater Civ Eng 29(4):04016263 36. Pan XH, Chu J, Yang Y, Cheng L (2020) A new biogrouting method for fine to coarse sand. Acta Geotech 15:1–16 37. Park SS, Choi SG, Nam IH (2014) Effect of plant-induced calcite precipitation on the strength of sand. J Mater Civ Eng 26(8):06014017 38. Rong H, Qian CX, Li LZ (2012) Influence of molding process on mechanical properties of sandstone cemented by microbe cement. Constr Build Mater 28(1):238–243 39. Simatupang M, Okamura M (2017) Liquefaction resistance of sand remediated with carbonate precipitation at different degrees of saturation during curing. Soils Found 57(4):619–631 40. Song JY, Sim Y, Jang J, Hong WT, Yun TS (2020) Near-surface soil stabilization by enzyme-induced carbonate precipitation for fugitive dust suppression. Acta Geotech 15:1967–1980. https:// doi.org/10.1007/s11440-019-00881-z 41. Sun XH, Miao LC, Tong TZ, Wang CC (2019) Study of the effect of temperature on microbially induced carbonate precipitation. Acta Geotech 14:627–638. https://doi.org/10.1007/s11440-0180758-y 489 42. Terzis D, Laloui L (2019) Cell-free soil bio-cementation with strength, dilatancy and fabric characterization. Acta Geotech 14(3):639–656 43. Tsesarsky M, Gat D, Ronen Z (2016) Biological aspects of microbial-induced calcite precipitation. Environ Geotech 5(2):69–78 44. Wang XR, Tao JL (2019) Polymer-modified microbially induced carbonate precipitation for one-shot targeted and localized soil improvement. Acta Geotech 14:657–671 45. Wen KJ, Li Y, Amini F, Li L (2020) Impact of bacteria and urease concentration on precipitation kinetics and crystal morphology of calcium carbonate. Acta Geotech 15:17–27 46. Whiffin VS, Van Paassen LA, Harkes MP (2007) Microbial carbonate precipitation as a soil improvement technique. Geomicrobiol J 24(5):417–423 47. Wu CZ, Chu J, Cheng L, Wu SF (2019) Biogrouting of aggregates using premixed injection method with or without pH adjustment. J Mater Civ Eng 31(9):06019008 48. Wu CZ, Chu J, Wu SF, Cheng L, van Paassen LA (2019) Microbially induced calcite precipitation along a circular flow channel under a constant flow condition. Acta Geotech 14:673–683 49. Yasuhara H, Neupane D, Hayashi K, Okamura M (2012) Experiments and predictions of physical properties of sand cemented by enzymatically-induced carbonate precipitation. Soils Found 52(3):539–549 50. Zita A, Hermansson M (1994) Effects of ionic strength on bacterial adhesion and stability of flocs in a wastewater activated sludge system. Appl Environ Microbiol 60(9):3041–3048 Publisher’s Note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations. 123