CN111893988A - A kind of microbe-induced silty fine sand consolidation soft soil roadbed ecological improvement method - Google Patents

A kind of microbe-induced silty fine sand consolidation soft soil roadbed ecological improvement method Download PDF

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CN111893988A
CN111893988A CN202010897366.9A CN202010897366A CN111893988A CN 111893988 A CN111893988 A CN 111893988A CN 202010897366 A CN202010897366 A CN 202010897366A CN 111893988 A CN111893988 A CN 111893988A
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方明镜
周然
夏齐勇
颜廷舟
郭峰祥
胡良年
曾勇
刘政伟
荣克明
危文康
郝刚
易毅
许梁
丁洁
廖斌
钱媛媛
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Abstract

本发明提供一种微生物诱导粉细砂固结软土路基生态改良方法,其中微生物采用巴氏芽孢杆菌,菌种开始为冻干粉,在培养液中进行细菌活化和培养,得到巴氏芽孢杆菌浓缩液;然后向软土中拌入粉细砂,粉细砂拌和比例在10‑20%,粉细砂为软土路提供大粒径骨料;将巴氏芽孢杆菌浓缩液掺入营养液中注入砂土路基,再注入固结液,直至路基未达到预期目标。本发明应用交叉学科,使用生物化学技术处理软土路基,克服了传统物理和化学方法处理路基的高污染、高能耗等问题,既能实现对软土路基的强化处理,又减少了环境污染和能耗问题。

Figure 202010897366

The invention provides a microorganism-induced powder fine sand consolidation soft soil roadbed ecological improvement method, wherein the microorganism adopts Bacillus pasteurii, the strain starts as freeze-dried powder, and the bacteria are activated and cultured in the culture solution to obtain the Bacillus pasteurii Concentrate; then mix silt and fine sand into the soft soil, and the mixing ratio of silt and fine sand is 10-20%, and the silt and fine sand provides large-diameter aggregate for the soft soil road; mix the Bacillus pasteurii concentrate into the nutrient solution Inject the sand subgrade into the middle, and then inject the consolidation liquid until the subgrade does not reach the expected target. The invention applies interdisciplinary and uses biochemical technology to treat the soft soil roadbed, overcomes the problems of high pollution and high energy consumption of the traditional physical and chemical methods to deal with the roadbed, and can not only realize the strengthening treatment of the soft soil roadbed, but also reduce environmental pollution and pollution. energy consumption issues.

Figure 202010897366

Description

一种微生物诱导粉细砂固结软土路基生态改良方法A kind of microbe-induced silty fine sand consolidation soft soil roadbed ecological improvement method

技术领域technical field

本发明涉及微生物诱导碳酸钙沉淀加固路基技术领域,具体涉及一种微生物诱导粉细砂固结软土路基生态改良方法。The invention relates to the technical field of microbe-induced calcium carbonate precipitation reinforcement roadbed, in particular to a microbe-induced silty sand consolidation soft soil roadbed ecological improvement method.

背景技术Background technique

软土路基,在日益增加的交通荷载(高速,重载)往复作用下,其疲劳寿命和工作性能不容乐观。如果路基土的承载力劣化与不足,甚至发生液化,则可能会引起与液化相关的工程灾害,如路基沉陷、地下管道及隧道的上浮、边坡失稳以及海岸或河岸的过度侵蚀等病害,影响其交通运输功能的发挥。Soft soil subgrade, under the reciprocating action of increasing traffic load (high speed, heavy load), its fatigue life and working performance are not optimistic. If the bearing capacity of the subgrade soil is degraded and insufficient, or even liquefies, it may cause engineering disasters related to liquefaction, such as subsidence of subgrade, floating of underground pipes and tunnels, slope instability, and excessive erosion of coasts or river banks. affect its transportation function.

传统的液化路基整治的方法有待改进与提高。比如土工织物加固技术存在耐久性不足的问题;基于水泥、石灰或有机胶的化学灌浆属高耗能和高排放产业;而路基土置换、桩基和强夯等物理加固方法技术经济性低,且在建成区施工成本高,大型施工机具受限。机械压实和化学灌浆是目前土体加固处理应用最为广泛的两种方式,但其高成本、高能耗以及对环境污染和破坏的缺点促使了对新型土体加固技术的探索。The traditional liquefaction roadbed remediation methods need to be improved and improved. For example, geotextile reinforcement technology has the problem of insufficient durability; chemical grouting based on cement, lime or organic glue is a high energy consumption and high emission industry; and physical reinforcement methods such as subgrade soil replacement, pile foundation and dynamic compaction are technically economical. Moreover, the construction cost in the built-up area is high, and the large-scale construction equipment is limited. Mechanical compaction and chemical grouting are the two most widely used methods for soil reinforcement treatment, but their high cost, high energy consumption, and the shortcomings of environmental pollution and damage have prompted the exploration of new soil reinforcement technologies.

发明内容SUMMARY OF THE INVENTION

本发明要解决的问题在于针对上述技术存在的不足,提供一种微生物诱导粉细砂固结软土路基生态改良方法。微生物采用巴氏芽孢杆菌,这种细菌是非致病性菌,用尿素水解的微生物诱导碳酸钙沉淀时,不需要引入外来微生物,有助于保持原有土壤生态环境,并且在一定的恶劣环境(如,酸碱,高盐度等)条件下,都能保持较强的生物活性。首先将粉细砂拌入软土路基中,改良路基土体结构,拌入粉细砂够的土体既含有一定数量的粗颗粒,使之具有足够的强度和水稳定性,又含有一定数量的细颗粒,能将粗颗粒粘结在一起,但细砂土易松散,对流水冲刷抵抗能力差,需要参配粘结物质,加强其稳定性。微生物诱导碳酸钙沉积(MICP)过程产生的碳酸钙沉淀具有一定的胶结功能,可以把砂土颗粒粘结到一起,改良土壤的工程性能,该项技术可以显著改善土体强度、刚度、渗透性,并且相比于传统土体改良工艺,其低能耗、低扰动、环境友好型特点更加符合可持续发展理念。The problem to be solved by the present invention is to provide a microorganism-induced silty sand consolidation soft soil roadbed ecological improvement method in view of the deficiencies of the above technologies. The microorganism adopts Bacillus Pasteurella, which is a non-pathogenic bacteria. When using urea-hydrolyzed microorganisms to induce calcium carbonate precipitation, there is no need to introduce foreign microorganisms, which helps to maintain the original soil ecological environment, and in a certain harsh environment ( Such as, acid-base, high salinity, etc.) conditions, can maintain strong biological activity. First, mix the silty sand into the soft soil subgrade to improve the soil structure of the subgrade. The soil mixed with enough silty sand not only contains a certain amount of coarse particles to make it have sufficient strength and water stability, but also contains a certain amount of The fine particles can bond the coarse particles together, but the fine sand is easy to loosen and has poor resistance to scouring by flowing water. The calcium carbonate precipitate produced by the microorganism-induced calcium carbonate deposition (MICP) process has a certain cementing function, which can bond the sand particles together and improve the engineering performance of the soil. This technology can significantly improve the strength, stiffness, and permeability of soil. , and compared with the traditional soil improvement process, its low energy consumption, low disturbance, and environment-friendly characteristics are more in line with the concept of sustainable development.

本发明为解决现有技术中存在的问题采用的技术方案如下:The technical scheme adopted by the present invention for solving the problems existing in the prior art is as follows:

一种微生物诱导粉细砂固结软土路基生态改良方法,其特征在于:首先向软土颗粒中拌和粉细砂,改良路基土体结构,其次向砂土中,传输菌液以及尿素和钙源等营养盐,从而使砂土孔隙中,尤其是砂土颗粒间被碳酸钙填充和胶凝,砂土孔隙中快速析出的碳酸钙胶凝结晶使软土路基固结改良,承载力提高,路基力学性能得到极大改善,具体步骤如下:A method for ecological improvement of soft soil roadbed by microbe-induced silt and fine sand consolidation is characterized in that: firstly, the silty fine sand is mixed with soft soil particles to improve the structure of the roadbed soil, and secondly, bacterial liquid, urea and calcium are transferred to the sandy soil Therefore, the pores of the sand, especially the sand particles, are filled and cemented with calcium carbonate, and the cemented crystallization of calcium carbonate rapidly precipitated in the pores of the sand can improve the consolidation of the soft soil roadbed and increase the bearing capacity. The mechanical properties of the subgrade have been greatly improved. The specific steps are as follows:

步骤1、微生物的活化与培养:微生物采用巴氏芽孢杆菌,是一种好氧的革兰氏阳性菌,能在新陈代谢过程中产生大量脲酶,菌种开始为冻干粉,在培养液中进行细菌活化和培养,得到巴氏芽孢杆菌浓缩液;Step 1. Activation and cultivation of microorganisms: The microorganisms are Bacillus Pasteurella, an aerobic gram-positive bacteria that can produce a large amount of urease during the metabolic process. Bacterial activation and cultivation to obtain pasteurized bacillus concentrate;

步骤2、加入粉细砂:向软土中拌入粉细砂,粉细砂拌和比例应在10-20%,粉细砂主要为软土路提供大粒径骨料,其目的在于改善路基土体结构、提高路基强度;Step 2. Add silt and fine sand: Mix silt and fine sand into the soft soil. The mixing ratio of silt and fine sand should be 10-20%. The silt and fine sand mainly provides large-sized aggregate for the soft soil road, and its purpose is to improve the roadbed. Soil structure, improve subgrade strength;

步骤3、将巴氏芽孢杆菌浓缩液掺入营养液中注入砂土路基:菌液及营养液按纵向连续注入软土路基中,横向间隔应在0.4-0.7m之间,然后静置,此步骤的主要目的是尽快激活巴氏芽孢杆菌及土壤原微生物的生物活性,并利用营养液将巴氏芽孢杆菌扩散到软土路基当中,避免细菌过于集中;Step 3. Mix the Bacillus pasteurii concentrate into the nutrient solution and inject it into the sand subgrade: the bacterial solution and the nutrient solution are continuously injected into the soft soil subgrade in the longitudinal direction. The main purpose of the step is to activate the biological activity of Pasteurella and soil microorganisms as soon as possible, and to use the nutrient solution to spread the Pasteurella to the soft soil subgrade, so as to avoid excessive concentration of bacteria;

步骤4、注入固结液:此步骤是为微生物提供水解物质及钙离子,固结液按纵向连续注入软土路基中,横向间隔应在0.4-0.7m之间,且与菌液注入路径保持一致;Step 4. Injecting the consolidation solution: This step is to provide hydrolyzed substances and calcium ions for the microorganisms. The consolidation solution is continuously injected into the soft soil subgrade in the longitudinal direction. consistent;

步骤5、重复步骤3~4,5遍之后检测路基固结情况:路基未达到预期目标则重复步骤3和步骤4,每重复一次检验路基固结情况,达到预期目标则进行下一步施工。Step 5. Repeat steps 3 to 4. After 5 times, check the consolidation of the subgrade: if the subgrade does not reach the expected target, repeat steps 3 and 4. Check the consolidation of the subgrade every time it is repeated, and proceed to the next step if the target is reached.

所述步骤1中活化和培养采用的培养液为ATCC 1376 NH4-YE培养液,培养时培养基的温度控制在30℃、PH8-9,培养时间应在17-19h,培养后的巴氏芽孢杆菌放入4℃冰箱保存,存放时间不宜超过30天。The culture medium used for activation and culture in the step 1 is ATCC 1376 NH4-YE culture medium, the temperature of the culture medium is controlled at 30°C, PH8-9, and the culture time should be 17-19h. The bacteria should be stored in a refrigerator at 4°C, and the storage time should not exceed 30 days.

所述步骤3中注入菌液及营养液后需静置1-2h。In the step 3, after injecting the bacterial liquid and the nutrient solution, it needs to stand for 1-2 hours.

所述步骤3中的营养液的成分主要为氯化钙与尿素的混合液,CaCl2浓度为0.60mol/L、尿素浓度为0.65mol/L。The components of the nutrient solution in the step 3 are mainly the mixed solution of calcium chloride and urea, the concentration of CaCl 2 is 0.60mol/L, and the concentration of urea is 0.65mol/L.

所述步骤4中灌注一次菌液之后灌注5次固结液且每灌注1次固结液静置6-8h。In the step 4, the bacterial solution is poured once and then the condensed solution is poured for five times, and each time the condensed solution is poured, the solution is allowed to stand for 6-8 hours.

所述步骤4中的固结液的成分主要为氯化钙与尿素的混合液,CaCl2浓度为0.60mol/L、尿素浓度为0.65mol/L,制备的固结液应尽快使用,以免固结液成分变质而影响效果。The components of the consolidation solution in the step 4 are mainly the mixed solution of calcium chloride and urea, the concentration of CaCl is 0.60mol /L, and the concentration of urea is 0.65mol/L. The prepared consolidation solution should be used as soon as possible to avoid solidification. The composition of the condensate is deteriorated and the effect is affected.

所述步骤5中预期目标采用CBR值作为检验标准,CBR值不低于4%即达到预期目标。The expected target in the step 5 adopts the CBR value as the inspection standard, and the expected target is achieved when the CBR value is not less than 4%.

本发明具有如下优点:The present invention has the following advantages:

本发明应用交叉学科,使用生物化学技术处理软土路基,克服了传统物理和化学方法处理路基的高污染、高能耗等问题,本发明,既能实现对软土路基的强化处理,又减少了环境污染和能耗问题。本发明内容不仅可以用粉细砂固结软土路基改良方法,而且由于微生物诱导碳酸钙沉积可以锁定重金属等有害元素,本改良方法可以进一步改进,与钢渣等固体废弃物一并开展软土路基的固结改良。The invention applies interdisciplinary and uses biochemical technology to treat the soft soil roadbed, and overcomes the problems of high pollution and high energy consumption of the traditional physical and chemical methods to treat the roadbed. Environmental pollution and energy consumption issues. The content of the present invention can not only consolidate the soft soil roadbed improvement method with silty fine sand, but also because the microorganism-induced calcium carbonate deposition can lock heavy metals and other harmful elements, the improvement method can be further improved, and the soft soil roadbed can be developed together with solid wastes such as steel slag. consolidation improvement.

附图说明Description of drawings

图1是本发明采用的微生物诱导碳酸钙沉淀技术示意图;Fig. 1 is the schematic diagram of the microorganism-induced calcium carbonate precipitation technology adopted in the present invention;

图2是本发明采用的微生物为碳酸钙沉淀提供核点过程示意图;Fig. 2 is that the microorganism that the present invention adopts provides nucleation process schematic diagram for calcium carbonate precipitation;

图3是本发明碳酸钙晶体填充砂土颗粒之间的缝隙,对砂土颗粒之间产生胶结作用结构示意图;Fig. 3 is that calcium carbonate crystal of the present invention fills the gap between sand particles, and produces a cementation structure schematic diagram between sand particles;

图4是本发明向砂土中,传输菌液以及尿素和钙源等营养盐示意图;Fig. 4 is the present invention in sandy soil, transmits the nutrient salt schematic diagram such as bacterial liquid and urea and calcium source;

图5是本发明将制备好的固结液注入砂土路基示意图;5 is a schematic diagram of the present invention injecting the prepared consolidation liquid into a sandy soil roadbed;

图6是本发明微生物诱导粉细砂加速固结软土路基效果图。Fig. 6 is the effect diagram of the microbe-induced silty sand accelerated consolidation soft soil roadbed of the present invention.

具体实施方式Detailed ways

下面通过实施例,并结合附图,对本发明的技术方案作进一步具体的说明,如图1、图2所示,为本发明采用的微生物诱导碳酸钙固结沉淀技术微观结构示意图,包括巴氏芽孢杆菌以尿素为能源,通过新陈代谢活动产生大量的高活性脲酶,将尿素水解生成NH4 +和CO3 2-,此后再向土壤中灌注钙盐溶液提供钙离子,由于微生物特殊的细胞壁结构,其表面一般带有大量负离子生命活动将CO3 2-运输到细胞表面与Ca2+结合形成碳酸钙晶体,反应方程式如下:The technical solution of the present invention will be further described in detail below by way of examples and in conjunction with the accompanying drawings. As shown in Figure 1 and Figure 2, it is a schematic diagram of the microstructure of the microbe-induced calcium carbonate consolidation and precipitation technology adopted in the present invention, including Pasteur Bacillus uses urea as energy, produces a large amount of highly active urease through metabolic activities, hydrolyzes urea to generate NH 4 + and CO 3 2- , and then pours calcium salt solution into the soil to provide calcium ions. Due to the special cell wall structure of microorganisms, Its surface generally has a large number of negative ions, and life activities transport CO 3 2- to the cell surface to combine with Ca 2+ to form calcium carbonate crystals. The reaction equation is as follows:

NH2-CO-NH2+3H2O→2NH4 ++CO3 2- NH 2 -CO-NH 2 +3H 2 O→2NH 4 + +CO 3 2-

Figure BDA0002658816180000041
Figure BDA0002658816180000041

当空隙溶液中CaCO3的浓度超过了其溶解能力,便会在空隙中析出碳酸钙沉淀。When the concentration of CaCO3 in the void solution exceeds its solubility, calcium carbonate precipitates in the voids.

进一步,在微生物培养之前应对微生物进行活化,微生物采用巴氏芽孢杆菌,是一种好氧的革兰氏阳性菌,能在新陈代谢过程中产生大量脲酶。菌种开始为冻干粉,需要进行细菌活化,采用ATCC 1376 NH4-YE培养液进行活化。Further, the microorganisms should be activated before the microorganisms are cultured. The microorganisms are Bacillus Pasteurella, an aerobic gram-positive bacteria that can produce a large amount of urease in the metabolic process. The strains are lyophilized powder at first, which needs to be activated by bacteria, using ATCC 1376 NH4-YE culture medium for activation.

进一步,培养微生物。将活化后的巴氏芽孢杆菌接种到ATCC 1376 NH4-YE培养液中,培养基的温度控制在30℃、PH8-9,培养时间应在17-19h,培养后的巴氏芽孢杆菌放入4℃冰箱保存,存放时间不宜超过30天,使用时将其取出,进行工程使用。Further, the microorganisms are cultured. Inoculate the activated Bacillus Pasteurella into the ATCC 1376 NH4-YE medium, the temperature of the medium should be controlled at 30°C, PH8-9, the culture time should be 17-19h, and the cultured Bacillus Pasteurella should be placed in 4 It should be stored in the refrigerator at ℃, and the storage time should not exceed 30 days. When using it, take it out and use it for engineering.

巴氏芽孢杆菌在此反应过程中起到两个核心作用:一是为水解尿素提供脲酶,二是为碳酸钙晶体沉积提供成核点。Pasteurella plays two core roles in this reaction process: one is to provide urease for the hydrolysis of urea, and the other is to provide a nucleation point for the deposition of calcium carbonate crystals.

如图3所示,为本发明碳酸钙晶体填充土颗粒之间的缝隙,对土颗粒之间产生胶结作用结构示意图。由于巴氏芽孢杆菌细胞壁的特殊结构,细胞表面带负电荷,当空隙环境中含有一定浓度钙离子时,钙离子会被细胞吸附,从而以细胞为晶体。碳酸钙晶体沉积积覆在土体颗粒表面,堵塞土体孔隙并黏结土体颗粒,使土体渗透性下降的同时提升其强度。As shown in FIG. 3 , it is a schematic diagram of the structure of the calcium carbonate crystals of the present invention filling the gaps between the soil particles and producing cementation between the soil particles. Due to the special structure of the cell wall of Bacillus pasteuri, the cell surface is negatively charged. When the interstitial environment contains a certain concentration of calcium ions, the calcium ions will be adsorbed by the cells, so that the cells are crystals. Calcium carbonate crystals are deposited on the surface of soil particles, blocking soil pores and bonding soil particles, reducing soil permeability and increasing its strength.

生成的碳酸钙晶体在土体中起到两点作用,首先碳酸钙晶体会填充土颗粒之间的缝隙,增加土体的密实程度以及土颗粒之间的摩擦,其次碳酸钙晶体会对土颗粒之间产生胶结作用,相当于一种粘结剂将微小土粒粘结在一起,形成密实块状体,增加土颗粒间的粘聚力,从而提高土体的抗剪强度。The resulting calcium carbonate crystals play two roles in the soil. First, the calcium carbonate crystals will fill the gaps between the soil particles, increasing the compactness of the soil and the friction between the soil particles. Second, the calcium carbonate crystals will fill the gaps between the soil particles. There is a cementation effect between them, which is equivalent to a binder that binds the tiny soil particles together to form a dense block, which increases the cohesion between the soil particles, thereby improving the shear strength of the soil.

如图4、图5所示,为本发明向砂土中,传输菌液以及尿素营养液,之后将制备好的固结液注入路基。As shown in FIG. 4 and FIG. 5 , the present invention transmits bacterial liquid and urea nutrient solution to the sandy soil, and then injects the prepared consolidation liquid into the roadbed.

如图4所示,将巴氏芽孢杆菌浓缩液参入营养液中注入砂土路基,菌液及营养液按纵向连续注入软土路基中,横向间隔应在0.4-0.7m之间,注入菌液及营养液后需静置1-2h,此步骤的主要目的是尽快激活巴氏芽孢杆菌及土壤原微生物的生物活性,并利用营养液将巴氏芽孢杆菌扩散到软土路基当中,避免细菌过于集中。As shown in Figure 4, the pasteurized bacillus concentrate is added into the nutrient solution and injected into the sandy soil roadbed. The bacteria solution and the nutrient solution are continuously injected into the soft soil roadbed in the longitudinal direction. The horizontal interval should be between 0.4-0.7m. The main purpose of this step is to activate the biological activity of Bacillus Pasteurella and soil original microorganisms as soon as possible, and use the nutrient solution to spread Bacillus Pasteurella into the soft soil roadbed to avoid excessive bacteria. concentrated.

如图5所示,向路基注入固结液,固结液的成分主要为氯化钙与尿素,CaCl2浓度为0.6mol/L、尿素浓度为0.65mol/L,注入固结液的目的是为微生物提供水解物质及钙离子,固结液按纵向连续注入软土路基中,横向间隔应在0.4-0.7m之间,且应与菌液注入路径保持一致,灌注一次菌液之后灌注5次固结液且每灌注1次固结液静置5-8h,制备的固结液应尽快使用,以免固结液成分变质而影响效果。As shown in Figure 5, the consolidation liquid is injected into the roadbed. The main components of the consolidation liquid are calcium chloride and urea. The concentration of CaCl 2 is 0.6mol/L and the concentration of urea is 0.65mol/L. Provide hydrolyzed substances and calcium ions for microorganisms. The consolidation liquid is continuously injected into the soft soil subgrade in the longitudinal direction. The horizontal interval should be between 0.4-0.7m, and it should be consistent with the injection path of the bacterial solution. After the bacterial solution is injected once, it is injected 5 times. The condensing liquid should be used as soon as possible, and the condensing liquid should be used as soon as possible to avoid the deterioration of the components of the consolidating liquid and affect the effect.

如图6所示,为本发明路基加固效果示意图,如果微生物诱导碳酸钙加固路基效果没有达到预期效果,应重复步骤3、步骤4和步骤5,依次循环直至达到路基工程效果。As shown in Figure 6, it is a schematic diagram of the subgrade reinforcement effect of the present invention. If the microbe-induced calcium carbonate reinforcement subgrade effect does not achieve the expected effect, steps 3, 4 and 5 should be repeated, and cycle until the subgrade engineering effect is achieved.

本发明的微生物诱导粉细砂加固软土路基的施工步骤依次进行,为使路基达到工程使用要求,应多次重复步骤3、步骤4和步骤5,从而得到路基加固最优材料配比与时间之间的关系。The construction steps of the microbe-induced silty sand to strengthen the soft soil roadbed of the present invention are carried out in sequence. In order to make the roadbed meet the engineering use requirements, steps 3, 4 and 5 should be repeated many times, so as to obtain the optimal material ratio and time for roadbed reinforcement. The relationship between.

本发明的保护范围并不限于上述的实施例,显然,本领域的技术人员可以对本发明进行各种改动和变形而不脱离本发明的范围和精神。倘若这些改动和变形属于本发明权利要求及其等同技术的范围内,则本发明的意图也包含这些改动和变形在内。The protection scope of the present invention is not limited to the above-mentioned embodiments. Obviously, those skilled in the art can make various changes and modifications to the present invention without departing from the scope and spirit of the present invention. If these changes and modifications belong to the scope of the claims of the present invention and their equivalents, the present invention is intended to include these changes and modifications.

Claims (7)

1. A microorganism-induced silty-fine sand consolidation soft soil roadbed ecological improvement method is characterized by comprising the following steps:
step 1, activation and culture of microorganisms: the microorganism adopts pasteurella, the strain is freeze-dried powder, and the bacteria is activated and cultured in the culture solution to obtain pasteurella concentrated solution;
step 2, adding fine sand: fine sand is mixed into the soft soil, the mixing proportion of the fine sand is 10-20%, and the fine sand provides large-particle-size aggregate for the soft soil road;
step 3, doping the bacillus pasteurii concentrated solution into the nutrient solution and injecting the nutrient solution into a sandy soil subgrade: continuously injecting the bacterial liquid and the nutrient solution into the soft soil roadbed according to the longitudinal direction, wherein the transverse interval is 0.4-0.7m, and then standing;
step 4, injecting consolidation liquid: continuously injecting consolidation liquid into the soft soil roadbed according to the longitudinal direction, wherein the transverse interval is 0.4-0.7m and is consistent with a bacterial liquid injection path;
and 5, repeating the steps 3-4, and detecting the roadbed consolidation condition after five times: and (4) repeating the step (3) and the step (4) when the roadbed does not reach the expected target, and performing the next construction when the roadbed is repeatedly checked to reach the expected target.
2. The method for ecologically improving the soft soil subgrade consolidated by the microorganism-induced fine sand powder as claimed in claim 1, wherein the method comprises the following steps: the culture solution adopted in the activation and culture in the step 1 is ATCC 1376 NH4-YE culture solution, the temperature of the culture medium is controlled at 30 ℃ during culture, the pH value is 8-9, the culture time is 17-19h, the cultured Paenibacillus pasteurianus is stored in a refrigerator at 4 ℃, and the storage time is not longer than 30 days.
3. The method for ecologically improving the soft soil subgrade consolidated by the microorganism-induced fine sand powder as claimed in claim 1, wherein the method comprises the following steps: and (3) standing for 1-2h after the bacterial liquid and the nutrient solution are injected in the step 3.
4. The method for ecologically improving the soft soil subgrade consolidated by the microorganism-induced fine sand powder as claimed in claim 1, wherein the method comprises the following steps: the nutrient solution in the step 3 mainly comprises a mixed solution of calcium chloride and urea and CaCl2The concentration is 0.60mol/L and the urea concentration is 0.65 mol/L.
5. The method for ecologically improving the soft soil subgrade consolidated by the microorganism-induced fine sand powder as claimed in claim 1, wherein the method comprises the following steps: and (4) after the one-time bacterial liquid is poured in the step (4), pouring the consolidation liquid for 5 times, and standing for 6-8 hours every time the consolidation liquid is poured for 1 time.
6. The method for ecologically improving the soft soil subgrade consolidated by the microorganism-induced fine sand powder as claimed in claim 1, wherein the method comprises the following steps: the consolidation liquid in the step 4 mainly comprises a mixed liquid of calcium chloride and urea and CaCl2The concentration is 0.60mol/L and the urea concentration is 0.65 mol/L.
7. The method for ecologically improving the soft soil subgrade consolidated by the microorganism-induced fine sand powder as claimed in claim 1, wherein the method comprises the following steps: and 5, adopting the CBR value as a check standard for the expected target in the step 5, wherein the expected target is achieved when the CBR value is not less than 4%.
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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112500040A (en) * 2020-12-03 2021-03-16 河海大学 Method for quickly recycling soft soil by combining microorganisms and high polymer resin
CN113431002A (en) * 2021-07-05 2021-09-24 河海大学 Method for solidifying farmland drainage ditch slope by utilizing microorganism induced calcium carbonate
CN113445490A (en) * 2021-06-29 2021-09-28 南京林业大学 Method for uniformly solidifying soft clay by microorganisms
CN114482087A (en) * 2021-12-23 2022-05-13 合肥工业大学 A method of microbial mineralization filling-magnesium oxide carbonization shotcrete curing slope

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008008023A (en) * 2006-06-29 2008-01-17 Hokkaido Univ Method of consolidation of ground containing calcium using microorganisms
JP2011157804A (en) * 2010-02-01 2011-08-18 Masayoshi Kondo Sand ground improvement method and apparatus used for the same
CN106168550A (en) * 2016-08-10 2016-11-30 天津大学 Microorganism solidification Extra-fine sand is used to form the Experimental Method in Laboratory of artificial crust layer
CN108999179A (en) * 2018-08-13 2018-12-14 重庆科技学院 The method of vacuum pre-pressed joint microorganism sand fixing technology reinforcing soft soil foundation
CN109763504A (en) * 2019-03-19 2019-05-17 长沙矿山研究院有限责任公司 A kind of slope ecological reinforcement and greening method
CN110424449A (en) * 2019-07-16 2019-11-08 河海大学 A kind of microbe controlling method of reinforced earth bulkhead and its long-time stability

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008008023A (en) * 2006-06-29 2008-01-17 Hokkaido Univ Method of consolidation of ground containing calcium using microorganisms
JP2011157804A (en) * 2010-02-01 2011-08-18 Masayoshi Kondo Sand ground improvement method and apparatus used for the same
CN106168550A (en) * 2016-08-10 2016-11-30 天津大学 Microorganism solidification Extra-fine sand is used to form the Experimental Method in Laboratory of artificial crust layer
CN108999179A (en) * 2018-08-13 2018-12-14 重庆科技学院 The method of vacuum pre-pressed joint microorganism sand fixing technology reinforcing soft soil foundation
CN109763504A (en) * 2019-03-19 2019-05-17 长沙矿山研究院有限责任公司 A kind of slope ecological reinforcement and greening method
CN110424449A (en) * 2019-07-16 2019-11-08 河海大学 A kind of microbe controlling method of reinforced earth bulkhead and its long-time stability

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112500040A (en) * 2020-12-03 2021-03-16 河海大学 Method for quickly recycling soft soil by combining microorganisms and high polymer resin
CN113445490A (en) * 2021-06-29 2021-09-28 南京林业大学 Method for uniformly solidifying soft clay by microorganisms
CN113431002A (en) * 2021-07-05 2021-09-24 河海大学 Method for solidifying farmland drainage ditch slope by utilizing microorganism induced calcium carbonate
CN114482087A (en) * 2021-12-23 2022-05-13 合肥工业大学 A method of microbial mineralization filling-magnesium oxide carbonization shotcrete curing slope
CN114482087B (en) * 2021-12-23 2024-05-07 合肥工业大学 Method for curing side slope by microorganism mineralization filling-magnesia carbonization slurry spraying

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