CN111501733A - A method for solidifying soil by stimulating and culturing in situ microorganisms - Google Patents
A method for solidifying soil by stimulating and culturing in situ microorganisms Download PDFInfo
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- E—FIXED CONSTRUCTIONS
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- E—FIXED CONSTRUCTIONS
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- E02B3/04—Structures or apparatus for, or methods of, protecting banks, coasts, or harbours
- E02B3/12—Revetment of banks, dams, watercourses, or the like, e.g. the sea-floor
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- E—FIXED CONSTRUCTIONS
- E02—HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
- E02D—FOUNDATIONS; EXCAVATIONS; EMBANKMENTS; UNDERGROUND OR UNDERWATER STRUCTURES
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Abstract
本发明公开了一种利用激发培养原位微生物固化土体的方法,包括:首先在土体中加入激发液促进土体内微生物繁殖,再向土体中加入胶结液固化土体。进一步地,通过土体的孔隙率、处理面积和处理深度,计算单次加入激发液和/或胶结液的用量。通过原位投加激发液,促进土体中自身的微生物繁殖,原位激发的微生物在土体环境中营养物质均衡,与其他微生物互相调节感应,生长繁殖快速,脲酶活性高;同时,原位激发微生物的方法,减少了向土体加入菌液的过程,大大减少了由于溶液的不均匀流动导致微生物分布不均的影响,有效提高MICP的效果。
The invention discloses a method for solidifying soil by stimulating and culturing in-situ microorganisms. Further, according to the porosity of the soil, the treatment area and the treatment depth, the amount of the excitation liquid and/or cementing liquid added at a time is calculated. By adding the excitation solution in situ, it can promote the reproduction of its own microorganisms in the soil. The microorganisms stimulated in situ have balanced nutrients in the soil environment, and interact with other microorganisms. The growth and reproduction are fast and the urease activity is high. The method of stimulating microorganisms reduces the process of adding bacterial liquid to the soil, greatly reduces the influence of uneven distribution of microorganisms caused by uneven flow of the solution, and effectively improves the effect of MICP.
Description
技术领域technical field
本发明属于岩土工程和微生物工程交叉领域,更具体的说,涉及一种利用激发培养原位微生物固化土体的方法。The invention belongs to the cross field of geotechnical engineering and microbial engineering, and more specifically relates to a method for solidifying soil by stimulating and culturing in-situ microorganisms.
背景技术Background technique
随着世界经济的快速发展,人口数量快速增加,对建设用地的需求不断增大。尤其是在我国,城镇化不断加剧,需要更多的基础设施来满足日益增长的人口需要。然而在建设过程中,存在着严重的土地供给不足问题,土地消耗不断增大,土质变差,这些大大限制了城市化的建设过程。因此,改良不能满足工程建设需求的土体,提高土壤利用率成为了关乎国计民生的大事。如何用高效、环保、经济的方法对土壤进行改良成为了当今社会亟待解决的问题。With the rapid development of the world economy and the rapid increase in population, the demand for construction land continues to increase. Especially in my country, where urbanization continues to intensify, more infrastructure is needed to meet the needs of the growing population. However, in the process of construction, there are serious problems of insufficient land supply, increasing land consumption and poor soil quality, which greatly limit the construction process of urbanization. Therefore, improving the soil that cannot meet the needs of engineering construction and improving the soil utilization rate has become a major event related to the national economy and people's livelihood. How to improve soil in an efficient, environmentally friendly and economical way has become an urgent problem to be solved in today's society.
传统的土壤改良方法,是利用机械或人造材料对土体进行物理化学加固,在机械施工和材料的制作时都会带来较大的能源消耗。这些方法大多对土壤扰动大,施工周期长,工作量大。其中,极为常见的化学灌浆技术,主要通过在土中掺加水泥、铬木素等化学浆材,以达到提高土壤强度,降低土壤渗透性的目的。然而,化学浆材多会带来土壤pH值的改变,并且多有毒,会对土壤、地下水、矿产资源、动植物和人体产生有害影响。The traditional soil improvement method is to use mechanical or artificial materials to strengthen the soil physicochemically, which will bring about large energy consumption during mechanical construction and material production. Most of these methods have large soil disturbance, long construction period and heavy workload. Among them, the very common chemical grouting technology mainly achieves the purpose of improving soil strength and reducing soil permeability by adding chemical slurry materials such as cement and chrome lignin into the soil. However, many chemical pulps will bring about changes in soil pH, and are more toxic, which will have harmful effects on soil, groundwater, mineral resources, animals and plants, and humans.
微生物矿化作用在自然界中普遍存在,某些微生物能够通过自身矿化作用产生多种矿物结晶。其中,微生物诱导碳酸钙沉积(Microbial Induced Calcite Precipitation,简称MICP)技术一直是近年来微生物矿化作用的研究热点。在该技术中,产脲酶微生物通过自身的代谢作用产生脲酶,不断分解扩散到细菌内部的尿素,产生的CO3 2-与环境中的Ca2+结合,生成碳酸钙沉积,生成的碳酸钙性质稳定,力学性能好,耐久性强,且具有优异的胶结作用。经过研究发现,MICP技术可以应用于多个领域,在土体固化方面效果显著。在MICP固化土体技术中,生物能代替了传统的机械能,微生物代谢产物代替了化学物质,具有节能环保,对土体扰动小等的优点,有利于环境的可持续发展。Microbial mineralization is ubiquitous in nature, and some microorganisms can produce a variety of mineral crystals through their own mineralization. Among them, Microbial Induced Calcite Precipitation (MICP) technology has been a research hotspot of microbial mineralization in recent years. In this technology, urease-producing microorganisms produce urease through their own metabolism, continuously decompose urea that diffuses into the bacteria, and the generated CO 3 2- combines with Ca 2+ in the environment to form calcium carbonate deposits, the resulting calcium carbonate properties Stable, good mechanical properties, strong durability, and excellent cementation. After research, it is found that MICP technology can be applied in many fields, and has a remarkable effect in soil solidification. In the MICP solidified soil technology, biological energy replaces traditional mechanical energy, and microbial metabolites replace chemical substances. It has the advantages of energy saving and environmental protection, and less disturbance to soil, which is conducive to the sustainable development of the environment.
在MICP固化土体的现有研究中,多在实验室条件活化培养产脲酶微生物,进而引入土体诱导碳酸钙沉积,从而起到固化土体的作用。然而,微生物在实验室条件下培养,存在培养基易富营养化,生长因子缺乏,人为破坏微生物之间的联系和忽视微生物间的互作关系的问题,这些容易导致微生物虽具有代谢功能,但生长繁殖缓慢(张作艳等,2018)。随后,在微生物引入土体后,打破了自然环境中微生物的平衡,由于土壤其他原生微生物的大肆掠夺与竞争,外源微生物的数量进一步下降。另外,在加入菌液的过程中,由于菌液在土体中的不均匀流动,使细菌在土体中的分布不均匀,影响土体固化的效果(Whiffin etal.2007;van Paassen et al.2009)。In the existing research on MICP-solidified soil, most of the urease-producing microorganisms are activated and cultured in laboratory conditions, and then introduced into the soil to induce calcium carbonate deposition, thus playing the role of solidifying the soil. However, when microorganisms are cultivated under laboratory conditions, there are problems such as easy eutrophication of the medium, lack of growth factors, artificial destruction of the connection between microorganisms and neglect of the interaction between microorganisms. These easily lead to microorganisms with metabolic functions, but Slow growth and reproduction (Zhang Zuoyan et al., 2018). Subsequently, after the microorganisms were introduced into the soil, the balance of microorganisms in the natural environment was broken, and the number of exogenous microorganisms further decreased due to the wanton plunder and competition of other native microorganisms in the soil. In addition, in the process of adding bacterial liquid, due to the uneven flow of bacterial liquid in the soil, the distribution of bacteria in the soil is not uniform, which affects the effect of soil solidification (Whiffin et al. 2007; van Paassen et al. 2009).
公开号为CN106284280A的现有技术公开了一种利用微生物制备碳酸钙固化砂土的方法。该方法将砂土倒入容器中;所述的容器中加入胶凝液和菌液,恒温震荡培养,得到混合液;定时定量从前述混合液中吸出少量,之后再向剩余混合液中加入定量胶凝液和砂土,连续数天后得到碳酸钙固化的砂土。该方法中不仅菌种选育耗费大量人力物力,并且微生物在培养时生长繁殖缓慢,加入土体后在土体中分布不均、存活率低。将砂土和溶液混合的胶结方法不适用于现场的实际操作,工程意义不大。The prior art with publication number CN106284280A discloses a method for preparing calcium carbonate-solidified sandy soil by using microorganisms. In the method, the sand is poured into a container; gelling liquid and bacterial liquid are added to the container, and the mixed liquid is obtained by constant-temperature shaking culture; a small amount is sucked out of the aforementioned mixed liquid at regular intervals, and then a quantitative amount is added to the remaining mixed liquid. Gelling liquid and sand, after several days in a row, calcium carbonate solidified sand is obtained. The method not only consumes a lot of manpower and material resources for the selection and breeding of bacterial species, but also the microorganisms grow and reproduce slowly during the cultivation, and the soil is unevenly distributed and the survival rate is low after being added to the soil. The cementation method of mixing sand and solution is not suitable for the actual operation on site, and has little engineering significance.
公开号为CN108441442A的现有技术公开了一种从土壤中直接提取微生物菌种制备碳酸钙的方法。该方法通过固体选择培养基从土壤中分离出芽孢杆菌菌种,将所分离菌种进行繁殖培养后,与胶凝液混合,加以恒温养护,得到微生物诱导碳酸钙沉淀。该方法中分离纯化细菌的过程复杂繁琐,耗费精力。另外,方法中的细菌虽然是从原始土壤中分离出来的,但培养环境仍然是实验室条件,培养过程中的上述问题仍然存在。并且方法仅限于溶液环境下的MICP处理,未进行固化土体的操作,不适用于实际工程条件下的应用。The prior art with publication number CN108441442A discloses a method for preparing calcium carbonate by directly extracting microbial strains from soil. In the method, Bacillus strains are separated from soil by using a solid selective medium, and the isolated strains are propagated and cultured, mixed with gelling liquid, and maintained at a constant temperature to obtain microbe-induced calcium carbonate precipitation. The process of isolating and purifying bacteria in this method is complicated, cumbersome, and labor-intensive. In addition, although the bacteria in the method are isolated from the original soil, the cultivation environment is still laboratory conditions, and the above-mentioned problems in the cultivation process still exist. And the method is limited to the MICP treatment in the solution environment, without the operation of solidifying the soil, and is not suitable for the application under actual engineering conditions.
综上,高效培养微生物,提高微生物在土体中的分布均匀性和存活率,用于MICP固化土体,并应用于不同实际工程条件,目前尚未有有效的解决方案。To sum up, there is no effective solution for cultivating microorganisms efficiently, improving the distribution uniformity and survival rate of microorganisms in soil, and using MICP to solidify soil and applying it to different actual engineering conditions.
发明内容SUMMARY OF THE INVENTION
1.要解决的问题1. The problem to be solved
本发明的目的在于克服现有MICP固化土体处理中通过外加培养的微生物生长繁殖缓慢,在土体中分布不均、存活率低,不适用于多样的实际工程条件等缺陷,提供一种利用激发培养原位微生物固化土体的方法,通过原位投加激发液,促进土体中自身的微生物繁殖,减少了向土体加入菌液的过程,大大减少了由于溶液的不均匀流动导致微生物分布不均的影响。The purpose of the present invention is to overcome the defects such as slow growth and reproduction of microorganisms through external culture in the existing MICP solidified soil treatment, uneven distribution in the soil body, low survival rate, unsuitable for various actual engineering conditions, etc. The method of stimulating and cultivating in-situ microorganisms to solidify the soil body, by adding the stimulating solution in situ, promotes the reproduction of microorganisms in the soil body, reduces the process of adding bacterial liquid to the soil body, and greatly reduces the uneven flow of the solution. uneven distribution.
本发明的另一目的在于,克服原位激发和原位胶结中溶液用量难以定量的问题,进一步提供了激发液和胶结液定量的方法。Another object of the present invention is to overcome the difficulty in quantifying the amount of solution in in-situ excitation and in-situ cementation, and further provide a method for quantifying excitation solution and cementation solution.
本发明的另一目的在于,克服激发时间与胶结时间难以确定的问题,进一步提供了判定方法。Another object of the present invention is to overcome the problem that the excitation time and the cementation time are difficult to determine, and further provide a determination method.
2.技术方案2. Technical solutions
为了解决上述问题,本发明所采用的技术方案如下:In order to solve the above problems, the technical scheme adopted in the present invention is as follows:
一种利用激发培养原位微生物固化土体的方法,包括:首先在土体中加入激发液促进土体内微生物繁殖,再向土体中加入胶结液固化土体。A method for solidifying soil by stimulating and culturing in-situ microorganisms comprises: firstly adding an exciting liquid to the soil to promote the reproduction of microorganisms in the soil, and then adding cementing liquid to the soil to solidify the soil.
优选地,通过土体的孔隙率、处理面积和处理深度,计算单次加入激发液和/或胶结液的用量。Preferably, according to the porosity, treatment area and treatment depth of the soil, the amount of the excitation liquid and/or cementing liquid added in a single time is calculated.
优选地,所述激发液中包括尿素。Preferably, the excitation solution includes urea.
优选地,所述激发液中还包括酵母提取物、葡萄糖和缓冲液。Preferably, the challenge solution further includes yeast extract, glucose and buffer.
优选地,所述胶结液中包括尿素和氯化钙。Preferably, the cementing solution includes urea and calcium chloride.
优选地,所述方法具体包括以下步骤:Preferably, the method specifically includes the following steps:
1)确定土体的孔隙率、处理面积和处理深度,计算单次加入激发液和胶结液的用量;1) Determine the porosity, treatment area and treatment depth of the soil, and calculate the amount of excitation liquid and cementing liquid added in a single time;
2)根据步骤1)算得的激发液用量在土体中加入激发液,每隔2~5d加入一次;2) Add the excitation solution to the soil according to the amount of the excitation solution calculated in step 1), and add it every 2-5 days;
在准备加入下一次激发液之前,取样测量土体中脲酶活性;脲酶活性定义为单位时间内单位质量土体水解的尿素量;根据脲酶活性判断激发液加入次数,当脲酶活性大于0.06mghydrolysed urea min-1g-1时,停止加入激发液;Before adding the next excitation solution, sample the soil to measure the urease activity in the soil; the urease activity is defined as the amount of urea hydrolyzed per unit mass of soil in unit time; the number of additions of the excitation solution is judged according to the urease activity, and when the urease activity is greater than 0.06 mghydrolysed urea min When -1 g -1 , stop adding the excitation solution;
3)根据步骤1)算得的胶结液用量在土体中加入胶结液,每隔2~5d加入一次;3) According to the amount of cementing liquid calculated in step 1), add cementing liquid to the soil, and add it once every 2~5d;
在准备加入下一次胶结液之前,取样测量土体中碳酸钙含量;根据碳酸钙含量判断胶结液加入次数,当细粒土碳酸钙含量大于4.0%或粗粒土碳酸钙含量大于8.0%时,停止加入胶结液。Before preparing to add the next cementitious solution, take a sample to measure the calcium carbonate content in the soil; according to the calcium carbonate content, judge the number of cementitious solution additions. Stop adding cement.
优选地,步骤1)中孔隙率,通过从待处理土体中取样测定,处理面积和处理深度根据工程需求确定。Preferably, the porosity in step 1) is determined by sampling from the soil to be treated, and the treatment area and treatment depth are determined according to engineering requirements.
优选地,步骤1)中激发液单次用量Ve(m3)为:Preferably, in step 1), the single dosage V e (m 3 ) of the excitation solution is:
Ve=αnSH (1)V e =αnSH (1)
其中,α为激发液用量修正系数,取值范围为1.05~1.55;n为土体孔隙率(%);S为处理面积(m2);H为处理深度(m)。以在保证了激发液的充分入渗和均匀分布,满足反应需求的同时,避免了激发液的浪费和工程周期的延长。Among them, α is the correction coefficient of the amount of excitation solution, and the value ranges from 1.05 to 1.55; n is the soil porosity (%); S is the treatment area (m 2 ); H is the treatment depth (m). In order to ensure the sufficient infiltration and uniform distribution of the excitation liquid and meet the reaction requirements, the waste of the excitation liquid and the extension of the engineering period are avoided.
优选地,步骤1)中胶结液单次用量Vc(m3)为:Preferably, in step 1), the single dosage V c (m 3 ) of the cementitious liquid is:
Vc=βVe (2)V c =βV e (2)
其中,β为Vc/Ve,即胶结液单次用量与激发液单次用量之比,取值范围为0.9~1.55,且保证αβ>1。以在保证胶结液加入后能充分填充土体孔隙和均匀分布,达到良好的固化效果需求的同时,避免了胶结液的浪费和工程周期的延长。Among them, β is V c /V e , that is, the ratio of the single dosage of the cementing solution to the single dosage of the excitation solution, and the value ranges from 0.9 to 1.55, and αβ>1 is guaranteed. In order to ensure that the soil pores can be fully filled and evenly distributed after the cementing liquid is added, so as to achieve the requirements of good curing effect, and at the same time, the waste of cementing liquid and the extension of the engineering period are avoided.
优选地,α和β的取值取决于土体渗透系数,如下表1所示:Preferably, the values of α and β depend on the soil permeability coefficient, as shown in Table 1 below:
表1 α和β的参考取值Table 1 Reference values of α and β
优选地,步骤2)中激发液成分为尿素,酵母提取物,葡萄糖和Tris-base缓冲液。所述尿素浓度为200~500mM,所述酵母提取物浓度为10~20g/L,所述葡萄糖浓度为20~40g/L,所述Tris-base缓冲液浓度为0.13M。所述尿素为细菌提供氮源,以便所需的产脲酶细菌的生长繁殖,同时,尿素水解产生的氨,能够提高土体环境的pH,有利于适于碱性环境的细菌生存,尤其是产脲酶细菌的生存。所述酵母提取物为产脲酶细菌的生长繁殖提供充足的营养物质。所述葡糖为细菌提供碳源,激发土壤中细菌的初始活动,为细菌活动提供能量。所述Tris-base缓冲液调节溶液的pH。Preferably, in step 2), the components of the excitation solution are urea, yeast extract, glucose and Tris-base buffer. The concentration of the urea is 200-500 mM, the concentration of the yeast extract is 10-20 g/L, the concentration of the glucose is 20-40 g/L, and the concentration of the Tris-base buffer is 0.13M. The urea provides a nitrogen source for bacteria, so that the desired urease-producing bacteria can grow and reproduce, and at the same time, the ammonia produced by the hydrolysis of urea can improve the pH of the soil environment, which is beneficial to the survival of bacteria suitable for an alkaline environment, especially the production of urea. Survival of urease bacteria. The yeast extract provides sufficient nutrients for the growth and reproduction of urease-producing bacteria. The glucose provides a carbon source for bacteria, stimulates the initial activity of bacteria in the soil, and provides energy for bacterial activity. The Tris-base buffer adjusts the pH of the solution.
优选地,步骤2)中所述取样测脲酶活性的具体步骤包括:Preferably, the specific steps of sampling and measuring urease activity described in step 2) include:
a)将取土铲和盛放土样的聚乙烯袋灭菌;a) Sterilize the soil shovel and the polyethylene bag holding the soil sample;
b)根据处理面积将土样适当划分为多个区域,在每一区域土体表面取土100g,分别放入聚乙烯袋中,保持土壤于黑暗中,所处环境温度同自然环境一致,并可自由接触空气;b) Divide the soil sample into multiple areas appropriately according to the treatment area, take 100g of soil from the soil surface of each area, put them into polyethylene bags respectively, keep the soil in the dark, and the ambient temperature is the same as the natural environment. Free access to air;
c)取样后尽快对土样进行处理,将土样通过2mm筛子(筛径也可根据实际土体条件进行选择,以筛去土样中较大颗粒石头和动植物碎片为宜);c) Treat the soil sample as soon as possible after sampling, and pass the soil sample through a 2mm sieve (the sieve diameter can also be selected according to the actual soil conditions, and it is appropriate to sieve out larger particles of stones and animal and plant fragments in the soil sample);
d)用电导率法测定脲酶活性。取c)中过筛土样20g,盛于锥形瓶,加入100mL0.2%焦磷酸钠溶液。用磁力搅拌仪搅拌后,将溶液用离心机离心5min(离心速度以分离出土壤细菌为宜)。取上清液5mL,加入45mL 1.6M的尿素溶液混合,搅拌均匀,用电导率仪测量5min内溶液电导率的变化,得到平均每分钟的电导率变化值(mSmin-1)。乘以尿素水解量的换算系数11,算得单位时间溶液中脲酶水解尿素量(mMurea hydrolysedmin-1)。再除以5mL上清液相应的土样质量1g后,乘以溶液的体积0.05L和尿素的摩尔质量60g/mol,得到单位时间内单位质量土体水解的尿素质量,作为测得的土体脲酶活性(mg urea hydrolysed min-1g-1)。对各区域土样的脲酶活性取平均值,作为最终测得的脲酶活性。也可用苯酚-次氯酸钠比色法,扩散法等方法进行测定,但以电导率法为宜,此方法操作简单,经济性高。d) Determination of urease activity by conductivity method. Take 20 g of the sieved soil sample in c), put it in a conical flask, and add 100 mL of 0.2% sodium pyrophosphate solution. After stirring with a magnetic stirrer, the solution was centrifuged with a centrifuge for 5 min (centrifugation speed is suitable for separating soil bacteria). Take 5mL of the supernatant, add 45mL of 1.6M urea solution to mix, stir evenly, measure the change of the conductivity of the solution within 5min with a conductivity meter, and obtain the average conductivity change value per minute (mSmin -1 ). Multiply by the conversion factor 11 of the amount of urea hydrolysis to calculate the amount of urea hydrolyzed by urease in the solution per unit time (mMurea hydrolysedmin -1 ). After dividing by 1 g of the corresponding soil sample mass of 5 mL of supernatant, multiply by the volume of the solution 0.05 L and the molar mass of urea 60 g/mol to obtain the mass of urea hydrolyzed per unit mass of soil in unit time, as the measured soil mass Urease activity (mg urea hydrolysed min -1 g -1 ). The average urease activity of soil samples in each area was taken as the final measured urease activity. It can also be determined by phenol-sodium hypochlorite colorimetry, diffusion method and other methods, but the conductivity method is suitable, which is simple to operate and highly economical.
优选地,步骤3)中胶结液为尿素、氯化钙和营养肉汤。所述的尿素和氯化钙,浓度范围为0.1~2.0M,配比范围为1:3~3:1。所述营养肉汤浓度为5g/L,为激发后的微生物提供充足的营养物质,维持微生物的活性。Preferably, the cementing liquid in step 3) is urea, calcium chloride and nutrient broth. The urea and calcium chloride have a concentration range of 0.1-2.0M, and a ratio of 1:3-3:1. The concentration of the nutrient broth is 5g/L, which provides sufficient nutrients for the stimulated microorganisms and maintains the activity of the microorganisms.
优选地,步骤3)中取样方法同步骤2)中a)~b)。所述土体碳酸钙含量测定用盐酸酸洗排水法,具体步骤包括:Preferably, the sampling method in step 3) is the same as a) to b) in step 2). Described soil calcium carbonate content determination uses hydrochloric acid pickling drainage method, and concrete steps include:
a)将取土铲和盛放土样的聚乙烯袋灭菌;a) Sterilize the soil shovel and the polyethylene bag holding the soil sample;
b)根据处理面积将土样适当划分为多个区域,在每一区域土体表面取土100g,分别放入聚乙烯袋中,保持土壤于黑暗中,所处环境温度同自然环境一致,并可自由接触空气;b) Divide the soil sample into multiple areas appropriately according to the treatment area, take 100g of soil from the soil surface of each area, put them into polyethylene bags respectively, keep the soil in the dark, and the ambient temperature is the same as the natural environment. Free access to air;
e)取b)中土样10g;将土样用去离子水浸泡12h,随后离心(4000rpm,5min),取沉淀物,烘干称重。将烘干的土样研磨至粉状,取5g,加入10mL 1.0M盐酸溶液浸泡12h,利用排水法测定生成CO2的体积;与标准曲线比较,并去除土中原有的碳酸钙含量,算得土样的实际碳酸钙含量。对各区域土样的实际碳酸钙含量取平均值,作为最终测得的碳酸钙含量。也可用酸洗称重法等方法进行测定。e) Take 10 g of the soil sample in b); soak the soil sample in deionized water for 12 h, then centrifuge (4000 rpm, 5 min), take the sediment, dry it and weigh it. Grind the dried soil sample to powder, take 5g, add 10mL of 1.0M hydrochloric acid solution to soak for 12h, use the drainage method to measure the volume of CO 2 generated; compare with the standard curve, and remove the original calcium carbonate content in the soil, calculate the soil the actual calcium carbonate content. The actual calcium carbonate content of the soil samples in each area was averaged as the final measured calcium carbonate content. It can also be determined by methods such as acid washing weighing method.
优选地,步骤2)~步骤3)中的溶液加入方式包括喷洒,灌浆,滴灌和漫灌的方式。Preferably, the methods of adding the solution in steps 2) to 3) include spraying, grouting, drip irrigation and flood irrigation.
优选地,根据不同的实际工程条件,工艺选择不同。如:处理深度较浅,或者黏性土条件,适用喷洒法和滴灌法;处理深度较深,或者砂土条件,适用漫灌法和灌浆法;平坦土体条件,适用滴灌或漫灌法;边坡条件,适用喷洒或灌浆法;堤坝加固条件,适用灌浆法;抗侵蚀、修复开裂处理,适用喷洒法、滴灌或漫灌法;浅层小规模建筑地基加固适用漫灌法;深部中大规模建筑地基加固,适用灌浆法。Preferably, the process selection is different according to different actual engineering conditions. Such as: shallow treatment depth, or cohesive soil conditions, suitable for spraying method and drip irrigation method; deep treatment depth, or sandy soil conditions, suitable for flood irrigation method and grouting method; flat soil conditions, suitable for drip irrigation or flood irrigation method; slope Condition, apply spraying or grouting method; dam reinforcement conditions, apply grouting method; anti-erosion, repair cracking treatment, apply spray method, drip irrigation or flood irrigation method; shallow small-scale building foundation reinforcement applies flood irrigation method; deep medium and large-scale building foundation reinforcement , apply the grouting method.
优选地,步骤2)~步骤3)中胶结液和激发液相邻两次的加入间隔天数,以溶液充分渗入并完全反应为宜。一般情况下,间隔天数受土质条件的影响,随土体渗透系数的增加,间隔天数减小。Preferably, in steps 2) to 3), the number of days between the addition of the cementing solution and the excitation solution adjacent to each other is that the solution is fully infiltrated and reacted completely. In general, the interval days are affected by soil conditions, and the interval days decrease with the increase of soil permeability coefficient.
优选地,步骤2)~步骤3)中的现场环境温度为5℃~40℃。并且施工尽量选择在没有雨水的天气进行,若在加入胶结液的1d内淋雨,在碳酸钙含量测试外,还需进行强度测试,必要时增加胶结液的加入次数,以弥补因淋雨造成的对固化效果的影响。Preferably, the on-site ambient temperature in steps 2) to 3) is 5°C to 40°C. And the construction should be carried out in the weather without rain as much as possible. If it rains within 1 day of adding the cementitious liquid, in addition to the calcium carbonate content test, a strength test should be carried out. influence on the curing effect.
3.有益效果3. Beneficial effects
采用本发明提供的技术方案,与已有的公知技术相比,具有如下显著效果:Adopting the technical scheme provided by the present invention, compared with the existing known technology, has the following remarkable effects:
(1)本发明通过产脲酶微生物固化土体,微生物产生的脲酶分解尿素,产生的CO3 2-与环境中的Ca2+结合,生成碳酸钙沉积,填充土体孔隙,桥接土体颗粒,使得土体强度显著提高,渗透性降低,具有明显的固化效果;由于尿素水解机制简单,该方法可控性高,反应时间短。此外,该方法成本低,环保相容性好,适用范围广;原位激发的微生物,由于原属于自然环境,维护了自然环境的生态平衡,生存能力强,存活率高;本发明采用激发培养原位微生物的方法,原位激发的微生物在土体环境中营养物质均衡,与其他微生物互相调节感应,生长繁殖快速,脲酶活性高;(1) The present invention solidifies the soil through urease-producing microorganisms, and the urease produced by the microorganisms decomposes urea, and the generated CO 3 2- combines with Ca 2+ in the environment to form calcium carbonate deposits, fill soil pores, and bridge soil particles, The soil strength is significantly improved, the permeability is reduced, and the solidification effect is obvious; due to the simple hydrolysis mechanism of urea, the method has high controllability and short reaction time. In addition, the method has low cost, good environmental compatibility and wide application range; the microorganisms stimulated in situ, because they belong to the natural environment, maintain the ecological balance of the natural environment, have strong survivability and high survival rate; the present invention adopts the stimulation culture In the method of in situ microorganisms, the microorganisms stimulated in situ have balanced nutrients in the soil environment, interact with other microorganisms, and grow rapidly and multiply, and have high urease activity;
(2)本发明采用激发培养原位微生物的方法,由于微生物是在激发液进入之后才被激发,减少了向土体加入菌液的过程,大大减少了由于溶液的不均匀流动导致微生物分布不均的影响;同时由于激发液黏性相对菌液较低,流动性好,能够较为充分入渗,尤其是在黏性土中,克服了菌液入渗困难的问题,激发的微生物在土壤中分布相对较深;进而能够对取得更优的固化效果;(2) The present invention adopts the method of stimulating and cultivating in-situ microorganisms. Since the microorganisms are stimulated after the stimulating liquid enters, the process of adding bacterial liquid to the soil is reduced, and the uneven distribution of microorganisms caused by the uneven flow of the solution is greatly reduced. At the same time, due to the relatively low viscosity of the excitation liquid and good fluidity, it can infiltrate more fully, especially in the cohesive soil, overcoming the difficulty of infiltration of the bacteria liquid, and the stimulated microorganisms in the soil The distribution is relatively deep; thus, it can achieve better curing effect;
(3)本发明采用激发培养原位微生物的方法,免去了实验室培养微生物的繁杂过程,发挥土壤中原生产脲酶微生物的作用,经济性高,操作简便,工程周期短,实际应用性强;(3) The present invention adopts the method of stimulating and cultivating in-situ microorganisms, which avoids the complicated process of culturing microorganisms in the laboratory, and exerts the effect of the original urease-producing microorganisms in the soil, with high economy, simple and convenient operation, short engineering cycle and strong practical applicability;
(4)本发明中根据土体孔隙度、处理面积和处理深度,利用公式Ve=αnSH和Vc=βVe,分别定量了原位处理中激发液和胶结液的单次用量,解决了原位激发和原位胶结中溶液用量难以定量的问题;对激发液用量修正系数α和胶结液单次用量与激发液单次用量之比β分别取合适的范围,使激发液和胶结液用量能充分入渗,填充孔隙,这既满足反应过程需求,又避免了溶液浪费,增加了工程实际应用的可行性;(4) According to the soil porosity, treatment area and treatment depth, the present invention uses the formulas Ve = αnSH and V c = βV e to quantify the single dosage of the excitation liquid and the cementing liquid in the in-situ treatment, respectively. It is difficult to quantify the amount of solution in in-situ excitation and in-situ cementation; the correction coefficient α for the amount of excitation solution and the ratio β of the single dosage of cementing solution to the single dosage of excitation solution are taken into appropriate ranges, so that the dosage of excitation solution and cementing solution is It can fully infiltrate and fill the pores, which not only meets the requirements of the reaction process, but also avoids the waste of solution and increases the feasibility of practical engineering applications;
(5)本发明中根据土体脲酶活性判定微生物激发完成时间,使微生物充分激发,以利于胶结反应的进行;根据土体碳酸钙含量判定胶结完成时间,使胶结充分完成,碳酸钙沉积的量达到最大。在最大程度固化土体的同时,又避免了溶液和浪费和工程周期的延长;(5) In the present invention, the completion time of microbial excitation is determined according to the activity of soil urease, so that the microorganisms are fully stimulated to facilitate the progress of the cementation reaction; to reach maximum. While solidifying the soil to the greatest extent, it also avoids solution and waste and prolonging the engineering cycle;
(6)本发明提供了喷洒、灌浆、滴灌和漫灌这四种激发和胶结工艺,发明的应用场景广泛,可适用于多种类的土质条件,包括砂土、粉砂土和黏性土等,以及多种要求的工程条件,包括水土保持、土体防裂、地基加固和堤坝加固等,发明根据不同的实际条件有针对性的给出了适用的工艺,工程应用性强;(6) The present invention provides four excitation and cementing processes of spraying, grouting, drip irrigation and flood irrigation. The invention has a wide range of application scenarios and can be applied to various soil conditions, including sandy soil, silt soil and cohesive soil, etc. And a variety of required engineering conditions, including soil and water conservation, soil crack prevention, foundation reinforcement and dam reinforcement, etc., the invention provides suitable processes according to different actual conditions, and has strong engineering applicability;
(7)本发明中激发液和胶结液中所用化学物质,均为无毒无害物质,环保性高;其中所用尿素是植被生长的重要肥料,后期可在土体上种植植物用于生态恢复;另外,不在土体中引入外源微生物,维护了自然环境的微生物平衡。(7) The chemical substances used in the excitation liquid and the cementing liquid in the present invention are all non-toxic and harmless substances, and have high environmental protection; wherein the urea used is an important fertilizer for vegetation growth, and plants can be planted on the soil body for ecological restoration in the later stage. ; In addition, no exogenous microorganisms are introduced into the soil, and the microbial balance of the natural environment is maintained.
附图说明Description of drawings
图1为实施例1中喷洒法进行原位激发培养微生物固化土体示意图;1 is a schematic diagram of in-situ excitation and cultivation of microorganisms to solidify soil by spraying method in Example 1;
图2为实施例12中滴灌法进行原位激发培养微生物固化土体示意图;2 is a schematic diagram of in-situ excitation and cultivation of microorganisms to solidify soil by drip irrigation method in Example 12;
图3为实施例13中漫灌法进行原位激发培养微生物固化土体示意图。FIG. 3 is a schematic diagram of the in-situ excitation and cultivation of microorganisms to solidify the soil by the flood irrigation method in Example 13. FIG.
图4为实施例14中灌浆法进行原位激发培养微生物固化土体示意图。FIG. 4 is a schematic diagram of the in-situ excitation and cultivation of microorganisms to solidify soil by the grouting method in Example 14. FIG.
图5为实施例1和对比例1A、1B中每一次喷洒激发液或菌液前测定的脲酶活性随测量次数变化曲线图。FIG. 5 is a graph showing the variation of urease activity with the number of measurements in Example 1 and Comparative Examples 1A and 1B before each spraying of the excitation liquid or bacterial liquid.
图6为实施例1和对比例1A、1B中每一次喷洒胶结液前测定的碳酸钙含量随测量次数变化曲线图。FIG. 6 is a graph showing the variation of calcium carbonate content with the number of measurements measured before each spraying of cementitious solution in Example 1 and Comparative Examples 1A and 1B.
图中:1、喷头;2、激发液/胶结液;3、胶结固化层;4、未处理土层;5、滴灌管;6、滴头;7、水龙头;8、注浆泵;9、注浆管;10、钻孔。In the picture: 1. Nozzle; 2. Exciting liquid/cementing liquid; 3. Cementing and solidifying layer; 4. Untreated soil layer; 5. Drip irrigation pipe; 6. Dripper; 7. Faucet; 8. Grouting pump; 9. Grouting pipe; 10. Drilling holes.
具体实施方式Detailed ways
除非另有定义,本文所使用的所有的技术和科学术语与属于本发明的技术领域的技术人员通常理解的含义相同;本文所使用的术语“和/或”包括一个或多个相关的所列项目的任意的和所有的组合。Unless otherwise defined, all technical and scientific terms used herein have the same meaning as commonly understood by one of ordinary skill in the art to which this invention belongs; as used herein, the term "and/or" includes one or more of the associated listed Any and all combinations of items.
实施例中未注明具体条件者,按照常规条件或制造商建议的条件进行。所用试剂或仪器未注明生产厂商者,均为可以通过市售购买获得的常规产品。If the specific conditions are not indicated in the examples, it is carried out according to the conventional conditions or the conditions suggested by the manufacturer. The reagents or instruments used without the manufacturer's indication are conventional products that can be purchased from the market.
如本文所使用,术语“约”用于提供与给定术语、度量或值相关联的灵活性和不精确性。本领域技术人员可以容易地确定具体变量的灵活性程度。As used herein, the term "about" is used to provide flexibility and imprecision associated with a given term, measure or value. The degree of flexibility of a particular variable can be readily determined by one skilled in the art.
浓度、量和其他数值数据可以在本文中以范围格式呈现。应当理解,这样的范围格式仅是为了方便和简洁而使用,并且应当灵活地解释为不仅包括明确叙述为范围极限的数值,而且还包括涵盖在所述范围内的所有单独的数值或子范围,就如同每个数值和子范围都被明确叙述一样。例如,约1至约4.5的数值范围应当被解释为不仅包括明确叙述的1至约4.5的极限值,而且还包括单独的数字(诸如2、3、4)和子范围(诸如1至3、2至4等)。相同的原理适用于仅叙述一个数值的范围,诸如“小于约4.5”,应当将其解释为包括所有上述的值和范围。此外,无论所描述的范围或特征的广度如何,都应当适用这种解释。Concentrations, amounts, and other numerical data may be presented herein in range format. It is to be understood that such range formats are used for convenience and brevity only, and are to be flexibly construed to include not only the values expressly recited as the limits of the range, but also all individual values or subranges subsumed within the stated range, As if each numerical value and sub-range were expressly stated. For example, a numerical range of about 1 to about 4.5 should be construed to include not only the expressly recited limit of 1 to about 4.5, but also individual numbers (such as 2, 3, 4) and subranges (such as 1 to 3, 2) to 4, etc.). The same principle applies to ranges reciting only one numerical value, such as "less than about 4.5," which should be construed to include all of the aforementioned values and ranges. Furthermore, this interpretation should apply regardless of the breadth of the scope or features described.
下面结合具体实施例对本发明进一步进行描述。The present invention will be further described below with reference to specific embodiments.
实施例1Example 1
本实施例土体为45°坡面,粉质黏土,土体渗透系数为5×10-6cm/s,工程环境温度为25℃,工程需求为提高土体抗侵蚀性,解决水土流失问题。In this example, the soil is a 45° slope, silty clay, the soil permeability coefficient is 5×10 -6 cm/s, and the engineering environment temperature is 25°C. The engineering requirements are to improve the soil erosion resistance and solve the problem of water and soil loss. .
1)通过标准贯入试验测定土体贯入强度,通过冲刷试验测定土体抗冲刷性,此处土体抗冲刷性定义为单位时间内的产土量。1) The penetration strength of the soil is measured by the standard penetration test, and the scour resistance of the soil is measured by the scour test, where the scour resistance of the soil is defined as the amount of soil produced per unit time.
2)从待处理土体中取样,测定土体的孔隙率为60%。土体处理面积S为10m2,处理深度H为0.1m。通过关系式(1)Ve=αnSH,计算激发液单次用量Ve(m3)。其中,激发液用量修正系数α取1.05,算得激发液单次用量为0.63m3。通过关系式(2)Vc=βVe,计算胶结液单次用量Vc(m3)。其中,胶结液单次用量与激发液单次用量之比β取1.0,算得激发液单次用量为0.63m3。2) Take samples from the soil to be treated, and measure the porosity of the soil to be 60%. The soil treatment area S is 10m 2 and the treatment depth H is 0.1m. According to the relational formula (1) V e =αnSH, the single dosage of excitation solution V e (m 3 ) is calculated. Wherein, the correction coefficient α of the dosage of the excitation liquid is taken as 1.05, and the single dosage of the excitation liquid is calculated as 0.63m 3 . According to the relational formula (2) V c =βV e , the single dosage of cementitious liquid V c (m 3 ) is calculated. Wherein, the ratio β of the single dosage of the cementing solution to the single dosage of the excitation solution was 1.0, and the single dosage of the excitation solution was calculated to be 0.63 m 3 .
3)如图1所示,根据步骤2)算得的激发液用量在土体中喷洒激发液,激发液成分为300mM尿素,20g/L酵母提取物,40g/L葡萄糖和0.13MTris-base缓冲液。在准备加入下一次激发液的前一天,取样,用电导率法测量土体中细菌脲酶活性,当脲酶活性大于0.06mghydrolysed urea min-1g-1时,停止加入激发液。本实施例中,每隔5d喷洒一次,喷洒过程缓慢均匀,保证覆盖目标处理面积,喷洒激发液第5轮后,达到上述指标(见图5),停止加液。3) As shown in Figure 1, spray the excitation solution in the soil according to the amount of the excitation solution calculated in step 2). The components of the excitation solution are 300mM urea, 20g/L yeast extract, 40g/L glucose and 0.13M Tris-base buffer. . One day before adding the next challenge solution, take a sample and measure the bacterial urease activity in the soil by the conductivity method. When the urease activity is greater than 0.06mghydrolysed urea min -1 g -1 , stop adding the challenge solution. In this embodiment, spray once every 5d, and the spraying process is slow and uniform to ensure that the target treatment area is covered. After the fifth round of spraying the excitation liquid, the above-mentioned indicators are reached (see Fig. 5), and the liquid addition is stopped.
4)如图1所示,根据步骤2)算得的胶结液用量在土体中加入胶结液,胶结液成分为1.0M尿素,1.0M氯化钙和5g/L营养肉汤。在准备加入下一次胶结液的前一天,取样,用盐酸酸洗排水法测量土体中碳酸钙含量,当碳酸钙含量大于4.0%时,停止加入胶结液。本实施例中,每隔5d加入一次,喷洒胶结液第5轮后,达到上述指标,停止加液。4) As shown in Figure 1, according to the amount of cementing liquid calculated in step 2), adding cementing liquid to the soil, the cementing liquid components are 1.0M urea, 1.0M calcium chloride and 5g/L nutrient broth. One day before the next cementing solution is to be added, samples are taken, and the calcium carbonate content in the soil is measured by the hydrochloric acid pickling drainage method. When the calcium carbonate content is greater than 4.0%, the cementing solution is stopped. In this example, the addition was done once every 5d, and after the fifth round of spraying the cementitious solution, the above-mentioned index was reached, and the addition of the solution was stopped.
5)对固化后的土体进行贯入试验,再次测得土体贯入强度和抗冲刷性。5) Carry out a penetration test on the solidified soil, and measure the penetration strength and erosion resistance of the soil again.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量5%,土体贯入强度提高55%,土体抗冲刷性提高55%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 5%, the penetration strength of the soil was increased by 55%, and the erosion resistance of the soil was improved by 55%. %.
对比例1AComparative Example 1A
本对比例土体条件和工程需求与实施例1相同,处理步骤与实施例1基本相同,区别在于:The soil conditions and engineering requirements of this comparative example are the same as those in Example 1, and the processing steps are basically the same as those in Example 1. The differences are:
不在土体中加入激发液,而是直接向土体中外加在培养基条件下培养的巴氏芽孢杆菌的细菌溶液(巴氏芽孢杆菌为工程常用的用于MICP处理的产脲酶细菌),加入菌液的脲酶活性为2.0mMhydrolysed urea min-1(这一活性的菌液为通常培养基条件下培养的脲酶活性较高的菌液),同样,在准备加入下一次菌液的前一天,测量土体中细菌脲酶活性,当脲酶活性大于0.06mg hydrolysed urea min-1g-1时,停止加入菌液。喷洒菌液第8轮后,达到上述指标,停止加液。之后,再向土体加入胶结液,加入轮次为6轮。Instead of adding the excitation solution to the soil body, directly add the bacterial solution of Bacillus Pasteurella cultured under the medium condition to the soil body (Bacillus Pasteurella is a urease-producing bacterium commonly used in engineering for MICP treatment), add The urease activity of the bacterial solution is 2.0 mM hydrolysed urea min -1 (the bacterial solution with this activity is the bacterial solution with higher urease activity cultivated under normal medium conditions). Similarly, the day before adding the next bacterial solution, measure Bacterial urease activity in the soil, when the urease activity is greater than 0.06mg hydrolysed urea min -1 g -1 , stop adding bacterial solution. After the 8th round of spraying the bacterial liquid, the above indicators were reached, and the liquid addition was stopped. After that, the cementing solution was added to the soil, and the addition round was 6 rounds.
实验结果:在本对比例中,利用向土体中外加含有产脲酶微生物的菌液,并进行MICP处理后,得到土体碳酸钙含量2.5%,土体贯入强度提高35%,土体抗冲刷性提高38%。Experimental results: In this comparative example, by adding a bacterial solution containing urease-producing microorganisms to the soil, and after MICP treatment, the calcium carbonate content of the soil was 2.5%, the penetration strength of the soil was increased by 35%, and the resistance of the soil was increased by 35%. 38% more washout.
对比例1BComparative Example 1B
本对比例土体条件和工程需求与实施例1相同,处理步骤与实施例1基本相同,区别在于:The soil conditions and engineering requirements of this comparative example are the same as those in Example 1, and the processing steps are basically the same as those in Example 1. The differences are:
αβ的取值小于1。激发液用量修正系数α取0.8;胶结液单次用量与激发液单次用量之比β取0.8。通过关系式(1)Ve=αnSH算得激发液单次用量为0.48m3,通过关系式(2)Vc=βVe算得胶结液单次用量为0.384m3。The value of αβ is less than 1. The correction coefficient α of the dosage of the excitation solution is taken as 0.8; According to the relational formula (1) V e =αnSH, the single dosage of the excitation solution is 0.48m 3 , and the single dosage of the cementitious liquid is 0.384m 3 according to the relational formula (2) V c =βV e .
本对比例中喷洒激发液第7轮后,停止加液;喷洒胶结液第6轮后,停止加液。In this comparative example, after the 7th round of spraying the excitation liquid, the liquid addition was stopped; after the 6th round of spraying the cementitious liquid, the liquid addition was stopped.
实验结果:在本对比例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量3.6%,土体贯入强度提高42%,土体抗冲刷性提高45%。Experimental results: In this comparative example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 3.6%, the penetration strength of the soil was increased by 42%, and the erosion resistance of the soil was improved by 45%. %.
实施例1和对比例1A、1B中,每一次喷洒激发液或菌液前测定的脲酶活性数据见图5;每一次喷洒胶结液前测定的碳酸钙含量数据见图6。通过对比实施例1和对比例1A可发现,实施例1中采用原位激发的方式微生物生长繁殖速度快,脲酶活性增长快,更快的达到MICP反应所需的微生物浓度,胶结过程中碳酸钙的生成速率高,更快达到胶结液的加入需求。实施例1中,溶液加入轮次少,大大节约了工程成本,缩短了工程周期。同时,实施例1中固化的土体较对比例1A的贯入强度和抗冲刷性均有较大提高,说明了本发明应用的激发培养原位微生物固化土体的方法的土体改良效果更明显,土体力学性质和工程性能提升更为显著,这与该方法培养的微生物分布更均匀,深度更深以及微生物活性更高有关。通过对比实施例1和对比例1B可发现,当αβ<1时,土体中微生物的脲酶活性增长更慢,即微生物在土体中被激发的速度更慢。同时,产生的碳酸钙沉淀速率也更慢,更难达到实验所需的碳酸钙含量指标,固化后土体的力学性能也较差。这会增长工程周期,降低土体处理效果,使难以达到工程需求,进一步说明了本发明中保证αβ>1的必要性。In Example 1 and Comparative Examples 1A and 1B, the urease activity data measured before each spraying of the excitation solution or bacterial solution is shown in Figure 5; the calcium carbonate content data measured before each spraying of the cementitious solution is shown in Figure 6. By comparing Example 1 and Comparative Example 1A, it can be found that in Example 1, the in-situ excitation method is used to stimulate the growth and reproduction of microorganisms rapidly, the urease activity increases rapidly, and the concentration of microorganisms required for the MICP reaction is reached faster. In the cementation process, calcium carbonate The formation rate is high, and the demand for cementing liquid can be reached faster. In Example 1, the number of times of adding the solution is small, which greatly saves the engineering cost and shortens the engineering cycle. At the same time, the penetration strength and scour resistance of the solidified soil in Example 1 are greatly improved compared to Comparative Example 1A, which shows that the method of stimulating the cultivation of in-situ microorganisms to solidify the soil applied in the present invention has a better soil improvement effect. Obviously, the improvement of soil mechanical properties and engineering performance is more significant, which is related to the more uniform distribution of microorganisms, deeper depth and higher microbial activity cultivated by this method. By comparing Example 1 and Comparative Example 1B, it can be found that when αβ<1, the urease activity of the microorganisms in the soil increases more slowly, that is, the speed at which the microorganisms are stimulated in the soil is slower. At the same time, the resulting calcium carbonate precipitation rate is also slower, it is more difficult to achieve the required calcium carbonate content index, and the mechanical properties of the solidified soil are also poor. This will increase the engineering period, reduce the soil treatment effect, and make it difficult to meet the engineering requirements, which further illustrates the necessity of ensuring αβ>1 in the present invention.
实施例2Example 2
本实施例土体条件和工程需求与实施例1相同,处理步骤与实施例1基本相同,区别在于:The soil conditions and engineering requirements of this example are the same as those of Example 1, and the processing steps are basically the same as those of Example 1. The differences are:
激发液用量修正系数α取1.15;胶结液单次用量与激发液单次用量之比β取0.9。通过关系式(1)Ve=αnSH算得激发液单次用量为0.69m3,通过关系式(2)Vc=βVe算得胶结液单次用量为0.621m3。The correction coefficient α of the dosage of the excitation solution is taken as 1.15; According to the relational formula (1) V e =αnSH, the single dosage of the excitation liquid is 0.69m 3 , and the single dosage of the cementing liquid is 0.621m 3 calculated from the relational formula (2) V c =βV e .
本实例中喷洒激发液第5轮后,停止加液;喷洒胶结液第6轮后,停止加液。In this example, after the fifth round of spraying the excitation liquid, the liquid addition was stopped; after the sixth round of spraying the cementitious liquid, the liquid addition was stopped.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量6.3%,土体贯入强度提高56%,土体抗冲刷性提高58%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 6.3%, the penetration strength of the soil was increased by 56%, and the erosion resistance of the soil was improved by 58%. %.
实施例3Example 3
本实施例土体条件和工程需求与实施例1相同,处理步骤与实施例1基本相同,区别在于:The soil conditions and engineering requirements of this example are the same as those of Example 1, and the processing steps are basically the same as those of Example 1. The differences are:
激发液用量修正系数α取1.1;胶结液单次用量与激发液单次用量之比β取1.1。通过关系式(1)Ve=αnSH算得激发液单次用量为0.66m3,通过关系式(2)Vc=βVe算得胶结液单次用量为0.726m3。The correction coefficient α of the dosage of the excitation solution is taken as 1.1; According to the relational formula (1) V e =αnSH, the single dosage of the excitation solution is 0.66m 3 , and the single dosage of the cementing liquid is 0.726m 3 according to the relational formula (2) V c =βV e .
激发液成分为200mM尿素,20g/L酵母提取物,40g/L葡萄糖和0.13MTris-base缓冲液;胶结液成分为1.0M尿素,1.0M氯化钙和5g/L营养肉汤。The components of the excitation solution are 200mM urea, 20g/L yeast extract, 40g/L glucose and 0.13M Tris-base buffer; the components of the cementing solution are 1.0M urea, 1.0M calcium chloride and 5g/L nutrient broth.
本实例中喷洒激发液第5轮后,停止加液;喷洒胶结液第6轮后,停止加液。In this example, after the fifth round of spraying the excitation liquid, the liquid addition was stopped; after the sixth round of spraying the cementitious liquid, the liquid addition was stopped.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量5.5%,土体贯入强度提高40%,土体抗冲刷性提高45%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 5.5%, the penetration strength of the soil was increased by 40%, and the erosion resistance of the soil was improved by 45%. %.
实施例4Example 4
本实施例土体条件和工程需求与实施例1相同,处理步骤与实施例3基本相同,区别在于:The soil conditions and engineering requirements of this embodiment are the same as those of
激发液成分为300mM尿素,20g/L酵母提取物,40g/L葡萄糖和0.13MTris-base缓冲液;胶结液成分为1.0M尿素,1.0M氯化钙和5g/L营养肉汤。The components of the excitation solution are 300mM urea, 20g/L yeast extract, 40g/L glucose and 0.13M Tris-base buffer; the components of the cementing solution are 1.0M urea, 1.0M calcium chloride and 5g/L nutrient broth.
本实例中喷洒激发液第5轮后,停止加液;喷洒胶结液第6轮后,停止加液。In this example, after the fifth round of spraying the excitation liquid, the liquid addition was stopped; after the sixth round of spraying the cementitious liquid, the liquid addition was stopped.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量6.8%,土体贯入强度提高65%,土体抗冲刷性提高65%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 6.8%, the penetration strength of the soil was increased by 65%, and the erosion resistance of the soil was improved by 65%. %.
实施例5Example 5
本实施例土体条件和工程需求与实施例1相同,处理步骤与实施例3基本相同,区别在于:The soil conditions and engineering requirements of this embodiment are the same as those of
激发液成分为500mM尿素,20g/L酵母提取物,40g/L葡萄糖和0.13MTris-base缓冲液;胶结液成分为1.0M尿素,1.0M氯化钙和5g/L营养肉汤。The components of the excitation solution are 500mM urea, 20g/L yeast extract, 40g/L glucose and 0.13M Tris-base buffer; the components of the cementing solution are 1.0M urea, 1.0M calcium chloride and 5g/L nutrient broth.
本实例中喷洒激发液第6轮后,停止加液;喷洒胶结液第6轮后,停止加液。In this example, after the 6th round of spraying the excitation liquid, the liquid addition was stopped; after the 6th round of spraying the cementitious liquid, the liquid addition was stopped.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量6.5%,土体贯入强度提高60%,土体抗冲刷性提高58%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 6.5%, the penetration strength of the soil was increased by 60%, and the erosion resistance of the soil was improved by 58%. %.
实施例6Example 6
本实施例土体条件和工程需求与实施例1相同,处理步骤与实施例3基本相同,区别在于:The soil conditions and engineering requirements of this embodiment are the same as those of
激发液成分为300mM尿素,20g/L酵母提取物,40g/L葡萄糖和0.13MTris-base缓冲液;胶结液成分为0.1M尿素,0.3M氯化钙和5g/L营养肉汤。The components of the excitation solution are 300mM urea, 20g/L yeast extract, 40g/L glucose and 0.13M Tris-base buffer; the components of the cementing solution are 0.1M urea, 0.3M calcium chloride and 5g/L nutrient broth.
本实例中喷洒激发液第5轮后,停止加液;喷洒胶结液第6轮后,停止加液。In this example, after the fifth round of spraying the excitation liquid, the liquid addition was stopped; after the sixth round of spraying the cementitious liquid, the liquid addition was stopped.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量4%,土体贯入强度提高20%,土体抗冲刷性提高25%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 4%, the penetration strength of the soil was increased by 20%, and the erosion resistance of the soil was improved by 25%. %.
实施例7Example 7
本实施例土体条件和工程需求与实施例1相同,处理步骤与实施例3基本相同,区别在于:The soil conditions and engineering requirements of this embodiment are the same as those of
激发液成分为300mM尿素,20g/L酵母提取物,40g/L葡萄糖和0.13MTris-base缓冲液;胶结液成分为0.1M尿素,0.3M氯化钙和5g/L营养肉汤。The components of the excitation solution are 300mM urea, 20g/L yeast extract, 40g/L glucose and 0.13M Tris-base buffer; the components of the cementing solution are 0.1M urea, 0.3M calcium chloride and 5g/L nutrient broth.
本实例中喷洒激发液第6轮后,停止加液;喷洒胶结液第6轮后,停止加液。In this example, after the 6th round of spraying the excitation liquid, the liquid addition was stopped; after the 6th round of spraying the cementitious liquid, the liquid addition was stopped.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量4%,土体贯入强度提高25%,土体抗冲刷性提高23%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 4%, the penetration strength of the soil was increased by 25%, and the erosion resistance of the soil was improved by 23%. %.
实施例8Example 8
本实施例土体条件和工程需求与实施例1相同,处理步骤与实施例3基本相同,区别在于:The soil conditions and engineering requirements of this embodiment are the same as those of
激发液成分为300mM尿素,20g/L酵母提取物,40g/L葡萄糖和0.13MTris-base缓冲液;胶结液成分为2.0M尿素,2.0M氯化钙和5g/L营养肉汤。The components of the excitation solution are 300mM urea, 20g/L yeast extract, 40g/L glucose and 0.13M Tris-base buffer; the components of the cementing solution are 2.0M urea, 2.0M calcium chloride and 5g/L nutrient broth.
本实例中喷洒激发液第6轮后,停止加液;喷洒胶结液第7轮后,停止加液。In this example, after the 6th round of spraying the excitation liquid, the liquid addition was stopped; after the 7th round of spraying the cementitious liquid, the liquid addition was stopped.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量4%,土体贯入强度提高25%,土体抗冲刷性提高25%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 4%, the penetration strength of the soil was increased by 25%, and the erosion resistance of the soil was improved by 25%. %.
实施例9Example 9
本实施例土体条件和工程需求与实施例1基本相同,处理步骤与实施例4相同,区别在于:The soil conditions and engineering requirements of this embodiment are basically the same as those of
本实施例工程环境温度为5℃。The engineering ambient temperature in this embodiment is 5°C.
本实施例中喷洒激发液第7轮后,停止加液;喷洒胶结液第7轮后,停止加液。在处理前后分别进行标准贯入试验测定土体贯入强度。In this example, after the 7th round of spraying the excitation liquid, the liquid addition was stopped; after the 7th round of spraying the cementitious liquid, the liquid addition was stopped. Standard penetration tests were performed before and after treatment to determine soil penetration strength.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量4%,土体贯入强度提高30%,土体抗冲刷性提高35%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 4%, the penetration strength of the soil was increased by 30%, and the erosion resistance of the soil was improved by 35%. %.
实施例10Example 10
本实施例土体条件和工程需求与实施例1基本相同,处理步骤与实施例4相同,区别在于:The soil conditions and engineering requirements of this embodiment are basically the same as those of
本实施例工程环境温度为40℃。The engineering ambient temperature in this embodiment is 40°C.
本实施例中喷洒激发液第7轮后,停止加液;喷洒胶结液第7轮后,停止加液。在处理前后分别进行标准贯入试验测定土体贯入强度。In this example, after the 7th round of spraying the excitation liquid, the liquid addition was stopped; after the 7th round of spraying the cementitious liquid, the liquid addition was stopped. Standard penetration tests were performed before and after treatment to determine soil penetration strength.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量4%,土体贯入强度提高35%,土体抗冲刷性提高40%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 4%, the penetration strength of the soil was increased by 35%, and the erosion resistance of the soil was increased by 40%. %.
实施例11Example 11
本实施例土体为平坦土地,粉土,土体渗透系数为5×10-5cm/s,工程环境温度为25℃,工程需求为步行道的小规模改造,只需提供硬化壳。The soil in this example is flat land, silt, the soil permeability coefficient is 5 × 10 -5 cm/s, and the engineering ambient temperature is 25°C. The engineering requirement is small-scale reconstruction of the walkway, and only a hardened shell needs to be provided.
1)通过标准贯入试验测定土体贯入强度。1) Determination of soil penetration strength by standard penetration test.
2)从待处理土体中取样,测定土体的孔隙率为55%。土体处理面积S为10m2,处理深度H为0.2m。通过关系式(1)Ve=αnSH,计算激发液单次用量Ve(m3)。其中,激发液用量修正系数α取1.2,算得激发液单次用量为1.32m3。通过关系式(2)Vc=βVe,计算胶结液单次用量Vc(m3)。其中,胶结液单次用量与激发液单次用量之比β取1.2,算得激发液单次用量为1.584m3。2) Take samples from the soil to be treated, and measure the porosity of the soil to be 55%. The soil treatment area S is 10m 2 and the treatment depth H is 0.2m. According to the relational formula (1) V e =αnSH, the single dosage of excitation solution V e (m 3 ) is calculated. Among them, the correction coefficient α of the amount of excitation liquid is taken as 1.2, and the single consumption of the excitation liquid is calculated as 1.32m 3 . According to the relational formula (2) V c =βV e , the single dosage of cementitious liquid V c (m 3 ) is calculated. Wherein, the ratio β of the single dosage of the cementing solution to the single dosage of the excitation solution was 1.2, and the single dosage of the excitation solution was calculated to be 1.584m 3 .
3)如图2所示,根据步骤2)算得的激发液用量,用滴灌法将激发液加入土中,相邻滴灌管间距1.0m,相邻滴头间距1.0m。激发液成分为300mM尿素,20g/L酵母提取物,40g/L葡萄糖和0.13MTris-base缓冲液。在准备加入下一次激发液的前一天,取样,用电导率法测量土体中细菌脲酶活性,当脲酶活性大于0.06mg hydrolysed urea min-1g-1时,停止加入激发液。本实施例中,每隔4d加入一次,加入激发液第5轮后,达到上述指标,停止加液。3) As shown in Figure 2, according to the amount of excitation liquid calculated in step 2), the excitation liquid is added to the soil by drip irrigation method, the distance between adjacent drip irrigation pipes is 1.0m, and the distance between adjacent drippers is 1.0m. The components of the challenge solution were 300 mM urea, 20 g/L yeast extract, 40 g/L glucose and 0.13 M Tris-base buffer. One day before adding the next challenge solution, take a sample and measure the bacterial urease activity in the soil by conductivity method. When the urease activity is greater than 0.06mg hydrolysed urea min -1 g -1 , stop adding the challenge solution. In this example, the addition was done once every 4 d, and after the fifth round of adding the excitation solution, the above-mentioned index was reached, and the addition of the solution was stopped.
4)如图2所示,根据步骤2)算得的胶结液用量在土体中加入胶结液,胶结液成分为1.0M尿素,1.0M氯化钙和5g/L营养肉汤。在准备加入下一次胶结液的前一天,取样,用盐酸酸洗排水法测量土体中碳酸钙含量,当碳酸钙含量大于4.0%时,停止加入胶结液。本实施例中,每隔4d加入一次。加入胶结液第5轮后,达到上述指标,停止加液。4) As shown in Figure 2, according to the amount of cementing liquid calculated in step 2), adding cementing liquid to the soil, the cementing liquid components are 1.0M urea, 1.0M calcium chloride and 5g/L nutrient broth. One day before the next cementing solution is to be added, samples are taken, and the calcium carbonate content in the soil is measured by the hydrochloric acid pickling drainage method. When the calcium carbonate content is greater than 4.0%, the cementing solution is stopped. In this embodiment, it is added every 4d. After the fifth round of adding the cementitious liquid, the above-mentioned indicators were reached, and the liquid addition was stopped.
5)对固化后的土体进行贯入试验,再次测得土体贯入强度。5) Carry out a penetration test on the solidified soil, and measure the penetration strength of the soil again.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量7.5%,土体贯入强度提高70%。Experimental results: In this example, the method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 7.5%, and the penetration strength of the soil was increased by 70%.
实施例12Example 12
本实施例土体为平坦土地,粉砂土,土体渗透系数为5×10-4cm/s,工程环境温度为25℃,工程需求为提高小型建筑的地基承载力。The soil in this example is flat land, silt soil, the soil permeability coefficient is 5×10 -4 cm/s, and the engineering ambient temperature is 25°C. The engineering requirement is to improve the foundation bearing capacity of small buildings.
1)通过标准贯入试验测定土体贯入强度,通过无侧限抗压强度试验测定土体无侧限抗压强度。1) The penetration strength of the soil mass is determined by the standard penetration test, and the unconfined compressive strength of the soil mass is determined by the unconfined compressive strength test.
2)从待处理土体中取样,测定土体的孔隙率为45%。土体处理面积S为10m2,处理深度H为0.8m。通过关系式(1)Ve=αnSH,计算激发液单次用量Ve(m3)。其中,激发液用量修正系数α取1.3,算得激发液单次用量为4.68m3。通过关系式(2)Vc=βVe,计算胶结液单次用量Ve(m3)。其中,胶结液单次用量与激发液单次用量之比β取1.3,算得激发液单次用量为6.084m3。2) Take samples from the soil to be treated, and measure the porosity of the soil to be 45%. The soil treatment area S is 10m 2 and the treatment depth H is 0.8m. According to the relational formula (1) V e =αnSH, the single dosage of excitation solution V e (m 3 ) is calculated. Among them, the correction coefficient α of the amount of the excitation liquid is taken as 1.3, and the single consumption of the excitation liquid is calculated to be 4.68m 3 . Through the relational formula (2) V c =βV e , the single dosage of cementing solution V e (m 3 ) is calculated. Wherein, the ratio β of the single dosage of the cementing solution to the single dosage of the excitation solution was taken as 1.3, and the single dosage of the excitation solution was calculated to be 6.084m 3 .
3)如图3所示,根据步骤2)算得的激发液用量,用漫灌法将激发液加入土中,漫灌过程水流不易过快或过慢,保证溶液均匀入渗,覆盖目标处理区域即可。激发液成分为300mM尿素,20g/L酵母提取物,40g/L葡萄糖和0.13MTris-base缓冲液。在准备加入下一次激发液的前一天,取样,用电导率法测量土体中细菌脲酶活性,当脲酶活性大于0.06mghydrolysed urea min-1g-1时,停止加入激发液。本实施例中,每隔3d加入一次,达到上述指标,加入激发液第5轮后,停止加液。3) As shown in Figure 3, according to the amount of the excitation solution calculated in step 2), the excitation solution is added to the soil by the flood irrigation method, and the water flow during the flood irrigation process is not easy to be too fast or too slow, to ensure that the solution infiltrates uniformly and covers the target treatment area. . The components of the challenge solution were 300 mM urea, 20 g/L yeast extract, 40 g/L glucose and 0.13 M Tris-base buffer. One day before adding the next challenge solution, take a sample and measure the bacterial urease activity in the soil by the conductivity method. When the urease activity is greater than 0.06mghydrolysed urea min -1 g -1 , stop adding the challenge solution. In this example, the addition was done once every 3 days to reach the above-mentioned index, and after the fifth round of adding the excitation solution, the addition of the solution was stopped.
4)如图3所示,根据步骤2)算得的胶结液用量在土体中加入胶结液,胶结液成分为1.0M尿素,1.0M氯化钙和5g/L营养肉汤。在准备加入下一次胶结液的前一天,取样,用盐酸酸洗排水法测量土体中碳酸钙含量,当碳酸钙含量大于8.0%时,停止加入胶结液。本实施例中,每隔3d加入一次,达到上述指标,加入胶结液第6轮后,停止加液。4) As shown in Figure 3, according to the amount of cementing liquid calculated in step 2), adding cementing liquid to the soil, the cementing liquid components are 1.0M urea, 1.0M calcium chloride and 5g/L nutrient broth. One day before the next cementing solution is to be added, the samples are taken, and the calcium carbonate content in the soil is measured by the hydrochloric acid pickling drainage method. When the calcium carbonate content is greater than 8.0%, the cementing solution is stopped. In this example, the addition was done once every 3 days to reach the above-mentioned index, and after the sixth round of adding the cementitious liquid, the addition of the liquid was stopped.
5)对固化后的土体进行贯入试验,再次测得土体贯入强度和无侧限抗压强度。5) Carry out a penetration test on the solidified soil, and measure the penetration strength and unconfined compressive strength of the soil again.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量8%,土体贯入强度提高90%,无侧限抗压强度提高80%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 8%, the penetration strength of the soil was increased by 90%, and the unconfined compressive strength was improved. 80%.
实施例13Example 13
本实例土体为40°坡体,细砂土,土体渗透系数为5×10-3cm/s,工程环境温度为25℃,工程需求为承载力提高需求较深的中型建筑地基处理。The soil in this example is a 40° slope, fine sandy soil, the soil permeability coefficient is 5×10 -3 cm/s, and the engineering ambient temperature is 25°C.
1)通过标准贯入试验测定土体贯入强度,通过无侧限抗压强度试验测定土体无侧限抗压强度。1) The penetration strength of the soil mass is determined by the standard penetration test, and the unconfined compressive strength of the soil mass is determined by the unconfined compressive strength test.
2)从待处理土体中取样,测定土体的孔隙率为40%。土体处理面积S为10m2,处理深度H为2m。通过关系式(1)Ve=αnSH,计算激发液单次用量Ve(m3)。其中,激发液用量修正系数α取1.4,算得激发液单次用量为11.2m3。通过关系式(2)Vc=βVe,计算胶结液单次用量Vc(m3)。其中,胶结液单次用量与激发液单次用量之比β取1.4,算得激发液单次用量为15.68m3。2) Take samples from the soil to be treated, and measure the porosity of the soil to be 40%. The soil treatment area S is 10m 2 and the treatment depth H is 2m. According to the relational formula (1) V e =αnSH, the single dosage of excitation solution V e (m 3 ) is calculated. Wherein, the correction coefficient α of the dosage of the excitation liquid is taken as 1.4, and the single dosage of the excitation liquid is calculated as 11.2m 3 . According to the relational formula (2) V c =βV e , the single dosage of cementitious liquid V c (m 3 ) is calculated. Among them, the ratio β of the single dosage of the cementing solution to the single dosage of the excitation solution was taken as 1.4, and the single dosage of the excitation solution was calculated to be 15.68m 3 .
3)如图4所示,根据步骤2)算得的激发液用量,用灌浆法将激发液加入土中,具体方法是在土体上开设钻孔,钻孔内径10cm,钻孔深度2.0m,相邻钻孔间距1.0m,钻孔呈正方形网格状均匀分布,通过注浆管注浆。激发液成分为300mM尿素,20g/L酵母提取物,40g/L葡萄糖和0.13MTris-base缓冲液。在准备加入下一次激发液的前一天,取样,用电导率法测量土体中细菌脲酶活性,当脲酶活性大于0.06mg hydrolysed urea min-1g-1时,停止加入激发液。本实施例中,每隔3d加入一次,加入激发液第5轮后,达到上述指标,停止加液。3) As shown in Figure 4, according to the amount of the excitation liquid calculated in step 2), the excitation liquid is added to the soil by the grouting method, and the concrete method is to open a hole in the soil body, the inner diameter of the hole is 10cm, and the depth of the hole is 2.0m, The spacing between adjacent drilling holes is 1.0m, and the drilling holes are evenly distributed in a square grid shape, and grouting is carried out through a grouting pipe. The components of the challenge solution were 300 mM urea, 20 g/L yeast extract, 40 g/L glucose and 0.13 M Tris-base buffer. One day before adding the next challenge solution, take a sample and measure the bacterial urease activity in the soil by conductivity method. When the urease activity is greater than 0.06mg hydrolysed urea min -1 g -1 , stop adding the challenge solution. In this example, the addition was performed once every 3 days, and after the fifth round of adding the excitation solution, the above-mentioned index was reached, and the addition of the solution was stopped.
4)如图4所示,根据步骤2)算得的胶结液用量在土体中加入胶结液,胶结液成分为1.0M尿素,1.0M氯化钙和5g/L营养肉汤。在准备加入下一次胶结液的前一天,取样,用盐酸酸洗排水法测量土体中碳酸钙含量,当碳酸钙含量大于4.0%时,停止加入胶结液。本实施例中,每隔3d加入一次,加入胶结液第5轮后,达到上述指标,停止加液。4) As shown in Figure 4, according to the amount of cementing liquid calculated in step 2), adding cementing liquid to the soil, the cementing liquid components are 1.0M urea, 1.0M calcium chloride and 5g/L nutrient broth. One day before the next cementing solution is to be added, samples are taken, and the calcium carbonate content in the soil is measured by the hydrochloric acid pickling drainage method. When the calcium carbonate content is greater than 4.0%, the cementing solution is stopped. In this example, the addition was done once every 3 days, and after the fifth round of adding the cementitious solution, the above-mentioned index was reached, and the addition of the solution was stopped.
5)对固化后的土体进行贯入试验,再次测得土体贯入强度和无侧限抗压强度。5) Carry out a penetration test on the solidified soil, and measure the penetration strength and unconfined compressive strength of the soil again.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量10%,土体贯入强度提高150%,无侧限抗压强度提高120%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 10%, the penetration strength of the soil was increased by 150%, and the unconfined compressive strength was improved. 120%.
实施例14Example 14
本实例土体为40°坡体,中砂土,土体渗透系数为5×10-2cm/s,工程环境温度为25℃,工程需求为承载力提高需求较深的大型建筑地基处理。The soil in this example is a 40° slope, medium sandy soil, the soil permeability coefficient is 5×10 -2 cm/s, and the engineering ambient temperature is 25°C.
1)通过标准贯入试验测定土体贯入强度,通过无侧限抗压强度试验测定土体无侧限抗压强度。1) The penetration strength of the soil mass is determined by the standard penetration test, and the unconfined compressive strength of the soil mass is determined by the unconfined compressive strength test.
2)从待处理土体中取样,测定土体的孔隙率为35%。土体处理面积S为10m2,处理深度H为3m。通过关系式(1)Ve=αnSH,计算激发液单次用量Ve(m3)。其中,激发液用量修正系数α取1.5,算得激发液单次用量为15.75m3。通过关系式(2)Vc=βVe,计算胶结液单次用量Ve(m3)。其中,胶结液单次用量与激发液单次用量之比β取1.5,算得激发液单次用量为23.625m3。2) Take samples from the soil to be treated, and measure the porosity of the soil to be 35%. The soil treatment area S is 10m 2 and the treatment depth H is 3m. According to the relational formula (1) V e =αnSH, the single dosage of excitation solution V e (m 3 ) is calculated. Among them, the correction coefficient α of the amount of excitation liquid is taken as 1.5, and the single consumption of excitation liquid is calculated as 15.75m 3 . According to the relational formula (2) V c =βV e , the single dosage of cementing solution V e (m 3 ) is calculated. Among them, the ratio β of the single dosage of the cementing solution to the single dosage of the excitation solution was taken as 1.5, and the single dosage of the excitation solution was calculated to be 23.625m 3 .
3)如图4所示,根据步骤2)算得的激发液用量,用灌浆法将激发液加入土中,激发液成分为300mM尿素,20g/L酵母提取物,40g/L葡萄糖和0.13MTris-base缓冲液。在准备加入下一次激发液的前一天,取样,用电导率法测量土体中细菌脲酶活性,当脲酶活性大于0.06mg hydrolysed urea min-1g-1时,停止加入激发液。本实施例中,每隔2d加入一次,加入激发液第4轮后,达到上述指标,停止加液。3) As shown in Figure 4, according to the amount of the excitation solution calculated in step 2), the excitation solution is added to the soil by the grouting method, and the components of the excitation solution are 300mM urea, 20g/L yeast extract, 40g/L glucose and 0.13MTris- base buffer. One day before adding the next challenge solution, take a sample and measure the bacterial urease activity in the soil by conductivity method. When the urease activity is greater than 0.06mg hydrolysed urea min -1 g -1 , stop adding the challenge solution. In this example, the addition was performed once every 2 d, and after the fourth round of adding the excitation solution, the above-mentioned index was reached, and the addition of the solution was stopped.
4)如图4所示,根据步骤2)算得的胶结液用量在土体中加入胶结液,胶结液成分为1.0M尿素,1.0M氯化钙和5g/L营养肉汤。在准备加入下一次胶结液的前一天,取样,用盐酸酸洗排水法测量土体中碳酸钙含量,当碳酸钙含量大于8.0%时,停止加入胶结液。本实施例中,每隔2d加入一次,加入激发液第5轮后,达到上述指标,停止加液。4) As shown in Figure 4, according to the amount of cementing liquid calculated in step 2), adding cementing liquid to the soil, the cementing liquid components are 1.0M urea, 1.0M calcium chloride and 5g/L nutrient broth. One day before the next cementing solution is to be added, the samples are taken, and the calcium carbonate content in the soil is measured by the hydrochloric acid pickling drainage method. When the calcium carbonate content is greater than 8.0%, the cementing solution is stopped. In this example, the addition was done once every 2d, and after the fifth round of adding the excitation solution, the above-mentioned index was reached, and the addition of the solution was stopped.
5)对固化后的土体进行贯入试验,再次测得土体贯入强度和无侧限抗压强度。5) Carry out a penetration test on the solidified soil, and measure the penetration strength and unconfined compressive strength of the soil again.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量12%,土体贯入强度提高200%,无侧限抗压强度提高150%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 12%, the penetration strength of the soil was increased by 200%, and the unconfined compressive strength was improved. 150%.
实施例15Example 15
本实例土体条件和工程需求与实施例14相同。本实施例处理步骤与实施例14基本相同,区别在于:The soil conditions and engineering requirements of this example are the same as those of Example 14. The processing steps of this embodiment are basically the same as those of Embodiment 14, the differences are:
激发液用量修正系数α取1.55;胶结液单次用量与激发液单次用量之比β取1.55。通过关系式(1)Ve=αnSH算得激发液单次用量为16.275m3,通过关系式(2)Vc=βVe算得胶结液单次用量为25.22625m3。The correction coefficient α of the dosage of the excitation solution is taken as 1.55; According to the relational formula (1) V e =αnSH, the single dosage of the excitation solution is 16.275m 3 , and the single dosage of the cementitious liquid is 25.22625m 3 calculated from the relational formula (2) V c =βV e .
本实例中加入激发液第4轮后,停止加液;加入胶结液第5轮后,停止加液。In this example, after the 4th round of adding the excitation liquid, the liquid addition was stopped; after the 5th round of adding the cementitious liquid, the liquid addition was stopped.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量12.5%,土体贯入强度提高220%,土体抗冲刷性提高160%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 12.5%, the penetration strength of the soil was increased by 220%, and the erosion resistance of the soil was increased by 160%. %.
实施例16Example 16
本实例土体条件和工程需求与实施例14相同。本实施例处理步骤与实施例14基本相同,区别在于:The soil conditions and engineering requirements of this example are the same as those of Example 14. The processing steps of this embodiment are basically the same as those of Embodiment 14, the differences are:
胶结液和激发液相邻两次的加入间隔天数均为4d。The interval between two consecutive additions of the cementing solution and the exciting solution was 4 days.
本实例中加入激发液第4轮后,停止加液;加入胶结液第4轮后,停止加液。In this example, after the 4th round of adding the excitation liquid, the liquid addition was stopped; after the 4th round of adding the cementitious liquid, the liquid addition was stopped.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量12.8%,土体贯入强度提高230%,土体抗冲刷性提高165%。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 12.8%, the penetration strength of the soil was increased by 230%, and the erosion resistance of the soil was improved by 165%. %.
实施例17Example 17
本实施例土体条件和工程需求与实施例1相同,处理步骤与实施例1基本相同,区别在于:The soil conditions and engineering requirements of this example are the same as those of Example 1, and the processing steps are basically the same as those of Example 1. The differences are:
土体处理面积为1000m2。The soil treatment area is 1000m 2 .
激发液用量修正系数α取1.15;胶结液单次用量与激发液单次用量之比β取0.9。通过关系式(1)Ve=αnSH算得激发液单次用量为69m3,通过关系式(2)Vc=βVe算得胶结液单次用量为62.1m3。The correction coefficient α of the dosage of the excitation solution is taken as 1.15; According to the relational formula (1) V e = αnSH, the single dosage of the excitation solution is 69 m 3 , and the single dosage of the cementing liquid is 62.1 m 3 calculated from the relation (2) V c = βV e .
本实例中喷洒激发液第5轮后,停止加液;喷洒胶结液第6轮后,停止加液。In this example, after the fifth round of spraying the excitation liquid, the liquid addition was stopped; after the sixth round of spraying the cementitious liquid, the liquid addition was stopped.
实验结果:在本实施例中,利用此方法原位激发产脲酶微生物,并进行MICP处理后,得到土体碳酸钙含量6.1%,土体贯入强度提高58%,土体抗冲刷性提高68%。本发明对土体的处理面积没有限制,具有通用性,以此实施例进一步进行了说明。Experimental results: In this example, this method was used to stimulate urease-producing microorganisms in situ, and after MICP treatment, the calcium carbonate content of the soil was 6.1%, the penetration strength of the soil was increased by 58%, and the erosion resistance of the soil was improved by 68%. %. The present invention has no limitation on the treatment area of the soil body, and has universality, which is further described with this embodiment.
以上示意性的对本发明及其实施方式进行了描述,该描述没有限制性,附图中所示的也只是本发明的实施方式之一,实际的结构并不局限于此。所以,如果本领域的普通技术人员受其启示,在不脱离本发明创造宗旨的情况下,不经创造性的设计出与该技术方案相似的结构方式及实施例,均应属于本发明的保护范围。The present invention and its embodiments have been described above schematically, and the description is not restrictive, and what is shown in the accompanying drawings is only one of the embodiments of the present invention, and the actual structure is not limited thereto. Therefore, if those of ordinary skill in the art are inspired by it, without departing from the purpose of the present invention, any structural modes and embodiments similar to this technical solution are designed without creativity, which shall belong to the protection scope of the present invention. .
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