KR20010100064A - Method for preparing liquid microbe material and accelated medicines for promoting nutrition for reducing contaminated soil and Method for bioremedition - Google Patents

Abstract

The present invention provides a method for producing a liquid microbial agent comprising a microorganism having a degrading ability to inhabit the surroundings contaminated with a specific material in order to promote the decomposition of the pollutant in the soil, and the microorganisms or indigenous microorganisms in the liquid microbial agent or The present invention relates to a method for preparing an accelerated nutrient for promoting the activity of foreign microorganisms and to accelerate the expression of contaminant degrading enzymes, and a biological purification method using the accelerated nutrients prepared by the method.

According to the present invention, for the biological purification of contaminated soil, especially soil contaminated by oil, high-speed cultivation and formulation of specific degrading microbial strains is applied and decomposition of accelerating nutrients and contaminants to promote the growth of foreign or indigenous microorganisms. The use of accelerated nutrients to promote the expression of enzymes directly involved in the process can significantly shorten the cleanup time of contaminated soils and consequently significantly reduce the cleanup costs of contaminated soils.

Description

Methods for preparing liquid microbe material and accelated medicines for promoting nutrition for reducing contaminated soil and Method for bioremedition}

The present invention provides a method for producing a liquid microbial agent comprising a microorganism having a degrading ability to inhabit the surroundings contaminated with a specific material in order to promote the decomposition of contaminants in the soil, and the microorganisms or indigenous microorganisms in the liquid microbial agent The present invention relates to a method for preparing an accelerated nutrient for promoting the activity and the expression of enzymes, and a biological purification method using them.

Rapid industrialization faces severe environmental pollution due to increased fossil fuel consumption, soaring pollutant emissions, population concentration in large cities, and natural destruction due to unreasonable development plans. Such environmental pollution not only has a rapid and direct effect on human life through the air or water, but also is exposed slowly through soil and groundwater for a long time. In particular, soil contamination caused by improper disposal of hazardous substances in the past, damage to old facilities, and sudden environmental accidents has been neglected for a long time due to wide range of pollution and huge disposal costs.

Contaminants that cause soil pollution can be oils such as diesel oil, diesel oil, heavy oil, lubricating oil, chlorophenol, polychlorinated biphenyl, polycyclic aromatic hydrocarbons, heavy metals, among which organic compounds based on hydrocarbons. Is used as a carbon source and energy source of certain microorganisms, and has biodegradation properties without any environmental pollution.

Biodegradation is a phenomenon in which certain microorganisms in natural ecosystems decompose harmful pollutants under proper conditions and use them as harmless or nutrient sources.By using these functions of microorganisms, biodegradation is used to pollute soil, groundwater, ocean and rivers. Comprehensive engineering techniques to purify are called bioremediation. If biological restoration techniques are effective, the end product must be converted into a harmless substance, such as water or carbon dioxide, to harm the environment or the organism. Such biological restoration technology is economical, and it has been recently spotlighted because there is an advantage that there is no secondary pollutant by using the purification ability of nature.

Bioremediation can be broadly classified into active restoration and passive restoration, depending on whether external techniques are applied to accelerate natural degradation in contaminated areas. Active restoration technology can be classified into on-site technology, which is treated on-site as it is for convenience, and off-site technology to which technology is applied by moving pollution mediators off-site for convenience.

For example, landfarming is a technique that can be applied in situ on contaminated soil near the surface. To promote the growth of microorganisms, nutrients, including nitrogen and phosphorus, are added to control water, and lime is used to control pH. In order to smoothly supply oxygen, a method of periodically inverting is used. In addition, microstimulation method that promotes the activity of microorganisms while using microorganisms already existing in contaminated soil is applied to soil cultivation technology, and microorganism injection method that adds foreign microorganisms having excellent resolution to specific pollutants ( Bioaugmentation may be applied. Soil cultivation technology can be used as a post-treatment of soil treated by other methods and has the great advantage that the treatment cost is the lowest. However, there is a disadvantage that the processing time is long and the decomposition rate is slow.

In order for these bioremediation technologies to succeed, that is, for microorganisms to effectively decompose contaminants in soil, the presence of nutrients necessary for the growth of microorganisms, the presence of electron acceptors such as oxygen, the delivery of pollutants as carbon and energy sources, Several conditions must be met, such as the activation of enzymes capable of breaking down contaminants. In order to solve this problem, fertilizers containing nitrogen and phosphorus, which may be insufficient in the soil, may be introduced, and oxygen may be introduced such as physical oxygen supply such as soil inversion or hydrogen peroxide such as hydrogen peroxide. The active agent may also be added. Biochemical degradation of contaminants takes several steps, eventually transforming them into carbon dioxide, water, and microbial organisms. Each step requires the proper activation of enzymes. In particular, the initial reaction that can break down the stabilized chemical structure of the pollutant is known to determine the overall decomposition rate, the activation of the enzyme involved in this is an important factor.

However, the existing biological restoration technology uses a method of adding basic nutrients in consideration of the primary metabolism of microorganisms, or decomposing microorganisms themselves, so that the degradation speed is very slow and the entire processing speed takes months to years. There was this. As a result, the introduced foreign microorganisms often disappear due to inadequate adaptation to the site soil environment, and even if the microorganism grows smoothly, the decomposition of the contaminated material is often very slow, thus preventing the rapid soil pollution. There was this.

The present invention has been made to solve the above problems, an object of the present invention is to provide a method for producing a liquid microbial preparation that can rapidly culture microorganisms having the ability to decompose pollutants present in contaminated soil.

It is another object of the present invention to provide a method for preparing an accelerated nutrient which promotes the activity of microorganisms inherent in soil to rapidly decompose and remove soil contaminants.

Another object of the present invention is to provide a biological purification method of maximizing decomposition by appropriately adding a combination of foreign microorganisms, which are powerful degradation strains, as a means for accelerating the decomposition of contaminants in the soil.

1 is a graph showing a change in phenanthrene decomposition rate according to the addition of the accelerated nutrient AN1 of the present invention in a liquid sample,

Figure 2 is a graph showing an increase in the number of microorganisms according to the addition of the accelerated nutrient AN1 of the present invention in a liquid sample,

Figure 3 is a graph showing the change of phenanthrene decomposition rate according to the addition of the accelerated nutrient AN2 of the present invention in a liquid sample,

Figure 4 is a graph showing the increase in the number of microorganisms according to the addition of the accelerated nutrient AN2 of the present invention in a liquid sample,

Figure 5 is a graph showing the change of decomposition rate according to the accelerated nutrient AN2 of the present invention in a high concentration soil sample.

Method for producing a liquid microbial preparation of the present invention for achieving the above object, the first step of collecting 100 ~ 500g of soil below 0 ~ 30cm from the ground surface of contaminated soil and surrounding soil; A composition comprising 2-7 g of ammonium chloride, 1-3 g of sodium phosphate, 0.2-0.6 g of IDT, 0.3-0.5 g of potassium chloride, 0.2-0.4 g of sodium sulfate, 0.2-0.4 g of magnesium sulfate, and 5-10 ml of mineral solution Adding a distilled water to 1 L to generate a general microbial culture medium; 5 to 50 g of the soil collected in the first step was added to 100 mL of the microorganism culture medium produced in the second step, and the mixture was shaken for 10 to 14 hours, preferably 12 hours, and then settled for about 1 hour to give a supernatant 50 to The third step taking 100 mL; The supernatant taken in the third step is administered to a concentration of 100 ~ 10000ppm of the pollutant as a carbon source and incubated for 10 days at 100-200rpm, preferably 150rpm at 25 ~ 35 ℃, preferably about 30 ℃ at 10mL Taking a fourth step of incubating one more time in the same manner in a total of 100mL medium; Taking a whole or part of the culture medium cultured in the fourth step, diluting 100 to 10,000 times and smearing on the nutritious agar medium in a sterile state; After culturing the culture broth in step 5 for 7 days, the colonies shown in the agar medium were separated and purely cultured, and then centrifuged and lyophilized to be stored at -60 to -80 ° C, preferably about -70 ° C. A sixth step; And a seventh step in which the microbial strain cryopreserved in the sixth step is added to the medium in which 5 to 10 g / L of glucose is added to the general microbial culture medium prepared in the second step, and shaken for two days under sterilization. It includes.

In addition, the method for producing a concentrate of the accelerated nutrient 1 (AN1) for maximizing cell growth and in situ adaptation of microorganisms or indigenous microorganisms or foreign microorganisms of the liquid microbial agent, glucose 3.0 to 5.0g, acetate 1.0 to 3.0g, nutritive 1.0 A first step of preparing a dissolved solution by adding a composition of ˜5.0 g, ethanol 1 g / L, tween 80 1 to 1.5 g / L, and 50 ml of root soil extract to 100 ml of distilled water; 30 g of soil 10 to 30 cm below the root of the wild acid is added to 1 to 3 g / L of ethanol, preferably 2 g / L, and Tween 80 to 1 to 10 g / L, preferably 3 g / L to 100 mL of distilled water. A second step of preparing a supernatant by extracting the near acid soil at 200 to 400 rpm, preferably 300 rpm, and centrifuging at 2000 to 4000 rpm, preferably about 3000 rpm for about 10 minutes; And a third step of mixing the solution prepared in the first step and the supernatant prepared in the second step and then passing the 0.2 um filter to form a solution.

In addition, the method for preparing a concentrate of the accelerated nutrient 2 (AN2) for maximizing the expression of the dehydrogenase of the aromatic hydrocarbon of the present invention includes 0.2 to 1.0 g of catechol, 0.025 to 0.5 g of mucoic acid, and 0.1 to 0.5 hydroxynaphthoic acid. g, salicylic acid 0.02 to 1 g, polylic acid 0.1 to 0.3 g, and a first step of preparing a 1.0 ml composition of vitamin B concentrate; And a second step of adding the composition prepared in the first step to 100 ml of 0.1% distilled water of ethanol and passing the dissolved solution through a 0.2um filter to form a solution.

Hereinafter, the present invention will be described in detail with reference to the accompanying drawings.

The present invention provides a method for preparing a liquid microorganism for purifying soil contaminated with oil, and also promotes the decomposition ability of liquid microorganisms, and promotes the decomposition ability of indigenous microorganisms or foreign microorganisms inherent in conventional soils even when used alone. The present invention relates to a method for preparing an accelerated nutrient concentrate, and a biological purification method using the prepared liquid microorganism and accelerated nutrients. In essence, it is an environmentally-friendly purification method that can induce microorganisms capable of degrading specific contaminants from natural or indigenous microorganisms present in nature at high speed, and promote the degradability to remove contaminants without any environmental pollution. .

The liquid microorganism preparation according to the present invention is achieved by separating microorganisms having the ability to remove contaminants from indigenous microorganisms inhabiting contaminated soil from the soil, and preparing liquid microorganisms using the same.

The method for preparing a liquid microorganism as described above, first, as a first step, 100 ~ 500g of soil below 0 ~ 30cm from the ground surface of soil and surrounding soil contaminated by oil or pollutants. The soil is agitated to mix evenly. Soil collection is particularly desirable for areas with high levels of contamination by contaminants.

After collecting the soil as described above, as a second step, to prepare a composition comprising the components and contents as shown in Table 1 below, and added to 1L of distilled water as an aqueous solution to form a general microbial culture medium.

division ingredient content One Ammonium Chloride (NH4Cl) 2.0-7.0 g 2 Sodium phosphate (NaH2PO4) 1.0-3.0 g 3 EDTA 0.2-0.6 g 4 Potassium Chloride (KCl) 0.3-0.5 g 5 Sodium sulfate (Na2SO4) 0.2-0.4 g 6 Magnesium Sulfate (MgSO47H2O) 0.2-0.4 g 7 Mineral solution 5-10ml

As a third step, 10 g of the soil collected in 100 mL of the general microbial culture medium cultured in the second step was added and shaken for 10 to 14 hours, preferably 12 hours, and then settled for about 1 hour to take the supernatant 75 mL. do.

Thereafter, the supernatant solution is administered with a contaminant as a carbon source at a concentration of 100 to 10000 ppm and incubated twice at a rate of about 25 to 35, preferably at 30 ° C. at 150 rpm per minute.

Take all or a part of the cultures incubated as described above, dilute 100 to 10,000 times, and smear on the nutritious agar medium under sterile conditions.

After culturing the culture solution for 7 days, the colonies appearing on the nutritious agar medium were separated and purely cultured, followed by centrifugation, lyophilization and storage at -60 to -80 ° C, preferably -70 ° C. The microbial strains stored as described above were added to a medium in which 1% by weight (10 g / L) of glucose was additionally added to the general microbial culture medium prepared based on Table 1, and cultured in a sterilized state for 2 days to form a liquid microorganism. Complete the manufacture of Liquid microorganisms prepared as described above are used to remove contaminants by applying directly to the contaminated soil or applied to the lower surface of the surface of a certain depth. The contaminant degrading ability of the liquid microbial agent prepared as described above will be described later with reference to the drawings.

In addition, the method for preparing a concentrate of the accelerated nutrient 1 (AN1) for maximizing cell growth and in situ adaptability of the liquid microorganism or indigenous microorganisms or foreign microorganisms, first, glucose 3.0 to 5.0 g, acetate 1.0 to 3.0 g, A composition of 1.0-5.0 g of nutrients, 0.1% by weight (1 g / L) of ethanol, 0.1-0.15% by weight (1-1.5 g / L) of tween 80, and 50 ml of root soil extract were added to 100 ml of distilled water and dissolved. Prepare the solution. The components of the composition used in the aforementioned accelerated nutrient 1 (AN1) are shown in Table 2 below.

division ingredient content One Glucose 3.0 to 5.0 g 2 Acetate 1.0-3.0 g 3 Nutrient broth 1.0-5.0 g 4 Ethanol 0.1 wt% 5 Tween 80 0.1-1.0 wt% 6 Soil extract 50 ml

After the solution is prepared as described above, 30 g of wild acid soil soil is 0.1 to 0.3% by weight of ethanol (1 to 3 g / L), preferably 0.2 to 2% of 2 g / L of ethanol and 0.1 to 1% by weight of tween 80 (as a second step). 1 to 10 g / L), preferably 0.3% by weight (3 g / L), is added to 100 mL of distilled water, extracted at about 300 rpm for about 2 hours, and centrifuged at 3000 rpm for 10 minutes to prepare a supernatant. The wild root soil specifically refers to the soil of about 10 ~ 30cm under the tree roots. Even if the order of the first and second steps is reversed, there is no problem in the preparation of the accelerated nutrient.

As a third step, after mixing the solution prepared in the first step and the supernatant prepared in the second step through a 0.2um filter to form a solution to prepare an accelerated nutrient (AN1). Accelerated nutrients prepared as described above may be used alone as an adjuvant for promoting the growth of indigenous microorganisms or foreign microorganisms or in the liquid microbial preparations.

In addition, the method for preparing a concentrate of the accelerated nutrient agent 2 (AN2) of the present invention for maximizing the expression of the decomposing enzyme of aromatic hydrocarbons includes 0.2 to 1.0 g of catechol, 0.025 to 0.5 g of mucoic acid, and hydroxynaph as a first step. 0.1 to 0.5 g of toic acid, 0.02 to 1.0 g of salicylic acid, 0.1 to 0.3 g of polylic acid and 1.0 ml of a vitamin B concentrate were prepared, and the prepared composition was added to 100 ml of distilled water of 0.1% ethanol as a second step. The dissolved solution is passed through a 0.2um filter to complete the preparation. The components of the composition are shown in Table 3 below.

division ingredient content One Catechol 0.2-1.0 g 2 Mucoic acid 0.025-0.5 g 3 1-hydroxy-2-naphtoic acid 0.1-0.5 g 4 Salicylic acid 0.02 ~ 1.0g 5 Folic acid 0.1-0.3 g 6 Vitamin B solution 1.0ml

In order to investigate the biodegradation of the liquid microbial agent of the present invention prepared as described above was prepared liquid samples and soil samples as follows.

For liquid samples, add 0.3% of Triton X-100 to the microbial medium from which the carbon source was removed, add powder phenanthrene at a concentration of 10-100 mg / L, and completely dissolve 50-100 mL of the sterilized medium in a 125-250 mL Erlenmeyer flask. It was. Soil samples were made by sprinkling 1-10 ml of acetone in which 0.03mg ~ 1mg of phenanthrene was dissolved in 1 ~ 10g of uniform silt soil in the form of fine powder and drying at room temperature.

To the contaminated liquid sample and / or contaminated soil sample was added 0.1 ~ 1% of the mixed liquid microbial agent prepared by the production method of the present invention and was treated for 7 to 21 days at 150rpm at room temperature. In order to measure the degradation efficiency of the microorganism was carried out under the following conditions.

During the treatment experiment, 1 ml of sample was collected and used for phenanthrene analysis, and 0.1 ml was used for measuring the number of microorganisms. In phenanthrene analysis, 1 ml of soil and liquid samples are placed in a stoppered 15 ml glass test tube, 10 ml of methylene chloride is added, extracted at 500 to 1000 rpm for 5 minutes, and repeated twice. 20 ml of the extract methylene chloride was volatilized at 40 ° C., and the residue was dissolved in 1-10 ml of acetonitrile and analyzed by liquid chromatography. The microorganisms in the samples were diluted with 100-10000 times distilled water and plated on nutritious agar medium, and the number of colonies that appeared after 3 days and 7 days was measured.

Table 4 shows the results of the respective tests in the liquid and soil samples by the tests performed as above. In this test, accelerated nutrients 1 and 2 were added as well as liquid microbial agents and the results were measured respectively.

division Sample state Microbial input Whether accelerated nutrient AN1 is added Accelerated nutrition AN2 injection Decomposition rate (%) 2 days later 7 days later 14 days later A Liquid X X X 2.7 2.9 3.4 B Liquid O X X 2.3 4.5 7.2 C Liquid O O X 11.4 16.7 24.3 D Liquid O O O 47.2 65.8 84.3

The liquid sample state is classified into A, B, C, and D according to the microbial input, the accelerated nutrient 1, and the accelerated nutrient 2, respectively, and the microbial input is indicated by X (not input) and O (insert). have.

As shown in the results shown in Table 4, when the microbial agent was added as compared to the sample (A) without any treatment in the liquid sample, the decomposition rate increased over time and showed about twice the decomposition efficiency. . When the accelerated nutrient AN1 was additionally added to the microbial preparation as in Sample C, the degradation efficiency increased by 7 times, and when AN2 was added, it increased by 25 times.

Referring to the state of the change in the decomposition rate, as shown in Figure 1, it was confirmed that the decomposition degree increases as the amount of the accelerated nutrient AN1 is increased. In addition, as shown in FIG. 2, the number of microbial viable cells was found to increase significantly as the amount of the accelerated nutrient AN1 was increased. In addition, in Figure 3 it can be seen that the decomposition degree is significantly increased as the amount of the accelerated nutrient AN2 is increased.

Comparing FIG. 4 with FIG. 2, the decomposition efficiency was higher in the case of AN2 treatment even though the number of microorganisms in FIG. 2 was much higher. An increase in the degradation rate was much more effective than the accelerated nutrient AN1, indicating that activation of enzymes that degrade contaminants has a greater effect on the degradation of contaminants than increases in the number of microorganisms. In addition, the decomposition rate according to the preparation of the microbial agent, accelerated nutrient 1 (AN1), accelerated nutrient 2 (AN2) to the prepared soil is shown in Table 5 below. According to this, it can be seen that the decomposition efficiency increases in the soil sample as compared with the liquid sample.

division Sample state Microbial input Whether accelerated nutrient AN1 is added Accelerated nutrition AN2 injection Decomposition rate (%) 2 days later 7 days later 14 days later E soil X X X 2.3 4.2 8.5 F soil O X X 11.3 100 - G soil O O X 24.4 100 - H soil O O O 94.5 100 -

In other words, even when only microorganisms were added, the decomposition efficiency increased drastically compared to the liquid samples because the stable microbial film formation and substrate accessibility of the soil samples were improved compared to the pure solution samples. Similarly for soil samples, the degradation efficiency was significantly increased with the addition of accelerated nutrients, and only two days were required for 95% degradation, especially with the addition of AN2. As shown in FIG. 5, even in the case of 10 times higher concentration of contaminated soil, it can be seen that the decomposition time did not increase significantly.

In addition, the indigenous microorganism utilization test was performed as follows. That is, 10% of general soil extracts considered to contain indigenous microorganisms in contaminated soil samples and liquid samples under the above conditions were added and their degree of decomposition was examined.

As shown in Table 6, indigenous microorganisms that are not adaptable to contaminants also showed a significantly faster rate of degradation by the addition of accelerated nutrients. This shows that even if a special microorganism is weakened in the competition with indigenous microorganisms, it is possible to activate the degrading enzyme at a high speed by adding an accelerating nutrient.

division Sample state Special Microorganisms Whether accelerated nutrient AN1 is added Accelerated nutrition AN2 injection Decomposition rate (%) 2 days later 7 days later 14 days later D Liquid O O O 47.2 65.8 84.3 I Liquid X O O 5.7 46.4 64.5 H soil O O O 94.5 100 - J soil X O O 27.8 77.0 85.7

In addition, by changing the way of accelerating nutrients was able to induce more efficient decomposition capacity. That is, accelerated nutrient 2 AN2 is rapidly used in the liquid sample as shown in FIG. 3, and the decomposition phenomenon becomes very slow after a certain time, as shown in Table 7 below. This continued maintenance was able to efficiently reduce the decomposition time as a whole.

Therefore, in the present invention, by using the liquid microbial agent, the accelerated nutrients 1, and the accelerated nutrients 2 are mixed, there is an advantage that the decomposition rate is significantly improved than the conventional decomposition performance.

Table 7 below shows the measurement results after 1 day, 2 days, 3 days, and 7 days after the decomposition rate according to the change of the dosing cycle of the accelerated nutrient AN2.

division Accelerated nutrient AN2 dosing cycle Decomposition rate (%) 1 day later 2 days later 3 days later 7 days later D Initial one time 37.4 47.2 53.1 65.8 K Once every 3 days - - 54.0 81.4 L Once daily 35.2 57.9 75.4 100

In particular, the accelerated nutrient for degrading enzyme expression was administered to 100 ~ 500mL per 1Kg of contaminated soil, showing the optimum degradation rate. Experimental results show that this applies either alone or in combination with other accelerated nutrients and liquid microbial agents. In addition, the accelerated nutrient for growth (AN1) also showed the optimum degradation rate when administered 100 ~ 500mL per Kg of contaminated soil.

Thus, according to the present invention, in the biological purification of oil contaminated soils, specific degradation strains are cultured and applied at high speed to formulate and express the expression of enzymes directly involved in the degradation of accelerating nutrients and contaminants that promote the growth of foreign microorganisms or indigenous microorganisms. The use of accelerating accelerated nutrients can significantly reduce the purification time and, consequently, significantly reduce the purification costs.

Claims (10)

A first step of collecting 100 to 500 g of soil below 0 to 30 cm from the soil surface of the contaminated soil and surrounding soil; A composition comprising 2-7 g of ammonium chloride, 1-3 g of sodium phosphate, 0.2-0.6 g of IDT, 0.3-0.5 g of potassium chloride, 0.2-0.4 g of sodium sulfate, 0.2-0.4 g of magnesium sulfate, and 5-10 ml of mineral solution Adding a distilled water to 1 L to generate a general microbial culture medium; 5 to 50 g of the soil collected in the first step was added to 100 mL of the microorganism culture medium produced in the second step, and the mixture was shaken for 10 to 14 hours, preferably 12 hours, and then settled for about 1 hour to give a supernatant 50 to The third step taking 100 mL; The supernatant taken in the third step is administered to a concentration of 100 ~ 10000ppm of the pollutant as a carbon source and incubated for 10 days at 100-200rpm, preferably 150rpm at 25 ~ 35 ℃, preferably about 30 ℃ at 10mL Taking a fourth step of incubating one more time in the same manner in a total of 100mL medium; Taking a whole or part of the culture medium cultured in the fourth step, diluting 100 to 10,000 times and smearing on the nutritious agar medium in a sterile state; After culturing the culture broth in step 5 for 7 days, the colonies shown in the agar medium were separated and purely cultured, and then centrifuged and lyophilized to be stored at -60 to -80 ° C, preferably about -70 ° C. A sixth step; And a seventh step in which the microbial strain cryopreserved in the sixth step is added to the medium in which 5 to 10 g / L of glucose is added to the general microbial culture medium prepared in the second step, and shaken for two days under sterilization. Method for producing a liquid microbial agent comprising a. A composition of glucose 3.0-5.0 g, acetate 1.0-3.0 g, nutrition 1.0-5.0 g, ethanol 1 g / L, tween 80 1-1.5 g / L, and 50 ml of root soil extract were added to 100 ml of distilled water and dissolved. A first step of preparing a solution; 30 g of soil 10 to 30 cm below the root of the wild acid is added to 1 to 3 g / L of ethanol, preferably 2 g / L, and Tween 80 to 1 to 10 g / L, preferably 3 g / L to 100 mL of distilled water. A second step of preparing a supernatant by extracting the near acid soil at 200 to 400 rpm, preferably 300 rpm, and centrifuging at 2000 to 4000 rpm, preferably about 3000 rpm for about 10 minutes; And a third step of mixing the solution prepared in the first step and the supernatant prepared in the second step and then passing the 0.2 um filter to form a solution, thereby accelerating the growth of microorganisms. Way. A composition of 0.2-1.0 g of catechol, 0.025-0.5 g of mucoic acid, 0.1-0.5 g of hydroxynaphthoic acid, 0.02--1 g of salicylic acid, 0.1-0.3 g of polylic acid, and 1.0 ml of vitamin B concentrate were prepared. The first step to do; And a second step of forming the solution by adding the composition prepared in the first step to 100 ml of 0.1% by weight of ethanol and distilled water through a 0.2um filter to dissolve the solution. Manufacturing method. Separation of microorganism strains that decompose contaminants on-site for high-speed culture to form a liquid microorganism, and treatment of contaminated soil by applying an accelerating nutrient for growth and an accelerating nutrient for accelerating enzyme expression to a predetermined depth from the surface or surface of contaminated soil. Biological purification method. The method of claim 4, wherein Biological purification method characterized in that the liquid microbial agent, the growth promoting accelerated nutrient, and the degradation enzyme expression promoting accelerated nutrients are selectively added to the ground surface or the bottom of the ground surface by a combination of two or more. The method according to claim 4 or 5, Biological purification method characterized in that the liquid microbial agent is prepared by the manufacturing method of claim 1. The method according to claim 4 or 5, Biological purification method characterized in that the growth promoting accelerated nutrient is prepared by the method of claim 2. The method according to claim 4 or 5, Biological purification method characterized in that the accelerated nutrient for degradation enzyme expression is prepared by the method of claim 3. The method according to claim 4 or 5, The growth promoting accelerated nutrient is a biological purification method characterized in that for administering 100 to 500mL per 1Kg of contaminated soil. The method according to claim 4 or 5, Biological purification method characterized in that the accelerated nutrient for degradation enzyme expression is administered 100 ~ 500mL per 1Kg of contaminated soil.