BACTERIAL CONSORTIUM EBC1000 AND A METHOD USING THE BACTERIAL CONSORTIUM EBC1000 FOR REMEDYING BIOLOGICALLY RECALCITRANT TOXIC CHEMICALS CONTAINED IN INDUSTRIAL WASTEWATER, WASTE MATERIALS AND SOILS

Abstract: The present invention relates to a novel bacterial consortium EBC1000 (KCTC 0652 BP) and a method for remedying biologically a chlorine compound and recalcitrant toxic chemicals contained in industrial wastewater, waste materials and soils using the bacterial consortium EBC1000. The novel bacterial consortium EBC1000(KCTC 0652 BP) is composed of aerobic bacterium easy to culture and useful for decomposing a chlorine compound and waste acidic or alkaline recalcitrant toxic chemicals of high concentration contained in the industrial waste materials, such as IPA, MC, DMA, AN, SHS, BD, Tamol-SN, EDTA, FES, TDDM, PMH, DEHA, MeOH, NaOH and CH3CN, thus preventing and recovering environmental pollutions.

Description: BACTERIAL CONSORTIUM EBCIOOO AND A METHOD USING THE BACTERIAL CONSORTIUM EBCIOOO FOR REMEDYING BIOLOGICALLY RECALCITRANT TOXIC CHEMICALS CONTAINED IN INDUSTRIAL WASTEWATER, WASTE MATERIALS AND SOILS TECHNICAL FIELD The present invention relates to a novel bacterial consortium EBCIOOO and a method for remedying biologically recalcitrant toxic chemicals contained in industrial wastewater, waste materials and soils using the bacterial consortium EBCIOOO. More particularly, the invention relates to a novel bacterial consortium EBCIOOO capable of remarkably decomposing a chlorine compound of high concentration and waste acidic or alkaline recalcitrant toxic chemicals difficult to be degraded that are isolated from waste soil and water, the recalcitrant toxic chemicals having a chemical oxygen demand (COD MΠ ) of 20,000 to 100,000 ppm and comprising chemicals, such as isopropyl alcohol(IPA), methylene chloride(MC), dimethylamine(DMA), acrylonitrile(AN), hydrosulfιte(SHS), butadiene(BD), sodium alkylaryl naphthalene sulfonate(Tamol-SN), tetra sodium ethylene diamine tetra acetate dihydrate(EDTA), ferrous sulfate heptahydrate(FES), tert-dodecyl mercaptan(TDDM), paramethane hydroperoxide(PMH), N-diethyl hydroxyl amine(DEHA), methanol(MeOH), NaOH and CH 3 CN. BACKGROUND ART Environmental contaminations caused by recalcitrant toxic substances causes degradation of food stuffs for human related to the food chain in the biosphere, prevalence of infectious diseases due to deteriorated immunity, spread of chronic diseases and energy exhaustion. Once the ecosphere is radically destroyed, it may take several hundred millions of years for recovery ofthe environment of ecosphere. There has been an attempt to remedy recalcitrant toxic substances contained in the industrial wastewater or noxious waste materials dumped into the sea normally, using physical and chemical methods such as incineration, landfill, chemicals, electrolysis, membrane separation or the like. However, these conventional methods also involve economical and environmental problems. The most efficient and safe method that meets requirements in every aspect of environmentology, sanitation, ecology and economy is the biological treatment method. Many studies have been made on the biological methods, for example, using the natural ecosystem such as silt at an estuary. However, these methods could not be a solution of treating a great mass of industrial waste materials. DISCLOSURE OF THE INVENTION It is, therefore, an object of the present invention to provide bioremediation to remedy biologically recalcitrant toxic chemicals contaminating industrial wastewater, waste materials and soils, etc., using a trace of useful specific bacterial consortium that exists in the ecological system. The present invention is directed to a novel bacterial consortium EBC 1000 and a method for remedying biologically recalcitrant toxic chemicals and chlorine compounds contained in industrial wastewater, waste materials, soils, or the like using the bacterial consortium EBCIOOO. More particularly, the invention is directed to a novel bacterial consortium EBCIOOO capable of remarkably degrading chlorine compounds of high concentration and waste acidic or waste alkaline recalcitrant toxic chemicals that are isolated from soil and wastewater having COD Π of 20,000 to 100,000 ppm, such as contained in the medical industrial wastewater to be dumped into the sea, e.g., isopropyl alcohol, methylene chloride, NaOH, Na 2 SO 4 , dimethylamine or methanol, or as contained in the petroleum industrial wastewater to be dumped into the sea, e.g., sodium hydrosulfite, butadiene, sodium alkylaryl naphthalene sulfonate, acrylonitrile, tetra sodium ethylene diamine tetra acetate dihydrate, ferrous sulfate heptahydrate, tert-dodecyl mercaptan, paramethane hydroperoxide, N-diethyl hydroxy amine, and CH 3 CN. The inventor isolated a novel bacterial consortium EBCIOOO (KCTC 0652 BP) having a characteristic of rapidly degrading recalcitrant waste materials of high concentration dumped into the sea as well as chlorine compounds, from the soils and wastewater collected from the Ulsan industrial complex and the petroleum chemical industrial complex in Korea. The bacterial consortium EBCIOOO consists of nine strains, each having the ability of degrading recalcitrant waste materials. It was found that the bacterial consortium EBCIOOO degrades waste acidic or waste alkaline recalcitrant waste materials having the COD MΠ of 20,000 to 100,000 ppm contained in the medical and petroleum industrial waste waters to be dumped into the sea by 80% within 7 days, 90% within 10 days and at least 80 to 90% within 240 hours in an aerobic manner. Examples of the waste acidic or alkaline recalcitrant waste materials contained in the medical industrial wastewater of e.g., pH 3 or 14 include isopropyl alcohol (IPA, 10,000 to 20,000 ppm), methylene chloride (MC, 100 to 7,000 ppm), NaOH (changeable), Na 2 SO 4 (changeable), dimethylamine (DMA, 70 to 2,500 ppm), methanol (MeOH, 27,000 to 54,000 ppm), organic matters and antibiotic residues(40,000 to 100,000ppm) and Cl " (4,000 to 33,000ppm). Examples of the waste acidic or alkaline recalcitrant waste materials contained in the petroleum industrial wastewater of e.g., pH 1.2, 3.0 or 5.0 include sodium hydrosulfite (SHS, (NaSO 2 ) , 30 ppm), butadiene (BD,changeable), sodium alkylaryl naphthalene sulfonate (Tamol-SN, 4,000 to 20,000 ppm), acrylonitrile (AN,changeable), tetra sodium ethylene diamine tetra acetate dihydrate (EDTA, 20 to 200 ppm), ferrous sulfate heptahydrate (FES, 60 ppm), tert-dodecyl mercaptan (TDDM, 4,000 ppm), paramethane hydroperoxide (PMH, 400 ppm), N-diethyl hydroxyl amine (DEHA, 200 ppm), and CH 3 CN (changeable). Accordingly, the present invention is to provide such a novel bacterial consortium EBCIOOO capable of degrading recalcitrant toxic chemicals and chlorine compounds, and a method using the bacterial consortium EBCIOOO in remedying biologically recalcitrant toxic chemicals and chlorine compounds contaminating industrial wastewater, waste materials and soils. BEST MODE FOR CARRYING OUT THE INVENTION Now, a description will be made to isolation, identification and activity of the novel bacterial consortium EBCIOOO. 1. Isolation of Novel Bacterial Consortium EBCIOOO (1) Isolation of 40 strains from shaking culture ofthe samples. The soil (1 g) and wastewater (10 ml) from the Ulsan industrial complex were inoculated in a waste acidic and alkaline waste liquid medium(prepared by dilution of K 2 HPO 4 (0.65 g), KH 2 PO 4 (0.17 g), MgSO 4 (0.1 g), NaNO 3 (0.5 g) and 10% waste acidic and alkaline wastewater containing recalcitrant chemicals in medical and petroleum industrial waste liquid, in 1 liter of deionized water, pH 0 to 14) and then in a chlorine compound liquid medium(prepared by dissolving of K 2 HPO 4 (0.65 g), KH 2 PO 4 (0.17 g), MgSO 4 (0.1 g), NaNO 3 (0.5 g) and pentachlorophenol (PCP, 50 ppm) in 1 liter of deionized water, pH 7.2), followed by shaking culture at 20 to 30 °C for more than 5 days. 1 ml of the shaken culture was collected and inoculated in a waste acidic or waste alkaline solid medium (prepared by adding only 1.5% of agar to the waste acidic or alkaline liquid culture, pH 7.0) and then a chlorine compound solid medium(prepared by adding 20 mg of BTB and 1.5% of agar to the chlorine compound liquid medium), followed by incubation at 20 to 30 °C for 3 to 10 days. The individual pure colonies isolated were further inoculated in the above- mentioned cultures and then shaking cultured, thus isolating 40 useful bacterial strains which have a different colony form formed respectively and the same colony after successive transfer culture. (2) Isolation of 9 competent strains after the bacterium isolated in step (1) are cultured in the medium of an increased concentration ofthe recalcitrant wastewater. The bacterium isolated in step (1) were in order and individually inoculated in a minimal medium containing 50% of the crude wastewater and 80% of wastewater containing the recalcitrant chemicals of the medical and petroleum wastewater and then a minimal medium containing 500 ppm of the pentachlorophenol compound and repeted to the same procedures of step (1), thus isolating nine competent strains viable in the wastewater of higher concentration ofthe recalcitrant chemicals. The nine bacterial strains, which constitute a single bacterial consortium, named "EBCIOOO", are designated as EBC 100, EBC 101, EBC 103, EBC 104, EBC 105, EBC 106, EBC 107, EBC 108 and EBC 109. The novel bacterial consortium EBCIOOO was deposited in the Korean Collection for Type Cultures in the Korea Research Institute of Bioscience and Biotechnology as the deposition No. KCTC 0652 BP on August 12, 1999. 2. Optimum Conditions for Growth of Bacterial Consortium EBCIOOO The bacterial consortium EBCIOOO had the best growth in the Luria-Bertani nutrient medium (containing 10 g of bacto-tryptone, 5 g of bacto-yeast extract and 10 g of NaCl in 1 liter of deionized water) at pH 5 to 8 and 25 to 35 °C with shaking at 50 to 100 rpm/min for 24 to 48 hours. The bacterial consortium EBCIOOO was also well grown in the successive transfer culture under the same conditions. 3. Identification of Bacterial Consortium EBCIOOO The individual strains constituting the bacterial consortium EBCIOOO, designated as EBC100, EBC101, EBC103, EBC104, EBC105, EBC106, EBC107, EBC 108 and EBC 109 are a mixture of Gram negative and positive bacterium and have unique shape and size. After culture for 24 hours in the Luria-Bertani medium, EBC 100 forms a lmm-diameter circular colony, EBC 101 a large about 2mm-diameter circular colony, EBC 103 a thick about 2mm-diameter circular colony, EBC 104 and EBC 105 a small about 0.5mm-diameter circular colony, EBC 106 a thick about 3mm- diameter colony, EBC 107 a about 1.2mm-diameter brownish colony, EBC 108 a about lmm-diameter yellowish colony, and EBC 109 a about 2-diameter double circle. These nine strains are aerobic and air permeable bacterium. EBC 100, EBC 101, EBC 103, EBC 106, EBC 107 and EBC 108 have high viability in the strong acidic condition of pH 3 to 4 and in the strong alkaline condition of pH 9 to 11. EBC 104, EBC 105 and EBC 109 are slow in growth and EBC 100, EBC 104, EBC 105 and EBC 109 show mobility. For the genera of the individual constituent strains of the bacterial consortium EBCIOOO included EBC 100, EBCIOI and EBC 103 are the strains of the genus Klebsiella, EBC 105 Providencia, EBC 104 and EBC 109 Escherichia, EBC 106 Bacillus, EBC 107 Gram-negative bacteria and EBC 108 Gram-positive Bacteria. The characteristics ofthe individual strains are presented in Tables 1 and 2. [Table la] [Table lb] [Table 2] On the other hand, the individual bacterial strains were analyzed for fatty acid Methyl Esters (FAMEs) by gas chromatography. For the FAMEs assay, there was used the Hewlett Packard series II Gas Chromatograph model 5890A (Microbial ID. Inc., Delaware, USA) with a 25cmχ0.22mmx0.33μm separation column, e.g., a capillary column (HP 19091B-102) fused with methylphenyl silicon. The gas chromatography was performed under the conditions that the carrier gas is hydrogen, the column head pressure 10 psi, the split ratio 100: 1, the split vent 50 ml/min, the septum purge 5 ml/min, the FID hydrogen flux 30 ml/min, the FID nitrogen flux 30 ml/min, the FID air 400 ml/min, the initial temperature 170 °C, the program rate 5 °C/min, the final temperature 270 °C, the FID temperature 300 °C, the temperature ofthe inlet port 250 °C, and the injection volume 2 μl. The FAME graphs were obtained using a microbial identification system software (Microbial ID, Inc., Delaware, USA). A comparison with a standard calibration mixture (Microbial ID. Inc., Delaware, USA) enabled peak identification, and determination of retention time, peak region and peak percentage. The assay of the FAMEs for the respective strains of EBC 100, 101 and 103 revealed that the intracellular fatty acids composition is C12:0, C14:0, C16:0, C16:l, C17:0 cyclo and C14:0 3OH for EBC100; C12:0, C14:0, C15:0, C16:0, C17:0 cyclo and C14:0 3OH for EBCIOI; and C14:0, C15:0, C16:0, C17:0 cyclo, and C14:0 3OH for EBC 103. 4. Isolation of Constituent Strains of Bacterial Consortium EBC 1000 The following procedures are performed for isolating the individual strains from the bacterial consortium EBCIOOO. When cultured in the Luria-Bertani agar solid nutrient medium (containing 10 g of bacto-tryptone, 5 g of bacto-yeast extract, 10 g of NaCl and 1.5% agar in 950 ml of deionized water), EBC 106 (Bacillus) is characterized by a thick wrinkle peculiar to the Bacillus, EBC 107 (Gram negative bacteria) a brownish colony, and EBC 108 (Gram positive bacteria) a yellowish colony. For the other strains the respective colonies can be identified by dilution- smearing the bacterial consortium EBCIOOO in desoxycholate agar containing 10 g of bacto-peptone, 10 g of bacto-lactose, 1 g of sodium desoxycholate, 5 g of sodium chloride, 2 g of dipotassium, 1 g of ferrous citrate, 1 g of sodium citrate, 15 g of bacto agar and 0.03 g of neutral red in 1 liter of deionized water (Difco manual, 1984). After cultured for 24 hours in the desoxycholate agar, EBC 100, EBCIOI and EBC 103 have white-in-red spots with viscosity and are slightly different in size, EBC 104 white-in- red spots without viscosity, EBC 105 brownish spots with viscosity, EBC 106 and EBC 107 light brownish spots with viscosity, EBC 108 colorless spots with viscosity, and EBC 109 red spots with viscosity (See. Dictionary of Microbiology and Molecular Biology, 2 nd , Paul Singleton Diana Sainsbury, 1987). 5. Characteristics of Bacterial Consortium EBCIOOO (1) Decomposition velocity of sodium alkylaryl naphthalene sulfonate (Tamol- SN) by bacterial Consortium EBCIOOO Batches of Tamol-SN with an increasing concentration of 500 ppm, 1000 ppm, 2000 ppm and 4000 ppm were added to the minimal medium (pH 7.2) prepared by dissolving 0.065 g of K 2 HPO 4 , 0.017 g of KH 2 PO 4 , 0.1 g of MgSO 4 and 0.5 g of NaNO 3 in 1 liter of deionized water. After inoculation of the bacterial consortium EBCIOOO, the absorbance and the Tamol-SN concentration were measured with an elapse of time. The results are presented in Table 3. [Table 3] As shown in Table 3, the decomposition velocity per hour of Tamol-SN was 1.3 mg/l/h at the Tamol-SN concentration of 500 ppm and 4.0 mg/l/h at the Tamol-SN concentration of 4000 ppm. (2) Decomposition velocity of pentachlorophenol compound by bacterial Consortium EBCIOOO Batches of pentachlorophenol compound with an increasing concentration of 200 ppm, 500 ppm, 1000 ppm and 2000 ppm were added to the medium prepared by dissolving 20 mg of BTB in 1 liter of deionized water under the same conditions of the minimal liquid medium as described in (1). After inoculation of the bacterial consortium EBCIOOO, the absorbance and the pentachlorophenol compound concentration per hour were measured. The results are presented in Table 4. [Table 4] 6. Treatment of Recalcitrant Industrial Wastewater with Bacterial Consortium EBCIOOO Experimental Example 1 : Use of Bacterial Consortium EBCIOOO in Treatment of a Recalcitrant Special Emulsifying agent Contained in Petroleum Industrial Wastewater. 1% of crude liquid of sodium alkylaryl naphthalene sulfonate(Tamol-SN), which is the typical recalcitrant chemical used in the petroleum plant, was added to 50 ml of a minimal medium (pH 7.2) prepared by dissolving 0.065 g of K HPO 4 , 0.017 g of KH 2 PO 4 , 0.1 g of MgSO 4 and 0.5 g of NaNO 3 in 1 liter of deionized water. After inoculating 2.0 x 10 4 /ml of the bacterial consortium EBCIOOO, shaking culture was performed at 100 rpm, at 25 to 30 °C for 10 days. The results are presented in Table 5. [Table 5] As shown in Table 5, the concentration of Tamol-SN was 850 ppm with the number of bacterium of 2.5 x 10 7 CFU/ml after four days of culture. Experimental Example 2: Use of Bacterial Consortium EBCIOOO in Treatment of recalcitrant crude wastewater from petroleum plants. Waste acidic and alkaline recalcitrant wastewater to be dumped into the sea was collected from the petroleum plants in the Ulsan industrial complex. The wastewater was crude wastewater contained 4000ppm of sodium alkylaryl naphthalene sulfonate (Tamol-SN), sodium hydrosulfιte[(NaSO 2 ) 2 ], butadiene (BD), acrylonitrile (AN), tetra sodium ethylene diamine tetra acetate dihydrate (EDTA), ferrous sulfate heptahydrate (FES), tert-dodecyl mercaptan (TDDM), paramethane hydroperoxide (PMH), N-diethyl hydroxy amine (DEHA) and CH 3 CN and so on. After inoculating 1.2 x 10 7 /ml of EBCIOOO in 200 ml of the crude wastewater, shaking culture was performed at 80 rpm, at 30 °C for 10 days. The results are presented in Table 6. [Table 6] As shown in Table 6, the COD value of the crude wastewater was reduced to 750 ppm with the decomposition efficiency of 80% after 10 days of culture. The TOC and BOD values had a downward tendency as the COD value and the number of bacterium was 5.1 x 10 CFU/ml with an at least hundred-fold increase. For a reference, the analytical methods used in the experimental examples of the present invention were as follows: 1) COD (Mn) Analysis The chemical oxygen demand (COD) was measured by the COD Mn method according to the official test method for water pollution and waste treatment (Official No. 1993-42, the Ministry of Environment) and Standard Methods (APHA, AWWA, WPCF, 18 th ed.). Each 10 ml of crude industrial wastewater or waste materials to be dumped into the sea and the wastewater after decomposition treatment of noxious substances with microorganisms were added to a water bath after addition of H SO 4 and 0.025N KMnO 4 , and then heated to 100 °C for 30 minutes. After adding 0.025N Na 2 C 2 O 4 , the mixture was titrated with KMnO 4 to measure the actual decrement of the COD. 2) BOD Analysis The biological oxygen demand (BOD) was measured as the amount of dissolved oxygen used for 5 days under the biological reaction at 20 °C according to the official test method for water pollution and waste treatment and Standard Methods. 3) TOC Analysis According to the standard method, the crude waste, wastewater and the time- based samples were centrifuged and the resulting supernatant liquids were analyzed for the total organic carbon (TOC) content with a TOC analyzer (TOC-5000 A, Shimadzu com.). 4) CFU Examination The consortiums of indigenous bacteria and inoculum of the individual treated samples were analyzed by the plate count method according to the standard method for bacteria examination, to measure the growth of the bacterium at the beginning of the test and with an elapse of time by a decrease in the noxious substances. 5) Extraction and Analysis of Chlorine Compound The chlorine compound was extracted and analyzed according to the contents of Korean Patent No. 154295 or Korean Patent Application No. 98-20706, and a paper by the inventor (Journal of Applied Microbiology 85-1-1-8, 1998; Journal of Korea Soil Environment Society, 1-1-39-46, 1996). Experimental Example 3 : Use of Bacterial Consortium EBC 1000 in Treatment of Recalcitrant Wastewater from Medicine Manufacturing Plant. Waste acidic and alkaline recalcitrant wastewater to be dumped into the sea was collected from the medicine manufacturing plants in the Ulsan industrial complex and the middle north region. The waste materials contained medical residues and isopropyl alcohol (IPA), methylene chloride (MC), NaOH, Na SO , dimethylamine (DMA) and methanol and exhibited a high COD Mn value of 20,000 to 100,000 ppm. After inoculating 2.0 x 10 7 /ml of EBCIOOO in each 200 ml of the wastewater, culture was performed with aeration at 20 to 25 °C for 14 days. The results are presented in Table 7. [Table 7] As shown in Table 7, the COD value of the crude wastewater was reduced to 4000 ppm with the decomposition efficiency of 90% after 10 days of culture. The TOC and BOD values also had a downward tendency as the COD value and the number of bacterium of EBCIOOO was 1.6 x 10 10 CFU/ml with an at least ten hundred-fold increase. 7. Tests for Soil and Timber Contaminated by Chlorine Compound Experimental Example 4: Use of Bacterial Consortium EBCIOOO in Treatment of Soil Contaminated by Chlorine Compound. 600 g of the soil contaminated by the pentachlorophenol compound (PCP) was dispersed in 5 liters of tap water standed for one day and added to a slurry apparatus. Compared to decomposition efficiency of the pentachlorophenol compound by the Bu34 strain + 11 decomposition strains (a deposited strain Bui presented in Korean Patent Application No. 98-20706 and 10 unidentified strains decomposing pentachlorophenol) + an unidentified indigenous strain (which appeared in a control apart from the decomposition strains and was isolated by a relative comparison in regard to the distribution of the indigenous strain), the novel bacterial consortium EBCIOOO showed a slightly higher decomposition efficiency, as seen in Table 8. For example, after 14 days, the decomposition efficiency for removal of the chlorine compound was 96% for the Bu34 strain but 98% for the novel bacterial consortium EBCIOOO. [Table 8] Experimental Example 5 After each 5 g of chip and sawdust of waste timber was added to 65 ml of the minimal liquid medium and, then EBCIOOO, subjected to shaking culture at 90 to 100 rpm and 30 °C for 90 hours. The results are presented in Table 9. As shown in Table 9, after 80 hours, the decomposition efficiency of pentachlorophenol(PCP) was 98% under inoculation of EBCIOOO with a hundred-fold increase in the number of bacterium. [Table 9] Experimental Example 6 200 g of sawdust of waste timber was added to 250 ml of the minimal liquid medium, followed by adding EBCIOOO of 2.0 x 10 8 /g (timber). Then, moisture and strains were added to the sawdust and the mixture was standed at the room temperature for 200 days (See. "Composting Method", McBain et al., Biodegradation 6, 47-55, 1995). The results are presented in Table 10. As shown in Table 10, the novel bacterial consortium EBCIOOO showed higher decomposition efficiency within shorter time than Bui or Bu34. [Table 10] As understood from the above experimental examples, the novel bacterial consortium EBCIOOO is useful for efficient decomposition of chlorine compounds as well as a high concentration of recalcitrant toxic chemicals contained in the wastewater to be dumped into the sea. 8. Analytical Test for Decomposition of Recalcitrant Wastewater [COD (Mn Method)] and Pentachlorophenol Compound by means of the Individual Constituent Strains of EBC 1000 The individual pure isolated colonies of EBC 100, EBCIOI, EBC 103, EBC 104, EBC 105, EBC 106, EBC 107, EBC 108 and EBC 109 were inoculated into 20 ml of the liquid medium of waste acidic or alkaline wastewater (prepared by diluting 10% waste acid or alkaline wastewater containing 0.65 g of K HPO 4 , 0.17 g of KH PO 4 , 0.1 g of MgSO 4 , 0.5 g of NaNO 3 and recalcitrant toxic chemicals of medical and petroleum industrial wastewater in 1 liter of deionized water, pH 0 to 14) and then to 20 ml ofthe liquid medium of chlorine compound (prepared by dissolving 0.65 g of K 2 HPO 4 , 0.17 g of KH 2 PO , 0.1 g of MgSO 4 , 0.5 g of NaNO 3 and 50 ppm of pentachlorophenol in 1 liter of deionized water, pH 7.2). After more than 10 days of shaking culture at 20 to 30 °C, the COD and the PCP concentration were measured. As a result, the COD and the PCP concentration were decreased by, on average, 85% for EBC 100, 67% for EBCIOI and EBC103, 50 to 55% for EBC106, EBC107 and EBC108, and about 20% for EBC 104, EBC 105 and EBC 109. This result showed that the individual constituent strains of the bacterial consortium EBCIOOO have the ability to decompose the recalcitrant toxic chemicals and chlorine compounds. However, the bacterial consortium EBCIOOO showed higher growth and decomposition efficiency than the individual constituent strains. As described above, the novel bacterial consortium EBCIOOO has the ability to rapidly decompose a high concentration of recalcitrant chemicals contained in the industrial wastewater and noxious waster materials to be dumped into the sea and purify soil, timber, seepage water and ground water contaminated by chlorine compounds, thus preventing and recovering excellently environmental pollutions. Further, the bacterial consortium EBCIOOO is useful for treating a high concentration of recalcitrant waste materials to be dumped into the sea, or soil, timber, seepage water and ground water contaminated by chlorine compounds in a way of aeration, as well as recovering the contaminated timber. Also, the present invention provides a mixture of Pseudomonas Bu34 strain (Korean Patent No. 154295) and genus Klebsiella Bui strain (Korean Patent Application No. 98-20706) used for recovery of contaminated timber or soil. BUDAPEST TREATY ON THE INTERNATIONAL RECOGNITION OF THE DEPOSIT OF MICROORGANISMS FOR THE PURPOSE OF PATENT PROCEDURE INTERNATIONAL FORM RECEIPT IN THE CASE OF AN ORIGINAL DEPOSIT issued pursuant to Rule 7.1 : LEE, Sung-Gie Keonyeong Apt. 105-304, #2099, Yoπgam-doπg, Sangdang-k-u, Cheongju 360-181, Republic of Korea I . IDENTIFICATION OF THE MICROORGANISM Accession number given by the Identification reference given by the INTERNATIONAL DEPOSITARY DEPOSITOR: AUTHORITY: Mix (EBCIOOO) KCTC. 0652BP D . SCIENTIFIC DESCRIPTION AND/OR PROPOSED TAXONOMIC DESIGNATION The microorganism identified under I above was accompanied by: [ x ] a scientific description [ ] a proposed taxonomic designation (Mark with a cross where applicable) HI. RECEIPT AND ACCEPTANCE This Internationa! Depositary Authority accepts the microorganism identified under I above, U w'lh-iiirchh Λ wi;aαcs K byw i irt A Δ iuigrr 1111 Λ 1 Q9Q9Q9. IV. RECEIPT OF REQUEST FOR CONVERSION The microorganism identified under I above was received by this International Depositary Authority on and a request to convert the original deposit to a deposit under the Budapest Treaty was received by it on V . INTERNATIONAL DEPOSITARY AUTHORITY Name Korean Collection for Type Cultures Signature(s) of person(s) having the power to represent the International Depositary Authoritv of authorized official(s): Address: Korea Research Institute of Bioscience and Biotechnology (KRIBB) #52, Oun-dong, Yusong-ku, Taejon 305-333, Republic of Korea Date: Aug 16 1999

Claims: WHAT IS CLAIMED IS: 1. A bacterial consortium EBCIOOO (KCTC 0652 BP) having an optimum growth under culture in a Luria-Bertani nutrient medium at pH 5 to 8, at a temperature of 25 to 35 °C with shaking at 50 to 100 rpm/min for 24 to 48 hours, the Luria-Bertani nutrient medium containing 10 g of bacto-tryptone, 5 g of bacto-yeast extract and 10 g of NaCl in 1 liter of deionized water, the bacterial consortium EBCIOOO being well grown in a successive transfer culture under the same conditions. 2. A method using a bacterial consortium EBCIOOO in treatment of waste acidic or alkaline recalcitrant toxic chemicals contained in medical or petroleum industrial wastewater to be dumped into the sea, or chlorine compounds, wherein the recalcitrant toxic chemicals contained in the medical industrial wastewater comprise isopropyl alcohol, methylene chloride, NaOH, Na SO 4 , dimethylamine and methanol, the recalcitrant toxic chemicals contained in the petroleum industrial wastewater comprise sodium hydrosulfιte[(NaSO 2 ) ], butadiene, sodium alkylaryl naphthalene sulfonate, acrylonitrile, tetra sodium ethylene diamine tetra acetate dihydrate, ferrous sulfate heptahydrate, tert-dodecyl mercaptan, para-methane hydroperoxide, N-diethyl hydroxyl amine and CH 3 CN, and the chlorine compounds comprise pentachlorophenol (PCP). 3. The bacterial consortium EBCIOOO as claimed in claim 1, comprising EBC 100 being a strain ofthe genus Klebsiella. 4. The bacterial consortium EBCIOOO as claimed in claim 1, comprising EBCIOI being a strain ofthe genus Klebsiella. 5. The bacterial consortium EBCIOOO as claimed in claim 1, comprising EBC 103 being a strain ofthe genus Klebsiella. 6. The bacterial consortium EBCIOOO as claimed in claim 1, comprising EBC 104 being a strain ofthe genus Escherichia. I. The bacterial consortium EBCIOOO as claimed in claim 1, comprising EBC 105 being a strain ofthe genus Providencia. 8. The bacterial consortium EBCIOOO as claimed in claim 1, comprising EBC 109 being a strain ofthe genus Escherichia. 9. The method as claimed in claim 2, wherein the bacterial consortium EBCIOOO comprises EBC 100 being a strain ofthe genus Klebsiella. 10. The method as claimed in claim 2, wherein the bacterial consortium EBCIOOO comprises EBCIOI being a strain ofthe genus Klebsiella. I I . The method as claimed in claim 2, wherein the bacterial consortium EBCIOOO comprises EBC 103 being a strain ofthe genus Klebsiella. 12. The method as claimed in claim 2, wherein the bacterial consortium EBC 1000 comprises EBC 104 being a strain of the genus Escherichia. 13. The method as claimed in claim 2, wherein the bacterial consortium EBCIOOO comprises EBC 105 being a strain ofthe genus Providencia. 14. The method as claimed in claim 2, wherein the bacterial consortium EBCIOOO comprises EBC 109 being a strain ofthe genus Escherichia.

Inventors: LEE SUNG-GIE, LEE, SUNG-GIE
Applicants: LEE SUNG GIE, LEE, SUNG-GIE
Application year: 2000
Main classification: C12N1
IPC codes: B09C1, C02F3, C12N1, C12P39, C12R1