KR100288578B1 - Sorting and method to purify soil, in the maintenance and restoration of the place reclaimed from rubbish - Google Patents
Sorting and method to purify soil, in the maintenance and restoration of the place reclaimed from rubbish Download PDFInfo
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- KR100288578B1 KR100288578B1 KR1019990022239A KR19990022239A KR100288578B1 KR 100288578 B1 KR100288578 B1 KR 100288578B1 KR 1019990022239 A KR1019990022239 A KR 1019990022239A KR 19990022239 A KR19990022239 A KR 19990022239A KR 100288578 B1 KR100288578 B1 KR 100288578B1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/10—Reclamation of contaminated soil microbiologically, biologically or by using enzymes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B07—SEPARATING SOLIDS FROM SOLIDS; SORTING
- B07B—SEPARATING SOLIDS FROM SOLIDS BY SIEVING, SCREENING, SIFTING OR BY USING GAS CURRENTS; SEPARATING BY OTHER DRY METHODS APPLICABLE TO BULK MATERIAL, e.g. LOOSE ARTICLES FIT TO BE HANDLED LIKE BULK MATERIAL
- B07B2220/00—Type of materials being separated
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Abstract
본 발명은 쓰레기 매립장 내의 오염된 토양을 처리하여 이를 유용한 토지로서 재활용하기 위한 것으로, 오염 토양을 굴착하여 조대 입자 및 고분자계 폐기물을 선별제거하고, 스크린을 통과시켜 입자 선별하고 풍력으로 비닐 성분을 분리제거한 후 전처리된 토양을 가열하여 열탈착시키는 단계 또는 전처리된 토양의 pH 및 반응조건을 조절하고 미생물과 반응시키는 단계를 포함하는 본 발명의 오염 토양의 정화방법에 따르면, 환경오염을 방지할 수 있을 뿐만 아니라 처리된 토양은 유용한 토지로 재활용될 수 있다.The present invention is to treat the contaminated soil in the landfill and to recycle it as a useful land, digging out the contaminated soil to screen and remove coarse particles and polymer-based waste, screening the particles through a screen to separate the vinyl components by wind power According to the method for purifying contaminated soil of the present invention, the method comprising the step of heating and desorbing the pretreated soil after removal or adjusting the pH and reaction conditions of the pretreated soil and reacting with microorganisms, can not only prevent environmental pollution. However, the treated soil can be recycled into useful land.
Description
본 발명은 열탈착 공정 또는 생물학적 처리 공정을 이용한 오염 토양의 처리 방법에 관한 것이다.The present invention relates to a method for treating contaminated soil using a thermal desorption process or a biological treatment process.
환경오염원으로서 가장 큰 부분을 차지하는 각종 쓰레기 및 산업 폐기물은 최종적으로 매립지에 매립 방치된 후, 물, 토양, 대기 등의 다양한 매개체를 통해 이동하면서 변화와 변형을 계속하여 토양 오염, 지하수 오염 및 악취 등을 유발함으로써 인간을 포함한 자연 생태계에 영향을 미치고 있다. 그러나, 토양을 매개체로 한 토양 오염의 피해는 수질과 대기를 통한 오염의 피해보다 상대적으로 노출속도가 느리고 전달경로가 복잡하여 이에 관한 처리기술은 아직 정립화되지 않은 상태이다.Various wastes and industrial wastes, which constitute the largest part of the environmental pollution source, are finally landfilled and then moved through various media such as water, soil, and atmosphere, and continue to change and transform, resulting in soil pollution, groundwater pollution, and odors. By affecting natural ecosystems, including humans. However, the damage caused by soil-mediated soil pollution is relatively slower than the damage caused by water quality and air pollution, and the delivery route is complicated. Therefore, the treatment technology has not been established.
기존의 오염 토양의 정화기술로는, 예를 들어 원위치 처리법(in-situ)으로서 오염지역에 주입공을 여러개 실치하고 설치된 주입공에 고온의 증기를 주입함으로써 오염물질을 추출하는 토양 증기 추출법(soil vapor extraction), 오염 토양 주입공에 고화제를 투입하여 오염 토양을 고화처리하는 토양 고화법(soil solidfication), 미생물 및 영양물질을 주입공에 국부적으로 투입하여 유기 오염물질을 분해하는 미생물 분해법(bioremediation), 소각로를 이용하여 오염물질을 직접 소각하는 소각 처리법(incineration treatment) 등이 있다. 그러나, 국내의 경우 토양 환경 정화 기술에 대한 지식과 경험이 부족하여 그 처리기술 개발이 아직 미흡한 실정이고, 외국은 물리/화학적 처리기술 분야는 상대적으로 개발이 완료되어 그 적용단계에 있으며 원위치 처리의 미생물 분해법(in-situ bioremediation) 분야는 1970 년대부터 연구가 활발히 수행되기 시작하여 그 적용단계에 있다.Existing techniques for the purification of contaminated soil, for example, in-situ, soil vapor extraction method that extracts contaminants by placing multiple injection holes in the contaminated area and injecting high-temperature steam into the installed injection holes. vapor extraction), soil solidfication to solidify contaminated soil by injecting a solidifying agent into the contaminated soil injection hole, and bioremediation to decompose organic pollutants by locally injecting microorganisms and nutrients into the injection hole. ), Incineration treatment, which incinerators directly incinerate contaminants. However, in Korea, there is a lack of knowledge and experience in soil environment purification technology, and the development of treatment technology is still insufficient. In the foreign countries, the physical / chemical treatment technology field is relatively developed and is in the application stage. The field of in-situ bioremediation has been actively researched since the 1970s and is in its application stage.
이에 본 발명자들은 기존 기술에 비하여 신규성 및 진보성이 있는 열탈착 또는 생물학적 처리공법을 이용함으로써 우리나라에 방치되어 있는 1000 여개의 불량 매립장의 오염 토양을 안정화시켜 재활용(체육시설, 주차장, 화훼 단지, 축사, 경작지 등)할 수 있는 기술을 개발하여 본 발명을 완성하였다.Accordingly, the present inventors stabilized the contaminated soils of about 1000 poor landfill sites that are left in Korea by using thermal desorption or biological treatment techniques, which are novel and advanced compared to the existing technologies, and recycle them (sports facilities, parking lots, flower gardens, barns, farmland). The present invention was completed by developing a technology that can be used.
본 발명의 목적은 쓰레기 매립장내 오염된 토양을 안정화시켜 재활용 가능한 수준으로 처리하는 방법, 및 이에 사용되는 선별장치를 제공하는 것이다.It is an object of the present invention to provide a method for stabilizing contaminated soil in a landfill and treating it to a recyclable level, and a sorting device used therein.
도 1은 본 발명의 쓰레기 선별과 오염토양의 안정화 방법의 흐름도이고,1 is a flow chart of the waste sorting and stabilization method of the soil of the present invention,
도 2는 본 발명에 사용되는 선별장치의 한 예의 개략도이고,2 is a schematic diagram of an example of a sorting apparatus used in the present invention,
도 3은 본 발명에 사용되는 생물 반응기의 한 예의 개략도이다.3 is a schematic diagram of one example of a bioreactor used in the present invention.
<도면의 주요부분에 대한 부호의 설명><Description of the symbols for the main parts of the drawings>
10 : 회전 선별기 드럼 11 : 스크린10: rotary sorter drum 11: screen
12 : 회전 기어 13 : 감속기12: rotary gear 13: reducer
14 : 가열버너 1 15 : 가열버너 214: heating burner 1 15: heating burner 2
16 : 투입구 17 : 콘베어16: Inlet 17: Conveyor
18 : 가이드 플레이트 19 : 송풍기 토출 후드18: guide plate 19: blower discharge hood
100 : 생물반응기 드럼 101 : 온도 조절기100 bioreactor drum 101 temperature controller
102 : 회전 조절기 103 : 세라믹 히터102: rotary regulator 103: ceramic heater
104 : 산기판 105 : 균주 투입 포트104: acid substrate 105: strain injection port
106 : 배출가스라인 107 : 송풍기106: exhaust gas line 107: blower
108 : 플로우 미터 109 : 필터108: flow meter 109: filter
110 : 세정기 111 : 흡착 여과탑110: washing machine 111: adsorption filtration tower
112 : 오염 토양112: contaminated soil
상기 목적을 달성하기 위해, 본 발명의 한 태양에서는 (1) 쓰레기 매립장내 오염 토양을 굴착하여 조대입자 및 고분자계 폐기물을 선별제거하는 단계; (2) 오염 토양을 스크린에 통과시켜 분리하고 풍력에 건조시켜 비닐 성분을 분리하는 단계; 및 (3) 선별 처리된 토양을 150 내지 350℃로 가열하여 열탈착시키는 단계를 포함하는 오염 토양의 정화방법을 제공한다.In order to achieve the above object, in one aspect of the present invention (1) the step of excavating the contaminated soil in the landfill to remove coarse particles and polymer-based waste; (2) separating the contaminated soil by passing it through a screen and drying in wind to separate the vinyl component; And (3) provides a method for the purification of contaminated soil comprising the step of heat desorption by heating the treated soil to 150 to 350 ℃.
본 발명의 다른 태양에서는, 상기 방법에서 단계 (3)으로서 전처리된 토양의 pH를 7 내지 8, 온도를 30 내지 50℃ 및 습도를 40 내지 50%로 조절한 후 토양에 미생물을 투입하여 토양 중의 오염 유기물질을 분해제거시키는 단계를 포함하는 방법을 제공한다.In another aspect of the present invention, the microorganisms are added to the soil by adjusting the pH of the pretreated soil to 7 to 8, the temperature to 30 to 50 ° C. and the humidity to 40 to 50% as step (3). It provides a method comprising the step of decomposing and removing contaminating organic material.
본 발명의 다른 목적을 달성하기 위하여, 본 발명에서는 오염토양 투입구(16), 투입구에 인접하여 위치된 오염토양을 가열하기 위한 가열버너(14 및 15), 가열처리된 토양과 기타 폐기물을 분리하기 위한 스크린(11) 및 폐기물을 배출하는 유출부(18)가 장착된 회전식 선별기 드럼(10) 및 폐기물 중의 비닐성분을 풍력에 의해 분리하기 위한 송풍기 토출 후드(19)를 포함하는, 제 1 항의 방법을 수행하기 위한 오염토양의 선별장치를 제공한다.In order to achieve another object of the present invention, in the present invention, the contaminated soil inlet 16, the heating burners 14 and 15 for heating the contaminated soil located adjacent to the inlet, separating the heat treated soil and other wastes. The method of claim 1 comprising a rotary sorter drum 10 equipped with a screen 11 and an outlet 18 for discharging waste and a blower discharge hood 19 for separating by wind the vinyl component in the waste. Provides a sorting device for contaminated soil to carry out.
이하 본 발명을 좀더 상세하게 설명한다.Hereinafter, the present invention will be described in more detail.
본 발명은 쓰레기 매립장의 오염된 토양을 정화복구하여 재활용하기 위한 것으로, 그 공정과정은 다음과 같다.The present invention is to purify and recover the contaminated soil in the landfill, the process is as follows.
우선, 쓰레기 매립지의 오염 토양을 굴착하여 취하고 분해되지 않은 조대입자 폐기물 및 고분자계 폐기물은 별도분리 소각처리하고 스크린에서 분리된 오염 토양은 열탈착 또는 생물처리 공정을 통해 각종 오염 물질을 제거한다.First, the contaminated soils of landfills are excavated, uncoated coarse particles and polymer wastes are separately incinerated, and contaminated soils separated from the screen are removed by various methods of thermal desorption or biotreatment.
이어서, 상기 전처리 과정을 거친 오염 토양에 함유된 농약류, 휘발성 유기화합물(VOC, SVOCs), 폴리염화된 비페닐(polychlorinated biphenyl) 등의 유기성 오염물질을 열탈착 또는 미생물 반응 공정으로 분해시켜 제거한다.Subsequently, organic contaminants such as pesticides, volatile organic compounds (VOCs, SVOCs), and polychlorinated biphenyls contained in the contaminated soil after the pretreatment are decomposed by thermal desorption or microbial reaction processes.
열탈착 공정에서는 오염 토양에서 오염 물질이 휘발될 수 있는 온도, 예를 들어 150 내지 350℃로 오염 토양을 가열 처리하여 오염 토양 중의 각종 오염 물질을 증기화 또는 열적 산화분해시킴으로 탈착제거한다.In the thermal desorption process, the contaminated soil is heated to a temperature at which contaminants can be volatilized in the contaminated soil, for example, 150 to 350 ° C., to desorb and remove various contaminants in the contaminated soil by vaporization or thermal oxidative decomposition.
미생물 반응 공정에서는 상기 전처리된 오염 토양의 미생물 생육 가능한 조건, 예를 들어 pH는 7 내지 8(산 또는 알칼리에 의해 조절), 습도는 40 내지 50%, 온도는 30 내지 50℃로 조절한 다음, 유기물질을 분해할 수 있는 미생물, 이들 미생물의 호흡 성장에 필요한 산소 및 각종 영양물질을 공급하여 오염 토양과 반응시킴으로써 오염 토양 중의 오염 유기물질을 생물학적으로 분해하여 제거한다. 이 과정에서, 오염 토양 중의 오염 유기물을 먹이로 하고 공급된 산소는 호기성 및 통혐기성 미생물의 호흡활성에 의해 빠른 속도로 분해 소비되어 CO2,H2O, 저급 탄화수소 및 열을 생산시킨다. 본 발명에서 사용할 수 있는 미생물로는 바실루스 서브틸리스(Bacillus subtilis), 바실루스 폴리믹사(Bacillius polymyxa), 로도슈도모나스(Rhodopseudomonas), 오토트로픽박터(Autotrophic bactor), 슈도모나스(Pseudomonas), 니트로박터(Nitro bacter), 트리코더마 비리드(Trichoderma viride), 셀룰로모나스(CellulomonasEp), 악티노마이세스(Actinomyces), 필라멘투스 펀지(Filamentous fungi) 등이 있으며, 이들 2종 이상 혼합하여 사용할 수도 있고, 특히 본 발명자들의 특허 제 134204 호에 기술된 균주인 바실루스 속(Bacilliussp.) 균주 KHR-10-MX,셀룰로모나스속(cellulomonassp.) KHR-15-MX 및 복합균주 KHR-5-MX를 단독 또는 혼합하여 사용하는 것이 바람직하다.In the microbial reaction process, conditions for microbial growth of the pretreated contaminated soil, for example, pH is adjusted to 7 to 8 (controlled by acid or alkali), humidity to 40 to 50%, and temperature to 30 to 50 ° C, Microorganisms capable of decomposing organic substances, oxygen and various nutrients necessary for respiration growth of these microorganisms are supplied and reacted with contaminated soil to biologically decompose and remove contaminated organic substances in contaminated soil. In this process, contaminated organics in contaminated soil are fed and the oxygen supplied is rapidly decomposed and consumed by the respiratory activity of aerobic and anaerobic microorganisms to produce CO 2, H 2 O, lower hydrocarbons and heat. A microorganism that can be used in the present invention include Bacillus subtilis (Bacillus subtilis), Bacillus poly miksa (Bacillius polymyxa), also Pseudomonas (Rhodopseudomonas), auto tropic bakteo (Autotrophic bactor), Pseudomonas (Pseudomonas), nitro bakteo (Nitro bacter ), Trichoderma viride , Cellulomonas Ep, Actinomyces , Filamentous fungi , and may be used in combination of two or more thereof. Bacillius sp. Strain KHR-10-MX, cellulomonas sp. KHR-15-MX and the combination strain KHR-5-MX, which are the strains described in the inventors' patent No. 134204, alone or in combination It is preferable to mix and use.
이와 같은 방법으로 매립지의 오염 토양을 정화 처리함으로써 오염 토양을 유용한 토지(화훼 단지, 축사, 공원, 체육시설 등)로 재활용할 수 있다.In this way, the contaminated soil in landfills can be purified and recycled into useful land (flower complexes, barns, parks, sports facilities, etc.).
이하 본 발명을 하기 실시예에 의하여 더욱 상세하게 설명하고자 한다. 단, 하기 실시예는 본 발명을 예시하기 위한 것일 뿐, 본 발명의 범위가 이들만으로 한정되는 것은 아니다.Hereinafter, the present invention will be described in more detail with reference to the following examples. However, the following examples are only for illustrating the present invention, and the scope of the present invention is not limited thereto.
실 시 예 1: 열탈착 공정에 의한 오염 토양 정화 Example 1 Purification of Contaminated Soil by Thermal Desorption Process
서울시 난지도 매립지에서 토양을 굴착기로 취하여 조대형 고형 협잡물질을 스크린을 통과시켜 선별하여 소각처리하고, 스크린을 통과시켜 오염물질을 분리하였다. 이어서, 도 2에 도시된 회전 선별 장치를 이용하여 열탈착 공정을 실시하였다. 먼저, 수평식 원통형으로 구성된 회전 선별기 드럼(10)의 투입구(16)에 콘베어(17)를 이용하여, 상기 전처리된 오염 토양을 투입하였다. 가열버너 1(14) 및 가열버너 2(15)를 150 내지 350℃가 유지되도록 가열하고, 감속기(13)와 회전 선별기 드럼(10)에 부착된 원통형 회전기어(12)를 연동시켜 드럼(10)을 회전하면서 드럼(10)에 직접 또는 간접으로 열을 전달시켜 오염물질을 열적 산화 분해하였다.Soil was taken from the landfill site of Nanjido, Seoul, and the coarse solid contaminants were screened and incinerated, and the contaminants were separated through the screen. Subsequently, the thermal desorption process was performed using the rotary sorting apparatus shown in FIG. First, the pretreated contaminated soil was introduced into the inlet 16 of the rotary sorter drum 10 having a horizontal cylindrical shape using a conveyor 17. The heating burner 1 (14) and the heating burner 2 (15) are heated to maintain 150 to 350 ° C, and the reduction gear 13 and the cylindrical rotary gear 12 attached to the rotary sorter drum 10 interlock with each other for the drum 10 The heat was transferred directly or indirectly to the drum 10 while rotating the thermally decomposed contaminants.
회전식 선별기(10) 전후단 스크린(11)을 통해 입자 크기별로 선별하여 배출하고, 잔류 비닐류는 가이드 플레이트(18)를 따라 배출하면서 송풍기 토출 후드(19)를 통해 풍압에 의해 분리시켜 배출하였다.The sorter was discharged by particle size through the front and rear end screens 11 of the rotary sorter 10, and the residual vinyls were discharged by being separated by wind pressure through the blower discharge hood 19 while being discharged along the guide plate 18.
오염 토양의 회전 속도 및 온도에 따른 오염 유기물질의 제거율을 토양 오염 시험 공정법으로 측정하여 하기 표 1에 나타내었다.The removal rate of the contaminated organic material according to the rotational speed and temperature of the contaminated soil was measured by the soil contamination test method and is shown in Table 1 below.
실 시 예 2 : 생물학적 공정에 의한 오염 토양 정화Example 2 Purification of Contaminated Soil by Biological Process
서울시 난지도(15년간 매립지로 사용), 대전시 대덕구 상서동 매립장(1년 5개월간 매립지로 사용), 공주시 신관동 매립장(7년간 매립지로 사용) 및 부여군 부여읍 구교리 매립장(17년간 매립지로 사용)의 오염된 토양을 각각 굴착기로 취하여 상기 실시예 1과 동일한 방법으로 조대형 고형 협잡물질을 선별하여 소각처리하고, 스크린 및 풍력 처리하여 비닐 성분을 제거하였다.Contaminated soil in Nanjido, Seoul (used as a landfill for 15 years), Sangseo-dong land in Daedeok-gu, Daejeon (used as a landfill for 1 year and 5 months), Singi-dong landfill in Gongju-si (used as a landfill for 7 years) and Gugyo-ri landfill site in Buyeo-eup, Buyeo-eup (used as landfill for 17 years) Each was taken as an excavator, the coarse solid contaminant was selected and incinerated in the same manner as in Example 1, and the screen and wind treatment were used to remove the vinyl component.
이어서, 도 3에 도시된 생물 반응기(100)에 상기 전처리된 오염 토양(112)을 투입하고, 온도 조절기(101)의 세라믹 히터(103)로 생물 반응기의 온도를 30 내지 50℃로 유지시키고, pH를 7 내지 8로 조정하고, 습도를 45%로 조정하여 바실루스속 균주 KHR-10-MX(대한민국 특허 제 134204 호)를 균주 투입 포트(105)에 투입하였다. 송풍기(107)에 의한 신선한 공기를 플로우 미터(108)로 송풍량을 조절하면서 필터(109)를 통과시켜 산기판(104)을 통해 공급시키고, 회전 조절기(102)를 이용하여 생물반응기(100)를 5 내지 17 rpm으로 회전시키면서 생물학적 반응을 진행시켰다. 생성된 가스는 배출가스라인(106)을 통해 배출시켜 배출가스 세정기(110) 및 흡착탑(111)을 거쳐 배기시켰다.Subsequently, the pretreated contaminated soil 112 is introduced into the bioreactor 100 illustrated in FIG. 3, and the temperature of the bioreactor is maintained at 30 to 50 ° C. with the ceramic heater 103 of the temperature controller 101. Bacillus strain KHR-10-MX (Korean Patent No. 134204) was introduced into the strain injection port 105 by adjusting the pH to 7-8 and the humidity to 45%. The fresh air by the blower 107 is passed through the filter 109 while controlling the air flow rate to the flow meter 108 to be supplied through the acid substrate 104, and the bioreactor 100 is operated using the rotation controller 102. The biological reaction proceeded while rotating at 5 to 17 rpm. The generated gas was discharged through the exhaust gas line 106 to be exhausted through the exhaust gas cleaner 110 and the adsorption tower 111.
상기 생물 반응기(100)에서의 우점종 미생물과 분해 메카니즘은 다음과 같다:The dominant species microorganisms and degradation mechanisms in the bioreactor 100 are as follows:
각 시험군에서의 시간 경과에 따른 오염 토양 중의 오염물질의 제거율을 토양 오염 시험 공정법으로 측정하여 하기 표 2에 나타내었다.The removal rate of contaminants in the contaminated soil over time in each test group was measured by the soil contamination test method and is shown in Table 2 below.
본 발명의 방법에 따르면 쓰레기 매립장내 오염 토양을 고효율로 정화 처리함으로써 환경오염을 방지할 수 있을 뿐만 아니라 정화된 토양은 유용한 토지로 재활용하여 국토이용을 극대화, 국가 재정을 절약하는 효과를 얻을 수 있다.According to the method of the present invention, the contaminated soil in the landfill can be efficiently purified to prevent environmental pollution, and the purified soil can be reused as useful land to maximize the use of land and save national finances. .
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KR20020013016A (en) * | 2000-08-10 | 2002-02-20 | 양인모 | Apparatus and method for bioremediation for contaminated sediments and soil |
KR100344359B1 (en) * | 2001-07-26 | 2002-07-22 | 김학로 | Landfill maintenance, restoration method and landfill self-formation, self-healing complex order floor construction method |
KR100750596B1 (en) | 2006-09-12 | 2007-08-21 | 전남대학교산학협력단 | Soil purification method using microwave radiation and microbe and purification system |
KR100796530B1 (en) | 2007-03-09 | 2008-01-21 | 전남대학교산학협력단 | Soil purification method using microorganism and microwave radiation |
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KR100301743B1 (en) * | 1999-06-23 | 2001-09-22 | 이이용 | The wastes vinyl separation device of a food garbage |
KR20010100077A (en) * | 2001-09-10 | 2001-11-14 | 김학로 | Stabilization, excavation and screening methods for the maintenance and restoration of unsanitary landfills |
KR20020013949A (en) * | 2002-01-22 | 2002-02-21 | 김진택 | restoration system of contamination soil and waste reclaiming soil |
KR100905522B1 (en) * | 2009-02-27 | 2009-07-01 | 금광개발 주식회사 | A restoration method and apparatus of soil polluted by oil and heavy metal |
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KR960000610Y1 (en) * | 1993-04-13 | 1996-01-18 | 용천성 | Terminal block |
KR970070163A (en) * | 1996-04-10 | 1997-11-07 | 최훈 | Method and apparatus for biological treatment of contaminated soil |
KR19980073418A (en) * | 1997-03-14 | 1998-11-05 | 박원훈 | Indirect heated fluidized bed apparatus with interpolated heating tubes for oil contaminated soil restoration |
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KR960000610Y1 (en) * | 1993-04-13 | 1996-01-18 | 용천성 | Terminal block |
KR970070163A (en) * | 1996-04-10 | 1997-11-07 | 최훈 | Method and apparatus for biological treatment of contaminated soil |
KR19980073418A (en) * | 1997-03-14 | 1998-11-05 | 박원훈 | Indirect heated fluidized bed apparatus with interpolated heating tubes for oil contaminated soil restoration |
Cited By (4)
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KR20020013016A (en) * | 2000-08-10 | 2002-02-20 | 양인모 | Apparatus and method for bioremediation for contaminated sediments and soil |
KR100344359B1 (en) * | 2001-07-26 | 2002-07-22 | 김학로 | Landfill maintenance, restoration method and landfill self-formation, self-healing complex order floor construction method |
KR100750596B1 (en) | 2006-09-12 | 2007-08-21 | 전남대학교산학협력단 | Soil purification method using microwave radiation and microbe and purification system |
KR100796530B1 (en) | 2007-03-09 | 2008-01-21 | 전남대학교산학협력단 | Soil purification method using microorganism and microwave radiation |
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