KR100828545B1 - Soil washing machine by high pressured air-lifting and turbulence - Google Patents

Soil washing machine by high pressured air-lifting and turbulence Download PDF

Info

Publication number
KR100828545B1
KR100828545B1 KR1020060120364A KR20060120364A KR100828545B1 KR 100828545 B1 KR100828545 B1 KR 100828545B1 KR 1020060120364 A KR1020060120364 A KR 1020060120364A KR 20060120364 A KR20060120364 A KR 20060120364A KR 100828545 B1 KR100828545 B1 KR 100828545B1
Authority
KR
South Korea
Prior art keywords
soil
air supply
air
washing tank
washing
Prior art date
Application number
KR1020060120364A
Other languages
Korean (ko)
Inventor
한승호
최규문
곽무영
Original Assignee
주식회사 드림바이오스
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by 주식회사 드림바이오스 filed Critical 주식회사 드림바이오스
Priority to KR1020060120364A priority Critical patent/KR100828545B1/en
Application granted granted Critical
Publication of KR100828545B1 publication Critical patent/KR100828545B1/en

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/02Extraction using liquids, e.g. washing, leaching, flotation

Abstract

An apparatus and a method for washing of soil are provided to allow the detergent to separate soil and a contamination source and remove the contamination source strongly adsorbed onto the soil through collision and friction between the soils by stirring contaminated soil and the detergent, forming a turbulent flow, and generating air-bubbles in a washing tank into which a proper detergent is injected, thereby performing a chemical treatment and a physical treatment in succession. An apparatus for washing of soil by high pressure ejected air-bubbles and turbulence comprises: a washing tank(1) in which a turbulent flow forming device(30) is embedded, the turbulent flow forming device comprising a turbulent flow forming cone(9) having whirling vanes(7) spirally formed on an outer periphery thereof, and a cylindrical draft(8) fixed by a plurality of fixing members; a solid-liquid transfer equipment(40) including a circulation pipe(4) connected to an inner part of the draft, a suction port(2) connected to the washing tank, a discharge pipe(14) for discharging contents of the washing tank, a solid-liquid transfer pump(3) formed on a part at which the circulation pipe, the suction port and the discharge pipe are connected to one another, and a discharge control valve(15) installed on the discharge pipe; an air supplying, joining and transferring equipment(50) including an air supply pump A(5) and an air supply pipe(6) which supplies air supplied from the air supply pump A, and of which an end portion is connected to the circulation pipe; and a high pressure air ejector(60) including ejection nozzles(12) which are installed on a bottom part of the washing tank and connected to a circular air supply pipe(11) such that the air supply pipe is connected to an air supply pump B(10).

Description

고압 분사된 공기방울 및 난류에 의한 토양세척장치{Soil washing machine by high pressured air-lifting and turbulence}Soil washing machine by high pressured air-lifting and turbulence

도 1 은 본 발명의 고압공기방울 및 난류형성장치에 의한 토양세척장치 전체 구성도1 is a overall configuration of the soil washing apparatus by the high-pressure air bubble and turbulence forming apparatus of the present invention

도 2 는 본 발명의 고액고압분사에 따른 유체 흐름도2 is a flow chart according to the high liquid-pressure injection of the present invention

도 3 는 본 발명의 공기고압분사에 따른 유체흐름도Figure 3 is a flow chart of the fluid according to the high pressure jet of the present invention

도 4 는 본 발명에 따른 전체 난류 흐름도
도 5는 본 발명의 고압공기방울 및 난류형성장치에 의한 토양세척장치 전체 구성도를 보인 단면예시도
4 is a complete turbulence flow chart in accordance with the present invention.
5 is a cross-sectional view showing the overall configuration of the soil washing apparatus by the high-pressure air bubble and turbulence forming apparatus of the present invention

<도면의 주요부분에 대한 부호의 설명><Description of the code | symbol about the principal part of drawing>

1 : 세척조 2 : 흡입구1: washing tank 2: suction port

3 : 고액이송펌프 4 : 순환관3: solid-liquid transfer pump 4: circulation pipe

5 : 공기공급펌프A 6 : 공기공급관5: air supply pump A 6: air supply pipe

7 : 회오리날개 8 : 드래프트7: whirlwind 8: draft

9 : 콘 10 : 공기공급펌프9: cone 10: air supply pump

11 : 공기공급관 12 : 분사노즐
14 ; 배출관 15 : 제어밸브
30 : 난류형성장치 40 : 고액이송장치부
50 : 이송장치 60 : 공기고압분사장치
11 air supply pipe 12 injection nozzle
14; Outlet line 15: control valve
30: turbulence forming device 40: solid-liquid transfer unit
50: conveying device 60: air high pressure jet device

삭제delete

삭제delete

본 발명은 유류로 오염되어 있는 토양을 복원하는 토양세척공법에 관한 것으로 좀더 상세하게는 물리적 교반을 기본으로 오염토양에 흡착되어 있는 유류를 탈착 또는 탈리시키며, 필요시 세척제를 투입하여 최적의 세척제의 양으로 대량의 오염토양을 물리화학적으로 동시에 처리할 수 있도록 한 장치이다.The present invention relates to a soil washing method for restoring soil contaminated with oil, and more particularly, to desorb or desorb oil adsorbed to contaminated soil based on physical agitation. It is a device that can simultaneously handle a large amount of contaminated soil in quantity.

국내에 산재한 주유소, 저유소 등의 석유류 저장시설 및 석유화학공장, 그리고 군사지역의 연료저장시설과 같이 토양환경보전법에서 토양오염유발시설로 지정된 시설들의 설비 노후화 및 취급 부주의 등으로 유출된 유류 및 유기오염물로 인한 토양오염은 간접적이고 만성적이며, 경제적으로나 시간적으로 완전복원이 어려운 특성을 가지고 있으며, 대부분의 저장연료는 복합성분의 석유계 탄화수소로 구성되어 있어 인체 및 토양생물에 유해한 성분들을 많이 함유하고 있기 때문에 이러한 오염토양에 대한 적절한 처리가 필요하다. 또한 공장의 이전 및 택지조성, 개발 등에 의하여 기존에 간과되었던 토양오염이 토양실태조사 및 토양환경평가 등에 의하여 현실적으로 토양오염의 심각성이 부각되고 있는 실정이며, 이 경우 토양오염정화공사는 건설공사에 수반되는 일련의 공정이 되고 있는 현실에서 오염토양을 굴착하여 저비용과 고효율로 단시간 내에 처리하는 방법이 선호되고 있는 실정이다.Oil and organic pollutants spilled due to equipment aging and careless handling of facilities designated as soil pollution facilities in the Soil Environment Conservation Act, such as petroleum storage facilities, petrochemical plants, etc. Soil pollution is indirect, chronic, economically and timely, it is difficult to fully restore. Most of the stored fuels are composed of complex petroleum hydrocarbons, which contain a lot of harmful substances to human body and soil organisms. Therefore, appropriate treatment for such contaminated soil is required. In addition, soil pollution, which has been previously overlooked due to factory relocation, land site development, and development, is being highlighted by soil status survey and soil environment evaluation. In this case, soil pollution purification work is accompanied by construction work. In the reality that a series of processes are being performed, a method of digging contaminated soil in a short time with low cost and high efficiency is preferred.

토양정화방법으로는 주유소, 정유공장과 화학공장 등과 같이 시설물의 철거 및 영업중단 등이 불가능한 지역은 현장에서 지중 오염원을 직접적으로 처리하는 현장내 처리법이 이용되고 있고, 그 외 굴착이 가능한 오염부지의 오염토양은 굴착 하여 처리하는 현장외 처리법이 이용되고 있다. 이 현장외 처리법 중 오염부지가 낮은 깊이의 오염원일 경우에는 지상으로 굴착한 후 지표면에 낮은 높이로 야적하여 주기적으로 뒤집기를 실시함으로써 공기를 공급해주는 호기성 생분해 공정인 토양경작법(Landfarming)이 사용되어 왔다. 그러나 토양경작법은 낮은 높이로 넓게 야적하여 대기와의 접촉 공간이 많아야 하므로 많은 처리공간이 필요하며, 휘발성 유기물질이 대기중으로 비산되어 2차 오염을 일으키는 문제점이 있고 생분해 정화작업 시 미생물 활성에 필수적인 산소가 효율적으로 공급되도록 주기적으로 경작처리를 해야하는 단점이 있다. 이에 따라 좁은 부지에서 오염토양을 지상으로 높게 야적하고 토양층 내부로 관입한 유공관으로 산소를 공급시켜 줌으로써 미생물의 활발한 분해반응을 통하여 유류 및 유기오염물질을 처리할 수 있는 지상야적처리방법(Biopile)이 사용되고 있다.In areas where it is impossible to dismantle or shut down facilities, such as gas stations, oil refineries, and chemical plants, on-site treatment is used to directly treat underground pollutants at the site. Off-site treatment is used to excavate contaminated soil. In the off-site treatment, if the polluted site is a source of low depth, the soil farming method, an aerobic biodegradation process that supplies air by excavating to the ground and depositing it on the ground at low height periodically, is used. come. However, the soil cultivation method requires a lot of processing space because it has to be wide-spread at low height and has a lot of contact space with the atmosphere, and there is a problem that volatile organic substances are scattered into the air causing secondary pollution and essential for microbial activity during biodegradation and purification work. There is a disadvantage in that the cultivation treatment must be performed periodically so that oxygen is efficiently supplied. As a result, the ground field treatment method (Biopile), which can treat oil and organic pollutants through active decomposition of microorganisms by supplying oxygen to contaminated soils that are highly confined to the ground and infiltrating into the soil layer from a narrow site, It is used.

지상야적처리방법은 오염토양을 굴착하여 지표면 바닥에 차수막과 배수로 등의 부지를 조성하여 부지 위에 오염토양을 상층부로 높게 쌓아 올린 후 오염토양 위로 차수막을 설치하고 토양층 내부에는 유공관을 설치하여 진공에 의한 감압 또는 가압의 공기를 공급하여 연속적인 공기흐름을 유도함으로써 토양의 기공에 잔류하는 유류 및 유기오염물의 증발을 촉진하여 제거한다. 이렇듯 좁은 부지에서의 적용이 가능하며 오염원을 기체상으로 변화시켜 처리함으로써 침출수 및 대기로 방출되는 휘발성 오염물질로 인한 제 2차 또는 3차 오염의 확산을 막을 수 있는 특징이 있지만 이 방법 역시 대상 부지의 확보가 어렵고 지하수가 다량 포함된 토양의 경우 적용의 한계가 있으며, 정화토양의 양에 따라 장시간이 소요되는 문제점이 있 다.Ground yard treatment method is to excavate contaminated soil, build a site such as a membrane and a drainage channel on the ground surface, pile up contaminated soil to the upper layer on the site, install a membrane over the contaminated soil, and install a perforated pipe inside the soil layer. By supplying air under reduced pressure or pressure, continuous air flow is induced to promote and remove oil and organic contaminants remaining in the pores of the soil. Although it can be applied in such a narrow site, it is possible to prevent the spread of secondary or tertiary pollution by volatile contaminants released to leachate and air by changing the pollutant source to gas phase, but this method is also the target site. Soil is difficult to secure and there is a limit to the application of soil containing a large amount of groundwater, it takes a long time depending on the amount of purified soil.

이에 따라 단시간에 오염토양을 직접적으로 처리할 수 있고 오염원의 농도가 높거나 정화장소의 협소함 등을 해소할 수 있는 토양세척법이 있는데, 이 방법은 굴착된 오염토양을 수세척 또는 세척제에 의하여 화학적으로 처리를 함으로써 오염원을 직접 회수하거나 기상이나 액상 등의 유리된 상태로 전환하여 처리하는 기술적인 방법을 사용하고 있다.Accordingly, there is a soil washing method that can directly treat the contaminated soil in a short time, and solve the high concentration of pollutants or narrowing of the purification site. This method uses chemical cleaning of the excavated contaminated soil by water washing or cleaning agent. The treatment is carried out using a technical method of directly recovering the pollutant source or converting it into a free state such as gaseous phase or liquid phase.

지금까지의 토양세척법은 지하수의 존재 유무에 관계없이 오염된 부지를 신속하게 정화하기 위하여 오염토양을 지상으로 굴착하고 굴착된 토양을 세척용수가 들어있는 세척장치에 간헐식 또는 연속식으로 이송하여 교반 또는 회전하는 드럼통에서 세척작업을 진행한 후에 세척된 토양은 배출하여 재활용하거나 매립하고 토양과 분리되어 발생된 세척수는 별도의 독립된 시설물에서 생물학적 또는 물리화학적으로 정화한 후 수질규제 농도를 만족시킨 후 배출하는 일련의 작업으로 진행된다. 또한 상기 토양세척법은 굴착된 오염토양을 일정한 세척장치에 투입하고, 계면활성제와 같은 세척제를 물리적으로 교반시키며, 세척제에 의한 화학적처리로 진행되는 것이 일반적으로서 기존 토양세척법은 세척시간이 장시간 소요되며, 세척제의 양이 유실량 등에 따라 적정량 이상으로 다량 소요되고 토양의 불균질성에 의하여 평균 오염농도에 따라 산정된 세척제량이 부족할 경우 정화효율이 저하되는 단점이 있다.So far, the soil washing method has excavated contaminated soil to the ground to quickly clean up the contaminated site regardless of the presence of groundwater and transported the excavated soil intermittently or continuously to the washing device containing the washing water. After washing in stirring or rotating drums, the washed soil is discharged and recycled or reclaimed, and the wash water generated by separating it from soil is biologically or physically purified in a separate facility and satisfies the water quality regulation. The discharge proceeds in a series of operations. In addition, the soil washing method is to put the excavated contaminated soil into a certain washing device, to physically agitate the cleaning agent, such as surfactant, and to proceed with chemical treatment by the cleaning agent, conventional soil washing method takes a long time to wash In addition, the amount of the cleaning agent takes a large amount more than the appropriate amount depending on the amount of loss, etc. There is a disadvantage that the purification efficiency is lowered if the amount of the cleaning agent calculated according to the average pollution concentration due to the heterogeneity of the soil.

이에 따라 토양세척법을 적용하기 위하여 물리적인 처리 효과를 향상시킴에 따라 세척제에 의한 화학적 처리 효율을 더욱 증대시켜서 적정한 세척제의 양을 주 입하여 경제성을 확보하고, 세척시간을 줄일 수 있는 토양세척장치가 필요하게 되었다.Accordingly, in order to apply the soil washing method, the physical treatment effect is improved, so that the chemical treatment efficiency by the washing agent is further increased. Was needed.

본 발명은 굴착된 유류오염토양을 현장외처리법 중 토양세척법에 의하여 정화하는 장치 및 방법으로서 적정한 세척제를 주입한 세척조 내에서 고액이송분사에 의한 오염토양과 세척제의 교반작업과 난류형성장치에 의한 난류생성 및 공기고압분사에 의한 공기방울에 의하여 화학적처리 및 물리적처리가 연속적으로 진행되어 세척제에 의한 토양과 오염원의 분리 및 토양간의 충돌 및 마찰에 의한 토양에 강하게 흡착된 오염원을 제거하기 위한 토양세척장치 및 방법이다.The present invention is an apparatus and method for purifying excavated oil contaminated soil by soil washing method in an off-site treatment method, by agitating and contaminating soils and a turbulence forming device by solid-liquid injection in a washing tank in which an appropriate detergent is injected. Soil cleaning to remove the pollutants strongly adsorbed on the soil by the separation of soil and pollutants by the cleaning agent and the collision and friction between the soil by chemical treatment and physical treatment by the air bubbles generated by the turbulence and high pressure spray Apparatus and method.

오염된 토양을 굴착하고 5mm이하의 입경으로 선별한 후 특별히 제작된 세척조에 세척제, 세척용수와 토양을 일정비율로 주입한다. 주입된 토양와 용수의 고액분은 세척조 하단부에 설치되어진 흡입구와 순환관을 통해 고액이송펌프를 의하여 동시에 고속으로 이송되며, 이 순환관의 말단부에서 공급되어진 고압공기와 접촉하면서 유체(流體)의 고압분사가 이루어지며 교반작업이 수반된다. 또한 분사되어진 유체는 세척조 하단 중앙에 설치된 난류형성장치에 의하여 난류를 일으키며 이 난류에 의하여 토양간의 충돌 및 마찰이 발생하여 토양간의 점착성 및 응집성을 약화시키고 특히 회오리식 날개에 의해 유체 흐름과 마찰력을 더욱 증가시켜 흡착된 오염원의 탈착이 이루어진다. 또한 세척조 하부에 설치된 산기관에서 고압으로 분사되어진 공기방울에 의하여 유류를 부상시키고 회오리식 날개를 따라 하강하는 유체가 원형반응기 가장자리에 침전되는 것을 방지하고 지속적인 난류흐름을 발생시킨 다.Excavate the contaminated soil and screen it with a particle size of 5mm or less and inject the cleaning agent, washing water and soil in a specific ratio into a specially designed cleaning tank. The solid solution of the injected soil and water is simultaneously transferred at high speed through the solid-liquid transfer pump through the suction port and the circulation pipe installed at the bottom of the washing tank, and the high-pressure jet of the fluid is in contact with the high pressure air supplied from the end of the circulation pipe. This is followed by stirring. In addition, the injected fluid causes turbulence by the turbulence forming device installed at the center of the bottom of the washing tank, and the turbulence causes collisions and frictions between the soils, weakening the adhesion and cohesion between the soils, and in particular, the fluid flow and frictional force by the whirlwind wing. Increasingly, desorption of adsorbed pollutants occurs. It also raises oil by air bubbles sprayed at high pressure from the diffuser installed at the bottom of the washing tank, and prevents the fluid descending along the whirlwind to settle at the edge of the circular reactor and generate continuous turbulent flow.

이에 따라 본 발명에 의하여 기존의 계면활성제와 같은 세척제와 오염토양간의 교반에 의하여 물리적 처리보다는 화학적 처리에 의존하여 세척제의 유실량 및 교반정도에 따른 효율저하에 의하여 세척제가 다량으로 주입되는 단점을 보완하였으며, 또한 미세토에 강하게 흡착되어 있는 오염원은 교반에 의하여도 탈착이 쉽게 되지 않는 단점을 보완하고자 고압분사에 의한 공기방울 및 난류형성장치에 의하여 물리적인 처리를 강화함으로서 미세토에 강하게 흡착되어 있는 오염원을 더욱 용이하게 제거할 수 있는 특징이 있다.Accordingly, the present invention compensates for the drawback of a large amount of detergent being injected due to a decrease in the efficiency of the detergent and the degree of agitation, depending on the chemical treatment rather than physical treatment by agitation between the detergent and the contaminated soil, such as the conventional surfactant. In addition, the pollutants strongly adsorbed to the fine soil are not easily desorbed even by agitation, so that they are strongly adsorbed on the fine soil by enhancing physical treatment by air bubbles and turbulence forming devices by high pressure injection. There is a feature that can be removed more easily.

또한 세척조에서 공기방울에 의하여 공기탈기법(Air Stripping)의 효과에 의하여 유류가 휘발되어 발생되는 휘발성 유기화합물(VOC, Volatile Organic Carbons)을 포함한 배출 가스는 대기로의 방출을 방지하기 위하여 휘발성가스저감기로 이송되어 저감될 것이다.In addition, the exhaust gas containing volatile organic compounds (VOC, Volatile Organic Carbons) generated by the volatilization of oil due to the effect of air stripping by air bubbles in the washing tank reduces volatile gas in order to prevent emissions to the atmosphere. Will be transferred to the machine and reduced.

본 발명에 의한 토양세척장치의 구성을 이하 첨부된 도면에 의해 설명하면 다음과 같다.Referring to the accompanying drawings the structure of the soil washing apparatus according to the present invention.

본 발명 장치는 도 1의 전체구성도와 같이 오염토양, 용수 및 세척액이 투입되도록 제작된 세척조(1)와; 상기 세척조(1)의 내부에 구성되는 오염원을 탈착하는 난류형성장치(30)와; 상기 세척조(1)의 내부에 오염토양과 세척용수를 순환 시키기 위한 고액이송장치부(40)와; 상기 고액이송장치부(40)에 공기를 투입하기 위한 공기공급합류 이송장치(50)와; 그리고 세척조(1)내부의 오염토양과 세척용수의 난류를 증대시키기 위한 공기고압분사장치(60)로 구성되어 있다.
상기 세척조(1)는 원형의 몸통으로 구성되어 있으며, 세척조(1)의 내부에 오염토양과 세척용수를 투입하기 위한 투입구가 구성되어 있다.
상기 난류형성장치(30)는 순환관(4)에서 투입되는 오염토양과 세척용수를 난류 시키기 위한 구성으로 난류형성 콘(9)과 콘(9)의 외주에 나선형으로 구성되는 적어도 3개 이상 구성되는 회오리날개(7)와 콘(9)과 여러 개의 고정간(8a)으로 고정되는 원통형의 드래프트(8)로 구성되어 있다.
상기 고액이송장치부(10)는 세척조(1)의 하단에 고정되는 흡입구(2)와 세척조(1)의 상부 중앙을 관통하여 내부에 구성되는 난류형성장치(30)에 구성된 드래프트(8)의 내부로 연결되는 순환관(4) 그리고 배출관(14)으로 이루어지며 흡입구(2)와 순환관(4) 그리고 배출관(14)이 서로 연결되는 부분에 고액이송펌프(3)가 구성되고, 배출관(14)에 배출 제어밸브(15)가 구성되는 구조 이루어져 있다.
상기 공기공급합류 이송장치(50)는 순환관(4)의 내부로 공기를 투입하는 장치로서, 공기공급펌프A(5)와 공기공급펌프A(5)에서 공급되는 공기를 공급하는 공기공급관(6)으로 구성되며, 상기 공기공급관(6)의 단부는 순환관(4)과 서로 연결 구성되는 구조로 이루어져 있다.
상기 공기고압분사장치(60)는 세척조(1) 내부에 있는 오염토양과 세척용수 강하게 난류를 형성하도록 고압으로 공기를 불어 넣어주는 장치로서, 세척조(1)의 하단에 적어도 4개 이상의 분사노즐(12)을 구성하고 상기 분사노즐(12)은 원형의 공기공급관(11)에 연결되고, 상기 공기공급관(11)은 공기공급펌프B(10)에 연결되는 구조로 이루어져 있다.
이때 분사노즐(12)이 향하는 방향은 콘(9)의 중앙을 향하도록 구성되나 약간 경사지도록 구성할 수 있다.
상기와 같이 구성되는 본 발명의 작용상태를 설명하면,
세척조(1)내에 5mm이하의 선별된 오염토양을 물과 오염세척용 세척액을 넣고 공기고압분사장치(60)의 공기공급펌프B(10)를 가동시키면 공기가 공기공급관(11)을 통해 분사노즐(12)로 공기를 분사하게 된다.
이로 인해 세척조(1)의 내부에 채워져 있는 오염토양과 물 그리고 세척액(이하 내용물이라 함)이 난류를 일으키게 되면서 서로 내용물을 교반 하게 되는 것이다.
또한 고압으로 분사되는 공기에 의하여 내용물이 접촉하면서 유체상승효과를 극대화 할 수 있는 것이다.
이와 동시에 고액이송장치부(40)의 제어밸브(15)를 잠근 상태에서 고액이송펌프(3)와 난류형성장치(30)를 가동시키게 되면, 내용물은 흡입구(2)와 순환관(4)을 통해 드래프트(8)의 상측에서 분사되게 되면서 콘(9)에 의해 난류를 일으키게 되는 것이다.
이때 순환되는 내용물은 공기공급합류 이송장치(50)의 공기공급펌프A(5)에서 발생 되는 공기가 순환관(4)으로 공기를 공급하게 되면 공급되는 내용물 상에 공기층이 형성되게 되어 마찰력과 난류성을 우수하게 할 수 있는 것이다.
이와 같은 상태를 반복하게 되면, 토양 간의 충돌로 인해 마찰력이 증가 되어 유류를 탈착시키게 되며 수중에 용존되어 있는 휘발성 유류를 휘발시키게 되어 유류를 부상시키게 되는 것이다.
특히 하부에서 분사노즐을 통해 분사되는 공기압에 의해 토양의 침강 및 침전을 방지하게 되어 오염토양이 골고루 세척이 이루어지게 되는 것이다.
이후 본 발명은 휘발성가스의 경우는 휘발성가스저감기를 사용하여 저감시킨 후 대기로 배출하고, 세척된 내용물은 제어밸브를 열게 되면 배출관을 통해 외부로 배출할 수 있는 것이다.
The apparatus of the present invention and the washing tank 1 is made so that the contaminated soil, water and the washing liquid as shown in the overall configuration of Figure 1; Turbulence forming device 30 for desorbing the contaminant formed in the washing tank (1); Solid-liquid transfer unit 40 for circulating the contaminated soil and washing water in the washing tank (1); An air supply confluence transporting device 50 for introducing air into the solid-liquid transporting unit 40; And it is composed of an air high-pressure spraying device 60 for increasing the turbulence of the contaminated soil and washing water in the washing tank (1).
The washing tank (1) is composed of a circular body, the inlet for introducing contaminated soil and washing water in the washing tank (1) is configured.
The turbulence forming apparatus 30 is configured to turbulent the contaminated soil and washing water introduced from the circulation pipe 4 and constitutes at least three or more spirally formed on the outer circumference of the turbulence forming cone 9 and the cone 9. It consists of a cylindrical draft (8) which is fixed by a whirlwind blade (7) and a cone (9) and several fixing rods (8a).
The solid-liquid transfer device unit 10 of the draft (8) configured in the turbulence forming device 30 is formed through the suction port 2 and the upper center of the washing tank 1 is fixed to the lower end of the washing tank (1) It consists of a circulation pipe (4) and the discharge pipe (14) connected to the inside, and the solid-liquid transfer pump (3) is configured at a portion where the inlet (2), the circulation pipe (4) and the discharge pipe (14) are connected to each other, the discharge pipe ( 14) is composed of a structure in which the discharge control valve (15) is configured.
The air supply confluence transfer device 50 is a device for introducing air into the circulation pipe 4, the air supply pipe for supplying air supplied from the air supply pump A (5) and the air supply pump (A) ( 6), the end of the air supply pipe (6) is made of a structure that is configured to be connected to the circulation pipe (4).
The high-pressure air injection device 60 is a device for blowing air at high pressure to form a strong turbulent turbulent soil and washing water in the washing tank (1), at least four or more injection nozzles at the bottom of the washing tank ( 12) and the injection nozzle 12 is connected to the circular air supply pipe 11, the air supply pipe 11 is made of a structure connected to the air supply pump B (10).
At this time, the direction that the injection nozzle 12 is configured to face the center of the cone (9) but may be configured to be slightly inclined.
Referring to the working state of the present invention configured as described above,
Water and the cleaning solution for washing the contaminated soil of 5 mm or less in the washing tank 1 are operated, and the air supply pump B 10 of the high-pressure spray device 60 is operated to spray air through the air supply pipe 11. Air is injected into (12).
This causes the contaminated soil and water and the washing liquid (hereinafter referred to as contents) filled in the inside of the washing tank (1) to cause turbulence and to agitate the contents.
In addition, the contents are contacted by the air injected at a high pressure to maximize the fluid rise effect.
At the same time, when the solid-liquid transfer pump 3 and the turbulence-forming apparatus 30 are operated while the control valve 15 of the solid-liquid transfer unit 40 is locked, the contents are connected to the inlet 2 and the circulation pipe 4. Will be injected from the upper side of the draft (8) through the turbulence is caused by the cone (9).
At this time, the circulated contents are formed when the air generated from the air supply pump A (5) of the air supply confluence transporting device (50) supplies air to the circulation pipe (4), so that an air layer is formed on the supplied contents, and thus frictional and turbulent properties It can be excellent.
When this condition is repeated, friction forces increase due to the collision between soils, thereby desorbing oil, and volatilizing volatile oils dissolved in water, thereby causing the oil to float.
In particular, it is possible to prevent the sedimentation and sedimentation of the soil by the air pressure sprayed through the injection nozzle in the lower portion is to evenly wash the contaminated soil.
Since the present invention is to reduce the volatile gas using a volatile gas reducer to discharge to the atmosphere, the washed contents can be discharged to the outside through the discharge pipe when the control valve is opened.

삭제delete

삭제delete

삭제delete

삭제delete

이상에서 설명한 바와 같이 본 발명은 유류로 오염된 토양을 오염토량에 관계없이 용량을 자율적으로 조절하여 제작할 수 있으며, 고정식 및 이동식으로 제작하여 현장 여건에 맞게 설치할 수 있다. 또한 기존 토양세척장치는 오염농도를 세척전에 미리 산정하여 세척액을 주입하여야하므로 적정한 세척액을 주입하지 못하여 세척효율이 낮아지거나, 너무 많은 양을 투입하여 비경제적으로 토양세척작업을 수행하는 단점이 있었다. 그러나 본 장비는 적정한 세척액 주입에 반하여 고액이송 및 고압분사에 의한 공기방울 및 난류형성에 의하여 물리적 처리를 동시에 하기 때문에 저비용으로 고효율의 토양세척작업을 수행할 수 있는 장점이 있다.As described above, the present invention can be produced by adjusting the capacity of the soil contaminated with oil irrespective of the contaminated soil, and can be installed according to the site conditions by fixed and mobile production. In addition, the existing soil washing apparatus has a disadvantage in that the washing efficiency is lowered by injecting the washing solution by calculating the pollution concentration before washing, and the washing efficiency is lowered due to the inability to insert the washing solution, or the soil washing operation is performed in an uneconomic manner. However, this equipment has the advantage of performing high-efficiency soil cleaning at low cost because it simultaneously performs physical treatment by air droplets and turbulence formation due to high liquid feed and high pressure injection, as opposed to proper washing liquid injection.

기존 토양세척장치는 과다한 세척액 주입 및 수중에 용존되어 있는 유류성분에 의하여 세척작업이 종료된 후 세척용수를 별도의 폐수처리시설로 처리를 해야하는 단점이 있으나, 본 발명은 고압분사에 의한 공기방울에 의하여 용존되어 있는 휘발성 유류를 휘발시키고 수중의 유류를 부상시킴으로, 부상된 유류만 제거함으로 서 세척용수를 별도로 폐수처리 할 필요가 없거나 재활용하여 사용할 수 있는 장점이 있다.Existing soil washing apparatus has the disadvantage that the washing water must be treated as a separate wastewater treatment facility after the washing operation is completed by the excessive injection of the washing liquid and dissolved oil components in the water, but the present invention is directed to air bubbles by high pressure spraying. By volatilizing the dissolved volatile oil and floating the oil in the water, there is an advantage that can be used to recycle the waste water does not need to separate the waste water treatment by removing only the injured oil.

또한 고액이송펌프에 의한 오염토양과 세척용수의 동시 이송에 의한 교반작업 및 수중으로의 고압분사 되어 난류형성장치에 의하여 발생한 난류에 의하여 토양간의 충돌 및 마찰에 의하여 토양에 강하게 흡착되어 있는 유류를 탈착시킴에 따라 세척액에 의한 정화효율의 한계를 극복하여 물리적인 처리효율을 향상시켜 전체 정화효율을 향상시킬 수 있는 장점이 있다.In addition, desorption of oils strongly adsorbed to soil by collision and friction between soils by turbulence generated by turbulence forming device due to stirring operation by simultaneous transfer of contaminated soil and washing water by solid-liquid transfer pump and high pressure injection into water By overcoming the limitation of the purification efficiency by the cleaning solution, there is an advantage that can improve the overall purification efficiency by improving the physical treatment efficiency.

Claims (4)

외주에 나선형으로 구성되는 회오리날개가 구성된 난류형성콘과 여러 개의 고정간으로 고정되는 원통형의 드래프트로 구성되는 난류성형장치가 내장된 세척조와;A washing tank having a turbulent forming device composed of a turbulent forming cone having a spiral whirlwind formed in a circumference and a cylindrical draft fixed between a plurality of fixed parts; 드래프트의 내부로 연결되는 순환관과 세척조와 연결되는 흡입구 그리고 세척조의 내용물을 배출하기 위한 배출관이 서로 연결되는 부분에 고액이송펌프가 구성되고, 상기 배출관에 배출 제어밸브가 구성되는 고액이송장치부;A solid-liquid transfer pump configured at a portion where a circulation pipe connected to the inside of the draft, a suction port connected to the washing tank, and a discharge pipe for discharging the contents of the washing tank are connected to each other, and a discharge control valve is configured at the discharge pipe; 공기공급펌프A와 공기공프펌프A에서 공급되는 공기를 공급하는 공기공급관으로 구성되며, 상기 공기공급관의 단부는 순환관과 서로 연결 구성되는 공기공급합류 이송장치와;An air supply pipe for supplying air supplied from the air supply pump A and the air ball pump A, and an end of the air supply pipe includes an air supply confluence transfer device configured to be connected to the circulation pipe; 세척조의 하단에 분사노즐을 구성하고, 상기 분사노즐은 원형의 공기공급관에 연결되고, 상기 공기공급관은 공기공급펌프B에 연결되는 구조로 구성된 공기고압분사장치로 구성된 것을 특징으로 하는 고압분사된 공기방울 및 난류를 이용한 토양세척장치The injection nozzle is configured at the bottom of the washing tank, and the injection nozzle is connected to a circular air supply pipe, and the air supply pipe is composed of an air high pressure injection device configured to be connected to an air supply pump B. Soil cleaning system using drops and turbulence 삭제delete 삭제delete 삭제delete
KR1020060120364A 2006-12-01 2006-12-01 Soil washing machine by high pressured air-lifting and turbulence KR100828545B1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
KR1020060120364A KR100828545B1 (en) 2006-12-01 2006-12-01 Soil washing machine by high pressured air-lifting and turbulence

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
KR1020060120364A KR100828545B1 (en) 2006-12-01 2006-12-01 Soil washing machine by high pressured air-lifting and turbulence

Publications (1)

Publication Number Publication Date
KR100828545B1 true KR100828545B1 (en) 2008-05-13

Family

ID=39650083

Family Applications (1)

Application Number Title Priority Date Filing Date
KR1020060120364A KR100828545B1 (en) 2006-12-01 2006-12-01 Soil washing machine by high pressured air-lifting and turbulence

Country Status (1)

Country Link
KR (1) KR100828545B1 (en)

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100906130B1 (en) * 2009-03-12 2009-07-07 주식회사케이에스티 Pollutants in the soil washing device
KR100950696B1 (en) * 2009-07-30 2010-03-31 주식회사케이에스티 Pollutants in the soil washing device
KR100976166B1 (en) * 2009-07-02 2010-08-16 신강하이텍(주) Polluted soil cultivation apparatus with steam jetting tube
CN102059247A (en) * 2010-11-29 2011-05-18 中国科学院地理科学与资源研究所 Vehicle-mounted repairing equipment and method for polluted site soil and underground water body
KR101049239B1 (en) 2011-03-31 2011-07-14 코오롱건설주식회사 Apparatus for Separating Contaminant from Contaminated Soil and Purifying Contaminated Soil
KR101092200B1 (en) 2009-05-15 2011-12-09 코오롱건설주식회사 Apparatus for Separating Contaminant from Contaminated Soil and Purifying Contaminated Soil
KR101148186B1 (en) * 2011-12-08 2012-05-24 제이에이치그린 주식회사 Soil washing apparatus using air jet
KR101322190B1 (en) 2013-06-21 2013-10-28 에이치플러스에코 주식회사 Continuous collection processing device for fine conteninants
KR101461214B1 (en) * 2014-04-29 2014-11-18 지우이앤이(주) System and Method for Purifying Contaminated Soil
KR101645426B1 (en) * 2015-09-09 2016-08-04 현대건설주식회사 System and method for remediation of dredged soil or sediment
CN109158416A (en) * 2018-09-25 2019-01-08 北京石油化工学院 A kind of soil cleaning method based on airlift internal-loop reactor
WO2019194804A1 (en) * 2018-04-04 2019-10-10 Somerset Environmental Solutions Inc. Apparatus and method for aerating wastewater
CN110369491A (en) * 2019-08-26 2019-10-25 何条红 A kind of formula soil remediation device
CN110404953A (en) * 2019-08-09 2019-11-05 周成宗 A kind of soil remediation method

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10229781A (en) 1997-02-19 1998-09-02 Kurosawa Micro Keisoku:Kk Method and device for deffusing air into water
JP2002177942A (en) 2000-12-14 2002-06-25 Kumagai Gumi Co Ltd Method of cleaning soil and flotation separator
KR200307201Y1 (en) 2002-12-11 2003-03-12 구흥회 The apparatus of activated native - microbe

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10229781A (en) 1997-02-19 1998-09-02 Kurosawa Micro Keisoku:Kk Method and device for deffusing air into water
JP2002177942A (en) 2000-12-14 2002-06-25 Kumagai Gumi Co Ltd Method of cleaning soil and flotation separator
KR200307201Y1 (en) 2002-12-11 2003-03-12 구흥회 The apparatus of activated native - microbe

Cited By (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100906130B1 (en) * 2009-03-12 2009-07-07 주식회사케이에스티 Pollutants in the soil washing device
KR101092200B1 (en) 2009-05-15 2011-12-09 코오롱건설주식회사 Apparatus for Separating Contaminant from Contaminated Soil and Purifying Contaminated Soil
KR100976166B1 (en) * 2009-07-02 2010-08-16 신강하이텍(주) Polluted soil cultivation apparatus with steam jetting tube
KR100950696B1 (en) * 2009-07-30 2010-03-31 주식회사케이에스티 Pollutants in the soil washing device
CN102059247A (en) * 2010-11-29 2011-05-18 中国科学院地理科学与资源研究所 Vehicle-mounted repairing equipment and method for polluted site soil and underground water body
KR101049239B1 (en) 2011-03-31 2011-07-14 코오롱건설주식회사 Apparatus for Separating Contaminant from Contaminated Soil and Purifying Contaminated Soil
KR101148186B1 (en) * 2011-12-08 2012-05-24 제이에이치그린 주식회사 Soil washing apparatus using air jet
KR101322190B1 (en) 2013-06-21 2013-10-28 에이치플러스에코 주식회사 Continuous collection processing device for fine conteninants
KR101461214B1 (en) * 2014-04-29 2014-11-18 지우이앤이(주) System and Method for Purifying Contaminated Soil
KR101645426B1 (en) * 2015-09-09 2016-08-04 현대건설주식회사 System and method for remediation of dredged soil or sediment
WO2019194804A1 (en) * 2018-04-04 2019-10-10 Somerset Environmental Solutions Inc. Apparatus and method for aerating wastewater
US11155482B2 (en) 2018-04-04 2021-10-26 Somerset Environmental Solutions Inc. Apparatus and method for aerating wastewater
CN109158416A (en) * 2018-09-25 2019-01-08 北京石油化工学院 A kind of soil cleaning method based on airlift internal-loop reactor
CN110404953A (en) * 2019-08-09 2019-11-05 周成宗 A kind of soil remediation method
CN110369491A (en) * 2019-08-26 2019-10-25 何条红 A kind of formula soil remediation device
CN110369491B (en) * 2019-08-26 2022-02-08 青岛市环境保护科学研究院 Pile type soil repairing device

Similar Documents

Publication Publication Date Title
KR100828545B1 (en) Soil washing machine by high pressured air-lifting and turbulence
KR100633111B1 (en) Soil washing device
CN113399448B (en) Remediation device for organic contaminated soil
CN102583712A (en) Method and system by using micro-nano bubbles to perform reinforcement in-situ remediation on polluted ground water
CN208883659U (en) A kind of combined soil ground water circulation processing unit
KR101955112B1 (en) Method for Field soil stabilization and remediation of polluted soil by Extraction / filling method using PMI-system
JP2007253059A (en) In situ cleaning method of oil-contaminated soil
KR101768006B1 (en) Soil Treatment System Using Nanobubble and Multi-Stage Washing of Inorganic Acid
KR20030087915A (en) Method for purifying a layer of contaminated soil and apparatus
KR100950696B1 (en) Pollutants in the soil washing device
KR101691425B1 (en) Complex Purification System of Oil-polluted Underground Water by Physical and Chemical
KR101691424B1 (en) Complex Purification System of Oil-polluted Underground Water by Physical and Biological
JP5430056B2 (en) Treatment method of contaminated soil
CN104475442B (en) Volatile contaminant soil and groundwater remediation system
KR101205123B1 (en) Semi-batch Apparatus for remediation of Contaminated soils using surfactant foam
KR100477765B1 (en) Double-structural well for remediation of contaminated soil and groundwater
JP2003145126A (en) Method for washing contaminated soil
US5957665A (en) Jet system total fluids recovery system
JPH10258266A (en) Method for repairing original position of polluted ground and pollutant treatment apparatus
KR100982809B1 (en) Apparatus and method for purifying polluted soil using direct ground boring-injecting
CN114751472A (en) Underground water circulating well device for in-situ remediation of contaminated site and remediation method
JP4421417B2 (en) Purification equipment for contaminated soil
KR100988043B1 (en) Sludge separating appratus of contaminated soil loaded in the vehicle
JP2019089049A (en) Contaminated soil purification system
JP5183538B2 (en) Surplus sludge reduction device

Legal Events

Date Code Title Description
A201 Request for examination
E902 Notification of reason for refusal
E701 Decision to grant or registration of patent right
GRNT Written decision to grant
FPAY Annual fee payment

Payment date: 20130502

Year of fee payment: 6

FPAY Annual fee payment

Payment date: 20140502

Year of fee payment: 7

FPAY Annual fee payment

Payment date: 20150501

Year of fee payment: 8

FPAY Annual fee payment

Payment date: 20160502

Year of fee payment: 9

FPAY Annual fee payment

Payment date: 20180502

Year of fee payment: 11

FPAY Annual fee payment

Payment date: 20190806

Year of fee payment: 12