KR20050083048A - Apparatus for control of supply of water with acidity - Google Patents

Apparatus for control of supply of water with acidity Download PDF

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KR20050083048A
KR20050083048A KR1020050069727A KR20050069727A KR20050083048A KR 20050083048 A KR20050083048 A KR 20050083048A KR 1020050069727 A KR1020050069727 A KR 1020050069727A KR 20050069727 A KR20050069727 A KR 20050069727A KR 20050083048 A KR20050083048 A KR 20050083048A
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drainage
storage tank
discharged
acid
acidic
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KR100522326B1 (en
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정원식
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한국건설기술연구원
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/40Devices for separating or removing fatty or oily substances or similar floating material
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • C02F1/62Heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/14Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
    • C02F11/143Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using inorganic substances
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/02Non-contaminated water, e.g. for industrial water supply
    • C02F2103/04Non-contaminated water, e.g. for industrial water supply for obtaining ultra-pure water
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/10Nature of the water, waste water, sewage or sludge to be treated from quarries or from mining activities

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  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

본 발명은 산악지형을 통과하는 터널 공사후 갱내에서 유출되는 산성배수를 소택지의 조성과 적니파우더를 이용하여 산성배수에 포함된 중금속을 제거함으로써 기존의 환경과 주변 생태계에 영향을 주지 않으면서 소정 수질기준 이상을 만족시킬 수 있는 산성배수의 처리장치에 관한 것이다.The present invention removes the heavy metals contained in the acid drainage by using the composition of the wetlands and the red mud powder by acidic drainage discharged from the pit after the tunnel construction passing through the mountainous terrain, without affecting the existing environment and the surrounding ecosystem. The present invention relates to an acid drainage treatment apparatus capable of satisfying more than a standard.

본 발명은, 산악지형의 고속도로 공사시, 갱내에서 유출되는 유출수에 포함된 슬러지를 침강시켜 제거하는 라임스톤 드레인; 상기 라임스톤 드레인에서 배출된 처리수를 저류하되, 우기시나 수리지질학적인 현장여건(대수층)등으로 인하여 다량의 갱내 지하수가 유출될 경우를 감안하여 일정량이 유입되면 방류하는 저류조; 및 상기 저류조에서 방류된 방류수에 적니파우더를 혼화시켜 산성배수에 포함된중금속 농도를 음용수 수질기준의 수준으로 처리하는 반응조를 포함하는 산성배수 처리장치를 제공한다.The present invention, limestone drain to remove the sediment contained in the runoff flowing out of the pit during mountainous highway construction; A storage tank for storing the treated water discharged from the limestone drain, but discharged when a predetermined amount is introduced in consideration of the case where a large amount of groundwater flows out due to rainy season or hydrogeological site conditions (aquifer); And a reaction tank for mixing the red mud powder with the discharge water discharged from the storage tank to treat the heavy metal concentration included in the acid drainage at the level of the drinking water quality standard.

Description

산성배수 처리장치{Apparatus for Control of Supply of Water with acidity}Apparatus for Control of Supply of Water with acidity

본 발명은 산악지형을 통과하는 도로 공사시, 갱내에서 유출되는 유출수에 포함된 산성배수를 처리하는 장치에 관한 것이다.The present invention relates to an apparatus for treating acidic drainage contained in effluent flowing out of a gang during road construction passing through mountainous terrain.

우리나라의 산악지형에는 여러가지 유해성 중금속을 함유한 암석이 많이 분포되어 있는데, 이러한 지질층을 갖는 산악지형을 통과하는 도로 공사시에는, 산성배수의 악영향에 대비하여 충분한 처리방안이 요구되고 있다.The mountainous terrain of Korea has a lot of rocks containing various harmful heavy metals, the road construction through the mountainous terrain having such a geological layer, a sufficient treatment for the adverse effects of acidic drainage is required.

특히, 지면 또는 터널 굴착에 따른 절개사면과 사토장에서 발생되는 중금속을 함유하고 있는 암버럭중, 황을 포함한 광물질의 경우 지하수나 빗물속에 용해되어 있는 용존산소와 반응하여 황산으로 변하고, 상기 황산은 광물에 포함된 각종 중금속을 용해시켜 강산성수를 생성하고, 이 강산성수는 강우에 의해 절개사면을 따라 하천으로 흘러들어감으로써 수생 생태계에 많은 악영향을 야기시킬 뿐만 아니라, 인근주민의 생활을 위협하고 있어 강산성 배수의 적절한 처리대책이 요구되고 있다. 따라서, 고속도로 시공업자는 터널굴착에서 발생되는 암버럭과 지하수와의 접촉을 원천적으로 차단하고, 터널에서 발생되는 지하수는 이미 강한 산성수로 특성이 변화된 상태에서 터널 외부로 유출되므로 하천으로 유입되기 전에 적절한 처리를 하여야 한다.Particularly, in the case of the rock containing heavy metals generated in the cut slope and the ground due to the excavation of the ground or tunnel, minerals including sulfur react with dissolved oxygen dissolved in groundwater or rainwater, and the sulfuric acid is mineralized. Strong acidic water is dissolved by dissolving various heavy metals contained in it, and this strong acidic water flows into rivers along the incline due to rainfall, causing not only bad effects on aquatic ecosystems, but also threatening the lives of nearby residents. Appropriate treatment measures are required. Therefore, the highway contractor basically blocks the contact between the rock block and the groundwater generated in the tunnel excavation, and the groundwater generated in the tunnel is discharged to the outside of the tunnel with the strong acidic water. It must be processed.

일반적으로, 광산 산성배수(AMD : acid mine drainage)는 pH가 6.0이하이고, 총산도(total acidity)가 총알칼리도(total alkalinity)를 초과하는 물로서 노천광이 가행되었던 지역, 가행중이거나 휴광 또는 폐광된 광산에서 유출되는 것으로 정의될 수 있으며, 또한 도로사면 절개부 및 터널 굴착시 노출된 지층, 도심지 지하철 터널에서 황철석(pyrite) 또는 백철석(marcasite)을 함유하는 지층이 공기중에 노출되면 산성수가 침출되어 나온다. In general, acid mine drainage (AMD) is water with a pH of 6.0 or less and total acidity above total alkalinity, in areas where open pits have been performed, running or It can be defined as an outflow from an abandoned mine, and acidic water leaches if exposed to air in the formation of road slope cuts and tunnel excavations, or in the underground subway tunnels containing pyrite or marcasite. Comes out.

이러한 산성배수를 처리하는 방법으로는 알칼리제를 이용하여 수중의 산도를 중화하고 중화된 산성 침출수에 응집제를 주입함으로써 유해 중금속의 침전효과를 극대화하는 물리화학적 방법과, 자연에서 일어나는 화학적 및 생물학적 반응을 이용하여 자연정화하며 현재 국내의 광산배수에 수 개소 도입하여 운영하고 있는 생물학적 방법으로 크게 나눌 수 있다.The treatment of acidic drainage uses physicochemical methods to maximize the precipitation effect of harmful heavy metals by neutralizing the acidity in water with alkaline agents and injecting flocculant into neutralized acidic leachate, and chemical and biological reactions occurring in nature. It can be largely divided into biological methods that are naturally purified and currently introduced and operated in several places in Korea.

전자의 물리화학적 처리방법은, 일반적인 산성폐수 처리방법과 같이 화학약품(예를 들면, 산 중화제)과 기계력을 사용하여 배수를 정화하는 기술로서, 집수조, 혼합조, 응집조, 침강조, 그리고 여과조 등의 처리공정으로 구성되며, 응집/침전법, 라임스톤 배수(Limestone Drains)법, 그라우팅 등이 있다.The former method of physicochemical treatment is a technology to purify wastewater by using chemicals (for example, acid neutralizers) and mechanical power as in general acid wastewater treatment methods. It is composed of treatment processes such as agglomeration / sedimentation method, limestone drainage method, grouting, and the like.

이러한 처리방법은 시설 운영비 및 화공 약품비, 그리고 인건비 등을 지속적으로 필요로 하는 문제점이 있다.This treatment method has a problem that requires a constant operating costs, chemicals, and labor costs.

상기 물리화학적 처리방법 중 응집/침전법은 첫번째 단계로서 수중의 입자들을 화학처리하여 점착성을 갖거나 불안정하게 하고, 두번째 단계로서 불안정하게 된 입자들을 서로 접촉시켜 응집물을 형성시키되 이 응집물을 침전이나 여과에 의해 제거함으로써, 지속적인 운전이 필요하고 그에 수반하는 경비가 많이 소요되는 문제점이 있다.In the physicochemical treatment method, agglomeration / precipitation method is chemical treatment of particles in water as a first step, and becomes cohesive or unstable, and in the second step, particles which become unstable are brought into contact with each other to form agglomerates. By eliminating by, there is a problem that the continuous operation is required and the accompanying costs are high.

다음으로, 상기 라임스톤 배수(Limestone Drains)법은 석회석과 산성광산배수를 접촉시켜서 산성배수를 알칼리수로 변환시키는 방법으로서, 운영비가 저렴하여 대규모 산성배수를 배출하는 곳에 많이 이용되고 있으나 처리 효율이 낮은 문제점이 있다.Next, the Limestone Drains method is a method of converting acidic wastewater into alkaline water by contacting limestone with acidic mine drainage. There is a problem.

상기 그라우팅은 지하수 유출 지점으로부터 유출되는 배수 자체를 원천적으로 봉쇄하고자 하는 방법으로, 정화개념 보다는 배수량을 줄이는데 그 목적이 있는 것이며, 이는 그라우팅을 통한 산성 배수 밀폐 시 암반 내의 특성 분석이 선행되어야 하며 다른 지층으로 누수가 되지 않도록 정밀한 지반조사와 함께 적정 그라우팅 재료 선정과 아울러 철저한 시공이 필요하다.The grouting is a method to fundamentally block the drainage discharged from the groundwater outflow point, and the purpose is to reduce the drainage rather than the concept of purification, which must be preceded by the characterization in the rock when the acidic drainage through the grouting is closed. In order to prevent water leakage, it is necessary to precisely investigate the ground, select the appropriate grouting material, and thoroughly construct it.

한편, 생물학적 방법에는 SAPS(Successive Alkalinity Producing System), 소택지법, 그리고 배수법 등이 있다.Biological methods include the Successive Alkalinity Producing System (SAPS), the marsh land method, and the drainage method.

먼저, SAPS를 이용한 처리법은 광산배수의 산도가 높고, 3가 철의 농도가 높아서 ALD(Anoxic Limestone Drains)나 Alkalinity를 공급하는 기존의 처리 시스템으로 광산배수를 처리하기 어려울 때 사용된다. First, the treatment method using SAPS is used when it is difficult to treat mine drainage with an existing treatment system that supplies ALD (Anoxic Limestone Drains) or Alkalinity due to high acidity of mine drainage and high concentration of trivalent iron.

다음으로, 소택지법은 미생물의 생화학적 작용에 의해서 산성 배수를 정화하는 자연정화식 처리기술로서 인위적으로 소택지(늪지)를 조성하여 소택지 내부의 생화학적 반응을 통해서 광산배수를 정화한다. 소택지법은 물리화학적 방법에 비해서 정화효율의 조절이 어렵고 운영상 계절적인 요소에 제약을 받는다. 그러나, 물리화학적 폐수처리는 운영비 및 관리비가 지속적으로 소요되지만 자연정화식은 최소 유지비용이 소요되므로 현재 폐광지역에서 활용되고 있다.Next, the marsh land method is a natural purification treatment technology for purifying acidic drainage by the biochemical action of microorganisms to artificially form marshes (bogs) to purify the mine drainage through biochemical reactions inside the marsh land. Compared with the physicochemical method, the marsh land method is difficult to control the purification efficiency and is limited by seasonal factors in operation. However, physicochemical wastewater treatment is continuously used in the waste mine area because operating and maintenance costs are continuously required, but natural purification formula requires minimum maintenance costs.

다음으로, 배수법은 일종의 자연정화식으로 갱도 또는 광산배수 유로에 정화물질, 즉 석회석 등으로 배수층을 설치하여 광산배수를 흐르게 하면서 중화 또는 오염물질을 제거하는 방법이다. 배수법은 저렴하면서도 시공이 간단하나 시간이 경과되면서 철산화물 등에 의한 배수층 피복 때문에 정화효율이 떨어지는 문제점이 있다.Next, the drainage method is a kind of natural purification method that removes neutralization or contaminants while installing a drainage layer with a purification material, that is, limestone, in a tunnel or a mine drainage passage. Although the drainage method is inexpensive and simple in construction, there is a problem in that the purification efficiency is lowered due to the drainage layer coating with iron oxide or the like over time.

따라서, 본 발명은 상기한 제반 문제점을 해결하기 위하여 제안된 것으로, 산악지형을 통과하는 터널 공사후 갱내에서 유출되는 산성배수를 소택지의 조성과 적니파우더를 이용하여 산성배수에 포함된 중금속을 제거함으로써 기존의 환경과 주변 생태계에 영향을 주지 않으면서 소정 수질기준 이상을 만족시킬 수 있는 산성배수의 처리장치를 제공하는데 그 목적이 있다.Therefore, the present invention has been proposed to solve the above problems, by removing the heavy metal contained in the acid drainage using the composition of the marsh and red mud powder to acid drainage discharged from the pit after the tunnel construction passing through the mountain terrain. Its purpose is to provide a treatment system for acidic wastewater that can satisfy a predetermined water quality standard without affecting the existing environment and surrounding ecosystem.

상기 목적을 달성하기 위한 본 발명은, 산악지형의 고속도로 공사시, 갱내에서 유출되는 유출수에 포함된 슬러지를 침강시켜 제거하는 라임스톤 드레인; 상기 라임스톤 드레인에서 배출된 처리수를 저류하되, 우기시나 수리지질학적인 현장여건(대수층)등으로 인하여 다량의 갱내 지하수가 유출될 경우를 감안하여 일정량이 유입되면 방류하는 저류조; 및 상기 저류조에서 방류된 방류수에 적니파우더를 혼화시켜 산성배수를 음용수 수질기준으로 처리하는 반응조를 포함하는 산성배수 처리장치를 제공한다.The present invention for achieving the above object is, limestone drain to settle and remove the sludge contained in the outflow water flowing out of the gangway during mountainous highway construction; A storage tank for storing the treated water discharged from the limestone drain, but discharged when a predetermined amount is introduced in consideration of the case where a large amount of groundwater flows out due to rainy season or hydrogeological site conditions (aquifer); And a reaction tank for mixing the red mud powder with the discharged water discharged from the storage tank to treat the acidic drainage on the basis of drinking water quality standards.

상술한 목적, 특징들 및 장점은 첨부된 도면과 관련한 다음의 상세한 설명을 통하여 보다 분명해 질 것이다. The above objects, features and advantages will become more apparent from the following detailed description taken in conjunction with the accompanying drawings.

이하, 첨부된 도면을 참조하여 본 발명에 따른 바람직한 일실시예를 상세히 설명한다.Hereinafter, exemplary embodiments of the present invention will be described in detail with reference to the accompanying drawings.

도1 은 본 발명에 따른 산성배수 처리장치에 대한 일실시예 구성도로서, 적니(Red Mud)를 이용한 산성배수 처리장치를 나타낸다.1 is a configuration diagram of an acid drainage treatment apparatus according to an embodiment of the present invention, and shows an acid drainage treatment apparatus using red mud.

도면에 도시된 바와 같이, 본 실시예는 현장에 갱내 지하수 유출량을 바탕으로 적당한 크기의 소택지를 조성하고, 여기에 산성배수를 저류한 후, 상기 적니 파우더(Red Mud Powder)를 단순 살포처리하는 방법으로서 산을 중화시키고 중금속 원소들은 상기 중금속 제거 물질에 흡착된 후 해리되지 못하도록 하는 중성화/안정화/고형화 기술이다.As shown in the figure, this embodiment is a method of forming a marsh land of a suitable size based on the groundwater outflow amount in the gang, storage acidic drainage therein, and then simply spraying the red mud powder Is a neutralization / stabilization / solidification technique that neutralizes acid and prevents heavy metal elements from adsorbing after they are adsorbed to the heavy metal removal material.

상기한 본 발명에 따른 적니 기술을 이용한 산성배수 처리장치는, 산악지형의 도로 공사시, 갱내에서 유출되는 유출수에 포함된 슬러지를 침강시켜 제거하는 라임스톤 드레인(210)과; 상기 라임스톤 드레인(210)에서 배출된 처리수를 저류하되, 우기시나 수리지질학적인 현장여건(대수층)등으로 인하여 다량의 갱내 지하수가 유출될 경우를 감안하여 일정량이 유입되면 방류하는 저류조(220)와; 상기 저류조(220)에서 방류된 방류수에 적니파우더를 혼화시켜 중금속을 제거함으로써 중금속 농도를 음용수 수질기준의 수준으로 처리하는 반응조(230)를 포함한다.The acid drainage treatment apparatus using the red mud technique according to the present invention, the limestone drain 210 for sedimentation and removal of sludge contained in the outflow water flowing out of the gang during the construction of the mountain terrain; The treated water discharged from the limestone drain 210 is stored, but a storage tank 220 is discharged when a predetermined amount is introduced in consideration of a large amount of groundwater flowing out due to the rainy season or hydrogeological site conditions (aquifer). Wow; It includes a reaction tank 230 to mix the red mud powder in the discharge water discharged from the storage tank 220 to remove the heavy metals to treat the heavy metal concentration to the level of drinking water quality standards.

상기 각각의 구성에 의한 산성배수처리공정을 좀더 상세히 설명하면 다음과 같다.Hereinafter, the acidic wastewater treatment process by each configuration will be described in detail.

상기 라임스톤 드레인(210)은 산성광산배수를 석회석에 접촉시켜 pH를 중화시킴으로써 상기 산성배수를 알칼리수로 변환시키며, 침강성이 좋은 일부 부유물질(탁질)을 제거하는 전처리 공정을 수행한다. 상기 저류조(220)는 산성배수의 저류과정에서 고탁질의 부유물질 및 상기 부유물질에 부착된 중금속을 침전제거하는 공정을 수행한다. 상기 반응조(230)는 적니파우더로 채워져 있어 응집/침전공정 후 탁질이 거의 없이 증금속이 함유된 유입수를 통과시켜 중금속을 제거하게 된다. The limestone drain 210 converts the acid drainage into alkaline water by neutralizing the pH by contacting the acid mine drainage with limestone and performing a pretreatment step of removing some suspended solids (suspension) having good settling properties. The storage tank 220 performs a process of sedimenting and removing the suspended solids and heavy metals attached to the suspended substances in the storage of the acidic drainage. The reactor 230 is filled with red mud powder to remove heavy metals by passing the influent containing the thick metal with little turbidity after the flocculation / precipitation process.

여기서, 상기 적니 파우더에 대하여 좀더 상세히 설명하면, 상기 적니파우더는 보오크사이트 원광석으로 수산화 알루미늄 또는 알루미나를 생산하는 과정에서 발생하는 부산물로서 산성배수의 중화 및 중금속 안정화에 이용되고 있다. 상기 적니는 높은 알칼리도를 가지고 있어 산을 중화시키고 독성의 중금속 원소들을 흡착하여 해리되지 않도록 하는 응집제 역활을 한다. 통상적인 상기 적니의 산중화능은 3.5 ∼ 7.5moles of acid/kg이며, 다양하게 전하된 입자들은 부가적인 수소이온을 결합할 수 있고, 공극수의 산도가 5이하로 존재하면 14 ∼ 20moles/kg 정도로 산을 중화시킬 수 있다.Herein, the red mud powder will be described in more detail. The red mud powder is a by-product generated in the process of producing aluminum hydroxide or alumina as bauxite ore and is used for neutralizing acid drainage and stabilizing heavy metals. The red mud has a high alkalinity and acts as a flocculant to neutralize acids and adsorb toxic heavy metal elements so that they do not dissociate. Typically, the acid neutralization capacity of the red mud is 3.5 to 7.5 moles of acid / kg, and variously charged particles may bind additional hydrogen ions, and if the acidity of the pore water is less than 5, about 14 to 20 moles / kg. Acid can be neutralized.

상기 반응조(230)에서의 중금속 처리과정은 적니파우더가 가지고 있는 고유의 알칼리도에 의하여 산성을 중화시키고, 독성의 중금속 원소들을 흡착하여 해리되지 못하도록 응집하는 것이다. 이에 따라 상기 반응조(230)를 거친 산성배수에 함유된 중금속농도가 음용수 수질기준의 수준으로 처리될 수 있는 것이다. Heavy metal treatment in the reactor 230 is to neutralize the acid by the intrinsic alkalinity of the red mud powder, and to aggregate the toxic heavy metal elements so as not to dissociate. Accordingly, the heavy metal concentration contained in the acidic wastewater passed through the reaction tank 230 may be treated to the level of drinking water quality standards.

상기 저류조(220) 및 반응조(230)는 단순 굴토하여 양 측벽과 바닥을 시멘트 벽체로 조성한 구조로 되어 있다. The storage tank 220 and the reaction tank 230 has a structure in which both side walls and the bottom are made of cement walls by simple excavation.

상기와 같이 구성된 본 실시예에 따르면, 중화제와 같은 화학약품 투입이 불필요하고, 응집제의 투입과 같은 후속공정이 필요 없으며, 중금속 처리도를 음용수 수질기준까지 높일 수 있고, 기계장치가 필요없어 유지관리에 용이하다.According to the present embodiment configured as described above, it is not necessary to add chemicals such as neutralizing agents, no subsequent process such as adding a flocculant, can increase the degree of heavy metal treatment up to drinking water quality standards, maintenance is not required It is easy to

이상에서 설명한 본 발명은 전술한 실시예 및 첨부된 도면에 의해 한정되는 것이 아니고, 본 발명의 기술적 사상을 벗어나지 않는 범위 내에서 여러 가지 치환, 변형 및 변경이 가능하다는 것이 본 발명이 속하는 기술분야에서 통상의 지식을 가진 자에게 있어 명백할 것이다.The present invention described above is not limited to the above-described embodiments and the accompanying drawings, and various substitutions, modifications, and changes are possible in the art without departing from the technical spirit of the present invention. It will be clear to those of ordinary knowledge.

상기한 바와 같이 본 발명에 따르면, 산악지형을 통과하는 도로 공사중 또는 후에 갱내에서 유출되는 산성배수에 포함된 중금속농도를 소택지 조성과 적니파우더가 채워진 반응조를 이용하여 처리함으로써 기존의 환경과 주변 생태계에 악영향을 주지 않으면서 산성배수를 일정 수질기준 이상의 용수로 만들 수 있는 효과가 있다. 또한, 관리가 쉬우며 저류조의 용량과 현장의 운전 여건을 고려하여 처리장 가동 시기를 조절할 수 있어 산성배수를 처리하는데 소요되는 비용을 절감할 수 있는 다른 효과가 있다.As described above, according to the present invention, the heavy metal concentration contained in the acid drainage discharged from the pit during or after the road construction passing through the mountainous terrain is treated by using a reaction tank filled with marsh land and red mud powder to the existing environment and the surrounding ecosystem. It has the effect of making acid drainage water above certain water quality standards without adversely affecting it. In addition, it is easy to manage and can adjust the operation time of the plant in consideration of the capacity of the storage tank and the operating conditions of the site, there is another effect that can reduce the cost of treating the acidic drainage.

도1은 본 발명에 따른 산성배수 처리장치에 일실시예 구성도.Figure 1 is an embodiment configuration of the acid wastewater treatment apparatus according to the present invention.

* 도면의 주요 부분에 대한 부호의 설명* Explanation of symbols for the main parts of the drawings

210 : 라임스톤 드레인 220 : 저류조210: limestone drain 220: reservoir

230 : 반응조230: reactor

Claims (3)

산악지형의 고속도로 공사시, 갱내에서 유출되는 유출수에 포함된 슬러지를 침강시켜 제거하는 라임스톤 드레인; Limestone drain for sedimentation and removal of sludge contained in the runoff flowing out of the pit during mountainous highway construction; 상기 라임스톤 드레인에서 배출된 처리수를 저류하되, 우기시나 수리지질학적인 현장여건(대수층)등으로 인하여 다량의 갱내 지하수가 유출될 경우를 감안하여 일정량이 유입되면 방류하는 저류조; 및A storage tank for storing the treated water discharged from the limestone drain, but discharged when a predetermined amount is introduced in consideration of the case where a large amount of groundwater flows out due to rainy season or hydrogeological site conditions (aquifer); And 상기 저류조에서 방류된 방류수에 적니파우더를 혼화시켜 산성배수에 포함된중금속을 제거하는 반응조A reaction tank for removing heavy metals contained in the acid drainage by mixing red mud powder with the discharge water discharged from the storage tank. 를 포함하는 산성배수 처리장치.Acid drainage treatment apparatus comprising a. 제 1 항에 있어서,The method of claim 1, 상기 저류조 및 반응조는,The storage tank and the reaction tank, 단순 굴토하여 양 측벽과 바닥을 시멘트 벽체로 조성되는 것을 특징으로 하는 산성배수 처리장치.The acid drainage treatment apparatus, characterized in that the simple sidewall and the bottom and both side walls and the bottom is composed of a cement wall. 제 1 항 또는 제 2 항에 있어서,The method according to claim 1 or 2, 상기 저류조는 산성배수에 포함된 고탁질의 부유물질 및 상기 부유물질에 부착된 중금속을 침전 제거하는 기능을 수행하는 것을 특징으로 하는 산성배수 처리장치.The storage tank is an acidic wastewater treatment apparatus, characterized in that to perform the function of sedimenting and removing the suspended solids and heavy metals attached to the suspended solids contained in the acidic drainage.
KR10-2005-0069727A 2005-07-29 2005-07-29 Apparatus for Control of Supply of Water with acidity KR100522326B1 (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100639656B1 (en) * 2006-07-21 2006-11-01 주식회사 도화종합기술공사 Acid rock drainage prevention method using field coating
CN103466778A (en) * 2013-10-09 2013-12-25 桂林理工大学 Method for making full use of acid neutralization potential of carbonate rock to process acid mine drainage
CN104150642A (en) * 2014-08-29 2014-11-19 昆明冶金研究院 Method for processing acidic wastewater by using modified red mud powder

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100639656B1 (en) * 2006-07-21 2006-11-01 주식회사 도화종합기술공사 Acid rock drainage prevention method using field coating
CN103466778A (en) * 2013-10-09 2013-12-25 桂林理工大学 Method for making full use of acid neutralization potential of carbonate rock to process acid mine drainage
CN104150642A (en) * 2014-08-29 2014-11-19 昆明冶金研究院 Method for processing acidic wastewater by using modified red mud powder

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