KR20030053271A - Electro-dewatering device for sludge using metal filter - Google Patents
Electro-dewatering device for sludge using metal filter Download PDFInfo
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/15—Treatment of sludge; Devices therefor by de-watering, drying or thickening by treatment with electric, magnetic or electromagnetic fields; by treatment with ultrasonic waves
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/42—Electrodialysis; Electro-osmosis ; Electro-ultrafiltration; Membrane capacitive deionization
- B01D61/56—Electro-osmotic dewatering
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
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- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/006—Electrochemical treatment, e.g. electro-oxidation or electro-osmosis
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- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/121—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F26—DRYING
- F26B—DRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
- F26B3/00—Drying solid materials or objects by processes involving the application of heat
- F26B3/32—Drying solid materials or objects by processes involving the application of heat by development of heat within the materials or objects to be dried, e.g. by fermentation or other microbiological action
- F26B3/34—Drying solid materials or objects by processes involving the application of heat by development of heat within the materials or objects to be dried, e.g. by fermentation or other microbiological action by using electrical effects
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/002—Construction details of the apparatus
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F26—DRYING
- F26B—DRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
- F26B2200/00—Drying processes and machines for solid materials characterised by the specific requirements of the drying good
- F26B2200/18—Sludges, e.g. sewage, waste, industrial processes, cooling towers
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/20—Sludge processing
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Abstract
Description
본 발명은 슬러지로부터 수분을 제거하는 전기탈수 장치에 관한 것으로서, 보다 상세하게는 전기탈수 효율을 높이기 위해 금속 여과필터를 사용하여 슬러지내부의 전도성을 증가시킨 슬러지 전기탈수 장치에 관한 것이다.The present invention relates to an electric dewatering apparatus for removing water from sludge, and more particularly, to a sludge electric dewatering apparatus for increasing conductivity in sludge using a metal filtration filter in order to increase the efficiency of electric dewatering.
일반적으로 폐기물 총 발생량의 12% 정도에 이르는 슬러지는 우리나라에서 1999년 한해동안 유기성 슬러지 약 590만톤과 무기성 슬러지 약 220만톤이 발생하였으며, 발생된 슬러지의 처리 비용은 대략 2,400∼4,000억원에 이르고 있다.In general, sludge, which accounts for 12% of the total amount of waste generated in Korea, generated about 5.9 million tons of organic sludge and about 2.2 million tons of inorganic sludge in 1999, and the treatment cost of sludge generated is about 240 to 400 billion won. .
상기한 슬러지 폐기물은 일반 폐기물과 달리 매립 및 소각 처리가 어려운데, 이것은 주로 슬러지에 함유된 수분 때문이며, 슬러지의 수분 함량이 많을수록 침출수 발생량이 증가하고, 소각 비용이 추가로 소요된다. 따라서 슬러지로부터 수분을 고효율로 제거하는 탈수 처리가 필수적이다.Unlike the general waste, the sludge waste is difficult to landfill and incineration, which is mainly due to the water contained in the sludge, the higher the water content of the sludge, the higher the leachate generation, the more incineration costs. Therefore, dehydration treatment to remove moisture from sludge with high efficiency is essential.
그러나 단순히 기계적 압력에 의해 슬러지를 눌러 탈수하는 기계적 탈수 처리는 슬러지 입자가 여과액과 함께 이동하여 여과포가 막히는 현상이 자주 발생하며, 이를 극복하기 위해 슬러지에 고압을 가할 경우, 오히려 여과포가 손상될 뿐만 아니라 에너지 소모가 높아지는 등의 단점을 안고 있다.However, mechanical dehydration treatment by simply depressing sludge by mechanical pressure often causes sludge particles to move together with the filtrate, causing the filter cloth to become clogged.In order to overcome this, high pressure is applied to the sludge. It also has disadvantages such as higher energy consumption.
이로서 도 6과 도 7에 도시한 바와 같이, 기계적 압착에 의한 탈수와 더불어 슬러지 내부에 전기장을 형성하여 슬러지 입자로부터 수분 입자를 분리시키는 방법을 병행한 전기탈수(electro-dewartering) 장치가 제안되었다.6 and 7, an electro-dewartering apparatus has been proposed in which a method of separating water particles from sludge particles by forming an electric field inside the sludge together with dehydration by mechanical compression is proposed.
상기 전기탈수 장치는 피스톤(1) 하단에 양극(3)을, 여과포(5) 하단에 음극(7)을 설치하여 피스톤(1)에 의한 압착과 동시에 슬러지(9) 내부에 전기장을 형성한다. 전기장에 의해 슬러지 입자와 수분 입자는 각각 (-)와 (+) 표면 전하를 띄게 되며, 각자의 슬러지 입자와 수분 입자는 양극(3)과 음극(7)으로 당겨지면서 탈수가 촉진된다.The electric dewatering device forms an electric field inside the sludge 9 at the same time as the positive electrode 3 is installed at the lower end of the piston 1 and the negative electrode 7 is installed at the lower end of the filter cloth 5. Due to the electric field, the sludge particles and the moisture particles have a (-) and a (+) surface charge, respectively, and the respective sludge particles and the moisture particles are attracted to the positive electrode 3 and the negative electrode 7 to promote dehydration.
그러나 종래 기술에 의한 전기탈수 장치는 비전도성인 여과포(5)에 의해 슬러지(9) 내부의 전기 흐름이 저하되어 탈수효율이 낮아지고, 탈수 초기에는 슬러지(9) 내부의 수분에 의해 슬러지(9) 내부의 전류 흐름이 활발하지만, 탈수가 진행됨에 따라 수분이 감소하면, 전기 저항에 의해 전류 흐름이 원활하지 않게 된다.However, the electric dewatering device according to the prior art lowers the flow of electricity in the sludge 9 due to the non-conductive filter cloth 5, and the dewatering efficiency is lowered. ) The current flow inside is active, but if moisture decreases as dehydration proceeds, current flow is not smooth due to electrical resistance.
이러한 결과로, 종래 기술에 의한 전기탈수 장치는 탈수가 진행될수록 전기탈수 효율이 급격히 낮아져 슬러지 폐기물로부터 수분을 고효율로 제거할 수 없는 한계를 안고 있다.As a result, the electric dehydration apparatus according to the prior art has a limitation that the dewatering efficiency is rapidly lowered as the dehydration proceeds, so that water can be removed from the sludge waste with high efficiency.
따라서 본 발명은 상기한 문제점을 해소하기 위한 것으로서, 본 발명은 슬러지의 전기탈수 과정에서 발생하는 전류 흐름 저하와, 이로 인한 탈수효율 저하를 억제할 수 있는 슬러지의 전기탈수 장치를 제공하는데 그 목적이 있다.Therefore, the present invention is to solve the above problems, the present invention is to provide an electrical dewatering device of the sludge that can suppress the current flow degradation occurring in the electrical dewatering process of the sludge, and thereby the dehydration efficiency decrease. have.
도 1은 본 발명에 의한 슬러지 전기탈수 장치의 개략도.1 is a schematic view of the sludge electric dewatering device according to the present invention.
도 2는 본 발명에 의한 슬러지 전기탈수 장치에서 슬러지 내부의 전류 흐름을 설명하기 위한 개략도.Figure 2 is a schematic diagram for explaining the current flow in the sludge in the sludge electrodehydration apparatus according to the present invention.
도 3은 본 발명에 의한 금속 필터의 개략도.3 is a schematic view of a metal filter according to the present invention;
도 4는 본 발명의 다른 실시예에 의한 금속 필터의 개략도.4 is a schematic view of a metal filter in accordance with another embodiment of the present invention.
도 5는 본 발명에 의한 전기탈수 장치와 종래 기술에 의한 전기탈수 장치 각각에서 전기탈수 후 슬러지의 수분 함량을 측정하여 나타낸 그래프.Figure 5 is a graph showing the measurement of the water content of the sludge after the electric dehydration in each of the electric dehydration apparatus according to the present invention and the electric dehydration apparatus according to the prior art.
도 6은 종래 기술에 의한 슬러지 전기탈수 장치의 개략도.Figure 6 is a schematic diagram of a sludge electric dewatering device according to the prior art.
도 7은 종래 기술에 의한 슬러지 전기탈수 장치에서 슬러지 내부의 전류 흐름을 설명하기 위한 개략도.Figure 7 is a schematic diagram for explaining the current flow inside the sludge in the sludge electric dewatering device according to the prior art.
상기의 목적을 달성하기 위하여 본 발명은,In order to achieve the above object, the present invention,
내부에 설치된 제1 전극 위에 슬러지를 담는 본체와, 본체와 결합하여 슬러지를 압착하는 피스톤과, 슬러지와 접하는 피스톤 일단에 설치되어 제1 전극과 함께 슬러지 내부에 전기장을 형성하는 제2 전극과, 슬러지와 접하는 제1, 2 전극의 일면에 제공되어 슬러지 고형분으로부터 수분을 선별하면서 각자의 제1, 2 전극과 동일 전위를 유지하여 슬러지의 전기장 세기를 증가시키는 도전성 금속 필터를 포함하는 슬러지 전기탈수 장치를 제공한다.A main body containing sludge on the first electrode installed therein, a piston coupled to the main body to compress the sludge, a second electrode provided at one end of the piston contacting the sludge to form an electric field in the sludge together with the first electrode, and the sludge A sludge electro-dehydration device comprising a conductive metal filter provided on one surface of the first and second electrodes in contact with the sludge to maintain moisture at the same potential as each of the first and second electrodes while increasing the electric field strength of the sludge. to provide.
이하, 첨부한 도면을 참고하여 본 발명의 바람직한 실시예를 보다 상세하게 설명하면 다음과 같다.Hereinafter, exemplary embodiments of the present invention will be described in detail with reference to the accompanying drawings.
도 1은 본 발명의 실시예에 따른 슬러지 전기탈수 장치의 개략도이고, 도 2는 슬러지 내부에 발생하는 전류 흐름을 설명하기 위한 개략도이다.FIG. 1 is a schematic diagram of an apparatus for dewatering sludge according to an embodiment of the present invention, and FIG. 2 is a schematic diagram for explaining a current flow generated in the sludge.
도시한 바와 같이 슬러지 전기탈수 장치는 슬러지(2)를 담는 본체(4)와, 본체(4) 내부에 설치되어 슬러지(2)를 지지하는 제1 전극(6)과, 본체(4)와 결합되어 슬러지(2)를 압착하는 피스톤(8)과, 슬러지(2)와 마주하는 피스톤(8) 일단에 설치되어 제1 전극(6)과 함께 슬러지(2)에 전기장을 형성하는 제2 전극(10)과, 제1, 2 전극(6, 10) 표면에 제공되어 슬러지(2)와 전극의 접촉을 제한하는 제1, 2 금속 필터(12a, 12b)를 포함한다.As shown, the sludge electric dewatering device is coupled to the main body 4 containing the sludge 2, the first electrode 6 installed in the main body 4 to support the sludge 2, and the main body 4. And a second electrode (8) for pressing the sludge 2 and one end of the piston 8 facing the sludge 2 to form an electric field in the sludge 2 together with the first electrode 6 ( 10) and first and second metal filters 12a and 12b provided on the surfaces of the first and second electrodes 6 and 10 to limit the contact between the sludge 2 and the electrodes.
상기 본체(4)는 제1 전극(6) 하단에 배출구(4a)를 형성하여 제1 전극(6)과 제1 금속 필터(12a)를 통과한 유출액을 외부로 배출하며, 피스톤(8)과 제2 전극(10) 사이에는 제2 전극(10)과 제2 금속 필터(12b)를 통과한 유출액을 모아주는 유출액 수집부(14)를 형성한다. 이 유출액 수집부(14)는 유출액을 흡입하는 진공 펌프(16)와 연결된다.The main body 4 discharges the effluent passing through the first electrode 6 and the first metal filter 12a to the outside by forming an outlet 4a at the lower end of the first electrode 6, and the piston 8 and An effluent collection part 14 is formed between the second electrodes 10 to collect effluent passing through the second electrode 10 and the second metal filter 12b. This effluent collection part 14 is connected with a vacuum pump 16 which sucks out the effluent.
이 때, 상기 제1, 2 전극(6, 10)은 다공성 재질로 이루어져 제1, 2 금속 필터(12a, 12b)와 함께 슬러지에 함유된 수분을 통과시킨다.At this time, the first and second electrodes 6 and 10 are made of a porous material to pass moisture contained in the sludge together with the first and second metal filters 12a and 12b.
그리고 슬러지(2)와 마주하는 피스톤(8) 일단에는 슬러지(2)의 온도를 측정하는 온도 센서(18)가 설치되어, 전기탈수 과정에서 슬러지(2)의 온도가 설정값 이상으로 상승하면, 제1, 2 전극(6, 10)의 전기 공급을 차단하여 슬러지(2)의 온도상승을 억제한다.Then, at one end of the piston 8 facing the sludge 2, a temperature sensor 18 for measuring the temperature of the sludge 2 is installed. The electrical supply of the 1st, 2nd electrodes 6 and 10 is interrupted | blocked, and the temperature rise of the sludge 2 is suppressed.
이로서 본체(4) 내부에 슬러지(2)를 담고 피스톤(8)을 동작시켜 슬러지(2)를 압착하면, 슬러지(2) 내부의 수분은 제1 금속 필터(12a)와 제1 전극(6)을 통과하여 배출구(4a)를 통해 외부로 배출되고, 제2 금속 필터(12b)와 제2 전극(10)을 통과한 유출액은 유출액 수집공간(14)으로 모인 다음, 진공 펌프(16)에 의해 외부로 배출된다.As a result, when the sludge 2 is contained in the main body 4 and the piston 8 is operated to compress the sludge 2, the moisture in the sludge 2 is reduced by the first metal filter 12a and the first electrode 6. After passing through the outlet 4a and discharged to the outside, the effluent passing through the second metal filter 12b and the second electrode 10 is collected in the effluent collection space 14, and then by the vacuum pump 16 It is discharged to the outside.
이와 동시에 제1, 2 전극(6, 10)에는 각각 (-) 전압과 (+) 전압이 공급되어 슬러지(2) 내부에 전기장을 형성하는데, 슬러지(2) 내부의 고형분은 (-) 표면 전하를 띄어 제2 전극(10)에 이끌리고, 유출액은 (+) 표면 전하를 띄어 제1 전극(6)에 이끌려 탈수가 촉진된다.At the same time, the first and second electrodes 6 and 10 are supplied with a negative voltage and a positive voltage, respectively, to form an electric field inside the sludge 2, and the solids inside the sludge 2 are charged with a negative surface charge. Is attracted to the second electrode 10, and the effluent has a positive surface charge to attract the first electrode 6 to promote dehydration.
이 때, 제1, 2 전극(6, 10) 표면에 위치하는 제1, 2 금속 필터(12a, 12b)는 일반 여과포와 마찬가지로 슬러지(2)와 전극의 접촉을 제한하면서 슬러지 고형분으로부터 유출액을 선별하는 역할을 하나, 상기 제1, 2 금속 필터(12a, 12b)는 종래의 여과포와 달리 도전성 금속으로 제작되기 때문에, 슬러지(2) 내부의 전기 전도성을 증가시키는 특징을 갖는다.At this time, the first and second metal filters 12a and 12b positioned on the surfaces of the first and second electrodes 6 and 10 select the effluent from the sludge solids while limiting the contact between the sludge 2 and the electrode, similar to the general filter cloth. However, since the first and second metal filters 12a and 12b are made of a conductive metal, unlike the conventional filter cloth, the first and second metal filters 12a and 12b have a feature of increasing electrical conductivity inside the sludge 2.
즉, 전기탈수의 원리는 슬러지(2)의 상, 하부에 직류 전기를 걸어, 하전된 슬러지 입자를 수분과 반대 방향으로 흐르게 하여 필터의 막힘 현상을 최소화하거나, 슬러지 사이의 이온성 물질을 수분과 동반하여 외부로 유출하는 것으로서, 전기탈수 과정에서 수분의 이동 속도는 다음의 수식으로 표현할 수 있다.That is, the principle of electric dehydration is applied to the upper and lower parts of the sludge (2) direct current to flow the charged sludge particles in the opposite direction to the water to minimize the clogging of the filter, or the ionic material between the sludge and water Accompanying the outflow to the outside, the movement speed of the water in the electrical dehydration process can be expressed by the following formula.
여기서, V는 전기탈수 과정에서 수분의 이동 속도(electro-osmotic flow velocity), U는 전기탈수의 유동성(electro-osmotic mobility), E는 전기장의 세기(electric field strength)를 나타낸다.Here, V is the electro-osmotic flow velocity of the water in the electrical dehydration process, U is the electro-osmotic mobility, E is the electric field strength (electric field strength).
이와 같이 전기탈수 효과는 슬러지(2)에 가해지는 전기장의 세기에 비례함을 알 수 있으며, 본 실시예는 제1, 2 전극(6, 10) 표면에 도전성 금속으로 제작된 제1, 2 금속 필터(12a, 12b)를 구비함에 따라, 슬러지(2) 내부의 전기 전도성을 크게 증가시켜 전기탈수 효과를 높이는 장점을 갖는다.As described above, it can be seen that the electric dehydration effect is proportional to the intensity of the electric field applied to the sludge 2. In this embodiment, the first and second metals are made of a conductive metal on the surfaces of the first and second electrodes 6 and 10. As the filters 12a and 12b are provided, the electrical conductivity inside the sludge 2 is greatly increased to increase the electric dewatering effect.
보다 구체적으로, 상기 제1, 2 금속 필터(12a, 12b)는 도 3에 도시한 바와 같이 미세한 금속 선을 격자 형태로 가공한 그물망(20) 또는 도4에 도시한 바와 같이 섬유상 미세 금속을 이용해 제조한 다공성 금속판(22)으로 이루어질 수 있다.More specifically, the first and second metal filters 12a and 12b may be formed using a mesh 20 processed in a lattice form as shown in FIG. 3 or a fibrous fine metal as shown in FIG. 4. It may be made of a porous metal plate 22 manufactured.
바람직하게, 상기 그물망 또는 다공성 금속판은 스테인리스, 티타늄 또는 티타늄이 코팅된 철 등으로 이루어지며, 유출액의 투과 정도를 고려하여 1∼1,000㎛ 범위의 격자 조직 또는 세공을 갖는 것으로 제작되는 것이 바람직하다.Preferably, the mesh or porous metal plate is made of stainless steel, titanium or titanium coated iron, etc., and is preferably manufactured to have a lattice structure or pores in the range of 1 to 1,000 μm in consideration of the degree of permeation of the effluent.
도 5는 슬러지의 주성분으로 몬모리노나이트를 이용하여 금속 필터를 사용한 본 발명에 의한 전기탈수 장치(실시예)와, 여과포를 사용한 종래 기술에 의한 전기탈수 장치(비교예) 각각에서 전기탈수 이후 슬러지 내부의 수분 함유량을 측정하여 나타낸 그래프이다.Figure 5 shows the sludge after the electric dewatering in each of the electric dewatering device according to the present invention (Example) using a metal filter using the montmorinoite as a main component of the sludge, and a conventional dewatering device (comparative example) using a filter cloth It is a graph which measured and measured the internal moisture content.
실험에 사용된 슬러지 부피는 50ml, 탈수 압력은 3기압, 탈수 시간은 30분으로 하였고, 제1, 2 전극 양단에 약 100V의 직류 전압을 인가하였다. 비교예 측정에는 대략 0.5∼1mm 두께를 갖는 합성수지 재질의 여과포를 사용하였으며, 실시예 측정에는 스테인리스 그물망으로 이루어진 금속 필터를 사용하였다.The sludge volume used in the experiment was 50 ml, the dehydration pressure was 3 atm, and the dehydration time was 30 minutes, and a DC voltage of about 100 V was applied to both ends of the first and second electrodes. In the measurement of the comparative example, a filter cloth made of a synthetic resin material having a thickness of about 0.5 to 1 mm was used, and a metal filter made of stainless steel mesh was used for the measurement of the example.
실험 결과, 여과포를 사용한 비교예는 전기탈수 후 슬러지의 수분 함유량이 50% 정도로 높게 나타나는 반면, 금속 필터를 사용한 본 실시예는 전기탈수 후 슬러지의 수분 함유량이 25% 정도로 낮게 나타났다.As a result of the experiment, the comparative example using the filter cloth showed that the water content of the sludge after the electric dehydration was as high as 50%, while the present embodiment using the metal filter showed that the water content of the sludge after the electric dehydration was as low as 25%.
따라서 본 실시예에 의한 전기탈수 장치가 종래 기술에 의한 전기탈수 장치와 비교하여 대략 2배 정도 향상된 전기탈수 효과를 나타냄을 확인할 수 있다.Therefore, it can be seen that the electric dewatering device according to the present embodiment exhibits about two times improved electric dewatering effect compared to the electric dewatering device according to the prior art.
상기에서는 본 발명의 바람직한 실시예에 대하여 설명하였지만, 본 발명은 이에 한정되는 것이 아니고 특허청구범위와 발명의 상세한 설명 및 첨부한 도면의 범위 안에서 여러 가지로 변형하여 실시하는 것이 가능하고 이 또한 본 발명의 범위에 속하는 것은 당연하다.Although the preferred embodiments of the present invention have been described above, the present invention is not limited thereto, and various modifications and changes can be made within the scope of the claims and the detailed description of the invention and the accompanying drawings. Naturally, it belongs to the range of.
이와 같이 본 발명은 슬러지로부터 수분을 걸러 통과시키는 여과 수단으로서 금속 필터를 사용함에 따라, 슬러지에 가해지는 전기장의 세기를 높여 슬러지 내부의 전기 전도성을 증가시킨다. 이러한 결과, 슬러지에 동일한 직류 전압이 가해지는 조건에서, 슬러지의 전기탈수 효과를 높일 수 있다.As described above, according to the present invention, the metal filter is used as a filtration means for filtering water from the sludge, thereby increasing the strength of the electric field applied to the sludge, thereby increasing the electrical conductivity inside the sludge. As a result, the electric dewatering effect of the sludge can be enhanced under the condition that the same DC voltage is applied to the sludge.
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CN107055984A (en) * | 2016-12-01 | 2017-08-18 | 浙江工业大学 | A kind of method that high-voltage pulse electrolytic tension filter method deep dehydration handles sludge |
CN107055985A (en) * | 2016-12-01 | 2017-08-18 | 浙江工业大学 | A kind of plate frame press filter device of additional electrolysis deep dehydration sludge |
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KR101164635B1 (en) * | 2010-03-29 | 2012-07-16 | 순천대학교 산학협력단 | A photocatalyst filter for air cleaning using high corrosion resistance chips and a manufacturing method thereof |
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US5376279A (en) * | 1988-09-12 | 1994-12-27 | British Technology Group Ltd. | Filtration using ionically and electrically conductive depth filter |
AUPN483495A0 (en) * | 1995-08-16 | 1995-09-07 | Commonwealth Scientific And Industrial Research Organisation | Dewatering of sludges |
KR200141913Y1 (en) * | 1996-07-31 | 1999-06-01 | 김광희 | A pressing dehydrating apparatus by electric osmosis |
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CN107055985A (en) * | 2016-12-01 | 2017-08-18 | 浙江工业大学 | A kind of plate frame press filter device of additional electrolysis deep dehydration sludge |
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