KR20080042788A - Carrier and the process for purify a heavy metal waste water or sewage - Google Patents

Carrier and the process for purify a heavy metal waste water or sewage Download PDF

Info

Publication number
KR20080042788A
KR20080042788A KR20080038998A KR20080038998A KR20080042788A KR 20080042788 A KR20080042788 A KR 20080042788A KR 20080038998 A KR20080038998 A KR 20080038998A KR 20080038998 A KR20080038998 A KR 20080038998A KR 20080042788 A KR20080042788 A KR 20080042788A
Authority
KR
South Korea
Prior art keywords
composition
weight
heavy metal
mixing
wastewater
Prior art date
Application number
KR20080038998A
Other languages
Korean (ko)
Other versions
KR100874197B1 (en
Inventor
손주현
최상열
박충보
Original Assignee
거성환경(주)
손주현
최상열
박충보
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 거성환경(주), 손주현, 최상열, 박충보 filed Critical 거성환경(주)
Priority to KR20080038998A priority Critical patent/KR100874197B1/en
Publication of KR20080042788A publication Critical patent/KR20080042788A/en
Application granted granted Critical
Publication of KR100874197B1 publication Critical patent/KR100874197B1/en

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • C02F3/105Characterized by the chemical composition
    • C02F3/106Carbonaceous materials
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • C02F3/105Characterized by the chemical composition
    • C02F3/107Inorganic materials, e.g. sand, silicates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • 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
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

A manufacturing method of an immobilized carrier for treatment of heavy metal-containing mine wastewater and sewage or wastewater is provided to improve treatment efficiency of heavy metals by forming the carrier from activated carbon, white charcoal, clinoptilolite, mordenite, granite porphyry and alkaline silicate, and retain a porous foamed space of the carrier for long time and substantially increase purification efficiency by reinforcing durability of the carrier. A manufacturing method of an immobilized carrier for treatment of heavy metal-containing mine wastewater and sewage or wastewater comprises: a first mixing step(S1) of mixing 10 to 20 wt.% of anthracite, 20 to 30 wt.% of activated carbon, and 30 to 36 wt.% of white charcoal to obtain a first composition of a powder form; a heating step(S2) of washing the first composition, and heating and drying the washed first composition to evaporate water from the first composition; a drying step(S3) of washing the first composition with a nitric acid solution, and naturally drying the washed first composition to evaporate water from the first composition; a second mixing step(S4) of mixing the first composition with 7 to 15 wt.% of clinoptilolite, 7 to 15 wt.% of mordenite, 2.5 to 7.5 wt.% of granite porphyry, and 5 to 15 wt.% of alkaline silicate to obtain a second composition; a processing step(S5) of processing the second composition into a specific form through a molding device; and a sintering step(S6) of sintering the second composition at a temperature of 800 to 900 deg.C for 5 to 7 hours through a sintering furnace.

Description

중금속함유 광산 폐수 및 하·폐수처리를 위한 고정화 담채 및 그 제조방법(고정화 담채 및 그 CAPH제조방법) { carrier and the process for purify a heavy metal waste water or sewage }Immobilized dyes for the treatment of heavy metal-containing mine wastewater and sewage and wastewater (Methods for manufacturing immobilized dyes and its CAPH) {carrier and the process for purify a heavy metal waste water or sewage}

본 발명은 중금속함유 광산 폐수 및 하·폐수처리를 위한 고정화 담채 및 그 제조방법에 관한 것으로서, 강한 산성의 폐수에서도 중금속을 정화하는 효과가 뛰어나고, 충격 등에 의해서 비표면적을 형성하는 다공성 발포공간이 파손되지 않도록, 무연탄(Anthracite)과 활성탄(active carbon), 백탄(white charcol), 크리노프티로라이트(Clinoptilolite), 몰데나이트(Mordenite), 그라니트포필리(Granite porphyry), 알칼리실리케이트(Alkaline Silicate)로 구성된 중금속함유 광산 폐수 및 하·폐수처리를 위한 고정화 담채 및 그 제조방법에 관한 것이다.The present invention relates to an immobilized tin for the treatment of heavy metal-containing mine wastewater and sewage and wastewater, and to a method of manufacturing the same. The present invention is excellent in purifying heavy metals even in strong acidic wastewater, and breaks the porous foam space that forms a specific surface area by impact. Anthracite, active carbon, white charcol, Clinoptilolite, Mordenite, Granite porphyry, Alkaline Silicate The present invention relates to an immobilized tin for heavy metal-containing mine wastewater and sewage and wastewater treatment, and a method of manufacturing the same.

본 발명의 주요목적이 되는 중금속이 포함된 폐수는 광산, 전기 도금 시설, 건설 현장, 교통 설비 및 전기 산업 시설 등과 같은 광범위한 산업 및 군사 시설에서 약 2,000,000톤 이상을 배출되고 있고, 이렇게 배출된 폐수는 4대 강을 비롯한 기타 하천에 유입되고 있는 실정이다.Wastewater containing heavy metals, which is the main purpose of the present invention, emits more than 2,000,000 tons in a wide range of industrial and military facilities such as mines, electroplating facilities, construction sites, transportation facilities, and electrical industry facilities. It is flowing into four rivers and other rivers.

상기 하천에 유입된 폐수는 다시 토양 및 지하수는 물론 하천에 유입됨으로써, 상수원 오염과 식수 오염의 주범으로 지적되고 있다. Wastewater introduced into the stream is again pointed out as a main culprit of water pollution and drinking water pollution by being introduced into the river as well as soil and groundwater.

그리고 각종 오·폐수에 함유된 구리, 납 등과 같은 양 이온형 중금속들은, 토양 중의 흡착 매체인 금속(수)산화물들과의 흡착 반응시 pH가 커질수록 흡착 매체에 흡착되어 산성도가 높아지고, 그 높은 산성의 양 이온형 중금속들은 토양 중의 흡착 매체인 금속(수)산화물에 의해 쉽게 제거되지 못하게 된다.In addition, positive ion heavy metals such as copper and lead contained in various wastewaters are adsorbed on the adsorption medium as the pH increases during the adsorption reaction with the metal (water) oxides, which are adsorption media in the soil, resulting in higher acidity. Acidic cationic heavy metals are not easily removed by metal (aqueous) oxides, which are adsorptive media in the soil.

위 흡착 매체에 흡수되지 못한 양 이온형 중금속들은 하천수 및 지하수 흐름을 따라 이동하면서 지하수, 하천 및 토양의 중금속 오염을 더욱 증대시키고 있는 실정이다.Cationic heavy metals that are not absorbed by the above adsorption medium move along the stream and groundwater streams to increase the heavy metal contamination of groundwater, rivers and soils.

위와 같이, 폐수에 포함된 중금속을 제거하기 위해서 많은 연구들이 수행되어 오고 있는데, 현재까지 실용화되었거나 또는 연구되고 있는 방법으로는 응집침전법, 이온교환법, 흡착법, 산화환원법, 전기분해법, 중화법 및 추출법 등과 같은 물리화학적 처리방법들이 주로 사용되고 있다.As described above, many studies have been conducted to remove heavy metals contained in wastewater, and the methods that have been put to practical use or being studied so far are flocculation sedimentation, ion exchange, adsorption, redox, electrolysis, neutralization and extraction. Physicochemical treatment methods such as these are mainly used.

상기 방법 중 흡착법은 중금속들을 흡착 제거하기 위한 흡착 매체인 금속산화물, 활성탄, 플라이 애쉬(fly ash), 피트(peat), 활성슬러지, 폐슬러지, 생흡착제 등과 같은 다양한 종류의 천연 또는 합성 흡착제로 구성된 담채가 다방면으로 연구되고 있고, 물속에 포함된 중금속을 특별히 제거를 위한 목적으로 활성탄을 단 일재료로 가공하여 널리 사용되고 있는 실정이다.Adsorption method is composed of various kinds of natural or synthetic adsorbents such as metal oxide, activated carbon, fly ash, peat, activated sludge, waste sludge, biosorbent, etc. The tin is being studied in various fields, and the active carbon is processed into a single material for the purpose of removing heavy metals contained in water.

상기 배경기술에서 설명된 바와 같이, 흡착법으로 물속에 포함된 중금속을 제거하기 위한 목적으로 제조된 폐수용 활성탄 담채는 중금속 처리효율 자체가 낮은 문제점이 있다.As described in the background art, activated carbon tin for wastewater prepared for the purpose of removing heavy metals contained in water by adsorption has a problem of low heavy metal treatment efficiency itself.

더욱이 약한 충격 및 폐수의 유속으로 담채 표면이 파손되거나 마모되어 비표면적을 형성하는 다공성 발포공간이 파손되고, 높은 pH농도의 폐수 속에 포함된 중금속을 정화하는 정화효율이 대폭 낮은 문제점이 있다.Furthermore, there is a problem in that the porous foam space forming the specific surface area is damaged due to the weak impact and the flow rate of the waste water, and the surface is damaged or worn, and the purification efficiency for purifying heavy metals contained in the waste water of high pH concentration is very low.

본 발명은 무연탄 10중량% 내지 20중량%와 활성탄 20중량% 내지 30중량%, 백탄 30중량% 내지 36중량%, 크리노프티로라이트 7중량% 내지 15중량%, 몰데나이트 7중량% 내지 15중량%, 그라니트포필리 2.5중량% 내지 7.5중량% 및 알칼리실리케이트 5중량% 내지 15중량%로 구성된 중금속함유 광산 폐수 및 하·폐수처리를 위한 고정화 담채.The present invention is 10 to 20% by weight of anthracite coal and 20 to 30% by weight activated carbon, 30 to 36% by weight of white coal, 7 to 15% by weight of crinotyrolite, 7 to 15% of mordenite Immobilized tin for heavy metal-containing mine wastewater and sewage / wastewater treatment consisting of 5% by weight to 15% by weight of Granite Popphyli, 2.5% to 7.5% by weight of granite popli.

그리고 무연탄 10중량% 내지 20중량%와 활성탄 20중량% 내지 30중량% 및 백탄 30중량% 내지 36중량%을 혼합정련하여 파우더 형태의 제1조성물을 획득하는 제1혼합단계와; 상기 제1혼합단계를 거친 후, 그 제1조성물을 수세하고, 그 수세 된 제1조성물이 흡수한 수분이 증발되도록 가열건조하는 가열단계와; 상기 가열단계를 거친 후, 그 제1조성물에 질산용액으로 다시 수세하고, 그 수세 된 제1조성물이 흡 수한 수분이 증발되도록 자연건조하는 건조단계와; 상기 건조단계를 거친 후, 그 제1조성물에 크리노프티로라이트 7중량% 내지 15중량%와 몰데나이트 7중량% 내지 15중량%, 그라니트포필리 2.5중량% 내지 7.5중량% 및 알칼리실리케이트 5중량% 내지 15중량%로 혼합하여 제2조성물을 획득하는 제2혼합단계와; 상기 제2혼합단계를 거친 후, 성형장치를 통해 제2조성물을 특정 형태로 가공하는 가공단계와; 상기 가공단계를 거친 후, 소결로를 통해 제2조성물을 800℃ 내지 900℃의 온도로 5시간 내지 7시간 소결하는 소결단계로 구성됨을 특징으로 하는 중금속함유 광산 폐수 및 하·폐수처리를 위한 고정화 담채의 제조방법을 본 발명의 과제 해결 수단으로 한다.And a first mixing step of mixing and refining 10% to 20% by weight of anthracite coal, 20% to 30% by weight of activated carbon, and 30% to 36% by weight of white coal to obtain a first composition in powder form; A heating step of washing the first composition after the first mixing step and heating and drying the water so that the moisture absorbed by the washed first composition is evaporated; After the heating step, the first composition is washed with the nitric acid solution again, and the drying step of natural drying so that the water absorbed by the washed first composition is evaporated; After the drying step, 7 wt% to 15 wt% of chrynophthyrolite and 7 wt% to 15 wt% of mordenite, 2.5 wt% to 7.5 wt% of granite pophili, and alkali silicate 5 in the first composition A second mixing step of obtaining a second composition by mixing by weight to 15% by weight; A processing step of processing the second composition into a specific form through a molding apparatus after the second mixing step; After the processing step, the sintering step of sintering the second composition at a temperature of 800 ℃ to 900 ℃ 5 hours to 7 hours through the sintering furnace, characterized in that the immobilization for the treatment of heavy metal-containing mine wastewater and sewage and waste water The manufacturing method of a tin is regarded as the problem solving means of this invention.

본 발명은 활성탄, 백탄, 크리노프티로라이트, 몰데나이트, 그라니트포필리, 알칼리실리케이트로 구성되어 중금속 처리효율 자체가 높은 효과가 있다.The present invention is composed of activated charcoal, white charcoal, crinophthyrolite, moldenite, granite popli, and alkali silicate, and thus the heavy metal treatment efficiency itself is high.

더욱이 내구성이 강화되어 약한 충격 및 폐수의 유속으로 담채 표면이 파손되거나 마모되지 않아서, 비표면적을 형성하는 다공성 발포공간이 장기간 유지되고, 높은 pH농도의 폐수 속에 포함된 중금속을 정화하는 정화효율이 대폭 높아지는 효과가 있다.In addition, the durability is enhanced, so that the surface is not damaged or worn due to weak impact and wastewater flow rate, so that the porous foam space forming the specific surface area is maintained for a long time, and the purification efficiency for purifying heavy metal contained in the wastewater of high pH concentration is greatly improved. There is a rising effect.

본 발명은 강한 산성의 폐수 속에 포함된 중금속을 정화하는 효과가 뛰어나고, 충격 등에 의해서 비표면적을 형성하는 다공성 발포공간이 파손되지 않도록, 무연탄 10중량% 내지 20중량%와 활성탄 20중량% 내지 30중량%, 백탄 30중량% 내지 36중량%, 크리노프티로라이트 7중량% 내지 15중량%, 몰데나이트 7중량% 내지 15중량%, 그라니트포필리 2.5중량% 내지 7.5중량% 및 알칼리실리케이트 5중량% 내지 15중량%로 구성된 중금속함유 광산 폐수 및 하·폐수처리를 위한 고정화 담채에 관한 것이다.The present invention is excellent in the effect of purifying heavy metals contained in the strong acid waste water, 10% to 20% by weight of anthracite coal and 20% to 30% by weight of activated carbon, so as not to break the porous foam space forming a specific surface area by impact, etc. %, 30% to 36% by weight of charcoal, 7% to 15% by weight of Crinotrophyrite, 7% to 15% by weight of mordenite, 2.5% to 7.5% by weight of granite popil and 5% of alkali silicate The present invention relates to an immobilized tin for heavy metal-containing mine wastewater and sewage / wastewater treatment composed of% to 15% by weight.

상기 본 발명의 중금속함유 광산 폐수 및 하·폐수처리를 위한 고정화 담채 의 제조방법은 무연탄 10중량% 내지 20중량%와 활성탄 20중량% 내지 30중량% 및 백탄 30중량% 내지 36중량%을 혼합정련하여 파우더 형태의 제1조성물을 획득하는 제1혼합단계와(S1); 상기 제1혼합단계를 거친 후, 그 제1조성물을 수세하고, 그 수세 된 제1조성물이 흡수한 수분이 증발되도록 가열건조하는 가열단계와(S2); 상기 가열단계를 거친 후, 그 제1조성물에 질산용액으로 다시 수세하고, 그 수세 된 제1조성물이 흡수한 수분이 증발되도록 자연건조하는 건조단계와(S3); 상기 건조단계를 거친 후, 그 제1조성물에 크리노프티로라이트 7중량% 내지 15중량%와 몰데나이트 7중량% 내지 15중량%, 그라니트포필리 2.5중량% 내지 7.5중량% 및 알칼리실리케이트 5중량% 내지 15중량%로 혼합하여 제2조성물을 획득하는 제2혼합단계와(S4); 상기 제2혼합단계를 거친 후, 성형장치를 통해 제2조성물을 특정 형태로 가공하는 가공단계와(S5); 상기 가공단계를 거친 후, 소결로를 통해 제2조성물을 800℃ 내지 900 ℃의 온도로 5시간 내지 7시간 소결하는 소결단계(S6)로 크게 6단계로 구성된다.The method for producing an immobilized tin for the treatment of heavy metal-containing mine wastewater and sewage and wastewater of the present invention comprises mixing and refining anthracite coal 10 wt% to 20 wt%, activated carbon 20 wt% to 30 wt%, and white coal 30 wt% to 36 wt%. A first mixing step of obtaining a first composition in powder form (S1); A heating step of washing the first composition after the first mixing step and heating and drying the water to absorb the water absorbed by the washed first composition (S2); After the heating step, the first composition is washed with the nitric acid solution again, the drying step of natural drying to evaporate the water absorbed by the washed first composition (S3); After the drying step, 7 wt% to 15 wt% of chrynophthyrolite and 7 wt% to 15 wt% of mordenite, 2.5 wt% to 7.5 wt% of granite pophili, and alkali silicate 5 in the first composition A second mixing step of obtaining a second composition by mixing by weight to 15% by weight (S4); After the second mixing step, the processing step of processing the second composition in a specific form through a molding apparatus (S5); After the processing step, the sintering step (S6) for sintering the second composition at a temperature of 800 ℃ to 900 ℃ 5 hours to 7 hours through a sintering furnace is composed of largely six steps.

이하 본 발명의 실시 예를 통한 첨부된 도면을 참조하여 더욱 상세하게 설명한다.Hereinafter, with reference to the accompanying drawings through an embodiment of the present invention will be described in more detail.

도 1은 본 발명의 제조방법을 도식화한 도면이다.1 is a diagram illustrating a manufacturing method of the present invention.

첫째, 제1혼합단계(S1)는 그레뉼(granulite) 형태의 분말 무연탄 10중량% 내지 20중량%와 그레뉼(granulite) 형태의 분말 활성탄 20중량% 내지 30중량% 및 그레뉼(granulite) 형태의 분말 백탄 30중량% 내지 36중량%을 제1조성물 형태로 혼합정련하여 제1조성물을 형성하는 것으로 구성된다.First, the first mixing step (S1) is 10% to 20% by weight of powdered anthracite coal in granule (granulite) form and 20% to 30% by weight of powdered activated carbon in granule (granulite) form and granulite form 30 wt% to 36 wt% of powdered white charcoal is mixed and refined in the form of a first composition to form a first composition.

둘째, 가열단계(S2)는 상기 제1혼합단계를 거친 제1조성물의 표면에 존재하는 이물질이 제거되도록, 맑은 물로 10회 내지 20회 수세하고, 그 수세과정으로 제1조성물이 흡수한 수분이 증발되도록 100℃ 이상의 온도로 7시간 ~ 11시간 동안 가열하여 건조하는 것으로 구성된다.Second, the heating step (S2) is washed 10 to 20 times with clear water to remove the foreign substances on the surface of the first composition after the first mixing step, the water absorbed by the first composition in the washing process It consists of drying by heating for 7 hours to 11 hours at a temperature of 100 ℃ or more to evaporate.

셋째, 건조단계(S3)는 상기 가열단계를 거친 제1조성물에 질산용액으로 다시 5회 내지 11회로 수세하고, 그 수세과정으로 제1조성물이 흡수한 수분이 증발되도록 30시간 ~ 70시간 동안 자연건조하는 것으로 구성된다.Third, the drying step (S3) is washed with the nitric acid solution again 5 times to 11 times to the first composition after the heating step, and the natural water for 30 to 70 hours so that the water absorbed by the first composition is evaporated by the washing process. It consists of drying.

넷째, 제2혼합단계(S4)는 상기 건조단계를 거친 제1조성물에 분말형태의 크리노프티로라이트 7중량% 내지 15중량%와 분말형태의 몰데나이트 7중량% 내지 15중량%, 분말형태의 그라니트포필리 2.5중량% 내지 7.5중량% 및 분말형태의 알칼리실리케이트 5중량% 내지 15중량%로 혼합하고, 다시 파우더 형태의 제2조성물을 형성하는 것으로 구성된다.Fourth, the second mixing step (S4) is 7% by weight to 15% by weight of Crinotropyrite in powder form and 7% by weight to 15% by weight in the form of powder in the first composition after the drying step, powder form 2.5 wt% to 7.5 wt% of granite pophyli and 5 wt% to 15 wt% of alkali silicate in powder form, followed by forming a second composition in powder form.

위 크리노프티로라이트와 몰데나이트는 제올라이트의 한 종류로서, 본원 발명에서 크리노프티로라이트와 몰데나이트의 선택적 이온교환 특성은 많은 무기염류(주된 성분은 마그네슘 및 칼슘 이온)가 녹아 있는 경수를 연 수화시키는 특성이 있다.The above Crinophthyrolite and mordenite are a kind of zeolite, and the selective ion exchange characteristics of the Crinophthyrolite and the mordenite in the present invention is a hard water in which many inorganic salts (main components magnesium and calcium ions) are dissolved. It has the property of softening.

더욱이 크리노프티로라이트는 제올라이트 중에서 결정화학적으로나 교환성 양이온 성격에 있어서 다양한 광물 상을 이루는 특징으로, 약알카리성으로 환원되어 칼슘 이온을 안정시키는 양이온교환역할을 한다.In addition, Crynovtirolite forms various mineral phases in the crystallographic and exchangeable cationic nature of zeolite, and is reduced to weak alkalinity and serves as a cation exchanger to stabilize calcium ions.

또한, 크리노프티로라이트와 몰데나이트는 구조상의 공동 내에는 양이온들 주위에 많은 양의 물이 존재하지만 외부의 온도 및 압력에 따라서 쉽게 탈수된다.In addition, Crinoftyrolite and Mordenite have a large amount of water around the cations in the structural cavity, but are easily dehydrated depending on the external temperature and pressure.

특히, 탈수된 크리노프티로라이트와 몰데나이트는 적합한 크기와 형태의 무기 및 유기분자들을 선택적으로 흡착함으로써, 서로 다른 분자들을 개별적으로 분 리할 수 있는 뛰어난 선택적 흡착성을 갖는다.In particular, dehydrated Clinopthyrolite and mordenite have excellent selective adsorption to selectively separate different molecules by selectively adsorbing inorganic and organic molecules of suitable size and shape.

위와 같이, 크리노프티로라이트는 공동의 크기가 약 4~5Å으로 중금속이온 및 방사성 물질의 흡착하는 역할을 하고, 모데나이트는 공동의 크기가 6~7Å으로 황화수소(H₂S), 중금속이온 및 방사성 물질의 흡착 및 소취하는 역할을 한다.As above, Clinoftyrolite has a role of adsorption of heavy metal ions and radioactive materials with a cavity size of about 4-5Å, and mordenite has a size of 6-7Å of hydrogen sulfide (H₂S), heavy metal ions and radioactivity. Adsorbs and deodorizes the material.

그리고 모데나이트는 제올라이트 중에서 상대적으로 우수한 표면활성과 큰 결정 공극 및 열적 안정성이 높기 때문에 흡착 및 분자체 특성이 우수하고, 타 광물에는 없는 무기염류(예를 들면 칼슘 이온)를 제공하는 역할을 한다.In addition, mordenite has excellent adsorption and molecular sieve properties because of its relatively good surface activity, large crystal voids, and high thermal stability among zeolites, and serves to provide inorganic salts (for example, calcium ions) that are not present in other minerals.

그리고 상기 그라니트포필리는 제1조성물의 역할을 보조하여, 원적외선 및 음이온의 방사로 인한 생체의 활성화, 무기염류의 제공 및 흡착성에 의한 중금속 제거 등의 역할을 한다.In addition, the granite poppies assist the role of the first composition, and play a role of activating a living body due to radiation of far infrared rays and anions, providing inorganic salts, and removing heavy metals by adsorption.

마지막으로 알칼리실리케이트는 상기 무연탄 활성탄, 백탄 크리노프티로라이트, 몰데나이트 및 그라니트포필리를 결합시키는 역할을 한다.Finally, the alkali silicate serves to bind the anthracite activated carbon, white coal Crinophtyrolite, molddenite and granite pophyli.

다섯째, 가공단계(S5)는 상기 제2혼합단계(S2)를 거친 제2조성물을 성형장치를 통해 사각형과 삼각형 및 원형 형태로 가공하는 것으로 구성된다.Fifth, the processing step (S5) consists of processing the second composition passed through the second mixing step (S2) in the shape of a square, triangle and circle through a molding apparatus.

여섯째, 소결단계(S6)는 상기 가공단계에 의해 특정한 모양으로 형성된 제2조성물을 소결로를 사용하여 800℃ 내지 900℃의 온도로 5시간 내지 7시간 소결하 는 것으로 구성된다.Sixth, the sintering step (S6) consists of sintering the second composition formed in a specific shape by the processing step at a temperature of 800 ℃ to 900 ℃ 5 hours to 7 hours using a sintering furnace.

상기와 같은 제조방법을 통하여, 다양한 형상으로 형성된 폐수처리용 담채는 중금속 처리효율 자체가 높은 효과가 있고, 내구성이 강화되어 약한 충격 및 폐수의 유속으로 담채 표면이 파손되거나 마모되지 않아서, 비표면적을 형성하는 다공성 발포공간이 유지되며, 폐수의 높은 pH농도에서도 중금속을 정화하는 정화효율이 대폭 높아지는 효과가 있다.Through the manufacturing method as described above, the wastewater treatment tines formed in various shapes have a high effect of the heavy metal treatment efficiency itself, and the durability is enhanced, so that the surface of the tint is not damaged or worn with a weak impact and wastewater flow rate, so that the specific surface area is reduced. The porous foam space to be formed is maintained, and the purification efficiency for purifying heavy metals at a high pH concentration of the waste water is greatly increased.

[실시 예][Example]

우선, 그레뉼 형태로 형성된 분말형태의 무연탄 150g과 분말형태의 활성탄 150g 및 분말형태의 백탄 330g을 믹서장치로 혼합정련하는 제1혼합단계(S1)를 진행하여, 파우더 형태의 제1조성물을 형성한다.First, 150 g of anthracite coal in powder form, 150 g of powdered activated carbon, and 330 g of powdered charcoal are mixed and refined with a mixer to form a first composition in powder form. do.

그 후, 상기 제1혼합단계(S1)를 거친 제1조성물을 맑은 물로 12회 수세하고, 150℃로 9시간 동안 가열하는 가열단계(S2)를 진행하여, 표면의 이물질이 제거된 제1조성물을 획득한다.Thereafter, the first composition passed through the first mixing step (S1) is washed 12 times with clear water, followed by a heating step (S2) of heating at 150 ° C. for 9 hours to remove foreign substances on the surface of the first composition. Acquire.

상기 가열단계(S2)를 거친 제1조성물에 질산용액으로 다시 8회로 수세하고, 50시간 동안 자연건조하는 건조단계(S3)를 진행하여, 가열단계(S2)에 형성된 이물 질이 제거된 제1조성물을 획득한다.The first composition passed through the heating step (S2) was washed again with the nitric acid solution eight times, the drying step (S3) to dry naturally for 50 hours, the first foreign material formed in the heating step (S2) is removed Obtain the composition.

그리고 상기 건조단계(S3)를 거친 제1조성물에 분말형태의 크리노프티로라이트 110g과 분말형태의 몰데나이트 110g, 분말형태의 그라니트포필리 50g 및 분말형태의 알칼리실리케이트 100g을 혼합하는 제2혼합단계(S4)를 진행하여, 다시 파우더 형태의 제2조성물을 획득한다.And a second mixture of 110 g of chlorinothyrolite in powder form, 110 g in powder form, 110 g in powder form, 50 g of granite porphyll in powder form, and 100 g of alkali silicate in powder form in the first composition after the drying step (S3). Proceed with the mixing step (S4), to obtain a second composition in the form of a powder again.

그 후, 상기 제2혼합단계(S4)를 거친 제2조성물을 압출성형장치를 사용하여 원형 형태로 가공하는 가공단계(S5)를 진행하여, 원형 형태로 가공된 제2조성물을 획득한다.Thereafter, the second composition passed through the second mixing step (S4) is processed in a circular shape by using an extrusion molding apparatus (S5) to obtain a second composition processed in a circular shape.

마지막으로, 상기 가공단계(S5)에 의해 특정한 모양으로 형성된 제2조성물을 소결로를 사용하여 850℃의 온도로 6시간 동안 가열하는 소결단계(S6)를 진행하여, 소결된 중금속함유 광산 폐수 및 하·폐수처리를 위한 고정화 담채를 획득한다.Finally, the sintering step (S6) of heating the second composition formed in a specific shape by the processing step (S5) for 6 hours at a temperature of 850 ℃ using a sintering furnace, the sintered heavy metal-containing mine wastewater and Acquire immobilized tin for sewage and wastewater treatment.

이렇게 구성된 본 발명은 3가지 종류의 시료를 A그룹으로 정하여, 종래의 활성탄이 실시된 정화장치를 통해 정화한 후의 시료 속에 포함된 성분의 양과, 그 A그룹과 동일한 시료를 B그룹으로 정하여, 본 발명이 실시된 정화장치를 통해 정화한 후의 시료 속에 포함된 성분의 양을 대비한 표1과 같이,The present invention configured as described above defines three types of samples as group A, the amount of components contained in the sample after purification through a purification apparatus in which activated carbon is applied, and the same sample as the group A as group B, As Table 1 compares the amount of the components contained in the sample after purification through the purification device according to the invention,

[표 1]TABLE 1

성분/그룹   Ingredient / Group A그룹  A group B그룹  B group 제1 시료  First sample 제2 시료 Second sample 제3 시료 Third sample 제1 시료 First sample 제2 시료 Second sample 제3 시료 Third sample pH (PPM) pH (PPM) 3.34 3.34 3.53 3.53 3.44 3.44 3.34 3.34 3.53 3.53 3.44 3.44 COD (㎎/ℓ) COD (mg / L) 10.58 10.58 7.5 7.5 15.28  15.28 0.21 0.21 0.075 0.075 0.15 0.15 알루미늄 (㎎/ℓ) Aluminum (mg / l) 19 19 15 15 14.8 14.8 0.38 0.38 0.15 0.15 0.44 0.44 카드뮴 (㎎/ℓ) Cadmium (mg / l) 0.22 0.22 0.24 0.24 0.25 0.25 0.008 0.008 0.009 0.009 0.013 0.013 구리 (㎎/ℓ) Copper (mg / l) 4 4 3 3 5 5 0.6 0.6 0.12 0.12 0.1 0.1 비소 (㎎/ℓ) Arsenic (mg / l) 0.489 0.489 0.191 0.191 0.21 0.21 0.04 0.04 0.026 0.026 0.27 0.27 철 (㎎/ℓ) Iron (mg / l) 149 149 202 202 221 221 1.49 1.49 4.04 4.04 11.05 11.05 망간 (㎎/ℓ) Manganese (mg / ℓ) 59 59 79 79 82 82 4.13 4.13 5.53 5.53 16.4 16.4 아연 (㎎/ℓ) Zinc (mg / l) 14  14 27  27 29  29 0.28 0.28 3.51 3.51 1.16 1.16 칼슘 (㎎/ℓ) Calcium (mg / L) 394 394 476 476 484 484 3.94 3.94 66.64 66.64 16.94 16.94 마그네슘 (㎎/ℓ) Magnesium (mg / l) 142 142 174 174 178 178 18.46 18.46 12.18 12.18 5.7 5.7

중금속 처리효율 자체가 높은 효과가 있고, 분말형태로 혼합되고 다시 가열되며, 또다시 혼합되고 건조됨에 따라, 모스경도가 7 이상으로 향상되어 비표면적을 형성하는 다공성 발포공간이 유지되고, 폐수의 높은 pH농도에서도 중금속을 정 화하는 처리유지되어 폐수에 포함된 중금을 정화하는 처리효율이 대폭 높아지는 효과가 있다.As the heavy metal treatment efficiency itself has a high effect, and mixed and dried in powder form, mixed and dried again, the Mohs hardness is improved to 7 or more to maintain a porous foam space to form a specific surface area, high waste water Even at pH concentration, the treatment to clean heavy metals is maintained, and the treatment efficiency to purify heavy metals contained in wastewater is greatly increased.

도 1은 본 발명의 공정도를 도시한 도면.1 is a process diagram of the present invention.

Claims (3)

중금속이 포함된 폐수처리용 담채에 있어서,In the wastewater treatment tin containing heavy metal, 무연탄 10중량% 내지 20중량%와 활성탄 20중량% 내지 30중량%, 백탄 30중량% 내지 36중량%, 크리노프티로라이트 7중량% 내지 15중량%, 몰데나이트 7중량% 내지 15중량%, 그라니트포필리 2.5중량% 내지 7.5중량% 및 알칼리실리케이트 5중량% 내지 15중량%로 구성된 중금속함유 광산 폐수 및 하·폐수처리를 위한 고정화 담채.10% to 20% by weight of anthracite coal, 20% to 30% by weight of activated carbon, 30% to 36% by weight of charcoal, 7% to 15% by weight of crinophthyriteite, 7% to 15% by weight of mordenite, Immobilized tin for heavy metal-containing mine wastewater and sewage / wastewater treatment consisting of 2.5 wt% to 7.5 wt% of granite popphyli and 5 wt% to 15 wt% of alkali silicate. 제 1항에 있어서,The method of claim 1, 백탄 70중량% ~ 90중량%와 알칼리실리케이트 10중량% 내지 20중량%로 구성됨을 특징으로 하는 중금속함유 광산 폐수 및 하·폐수처리를 위한 고정화 담채.Immobilized tin for heavy metal-containing mine wastewater and sewage and wastewater treatment, characterized by consisting of 70% to 90% by weight of white coal and 10% to 20% by weight of alkali silicate. 폐수처리용 담채의 제조방법에 있어서,In the manufacturing method of the waste water treatment tin, 무연탄 10중량% 내지 20중량%와 활성탄 20중량% 내지 30중량% 및 백탄 30중량% 내지 36중량%을 혼합정련하여 파우더 형태의 제1조성물을 획득하는 제1혼합단계와;A first mixing step of mixing and refining 10% to 20% by weight of anthracite coal, 20% to 30% by weight of activated carbon, and 30% to 36% by weight of white coal to obtain a first composition in powder form; 상기 제1혼합단계를 거친 후, 그 제1조성물을 수세하고, 그 수세 된 제1조성물이 흡수한 수분이 증발하도록 가열건조하는 가열단계와;A heating step of washing the first composition after the first mixing step and heating and drying the water to absorb the water absorbed by the washed first composition; 상기 가열단계를 거친 후, 그 제1조성물에 질산용액으로 다시 수세하고, 그 수세 된 제1조성물이 흡수한 수분이 증발하도록 자연건조하는 건조단계와;After the heating step, the first composition is washed with the nitric acid solution again, the drying step of natural drying so that the water absorbed by the washed first composition evaporates; 상기 건조단계를 거친 후, 그 제1조성물에 크리노프티로라이트 7중량% 내지 15중량%와 몰데나이트 7중량% 내지 15중량%, 그라니트포필리 2.5중량% 내지 7.5중량% 및 알칼리실리케이트 5중량% 내지 15중량%로 혼합하여 제2조성물을 획득하는 제2혼합단계와;After the drying step, 7 wt% to 15 wt% of chrynophthyrolite and 7 wt% to 15 wt% of mordenite, 2.5 wt% to 7.5 wt% of granite pophili, and alkali silicate 5 in the first composition A second mixing step of obtaining a second composition by mixing by weight to 15% by weight; 상기 제2혼합단계를 거친 후, 성형장치를 통해 제2조성물을 특정 형태로 가공하는 가공단계와;A processing step of processing the second composition into a specific form through a molding apparatus after the second mixing step; 상기 가공단계를 거친 후, 소결로를 통해 제2조성물을 800℃ 내지 900℃의 온도로 5시간 내지 7시간 소결하는 소결단계로 구성됨을 특징으로 하는 중금속함유 광산 폐수 및 하·폐수처리를 위한 고정화 담채의 제조방법.After the processing step, the sintering step of sintering the second composition at a temperature of 800 ℃ to 900 ℃ 5 hours to 7 hours through the sintering furnace, characterized in that the immobilization for the treatment of heavy metal-containing mine wastewater and sewage and waste water Method of making tin
KR20080038998A 2008-04-25 2008-04-25 Immobilized tin and its manufacturing method for the treatment of heavy metal-containing mine wastewater and sewage and wastewater (Method of immobilized tin and its CAPH) KR100874197B1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
KR20080038998A KR100874197B1 (en) 2008-04-25 2008-04-25 Immobilized tin and its manufacturing method for the treatment of heavy metal-containing mine wastewater and sewage and wastewater (Method of immobilized tin and its CAPH)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
KR20080038998A KR100874197B1 (en) 2008-04-25 2008-04-25 Immobilized tin and its manufacturing method for the treatment of heavy metal-containing mine wastewater and sewage and wastewater (Method of immobilized tin and its CAPH)

Publications (2)

Publication Number Publication Date
KR20080042788A true KR20080042788A (en) 2008-05-15
KR100874197B1 KR100874197B1 (en) 2008-12-15

Family

ID=39649363

Family Applications (1)

Application Number Title Priority Date Filing Date
KR20080038998A KR100874197B1 (en) 2008-04-25 2008-04-25 Immobilized tin and its manufacturing method for the treatment of heavy metal-containing mine wastewater and sewage and wastewater (Method of immobilized tin and its CAPH)

Country Status (1)

Country Link
KR (1) KR100874197B1 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100915958B1 (en) * 2008-06-24 2009-09-10 주식회사 루미라이트 Eco-friendly active natural mineral water quality improvement composition and its manufacturing method

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2556110Y2 (en) 1991-03-08 1997-12-03 サングリーン商事株式会社 Composite porous carrier

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100915958B1 (en) * 2008-06-24 2009-09-10 주식회사 루미라이트 Eco-friendly active natural mineral water quality improvement composition and its manufacturing method
WO2009157681A3 (en) * 2008-06-24 2010-03-11 Lumilite Co., Ltd. Water quality improvement composition containing eco-friendly active natural minerals and method of manufacturing the same

Also Published As

Publication number Publication date
KR100874197B1 (en) 2008-12-15

Similar Documents

Publication Publication Date Title
Chiban et al. Single, binary and multi-component adsorption of some anions and heavy metals on environmentally friendly Carpobrotus edulis plant
Katsou et al. Use of ultrafiltration membranes and aluminosilicate minerals for nickel removal from industrial wastewater
Yin et al. Dual removal of phosphate and ammonium from high concentrations of aquaculture wastewaters using an efficient two-stage infiltration system
KR101409721B1 (en) Biochar-Alginate bead for removal of heavy metal using biochar powder and the method of manufacturing the same
US10173213B2 (en) Particulate medium prepared from partially decomposed organic matter for selective sorption between competing metal ions in aqueous solutions
US10118154B2 (en) Particulate sorption medium prepared from partially decomposed organic matter
KR101415656B1 (en) adsorbent for adsorption treatment of anion in waste water, and method for manufacturing the adsorbent
Sizirici et al. Adsorptive removal capacity of gravel for metal cations in the absence/presence of competitive adsorption
Li et al. Activation of Firmiana simplex leaf and the enhanced Pb (II) adsorption performance: equilibrium and kinetic studies
EP2969970A2 (en) Particulate sorption medium prepared from partially decomposed organic matter
Chowdhury et al. Zeolite for nutrient stripping from farm effluents
Letshwenyo et al. Phosphorus removal from secondary wastewater effluent using copper smelter slag
Mandoreba et al. Defluoridation of drinking water using a ceramic filter decorated with iron oxide‐biochar composites
WO2017147384A1 (en) Particulate medium prepared from partially decomposed organic matter for selective sorption between competing metal ions in aqueous solutions
Wang et al. Removal of nitrate from constructed wetland in winter in high-latitude areas with modified hydrophyte biochars
KR100874197B1 (en) Immobilized tin and its manufacturing method for the treatment of heavy metal-containing mine wastewater and sewage and wastewater (Method of immobilized tin and its CAPH)
Shah et al. Waste water treatment-bed of coal fly ash for dyes and pigments industry
Zhang et al. Heavy metal adsorption of a novel membrane material derived from senescent leaves: Kinetics, equilibrium and thermodynamic studies
Sõukand et al. Selection of adsorbents for treatment of leachate: batch studies of simultaneous adsorption of heavy metals
Helard et al. Removal of nitrate from groundwater by column using pumice as adsorbent as an effort for water resources conservation
KR100863755B1 (en) Composition comprising gadolinium oxide and water filtering method using the same
Balkaya et al. Influence of operating parameters on lead removal from wastewater by phosphogypsum
CN101049997A (en) Silicon dioxide adulterated composite material of humic acid and calcium, preparation method and application
Tilaki et al. Removal of ammonium ions from water by raw and alkali activated Bentonite
Nassef Thermodynamics and kinetic study of using modified clay as an adsorbent for the removal of Zn ions from waste water

Legal Events

Date Code Title Description
A201 Request for examination
A302 Request for accelerated examination
E902 Notification of reason for refusal
E701 Decision to grant or registration of patent right
GRNT Written decision to grant
LAPS Lapse due to unpaid annual fee