KR940010114B1 - Method for the preparation iron oxide microparticles - Google Patents
Method for the preparation iron oxide microparticles Download PDFInfo
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- KR940010114B1 KR940010114B1 KR1019910022606A KR910022606A KR940010114B1 KR 940010114 B1 KR940010114 B1 KR 940010114B1 KR 1019910022606 A KR1019910022606 A KR 1019910022606A KR 910022606 A KR910022606 A KR 910022606A KR 940010114 B1 KR940010114 B1 KR 940010114B1
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- C01—INORGANIC CHEMISTRY
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- C01G49/00—Compounds of iron
- C01G49/02—Oxides; Hydroxides
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Abstract
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Description
본 발명은 강의 산세 폐액과 크롬 도금 폐기스러지를 합성하여 내열성 흑갈색 합성산화철 미립자를 제조하는 방법에 관한 것이다. 제강업계에서는 제품의 물성을 향상시킬 목적으로 강을 가공하기 전에 강제표면의 산화철을 제거하여야 하는 바 이에는 산세 처리방식이 널리 이용하고 있으며, 여기에서 발생하는 산세폐액은 다음 방정식으로 생성되어 식수, 지하수 또는 해수등을 오염시키는 원인이 되고 있다.The present invention relates to a method for producing heat-resistant dark brown synthetic iron oxide fine particles by synthesizing pickling waste liquid and chromium plating waste of steel. In the steel industry, it is necessary to remove iron oxide from the steel surface before machining steel for the purpose of improving the properties of the product. The pickling treatment method is widely used. It causes pollution of groundwater or seawater.
Fe-산화물+…………………………………(1)Fe-oxide + … … … … … … … … … … … … … (One)
Fe-산화물+…………………………………(2)Fe-oxide + … … … … … … … … … … … … … (2)
강의 산세 처리시 주로(1)식과 같이 반응하며 극히 소량이 (2)식과 같이 반응하는데 보통 8-12%철을 용해한 폐액이 발생한다. 더욱이 이때 반응이 정 방향으로 촉진시켜 산세속도를 향상시키기 위하여 과잉의 산이 요구되므로 보통의 경우 과잉의 산이 8-10% 잔존하여 폐액이 발생한다. 한편 강재의 수명 연장을 위하여 강재표면에 크롬도금을 실시하는 업계에서는 6가크롬을 산성용액중에 사용한다. 그러나 도금이 진행되는 동안 크롬 도금액중에 피도금체 성분 Fe등이 용해 혼입되기 쉬우며 그 혼입량이 일정치 이상이 되면 도금의 성능은 곤란하게 된다.During the pickling process of steel, it reacts mainly in the formula (1) and very small amount reacts in the formula (2). Moreover, since the acid is required in order to accelerate the reaction in the forward direction and improve the pickling rate, in general, 8 to 10% of the excess acid remains and waste liquid is generated. On the other hand, hexavalent chromium is used in acid solution in the industry where chromium plating is applied to steel surface to extend the life of steel. However, the plating component Fe and the like are easily dissolved and mixed in the chromium plating solution during the plating process, and the plating performance becomes difficult when the amount of the mixture is more than a predetermined value.
이러한 과정에서 6가크롬 및 피도금체 성분인 Fe등이 용해된 도금 폐액이 발생된다. 이 도금 폐액중 6가 크롬은 극도로 위험한 독극성이 있으므로 다음(3),(4),(5)식과 같이 수용액중에서 아황산 가스, 아황산 소다등과 같은 환원제로 크롬을 6가에서 3가로 환원한 다음 NaOH, Ca(OH)2등과 같은 알카리로 반응시켜 크롬을 Cr(OH)3의 크롬수산화물로 철을 Fe(OH)2로 침전 분리시켜 스러지 상태의 폐기물이 발생한다.In this process, a plating waste liquid in which hexavalent chromium and Fe, which is a component to be plated, are dissolved, is generated. Since hexavalent chromium is extremely dangerous in this plating waste, chromium was reduced from hexavalent to trivalent by reducing agents such as sulfurous acid gas and sodium sulfite in aqueous solution as shown in the following formulas (3), (4) and (5). Next, by reacting with alkali such as NaOH, Ca (OH) 2 and the like, chromium is precipitated and separated into Fe (OH) 2 with chromium hydroxide of Cr (OH) 3 to generate waste of sludge.
H2Cr2O7+3Na2SO3+3H2SO4………Cr2(SO4)3+3Na2SO4+4H2O ……(3)H 2 Cr 2 O 7 +3 Na 2 SO 3 + 3H 2 SO 4 ... … … Cr 2 (SO 4 ) 3 +3 Na 2 SO 4 + 4H 2 O... … (3)
Cr2(SO4)3+6NaOH …………………2Cr(OH)3+3Na2SO4……………(4)Cr 2 (SO 4 ) 3 +6 NaOH. … … … … … … 2Cr (OH) 3 + 3Na 2 SO 4 ... … … … … (4)
Fe(SO4)+2NaOH ……………………Fe(OH)2+Na2SO4………………(5)Fe (SO 4 ) + 2 NaOH... … … … … … … … Fe (OH) 2 + Na 2 SO 4 ... … … … … … (5)
이 폐기스러지에는 (3), (4), (5)식과 같이 Cr이 2-6%, Fe가 1-3%, 수분이 80-92%이 함유되어 발생한다. 이와 같이 주로 (1), (2), (3), (4), (5)식과 같이 생성된 강의 산세폐액과 크롬 도금 폐기 스러지는 중금속 공해의 원인이 된다.This waste is generated by containing 2-6% of Cr, 1-3% of Fe and 80-92% of water as in the formulas (3), (4) and (5). Thus, pickling liquor and chromium plating waste of steel produced as in the following formulas (1), (2), (3), (4) and (5) mainly cause heavy metal pollution.
본 발명은 위와 같은 강의 산세폐액과 크롬도금폐기스러지에 의한 중금속 공해를 방지하고 이들 폐기물들을 합성 가공하여 부가가치가 높은 내열 흑갈색의 합성산화철 미립자를 제조하는 방법에 관한 것이다. 강의 산세폐액에는 주로 2가 Fe 이온과 극히 일부의 3가 Fe 이온으로 구성되어 있으며 크롬도금 폐기스러지에는 주로 Cr(OH)3와 일부의 Fe(OH)2로 구성되어 있다. 이 두 폐기물을 혼합함에 있어 Cr/Fe 성분비를 중량비로 12-25%이 되도록 혼합교반한 후 KOH, NaOH 및 Ca(OH)2, NH4OH등의 알카리(OH-) 용액을 첨가하여 pH 7-8로 조절하여 위 두 폐기물중 중금속 성분을 침전분리 한다. 침전물을 대기중에서 20-90℃의 낮은 온도로 가열, 연소 및 건조를 행함으로서 극미립의 내열성 흑갈색의 합성산화철 미립자를 얻는다. 이상과 같이 얻어진 미립자는 1,000℃까지 흑갈색이 변색되지 않는 내열성을 갖으며 흑갈색의 파장 680-700㎚에서 11.0-12.5%의 반사율을 갖는다. 그 입도는 0.08-0.30㎛의 범위를 갖는다.The present invention relates to a method for producing heavy added heat-resistant dark brown synthetic iron oxide fine particles by preventing heavy metal pollution caused by pickling waste liquid and chromium plating waste of steel as described above and by synthetically processing these wastes. The pickling liquor of steel consists mainly of divalent Fe ions and very few trivalent Fe ions, while the chromium plating waste consists mainly of Cr (OH) 3 and some Fe (OH) 2 . After being stirred mixture so that the two waste as it mixed with 12-25% of the Cr / Fe ratio by weight component ratio KOH, NaOH and Ca (OH) 2, NH 4 OH , such as alkali (OH -) in a pH 7 by addition of a solution Set to -8 to sediment and separate heavy metals from the two wastes. The precipitate is heated, burned, and dried in the air at a low temperature of 20-90 ° C. to obtain ultrafine heat resistant dark brown synthetic iron oxide fine particles. The microparticles | fine-particles obtained as mentioned above have heat resistance which does not discolor black-brown to 1,000 degreeC, and has the reflectance of 11.0-12.5% at the wavelength of 680-700 nm of black-brown. The particle size is in the range of 0.08-0.30 µm.
여기서 두 폐기물을 혼합할 때 Cr/Fe비가 12% 이하는 최종침전물의 갈색이 쇄퇴하여 적색이 되기 쉽고 25% 이상은 갈색이 쇄퇴하여 녹색이 되기 쉽다. 그리고 두 폐기물 혼합 후 pH 7 이하에서는 Fe,Cr이 용해, pH 8 이상에서는 Cr이 용해하기 쉬워 수질 오염의 공해문제를 다시 발생할 수 있다.When mixing the two wastes, brown of the final precipitate having a Cr / Fe ratio of 12% or less decays and becomes red, and 25% or more of brown decays and green. After mixing the two wastes, Fe and Cr are dissolved at a pH below 7 and Cr is easily dissolved at a pH above 8, which may cause pollution problems of water pollution.
본 발명은 강의 산세폐액과 크롬도금폐기 스러지를 혼합가공하여 부가가치가 높은 내열성 흑갈색의 합성 산화철 미립자 소재로 제조함으로서 폐기물 발생기업의 폐기물 처리를 강화할 수 있을 뿐만 아니라 외국으로부터 수입에 의존하고 있는 내열성 흑갈색 산화철 미립자를 국산화함으로서 외화 절감효과도 얻을 수 있을 뿐만아니라 날로 심각하게 부상하고 있는 국내의 환경 보전의 문제중 중금속 오염의 공해문제를 근본적으로 해결할 수 있는 매우 유용한 발명인 것이다.The present invention is made of a high value-added heat-resistant dark brown synthetic iron oxide fine particles by mixing and processing steel pickling waste liquid and chromium-plated waste sludge, which not only enhances waste treatment of waste generating companies but also relies on imports from foreign countries. Localization of the fine particles not only can reduce foreign currency, but it is also a very useful invention that can fundamentally solve the pollution problem of heavy metal pollution among the problems of environmental preservation in Korea.
[실시예]EXAMPLE
강의 산세폐액과 크롬도금 폐기 스러지를 혼합함에 있어서 Cr/Fe의 혼합비를 중량비로 18% 되도록 혼합 교반시킨 후 KOH, NaOH, 및 Ca(OH)2, NH4OH등의 알카리(OH-) 용액을 첨가하여 pH 7로 조절하여 이들 폐기물중 중금속 성분을 침전 분리한다. 침전물을 200℃에서 대기중 가열 연소하여 내열성 흑갈색의 합성 산화철 미립자를 얻는다.In mixing the pickling liquid of the steel and the chromium plating waste sludge, the mixing ratio of Cr / Fe is mixed to 18% by weight, followed by stirring with alkaline (OH − ) solutions such as KOH, NaOH, Ca (OH) 2 , and NH 4 OH. By adding to pH 7 to precipitate and separate heavy metals from these wastes. The precipitate is heated and burned in air at 200 ° C. to obtain heat-resistant dark brown synthetic iron oxide fine particles.
이 미립자는 1,000℃까지 흑갈색이 변색되지 않는 내열성을 갖으며 흑갈색의 파장 700㎚에서 11.0-12.5%의 반사율을 갖는다.These fine particles have heat resistance that black brown does not discolor until 1,000 ° C., and has a reflectance of 11.0-12.5% at a wavelength of 700 nm of black brown.
그 입도는 0.08-0.30㎛의 미립자가 얻어진다. 한편 이때 생성된 상등액중의 잔유 중금속 성분은 표1에 표시한 바와 같이 정화되었으며 그외의 금속성분은 검출되지 않았다. 이 결과는 표1의 밑에 표시한 현행 환경보전상의 허용치 보다 훨씬 낮은 값으로 우수하게 수질을 정화할 수 있다. 따라서 본 방법에 의해 생성되는 방류수는 환경 보전에 문제점이 없다.Particle size of 0.08-0.30 µm is obtained. Meanwhile, the residual heavy metal component in the supernatant produced was purified as shown in Table 1, and no other metal components were detected. This result is excellent in purifying water quality to a value much lower than the current environmental conservation allowances indicated in Table 1 below. Therefore, the effluent produced by the present method has no problem of environmental conservation.
[표 1] 상등액중의 잔류 중금속 함량(ppm)Table 1 Residual Heavy Metal Content in Supernatant (ppm)
수질환경보전법상의 허용치(환경관련 벌령집 제40조, 방류수 수질기준, 1995년 12월 31일까지 허용)Permissible value under the Water Quality Preservation Act
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KR1019910022606A KR940010114B1 (en) | 1991-12-11 | 1991-12-11 | Method for the preparation iron oxide microparticles |
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KR940010114B1 true KR940010114B1 (en) | 1994-10-21 |
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