JPH05345658A - Pollution-free sintered ceramic of soluble chromic acid salt and its production - Google Patents

Pollution-free sintered ceramic of soluble chromic acid salt and its production

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Publication number
JPH05345658A
JPH05345658A JP4197373A JP19737392A JPH05345658A JP H05345658 A JPH05345658 A JP H05345658A JP 4197373 A JP4197373 A JP 4197373A JP 19737392 A JP19737392 A JP 19737392A JP H05345658 A JPH05345658 A JP H05345658A
Authority
JP
Japan
Prior art keywords
weight
less
pollution
soluble chromate
soluble
Prior art date
Legal status (The legal status 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 status listed.)
Pending
Application number
JP4197373A
Other languages
Japanese (ja)
Inventor
Hideo Igami
英雄 居上
Chisato Ota
千里 太田
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
KUREE BAAN CERAMICS KK
Original Assignee
KUREE BAAN CERAMICS KK
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 KUREE BAAN CERAMICS KK filed Critical KUREE BAAN CERAMICS KK
Priority to JP4197373A priority Critical patent/JPH05345658A/en
Publication of JPH05345658A publication Critical patent/JPH05345658A/en
Pending legal-status Critical Current

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  • Processing Of Solid Wastes (AREA)
  • Compositions Of Oxide Ceramics (AREA)

Abstract

PURPOSE:To obtain a pollution-free sintered ceramic of a soluble chromic acid salt by compounding a substance containing a soluble chromic acid salt with a slag, a hydraulic cement, a silicate and a carbonaceous material at specific ratios and sintering the mixture. CONSTITUTION:A raw material mixture is produced by compounding 30-70wt.% of a substance containing a soluble chromic acid salt (e.g. waste of chromium refractory and smelting residue of chromium ore) with 4-20wt.% of slag, 5-15wt.% of a hydraulic cement, 13-37wt.% of a silicate (e.g. fly ash) and 0-6wt.% of a carbonaceous material (e.g. coal). The weight ratio of the carbonaceous material to the soluble chromic acid salt is 5-10 or above. The mixture is incorporated with 0.01-0.03 pts.wt. (based on the carbonaceous material) of Al and/or Si carbides. The obtained mixture is hydrated, kneaded, optionally cured in wet atmosphere, press-formed, dried and burnt in a strongly reducing flame atmosphere for >=1hr up to 1000 deg.C in the temperature-increasing stage and, thereafter, in a normal reducing flame atmosphere at 1000-1300 deg.C for 1-2hr.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、公害の原因となる有害
な可溶性クロム化合物を含有する有害廃棄物を不溶性か
つ無公害化し、有用材料とする環境保全に関する分野で
ある。具体的には、マグネシアクロム耐火物としてセメ
ントキルンガラス窯炉に使用された使用済み廃棄れん
が、クロム化学工場の抽出残渣等、可溶性のクロム酸並
にクロム酸塩類を含有する有害物を無公害材料とした安
定化焼結セラミックスとその製造法に関するものであ
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the field of environmental protection in which harmful waste containing a harmful soluble chromium compound that causes pollution is rendered insoluble and non-polluting to be a useful material. Specifically, used waste bricks used in cement kiln glass kiln as magnesia chrome refractory, extractable residue of chrome chemical factory, etc., and toxic substances containing soluble chromic acid as well as chromates are pollution-free materials. The present invention relates to the stabilized sintered ceramics and the manufacturing method thereof.

【0002】[0002]

【従来の技術】[Prior Art]

(1)クロム化合物中特に、4価、5価、6価のクロム
酸塩類は、有害であるので、安全である3価の酸化クロ
ムとすることが従来種々試みられたが、技術上種々の難
点があった。 (2)可溶性クロム酸並にその塩類の処理は、不溶性
化、吸着法、融着法、等が考案され、実施されている。 i)第1の従来技術 不溶性化としては、還元焙焼して不溶性の酸化クロム
(Cr)に還元する。 ii)第2の従来技術 廃棄物中の可溶性クロム酸並にその塩類を主として無機
質吸着材に吸着させたもの並に/又は廃棄マグクロれん
が等は粉砕した後にポルトランドセメントを加えてセメ
ント水和物内にCrイオンを吸着せしめ硬化させる。こ
れらの硬化物はセメントブロックとして使用する。 iii)第3の従来技術 可溶性クロム酸塩類を含む廃棄物をガラス屑等と混合溶
融しガラス材料とする。
(1) Among chromium compounds, in particular, tetravalent, pentavalent, and hexavalent chromates are harmful, so various attempts have been made to make safe trivalent chromium oxides. There were difficulties. (2) For the treatment of soluble chromic acid and its salts, insolubilization, adsorption method, fusion method and the like have been devised and implemented. i) First Prior Art As insolubilization, reduction roasting is performed to reduce insoluble chromium oxide (Cr 2 O 3 ). ii) Second conventional technique Soluble chromic acid in waste and its salts are adsorbed mainly on an inorganic adsorbent and / or waste mag bricks are crushed and then Portland cement is added to the cement hydrate. Cr ions are adsorbed on and cured. These cured products are used as a cement block. iii) Third Prior Art A waste material containing soluble chromates is mixed with glass scraps and melted to obtain a glass material.

【0003】[0003]

【本発明の目的:解決すべき問題点】第1の従来技術で
ある還元焙焼法では、確かに一応は、安定したCr
にすることは可能である。しかし、クロム系耐火物の
廃棄物などでは多種多様な4価、5価、6価などの可溶
性クロム酸塩を含有しており,特にセメントキルンの内
張として使用された耐火物にはKSO、KCl、N
SOなどのアルカリ類と様々な化学結合をしてお
り、此等がクロムスピネルの表面や空隙部にクロム塩と
して生成している為、そのまま還元焙焼しても完全に不
溶化する事は困難であるという欠点がある。第2の従来
技術は、従来、広く採用されている方法であるが、ポル
トランドセメントなどの水硬性セメント類と混合して、
セメントの水和反応で生成するアルミイオンとイオン交
換して水和物として固定し硬化させ不溶化してコンクリ
ートブロック等に使用する方法であるがセメント生硬化
体は炭酸化やアルカリ骨材反応などで中長期的に劣化し
て再び有害クロムイオンを溶出するおそれが大である、
という問題点がある。第3の従来技術は、可溶性クロム
酸塩を含む廃棄物のガラスと共に溶解してガラス内にク
ロムイオンを固定する方法であるが、長期的に水によっ
て溶解して行くものであり、特に酸性雨などの条件で
は、クロムイオンの溶出が起こるという欠点を有してい
る。
Object of the present invention: Problems to be solved In the reduction roasting method which is the first conventional technique, it is true that stable Cr 2 O
It is possible to set it to 3 . However, waste materials such as chromium-based refractory materials contain a wide variety of soluble salts of tetravalent, pentavalent, hexavalent, etc. In particular, the refractory used as the lining of the cement kiln contains K 2 SO 4 , KCl, N
Since it has various chemical bonds with alkalis such as a 2 SO 4 and these are formed as chromium salts on the surface and voids of the chromium spinel, they can be completely insolubilized even if they are directly reduced and roasted. Has the drawback of being difficult. The second prior art is a method that has been widely adopted in the past, but by mixing with hydraulic cements such as Portland cement,
It is a method of ion exchange with aluminum ions generated by the hydration reaction of cement, fixing it as a hydrate, hardening and insolubilizing it and using it for concrete blocks etc.Cement biohardening material is used for carbonation and alkali aggregate reaction etc. There is a great risk that it will deteriorate over the medium to long term and elute harmful chromium ions again.
There is a problem. The third prior art is a method of fixing chromium ions in the glass by dissolving it together with a waste glass containing soluble chromate, but it is a method of dissolving it with water for a long period of time, particularly acid rain. Under such conditions, there is a drawback that chromium ions are eluted.

【0004】本発明は、上記すべての従来技術の諸欠点
を除去して、幾つかの工程を経て、可溶性クロム酸塩を
中性酸化物であって化学的に安定し、酸性雨等によって
も分解しない、クロムスピネル固熔体に変換することに
より、不溶化、無公害化し、更にその上に第2次的利用
に使用しうる物とその製造方法とを創始し提供すること
を目的とする。
The present invention eliminates all the above-mentioned drawbacks of the prior art, and after several steps, the soluble chromate is a neutral oxide which is chemically stable and can be treated by acid rain. It is an object of the present invention to make insoluble and pollution-free by converting it into a chromium spinel solid solution which does not decompose, and further to establish and provide a material that can be used for secondary use and a manufacturing method thereof.

【0005】[0005]

【本発明の構成:課題解決の手段】上記目的を達成する
ための、本発明に係る焼結物の組成の特徴は、可溶性ク
ロム酸塩含有物30重量[%]以上70重量[%」以
下、スラグ4重量[%]以上20重量[%]以下、クロ
ムイオンを吸着する水硬性セメント成分5重量[%]以
上15重量[%]以下、珪酸塩質物13重量[%]以上
37重量[%]以下、及び、還元作用を行なう炭素質物
0重量[%]以上6重量[%]以下を成分とし、クロム
が安定化、不溶化かつ無公害化されていることである。
また、前記可溶性クロム酸塩含有物が、例としてクロム
系耐火物の廃棄物、及び/又は、クロム鉱精練残渣をそ
の成分の源とするものであることである。並に、本発明
のクロム無公害化焼結セラミックスの製造方法の特徴
は、無水換算で得られる原料配合物に、該原料配合物の
可溶性クロム酸塩に対し、重量で5倍以上10倍以下の
炭素質物及び、必要に応じ、該炭素質物の1/100重
量部以上、3/100重量部以下のAl,Si金属の1
種以上を添加配合し、加水混練し、必要に応じ、湿空養
生し、加圧成形、乾燥した後、昇温過程において、少な
くも1時間以上、1000[℃]までは強還元焔雰囲気
として、次に1000[℃]を超え1300[℃]以下
では、1時間以上、2時間以下、通常の還元焔雰囲気で
焼成することである。更に、上記無公害化焼結セラミッ
クスをより良く、より美しい状態で使用され安くするた
めの製造方法の特徴は、前記に記載の製造方法の各工程
後において、更に該焼結物を600[℃]以上900
[℃]以下の温度範囲で、かつ炭素微粒子を含む還元雰
囲気中で、燻化焼成を行なうことである。而して、前記
本発明の構成を技術理論的に説明する。先ず第1の要素
は、可溶性クロム酸塩と水硬性セメントに加水し、水和
反応により可溶性クロムイオンをAlイオンとイオン交
換させて、一時的に固定する従来技術の理論も一部使用
するが、本発明はスラグ 、石膏を用いて、一旦、多量
のセンイ状エトリンガイト(3CaO・CaSO・A
・nHO)を生成させて、前記のイオン交換
を完全に行なわせ焼成時の還元反応が迅速に起こり易い
状態とする。第2の要素は焼成過程に於て、上記、水和
物の脱水反応によって現われたCr+6イオンを発生機
の状態で最も効率よく還元する為の還元剤の選択をした
ことである。更に、構成原理の詳細な説明を加える。
Constitution of the present invention: Means for solving the problems In order to achieve the above object, the composition of the sintered product according to the present invention is characterized in that the content of the soluble chromate is 30% by weight or more and 70% by weight or less. , Slag 4% by weight or more and 20% by weight or less, hydraulic cement component that adsorbs chromium ions 5% by weight or more and 15% by weight or less, silicate material 13% by weight or more and 37% by weight ], And a carbonaceous substance that performs a reducing action in an amount of 0% by weight or more and 6% by weight or less, the chromium is stabilized, insolubilized, and made pollution-free.
In addition, the soluble chromate-containing material uses, for example, waste of a chromium-based refractory and / or a chrome ore refining residue as a source of its components. Similarly, the characteristic feature of the method for producing a chromium-free pollution-free sintered ceramics of the present invention is that the raw material mixture obtained on an anhydrous basis has a weight of 5 to 10 times the soluble chromate salt of the raw material mixture. 1 to 100 parts by weight or more and 3/100 parts by weight or less of Al and Si metal of 1 to 100 parts by weight of the carbonaceous material
After adding and blending at least one species, hydro-kneading, if necessary, curing in humid air, pressure molding, and drying, in the temperature rising process, a strong reducing flame atmosphere is maintained for at least 1 hour or more, up to 1000 [° C]. Next, when the temperature exceeds 1000 [° C.] and 1300 [° C.] or less, the firing is performed in a normal reducing flame atmosphere for 1 hour or more and 2 hours or less. Furthermore, the characteristic of the manufacturing method for using the pollution-free sintered ceramics in a better, more beautiful state and at a lower price is that after each step of the manufacturing method described above, the sintered product is further heated to 600 [° C. ] Over 900
Sintering is performed in a temperature range of [° C.] or less and in a reducing atmosphere containing carbon fine particles. The structure of the present invention will be described theoretically. First, the first element uses a part of the theory of the prior art in which soluble chromate and hydraulic cement are hydrolyzed, and soluble chromium ions are ion-exchanged with Al ions by a hydration reaction to temporarily fix them. The present invention uses slag and gypsum to once produce a large amount of senyi-like ettringite (3CaO · CaSO 4 · A).
(1 2 O 3 .nH 2 O) is generated to completely carry out the above-mentioned ion exchange so that the reduction reaction during firing is likely to occur quickly. The second factor is that, in the firing process, the reducing agent was selected so as to most efficiently reduce the Cr +6 ion, which was generated by the dehydration reaction of the hydrate, in the state of the generator. Furthermore, a detailed description of the configuration principle will be added.

【請求項1】の材料組成物に於て可溶性クロム酸塩を含
む無機質の原料として30[%]〜70[%]の範囲を
選んだのは、一般の対称廃棄物に於てはCrO即ち、
Cr+6の含有量は0.1[%]〜2.0[%]の範囲
であり、組成物に30[%]以下の配合の場合は、廃棄
物処理の有害廃棄物の基準範囲外となる場合もあり、上
限を70[%]としたのは焼結体を造る上での結合剤や
還元剤の合計量が30[%]以下では、工業的に焼結体
製品の製造時の成形や焼成条件を満たさない。スラグ
は、水硬性セメント類と併用して水和時のエトリンガイ
トの生成、或は、Na.K.などのアルカリ塩水溶液な
どと反応してエトリンガイトの生成が起こるものであ
る。更に、焼成過程に於て800〜1000[℃]の結
晶化による発熱反応により焼成時間を短くして生産性を
高め、又、クロム質耐火物と反応して焼結温度を低下さ
せる作用を有し、更にスラグ中に0.2〜1.0[%]
含有するカーボンやイオウ(S)の高温域の還元作用も
有効に活用出来る成分であり、現成分としては、セメン
ト含有率と逆比例的に増減して結成を調整するものであ
るが、スラグが20[%]を超えると焼結温度が高くな
り経済的に好ましくなく、10〜15[%]の範囲が好
ましい範囲である。水硬性セメント類はポルトランドセ
メント、高炉セメント、アルミナセメントなど石膏を含
むものであり、15[%]以上含むと焼結体の強度特性
が低下する。又、4[%]以下の場合はスラグを多く併
用しても水渣からのエトリンガイトの生成が遅くなり生
産性が低下する。炭素質物は木材、紙、でんぷんなどの
有機質のものを使用することも出来るが此等の材料は焼
成過程に於いて組織内の還元状態を保持する温度範囲が
狭く発生期のCr+6と還元作用をさせる管理が困難で
あり、本発明に於ては種々実験の結果、石炭、コーク
ス、グラファイトなどの炭素質物が有効である。特に、
石炭灰(フライアッシュ)などの様に珪酸塩ガラス質と
一部反応固着したり、スラグの様にガラス質組織内に封
入されている炭素質物は発生機のCr+6を高温サイド
に於て効果的な還元作用を行なうことを発明した。猶、
炭素質物の炭素としての含有量はCrOなど可溶性ク
ロム酸塩の含有量によって調整し、焼結過程に於て、焼
成体表面部で酸化消失するロス分を見込んでCrO
有量の5〜10倍が必要である。なお、10%以上の過
剰の含有は焼結体の物性上好ましくないものである。
又、還元剤として金属AlやMg、或はイオン(S)を
加えることも、本発明の技術的範囲内である。
1. In the material composition of claim 1, the range of 30 [%] to 70 [%] is selected as the inorganic raw material containing soluble chromate, and it is because CrO 3 in general symmetrical waste is selected. That is,
The content of Cr +6 is in the range of 0.1 [%] to 2.0 [%], and when the composition is less than 30 [%], it is out of the standard range of hazardous waste for waste treatment. In some cases, the upper limit is set to 70 [%] when the total amount of the binder and the reducing agent for making a sintered body is 30 [%] or less, which is industrially used when manufacturing a sintered body product. Does not meet molding and firing conditions. Slag is used in combination with hydraulic cements to form ettringite upon hydration, or Na. K. Etlingite is produced by reacting with an aqueous solution of an alkaline salt such as. Further, in the firing process, the exothermic reaction due to crystallization at 800 to 1000 [° C.] shortens the firing time to improve the productivity, and also has the effect of reacting with the chrome refractory to lower the sintering temperature. And 0.2 to 1.0 [%] in the slag
It is a component that can also effectively utilize the reducing action of the contained carbon and sulfur (S) in the high temperature range. As the current component, the composition is adjusted in inverse proportion to the cement content, but the slag is If it exceeds 20%, the sintering temperature becomes high, which is economically unfavorable, and the range of 10 to 15% is a preferable range. Hydraulic cements include gypsum, such as Portland cement, blast furnace cement, and alumina cement, and if it is contained in an amount of 15% or more, the strength characteristics of the sintered body deteriorate. If it is 4% or less, the production of ettringite from the water residue is delayed and the productivity is lowered even if a large amount of slag is used together. As the carbonaceous material, organic materials such as wood, paper, and starch can be used, but these materials have a narrow temperature range for maintaining the reduced state in the tissue during the firing process and Cr +6 in the nascent stage and the reducing action. However, as a result of various experiments, carbonaceous substances such as coal, coke and graphite are effective in the present invention. In particular,
The carbonaceous material that partially reacts with silicate glass such as coal ash (fly ash), and the carbonaceous material enclosed in the glassy structure such as slag is effective with Cr +6 of the generator on the high temperature side. Invented to carry out a reduction action. Grace
The content of the carbon in the carbonaceous material is adjusted depending on the content of soluble chromates such as CrO 3, At a sintering process, 5 of CrO 3 content in anticipation of loss in the loss oxidized in the baking surface portion You need 10 times. An excessive content of 10% or more is not preferable in terms of physical properties of the sintered body.
It is also within the technical scope of the present invention to add metal Al, Mg, or ions (S) as a reducing agent.

【請求項3】は、廃棄物中に存在する可溶性クロム酸塩
で不動態の形で存在するものは、600[℃]以下の還
元温度範囲では完全な安定化が出来上がっている場合も
あり、この場合、Alなどの金属を少量添加して高温サ
イドへ還元域を広げる事により効果的であったことによ
る。猶、還元作用をより安定化するため1000[℃]
迄は強還元雰囲気で焼成する。
3. The soluble chromate present in the waste, which exists in a passive form, may be completely stabilized in the reduction temperature range of 600 [° C.] or lower, In this case, it is effective to add a small amount of metal such as Al to expand the reduction region to the high temperature side. 1,000 [℃] to stabilize the reducing action
Until it is baked in a strong reducing atmosphere.

【請求項4】は一般的にいぶし瓦の技法とて知られる燃
料生ガスによる燻化処理を施して、焼結体全部を炭素質
の被膜で包んだ状態としてより完全な不溶化物とし、ま
た美麗化するものであり、焼成過程の冷却は600〜9
00[℃]の温度域で燻化処理を行なって製造するもの
である。
4. A smoldering treatment using a raw fuel gas, which is generally known as a technique of smoldering roof tiles, is carried out to make a more complete insolubilized product in a state in which the whole sintered body is wrapped with a carbonaceous film, and It is beautiful, and cooling in the firing process is 600-9.
It is manufactured by performing a smoke treatment in a temperature range of 00 [° C.].

【0006】[0006]

【 作 用 】本発明の作用の特徴とするところは、 (1) 可溶性クロム酸塩が廃煉瓦などの様に複雑な状
態で存在し、不活性の状態にあるものをCaOなどのア
ルカリ塩水溶液で活性化して水和物とて一時固定、焼成
過程の結合水の脱水時期に発生機のCr+6イオンもと
らえて有効に還元安定化させる事が第1の特徴である。 (2) 第2の特徴は発生機のCr+6イオンを焼成昇
温過程の中で広い温度範囲にわたって還元状態を保持す
る為、特に通常の陶磁器質焼結体の製造工程と同様に配
合、成形、焼成という一貫した工程の中で完全な安定化
を行なうものである。
[Operation] The features of the action of the present invention are: (1) Soluble chromate is present in a complicated state such as waste brick, and is in an inactive state, an aqueous solution of an alkali salt such as CaO. The first characteristic is that it is activated as a hydrate and temporarily fixed as a hydrate, and is effectively reduced and stabilized by capturing the Cr +6 ion of the generator at the dehydration time of the bound water in the firing process. (2) The second characteristic is that the Cr +6 ions of the generator are kept in a reduced state over a wide temperature range during the firing temperature raising process, and therefore, the compounding and molding are performed in the same manner as in the usual manufacturing process of a ceramic sinter. , Complete stabilization is performed in a consistent process of firing.

【請求項1】の組成物の製造過程の作用を考慮して予
め、可溶性クロム酸塩の含有量を確認して炭素質物など
還元剤の増加量を算出して、配合するので計100重量
[%]となる。クロム含有原料は粒度1[mm]以下に
粉砕されたものが必要であり、スラグは微粉末で表面積
の大きいもの程有効である。此等の配合物に対し、水硬
性セメント及びスラグの配合量は35[%]以下であ
り、成形工程に於て適正な成形水分を持つ様に清水を加
えて、混合、混練した後、少なくも5時間以上養生させ
て、一時的にエトリンガイトを主成分とする水和物にC
+6イオンをイオン交換吸着させる成形杯土組成物を
造り、所定の形状の金型を用いて加圧、成形して乾燥す
る。焼成は1000[℃]迄は、少なくもCOガス20
[%]以上の焼成雰囲気で焼成する事により安定な還元
作用をする事により、最終的にスピネル中にクロムを結
合させて安定化出来るものであった。焼成過程に於る反
応は、Cr+6イオンを含む水和物の脱水が250
[℃]付近から開始され約500[℃]迄、継続的に行
なわれる。一方、還元剤となる炭素成分は350[℃]
付近から燃焼発熱が開始され、還元雰囲気下では約50
0[℃]迄継続して燃焼が起こるものであるが、特に石
灰炭などの珪酸塩ガラス質に糊着し、一部炭化物の様な
形で存在するものは600[℃]に於ても燃焼による発
熱反応が残っている事が熱分析実験により確認され水和
物からの発生期のCr+6で最も反応活性の高い状態で
還元作用を行なう事が出来るものであった。この様にし
て可溶性クロム酸塩は、約1000[℃]迄の温度に於
て、完全に不溶性のCrOとなる事を、X線解析、及
び溶出試験によって確認することができる。結局、本発
明方法によれば、6価クロムは、1000[℃]の高温
度に於ては高炉水滓中のCaOやFeOその他の珪酸塩
と焼結反応を起こしてクロムCr+3とFeを含有する
複合固溶体として安定化した焼結体を得る事が出来るの
である。
1. Considering the action of the composition in the production process, the content of soluble chromate is confirmed in advance to calculate the increasing amount of the reducing agent such as carbonaceous material, and the total amount is 100 weight [in total]. %]. The chromium-containing raw material needs to be crushed to have a particle size of 1 [mm] or less, and the slag is more effective if it is a fine powder and has a large surface area. The blending amount of hydraulic cement and slag is 35% or less with respect to these blends, and after mixing and kneading by adding fresh water so as to have proper molding water in the molding process, a small amount is obtained. Is also cured for 5 hours or more, and temporarily converted into hydrate containing ettringite as a main component.
A molded clay composition for adsorbing r +6 ions by ion exchange is prepared, pressurized and molded using a mold having a predetermined shape, and dried. Firing up to 1000 [° C], at least CO gas 20
By firing in a firing atmosphere of [%] or more, a stable reducing action was achieved, and finally chromium could be bound in the spinel and stabilized. The reaction in the firing process was carried out by dehydrating the hydrate containing Cr +6 ions to 250
It starts from around [° C] and continues to about 500 ° C. On the other hand, the carbon component serving as a reducing agent is 350 [° C]
Combustion heat generation starts in the vicinity, and about 50 in a reducing atmosphere.
Combustion occurs continuously up to 0 [° C], but especially those that adhere to silicate glass such as lime charcoal and are partly in the form of carbide even at 600 [° C] It was confirmed by a thermal analysis experiment that an exothermic reaction due to combustion remained, and it was possible to carry out the reducing action in the state where Cr +6 in the nascent stage from the hydrate had the highest reaction activity. In this way, it can be confirmed by X-ray analysis and dissolution test that the soluble chromate becomes completely insoluble CrO 3 at a temperature up to about 1000 [° C.]. After all, according to the method of the present invention, hexavalent chromium causes a sintering reaction with CaO, FeO and other silicates in the slag of the blast furnace at a high temperature of 1000 [° C.] to form chromium Cr +3 and Fe. It is possible to obtain a stabilized sintered body as the contained composite solid solution.

【0007】[0007]

【実施例1】配合は次の通りであった。 (a) セメントロータリーキルン廃煉瓦でCrO
0.3[%]含むものを1[mm]以下に粉砕し、重量
比50[%]を用いた。 (b) スラグは44[μ]以下に微粉砕された粉末を
15[%] (C) フライアッシュは炭素含有量8.5[%]を含
む20[μm]以下の粉末を20[%] (d) ポルトランドセメント 15[%] 以上の配合率で混合し、水分15[%]を加えて混合混
練した組成物杯土を12[時間]養生し、団粒状となっ
た養生杯土を2[mm]以下に解砕した後、10[c
m]x20[cm]x1[cm]の立方体に200[k
g/cm]圧力で加圧成形し1000[℃]迄の温度
域をCOガス30[%]の還元雰囲気で10[℃/分]
の昇温速度で焼成し、引続き1000〜1200[℃]
迄をCOガス5[%]の雰囲気で焼成して焼結体を得
た。かさ比重2.3[g/cc】曲げ強度180[kg
/cm]であった。更に、上記の廃棄物について、前
記第1の従来技術による処理物と本発明による処理物と
を、JISKO102−65−2−1により、Cr+6
の溶出比較試験を行なった。各処理物を上に試験方法に
基き廃煉瓦1[kg]を5[l]の清水中に入れて1時
間沸騰した後5日間放置して溶出させ溶出液中の含有量
を測定した。その結果、総理府の全国の溶出許容基準
0.5[ppm]に対し、第1の従来技術処理物の溶出
液のCr+6は2.5[ppm]であったが、本発明に
よる処理物の溶出液のCr+6は、従来の方法によるも
のと非常に異なり、殆んどトレースも認められないもの
であった。
Example 1 The formulation was as follows. (A) A cement rotary kiln waste brick containing 0.3 [%] of CrO 3 was crushed to 1 [mm] or less, and a weight ratio of 50 [%] was used. (B) Slag is 15% of finely pulverized powder to 44 [μ] or less (C) Fly ash is 20 [%] of powder of 20 [μm] or less including carbon content of 8.5 [%] (D) Portland cement 15 [%] The composition clay mixed by mixing at a mixing ratio of 15% or more, and mixed and kneaded with water 15%, was aged for 12 hours, and the aggregated agglomerated earth was 2 times. After crushing to less than [mm], 10 [c
200 [k] for a cube of m] x 20 [cm] x 1 [cm]
pressure molding at a pressure of g / cm 2 ] and a temperature range up to 1000 [° C.] in a reducing atmosphere of CO gas 30 [%] of 10 [° C./min]
Firing at a heating rate of 1000 to 1200 [° C]
The sintered body was fired in an atmosphere of CO gas of 5% to obtain a sintered body. Bulk specific gravity 2.3 [g / cc] Bending strength 180 [kg
/ Cm 2 ]. Further, regarding the above-mentioned waste, the processed product according to the first conventional technique and the processed product according to the present invention are Cr +6 according to JISKO102-65-2-1.
The dissolution comparison test was conducted. Based on the test method, 1 [kg] of waste brick was put into 5 [l] of clear water based on the above test method, boiled for 1 hour and left to stand for 5 days to elute, and the content in the eluate was measured. As a result, the Cr + 6 of the eluate of the first conventional technology treated product was 2.5 [ppm] with respect to the national elution acceptance standard of 0.5 [ppm] of the Prime Minister's Office. Cr +6 in the eluate was very different from that obtained by the conventional method, and almost no trace was observed.

【0008】[0008]

【実施例2】配合は下記の通りにした。 前記廃煉瓦1[%]以下粉末 35[%」 スラグ粉末 20[%] フライアッシュ(炭素8.5[%]含有) 20[%] 木節粘土(石炭6.2[%]含有) 15[%] ポルトランドセメント 10[%] 実施例1と同様に処理、同条件で焼成したものは物性か
さ比重2.1[g/cc]曲げ強度220[kg/cm
]であった。更に、上記廃棄物について、前記第2の
従来技術による処理物と本発明による処理物とを、JI
SKO102−65−2−1により、Cr+6の溶出比
較試験を行なった。具体的方法は実施例1と同様であっ
た。その結果、総理府令による溶出許容基準0.5〔p
pm]に対し、第2の従来技術処理物の溶出液のCr
+6は1.9[ppm]であったが、本発明による処理
物の溶出液のCr+6は殆んど痕跡も認められなかっ
た。
Example 2 The formulation was as follows. Waste brick 1 [%] or less Powder 35 [%] Slag powder 20 [%] Fly ash (containing 8.5 [%] carbon) 20 [%] Kibushi clay (containing 6.2 [%] coal) 15 [ %] Portland cement 10 [%] Physical properties of the bulk specific gravity of 2.1 [g / cc] bending strength of 220 [kg / cm] are the same as in Example 1 and fired under the same conditions.
2 ]. Further, regarding the above-mentioned waste, the second conventional technique and the present invention are treated as JI.
A dissolution comparison test of Cr +6 was performed by SKO102-65-2-1. The specific method was the same as in Example 1. As a result, the elution acceptance standard of 0.5 [p
pm], Cr of the eluate of the second prior art treated product
+6 was 1.9 [ppm], but almost no trace of Cr +6 in the eluate of the treated product of the present invention was observed.

【0009】[0009]

【本発明の効果】[Effect of the present invention]

(1) 環境保全の推進は、現今において、世界的に重
要なテーマである。その一環として、本発明は生体に有
害な廃棄物の安全化処理と未利用資源の活用の両面から
物資が活用されることとなる。即ち、可溶性クロム酸塩
を、極めて経済性の高い処理方法で長期的に安定な無公
害物に転換して、建設材料用セラミックス(煉瓦舗道
板、タイルなど)として高度の付加価値をもつ商品にす
る為の、全く新しい技術が提供される。正に一石二鳥の
効果がある。 (2) 従来技術のいずれもが、そのCr+6の溶出量
において、地方の溶出規制基準の0.1[ppm]を満
たすことができないのは勿論のこと、総理府令の全国許
容基準0.5[ppm]にも合格しえない処、本発明の
処理物はCr+6の溶出の痕跡も殆んどないのであるか
ら、従来に比し、画期的顕著な効果が得られたものとい
うことができる。これは特に現今においては国際的に重
要な効果である。 (3) 現在セメントキルン用の内張煉瓦として、クロ
ームマグネシア耐火物の他に代替材料が見当たらない優
れた特性がありながら、廃煉瓦の公害対策として、クロ
マグ耐火物の製造使用の減退が起こりつつある中で、此
等の処理技術を完成する事により、高熱工業全体に関し
て優れた経済効果をも期待する事が出来る。
(1) Promotion of environmental protection is an important theme worldwide today. As part of this, the present invention will utilize materials both from the viewpoint of safety treatment of waste that is harmful to living organisms and the utilization of unused resources. In other words, by converting soluble chromate into a long-term stable pollution-free substance by an extremely economical treatment method, it becomes a product with a high added value as ceramics for construction materials (brick pavement boards, tiles, etc.). To provide a completely new technology to do. It has the effect of two birds with one stone. (2) It is needless to say that none of the conventional techniques can meet the local elution regulation standard of 0.1 [ppm] in the amount of Cr +6 elution, and the national permissible standard of the Prime Minister's Order is 0.5. When it does not pass [ppm], the treated product of the present invention has almost no trace of elution of Cr +6 , so that it is said that an epoch-making remarkable effect is obtained as compared with the conventional one. You can This is an internationally important effect, especially in the present. (3) Currently, as a lining brick for cement kiln, while it has excellent characteristics that alternative materials other than chrome magnesia refractory are not found, as a measure against pollution of abandoned bricks, production and use of chrome mag refractory is decreasing. Among them, by completing these treatment technologies, it is possible to expect excellent economic effects for the entire high heat industry.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】可溶性クロム酸塩含有物30重量[%]以
上70重量[%]以下、スラグ4重量[%]以上20重
量[%]以下、水硬性セメント5重量[%]以上15重
量[%]以下、珪酸塩質物13重量[%]以上37重量
[%]以下、及び、炭素質物0重量[%]以上6重量
[%]以下を成分とし、焼結無公害化されていること、
を特徴とする、可溶性クロム酸塩の無公害化焼結セラミ
ックス。
1. Soluble chromate-containing material 30% by weight or more and 70% by weight or less, slag 4% by weight or more and 20% by weight or less, hydraulic cement 5% by weight or more and 15% by weight %] Or less, a silicate substance 13 wt% or more and 37 wt% or less, and a carbonaceous substance 0 wt% or more and 6 wt% or less, as components, and sinter-free.
Pollution-free sintered ceramics of soluble chromate characterized by:
【請求項2】前記可溶性クロム酸塩含有物が、クロム系
耐火物の廃棄物、及び/又は、クロム鉱精錬残渣であ
る、請求項1に記載の可溶性クロム酸塩の無公害化焼結
セラミックス。
2. The soluble chromate-containing pollution-free sintered ceramics according to claim 1, wherein the soluble chromate-containing material is a waste material of a chromium-based refractory and / or a smelting residue of a chromium ore. ..
【請求項3】前記請求項1に記載の組成物が、無水換算
で得られる原料配合物に、該原料配合物中の可溶性クロ
ム酸塩に対し、重量で5倍以上10倍以下の炭素質物
と、更にAl,Ng,Siのうちより選ばれた1種以上
の炭化物を該炭素質物の1/100重量部以上3/10
0重量部以下とを添加配合し、加水混練し、必要に応
じ、湿空養生し、加圧成形、乾燥した後、昇温過程にお
いて、少なくも1時間以上、1000[℃]までは強還
元焔雰囲気として、次に1000[℃]を超え1300
[℃]以下では、1時間以上、2時間以下、通常の還元
焔雰囲気で焼成することを特徴とする、可溶性クロム酸
塩の無公害化焼結セラミックスの製造方法。
3. A carbonaceous material in which the composition according to claim 1 is contained in a raw material mixture obtained on an anhydrous basis in an amount of 5 times or more and 10 times or less the weight of the soluble chromate in the raw material mixture. And one or more kinds of carbides selected from Al, Ng, and Si in an amount of 1/100 parts by weight or more and 3/10 or more by weight of the carbonaceous material.
0 parts by weight or less is added and blended, hydro-kneaded, and if necessary, cured under humid air, pressure-molded and dried, and then strongly reduced for at least 1 hour or more, up to 1000 [° C] in the temperature rising process. The flame atmosphere then exceeds 1000 [° C] and exceeds 1300
A method for producing a pollution-free sintered ceramics of soluble chromate, which comprises firing in an ordinary reducing flame atmosphere for 1 hour or more and 2 hours or less at [° C.] or less.
【請求項4】前記請求項3に記載の製造方法の各工程後
において、更に該焼結物を600[℃]以上900
[℃]以下の温度範囲で、かつ炭素微粒子を含む還元雰
囲気中で、燻化焼成を行なうことを特徴とする、可溶性
クロム酸塩の無公害化焼結セラミックスの製造方法。
4. After each step of the manufacturing method according to claim 3, the sintered product is further heated to 600 [° C.] or more and 900 or more.
A method for producing pollution-free sintered ceramics of soluble chromate, which comprises performing smoldering firing in a temperature range of [° C.] or less and in a reducing atmosphere containing carbon fine particles.
JP4197373A 1992-06-16 1992-06-16 Pollution-free sintered ceramic of soluble chromic acid salt and its production Pending JPH05345658A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4197373A JPH05345658A (en) 1992-06-16 1992-06-16 Pollution-free sintered ceramic of soluble chromic acid salt and its production

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4197373A JPH05345658A (en) 1992-06-16 1992-06-16 Pollution-free sintered ceramic of soluble chromic acid salt and its production

Publications (1)

Publication Number Publication Date
JPH05345658A true JPH05345658A (en) 1993-12-27

Family

ID=16373427

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4197373A Pending JPH05345658A (en) 1992-06-16 1992-06-16 Pollution-free sintered ceramic of soluble chromic acid salt and its production

Country Status (1)

Country Link
JP (1) JPH05345658A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002239378A (en) * 2001-02-14 2002-08-27 Taiheiyo Cement Corp Heavy metal elution suppressant
CN104984982A (en) * 2015-07-10 2015-10-21 中信大锰矿业有限责任公司大新锰矿分公司 Innocent treatment method of electrolytic manganese and chromium residues

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5150921A (en) * 1974-10-31 1976-05-06 Mitsubishi Heavy Ind Ltd
JPS51115510A (en) * 1975-04-02 1976-10-12 Tipton Mfg Co Method of manufacturing mold sintered articles fromsludge obtained by treatment of plating waste liquids
JPS545869A (en) * 1977-06-17 1979-01-17 Nippon Toki Kk Sintering fixation of chromium containing matter

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5150921A (en) * 1974-10-31 1976-05-06 Mitsubishi Heavy Ind Ltd
JPS51115510A (en) * 1975-04-02 1976-10-12 Tipton Mfg Co Method of manufacturing mold sintered articles fromsludge obtained by treatment of plating waste liquids
JPS545869A (en) * 1977-06-17 1979-01-17 Nippon Toki Kk Sintering fixation of chromium containing matter

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002239378A (en) * 2001-02-14 2002-08-27 Taiheiyo Cement Corp Heavy metal elution suppressant
JP4589544B2 (en) * 2001-02-14 2010-12-01 太平洋セメント株式会社 Heavy metal elution reducing material
CN104984982A (en) * 2015-07-10 2015-10-21 中信大锰矿业有限责任公司大新锰矿分公司 Innocent treatment method of electrolytic manganese and chromium residues

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