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JPH07102983B2 - How to neutralize slag - Google Patents
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JPH07102983B2 - How to neutralize slag - Google Patents

How to neutralize slag

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Publication number
JPH07102983B2
JPH07102983B2 JP20220791A JP20220791A JPH07102983B2 JP H07102983 B2 JPH07102983 B2 JP H07102983B2 JP 20220791 A JP20220791 A JP 20220791A JP 20220791 A JP20220791 A JP 20220791A JP H07102983 B2 JPH07102983 B2 JP H07102983B2
Authority
JP
Japan
Prior art keywords
slag
strain
ferm
microorganism
liter
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.)
Expired - Lifetime
Application number
JP20220791A
Other languages
Japanese (ja)
Other versions
JPH0525557A (en
Inventor
隆一郎 倉根
豊一 横幕
秀明 松山
一郎 山本
Original Assignee
工業技術院長
環境エンジニアリング株式会社
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 工業技術院長, 環境エンジニアリング株式会社 filed Critical 工業技術院長
Priority to JP20220791A priority Critical patent/JPH07102983B2/en
Publication of JPH0525557A publication Critical patent/JPH0525557A/en
Publication of JPH07102983B2 publication Critical patent/JPH07102983B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Preparation Of Compounds By Using Micro-Organisms (AREA)
  • Curing Cements, Concrete, And Artificial Stone (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Furnace Details (AREA)

Description

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

【0001】[0001]

【産業上の利用分野】本発明はアルカリ性スラグの中和
方法に関し、更に詳しくは合成有機酸や無機酸を使用す
ることなく、アルカリ性スラグを有効に中和することが
出来るアルカリ性スラグの中和方法を提供する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for neutralizing alkaline slag, and more specifically, a method for neutralizing alkaline slag which can effectively neutralize alkaline slag without using synthetic organic acid or inorganic acid. I will provide a.

【0002】[0002]

【従来の技術】従来、各種製鉄所や製錬所においては、
金属の生産及び精練に際し多量のスラグ(鉱滓)が発生
し、これらの鉱滓は種類によってセラミック、セメント
等の他の有用物品の製造原料に使用されたり、或は建築
現場の基礎材、沼地、海岸、低地等の埋め立て等に利用
されている。
2. Description of the Related Art Conventionally, in various steelworks and smelters,
A large amount of slag (slag) is generated during metal production and refining, and depending on the type, these slags are used as raw materials for manufacturing other useful articles such as ceramics and cement, or as a base material for construction sites, marshes and coasts. It is used for land reclamation of lowlands.

【0003】[0003]

【発明が解決しようとしている問題点】これらの鉱滓の
中には、例えば、酸化カルシウム等の酸化物に基づいて
アルカリ性が高いものが多く、製鉄所や製錬所等の発生
箇所に保管中、輸送中、実際の使用中に雨水等に曝され
ると、多量の強アルカル水が出し、環境汚染、薬害等
の種々の問題が発生する。勿論、上記のアルカリ性の中
和には、他の薬剤(酸)を使用することで簡単に且つ簡
便に中和することが可能であるが、鉱滓自体が極めて安
価である為、他の中和剤の使用は経済的に使用困難であ
り、逆に中和剤による環境汚染、スラグの品質劣化等の
問題が発生する。従って本発明の目的は、人工物の中和
剤を使用せず、環境汚染や他の薬害を発生することな
く、アルカリ性スラグを経済的に中和することが出来る
方法を提供することである。
[Problems to be solved by the invention] Among these slags, for example, many of them have high alkalinity based on oxides such as calcium oxide, and are stored in a place where iron or smelter is generated. during transport, when exposed to rain water during actual use such issues a large amount of strong Arukaru water 滲, environmental pollution, various problems occur such as phytotoxicity. Of course, for the above-mentioned alkaline neutralization, it is possible to neutralize easily and simply by using other chemicals (acids), but since the slag itself is extremely inexpensive, other neutralization is possible. It is economically difficult to use the agent, and conversely, problems such as environmental pollution due to the neutralizing agent and deterioration of slag quality occur. Therefore, it is an object of the present invention to provide a method capable of economically neutralizing alkaline slag without using a neutralizing agent for artificial substances and without causing environmental pollution or other chemical damage.

【0004】[0004]

【問題点を解決する為の手段】上記目的は以下の本発明
によって達成される。即ち、本発明は、アルカリ性スラ
グにロードコッカス・エリスロポレス又は、シュウドモ
ナス属、アシネトバクター属、アグロバクテリウム属、
エンテロバクター属、オーレオバクテリウム属及びオエ
ルスコビア属からなる群から選ばれる少なくとも1属に
属する菌及び/又はその培養物並びに必要により栄養源
を混合することを特徴とするスラグの中和方法である。
The above object can be achieved by the present invention described below. That is, the present invention relates to alkaline slag and Rhodococcus erythropoles or Pseudomonas
Eggplant, Acinetobacter, Agrobacterium,
Enterobacter, Aureobacteria and Oe
At least one genus selected from the group consisting of the genus Ruscovia
A method for neutralizing slag, which comprises mixing a bacterium belonging thereto and / or a culture thereof and optionally a nutrient source .

【0005】[0005]

【作用】アルカリ性スラグ中に耐アルカリ性微生物(必
要に応じてその栄養物)或はその培養物(必要に応じて
その栄養物)を混在させておくと、微生物によって有機
物が分解されて炭酸ガスが発生し、この炭酸ガスがスラ
グ中のアルカリ成分を中和する。この際、微生物として
凝集剤を生産する微生物を使用すると、炭酸ガスと共に
凝集剤も発生し、この凝集剤によって微生物の流出が防
止されると共に微生物が増殖する環境が良好に保持さ
れ、更に滲出水と共に流出するコロイド状微粒子の流出
も防止される。
[Function] When alkaline-resistant microorganisms (the nutrients as needed) or cultures thereof (if necessary, the nutrients) are mixed in the alkaline slag, the organic substances are decomposed by the microorganisms and carbon dioxide gas is generated. It is generated and this carbon dioxide gas neutralizes the alkaline component in the slag. At this time, when a microorganism that produces a flocculant is used as the microorganism, a flocculant is also generated together with carbon dioxide, and the flocculation agent prevents the outflow of the microorganism and maintains an environment in which the microorganism proliferates well. It is also possible to prevent the colloidal fine particles from flowing out together.

【0006】[0006]

【好ましい実施態様】次に好ましい実施態様を挙げて本
発明を更に詳しく説明する。本発明の中和方法の対象と
なるスラグはいずれのスラグでもよいが、例えば、代表
的な例として、高炉スラグ、転炉スラグ、電気炉スラ
グ、脱硫スラグ等が挙げられる。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described in more detail with reference to the preferred embodiments. Although any slag may be used as the target of the neutralization method of the present invention, typical examples thereof include blast furnace slag, converter slag, electric furnace slag, desulfurization slag, and the like.

【0007】本発明で使用する微生物は、例えば、微生
物排水処理に広く使用されている活性汚泥等の強アルカ
リ性に耐久性のある微生物であればいずれの微生物でも
よく、その中でも凝集剤生産菌であるロードコッカス・
エリスロポレスが好ましい微生物である。ロードコッカ
ス・エリスロポレス以外の凝集剤生産菌は、シュウドモ
ナス属、アシネトバクター属、アグロバクテリウム属、
エンテロバクター属、オーレオバクテリウム属及びオエ
ルスコビア属からなる群から選ばれる少なくとも1属に
属する凝集剤生産能を有する菌が挙げられる。又、これ
らの属に属する凝集剤生産菌は、従来公知のロードコッ
カス・エリスロポレスKR−256−2、FERM−P
No.3923及びロードコッカス・エリスロポレスK
R−S−1、FERM−P No.3530等とは異な
る属であって、ロードコッカス・エリスロポレスが生産
するバイオ凝集剤と異なった新規なバイオ凝集剤を生産
し、優れた凝集剤を生産する微生物として、シュウドモ
ナス属、アシネトバクター属、アグロバクテリウム属、
エンテロバクター属、オーレオバクテリウム属及びオエ
ルスコビア属からなる群から選ばれる少なくとも1属を
含む微生物群が挙げられ、本発明ではこれらをR−3と
称しているが、夫々既に微工研寄託第11333号(F
ERM P−11333)、同第11334号(FER
M P−11334)、同第11335号(FERM
P−11335)、同第11336号(FERM P−
11336)、同第11337号(FERM P−11
337)、同第11357号(FERM P−1135
7)及び同第11358号(FERMP−11358)
として寄託されている。
The microorganism used in the present invention may be any microorganism that is durable to strong alkalinity such as activated sludge that is widely used for treating microbial wastewater, and among them, it is a flocculant-producing bacterium. A certain Road Coccus
Erythropoleth is the preferred microorganism. Coagulant-producing bacteria other than Rhodococcus erythropoles include Pseudomonas spp., Acinetobacter spp., Agrobacterium spp.
Bacteria having a flocculant-producing ability belonging to at least one genus selected from the group consisting of Enterobacter, Aureobacteria, and Oerscovia. Further, the flocculant-producing bacteria belonging to these genera are the conventionally known Rhodococcus erythropoles KR-256-2 and FERM-P.
No. 3923 and Rhodococcus erythropoleth K
R-S-1, FERM-P No. As a microorganism that is a genus different from 3530, etc. and produces a novel bio-flocculant different from the bio-flocculant produced by Rhodococcus erythropoles, and producing an excellent flocculant, Pseudomonas sp., Acinetobacter sp., Agrobacterium sp. Umm,
Examples of the microorganisms include at least one genus selected from the group consisting of Enterobacter, Aureobacteria, and Oerscovia. These are referred to as R-3 in the present invention. 11333 (F
ERM P-11333), No. 11334 (FER)
MP-11334), No. 11335 (FERM
P-11335), No. 11336 (FERM P-
11336), No. 11337 (FERM P-11
337) and No. 11357 (FERM P-1135).
7) and No. 11358 (FERMP-11358).
Has been deposited as.

【0008】上記凝集剤生産微生物の菌学的性質は、既
に出願した特願平3−87428号明細書に詳述してあ
る。又、これらの菌学的性質について、細菌の同定書で
あるバージー・マニュアル・システマチック・バクテオ
ロジー第1、2巻(Bergey'sManualof Systematic Bacte
riology Volume 1、2)、(1984 年)で検討した結果、KY
M−1株は同書165頁に記載されているシュウドモナ
ス・フルオレセンスと一致し、KYM−1株はシュウド
モナス・フルオレッセンスと同定し、微工研寄託第11
333号(FERM P−11333)として寄託され
ている。KYM−2株は同書175頁記載のシュウドモ
ナス・セパシアと考えると妥当であり、微工研寄託第1
1334号(FERM P−11334)として寄託さ
れている。KYM−3株は同書303頁記載のアシネト
バクター属細菌と一致し、微工研寄託第11335号
(FERM P−11335)として寄託されている。
KYM−4株は同書254頁記載のアグロバクテリウム
・レイデオバクターと殆ど記載は一致するものの、糖の
資化性等細かい点で少し異なるので同種の近縁類と考え
るのが分類学的に妥当であり、本菌は微工研寄託第11
336号(FERM P−11336)として寄託され
ている。KYM−5株は同書465頁記載のエンテロバ
クター属細菌と属レベルで完全に一致し、微工研寄託第
11337号(FERM P−11337)として寄託
されている。KYM−6株は同書1323頁記載のオー
レオバクテリウム属細菌、KYM−7株は同書1489
頁記載のオエルスコビア属細菌と夫々属レベルの記載は
一致する。KYM−6株は、微工研寄託第11357号
(FERM P−11357)、KYM−7株は、微工
研寄託第11358号(FERM P−11358)と
して夫々寄託されている。
The mycological properties of the above flocculant-producing microorganisms are described in detail in Japanese Patent Application No. 3-87428, which has already been filed. In addition, regarding these mycological properties, Bergey's Manual of Systematic Bacte
riology Volume 1, 2), (1984), KY
The M-1 strain was identical to Pseudomonas fluorescens described on page 165 of the same book, and the KYM-1 strain was identified as Pseudomonas fluorescens, and was deposited by the Institute of Microtechnology Deposit No. 11
Deposited as No. 333 (FERM P-11333). The KYM-2 strain is appropriate when considered to be Pseudomonas cepacia described on page 175 of the same document, and is deposited by the Institute of Microscopy, No. 1
Deposited as 1334 (FERM P-11334). The KYM-3 strain coincides with the bacterium of the genus Acinetobacter described on page 303 of the same document, and has been deposited as Micromachine Research Deposit No. 11335 (FERM P-11335).
Although the description of KYM-4 strain is almost the same as Agrobacterium reideobacter described on page 254 of the same book, it is taxonomically considered to be a related species because it is slightly different in details such as sugar assimilation. It is valid, and this bacterium is the 11th deposit
Deposited as 336 (FERM P-11336). The KYM-5 strain is completely in genus level with the bacteria of the genus Enterobacter described on page 465 of the same document, and has been deposited as Microindustrial Research Deposit No. 11337 (FERM P-11337). The KYM-6 strain is a bacterium of the genus Aureobacterium described on page 1323 of the same book, and the KYM-7 strain is 1489 of the same book.
The description at the genus level is the same as that of the genus Oerscovia described on the page. The KYM-6 strain has been deposited as the Japan Institute of Mechanical Engineering deposit No. 11357 (FERM P-11357), and the KYM-7 strain has been deposited as the Japan Institute of Mechanical Engineering deposit No. 11358 (FERM P-11358).

【0009】以下に公知菌であるードコッカス・エリ
スロポレスKR−S−1(FERM−P No.353
0)(S−1菌)及びR−3菌の培養方法の1例を示す
(尚、R−3菌の培養によって生産される凝集剤の物性
は既に出願した特願平3−87428号明細書に詳述し
てある。)培養方法 (1)S−1菌 温度、DO及びpH計を設置した5リットルのジャーフ
ァーメンターに下記の生産培地を3リットル入れ、オー
トクレーブ滅菌した。これに培養液を2%(V/V)接
種し、温度28〜30℃、空気量1.5リットル/mi
n.、撹拌強度200rpmの条件で1週間培養した。液体培地の組成 炭素源(単糖類) 10g/リットル KHPO 5g/リットル KHPO 2g/リットル MgSO 0.2g/リットル (NHSO 0.5g/リットル NaCl 0.1g/リットル イースト抽出物 0.5g/リットル (2)R−3菌 温度、DO及びpH計を設置した5リットルのジャーフ
ァーメンターに下記の生産培地を3リットル入れ、オー
トクレーブ滅菌した。これに培養液を2%(V/V)接
種し、温度25〜27℃、空気量3リットル/mi
n.、撹拌強度200rpmの条件で1週間培養した。
但し、培養2日目より培養液の粘性が増加したので、撹
拌強度を400rpmに上げた。液体培地の組成 炭素源(多糖類) 10g/リットル KHPO 5g/リットル KHPO 2g/リットル MgSO 0.2g/リットル (NHSO 0.5g/リットル NaCl 0.1g/リットル イースト抽出物 0.5g/リットル
[0009] is a known bacteria following Russia Dokokkasu-Erisuroporesu KR-S-1 (FERM- P No.353
0) One example of a method for culturing (S-1 bacterium) and R-3 bacterium (the physical properties of the aggregating agent produced by culturing R-3 bacterium are described in Japanese Patent Application No. 3-87428). Culture method (1) S-1 bacterium 3 liters of the following production medium was placed in a 5 liter jar fermenter equipped with a temperature, DO and pH meter, and sterilized by autoclave. The culture solution was inoculated with 2% (V / V) of the culture solution, the temperature was 28 to 30 ° C., and the air amount was 1.5 liter / mi.
n. The cells were cultured for 1 week under the conditions of stirring intensity of 200 rpm. Composition of liquid medium Carbon source (monosaccharide) 10 g / liter K 2 HPO 4 5 g / liter KH 2 PO 4 2 g / liter MgSO 4 0.2 g / liter (NH 4 ) 2 SO 4 0.5 g / liter NaCl 0.1 g / Liter yeast extract 0.5 g / liter (2) R-3 bacterium 3 liters of the following production medium was placed in a 5 liter jar fermenter equipped with a temperature, DO and pH meter and autoclaved. The culture solution was inoculated with 2% (V / V) of this, the temperature was 25 to 27 ° C., and the air amount was 3 liters / mi.
n. The cells were cultured for 1 week under the conditions of stirring intensity of 200 rpm.
However, since the viscosity of the culture solution increased from the second day of culture, the stirring intensity was increased to 400 rpm. Liquid medium composition Carbon source (polysaccharide) 10 g / liter K 2 HPO 4 5 g / liter KH 2 PO 4 2 g / liter MgSO 4 0.2 g / liter (NH 4 ) 2 SO 4 0.5 g / liter NaCl 0.1 g / Liter Yeast extract 0.5g / liter

【0010】本発明の中和方法は、上記のスラグに上記
の如き微生物或はそれらの培養物を混合することを特徴
としている。両者の混合方法としては、スラグ粉末が微
生物の生存に影響しない程度の温度(通常50℃以下)
に低下した後に混合するのであれば、いかな方法でも
よく、又、スラグの堆積物の表面から微生物を含む液或
は培養物を散布してこれらのスラグの表面からしみ込ま
せる等の方法も好適な方法である。使用する微生物は微
生物そのもの(但し必要に応じて微生物の栄養源を併用
する)、その培養物、培養処理物、培養液そのもの、そ
の濃縮物、濾液、その濾過残渣、それらの乾燥物等いず
れの形態でもよい。微生物の使用量は被処理物であるア
ルカリ性スラグの種類によって変化するので一概には規
定出来ないが、例えば、製鉄スラグの場合には1トンあ
たり乾燥状態で50〜100g程度の範囲が好ましい範
囲である。
The neutralization method of the present invention is characterized by mixing the above-mentioned slag with the above-mentioned microorganism or a culture thereof. As a method for mixing the two, a temperature at which the slag powder does not affect the survival of microorganisms (usually 50 ° C or lower)
If the mix after drops, may be Ikana Ru method, also methods such as impregnated from the surface of these slags by spraying the liquid or the culture containing microorganisms from the surface of the slag deposit This is the preferred method. The microorganism to be used may be any of the microorganism itself (however, the nutrient source of the microorganism is also used in combination), its culture, culture-treated product, culture solution itself, its concentrate, filtrate, its filtration residue, their dried product, etc. It may be in the form. The amount of microorganisms used cannot be unconditionally specified because it varies depending on the type of the alkaline slag that is the object to be treated, but for example, in the case of iron-making slag, a range of about 50 to 100 g in a dry state per ton is a preferable range. is there.

【0011】[0011]

【実施例】次に実施例により本発明を更に具体的に説明
する。 実施例1(S−1菌使用例) 高炉徐冷滓に、前記S−1菌の培養液を約3リットル散
布して染み込ませ、この濡れたスラグを3分割し、栄養
源(単糖類)を30重量%、15重量%及び7.5重量
%の濃度で加えた3種の液を夫々別々のスラグに均一に
散布して染み込ませた。その3時間後に、夫々のスラグ
を底部がメッシュ状になっている20リットルの開放容
器に約15リットル充填して固めた後1週間放置した。
その後各スラグ表面に約30秒間で2リットルの水道水
を散水し、散水1分後に容器の底部から漏出した水分を
採取してそのpHを測定した。この操作を100日間で
合計5回行った。その結果を図1に示す。尚、比較例
(BK)は微生物培養液を使用しない以外は上記と同一
の操作を行ったものである。 実施例2(R−3菌使用例) 高炉徐冷滓に、前記R−3菌の培養液を約3リットル散
布して染み込ませ、この濡れたスラグを3分割し、栄養
源(多糖類)を30重量%、15重量%及び7.5重量
%の濃度で加えた3種の液を夫々別々のスラグに均一に
散布して染み込ませた。その3時間後に、夫々のスラグ
を底部がメッシュ状になっている20リットルの開放容
器に約15リットル充填して固めた後1週間放置した。
その後各スラグ表面に約30秒間で2リットルの水道水
を散水し、散水1分後に容器の底部から漏出した水分を
採取してそのpHを測定した。この操作を100日間で
合計5回行った。その結果を図2に示す。尚、比較例
(BK)は微生物培養液を使用しない以外は上記と同一
の操作を行ったものである。 実施例3(活性汚泥菌使用例) 高炉徐冷滓に、活性汚泥の培養液約2リットル散布して
染み込ませ、この濡れたスラグを2分割し、栄養源(単
糖類及び多糖類)を15重量%及び7.5重量%の濃度
で加えた2種の液を夫々別々のスラグに均一に散布して
染み込ませた。その3時間後に、夫々のスラグを底部が
メッシュ状になっている20リットルの開放容器に約1
5リットル充填して固めた後1週間放置した。その後各
スラグ表面に約30秒間で2リットルの水道水を散水
し、散水1分後に容器の底部から漏出した水分を採取し
てそのpHを測定した。この操作を100日間で合計5
回行った。その結果を図3に示す。尚、比較例(BK)
は微生物培養液を使用しない以外は上記と同一の操作を
行ったものである。
EXAMPLES Next, the present invention will be described more specifically by way of examples. Example 1 (Example of using S-1 bacterium) About 3 liters of the culture solution of the S-1 bacterium was sprayed onto a blast furnace slag to allow it to soak, and the wet slag was divided into 3 parts to supply a nutrient source (monosaccharide). Was added at a concentration of 30% by weight, 15% by weight and 7.5% by weight, and the three kinds of liquids were uniformly sprayed on separate slags to be impregnated with the liquids. Three hours after that, about 15 liters of each slag was filled in a 20 liter open container having a mesh-like bottom and solidified, and left for one week.
Then, 2 liters of tap water was sprinkled on the surface of each slag for about 30 seconds, and 1 minute after sprinkling water, water leaked from the bottom of the container was collected and the pH thereof was measured. This operation was performed 5 times in total for 100 days. The result is shown in FIG. In Comparative Example (BK), the same operation as described above was performed except that the microorganism culture solution was not used. Example 2 (Example of using R-3 bacterium) About 3 liters of the culture solution of the R-3 bacterium was sprayed on a blast furnace slag to allow it to soak, and the wet slag was divided into 3 parts to supply a nutrient source (polysaccharide). Was added at a concentration of 30% by weight, 15% by weight and 7.5% by weight, and the three kinds of liquids were uniformly sprayed on separate slags to be impregnated with the liquids. Three hours after that, about 15 liters of each slag was filled in a 20 liter open container having a mesh-like bottom and solidified, and left for one week.
Then, 2 liters of tap water was sprinkled on the surface of each slag for about 30 seconds, and 1 minute after sprinkling water, water leaked from the bottom of the container was collected and the pH thereof was measured. This operation was performed 5 times in total for 100 days. The result is shown in FIG. In Comparative Example (BK), the same operation as described above was performed except that the microorganism culture solution was not used. Example 3 (Example of using activated sludge bacteria) About 2 liters of the activated sludge culture solution was sprayed on a blast furnace slag to allow it to soak, the wet slag was divided into two, and nutrient sources (monosaccharides and polysaccharides) were divided into 15 parts. The two kinds of liquids added at the concentrations of 7% by weight and 7.5% by weight were evenly spread on separate slags and impregnated with them. Three hours later, each slag was placed in an open container of 20 liters with a mesh-like bottom and about 1
After filling 5 liters and hardening, it was left for 1 week. Thereafter, 2 liters of tap water was sprinkled on the surface of each slag for about 30 seconds, and 1 minute after sprinkling water, water leaked from the bottom of the container was collected and the pH thereof was measured. This operation totals 5 in 100 days
I went there. The result is shown in FIG. Comparative example (BK)
Is the same as the above except that the microbial culture is not used.

【0012】[0012]

【効果】以上の如き本発明によれば、アルカリ性スラグ
中に耐アルカリ性微生物(必要に応じてその栄養物)或
はその培養物(必要に応じてその栄養物)を混在させて
おくと、微生物によって有機物が分解されて炭酸ガスが
発生し、この炭酸ガスがスラグ中のアルカリ成分を中和
する。この際、微生物として凝集剤を生産する微生物を
使用すると、炭酸ガスと共に凝集剤も発生し、この凝集
剤によって微生物の流出が防止されると共に微生物が増
殖する環境が良好に保持され、更に滲出水と共に流出す
るコロイド状微粒子の流出も防止される。
[Effect] According to the present invention as described above, when an alkali-resistant microorganism (the nutrient as necessary) or a culture thereof (the nutrient as necessary) is mixed in the alkaline slag, the microorganism is mixed. As a result, organic matter is decomposed to generate carbon dioxide gas, and the carbon dioxide gas neutralizes the alkaline component in the slag. At this time, when a microorganism that produces a flocculant is used as the microorganism, a flocculant is also generated together with carbon dioxide, and the flocculation agent prevents the outflow of the microorganism and maintains an environment in which the microorganism proliferates well. It is also possible to prevent the colloidal fine particles from flowing out together.

【図面の簡単な説明】[Brief description of drawings]

【図1】スラグ浸透水のpHと経過日数との関係を表す
図。
FIG. 1 is a diagram showing the relationship between the pH of slag permeated water and the number of days elapsed.

【図2】スラグ浸透水のpHと経過日数との関係を表す
図。
FIG. 2 is a diagram showing the relationship between the pH of slag-permeated water and the number of days elapsed.

【図3】スラグ浸透水のpHと経過日数との関係を表す
図。
FIG. 3 is a diagram showing the relationship between the pH of slag-permeated water and the number of days elapsed.

【符号の説明】[Explanation of symbols]

なし None

───────────────────────────────────────────────────── フロントページの続き (72)発明者 松山 秀明 東京都千代田区鍛冶町1−5−7 環境エ ンジニアリング株式会社内 (72)発明者 山本 一郎 東京都千代田区鍛冶町1−5−7 環境エ ンジニアリング株式会社内 審査官 天野 斉 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Hideaki Matsuyama 1-5-7 Kajimachi, Chiyoda-ku, Tokyo Inside Environmental Engineering Co., Ltd. (72) Ichiro Yamamoto 1-5-7 Kajimachi, Chiyoda-ku, Tokyo Hitoshi Amano, Examiner, Environmental Engineering Co., Ltd.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 アルカリ性スラグにロードコッカス・エ
リスロポレス又は、シュウドモナス属、アシネトバクタ
ー属、アグロバクテリウム属、エンテロバクター属、オ
ーレオバクテリウム属及びオエルスコビア属からなる群
から選ばれる少なくとも1属に属する菌及び/又はその
培養物並びに必要により栄養源を混合することを特徴と
するスラグの中和方法。
1. Alkaline slag and Rhodococcus et al.
Lithropoles or Pseudomonas sp., Acinetobacter
-Genus, Agrobacterium, Enterobacter, Oh
-Group consisting of Rheobacterium and Oerscovia
A method for neutralizing slag, which comprises mixing a bacterium belonging to at least one genus selected from the above and / or a culture thereof and optionally a nutrient source .
【請求項2】 微生物菌が、KR−S−1株(FERM
P−3530)、KYM1株(FERM P−113
33)、KYM2株(FERM P−11334)、K
YM3株(FERM P−11335)、KYM4株
(FERM P−11336)、KYM5株(FERM
P−11337)、KYM6株(FERM P−11
357)及びKYM7株(FERM P−11358)
からなる群から選ばれる少なくとも1株に属する菌であ
る請求項1に記載のスラグの中和方法。
2. The microbial strain is KR-S-1 strain (FERM
P-3530), KYM1 strain (FERM P-113
33), KYM2 strain (FERM P-11334), K
YM3 strain (FERM P-11335), KYM4 strain (FERM P-11336), KYM5 strain (FERM
P-11337), KYM6 strain (FERM P-11
357) and KYM7 strain (FERM P-11358).
The method for neutralizing slag according to claim 1, which is a bacterium belonging to at least one strain selected from the group consisting of:
【請求項3】 スラグが製鉄所又は製錬所から発生する
鉱滓である請求項1に記載のスラグの処理方法。
3. The method for treating slag according to claim 1, wherein the slag is a slag generated from a steel mill or a smelter.
JP20220791A 1991-07-18 1991-07-18 How to neutralize slag Expired - Lifetime JPH07102983B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP20220791A JPH07102983B2 (en) 1991-07-18 1991-07-18 How to neutralize slag

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP20220791A JPH07102983B2 (en) 1991-07-18 1991-07-18 How to neutralize slag

Publications (2)

Publication Number Publication Date
JPH0525557A JPH0525557A (en) 1993-02-02
JPH07102983B2 true JPH07102983B2 (en) 1995-11-08

Family

ID=16453741

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Country Status (1)

Country Link
JP (1) JPH07102983B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6478679B1 (en) 1997-08-08 2002-11-12 Sega Enterprises, Ltd. Memory device, controller and electronic device

Also Published As

Publication number Publication date
JPH0525557A (en) 1993-02-02

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