JP3284861B2 - Waste treatment method for cement raw materials - Google Patents

Waste treatment method for cement raw materials

Info

Publication number
JP3284861B2
JP3284861B2 JP33045595A JP33045595A JP3284861B2 JP 3284861 B2 JP3284861 B2 JP 3284861B2 JP 33045595 A JP33045595 A JP 33045595A JP 33045595 A JP33045595 A JP 33045595A JP 3284861 B2 JP3284861 B2 JP 3284861B2
Authority
JP
Japan
Prior art keywords
waste
cement raw
raw material
water
chlorine
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
JP33045595A
Other languages
Japanese (ja)
Other versions
JPH09165243A (en
Inventor
昭二 久芳
茂 小松
知彦 坂本
一郎 江波戸
典夫 三小田
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.)
Mitsubishi Materials Corp
Original Assignee
Mitsubishi Materials Corp
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 Mitsubishi Materials Corp filed Critical Mitsubishi Materials Corp
Priority to JP33045595A priority Critical patent/JP3284861B2/en
Publication of JPH09165243A publication Critical patent/JPH09165243A/en
Application granted granted Critical
Publication of JP3284861B2 publication Critical patent/JP3284861B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B7/00Hydraulic cements
    • C04B7/24Cements from oil shales, residues or waste other than slag
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B7/00Hydraulic cements
    • C04B7/36Manufacture of hydraulic cements in general
    • C04B7/38Preparing or treating the raw materials individually or as batches, e.g. mixing with fuel
    • 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
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/10Production of cement, e.g. improving or optimising the production methods; Cement grinding

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Organic Chemistry (AREA)
  • Processing Of Solid Wastes (AREA)

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明はセメント原料用廃棄
物の処理方法に係り、特に、各種ボイラー灰、焼却灰、
汚泥等の廃棄物中に含有される塩素、更にはフッ素、硫
黄、炭素等を効率的に除去して、セメント原料としての
有効利用を図るセメント原料用廃棄物の処理方法に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating waste materials for cement raw materials, and more particularly to various boiler ash, incinerated ash,
The present invention relates to a method for treating waste for cement raw materials that efficiently removes chlorine, fluorine, sulfur, carbon, and the like contained in wastes such as sludge and aims to effectively use the raw materials as cement raw materials.

【0002】[0002]

【従来の技術】近年、セメント工場においては、セメン
ト原料としての各種ボイラー灰、焼却灰や汚泥等の各種
廃棄物使用量が多くなる傾向にある。これは、これらの
廃棄物の海洋投棄による環境汚染を解消する対策の一つ
として、これらの廃棄物をセメント原料として利用する
ことが有効であることによる。即ち、セメントの製造に
当っては、原料を1500℃の高温で加熱するため、廃
棄物中の有害な有機物の分解が可能である上に、SO
等の有害物質を放出することもない。
2. Description of the Related Art In recent years, various types of waste such as various boiler ash, incinerated ash, and sludge as cement raw materials have tended to be increased in cement plants. This is due to the fact that it is effective to use these wastes as a raw material for cement as one of the measures to eliminate environmental pollution caused by dumping these wastes into the ocean. In other words, in the production of cement, since the raw material is heated at a high temperature of 1500 ° C., it is possible to decompose harmful organic substances in the waste, and also SO x
No harmful substances are released.

【0003】ところで、各種ボイラー灰、焼却灰や汚泥
等の廃棄物は、一般に塩素、更にはフッ素、硫黄、各種
有機物を含むため、これらの廃棄物の使用量の増加に伴
い、原料中の塩素量や、フッ素、硫黄、炭素量が増加す
る。
By the way, wastes such as various boiler ash, incinerated ash and sludge generally contain chlorine, furthermore, fluorine, sulfur and various organic substances. The amount and the amount of fluorine, sulfur and carbon increase.

【0004】一方、現在多くのセメント工場で稼動して
いる装置は、サスペンションプレヒーターとキルンとか
らなるSP及びNSP方式である。この装置は、熱効率
に優れる反面、系内の塩素やフッ素、硫黄、炭素が多く
なると、装置の腐食のみならず、プレヒーターの閉塞を
きたし、運転が不可能となる。
[0004] On the other hand, the devices currently operating in many cement plants are of the SP and NSP type comprising a suspension preheater and a kiln. Although this device is excellent in thermal efficiency, when the amount of chlorine, fluorine, sulfur, and carbon in the system increases, not only corrosion of the device, but also clogging of the pre-heater occurs, and operation becomes impossible.

【0005】従って、セメント工場でより多くの廃棄物
をセメント原料として使用して環境汚染を低減するため
には、前処理として、セメント原料に用いる廃棄物中の
塩素やフッ素、硫黄、炭素を除去する処理を施す必要が
ある。
Therefore, in order to reduce environmental pollution by using more waste as a cement raw material in a cement plant, chlorine, fluorine, sulfur and carbon in the waste used for the cement raw material must be removed as a pretreatment. Must be performed.

【0006】現在、セメント工場における脱塩素法とし
て水洗が行われている。これは、コンクリート用骨材の
除塩処理と同様に、一定の敷地内に廃棄物を置き、上部
から散水することにより、水溶性塩素を除去するもので
ある。
At present, water is washed as a dechlorination method in a cement plant. This is to remove water-soluble chlorine by placing waste in a certain site and sprinkling water from above, as in the salt removal treatment of concrete aggregate.

【0007】[0007]

【発明が解決しようとする課題】セメント原料としての
有効利用が期待される各種廃棄物中の塩素の多くは水可
溶性であり、廃棄物粒子の表面にアルカリ塩として存在
している。このため、比較的粒子の大きい粗粒廃棄物で
あれば、比表面積が小さく、付着している塩素量も少な
いことから、廃棄物を簡単に水洗いする程度で塩素を除
去できる。
Most of chlorine in various kinds of wastes expected to be effectively used as a cement raw material is water-soluble, and exists as alkali salts on the surfaces of the waste particles. Therefore, in the case of coarse-grained waste having relatively large particles, the specific surface area is small and the amount of adhered chlorine is small, so that chlorine can be removed by simply washing the waste with water.

【0008】しかしながら、各種ボイラー灰や汚泥等の
微粒子廃棄物の場合、比表面積が大きいため、付着して
いる塩素量も多い上に、廃棄物微粒子が水に懸濁してし
まうため、単なる水洗では塩素を十分に除去することが
不可能である。
However, in the case of fine particle waste such as various boiler ash and sludge, the specific surface area is large, the amount of chlorine adhering is large, and the fine particles of waste are suspended in water. It is impossible to remove chlorine sufficiently.

【0009】このため、従来、廃棄物の水洗による脱塩
素処理は、粒径数mm以上の粗粒廃棄物にのみ適用され
ており、微粒子廃棄物には適用されていない。従来は、
大量の微粒子廃棄物の脱塩素処理を経済的に行うのは困
難とされており、脱塩素を行うことができないために、
多くの廃棄物がセメント原料として使用できない状況に
ある。
For this reason, conventionally, the dechlorination treatment of waste by washing with water has been applied only to coarse waste having a particle size of several mm or more, and not to fine particle waste. conventionally,
It is considered difficult to economically dechlorinate large amounts of particulate waste, and because it is not possible to dechlorinate,
Many wastes cannot be used as cement raw materials.

【0010】なお、塩素、フッ素、硫黄、炭素を含む水
不溶性ないし水難溶性の物質は水洗で除去することはで
きず、現在、これらの有効な除去方法は提案されていな
いのが現状である。
[0010] Incidentally, water-insoluble or hardly water-soluble substances containing chlorine, fluorine, sulfur and carbon cannot be removed by washing with water, and at present, no effective method for removing these substances has been proposed.

【0011】本発明は上記従来の問題点を解決し、各種
ボイラー灰、焼却灰、汚泥等の廃棄物中に含有される塩
素、更にはフッ素、硫黄、炭素等を効率的に除去して、
セメント原料としての有効利用を図るセメント原料用廃
棄物の処理方法を提供することを目的とする。
The present invention solves the above-mentioned conventional problems and efficiently removes chlorine, fluorine, sulfur, carbon, and the like contained in wastes such as various boiler ash, incinerated ash, and sludge.
An object of the present invention is to provide a method for treating waste for cement raw materials, which is intended to be effectively used as a cement raw material.

【0012】[0012]

【課題を解決するための手段】請求項1のセメント原料
用廃棄物の処理方法は、セメント原料用廃棄物を水と混
合した後、分級するセメント原料用廃棄物の処理方法
あって、分級により得られた粗粒分をセメント原料とす
ると共に、微粒分を含むスラリーを脱水した後セメント
原料とすることを特徴とする。
Processing method cement raw material waste claim 1 Means for Solving the Problems], the cement raw material waste after mixing with water, in the processing method of classification to Rousset instrument feedstock waste
The method is characterized in that the coarse particles obtained by the classification are used as the cement raw material, and the slurry containing the fine particles is dewatered to be used as the cement raw material.

【0013】請求項のセメント原料用廃棄物の処理方
法は、請求項1の方法において、分級を湿式サイクロン
で行うことを特徴とする。
[0013] processing method according to claim 2 of the cement raw material waste, in the method of claim 1, and performs classification by a wet cyclone.

【0014】廃棄物を水と混合してスラリー化し、水溶
性塩素を溶出させた後、分級すると、水溶性塩素が十分
に除去された粗粒分が分級と同時に脱水濃縮され、含水
率が低減されるため、この粗粒分は直ちにセメント原料
として使用可能となる。一方、微粒分を含むスラリーを
脱水機で脱水することにより、脱塩素された微粒分を回
収することができる。
The waste is mixed with water to form a slurry, and water-soluble chlorine is eluted. After classification, coarse particles from which the water-soluble chlorine has been sufficiently removed are simultaneously declassified and dehydrated and concentrated to reduce the water content. Therefore, this coarse fraction can be used immediately as a cement raw material. On the other hand, by dewatering the slurry containing the fine particles with a dehydrator, the dechlorinated fine particles can be recovered.

【0015】請求項のセメント原料用廃棄物の処理方
法は、セメント原料用廃棄物を水洗した後、400℃以
上の水蒸気と接触させるセメント原料用廃棄物の処理方
法であって、セメント原料用廃棄物を水と混合した後分
級し、得られた粗粒分を400℃以上の水蒸気と接触さ
せ、微粒分を脱水した後400℃以上の水蒸気と接触さ
せることを特徴とする。
The method for treating waste for cement raw materials according to claim 3 is a method for treating waste for cement raw materials after the waste for cement raw materials is washed with water and then brought into contact with steam at 400 ° C. or higher.
After mixing cement waste with water
The obtained coarse particles are contacted with steam at 400 ° C or higher.
And dehydrate the fine particles, and then contact with steam at 400 ° C or more.
And characterized in that.

【0016】400℃以上の水蒸気と接触させることに
より、セメント原料用廃棄物の一部又は全部が熱分解さ
れ、廃棄物中の塩素化合物、フッ素化合物、硫黄化合
物、炭素化合物は、各々、下記〜式に従ってガス化
される。また、フッ素化合物から生成したフッ化水素酸
は、系内に珪石等の珪酸化合物がある場合には、下記
式の反応で珪フッ化水素となる。ここで、発生するガス
は、いずれも酸性であるため、アルカリ性の溶液で吸収
して固定することができる
By contacting with steam at 400 ° C. or higher, part or all of the cement raw material waste is thermally decomposed, and the chlorine compound, fluorine compound, sulfur compound, and carbon compound in the waste are as follows: It is gasified according to the formula. Hydrofluoric acid generated from a fluorine compound is converted into hydrogen fluorosilicate by a reaction of the following formula when a silicate compound such as silica stone is present in the system. Here, since all generated gas is acidic, it can be absorbed and fixed by an alkaline solution .

【0017】[0017]

【化1】 Embedded image

【0018】本発明では、水でセメント原料用廃棄物中
の水溶性塩素を予め溶出除去した後、上記水蒸気処理を
行うことにより、より一層効率的な脱塩素、脱フッ素、
脱硫黄、脱炭素を行える。
In the present invention, the water-soluble chlorine in the cement raw material waste is previously eluted and removed with water, and then the above-mentioned steam treatment is carried out, so that more efficient dechlorination and defluorination can be achieved.
Desulfurization and decarbonization can be performed.

【0019】[0019]

【発明の実施の形態】以下、図面を参照して本発明を詳
細に説明する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below in detail with reference to the drawings.

【0020】図1は、請求項1,2の実施例方法を示す
系統図である。
FIG. 1 is a system diagram showing a method according to the first and second embodiments.

【0021】図1に示す方法においては、スラリーホッ
パー1、スラリーポンプ2、湿式サイクロン3及び脱水
機4からなる脱塩素装置を用い、まず、スラリーホッパ
ー1にセメント原料用廃棄物と水とを投入し、混合して
スラリー化し、水溶性塩素を溶出させる。この場合、ス
ラリーを撹拌することにより効率的に溶出させる必要が
あるが、本実施例では、スラリーホッパー1とスラリー
ポンプ2とを連結し、スラリーを循環させることによ
り、スラリーポンプ2のインペラーの回転力を撹拌に利
用して、効率的に塩素を溶出させる。次いで、撹拌後の
スラリーを湿式サイクロン3で分級する。この分級によ
り、粗粒分を含むスラリーは、分級と同時に濃縮される
ため、通常の場合、含水率20%、或いはそれ以下の脱
塩素された粗粒分が得られる。このものは直ちにセメン
ト原料として使用可能である。一方、微粒分を含むスラ
リーは分級により希釈されるため、塩素の溶出が促進さ
れる。このものは、脱水機4で脱水してセメント原料と
して使用することができる。なお、この湿式サイクロン
3で分級された微粒分を含むスラリーが低濃度スラリー
である場合には、この一部をスラリーホッパーに戻して
も良い。
In the method shown in FIG. 1, a dechlorination apparatus including a slurry hopper 1, a slurry pump 2, a wet cyclone 3 and a dehydrator 4 is used. And mix to form a slurry to elute the water-soluble chlorine. In this case, it is necessary to efficiently elute the slurry by stirring it. In this embodiment, the slurry hopper 1 and the slurry pump 2 are connected and the slurry is circulated to rotate the impeller of the slurry pump 2. The chlorine is efficiently eluted by using the power for stirring. Next, the slurry after the stirring is classified by the wet cyclone 3. By this classification, the slurry containing the coarse particles is concentrated at the same time as the classification, so that in general, a dechlorinated coarse particle having a water content of 20% or less is obtained. It can be used immediately as a cement raw material. On the other hand, the slurry containing fine particles is diluted by classification, so that the elution of chlorine is promoted. This can be dewatered by the dehydrator 4 and used as a cement raw material. If the slurry containing fine particles classified by the wet cyclone 3 is a low-concentration slurry, a part of the slurry may be returned to the slurry hopper.

【0022】なお、セメント原料用廃棄物と混合する水
の量は、セメント原料用廃棄物の塩素含有量や粒度によ
っても異なるが、通常の場合セメント原料用廃棄物10
0重量部に対して200〜2000重量部程度とされ
る。
The amount of water mixed with the cement raw material waste depends on the chlorine content and the particle size of the cement raw material waste.
It is about 200 to 2000 parts by weight with respect to 0 parts by weight.

【0023】このような方法によれば、スラリーホッパ
ー1とスラリーポンプ2とを連結し、両者間でスラリー
を循環させることで、効率的に塩素を溶出させることが
でき、これにより、大量の微粒子廃棄物を処理する場合
でも、大型の撹拌装置を必要とすることなく、容易に塩
素の溶出処理を行える。また、大量のスラリーを脱水す
るには、大型の脱水設備が必要となるが、湿式サイクロ
ン3と脱水機4とを併用することで、狭い敷地内での効
率的な脱水が可能である。
According to such a method, chlorine can be efficiently eluted by connecting the slurry hopper 1 and the slurry pump 2 and circulating the slurry between the two, thereby enabling a large amount of fine particles to be eluted. Even in the case of treating waste, the elution treatment of chlorine can be easily performed without the need for a large-scale stirring device. In addition, large-scale dewatering equipment is required to dewater a large amount of slurry. However, by using the wet cyclone 3 and the dehydrator 4 together, efficient dehydration in a narrow site is possible.

【0024】このような本発明による脱塩素処理は、特
に、従来の水洗による方法では脱塩素が困難な、各種ボ
イラー灰や汚泥等の微粒子廃棄物の処理に有効であり、
通常の場合、塩素含有率300ppm以上の廃棄物を塩
素含有率100ppm以下にまで低減することができ
る。
Such a dechlorination treatment according to the present invention is particularly effective for treating various kinds of fine particle waste such as boiler ash and sludge, which are difficult to dechlorinate by a conventional method of washing with water.
In a normal case, waste having a chlorine content of 300 ppm or more can be reduced to a chlorine content of 100 ppm or less.

【0025】図2は請求項の実施例方法に用いられる
装置の一例を示す側面図である。
FIG. 2 is a side view showing an example of an apparatus used in the method according to the third embodiment.

【0026】請求項の方法は、要するに被処理廃棄物
水と混合した後分級して得られた相粒分、及び微粒分
を脱水したものを400℃以上の高温水蒸気と接触させ
るというものであり、そのための装置としては、粉粒体
を加熱する手段と、この加熱手段の雰囲気に水蒸気を含
ませるための水蒸気添加手段とを備えている各種のもの
を用いることができる。図2は回転胴5の一端側から原
料(被処理廃棄物)と高温水蒸気とを導入し、回転胴5
内で原料と高温水蒸気とを接触させ、製品出口6から処
理済廃棄物を取り出すようにした装置を示している。な
お、7は駆動ローラ、8は支持ローラを示す。もちろ
ん、本発明方法は、図2以外の各種の装置を用いて実施
できる。
The method according to claim 3 is a method of mixing the waste to be treated with water and then classifying the waste and the fine particles.
The dewatered material is brought into contact with high-temperature steam of 400 ° C. or more, and as an apparatus therefor, means for heating the powder and granules, and steam addition means for including steam in the atmosphere of the heating means Various types having the following can be used. FIG. 2 shows that a raw material (waste to be treated) and high-temperature steam are introduced from one end of the rotating drum 5 and the rotating drum 5 is rotated.
1 shows an apparatus in which a raw material and high-temperature steam are brought into contact with each other to take out treated waste from a product outlet 6. Reference numeral 7 denotes a driving roller, and reference numeral 8 denotes a support roller. Of course, the method of the present invention can be implemented using various devices other than FIG.

【0027】これにより、セメント原料用廃棄物中の塩
素、フッ素、硫黄、炭素は、前述の〜の反応により
ガス化され、セメント原料用廃棄物から効率的に除去さ
れる。
Thus, chlorine, fluorine, sulfur, and carbon in the waste for cement raw material are gasified by the above-mentioned reaction (1), and are efficiently removed from the waste for cement raw material.

【0028】なお、セメント原料用廃棄物を処理する水
蒸気の温度は400℃以上であるが、処理時間を短縮す
るためには、高温である程良く、800℃以上の水蒸気
を用いるのが好ましい。水蒸気量及び処理時間は、セメ
ント原料用廃棄物中の塩素、フッ素、硫黄、炭素含有量
や、処理するセメント原料用廃棄物量、水蒸気温度等に
より適宜決定される。
The temperature of the steam for treating the cement raw material waste is 400 ° C. or higher, but in order to shorten the processing time, the higher the temperature, the better, and it is preferable to use the steam of 800 ° C. or higher. The amount of steam and the treatment time are appropriately determined according to the chlorine, fluorine, sulfur, and carbon contents in the waste for cement raw material, the amount of waste for cement raw material to be treated, the steam temperature, and the like.

【0029】本発明においては、前述のセメント原料用
廃棄物と水との混合、分級による脱塩素処理後に上記水
蒸気による処理を行うため、廃棄物中の水可溶性塩素を
除去した後に水蒸気処理することでより一層効率的な脱
塩素、脱フッ素、脱硫黄、脱炭素を行える。
In the present invention, the steam treatment after removal of water-soluble chlorine mixtures, classifying the row processing by the steam after dechlorination by Utame, in the waste with cement raw material waste and water above This makes it possible to perform dechlorination, defluorination, sulfur removal, and carbon removal more efficiently.

【0030】[0030]

【実施例】以下に実施例及び比較例を挙げて本発明をよ
り具体的に説明するが、本発明はその要旨を超えない限
り、以下の実施例に限定されるものではない。
The present invention will be described more specifically with reference to examples and comparative examples, but the present invention is not limited to the following examples unless it exceeds the gist.

【0031】実施例1 図1に示す方法に従って、表1に示す各種のセメント原
料用廃棄物の脱塩素処理を行った。
Example 1 According to the method shown in FIG. 1, various kinds of cement raw material wastes shown in Table 1 were dechlorinated.

【0032】まず、セメント原料用廃棄物(塩素含有量
は表1に示す通り。)に、表1に示す量の水を混合し、
スラリーホッパー1とスラリーポンプ2とを循環させ
て、表1に示す時間撹拌処理した。
First, the amount of water shown in Table 1 was mixed with the waste for cement raw materials (the chlorine content is as shown in Table 1).
The slurry hopper 1 and the slurry pump 2 were circulated, and a stirring treatment was performed for the time shown in Table 1.

【0033】これを湿式サイクロンで分級し、表1に示
す平均粒径、含水率及び塩素含有率の粗粒分を得た。一
方、微粒分を含むスラリーを脱水機で脱水し、表1に示
す平均粒径、含水率及び塩素含有率の微粒分を得た。
This was classified by a wet cyclone to obtain coarse particles having an average particle diameter, a water content and a chlorine content shown in Table 1. On the other hand, the slurry containing fine particles was dehydrated by a dehydrator to obtain fine particles having an average particle diameter, a water content and a chlorine content shown in Table 1.

【0034】[0034]

【表1】 [Table 1]

【0035】表1より、本発明によれば、セメント原料
用廃棄物中の塩素を効率的に除去できることが明らかで
ある。
From Table 1, it is clear that according to the present invention, chlorine in wastes for cement raw materials can be efficiently removed.

【0036】比較例1 実施例1のNo.1と同様にして流動床ボイラー灰と水
とを混合した後、湿式サイクロンで分級することなく脱
水機で脱水したところ、得られた粒分は、含水率47
%、塩素含有率180ppmで、塩素除去効率は悪かっ
た。
Comparative Example 1 After mixing the fluidized-bed boiler ash and water in the same manner as in Example 1, the mixture was dewatered by a dehydrator without classification by a wet cyclone.
% And a chlorine content of 180 ppm, the chlorine removal efficiency was poor.

【0037】比較例2 図3に示す方法に従って、表2に示すセメント原料用廃
棄物の脱塩素、脱フッ素、脱硫黄、脱炭素を行った。
Comparative Example 2 In accordance with the method shown in FIG. 3, the waste materials for cement raw materials shown in Table 2 were subjected to dechlorination, defluorination, desulfurization and decarbonization.

【0038】図3に示す方法においては、セメント原料
用廃棄物10をマッフル炉11の磁性管12内に入れ、
この磁性管12内に、70℃程度の温水13を酸素ボン
ベ14から流量計15を経て送給される酸素で搬送し、
加熱することで水蒸気処理する。セメント原料用廃棄物
の熱分解で発生したガスは、炭酸ナトリウム水溶液16
等のアルカリ溶液で吸収して固定する。
In the method shown in FIG. 3, waste 10 for cement raw material is put in a magnetic tube 12 of a muffle furnace 11,
Into this magnetic tube 12, hot water 13 of about 70 ° C. is transported by oxygen supplied from an oxygen cylinder 14 through a flow meter 15,
Steam treatment is performed by heating. Gas generated by thermal decomposition of cement raw material waste is
Absorb and fix with an alkaline solution such as

【0039】水蒸気温度、水蒸気流量、処理時間及び処
理後のセメント原料用廃棄物の塩素量、フッ素量、硫黄
量、及び強熱減量は表2に示す通りであり、本発明によ
れば、効率的な脱塩素、脱フッ素、脱硫黄、脱炭素を行
えることが明らかである。
The steam temperature, the steam flow rate, the treatment time, and the chlorine content, fluorine content, sulfur content, and ignition loss of the cement raw material waste after treatment are as shown in Table 2. According to the present invention, the efficiency was It is clear that typical dechlorination, defluorination, desulfurization and decarbonization can be performed.

【0040】比較例 水蒸気温度を300℃としたこと以外は比較例2のN
o.4と同様に行ったところ、処理後のセメント原料用
廃棄物の塩素量、フッ素量、硫黄量、及び強熱減量は表
2に示す通りであり、脱塩素、脱フッ素、脱硫黄、脱炭
素を十分に行うことはできなかった。
Comparative example3  Except that the steam temperature was 300 ° CComparisonN of Example 2
o. After performing the same procedure as in 4, for the cement material after treatment
The amounts of chlorine, fluorine, sulfur, and ignition loss of waste are shown in the table.
As shown in 2, dechlorination, defluorination, desulfurization, decarburization
I couldn't do enough.

【0041】[0041]

【表2】 [Table 2]

【0042】実施例 セメント原料用廃棄物として、表2のNo.4に示す塩
素量、フッ素量、硫黄量及び強熱減量の流動床ボイラ灰
を、実施例1のNo.1と同様にして脱塩素処理した
後、得られた粗粒分と微粒分とをそれぞれ比較例2のN
o.4と同様にして水蒸気処理した。
Example 2 As wastes for cement raw materials, The fluidized-bed boiler ash having the chlorine amount, the fluorine amount, the sulfur amount, and the loss on ignition shown in No. 4 was subjected to No. After the dechlorination treatment was performed in the same manner as in Example 1, the obtained coarse particles and fine particles were separated by the N method of Comparative Example 2.
o. Steam treatment was performed in the same manner as in Example 4.

【0043】その結果、処理後の粗粒分及び微粒分の塩
素量、フッ素量、硫黄量及び強熱減量は表3に示す通り
となり、効率的な脱塩素、脱フッ素、脱硫黄、脱炭素を
行うことができた。
As a result, the amount of chlorine, the amount of fluorine, the amount of sulfur, and the loss on ignition of the coarse and fine particles after the treatment are as shown in Table 3, and efficient dechlorination, defluorination, de-sulfurization, decarbonization Was able to do.

【0044】[0044]

【表3】 [Table 3]

【0045】[0045]

【発明の効果】以上詳述した通り、本発明のセメント原
料用廃棄物の処理方法によれば、セメント原料用廃棄物
中の塩素、更には、塩素、フッ素、硫黄、炭素を効率的
に除去して、セメント原料として大量に有効利用するこ
とが可能である。
As described in detail above, according to the method for treating waste for cement raw materials of the present invention, chlorine in waste for cement raw materials, and furthermore, chlorine, fluorine, sulfur and carbon are efficiently removed. Thus, it can be effectively used as a cement raw material in a large amount.

【0046】従って、本発明によれば、埋立、海洋投棄
等で処分されている廃棄物をセメント原料として無害化
すると共に有効利用することで環境汚染問題を解消する
と共に、原料コストの低減を図ることができ、本発明の
工業的有用性は極めて大きい。
Therefore, according to the present invention, the waste disposed of by landfilling, dumping at sea, etc. is rendered harmless as a cement raw material and is effectively used, thereby solving the environmental pollution problem and reducing the raw material cost. Therefore, the industrial utility of the present invention is extremely large.

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

【図1】本発明によるセメント原料用廃棄物の脱塩素方
法の一実施例方法を示す系統図である。
FIG. 1 is a system diagram showing an embodiment of a method for dechlorinating waste for cement raw materials according to the present invention.

【図2】本発明によるセメント原料用廃棄物の脱塩素、
脱フッ素、脱硫黄、脱炭素方法を示す装置構成図であ
る。
FIG. 2 shows the dechlorination of cement raw material waste according to the present invention;
It is an apparatus block diagram which shows a defluorination, a sulfur removal, and a carbon removal method.

【図3】実施例2におけるセメント原料用廃棄物の脱塩
素、脱フッ素、脱硫黄、脱炭素方法を示す装置構成図で
ある。
FIG. 3 is an apparatus configuration diagram showing a method for dechlorination, defluorination, sulfur removal, and decarbonization of cement raw material waste in Example 2.

【符号の説明】[Explanation of symbols]

1 スラリーホッパー 2 スラリーポンプ 3 湿式サイクロン 4 脱水機 10 廃棄物 11 マッフル炉 12 磁性管 13 温水 14 酸素ボンベ 15 流量計 16 炭酸ナトリウム水溶液 DESCRIPTION OF SYMBOLS 1 Slurry hopper 2 Slurry pump 3 Wet cyclone 4 Dehydrator 10 Waste 11 Muffle furnace 12 Magnetic tube 13 Hot water 14 Oxygen cylinder 15 Flow meter 16 Sodium carbonate aqueous solution

フロントページの続き (72)発明者 坂本 知彦 福岡県北九州市八幡西区洞南町1番地1 三菱マテリアル株式会社セメント開発 センター内 (72)発明者 江波戸 一郎 福岡県北九州市八幡西区洞南町1番地1 三菱マテリアル株式会社セメント開発 センター内 (72)発明者 三小田 典夫 福岡県北九州市八幡西区洞南町1番地1 三菱マテリアル株式会社セメント開発 センター内 (56)参考文献 特開 平7−51652(JP,A) 特表 平2−504626(JP,A) (58)調査した分野(Int.Cl.7,DB名) C04B 7/00 - 7/60 C04B 18/00 - 18/30 Continuing from the front page (72) Inventor Tomohiko Sakamoto 1-Donan-cho, Yawatanishi-ku, Kitakyushu-city, Fukuoka Prefecture Inside the Cement Development Center of Mitsubishi Materials Corporation (72) Inventor Ichiro Ebato 1-Donami-cho, Yawata-Nishi-ku, Fukuoka Prefecture 1 Mitsubishi Materials Inside the Cement Development Center Co., Ltd. (72) Norio Sankoda, 1-Donan-cho, Yawata-nishi-ku, Kitakyushu-city, Fukuoka Prefecture 1 Inside the Cement Development Center, Mitsubishi Materials Corporation (56) References JP-A-7-51652 (JP, A) Hei 2-504626 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) C04B 7 /00-7/60 C04B 18/00-18/30

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 セメント原料用廃棄物を水と混合した
後、分級するセメント原料用廃棄物の処理方法であっ
て、 分級により得られた粗粒分をセメント原料とすると共
に、微粒分を含むスラリーを脱水した後セメント原料と
することを特徴とするセメント原料用廃棄物の処理方
法。
1. A cement raw material waste is mixed with water.
After, classifyRuseOf raw material wasteSo
hand, When the coarse particles obtained by classification are used as cement raw materials,
Then, after dewatering the slurry containing fine particles,
Of waste for cement raw materials characterized by the following
Law.
【請求項2】 請求項1の方法において、分級を湿式サ
イクロンで行うことを特徴とするセメント原料用廃棄物
の処理方法。
2. The method according to claim 1, wherein the classification is performed by a wet cyclone.
【請求項3】 セメント原料用廃棄物を水洗した後、4
00℃以上の水蒸気と接触させるセメント原料用廃棄物
の処理方法であって、 セメント原料用廃棄物を水と混合した後分級し、得られ
た粗粒分を400℃以上の水蒸気と接触させ、微粒分を
脱水した後400℃以上の水蒸気と接触させることを特
徴とするセメント原料用廃棄物の処理方法。
3. After the cement raw material waste is washed with water,
Contact with steam over 00 ° CRuseRaw material waste
Processing methodAnd After mixing the waste for cement raw materials with water and classifying it,
The coarse fraction is brought into contact with steam at 400 ° C or higher,
After dehydration, contact with steam of 400 ° C or more
The method of treating waste for cement raw materials.
JP33045595A 1995-12-19 1995-12-19 Waste treatment method for cement raw materials Expired - Lifetime JP3284861B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP33045595A JP3284861B2 (en) 1995-12-19 1995-12-19 Waste treatment method for cement raw materials

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP33045595A JP3284861B2 (en) 1995-12-19 1995-12-19 Waste treatment method for cement raw materials

Publications (2)

Publication Number Publication Date
JPH09165243A JPH09165243A (en) 1997-06-24
JP3284861B2 true JP3284861B2 (en) 2002-05-20

Family

ID=18232814

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP3284861B2 (en)

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006095383A (en) * 2004-09-28 2006-04-13 Mitsui Eng & Shipbuild Co Ltd Method and apparatus for treating decomposed gas in pollutant purifying apparatus
JP4329906B2 (en) * 2005-02-02 2009-09-09 現代建設株式會社 Method and system for removing chlorine compounds contained in bottom ash
JP2009061365A (en) * 2007-09-04 2009-03-26 Sumitomo Osaka Cement Co Ltd Washing method for incineration ash
JP4937074B2 (en) * 2007-10-04 2012-05-23 三菱重工環境・化学エンジニアリング株式会社 Incineration ash washing method and system
JP2009242741A (en) * 2008-03-31 2009-10-22 Nippon Paper Industries Co Ltd Method of manufacturing filler or pigment from papermaking sludge
JP5561326B2 (en) * 2012-08-06 2014-07-30 住友大阪セメント株式会社 Cleaning method of incineration ash
JP6189717B2 (en) * 2013-11-07 2017-08-30 太平洋セメント株式会社 Method for converting incineration ash to cement

Also Published As

Publication number Publication date
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