JPH09290234A - Method of reforming coal ash and method of using reformed cool ash - Google Patents

Method of reforming coal ash and method of using reformed cool ash

Info

Publication number
JPH09290234A
JPH09290234A JP12630896A JP12630896A JPH09290234A JP H09290234 A JPH09290234 A JP H09290234A JP 12630896 A JP12630896 A JP 12630896A JP 12630896 A JP12630896 A JP 12630896A JP H09290234 A JPH09290234 A JP H09290234A
Authority
JP
Japan
Prior art keywords
coal ash
thermal spray
thermal spraying
ash
furnace body
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.)
Granted
Application number
JP12630896A
Other languages
Japanese (ja)
Other versions
JP3687869B2 (en
Inventor
Kazuo Maeda
一夫 前田
Hideo Ide
秀夫 井出
Akio Ishii
章生 石井
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.)
Nippon Steel Corp
Original Assignee
Nippon Steel 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 Nippon Steel Corp filed Critical Nippon Steel Corp
Priority to JP12630896A priority Critical patent/JP3687869B2/en
Publication of JPH09290234A publication Critical patent/JPH09290234A/en
Application granted granted Critical
Publication of JP3687869B2 publication Critical patent/JP3687869B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

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  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To burn and remove carbon contained in coal ash and at the same time to melt the carbon ash to make its granular shape a spherical shape by melt-spraying the coal ash, to improve its fluidity when it is used as a concrete admixture substituting for sand to efficiently use all coal ash generated and also to save resources. SOLUTION: A thermal spraying device constituted of a thermal spraying burner, a lance, a utility control panel and a powder feeder and a furnace body for providing a space for performing thermal spraying are used. The thermal spraying device is installed in an opening of the furnace body so that flames formed by the thermal spraying burner 1 may be blown into the furnace body. Coal ash 2 is sprayed from the thermal spraying burner 1 together with carrier gas so that they may be passed through a thermal spraying flame 10.

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、発電所などで石炭
燃焼時に発生する石炭灰の改質方法及び改質した石炭灰
の使用方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for reforming coal ash generated during coal combustion in a power plant and a method for using the reformed coal ash.

【0002】[0002]

【従来の技術】現在、全石炭灰の約60%は、セメント
原料等として再利用されているが、残りの約40%は産
業廃棄物として埋め立てなどにより処理されている。し
かし、今後とも大量に発生する石炭灰の廃棄処理に際し
ては、埋め立て地及び環境に問題が生じる。
2. Description of the Related Art Currently, about 60% of all coal ash is reused as a raw material for cement and the like, and the remaining about 40% is treated as industrial waste by landfill. However, disposal of coal ash, which will be generated in large quantities, will cause problems in the landfill and the environment.

【0003】石炭灰には未燃カーボンが含まれており、
その量が多いと石炭灰をコンクリートの混和材料として
使用する場合、セメントに添加されている減水剤、空気
連行剤が石炭灰に含まれるカーボンに吸着され、各添加
剤の機能を損なうことからカーボン量によって使用に制
限がある。石炭灰に含まれるカーボンの除去について
は、特開平4−300663号公報に提案されている。
すなわち、焼却炉より排出される石炭灰を粉砕装置によ
って粉砕すると、未燃カーボンをシリカ分で包んだ状態
の石炭灰がシリカ分と未燃カーボンに分離する。更にシ
リカ分と未燃カーボンとが分離した状態の石炭灰を選別
装置によってシリカ分と未燃カーボンとに選別し、未燃
カーボンを除去する方法である。
Coal ash contains unburned carbon,
If a large amount of coal ash is used as an admixture material for concrete, the water reducing agent and air entraining agent added to the cement are adsorbed by the carbon contained in the coal ash, and the function of each additive is impaired. Use is limited depending on the amount. The removal of carbon contained in coal ash has been proposed in JP-A-4-300663.
That is, when the coal ash discharged from the incinerator is crushed by the crushing device, the coal ash in a state in which unburned carbon is wrapped with silica is separated into silica and unburned carbon. Further, the coal ash in a state where the silica content and the unburned carbon are separated is sorted into a silica content and unburned carbon by a sorting device to remove the unburned carbon.

【0004】また、特開平4−70529号公報には、
石炭灰を石炭灰改質炉出口のダストを含む排ガスに混合
し予熱した後、排ガスから分離して石炭灰改質炉に供給
するとともに、石炭灰改質炉に酸素富化空気を供給す
る。更にこの酸素富化空気は改質炉外の改質灰冷却器で
改質灰と熱交換して予熱された後、改質炉内の炉内加熱
器で燃焼ガスと熱交換して加熱される方法が提案されて
いる。
Further, Japanese Patent Laid-Open No. 4-70529 discloses that
After the coal ash is mixed with the exhaust gas containing dust at the outlet of the coal ash reforming furnace and preheated, it is separated from the exhaust gas and supplied to the coal ash reforming furnace, and oxygen-enriched air is supplied to the coal ash reforming furnace. Furthermore, this oxygen-enriched air is preheated by exchanging heat with the reformed ash in the reformed ash cooler outside the reforming furnace, and then heated by exchanging heat with the combustion gas in the in-reactor inside the reforming furnace. Methods have been proposed.

【0005】[0005]

【発明が解決しようとする課題】しかしながら、上記の
方法では工程が複雑で設備規模も大きく、石炭灰の品質
によっては条件設備が煩雑となり、処理効率が低いとい
う問題点がある。本発明は、コンクリートの混和材料と
して使用できるように石炭灰のカーボン量を低減するよ
う改質して、発生する石炭灰の全量を有効に利用するこ
とを目的とする。
However, in the above method, there are problems that the process is complicated, the equipment scale is large, the condition equipment is complicated depending on the quality of the coal ash, and the treatment efficiency is low. An object of the present invention is to modify coal ash so that it can be used as an admixture for concrete so as to reduce the amount of carbon, and to effectively utilize the total amount of coal ash generated.

【0006】[0006]

【課題を解決するための手段】本発明は、前記課題を解
決すべく提供されたもので、その要旨とするところは、
下記の通りである。 (1) 溶射バーナー、ランス、ユーティリティ制御盤
及び粉体供給機から構成される溶射装置において、溶射
バーナーに形成される火炎が炉体内部に吹き込まれるよ
うに炉体開口部に設置し、該溶射バーナーから石炭灰を
溶射火炎内を通過するようにキャリアガスと共に噴射し
て、石炭灰に含まれるカーボンの一部または全部を燃焼
除去すると同時に石炭灰を溶融させてその形状を球状化
する。
SUMMARY OF THE INVENTION The present invention has been provided to solve the above problems, and the gist of the invention is as follows.
It is as follows. (1) In a thermal spraying apparatus composed of a thermal spraying burner, a lance, a utility control panel, and a powder feeder, the thermal spraying burner is installed in the furnace body opening so that the flame formed in the thermal spraying burner is blown into the furnace body. Coal ash is injected from a burner together with a carrier gas so as to pass through the thermal spray flame to burn off some or all of the carbon contained in the coal ash, and at the same time melt the coal ash to make it spherical.

【0007】(2) (1)の方法で改質した石炭灰を
コンクリートの砂の代替に使用する。本発明の石炭灰改
質方法は、石炭灰をキャリアガスと共に高温の溶射火炎
内に、噴射すると、石炭灰は溶射火炎からの輻射熱によ
り火炎通過時に高温となる。その時、石炭灰に含まれる
カーボンは着火温度に到達しキャリアガスの酸素によっ
て、カーボンは燃焼し石炭灰に含まれるカーボンは除去
される。また、同時に石炭灰自体も溶融し、石炭灰の粒
形状は球状を呈する。溶射バーナーを炉体開口部に設置
して、溶射火炎を炉内に吹き込むようにすることで、炉
内温度は、溶射火炎により高温となり大気中で溶射火炎
を形成して上記の石炭灰の改質を行う場合に比し格段に
熱効率が向上して、石炭灰の処理量が増大する。石炭灰
に含まれるカーボンを除去でき、かつ、石炭灰自体を球
状とできることから、コンクリートの砂の代替として改
質した石炭灰を使用することが可能となり、さらに石炭
灰の粒形状を球状とできることからセメント、砂利等と
の配合において流動性が向上し、充填性も良好となる。
(2) The coal ash modified by the method of (1) is used as a substitute for concrete sand. In the coal ash reforming method of the present invention, when coal ash is injected into a high-temperature spray flame together with a carrier gas, the coal ash becomes high in temperature when passing through the flame due to radiant heat from the spray flame. At that time, the carbon contained in the coal ash reaches the ignition temperature, the oxygen in the carrier gas burns the carbon, and the carbon contained in the coal ash is removed. At the same time, the coal ash itself also melts, and the particle shape of the coal ash is spherical. By installing a thermal spray burner at the opening of the furnace body and blowing the thermal spray flame into the furnace, the temperature inside the furnace becomes high due to the thermal spray flame, forming a thermal spray flame in the atmosphere and modifying the above coal ash. Compared with the case of quality, the thermal efficiency is remarkably improved and the throughput of coal ash is increased. Since the carbon contained in the coal ash can be removed, and the coal ash itself can be made spherical, it is possible to use the modified coal ash as a substitute for concrete sand, and the particle shape of the coal ash can be made spherical. Therefore, when mixed with cement, gravel, etc., the fluidity is improved and the filling property is also improved.

【0008】[0008]

【発明の実施の形態】以下、本発明の実施例を図面を参
照しつつ説明する。本発明の石炭灰の改質方法の一実施
例を図1に示す。図1において、ランス2は溶射バーナ
ー1を接続して支持すると共にランス駆動機3に搭載さ
れ、ランス駆動機3の前後駆動によりランス2を前後進
して、溶射バーナー1に形成される溶射火炎10を炉体
6aの内部に吹き込むように炉体6aの開口部に設置さ
れる。 改質されるユーティリティは、一次側ユーティ
リティ配管9aからユーティリティ制御盤4に供給さ
れ、ユーティリティ制御盤4において、所定の圧力、流
量に調整後、燃料ガス配管9b、冷却水配管9c、ラン
ス2を経て、溶射バーナー1に至る。燃料ガスは溶射バ
ーナー1から噴射、燃焼して溶射火炎10を形成する。
冷却水は、溶射バーナー1を折り返し点として、ランス
2及び冷却水配管9dを経て排水される。また、ユーテ
ィリティ制御盤4において、所定の圧力、流量に調整さ
れたキャリアガスはキャリアガス配管9eを経て粉体ホ
ッパー5bと切り出し機5cで構成される粉給機に供給
され、切り出し機5cで所定量切り出した改質前石炭灰
11をキャリアガスと共に粉体配管9f、ランス2を経
て溶射バーナー1から溶射火炎10内に噴射される。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described below with reference to the drawings. An embodiment of the method for reforming coal ash according to the present invention is shown in FIG. In FIG. 1, a lance 2 is connected to and supports the thermal spray burner 1 and is mounted on a lance driving machine 3, and the lance 2 is moved forward and backward by the lance driving machine 3 to move forward and backward to form a thermal spray flame formed on the thermal spray burner 1. It is installed in the opening of the furnace body 6a so that 10 is blown into the furnace body 6a. The utility to be reformed is supplied from the primary side utility pipe 9a to the utility control panel 4, and after being adjusted to a predetermined pressure and flow rate in the utility control panel 4, the utility gas is passed through the fuel gas pipe 9b, the cooling water pipe 9c, and the lance 2. , To the thermal spray burner 1. The fuel gas is injected from the thermal spray burner 1 and burned to form a thermal spray flame 10.
The cooling water is drained through the lance 2 and the cooling water pipe 9d with the thermal spray burner 1 as a turning point. Further, in the utility control panel 4, the carrier gas adjusted to a predetermined pressure and flow rate is supplied to the powder feeder composed of the powder hopper 5b and the cutting machine 5c through the carrier gas pipe 9e, and the cutting machine 5c is used. The pre-reformation coal ash 11 cut out in a fixed amount is jetted together with the carrier gas from the thermal spray burner 1 into the thermal spray flame 10 through the powder pipe 9f and the lance 2.

【0009】改質前石炭灰11の粉体ホッパー5bへの
供給は、粉体ホッパー5bの上方に開閉弁5dを介して
設置した補給用粉体ホッパー5aに改質前石炭灰11を
投入しておき、開閉弁5dを開放することにより補給用
粉体ホッパー5aから粉体ホッパー5bに改質前石炭灰
11を落下して投入する。粉体ホッパー5bへの投入に
より補給用粉体ホッパー5aの改質前石炭灰の残量が所
定量まで減量すると、補給用粉体ホッパー5aに改質前
石炭灰11を投入して粉体ホッパー5bへの供給の準備
をしておく。
The unmodified coal ash 11 is supplied to the powder hopper 5b by supplying the unmodified coal ash 11 to the replenishment powder hopper 5a installed above the powder hopper 5b through the on-off valve 5d. In addition, by opening the on-off valve 5d, the pre-reforming coal ash 11 is dropped from the replenishing powder hopper 5a and dropped into the powder hopper 5b. When the remaining amount of the pre-reforming coal ash in the replenishing powder hopper 5a is reduced to a predetermined amount by charging the refilling powder hopper 5b, the pre-reforming coal ash 11 is fed into the replenishing powder hopper 5a and the powder hopper Prepare for supply to 5b.

【0010】炉体6aには、炉体6a内の燃料排ガスを
強制排気すると共に燃料排ガス中の改質後石炭灰12を
分離回収するため、炉体頂部6aからの導管を通じて集
塵機6bを設置している。溶射火炎10に噴射された改
質前石炭灰11は、溶射火炎10を通過して、カーボン
の燃焼や改質前石炭灰11の溶融により改質され、重力
により炉体6aの底部に堆積する。所定量堆積した改質
後石炭灰12は、炉体6a底部に設置された開閉蓋7a
を開放することで、開閉蓋7aの下方に設置した回収箱
8aに落下、堆積させることで改質後石炭灰12を炉体
6aから回収する。一方、溶射火炎10を通過して、燃
焼排ガスと共に集塵機6bに入り、集塵機6b内に設置
されているフィルター(図示せず)で改質後石炭灰12
は分離され、集塵機6bの下方に所定量堆積すると、集
塵機6b下方に設置された開閉蓋7bを開放することで
回収箱8bに落下、堆積させることで改質後石炭灰12
を集塵機6bから回収する。
A dust collector 6b is installed in the furnace body 6a through a conduit from the top 6a of the furnace body 6a in order to forcibly exhaust the fuel exhaust gas in the furnace body 6a and separate and recover the reformed coal ash 12 in the fuel exhaust gas. ing. The pre-reformation coal ash 11 injected into the thermal spray flame 10 passes through the thermal spray flame 10, is reformed by burning carbon and melting the pre-reformation coal ash 11, and is deposited on the bottom of the furnace body 6a by gravity. . The reformed coal ash 12 accumulated in a predetermined amount is provided with an opening / closing lid 7a installed at the bottom of the furnace body 6a.
Is opened, the coal ash 12 after reforming is recovered from the furnace body 6a by dropping and depositing it in a recovery box 8a installed below the opening / closing lid 7a. On the other hand, after passing through the spray flame 10, it enters the dust collector 6b together with the combustion exhaust gas, and is reformed with the filter (not shown) installed in the dust collector 6b.
Are separated, and when a predetermined amount is deposited below the dust collector 6b, the opening / closing lid 7b installed below the dust collector 6b is opened to drop and deposit in the collection box 8b.
Are collected from the dust collector 6b.

【0011】図1に示した回収方法で、石炭を燃料とす
る発電所から発生した石炭灰を、燃料ガスにプロパン、
支援ガスに酸素を使用し、溶射バーナー内でプロパンと
酸素を予混合して溶射バーナーに形成される溶射火炎内
に、キャリアガスの酸素と共に噴射することで、石炭灰
中のカーボンは溶射火炎通過中に燃焼(カーボン+酸
素)して除去される。このときの火炎温度は2200℃
〜2300℃の範囲であった。また、同時に石炭灰自体
が溶融してガラス化(非晶質)すると共に粒形状は球状
を呈する(表1)。
In the recovery method shown in FIG. 1, coal ash generated from a coal-fired power plant is used as fuel gas for propane,
By using oxygen as a supporting gas and premixing propane and oxygen in the thermal spray burner and injecting it together with oxygen in the carrier gas into the thermal spray flame formed in the thermal spray burner, the carbon in the coal ash passes through the thermal spray flame. It is burned (carbon + oxygen) and removed. The flame temperature at this time is 2200 ℃
Was in the range of ˜2300 ° C. At the same time, the coal ash itself melts and vitrifies (amorphous), and the grain shape is spherical (Table 1).

【0012】[0012]

【表1】 [Table 1]

【0013】溶射バーナーを炉外の大気中において前記
と同様の改質を行った場合、溶射火炎から大気への放散
熱量が増加して石炭灰への伝熱量が低下するため、石炭
灰の供給量は約30〜40%少なくなる。また、石炭灰
自体がガラス化するため、石炭灰に含まれるカーボンが
燃焼除去後に残存してもガラスで包含できるため、残存
カーボンが減水剤、空気連行剤等のセメント添加剤に及
ぼす影響は無い。
When the thermal spray burner is reformed in the atmosphere outside the furnace in the same manner as described above, the amount of heat dissipated from the thermal spray flame to the atmosphere increases and the amount of heat transfer to the coal ash decreases. The amount is reduced by about 30-40%. In addition, since the coal ash itself vitrifies, the carbon contained in the coal ash can be included in the glass even if it remains after combustion removal, so there is no effect of residual carbon on cement additives such as water reducing agents and air entraining agents. .

【0014】なお、燃料ガスとしてプロパンに限定する
ものではなく、石炭灰を火炎通過時に溶融できる高温火
炎を形成する、例えばアセチレン、コークス炉発生ガ
ス、水素等であっても良く、液体燃料として例えば灯油
を、固体燃料として例えば微粉炭、金属アルミ、金属シ
リコンを使用しても良い。支援ガスも前記の燃料ガスと
混合して高温火炎が得られるなら酸素濃度を限定するも
のではない。これらの燃料の違いによって火炎温度も異
なってくる。
The fuel gas is not limited to propane, but may be acetylene, coke oven gas, hydrogen or the like that forms a high temperature flame that can melt coal ash when passing through a flame. Kerosene may be used as the solid fuel, for example, pulverized coal, metallic aluminum or metallic silicon. The oxygen concentration is not limited as long as the supporting gas is mixed with the fuel gas to obtain a high temperature flame. The flame temperature also differs depending on the difference in these fuels.

【0015】更に、キャリアガスは酸素に限定するもの
ではなく、石炭灰に含まれるカーボンを燃焼できる酸素
濃度であれば良い。同様に、カーボンを燃焼できる酸素
濃度のガスを溶射火炎内に噴射でき、石炭灰に含まれる
カーボンを燃焼できれば、キャリアガスとは別の方法で
噴射させても良い。
Further, the carrier gas is not limited to oxygen, but may be any oxygen concentration that can burn carbon contained in coal ash. Similarly, if a gas having an oxygen concentration capable of burning carbon can be injected into the thermal spray flame and the carbon contained in the coal ash can be burned, a method other than the carrier gas injection may be used.

【0016】本発明の方法で改質した石炭灰をコンクリ
ートの砂の代替として使用する際に問題が無いかどうか
をJIS R 5201に準じてポルトランドセメン
ト、標準砂、改質前及び改質後石炭灰を用いて、セメン
ト強さ試験を実施し評価した。その結果を表2に示す。
According to JIS R 5201, there is no problem in using the coal ash modified by the method of the present invention as a substitute for concrete sand. Portland cement, standard sand, unmodified and modified coal. A cement strength test was performed and evaluated using ash. The results are shown in Table 2.

【0017】[0017]

【表2】 [Table 2]

【0018】表2の実施例は本発明で得られた改質後石
炭灰を標準砂と置き換えたものである。比較例1はJI
S R 5201に規定されたセメントと標準砂の配合
割合であり、現状技術のレベルであると言える。比較例
2は改質前石炭灰を標準砂と置き換えたものである。圧
縮強度はいずれも材令28日の値である。実施例はいず
れも比較例1の現状技術レベルと同等以上の強度を示し
た。また、実施例2と比較例2より同じ配合割合でも石
炭灰を改質することにより強度が向上した。なお、本発
明の改質石炭灰の砂に対する代替率としては、70%以
下が好ましい。70%を越えると硬化前のコンクリート
を構成する材料の全比表面積に対する改質石炭灰の比表
面積の割合が増加して添加水分が改質石炭灰に吸着さ
れ、セメントに必要な水分が十分に得られないため、添
加水分を増量しなければならない場合がある。
The examples in Table 2 are obtained by replacing the modified coal ash obtained by the present invention with standard sand. Comparative Example 1 is JI
It is the mixing ratio of cement and standard sand specified in S R 5201, and can be said to be at the level of the existing technology. In Comparative Example 2, the unmodified coal ash was replaced with standard sand. The compressive strength is a value of 28 days of age. Each of the examples showed a strength equal to or higher than the current technical level of Comparative Example 1. Further, the strength was improved by modifying the coal ash even in the same mixing ratio as in Example 2 and Comparative Example 2. The alternative rate of the modified coal ash of the present invention for sand is preferably 70% or less. If it exceeds 70%, the ratio of the specific surface area of the modified coal ash to the total specific surface area of the material constituting the unhardened concrete increases, the added water is adsorbed by the modified coal ash, and the water necessary for the cement is sufficient. Since it cannot be obtained, it may be necessary to increase the amount of added water.

【0019】[0019]

【発明の効果】本発明により、石炭灰をコンクリートの
砂と代替できる品質を確保できることから、全量を有効
活用でき、かつ、省資源が図れる。また、改質した石炭
灰の流動性が良好なことからセメント、あるいは砂利と
の配合、混練及び施工において作業性の向上が期待でき
る。更に、燃焼排ガス中には水分や炭酸ガスが含まれて
いるので、燃焼排ガスを遊離石灰を含む製鋼スラグと接
触させて遊離石灰を水酸化カルシュウムや炭酸カルシュ
ウムの形で安定化させれば燃焼排ガスの有効利用とな
る。また、本発明に於ける改質方法は石炭灰に限定され
るものではなく、他の産業廃棄物、例えばアルミ残灰や
汚泥の改質にも利用できる。
According to the present invention, it is possible to ensure the quality of replacing coal ash with concrete sand, so that the entire amount can be effectively utilized and resource saving can be achieved. Further, since the fluidity of the modified coal ash is good, improvement in workability can be expected in the mixing, kneading and construction with cement or gravel. Furthermore, since the combustion exhaust gas contains water and carbon dioxide gas, if the combustion exhaust gas is brought into contact with steelmaking slag containing free lime to stabilize the free lime in the form of calcium hydroxide or calcium carbonate, the combustion exhaust gas Will be effectively used. Further, the reforming method in the present invention is not limited to coal ash, but can be used for reforming other industrial wastes such as aluminum residual ash and sludge.

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

【図1】本発明の第1実施例に係る石炭灰の改質方法及
び装置の一例を示す模式説明図。
FIG. 1 is a schematic explanatory view showing an example of a coal ash reforming method and apparatus according to a first embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 溶射バーナー 2 ランス 3 ランス駆動機 4 ユーティリティ制御盤 5a 補給用粉体ホッパー 5b 粉体ホッパー 5c 切り出し機 5d 開閉弁 6a 炉体 6b 集塵機 7a、7b 開閉蓋 8a、8b 回収箱 9a 一次側ユーティリティ配管 9b 燃料ガス配管 9c、9d 冷却水配管 9e キャリアガス配管 9f 粉体配管 10 溶射火炎 11 改質前石炭灰 12 改質後石炭灰 1 Spraying burner 2 Lance 3 Lance driver 4 Utility control panel 5a Powder hopper for replenishment 5b Powder hopper 5c Cutting machine 5d Open / close valve 6a Furnace body 6b Dust collector 7a, 7b Open / close lid 8a, 8b Recovery box 9a Primary side utility piping 9b Fuel gas piping 9c, 9d Cooling water piping 9e Carrier gas piping 9f Powder piping 10 Thermal spray flame 11 Coal ash before reforming 12 Coal ash after reforming

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 溶射バーナー、ランス、ユーティリティ
制御盤及び粉体供給機から構成される溶射装置と溶射処
理を実施するための空間を提供する炉体とを用い、溶射
バーナーに形成される火炎が炉体内部に吹き込まれるよ
うに炉体開口部に溶射装置を設置し、該溶射バーナーか
らキャリアガスと共に石炭灰を溶射火炎内を通過するよ
うに噴射することを特徴とする石炭灰の改質方法。
1. A flame formed on a thermal spray burner using a thermal spray apparatus comprising a thermal spray burner, a lance, a utility control panel and a powder feeder and a furnace body providing a space for performing thermal spray processing. A method for reforming coal ash, characterized in that a thermal spraying device is installed in the furnace body opening so as to be blown into the furnace body, and coal ash is injected together with carrier gas from the thermal spray burner so as to pass through the thermal spray flame. .
【請求項2】 請求項1記載の石炭灰の改質方法で改質
した石炭灰をコンクリートの砂の代替として使用するこ
とを特徴とする改質石炭灰の使用方法。
2. A method of using modified coal ash, characterized in that the coal ash modified by the method for modifying coal ash according to claim 1 is used as a substitute for concrete sand.
JP12630896A 1996-04-24 1996-04-24 Method for modifying coal ash and method for using modified coal ash Expired - Fee Related JP3687869B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP12630896A JP3687869B2 (en) 1996-04-24 1996-04-24 Method for modifying coal ash and method for using modified coal ash

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12630896A JP3687869B2 (en) 1996-04-24 1996-04-24 Method for modifying coal ash and method for using modified coal ash

Publications (2)

Publication Number Publication Date
JPH09290234A true JPH09290234A (en) 1997-11-11
JP3687869B2 JP3687869B2 (en) 2005-08-24

Family

ID=14931982

Family Applications (1)

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

Country Link
JP (1) JP3687869B2 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6457425B1 (en) 1999-11-02 2002-10-01 Consolidated Engineering Company, Inc. Method and apparatus for combustion of residual carbon in fly ash
US7273015B2 (en) 1999-11-02 2007-09-25 Consolidated Engineering Company, Inc. Method and apparatus for combustion of residual carbon in fly ash
KR101131932B1 (en) * 2011-06-30 2012-04-03 서울대학교산학협력단 Facility and method for manufacturing granular filler using bottom ash of thermal power station
WO2016017669A1 (en) * 2014-07-31 2016-02-04 勝義 近藤 Method for detoxifying combustion ash from organic waste and combustion facility for organic waste

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6457425B1 (en) 1999-11-02 2002-10-01 Consolidated Engineering Company, Inc. Method and apparatus for combustion of residual carbon in fly ash
US7273015B2 (en) 1999-11-02 2007-09-25 Consolidated Engineering Company, Inc. Method and apparatus for combustion of residual carbon in fly ash
KR101131932B1 (en) * 2011-06-30 2012-04-03 서울대학교산학협력단 Facility and method for manufacturing granular filler using bottom ash of thermal power station
WO2016017669A1 (en) * 2014-07-31 2016-02-04 勝義 近藤 Method for detoxifying combustion ash from organic waste and combustion facility for organic waste
JPWO2016017669A1 (en) * 2014-07-31 2017-04-27 勝義 近藤 Detoxification method of combustion ash of organic waste and combustion facility of organic waste

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