JPH1183000A - Materials for melting part of waste combustion ash - Google Patents
Materials for melting part of waste combustion ashInfo
- Publication number
- JPH1183000A JPH1183000A JP10182173A JP18217398A JPH1183000A JP H1183000 A JPH1183000 A JP H1183000A JP 10182173 A JP10182173 A JP 10182173A JP 18217398 A JP18217398 A JP 18217398A JP H1183000 A JPH1183000 A JP H1183000A
- Authority
- JP
- Japan
- Prior art keywords
- waste
- ash
- combustion
- melting
- molten slag
- 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
Links
Landscapes
- Gasification And Melting Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
- Compositions Of Oxide Ceramics (AREA)
- Curing Cements, Concrete, And Artificial Stone (AREA)
Abstract
(57)【要約】
【課題】 廃棄物を元とする燃焼物を燃焼させて生ずる
灰分を加熱して溶融スラグにする炉内面を構成する廃棄
物燃焼灰分の溶融部用部材の前記灰溶融スラグに対する
耐食性を向上すること。
【解決手段】 廃棄物を元とする燃焼物を燃焼させて生
ずる灰分を加熱して溶融スラグにする炉内面を構成する
廃棄物燃焼灰分の溶融部用部材において、該溶融部用部
材は、スピネル型化合物MCr2O4(MはMg又は2価
のFe)耐火材から成ることを特徴とするものである。
該スピネル型化合物耐火材は熱力学的に安定で、アルカ
リ元素との両立性が高いので、最初からアルカリ元素を
含有する溶融スラグによる耐火物の浸食を抑制できる。
Abstract: PROBLEM TO BE SOLVED: To provide a ash melting slag of a member for a melting portion of a waste combustion ash constituting a furnace inner surface constituting a furnace inner surface by heating an ash generated by burning a combustion material based on the waste to form a molten slag. To improve corrosion resistance against SOLUTION: A member for a melting portion of a waste combustion ash constituting an inner surface of a furnace which heats an ash generated by burning a combustion material based on a waste to form a molten slag, wherein the melting portion member is a spinel. It is characterized by comprising a refractory material of a type compound MCr 2 O 4 (M is Mg or divalent Fe).
Since the spinel-type compound refractory is thermodynamically stable and highly compatible with an alkali element, erosion of the refractory by molten slag containing the alkali element from the beginning can be suppressed.
Description
【0001】[0001]
【発明の属する技術分野】本発明は、廃棄物(家庭やオ
フィスなどから出される都市ごみなどの一般廃棄物、廃
プラスチック、カーシュレッダー・ダスト、廃オフィス
機器、電子機器、化粧品などの産業廃棄物など、可燃物
を含むもの)を焼却処理して生ずる灰分を加熱して溶融
スラグとする溶融炉内面を構成する廃棄物燃焼灰分の溶
融部用部材、該部材の改質方法及び廃棄物処理装置に関
するものである。The present invention relates to industrial waste such as waste (general waste such as municipal waste from homes and offices, waste plastic, car shredder dust, waste office equipment, electronic equipment, cosmetics, etc.). Etc., a member for the melting part of waste combustion ash constituting the inner surface of a melting furnace which forms slag by heating ash generated by incineration of a material containing a combustible material, a method of reforming the member and a waste treatment apparatus It is about.
【0002】[0002]
【従来の技術】都市ごみ等の一般廃棄物や廃プラスチッ
ク等の可燃物を含む廃棄物の処理装置の一つとして、廃
棄物を熱分解反応器に入れて低酸素雰囲気中で加熱して
熱分解し、熱分解ガス(乾留ガス)と主として不揮発性
成分からなる熱分解残留物とを生成し、この熱分解ガス
と熱分解残留物とを排出装置において分離し、更に熱分
解残留物を不活性雰囲気下の冷却装置で冷却した後、分
離装置に供給して熱分解カーボンを主体とする燃焼性成
分と、例えば金属や陶器、砂利等の不燃焼性成分とに分
離し、燃焼性成分を粉砕して粉体とし、この粉砕された
燃焼性成分と前記した熱分解ガスとを燃焼溶融炉に導い
て燃焼させ、生じた燃焼灰をその燃焼熱により加熱して
溶融スラグとなし、この溶融スラグは耐火材で覆われた
炉内面を伝って流下し、排出部から外部に排出して冷却
固化させるようにした廃棄物処理装置が知られている
(特公平6−56253号公報)。燃焼溶融炉で発生し
た高温の燃焼排ガス(約1200℃)は、後段に設けら
れている熱交換器により熱エネルギーを回収され、更に
集塵器で集塵され、最終的にクリーンな排ガスとなって
煙突から大気中に放出される。耐火物は鉄鋼、非鉄、セ
メント、ガラス、窯業など高温処理を必要とする工業の
窯炉やボイラ、廃棄物焼却炉などに使用される。溶融ス
ラグと接触する環境での使用においては、酸素分圧、ア
ルカリ分圧などの気相側環境と共に溶融スラグの関与す
る苛酷な高温腐食も考慮する必要がある。一般に、酸素
分圧の高い場合においては酸化物系耐火物が使用される
が、その腐食性選定の目安として、スラグの塩基度が1
以上の場合は塩基性耐火物が、1以下の場合は中性また
は酸性耐火物が使用される。空気で燃焼溶融するごみ焼
却での酸化物系耐火物の場合、スラグ塩基度は1以下の
ことが多く、Al2O3を主体とする中性耐火物が選ばれ
ている。2. Description of the Related Art As one of treatment apparatuses for waste including general waste such as municipal solid waste and combustibles such as waste plastics, the waste is put into a thermal decomposition reactor and heated in a low oxygen atmosphere to heat the waste. Decomposes to generate a pyrolysis gas (dry distillation gas) and a pyrolysis residue mainly composed of non-volatile components. The pyrolysis gas and the pyrolysis residue are separated in a discharge device, and the pyrolysis residue is further purified. After cooling with a cooling device under an active atmosphere, it is supplied to a separation device and separated into a combustible component mainly composed of pyrolytic carbon and a non-combustible component such as metal, pottery, and gravel. Pulverized into a powder, the pulverized combustible component and the above-mentioned pyrolysis gas are introduced into a combustion melting furnace and burned, and the resulting combustion ash is heated by the combustion heat to form a molten slag, and the molten slag is formed. The slag flows along the inner surface of the furnace covered with refractory material. And, waste is discharged to the outside so as to cool and solidify processing apparatus is known from the discharge portion (KOKOKU 6-56253 Patent Publication). The high-temperature flue gas (approximately 1200 ° C.) generated in the combustion melting furnace is recovered heat energy by a heat exchanger provided at the subsequent stage, and is further collected by a dust collector, and finally becomes clean exhaust gas. From the chimney. Refractories are used in industrial kilns, boilers, waste incinerators, etc. that require high-temperature treatment, such as steel, non-ferrous, cement, glass, and ceramics. In use in an environment that comes into contact with molten slag, it is necessary to consider severe high-temperature corrosion involving the molten slag as well as the gas-phase environment such as oxygen partial pressure and alkali partial pressure. In general, when the oxygen partial pressure is high, an oxide refractory is used.
In the above case, a basic refractory is used. In the case of 1 or less, a neutral or acidic refractory is used. In the case of oxide refractories in incineration of refuse which is burned and melted with air, the slag basicity is often 1 or less, and a neutral refractory mainly composed of Al 2 O 3 is selected.
【0003】[0003]
【発明が解決しようとする課題】上記灰分を溶融させた
溶融スラグは、製鋼スラグやその他の溶融物と比較して
NaやKといったアルカリ元素の含有率が高い。そのた
め、Al2O3−SiO2、Al2O3−SiC等のSi含
有耐火材の場合、最初から存在する又は生成されたSi
O2が灰溶融スラグ中のアルカリと反応し、低融点のア
ルカリシリケートが生成される。この化合物は流動化す
るため該耐火材は徐々に減肉する。一方、Al2O3系耐
火材或いはセラミックスの場合、いわゆるβ−アルミナ
を形成し、低融点化する。従って、耐火材の寿命が短く
なる。The molten slag obtained by melting the above ash has a higher content of alkali elements such as Na and K than steelmaking slag and other molten materials. Therefore, in the case of a Si-containing refractory material such as Al 2 O 3 —SiO 2 and Al 2 O 3 —SiC, Si that is present or generated from the beginning
O 2 reacts with the alkali in the ash molten slag to produce a low melting alkali silicate. Since this compound is fluidized, the refractory material gradually loses its thickness. On the other hand, in the case of an Al 2 O 3 refractory material or ceramics, so-called β-alumina is formed, and the melting point is lowered. Therefore, the life of the refractory material is shortened.
【0004】本発明の課題は、廃棄物を元とする燃焼物
を燃焼させて生ずる灰分を加熱して溶融スラグにする炉
内面を構成する廃棄物燃焼灰分の溶融部用部材の前記灰
溶融スラグに対する耐食性を向上することにある。[0004] It is an object of the present invention to provide a ash melting slag of a member for a melting portion of a waste combustion ash which constitutes a furnace inner surface which forms a furnace slag by heating an ash generated by burning a combustion product based on the waste. The purpose is to improve the corrosion resistance to corrosion.
【0005】[0005]
【課題を解決するための手段】上記課題を達成するた
め、本願請求項1記載発明は、廃棄物を元とする燃焼物
を燃焼させて生ずる灰分を加熱して溶融スラグにする炉
内面を構成する廃棄物燃焼灰分の溶融部用部材におい
て、該溶融部用部材は、下記式(1)で表されるスピネ
ル型化合物から成ることを特徴とするものである。In order to achieve the above-mentioned object, the invention according to claim 1 of the present invention comprises an inner surface of a furnace which heats ash generated by burning a combusted material based on waste to form a molten slag. The member for the melting portion of the waste combustion ash is characterized in that the member for the melting portion is made of a spinel-type compound represented by the following formula (1).
【0006】[0006]
【化4】 Embedded image
【0007】該溶融部用部材によれば、前記灰分を加熱
して(約1300℃)溶融スラグにする際に、これと接
触する部材をCr含有スピネル型化合物で構築すれば、
次のような効果により、激しい侵食を免れることができ
る。 Cr2O3は溶融スラグとの表面張力が大きく、濡れ
にくい。そのため、溶融スラグの浸透が抑制される。 Cr2O3は溶融スラグ中への溶解にあたり、液相の
粘性を高める。そのため、耐火材に接するスラグ境界層
中の物質移動速度は小さくなる。 Cr2O3単独物は、その性質が酸性酸化物であるた
めアルカリ含有スラグ中への溶解度は高くなる傾向にあ
るが、MgOなどの塩基性酸化物との等モル化合物であ
るスピネル型物質を構成すると、アルカリ含有スラグ中
への溶解度はそれ程大きくならない。When the ash is heated (about 1300 ° C.) to form a molten slag, the member that comes into contact with the slag is made of a Cr-containing spinel type compound.
The following effects can prevent severe erosion. Cr 2 O 3 has a large surface tension with the molten slag and is hardly wet. Therefore, penetration of the molten slag is suppressed. Cr 2 O 3 increases the viscosity of the liquid phase upon dissolution in the molten slag. Therefore, the mass transfer rate in the slag boundary layer in contact with the refractory material decreases. Cr 2 O 3 alone tends to have a high solubility in alkali-containing slag because of its nature as an acidic oxide, but a spinel-type substance that is an equimolar compound with a basic oxide such as MgO is used. With this configuration, the solubility in the slag containing alkali does not increase so much.
【0008】このような特性を有するスピネル型化合物
物質の代表例には、ピクロクロマイトMgCr2O4やク
ロマイトFeCr2O4がある。この時、スピネル型化合
物中のMOとCr2O3とのモル比は1:1(定比)であ
る必要はなく、1300℃におけるMgO・nAl2O3
の場合から類推し、Cr2O3の比率が50〜58mol%
の範囲でスピネル型構造を作り得る(不定比性)。この
比率は、下記式(4)のものでは、0.714≦β≦1
に相当する。ここで、スピネル構造中の4配位位置の金
属元素Mとしては、Mg又は2価のFeのいずれか一
方、或いは両者の任意比率の混合状態であってもよい。[0008] Representative examples of the spinel-type compound substance having such properties include picrochromite MgCr 2 O 4 and chromite FeCr 2 O 4 . At this time, the molar ratio between MO and Cr 2 O 3 in the spinel-type compound does not need to be 1: 1 (constant ratio), but MgO · nAl 2 O 3 at 1300 ° C.
By analogy with the above case, the ratio of Cr 2 O 3 is 50 to 58 mol%.
Can form a spinel type structure (nonstoichiometric). In the case of the following equation (4), this ratio is 0.714 ≦ β ≦ 1
Is equivalent to Here, the metal element M at the 4-coordinate position in the spinel structure may be either Mg or divalent Fe, or a mixed state of both in an arbitrary ratio.
【0009】[0009]
【化5】 Embedded image
【0010】さらに、スピネル構造中の6配位位置の金
属元素としては、少なくとも半数以上がCr、残りがA
l又は3価のFeとする。このような6配位位置におけ
るCrが半数以上を占めるスピネル型化合物は、定比お
よび不定比化合物のいずれにおいても、前述の理由によ
り、アルカリ元素を高濃度含有する溶融スラグによる浸
食を有効に抑制できる。[0010] Further, as the metal element at the 6-coordinate position in the spinel structure, at least half or more are Cr and the rest are A
Let it be 1 or trivalent Fe. The spinel-type compound in which Cr in the six-coordinate position occupies more than half of the stoichiometric compound effectively suppresses erosion by molten slag containing a high concentration of an alkali element in both the stoichiometric and nonstoichiometric compounds for the above-mentioned reason. it can.
【0011】本願請求項2記載発明は、請求項1記載発
明において、前記スピネル型化合物単一相のみならず、
該溶融部用部材として、前記スピネル型化合物SPと下
記式(2)で表されるコランダム型化合物CORとの2
相混合物(1−η)・SP+η・COR(ただし、0<
η<1.0)から成ることを特徴とするものである。コ
ランダム型化合物COR、酸化クロム単独物や酸化クロ
ムリッチな酸化クロム−酸化アルミニウム固溶体等が包
含される。本コランダム型化合物は、使用中に稼働面近
傍で、原料ごみ中のMO成分と反応し、下記式(3)で
表される化合部を生成し、耐食性が向上する。The invention of claim 2 of the present application is directed to the invention of claim 1, wherein not only the spinel-type compound single phase but also
As the member for the fusion zone, the spinel-type compound SP and a corundum-type compound COR represented by the following formula (2) are used.
Phase mixture (1-η) · SP + η · COR (where 0 <
η <1.0). Corundum type compound COR, chromium oxide alone, chromium oxide-rich chromium oxide-aluminum oxide solid solution, and the like are included. The corundum type compound reacts with the MO component in the raw material refuse in the vicinity of the operating surface during use, generates a compound represented by the following formula (3), and improves corrosion resistance.
【0012】[0012]
【化6】 Embedded image
【0013】[0013]
【化7】 Embedded image
【0014】本願請求項3記載発明は、本系スピネル型
化合物を例えば不定形耐火物として施工するにあたり、
そのマトリックス部の焼結性を向上させるための手段を
提供する。すなわち、これまでに、本系に近い耐火材料
が提案されているが(特開平9−71477号公報)、
その原料は電融耐火材料であって、焼結性向上に不可欠
な微粉は容易に得がたく、得られたとしてもコストが高
い。本項の方法によれば、固相反応には充分であるが、
あまり強くは焼結しない温度を選択できるため、軽度の
粉砕により安価に微粉を得ることができる。[0014] The invention according to claim 3 of the present invention relates to the application of the present spinel type compound as, for example, an amorphous refractory.
A means for improving the sinterability of the matrix portion is provided. That is, a refractory material close to the present system has been proposed (JP-A-9-71477).
The raw material is an electrofused refractory material, and fine powder indispensable for improving sinterability is difficult to obtain easily, and even if obtained, the cost is high. According to the method of this section, it is sufficient for the solid phase reaction,
Since a temperature at which sintering is not so strong can be selected, fine powder can be obtained at low cost by light pulverization.
【0015】本願請求項4記載発明は、請求項1又は2
記載発明において、前記溶融部用部材の材料内の使用前
の状態として金属Crが5重量%以上40重量%以下混
在しているものを、金属製部材の表面に皮膜として形成
することを特徴とする。使用中に稼働面近傍で、原料中
のMO成分及び気相中の酸素と該金属Crが反応してス
ピネル型化合物MCr2O4を生成し、耐食性が向上す
る。ただし添加するCr金属粉は配合物全体の40重量
%以上であると、使用中に酸化反応に起因して局部膨張
が大きくなる恐れがあるので、40重量%以下とする。
また、5重量%以下であると、金属製部材とのなじみ性
に欠け、皮膜が剥離しやすくなるので、5重量%以上と
する。これにより、表面に溶融スラグ耐食性の皮膜を形
成することで、耐火物を支持する構造部材としての金属
材料の耐久性が向上する。[0015] The invention described in claim 4 of the present application is claim 1 or 2.
In the invention described above, as a material before use in the material for the fusion zone member, a material in which 5% by weight or more and 40% by weight or less of metal Cr are mixed is formed as a film on the surface of the metal member. I do. During use, near the operating surface, the metal Cr reacts with the MO component in the raw material and oxygen in the gas phase to generate the spinel compound MCr 2 O 4 , thereby improving the corrosion resistance. However, if the amount of the Cr metal powder to be added is 40% by weight or more of the whole composition, local expansion may be increased due to an oxidation reaction during use, so the content is set to 40% by weight or less.
Further, when the content is 5% by weight or less, the film lacks conformability with a metal member and the film is easily peeled off. Thereby, the durability of the metal material as a structural member for supporting the refractory is improved by forming the molten slag corrosion resistant film on the surface.
【0016】本願請求項5記載発明は、廃棄物を元とす
る燃焼物を燃焼させて生ずる灰分を加熱して溶融スラグ
にする際に、前記廃棄物の中に予め2価の金属M又はM
含有化合物を添加し、溶融炉内面を構成するCr2O3を
含有する耐火物と反応させて請求項1又は2に記載の下
記式(3)(ただしMはMg又は2価のFeのいずれか
一方、或いは両者の任意比率の混合状態である)で表さ
れるスピネル型化合物、特にMCr2O4を生成させたも
のである。According to a fifth aspect of the present invention, when the ash produced by burning a combustion product based on a waste is heated into molten slag, the divalent metal M or M is previously contained in the waste.
Was added containing compound represented by the following formula (3) (wherein M according to claim 1 or 2 is reacted with refractory material Cr 2 O 3 content constituting the melting furnace inner surface either Mg or a divalent Fe Or a mixed state of any ratio of the two), in particular, MCr 2 O 4 .
【0017】[0017]
【化8】 Embedded image
【0018】また本願請求項6記載発明は、廃棄物を元
とする燃焼物を燃焼させて生ずる灰分を加熱して溶融ス
ラグにする際に、前記廃棄物の中に予め2価の金属M又
はM含有化合物を添加し、溶融炉内面を構成するCr2
O3を含有する耐火物と反応させて上記式(3)で表さ
れるスピネル型化合物を生成させることを特徴とする廃
棄物燃焼灰分の溶融部用部材の改質方法。Further, the invention according to claim 6 of the present application is characterized in that when the ash produced by burning the combustion material based on the waste material is heated into molten slag, the waste material contains a divalent metal M or M 2 -containing compound is added, and Cr 2 constituting the inner surface of the melting furnace
A method for reforming a member for a melting portion of waste combustion ash, which comprises reacting with a refractory containing O 3 to generate a spinel-type compound represented by the above formula (3).
【0019】これらの発明によれば、灰分を加熱して溶
融スラグにする際に、予め添加された前記M成分(Mg
又はFe)と耐火物中のCr2O3成分とが反応して、該
耐火物表面にスピネル型化合物(MCr2O4)が生成さ
れ、前記溶融スラグに対する保護膜の働きをする。According to these inventions, when heating the ash to form a molten slag, the M component (Mg) added in advance is used.
Alternatively, Fe) reacts with the Cr 2 O 3 component in the refractory to form a spinel type compound (MCr 2 O 4 ) on the surface of the refractory, and acts as a protective film for the molten slag.
【0020】本願請求項7記載発明は、廃棄物を元とす
る燃焼物を燃焼させて生ずる灰分を加熱して溶融スラグ
にする炉内面を構成する廃棄物燃焼灰分の溶融部用部材
において、該溶融部用部材の部分に設けられて温度計測
を行う熱電対の保護材の材料として請求項1〜5のいず
れかに記載の材料を用いることを特徴とするものであ
る。下記式(5)で表されるスピネル型化合物における
6配位位置のCr以外の成分の添加は、耐食性発現を損
なわないように、添加元素であるAlと3価のFeの合
計がCr量を超えない範囲とする。According to a seventh aspect of the present invention, there is provided a member for a melting portion of a waste combustion ash constituting an inner surface of a furnace which heats an ash generated by burning a combustion product based on the waste to form a molten slag. The material according to any one of claims 1 to 5 is characterized in that the material according to any one of claims 1 to 5 is used as a material for a protective material of a thermocouple which is provided at a portion of the member for the fusion zone and measures a temperature. Addition of a component other than Cr at the 6-coordinate position in the spinel-type compound represented by the following formula (5) makes the total amount of the additive element Al and trivalent Fe lower the amount of Cr so as not to impair the corrosion resistance. Do not exceed the range.
【0021】[0021]
【化9】 Embedded image
【0022】本願請求項8記載発明は、廃棄物を熱分解
して熱分解ガスおよび熱分解残留物を生成する熱分解反
応器と、前記熱分解残留物を不活性雰囲気下で冷却する
冷却装置と、冷却された熱分解残留物を燃焼性成分およ
び不燃焼性成分に分離する分離装置と、前記熱分解ガス
および燃焼性成分を灰分を溶融させる温度で燃焼させて
不燃焼分を溶融スラグとして排出部から排出する燃焼溶
融炉と、燃焼溶融炉で生じた高温ガスの熱を空気と熱交
換させて回収する熱交換器とを備えた廃棄物処理装置に
おいて、前記燃焼溶融炉の炉内面を構成する部材は請求
項1〜5又は7のいずれかに記載の溶融部用部材である
ことを特徴とするものである。これにより、燃焼溶融炉
の耐久性が向上し、もって該装置の運転効率を向上でき
る。[0022] The invention according to claim 8 of the present application provides a pyrolysis reactor for pyrolyzing waste to produce a pyrolysis gas and a pyrolysis residue, and a cooling device for cooling the pyrolysis residue in an inert atmosphere. And a separation device for separating the cooled pyrolysis residue into a combustible component and a non-combustible component, and burning the pyrolysis gas and the combustible component at a temperature at which ash is melted to convert the non-combustible component into molten slag. In a waste treatment apparatus provided with a combustion and melting furnace discharged from a discharge unit and a heat exchanger that recovers heat of a high-temperature gas generated in the combustion and melting furnace by exchanging heat with air, the furnace inner surface of the combustion and melting furnace is removed. The constituent member is the member for a fusion zone according to any one of claims 1 to 5 or 7. Thereby, the durability of the combustion melting furnace is improved, so that the operation efficiency of the apparatus can be improved.
【0023】[0023]
(実施例1)Cr2O3とMgOを重量比で79:21の
割合で混合した粉末を金型に充填し静水圧プレス法によ
り成型した。この成型体を大気雰囲気中で1600℃の
温度にて5時間加熱した。得られた固相反応物は、X線
回折によりピクロクロマイトであることを確認した。こ
れを通常のボールミルで粉砕し、分級後、各種サイズの
粉体を焼結助剤のスルファミン酸と共に混合し、プレス
成形後、焼結し試験体を得た。焼結は1700℃・3時
間で行った。It was molded by (Example 1) Cr 2 O 3 and MgO filled with powder in a mixing ratio of 79:21 in a weight ratio to the mold hydrostatic pressing method. The molded body was heated at 1600 ° C. for 5 hours in an air atmosphere. The obtained solid phase reaction product was confirmed to be picrochromite by X-ray diffraction. This was pulverized by an ordinary ball mill, classified, mixed with powders of various sizes together with a sintering aid, sulfamic acid, pressed and sintered to obtain a test body. Sintering was performed at 1700 ° C. for 3 hours.
【0024】この焼結体から立方体を試験試料として切
り出し、N2+5%O2+1000ppmHCl雰囲気で、13
50℃、20時間、灰溶融スラグ中に浸漬した後、浸食
量を測定した。比較のため、Al2O3焼結体およびAl
2O3−SiC焼結体につき、同様の条件で浸食テストを
行った。これらの実験条件は、ごみ焼却炉の溶融スラグ
環境を模擬したものである。得られた結果を表1に示
す。また灰溶融スラグの化学組成は表2に示した。これ
によれば、Crを6配位位置に有するスピネル型化合物
であるピクロクロマイトMgCr2O4焼結体は、Al2
O3焼結体およびAl2O3−SiC焼結体に比べ、ごみ
焼却で生ずる灰分を加熱して溶融スラグとする環境にお
いても耐食性に優れていることがわかる。A cube was cut out from this sintered body as a test sample, and the test piece was cut in a N 2 + 5% O 2 +1000 ppm HCl atmosphere.
After immersion in ash molten slag at 50 ° C. for 20 hours, the amount of erosion was measured. For comparison, an Al 2 O 3 sintered body and Al
Per 2 O 3 -SiC sintered body was subjected to erosion test under the same conditions. These experimental conditions simulate the molten slag environment of a refuse incinerator. Table 1 shows the obtained results. Table 2 shows the chemical composition of the ash molten slag. According to this, picrochromite MgCr 2 O 4 sintered body, which is a spinel-type compound having Cr at the 6-coordinate position, is made of Al 2
It can be seen that, compared to the O 3 sintered body and the Al 2 O 3 —SiC sintered body, the corrosion resistance is excellent even in an environment where the ash generated by incineration of the refuse is heated to form a molten slag.
【0025】[0025]
【表1】 [Table 1]
【0026】[0026]
【表2】 [Table 2]
【0027】また、鉄製部材の表面で、ピクロマイトに
金属Crを20重量%混在させたものを溶射により皮膜
形成し、浸食テストを行ったところ、表面近傍の金属C
rはCr2O3またはスピネル型化合物MCr2O4に変わ
っており、その耐食性は良好であった。On the surface of the iron member, a film was formed by spraying a mixture of picromite and 20% by weight of metal Cr, and an erosion test was carried out.
r was changed to Cr 2 O 3 or spinel type compound MCr 2 O 4 , and the corrosion resistance was good.
【0028】(実施例2)次に本発明に係る廃棄物燃焼
灰分の溶融部用部材を備えた廃棄物処理装置の一例を図
1に基づいて説明する。本実施の形態の廃棄物処理装置
において、都市ごみ等の廃棄物50aは、例えば二軸剪
断式等の粉砕機で、150mm角以下の大きさに粉砕さ
れ、コンベア等により投入部50内に投入される。投入
部50に投入された廃棄物50aはスクリューフィーダ
51を経て熱分解反応器52内に供給される。熱分解反
応器52としてはこの例では横型回転式ドラムが用いら
れ、ドラム内の加熱分解室は図示しないシール構造によ
り、その内部は低酸素雰囲気に保持されている。(Embodiment 2) Next, an example of a waste treatment apparatus provided with a member for a melting portion of waste combustion ash according to the present invention will be described with reference to FIG. In the waste treatment apparatus of the present embodiment, waste 50a such as municipal waste is crushed to a size of 150 mm square or less by, for example, a crusher such as a biaxial shearing method, and is charged into the charging section 50 by a conveyor or the like. Is done. The waste 50 a charged into the charging section 50 is supplied into the pyrolysis reactor 52 via the screw feeder 51. In this example, a horizontal rotary drum is used as the thermal decomposition reactor 52, and the inside of the thermal decomposition chamber in the drum is kept in a low oxygen atmosphere by a seal structure (not shown).
【0029】廃棄物50aは熱分解反応器52内で熱分
解されるが、その熱源は、後述する燃焼溶融炉53の後
流側に配置された熱交換器である高温空気加熱器1によ
り加熱され加熱空気ラインL1を介して供給される加熱
空気8g(熱媒体)である。この加熱空気8gにより熱
分解反応器52内は300〜600℃に、通常は450
℃程度に維持される。The waste 50a is thermally decomposed in the pyrolysis reactor 52, and its heat source is heated by a high-temperature air heater 1 which is a heat exchanger disposed downstream of a combustion melting furnace 53 described later. a heated air 8 g (heat medium) supplied through a heated air line L 1 is. With 8 g of the heated air, the inside of the pyrolysis reactor 52 is maintained at 300 to 600 ° C., usually 450 ° C.
It is maintained at about ° C.
【0030】更に、加熱空気8gにより加熱された廃棄
物50aは、熱分解して熱分解ガスG1と、主として不
揮発性成分からなる熱分解残留物54とになり、排出装
置55に送られて分離される。排出装置55で分離され
た熱分解ガスG1は、排出装置55の上部から熱分解ガ
スラインL2を経て燃焼溶融炉53のバーナ56に供給
される。排出装置55から排出された熱分解残留物54
は、450℃程度の比較的高温であるため、後述する冷
却装置57により不活性雰囲気下で80℃程度に冷却さ
れる。Furthermore, waste 50a heated by the heated air 8g is thermally decomposed to the pyrolysis gas G 1, becomes the pyrolysis residue 54 consisting mainly of non-volatile components, it is sent to the discharge device 55 Separated. The pyrolysis gas G 1 separated by the discharge device 55 is supplied from above the discharge device 55 to the burner 56 of the combustion melting furnace 53 via the pyrolysis gas line L 2 . Pyrolysis residue 54 discharged from discharge device 55
Is cooled to about 80 ° C. in an inert atmosphere by a cooling device 57 to be described later.
【0031】その後、冷却された熱分解残留物54は、
例えば磁選式、うず電流式、遠心式又は風力選別式等の
公知の単独又は組み合わされた分離装置58に供給さ
れ、ここで細粒の燃焼性成分58d(灰分を含む)と
鉄、瓦礫等の不燃焼性成分58cとに分離され、不燃焼
性成分58cはコンテナ59に回収され再利用される。Thereafter, the cooled pyrolysis residue 54 is
For example, it is supplied to a known single or combined separation device 58 such as a magnetic separation type, an eddy current type, a centrifugal type or a wind separation type, where the fine combustible component 58d (including ash) and iron, rubble, etc. The non-combustible component 58c is separated into the non-combustible component 58c, and is collected and reused in the container 59.
【0032】更に、燃焼性成分58dは、主として熱分
解カーボンから成るが、粉砕機60により、例えば1m
m以下に微粉砕されて粉体カーボンとなり、燃焼性成分
ラインL3を経て燃焼溶融炉53のバーナ56に供給さ
れ、熱分解ガスラインL2から供給された熱分解ガスG1
と送風機61により空気ラインL4から供給された燃焼
用空気61eと共に1,300℃程度の高温域で燃焼さ
れる。Further, the combustible component 58d is mainly composed of pyrolytic carbon.
are milled below m becomes powder carbon, combustible component line L 3 a via is supplied to the burner 56 of the burning melting furnace 53, pyrolysis gas G 1 supplied from the pyrolysis gas line L 2
It is burned in a high temperature range of about 1,300 ° C. with the supplied combustion air 61e from the air line L 4 by the blower 61 and.
【0033】上記燃焼で発生した灰分はその燃焼熱によ
り溶融スラグ53fとなって、この燃焼溶融炉53の内
壁に付着し、更に、内壁を流下し底部排出口62から筒
状の排出部71を通って水槽63に落下し冷却固化され
る。燃焼溶融炉53は、カーボン等の燃焼性成分58d
を1300℃程度の高温で燃焼させ、灰分を含む不燃焼
分を溶融させて溶融スラグ53fと高温の燃焼排ガスG
2とを生成する。燃焼排ガスG2は、秒速2〜3m、温度
1000〜1100℃のガス流となって、炉内下流側に
設けた高温空気加熱器1の伝熱管体により熱回収され
る。The ash generated by the combustion becomes molten slag 53f due to the heat of combustion, adheres to the inner wall of the combustion furnace 53, flows down the inner wall, and discharges the cylindrical discharge portion 71 from the bottom discharge port 62. Then, it falls into the water tank 63 and is cooled and solidified. The combustion melting furnace 53 includes a combustible component 58d such as carbon.
Is burned at a high temperature of about 1300 ° C., and the unburned portion including the ash is melted, and the molten slag 53f and the high-temperature flue gas G are melted.
2 and generate Combustion exhaust gas G 2 is, per second 2 to 3 m, so the temperature 1000 to 1100 ° C. in a gas stream, is heat recovered by the heat transfer tube of the hot air heater 1 provided in the furnace downstream.
【0034】ここで、燃焼溶融炉は本発明に係る廃棄物
燃焼灰分の溶融部用部材で形成されている。この例では
スピネル型化合物耐火材で形成されている。すなわち溶
融スラグはNaやKなどのアルカリ元素を高濃度で含ん
でいるが、それに対する耐食性が高いもので形成されて
いる。Here, the combustion melting furnace is formed of the member for the melting portion of the waste combustion ash according to the present invention. In this example, it is formed of a spinel type compound refractory material. That is, the molten slag contains a high concentration of an alkali element such as Na or K, but is formed of a material having high corrosion resistance to the alkali element.
【0035】前記高温空気加熱器1の部分を通過した燃
焼排ガスG2は、煙道ガスラインL5を介して廃熱ボイラ
64で熱回収され、集塵器65で除塵され、更に排ガス
浄化装置66で塩素等の有害成分が除去された後、低温
のクリーンな排ガスG3となって誘引送風機67を介し
て煙突68から大気へ放出される。廃熱ボイラ64で生
成した蒸気は、蒸気タービンを有する発電機69で発電
に利用される。クリーンな排ガスG3の一部はファン7
0を介してガスラインL6により冷却装置57に供給さ
れる。The flue gas G 2 that has passed through the high-temperature air heater 1 is recovered by a waste heat boiler 64 via a flue gas line L 5 , removed by a dust collector 65, and further purified by an exhaust gas purifier. After harmful components such as chlorine are removed at 66, the exhaust gas G 3 is discharged into the atmosphere from the chimney 68 via the induction blower 67 as clean low-temperature exhaust gas G 3 . The steam generated by the waste heat boiler 64 is used for power generation by a generator 69 having a steam turbine. Part of the clean exhaust gas G 3 is fan 7
0 is supplied to the cooling device 57 by a gas line L 6 through.
【0036】次に、作用を説明する。6配位位置にCr
を有する上記式(3)で表されるスピネル型化合物耐火
物は、熱力学的に安定で、アルカリ元素との両立性が高
いので、燃焼溶融炉53内で生成したこの種溶融スラグ
による浸食を抑制できる。従って、燃焼溶融炉の耐久性
が向上し、もって廃棄物処理装置の運転効率を向上でき
る。Next, the operation will be described. Cr at 6 coordination position
Since the spinel-type compound refractory represented by the above formula (3) having thermodynamic stability is thermodynamically stable and has high compatibility with an alkali element, erosion due to this kind of molten slag generated in the combustion melting furnace 53 is suppressed. Can be suppressed. Therefore, the durability of the combustion melting furnace is improved, and the operation efficiency of the waste treatment device can be improved.
【0037】尚、実施例2では燃焼溶融炉は最初からス
ピネル型化合物耐火物で形成されているものについて説
明したが、最初はスピネル型化合物は形成されていなく
ても、耐火材としてCr2O3を含有するものを用い、予
め廃棄物にMgやFeを添加しておき、溶融スラグの生
成と同時にスピネル型化合物が生成されるようにしても
よい。Although the combustion melting furnace was described in Example 2 as being made of a spinel-type compound refractory from the beginning, even if the spinel-type compound was not initially formed, Cr 2 O was used as a refractory material. with those containing 3, possible to add the Mg and Fe in advance waste, may be simultaneously spinel compound producing a molten slag is produced.
【0038】尚、以上においては、本発明を図示の実施
形態について詳述したが、本発明はそれらの実施形態の
みに限定されるものではなく、本発明の精神を逸脱せず
して種々改変を加え、多種多様の変形をなし得ることは
云うまでもない。In the above, the present invention has been described in detail with reference to the illustrated embodiments. However, the present invention is not limited to only those embodiments, and various modifications can be made without departing from the spirit of the present invention. It goes without saying that a wide variety of modifications can be made.
【0039】[0039]
【発明の効果】本発明によれば、廃棄物を元とする燃焼
物を燃焼させて生ずる灰分を加熱して溶融スラグにする
炉内面を構成する廃棄物燃焼灰分の溶融部用部材の前記
灰溶融スラグに対する耐食性を向上することができる。
本発明において、スピネル型化合物における6配位位置
へのCr以外の成分の添加は、本化合物の製造しやすさ
を増加し、かつ、製造コストを引き下げる効果がある。According to the present invention, according to the present invention, the ash of the member for the melting portion of the waste combustion ash constituting the furnace inner surface which forms the furnace inner surface by heating the ash generated by burning the combustion material based on the waste to form a molten slag Corrosion resistance to molten slag can be improved.
In the present invention, the addition of a component other than Cr to the 6-coordinate position in the spinel-type compound has effects of increasing the ease of producing the present compound and reducing the production cost.
【図1】本発明に係る廃棄物処理装置の一例を示す概略
図である。FIG. 1 is a schematic diagram showing an example of a waste disposal apparatus according to the present invention.
53 燃焼溶融炉 53f 溶融スラグ 53 Combustion melting furnace 53f Molten slag
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI F23G 5/46 ZAB F23G 5/46 ZABZ F23J 1/00 F23J 1/00 B // B09B 3/00 B09B 3/00 303D (72)発明者 西村 直之 岡山県玉野市玉3丁目1番1号 三井造船 株式会社玉野事業所内──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 6 Identification code FI F23G 5/46 ZAB F23G 5/46 ZABZ F23J 1/00 F23J 1/00 B // B09B 3/00 B09B 3/00 303D (72 ) Inventor Naoyuki Nishimura 3-1-1, Tamano, Tamano-shi, Okayama Mitsui Engineering & Shipbuilding Co., Ltd.
Claims (8)
ずる灰分を加熱して溶融スラグにする炉内面を構成する
廃棄物燃焼灰分の溶融部用部材において、該溶融部用部
材は、下記式(1)で表されるスピネル型化合物から成
ることを特徴とする廃棄物燃焼灰分の溶融部用部材。 【化1】 Claims: 1. A member for a melting part of a waste combustion ash constituting an inner surface of a furnace that heats an ash generated by burning a combustion material based on a waste to form a molten slag, wherein the member for a melting part is: A member for a melting part of waste combustion ash, comprising a spinel compound represented by the following formula (1). Embedded image
て、前記スピネル型化合物SPと下記式(2)で表され
るコランダム型化合物CORとの2相混合物(1−η)
・SP+η・COR(ただし、0<η<1.0)から成
ることを特徴とする廃棄物燃焼灰分の溶融部用部材。 【化2】 2. The two-phase mixture (1-η) of the spinel-type compound SP and a corundum-type compound COR represented by the following formula (2) as the member for a fusion zone.
A member for a melting portion of waste combustion ash, comprising SP + η · COR (where 0 <η <1.0). Embedded image
ル型化合物は、構成元素Mg、Fe、Cr、Alを含む
単独原料または複合原料から、固相反応により合成し、
それを粉末化し、該粉末を成形・焼成して使用すること
を特徴とする廃棄物燃焼灰分の溶融部用部材の製造方
法。3. The spinel-type compound according to claim 1 or 2, synthesized from a single raw material or a composite raw material containing the constituent elements Mg, Fe, Cr, and Al by a solid-phase reaction,
A method for producing a member for a molten portion of waste combustion ash, which comprises pulverizing the powder, shaping and firing the powder.
部材の材料内の使用前状態として、金属Crが5重量%
以上40重量%以下混在しているものを、金属製部材の
表面に皮膜としてコーティングしたものであることを特
徴とする廃棄物燃焼灰分の溶融部用部材。4. The material according to claim 1, wherein 5% by weight of metal Cr is used as the pre-use state in the material of the member for the fusion zone.
A member for a melting portion of waste combustion ash, characterized in that a mixture of not less than 40% by weight is coated on the surface of a metal member as a film.
ずる灰分を加熱して溶融スラグにする際に、前記廃棄物
の中に予め2価の金属M又はM含有化合物を添加し、溶
融炉内面を構成するCr2O3を含有する耐火物と反応さ
せて請求項1又は2に記載の下記式(3)(ただしMは
Mg又は2価のFeのいずれか一方、或いは両者の任意
比率の混合状態である)で表されるスピネル型化合物を
生成させたものであることを特徴とする廃棄物燃焼灰分
の溶融部用部材。 【化3】 5. When heating the ash produced by burning the combustion material based on the waste material into molten slag, a divalent metal M or an M-containing compound is added to the waste material in advance, The following formula (3) according to claim 1 or 2 (where M is either Mg or divalent Fe, or both) by reacting with the refractory containing Cr 2 O 3 constituting the inner surface of the melting furnace. (A mixed state in an arbitrary ratio) is produced by producing a spinel-type compound represented by the formula (1): Embedded image
ずる灰分を加熱して溶融スラグにする際に、前記廃棄物
の中に予め2価の金属M又はM含有化合物を添加し、溶
融炉内面を構成するCr2O3を含有する耐火物と反応さ
せて請求項5に記載のスピネル型化合物を生成させるこ
とを特徴とする廃棄物燃焼灰分の溶融部用部材の改質方
法。6. When heating the ash produced by burning the combustion material based on the waste material into molten slag, a divalent metal M or a compound containing M is added to the waste material in advance, A method for modifying a member for a melting portion of waste combustion ash, comprising reacting with a refractory containing Cr 2 O 3 constituting an inner surface of a melting furnace to generate a spinel-type compound according to claim 5.
ずる灰分を加熱して溶融スラグにする炉内面を構成する
廃棄物燃焼灰分の溶融部用部材において、該溶融部用部
材の部分に設けられて温度計測を行う熱電対の保護材の
材料として請求項1〜5のいずれかに記載の材料を用い
ることを特徴とする廃棄物燃焼灰分の溶融部用部材。7. A member for a melting part of a waste combustion ash constituting an inner surface of a furnace which heats an ash generated by burning a combustion material based on the waste to form a molten slag, the part of the member for the melting part A member for a molten portion of waste ash, characterized in that the material according to any one of claims 1 to 5 is used as a material of a protective material of a thermocouple provided in the thermocouple for measuring a temperature.
分解残留物を生成する熱分解反応器と、前記熱分解残留
物を不活性雰囲気下で冷却する冷却装置と、冷却された
熱分解残留物を燃焼性成分および不燃焼性成分に分離す
る分離装置と、前記熱分解ガスおよび燃焼性成分を灰分
を溶融させる温度で燃焼させて不燃焼分を溶融スラグと
して排出部から排出する燃焼溶融炉と、燃焼溶融炉で生
じた高温ガスの熱を空気と熱交換させて回収する熱交換
器とを備えた廃棄物処理装置において、前記燃焼溶融炉
の炉内面を構成する部材は請求項1〜5又は7のいずれ
かに記載の溶融部用部材であることを特徴とする廃棄物
処理装置。8. A pyrolysis reactor for pyrolyzing waste to produce a pyrolysis gas and a pyrolysis residue; a cooling device for cooling the pyrolysis residue in an inert atmosphere; A separation device for separating the decomposition residue into a combustible component and an incombustible component, and a combustion device in which the pyrolysis gas and the combustible component are burned at a temperature at which ash is melted, and the unburned component is discharged from a discharge portion as molten slag. In a waste treatment apparatus including a melting furnace and a heat exchanger that recovers heat of a high-temperature gas generated in the combustion melting furnace by exchanging heat with air, a member constituting a furnace inner surface of the combustion melting furnace is claimed. A waste treatment apparatus, which is a member for a fusion zone according to any one of 1 to 5 or 7.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP10182173A JPH1183000A (en) | 1997-06-30 | 1998-06-29 | Materials for melting part of waste combustion ash |
Applications Claiming Priority (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP17488697 | 1997-06-30 | ||
| JP9-174886 | 1997-06-30 | ||
| JP10182173A JPH1183000A (en) | 1997-06-30 | 1998-06-29 | Materials for melting part of waste combustion ash |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH1183000A true JPH1183000A (en) | 1999-03-26 |
Family
ID=26496339
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP10182173A Pending JPH1183000A (en) | 1997-06-30 | 1998-06-29 | Materials for melting part of waste combustion ash |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH1183000A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2012511081A (en) * | 2008-12-08 | 2012-05-17 | ゼネラル・エレクトリック・カンパニイ | Gasifier additive for improved heat-resistant life |
| WO2015129083A1 (en) * | 2014-02-27 | 2015-09-03 | 三菱日立パワーシステムズ株式会社 | Wet bottom furnace |
-
1998
- 1998-06-29 JP JP10182173A patent/JPH1183000A/en active Pending
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2012511081A (en) * | 2008-12-08 | 2012-05-17 | ゼネラル・エレクトリック・カンパニイ | Gasifier additive for improved heat-resistant life |
| WO2015129083A1 (en) * | 2014-02-27 | 2015-09-03 | 三菱日立パワーシステムズ株式会社 | Wet bottom furnace |
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