JP2679598B2 - Method and equipment for removing dioxins from fly ash in a refuse incinerator - Google Patents
Method and equipment for removing dioxins from fly ash in a refuse incineratorInfo
- Publication number
- JP2679598B2 JP2679598B2 JP5301104A JP30110493A JP2679598B2 JP 2679598 B2 JP2679598 B2 JP 2679598B2 JP 5301104 A JP5301104 A JP 5301104A JP 30110493 A JP30110493 A JP 30110493A JP 2679598 B2 JP2679598 B2 JP 2679598B2
- Authority
- JP
- Japan
- Prior art keywords
- fly ash
- thin plate
- refuse incinerator
- barrel
- rotary kiln
- 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 - Fee Related
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- Processing Of Solid Wastes (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明はゴミ焼却炉、特に流動床
ゴミ焼却炉から回収される飛灰中のダイオキシン類の除
去に係る。FIELD OF THE INVENTION The present invention relates to the removal of dioxins in fly ash recovered from refuse incinerators, especially fluidized bed refuse incinerators.
【0002】[0002]
【従来の技術】一般にダイオキシンと総称されるポリ塩
素化ダイオキシンとポリ塩素化ジベンゾフランは強い発
癌性と催奇性を有し、人体に蓄積するときわめて有害な
物質である。実験報告(「都市ごみ焼却施設のダイオキ
シンの生成と防止技術」花井−安全工学Vol27.NO.
6.1988) によれば、ダイオキシン類の発生は焼却炉
ではなく、大部分が電気集塵機において生成されてい
る。これはゴミの焼却が炭素を含む高分子の固体が熱分
解して低分子化し、気化して空気中の酸素と結合して炭
酸ガスに変化する過程があるが、ここで酸素ではなく含
塩素のプラスチックから供給される塩素と結合すると有
機塩素化合物が生成される。ところが焼却炉内は高温の
ため熱分解によって気化した成分はすぐに酸化されるた
め塩素化反応は殆どないか、さらに酸化されるのに対
し、電気集塵機内は低温(約 300℃前後)で飛灰の滞留
時間も長いから、酸化反応でなく塩素化反応が進行する
ことを確認している。2. Description of the Related Art Polychlorinated dioxins and polychlorinated dibenzofurans, which are generally called dioxin, have strong carcinogenicity and teratogenicity, and are extremely harmful substances when accumulated in the human body. Experimental report ("Dioxin generation and prevention technology in municipal waste incineration facility" Hanai-Safety Engineering Vol 27. NO.
6.1988), dioxins are mostly generated not in the incinerator but in the electrostatic precipitator. There is a process in which incineration of dust causes carbon-containing polymer solids to undergo thermal decomposition to lower molecular weight, vaporize and combine with oxygen in the air to change to carbon dioxide gas. Organochlorine compounds are formed when combined with chlorine supplied from plastics. However, since the inside of the incinerator is at a high temperature, the components vaporized by thermal decomposition are immediately oxidized, so there is almost no chlorination reaction, or it is further oxidized. Since the retention time of ash is long, it has been confirmed that the chlorination reaction proceeds, not the oxidation reaction.
【0003】焼却炉の集塵機で回収される飛灰から有害
なダイオキシン類を除去する課題は当然環境問題の中で
も緊急を要する重要な主題であり、このため多くの従来
技術が開示されてきた。回収した飛灰を効率よく熱分解
する技術が中心であり、たとえば加熱下で不活性ガス処
理を行ないV/TiO2 を触媒として使用する特開平5
−138150号公報、ダイオキシンの加熱と冷却を均
等にする炉構造に係る特開平5−146772号公報、
高温の燃焼ガスを直接飛灰に接触して熱分解する特開平
5−154461号公報などがある。The problem of removing harmful dioxins from fly ash collected by a dust collector of an incinerator is naturally an important and urgent subject among environmental problems, and therefore many conventional techniques have been disclosed. The main technology is the efficient thermal decomposition of the recovered fly ash. For example, an inert gas treatment is performed under heating and V / TiO 2 is used as a catalyst.
-138150, JP-A-5-146772, which relates to a furnace structure for uniformly heating and cooling dioxin,
JP-A-5-154461 discloses a method in which high-temperature combustion gas is directly contacted with fly ash for thermal decomposition.
【0004】一方、特開平5−33914号公報では回
収した飛灰に必要に応じて水または適当な結合剤を添加
した後、造粒装置に導入して加圧成形し、この粒体をゴ
ミ投入ホッパへゴミとともに投入して燃焼させることに
より、有機塩素化合物を熱分解させる。処理後の飛灰な
どを焼却炉の下底部から取り出し廃棄するという分解方
法を示している。On the other hand, in Japanese Patent Laid-Open No. 5-33914, water or a suitable binder is added to the collected fly ash as necessary, and then the fly ash is introduced into a granulator and pressure-molded, and the granules are trash The organic chlorine compound is thermally decomposed by throwing it into the feeding hopper together with dust and burning it. It shows a method of disassembling fly ash after processing from the bottom of the incinerator and discarding it.
【0005】[0005]
【発明が解決しようとする課題】以上に例示した従来技
術のうち、前三者はいずれも加熱、冷却の条件設定に工
夫を凝らした内容であり、それなりに熱分解効率の向上
に有効であると評価できるが、微粉である飛灰を含む回
収物をそのまま加熱することは別の課題を誘発する恐れ
が大きい。微粉と粒体が混合するとキルン内での滞留時
間分布の幅が広がり分解率にばらつきが生じて完全分解
を徹底するうえで不都合となる。また、300〜500℃の熱
風と接触することによって微粉の飛灰は溶融または軟化
して、キルン内壁に付着成長し、付着層が累積すると連
続運転に支障を来すようになるので、キルンを停止して
この付着物を取り除く作業を余儀なく強いられる。ま
た、微粉を含んだまま大量の熱風を通過させると粉塵の
飛散も激しく、排ガスの集塵機の捕集量も増加して再度
キルン内へ投入するという悪循環に悩まされることも予
想される。Among the above-mentioned prior arts, the former three are all devised in setting the conditions for heating and cooling, and are effective in improving the thermal decomposition efficiency. However, heating the recovered material containing fly ash, which is fine powder, as is is likely to cause another problem. When fine powder and granules are mixed, the width of the residence time distribution in the kiln widens and the decomposition rate varies, which is inconvenient for thorough decomposition. In addition, the fly ash of fine powder is melted or softened by coming into contact with hot air of 300 to 500 ° C and adheres and grows on the inner wall of the kiln, and if the adhered layer accumulates, it will hinder continuous operation. You have to stop and remove this deposit. In addition, if a large amount of hot air is passed through while containing fine powder, the dust will be severely scattered, the amount of exhaust gas collected by the dust collector will increase, and it may be troubled by the vicious cycle of re-introducing into the kiln.
【0006】この点では四番目の従来技術は飛灰を造粒
機にかけて微粉を粒状に成形しているから前記の従来技
術におけるかなりの課題は解決される。しかし、都市ゴ
ミの焼却炉としてはストーカ(火格子)式と流動床式と
に大別され、ストーカ式の場合には集塵機で回収した飛
灰を粒状化して再度炉内へゴミとともに投入すれば、熱
分解して無害化した灰分を炉の下底部から回収すること
ができるが、流動床式の場合には燃焼によって生じた灰
分の大部分は電気集塵機で回収されるという特性があ
り、 300℃程度の運転条件で既に述べたようにダイオキ
シン類が生成するのであるから、仮に回収した飛灰を粒
状に固めて再度炉内へ投入しても再度電気集塵機内で同
じダイオキシン類生成反応を繰り返すだけで悪循環を続
けるに過ぎない。In this respect, in the fourth prior art, fly ash is granulated by a granulator to form fine powder into granules, so that the considerable problems in the above prior art can be solved. However, incinerators for municipal waste are roughly classified into a stoker (grate) type and a fluidized bed type. In the case of a stoker type, if fly ash collected by a dust collector is granulated and then thrown into the furnace together with the waste. However, the ash content that has been pyrolyzed and rendered harmless can be recovered from the bottom of the furnace, but in the case of the fluidized bed type, most of the ash content generated by combustion is recovered by an electric dust collector. Since dioxins are generated as described above under operating conditions of about ℃, even if the collected fly ash is granulated and put into the furnace again, the same dioxins generation reaction is repeated in the electrostatic precipitator again. It just continues a vicious circle.
【0007】また、粒状に造粒したときは、飛灰のよう
に加熱によって溶融、軟化する恐れがない代りに同一温
度に粒子の内外が加熱されるまでに時間の浪費が多く、
完全に内部まで熱分解するための滞留時間を多く必要と
する。梅村の論文(「ごみ焼却炉飛灰中ダイオキシン類
の熱分解装置」産業機械1992年5月号)によれば、ダイ
オキシン類の熱分解処理の必須条件として 酸素欠乏状態の維持 一定温度(約 400℃)の維持 滞留時間(約1時間)の維持、ダイオキシン濃度によ
ってはさらに必要 滞留後 140℃以下で排出 を挙げているが、微粉のままでの熱分解には前記の課題
が残り、また固化造粒した場合にはの課題が残る。Further, when granulated into granules, there is no risk of melting and softening due to heating like fly ash, but a lot of time is wasted until the inside and outside of the particles are heated to the same temperature.
A long residence time is required to completely pyrolyze the interior. According to a paper by Umemura (“Pyrolysis equipment for dioxins in fly ash in a refuse incinerator”, May 1992, Industrial Machinery), maintaining oxygen deficiency at a constant temperature (about 400 Maintaining the retention time (about 1 hour), further required depending on the dioxin concentration Emission at 140 ° C or less after retention is mentioned, but the above problems remain for pyrolysis in the form of fine powder and solidification The problem remains when granulating.
【0008】本発明は以上に述べた課題のすべてを解決
し、効率的に飛灰を処理して環境改善に貢献するダイオ
キシン類の除去方法とその装置の提供を目的とする。An object of the present invention is to solve all of the above-mentioned problems, and to provide a method and an apparatus for removing dioxins that efficiently treat fly ash and contribute to environmental improvement.
【0009】[0009]
【課題を解決するための手段】本発明に係るゴミ焼却炉
の飛灰中のダイオキシン除去方法は、ごみ焼却炉の排ガ
スから捕集した飛灰粉末だけを相互に反対方向へ回転す
る一対の成形ロール間で挾圧搾出して薄板状に成形し、
該薄板成形体を解砕して偏平細片に細分化し、さらに微
粉を取り除いた該偏平細片を低酸素雰囲気内の回転窯内
で加熱することによって前記の課題を解決した。A method for removing dioxin in fly ash of a refuse incinerator according to the present invention is a pair of moldings in which only fly ash powder collected from exhaust gas of a refuse incinerator is rotated in mutually opposite directions. Squeeze between rolls to form a thin plate,
The above-mentioned problems were solved by crushing the thin plate molded body to subdivide it into flat strips, and heating the flat strips from which fine powder was removed in a rotary kiln in a low oxygen atmosphere.
【0010】より具体的には、薄板成形体の板厚は3〜
5mmの範囲とし、偏平細片の大きさは0.5〜8mmの
範囲で篩分けされていること、および加熱中の回転窯の
内部は酸素濃度が 5Vol%以下の雰囲気になっているこ
とがきわめて好ましい実施例である。More specifically, the thickness of the thin plate molded body is 3 to.
It should be in the range of 5 mm, the size of the flat strips should be sieved in the range of 0.5 to 8 mm, and the inside of the rotary kiln during heating should be in an atmosphere with an oxygen concentration of 5 Vol% or less. This is a very preferred embodiment.
【0011】前記の方法に使用する装置としては、互い
に平行な回転軸で軸支され所望の開度を隔てて反対方向
に回転する一対の成形ロール11と、該成形ロール間に
ゴミ焼却炉の排ガスから捕集した飛灰粉末だけを供給さ
れるホッパ12と、ホッパの下底部に連接した円筒状の
バレル13と、バレルの中心軸上で回転するスクリュー
14とを具えた飛灰粉末の薄板成形機1と、該薄板成形
体を偏平細片に細分化する解砕機2と、細分化した偏平
細片に含まれる微粉を篩分ける振動篩5と、横長筒状の
胴体へ前記偏平細片を装入し、胴体31をほぼ水平に維
持して回転しつつ低酸素雰囲気中で加熱するロータリー
キルン3よりなる構成が要件である。The apparatus used in the above method includes a pair of forming rolls 11 which are rotatably supported by mutually parallel rotating shafts and rotate in opposite directions with a desired opening, and a dust incinerator between the forming rolls. A thin plate of fly ash powder including a hopper 12 to which only the fly ash powder collected from the exhaust gas is supplied, a cylindrical barrel 13 connected to the lower bottom of the hopper, and a screw 14 rotating on the central axis of the barrel. A molding machine 1, a crusher 2 for subdividing the thin plate compact into flat strips, a vibrating sieve 5 for sieving fine powder contained in the subdivided flat strips, and the flat strips into a horizontally elongated tubular body. It is a requirement to have a configuration of a rotary kiln 3 in which the body 31 is charged and the body 31 is rotated in a low oxygen atmosphere while rotating while being kept substantially horizontal.
【0012】この装置の構成において、薄板成形機1は
バレル13の内周面上にバレル始端で最も深くはじまり
次第に浅く傾斜してバレルの終端から少なくともスクリ
ューの1ピッチ分以上残した中間点で消滅する複数の勾
配溝15を具え、ロータリーキルン3は外的加熱方式で
あって、胴体31の断面形状がほぼ正六角形で形成され
ていることが目的達成に最も有効である。In the construction of this apparatus, the thin plate molding machine 1 starts deepest on the inner peripheral surface of the barrel 13 at the beginning of the barrel and gradually inclines gradually, and disappears at an intermediate point left at least one pitch of the screw from the end of the barrel. It is most effective to achieve the purpose that the rotary kiln 3 is provided with a plurality of gradient grooves 15 and the rotary kiln 3 is of an external heating type, and the body 31 has a substantially hexagonal cross section.
【0013】[0013]
【作用】本発明の作用の特徴の一つは微粉状態の飛灰に
水分も結合剤も一切添加せず、乾燥状態の粉体だけを強
力にロール間で挾圧して成形する点にある。添加水分も
結合剤もなしで乾態成形すれば、目的の熱分解時にきわ
めて有利であることは当然であるが、実際にこのような
成形を可能とするには、成形ロール間で薄板状に挾圧搾
出する方法が抜群に優れている。次に薄板状の成形体を
解砕して偏平細片に細分し微粉を篩分けして取り除くこ
とも重要な意義がある。偏平であり細片であると、造粒
機による粒体と違って熱が全体に及んで均熱化するまで
の時間が短く、きわめて熱効率が高い成果に結びつく。
一般にダイオキシン類の熱分解は400℃ 前後が最適であ
り、全体を逸早くこの適正温度に加熱し、分解後 150℃
以下に急冷することが要諦とされている。その点、偏平
細片を急速に適正温度まで均熱化し、微粉の混合もない
から溶融、軟化して炉壁に付着する懸念もなく、効率的
に熱分解の反応が完結することはきわめて有利な作用と
言える。ACTION One of the features of the action of the present invention is that only the dry powder is strongly pressed between the rolls to form the fly ash in the form of fine powder without adding any water or binder. Naturally, dry molding without added water or binder is extremely advantageous at the time of intended thermal decomposition, but in order to actually enable such molding, it is necessary to form thin plates between molding rolls. The method of squeezing is excellent. Next, it is also important to disintegrate the thin plate-shaped compact into fine flat pieces and remove fine powder by sieving. The flat shape and the small pieces, unlike the granules produced by the granulator, takes a short time until the heat is evenly distributed over the whole body, resulting in extremely high thermal efficiency.
Generally, the optimum thermal decomposition of dioxins is around 400 ° C, and the whole is heated up to this proper temperature quickly, and after decomposition, 150 ° C.
It is essential to quench below. In that respect, it is extremely advantageous that the flat strips are rapidly soaked to the proper temperature, and there is no mixing of fine powder, so there is no concern that they will melt and soften and adhere to the furnace wall, and that the pyrolysis reaction will be completed efficiently. It can be said that it is an action.
【0014】外熱式のロータリーキルンで加熱する時点
において、炉の胴体が回転するにつれ、被加熱物は炉壁
に沿って持ち上げられて、ある点で自重によって落下す
るというカスケード運動を繰り返すが、図6にその運動
の概念を示している。すなわち、カスケード運動は、A
−回転上昇運動、B−ゆるやかな層の崩壊による方向転
換、C−なだれ運動、D−停留帯に分けて考えられる
が、微粉が主体である飛灰の場合には、炉壁に沿って持
ち上げられる部分で滑りが生じて上へ持ち上げられず、
その上部における雪崩運動を誘発することができないた
め、被加熱物同士の入れ替えがなくなって攪拌現象が衰
えて熱効率を著しく減退させることが多い。この点、偏
平細片であれば相互の摩擦係数が増加し絡み合って相互
に拘束するから、単体の微粉のような空滑りを発生する
ことは少なくて済む。これも有利な作用であるが、後述
の実施例のように装置を特定のものに限定すれば、この
作用はより効果的に昂進することができる。At the time of heating with an external heat type rotary kiln, as the body of the furnace rotates, the object to be heated is lifted along the wall of the furnace and falls at a certain point due to its own weight. Figure 6 shows the concept of the movement. That is, the cascade motion is A
-It can be considered to be divided into rotational ascending motion, B-direction change due to gradual collapse of layer, C-avalanche motion, and D-stop zone, but in the case of fly ash mainly composed of fine powder, it is lifted along the furnace wall. Slippage occurs at the part to be lifted and cannot be lifted up,
Since it is not possible to induce avalanche movement in the upper part, it is often the case that the objects to be heated are not exchanged with each other and the stirring phenomenon is weakened, resulting in a marked decrease in thermal efficiency. On the other hand, in the case of flat strips, the mutual friction coefficient increases and they are entangled with each other and restrained from each other. This is also an advantageous action, but if the device is limited to a specific one as in the embodiments described later, this action can be promoted more effectively.
【0015】[0015]
【実施例】図1は本発明の実施例のフローを示す正面概
略図でる。図の中で前工程として、流動床式ゴミ焼却炉
F、排ガスの冷却室C、空気予熱器H、電気集塵機Eと
誘引送風機Bが具えられて、飛灰が灰バンカ4、定量供
給機41を経由して薄板成形機1のホッパ12へ供給さ
れる。薄板成形機1は機種としてはローラコンパクタと
呼ばれる乾式の粉体成形機であり、その詳細は図2
(A)に示すように漏斗形のホッパ12の軸線にスクリ
ュー14を回転させてバレル13内へ飛灰を強制的に押
し込む。バレルの下方に相互に反対方向へ回転する一対
の成形ロール11があり飛灰を挾圧して薄板状に搾出す
る。1 is a schematic front view showing a flow of an embodiment of the present invention. As a pre-process in the figure, a fluidized bed waste incinerator F, an exhaust gas cooling chamber C, an air preheater H, an electric dust collector E and an induced air blower B are provided, and fly ash is an ash bunker 4 and a constant quantity feeder 41. And is supplied to the hopper 12 of the thin plate forming machine 1. The thin plate molding machine 1 is a dry powder molding machine called a roller compactor as a model, and its details are shown in FIG.
As shown in (A), the screw 14 is rotated around the axis of the funnel-shaped hopper 12 to forcibly push fly ash into the barrel 13. Below the barrel, there is a pair of forming rolls 11 that rotate in mutually opposite directions, and the fly ash is pinched and squeezed into a thin plate.
【0016】この機種は本来、摩擦係数が小さく成形し
難い粉体材料の成形に他の機種よりも優れているが、な
お、微粉の多い飛灰の成形に際しては、飛灰とバレルの
内周面との摩擦よりもスクリューの羽根表面との摩擦の
方が勝るため、滑りを生じて飛灰が羽根と共回りを起こ
して逃げる懸念も残る。そのために出願人自身の開発に
よる実公平3−12478号公報の従来技術を流用し
て、図(B)で例示するようにバレルの内面の始端で始
まり終端から少なくともスクリュー1ピッチ分残した中
間点で消滅する複数の勾配溝15を刻設した実施例が好
結果をもたらす。すなわちこの勾配溝15に充填した飛
灰はその凹側面に捉えられて拘束係止を受け、共回りし
ようとする羽根周辺との間に剪断作用が働いて、飛灰の
送り作用が増進されるのである。この場合、成形に当っ
ては純粋に飛灰だけを供給し、その他の水分や結合剤な
ど一切の添加を行なわないことが本発明の特徴であり、
以後の熱分解工程での熱効率の向上を約束する要因であ
る。成形時の薄板の板厚は3〜5mm、特に4mm程度
に成形したものが好都合である。This model is originally superior to other models in molding powder materials that have a small friction coefficient and are difficult to mold. However, in molding fly ash containing a large amount of fine powder, fly ash and the inner circumference of the barrel Since the friction with the surface of the blade of the screw is greater than the friction with the surface, there is a concern that slip may occur and fly ash may co-rotate with the blade and escape. For that purpose, the conventional technique of Japanese Utility Model Publication No. 3-12478 developed by the applicant is diverted, and as shown in FIG. (B), a middle point left at least one screw pitch from the start end of the inner surface of the barrel An embodiment in which a plurality of sloped grooves 15 that disappear in step S1 are engraved gives good results. That is, the fly ash filled in the gradient groove 15 is caught by the concave side surface thereof and is restrained and locked, and a shearing action is exerted between the fly ash and the periphery of the blade that tries to rotate together, so that the fly ash feeding action is enhanced. Of. In this case, it is a feature of the present invention that only pure fly ash is supplied during molding, and no addition of other water or binder is performed.
This is a factor that promises to improve the thermal efficiency in the subsequent thermal decomposition process. It is convenient that the thin plate at the time of molding has a thickness of 3 to 5 mm, especially about 4 mm.
【0017】薄板状の成形体を偏平細片に細分化するの
は解砕機2であるが、その一例は図3(A)(B)に示
す粗砕機21(ブレーカ)と図4(A)(B)に示す整
粒機22(グラニュレータ)とを連結して形成されてい
る。粗砕機は投入口26から供給される薄板成形体を投
入口部に取付けた固定歯25と回転軸23に植設した回
軸歯24の間で破砕して適宜の大きさの偏平細片として
下方の整粒機22へ送る。整粒機は中央へ水平に横架し
た断面が六角形の中空筒体27の角コーナへ破砕刃28
を配置し、この中空筒体の外周囲を金網または多孔板な
どのスクリーン29を具備し、該中空筒体に供給された
適宜の大きさの偏平細片を破砕刃28にて解砕し、スク
リーン目開き以下の大きさに整粒後、スクリーンの外部
に放出し、回収後さらに図1のように振動篩5にかけて
微粉を確実に取り除きロータリーキルン3へ供給する。It is the crusher 2 that subdivides the thin plate-shaped compact into flat strips, one example of which is the coarse crusher 21 (breaker) shown in FIGS. 3 (A) and 3 (B) and FIG. 4 (A). It is formed by connecting with a granulator 22 (granulator) shown in (B). The crusher crushes the thin plate molded body supplied from the charging port 26 between the fixed teeth 25 attached to the charging port and the rotary shaft teeth 24 planted on the rotary shaft 23 to form a flat strip having an appropriate size. It is sent to the granulator 22 below. The sieving machine is crushed by a crushing blade 28 into the corner of a hollow cylindrical body 27 with a hexagonal cross section that is horizontally laid horizontally in the center.
And a screen 29 such as a wire net or a perforated plate is provided around the outer periphery of the hollow cylinder, and the flat pieces of an appropriate size supplied to the hollow cylinder are crushed by a crushing blade 28. After sizing to a size equal to or smaller than the screen opening, the particles are discharged to the outside of the screen, and after collection, they are passed through a vibrating sieve 5 to reliably remove fine powder and supplied to the rotary kiln 3.
【0018】本実施例で適用するロータリーキルン3
は、出願人自身の考案に係る実開昭62−145098
号公報の従来技術を流用した。この従来技術は図5
(A)(B)に示すように外熱炉32を具えたロータリ
ーキルンの一形式であるが、その胴体31がほぼ正六角
形を形成する断面からなり、ほぼ中央に飛灰の温度計3
3を具えている。先に述べたとおり図6に示した炉内で
の飛灰のカスケード運動が、微粉のままであれば炉の内
壁に沿った滑り現象が生じて材料間の攪拌作用が著しく
阻害されるため、本発明では偏平細片としてこの課題に
対処したのであるが、、炉壁内面が滑らかであれば、微
粉状態よりも遥かに滑り難い偏平細片といえども、な
お、滑り運動−Gの発生する懸念が残るので、念の為に
最も空滑り現象を防止できる角形の断面を具えた胴体か
らなるロータリーキルンとしたのである。この結果、炉
内におけるカスケード運動は図(B)のように滑りが殆
ど阻止されて細片同士の攪拌が十分に進行し、装入され
た飛灰の細片がほぼ均等に同時加熱を受け、迅速に熱分
解反応が進行する。Rotary kiln 3 applied in this embodiment
Is based on the applicant's own invention, Shokai 62-145098.
The conventional technique disclosed in the publication is used. This prior art is shown in FIG.
As shown in (A) and (B), this is a type of rotary kiln equipped with an external heating furnace 32, but its body 31 has a cross section forming an approximately hexagonal shape, and a fly ash thermometer 3 is provided approximately in the center.
It has three. As described above, if the cascade motion of fly ash in the furnace shown in FIG. 6 remains as fine powder, a sliding phenomenon along the inner wall of the furnace occurs and the stirring action between the materials is significantly hindered. In the present invention, this problem is dealt with as a flat strip, but if the inner wall of the furnace wall is smooth, even if it is a flat strip that is much less slippery than in the fine powder state, sliding motion -G still occurs. Because of concern, the rotary kiln consisted of a fuselage with a rectangular cross-section that most effectively prevents slipping. As a result, the cascade motion in the furnace is almost completely prevented from slipping as shown in Fig. (B), the agitation between the pieces is sufficiently advanced, and the loaded fly ash pieces are simultaneously heated substantially evenly. , The thermal decomposition reaction proceeds rapidly.
【0019】図1に示すようにロータリーキルン3の一
端には窒素発生装置32が連結して、加熱中は常に窒素
気流が炉内へ流入して非酸化性の雰囲気としている。ロ
ータリーキルン3から排出した熱分解処理済みの灰分は
冷却器33へ送り込まれ、窒素雰囲気中で冷却されて
後、排出され最終的に灰バンカ34へ貯溜され回収され
る。なお、ロータリーキルンの供給側には集塵機35と
誘引送風機36を具え、再度微粉を回収して薄板成形機
1へ戻す。As shown in FIG. 1, a nitrogen generator 32 is connected to one end of the rotary kiln 3 so that a nitrogen gas stream constantly flows into the furnace during heating to create a non-oxidizing atmosphere. The pyrolyzed ash discharged from the rotary kiln 3 is sent to a cooler 33, cooled in a nitrogen atmosphere, discharged, and finally stored in an ash bunker 34 and collected. A dust collector 35 and an induced air blower 36 are provided on the supply side of the rotary kiln to collect fine powder again and return it to the thin plate molding machine 1.
【0020】[0020]
【発明の効果】以上に述べたとおり本発明に係るゴミ焼
却炉の飛灰中のダイオキシン類の除去方法とその装置
は、従来技術の何れと比べてもダイオキシン類の熱分解
効率が高く、有害成分のほぼ完全な除去を実現すること
ができる。効果の一例を次の実施例で説明する。実施例
の試料作成の条件は、流動床焼却炉の排ガスを電気集塵
機で回収した飛灰を出発原料とする。このときの飛灰の
粒度は平均粒径が27μm、嵩比重が0.66であった。この
飛灰を回転数8rpm、圧縮圧2.5t/cm2のローラコ
ンパクタにかけて、板厚4.3mm、板幅60mmの薄板に
成形し、さらに粗砕機、整粒機にかけた後、振動篩で微
粉と分離して 0.5〜8mmの偏平細片として72.5%が回
収され、0.5mm以下の微粉は27.5%で、再びローラコ
ンパクタへ戻して飛灰とともに供給した。外熱式のロー
タリーキルンの内部の酸素濃度は1%、加熱温度は飛灰
の温度で410℃、 炉内の加熱部分の滞留時間は60分とし
た。この実施例に対してロータリーキルンにおける熱分
解条件はほぼ同一に揃え、前処理である偏平細片までの
工程を省き単なる微粉のままの飛灰を出発原料として比
較例とした。それぞれのダイオキシンの熱分解成績を表
1に列記する。INDUSTRIAL APPLICABILITY As described above, the method and apparatus for removing dioxins in fly ash of a refuse incinerator according to the present invention have a higher thermal decomposition efficiency for dioxins than any of the conventional techniques and are harmful. Nearly complete removal of components can be achieved. An example of the effect will be described in the following embodiment. The conditions for sample preparation in the examples are as follows: fly ash obtained by collecting the exhaust gas from the fluidized bed incinerator with an electric dust collector is used as a starting material. At this time, the fly ash had an average particle size of 27 μm and a bulk specific gravity of 0.66. This fly ash was applied to a roller compactor with a rotation speed of 8 rpm and a compression pressure of 2.5 t / cm 2 to form a thin plate with a plate thickness of 4.3 mm and a plate width of 60 mm, which was further subjected to a crushing machine and a sizing machine, and then finely powdered with a vibrating sieve. 72.5% was recovered as a flat strip of 0.5 to 8 mm and fine powder of 0.5 mm or less was 27.5%, which was returned to the roller compactor again and supplied together with fly ash. The oxygen concentration inside the externally heated rotary kiln was 1%, the heating temperature was 410 ° C at the temperature of fly ash, and the residence time of the heated portion in the furnace was 60 minutes. The pyrolysis conditions in the rotary kiln were substantially the same as those in this example, and the process up to the flat strip, which was a pretreatment, was omitted, and a simple ash fly ash was used as a starting material for a comparative example. The thermal decomposition results of each dioxin are listed in Table 1.
【0021】[0021]
【表1】 [Table 1]
【0022】表からも明らかなとおり実施例と比較例と
をみれば、実施例は塩素化ダイオキシン(PCDD)も
塩素化ジベンゾフラン(PCDF)もその除去率は優れ
ている。特に実施例のTEQ(毒性等価濃度)の低減率
が抜群によく、実際の現地に操業した場合の環境問題に
及ぼす貢献の大きさが確かに予想される。除去率以外に
比較例ではロータリキルンの胴体の内壁面への微粉の溶
着,付着が発生し、付着物の成長のため長時間安定した
運転が出来なかったが実施例では溶着付着が全く発生せ
ず安定した運転が可能であった。As is clear from the table, when the examples and the comparative examples are seen, the examples show that the chlorinated dioxin (PCDD) and chlorinated dibenzofuran (PCDF) have excellent removal rates. In particular, the reduction rate of TEQ (toxic equivalent concentration) in the examples is excellent, and the contribution to the environmental problems when actually operating in the field is certainly expected. In addition to the removal rate, in the comparative example, fine powder was welded and adhered to the inner wall surface of the body of the rotary kiln, and stable operation could not be performed for a long time due to the growth of the adhered substance. Without this, stable operation was possible.
【図1】本発明の工程を示すフロー図である。FIG. 1 is a flow chart showing steps of the present invention.
【図2】実施例のうち、薄板成形機の縦断正面図(A)
とバレルの横断正面図(B)である。FIG. 2 is a vertical cross-sectional front view of the thin plate molding machine in the examples (A).
It is a transverse front view (B) of the barrel.
【図3】粗砕機の縦断正面図(A)と側面断面図(B)
である。FIG. 3 is a vertical front view (A) and a side sectional view (B) of the crusher.
It is.
【図4】整粒機の縦断正面図(A)と側面断面図(B)
である。FIG. 4 is a vertical front view (A) and a side cross-sectional view (B) of the granulator.
It is.
【図5】ロータリーキルンの正面図(A)と胴体の断面
図(B)である。FIG. 5 is a front view (A) of a rotary kiln and a sectional view (B) of a body.
【図6】従来技術における課題を示すロータリーキルン
の胴体の断面図である。FIG. 6 is a sectional view of a body of a rotary kiln showing a problem in the related art.
1 薄板成形機 2 解砕機 3 ロータリーキルン 4 灰バンカ 5 振動篩 11 成形ロール 12 ホッパ 13 バレル 14 スクリュー 15 勾配溝 21 粗砕機 22 整粒機 23 回転軸 24 回転歯 25 固定歯 26 投入口 27 筒体 28 破砕刃 29 スクリーン 31 胴体 32 窒素発生装置 33 冷却器 34 灰バンカ 35 集じん機 36 誘引送風機 F 流動床式ごみ焼却炉 C 排ガス冷却室 H 空気予熱機 E 電気集塵機 B 誘引送風機 1 Thin Plate Forming Machine 2 Crushing Machine 3 Rotary Kiln 4 Ash Bunker 5 Vibrating Sieve 11 Forming Roll 12 Hopper 13 Barrel 14 Screw 15 Gradient Groove 21 Coarse Crusher 22 Granulator 23 Rotating Shaft 24 Rotating Teeth 25 Fixed Teeth 26 Input 27 Cylindrical 28 Crushing blade 29 Screen 31 Body 32 Nitrogen generator 33 Cooler 34 Ash bunker 35 Dust collector 36 Induction blower F Fluidized bed waste incinerator C Exhaust gas cooling room H Air preheater E Electric dust collector B Induction blower
───────────────────────────────────────────────────── フロントページの続き (72)発明者 鎌形 昌美 大阪府大阪市西区北堀江1丁目12番19号 株式会社栗本鐵工所内 (56)参考文献 特開 平4−84977(JP,A) 特開 平5−146772(JP,A) 特開 平5−15867(JP,A) 特開 平5−104073(JP,A) 特開 平5−228462(JP,A) ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Masami Kamagata 1-12-19 Kitahorie, Nishi-ku, Osaka City, Osaka Prefecture Kurimoto Iron Works Co., Ltd. (56) Reference JP-A-4-84977 (JP, A) Kaihei 5-146772 (JP, A) JP 5-15867 (JP, A) JP 5-104073 (JP, A) JP 5-228462 (JP, A)
Claims (5)
末だけを相互に反対方向へ回転する一対の成形ロール間
で挾圧搾出して薄板状に成形し、該薄板成形体を解砕し
て偏平細片に細分化し、さらに微粉を取り除いた該偏平
細片を低酸素雰囲気内の回転窯内で加熱することを特徴
とするゴミ焼却炉の飛灰中のダイオキシン類の除去方
法。1. A fly ash powder collected from the exhaust gas of a refuse incinerator is pressed and squeezed between a pair of forming rolls rotating in opposite directions to form a thin plate, and the thin plate formed body is crushed. A method for removing dioxins in fly ash of a refuse incinerator, characterized by heating the flat strips, which have been finely divided into flat strips, and fine powders have been removed, in a rotary kiln in a low oxygen atmosphere.
3〜5mmの範囲とし、偏平細片の大きさは0.5〜8m
mの範囲で篩分けされていることを特徴とするゴミ焼却
炉の飛灰中のダイオキシン類の除去方法。2. The thin plate molding according to claim 1, wherein the plate thickness is in the range of 3 to 5 mm, and the flat strip has a size of 0.5 to 8 m.
A method for removing dioxins from fly ash of a refuse incinerator, which is characterized by being screened in a range of m.
転窯の内部は酸素濃度が 5Vol%以下の雰囲気になって
いることを特徴とするゴミ焼却炉の飛灰中のダイオキシ
ン類の除去方法。3. The method for removing dioxins in fly ash of a refuse incinerator according to claim 1 or 2, wherein the inside of the rotary kiln during heating is in an atmosphere having an oxygen concentration of 5 Vol% or less. .
度を隔てて反対方向に回転する一対の成形ロール11
と、該成形ロール間にゴミ焼却炉の排ガスから捕集した
飛灰粉末だけを供給されるホッパ12と、ホッパの下底
部に連接した円筒状のバレル13と、バレルの中心軸上
で回転するスクリュー14とを具えた飛灰粉末の薄板成
形機1と、該薄板成形体を偏平細片に細分化する解砕機
2と、細分化された偏平細片に含まれる微粉を篩分けす
る振動篩5と、横長筒状の胴体へ前記偏平細片を装入
し、胴体31をほぼ水平に維持して回転しつつ低酸素雰
囲気中で加熱するロータリーキルン3よりなることを特
徴とするゴミ焼却炉の飛灰中のダイオキシン類除去装
置。4. A pair of forming rolls 11 supported by rotating shafts parallel to each other and rotating in opposite directions with a desired opening.
A hopper 12 to which only fly ash powder collected from the exhaust gas of the refuse incinerator is supplied between the forming rolls, a cylindrical barrel 13 connected to the lower bottom of the hopper, and rotating on the central axis of the barrel. A fly ash powder thin plate forming machine 1 equipped with a screw 14, a crusher 2 for dividing the thin plate formed body into flat strips, and a vibrating screen for sieving fine powders contained in the flat strips. 5 and a rotary kiln 3 for loading the flat strip into a horizontally long tubular body and heating the body 31 in a low oxygen atmosphere while rotating while keeping the body 31 substantially horizontal. Equipment for removing dioxins in fly ash.
ル13の内周面上にバレル始端で最も深く始まり次第に
浅く傾斜してバレルの終端から少なくともスクリューの
1ピッチ分以上残した中間点で消滅する複数の勾配溝1
5を具え、ロータリーキルン3が外的加熱方式であっ
て、胴体31の断面形状がほぼ正六角形で形成されてい
ることを特徴とするゴミ焼却炉の飛灰中のダイオキシン
類除去装置。5. The thin plate molding machine 1 according to claim 4, wherein the thin plate forming machine 1 starts deepest on the inner peripheral surface of the barrel 13 at the barrel start end, and gradually inclines shallowly at an intermediate point at least one pitch of the screw left from the end of the barrel. Multiple disappearing gradient grooves 1
5. The apparatus for removing dioxins in fly ash of a refuse incinerator, comprising a rotary kiln 3 according to claim 5, which is of an external heating type, and a body 31 having a substantially hexagonal cross section.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP5301104A JP2679598B2 (en) | 1993-11-04 | 1993-11-04 | Method and equipment for removing dioxins from fly ash in a refuse incinerator |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP5301104A JP2679598B2 (en) | 1993-11-04 | 1993-11-04 | Method and equipment for removing dioxins from fly ash in a refuse incinerator |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH07124536A JPH07124536A (en) | 1995-05-16 |
JP2679598B2 true JP2679598B2 (en) | 1997-11-19 |
Family
ID=17892901
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP5301104A Expired - Fee Related JP2679598B2 (en) | 1993-11-04 | 1993-11-04 | Method and equipment for removing dioxins from fly ash in a refuse incinerator |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2679598B2 (en) |
Families Citing this family (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP3131626B2 (en) * | 1996-06-10 | 2001-02-05 | 工業技術院長 | Decomposition method of dioxins by supercritical water |
CN102233349B (en) * | 2010-04-28 | 2015-04-08 | 盐城豪瑞达实业有限公司 | Burning fly ash pretreatment technology |
CN107500577B (en) * | 2017-08-07 | 2022-12-20 | 中国计量大学 | Control device and method for recycling dioxin by treating solid waste kiln dust in cooperation with cement kiln |
CN114877344B (en) * | 2022-06-02 | 2024-06-07 | 天津中材工程研究中心有限公司 | System and method for continuously disposing dioxin in fly ash |
CN118089037A (en) * | 2024-04-15 | 2024-05-28 | 浙江大学 | Device and method for self-maintaining type smoldering disposal of dioxin in waste incineration fly ash |
-
1993
- 1993-11-04 JP JP5301104A patent/JP2679598B2/en not_active Expired - Fee Related
Also Published As
Publication number | Publication date |
---|---|
JPH07124536A (en) | 1995-05-16 |
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