JPH09243047A - Waste fusing facility equipped with slag cleaner, and manufacture of granulated slag - Google Patents

Waste fusing facility equipped with slag cleaner, and manufacture of granulated slag

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Publication number
JPH09243047A
JPH09243047A JP8047781A JP4778196A JPH09243047A JP H09243047 A JPH09243047 A JP H09243047A JP 8047781 A JP8047781 A JP 8047781A JP 4778196 A JP4778196 A JP 4778196A JP H09243047 A JPH09243047 A JP H09243047A
Authority
JP
Japan
Prior art keywords
slag
water
washing
tank
cleaning
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
JP8047781A
Other languages
Japanese (ja)
Other versions
JP3549135B2 (en
Inventor
Masahide Nishigaki
正秀 西垣
Takeshi Shinohara
武 篠原
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.)
Takuma Co Ltd
Original Assignee
Takuma Co Ltd
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 Takuma Co Ltd filed Critical Takuma Co Ltd
Priority to JP04778196A priority Critical patent/JP3549135B2/en
Publication of JPH09243047A publication Critical patent/JPH09243047A/en
Application granted granted Critical
Publication of JP3549135B2 publication Critical patent/JP3549135B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To roughly zero the heavy metal pollution of granulated slag by discharging the granulated slag primarily cleaned at the end of a conveyor by a nozzle, and cleaning this with a washing conveyor, and also cleaning it at the end by a nozzle. SOLUTION: Fused slag C falls into a slag water-cooling vessel 6, and becomes granulated slag D1, and then it is conveyed up onto water surface by the slag conveyor 7 within a water cooling vessel 6. The granulated slag D1 in the vicinity of the uppermost part of the slag conveyor 7 is cleaned in the position where it is exposed onto the surface of the water blown by a primary cleaning nozzle 8. The slag D1 from which a great part of the slag cleaning water F adhering to the surface is washed off is successively thrown into the slag washing vessel 9 provided under it. The granulated slag D1 which has dropped into the lower tank of the slag washing vessel 9 is cleaned again by the pure water E from the secondary cleaning nozzle 11 at the uppermost part of the slag washing vessel 9 while being conveyed up by a washing conveyor 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】本発明はごみ焼却炉からの焼
却残査、飛灰、都市ごみ等を溶融処理する廃棄物溶融処
理設備に於いて利用されるものであり、溶融処理設備に
付属する水砕スラグの処理システムに改良を加えること
により、ランニングコストの増加を招くことなしに重金
属汚染の殆んどない高品質の水砕スラグを得られるよう
にした、スラグ洗浄装置を備えた廃棄物溶融処理設備と
これを用いた水洗スラグの製造方法に関するものであ
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention is used in a waste melting treatment facility for melting incineration residue from a refuse incinerator, fly ash, municipal solid waste, etc., and is attached to the melting treatment facility. Waste with a slag cleaning device, by improving the granulated slag treatment system so that high quality granulated slag with almost no heavy metal contamination can be obtained without increasing running costs. The present invention relates to a melting treatment facility and a method for producing a water washing slag using the same.

【0002】[0002]

【従来の技術】近年、ごみ焼却炉から排出される焼却残
査や飛灰の減容及び無害化を図るため、焼却残査等の溶
融固化処理法が注目され、現実に実用に供されている。
焼却残査等は溶融固化することにより、その容積を1/
2〜1/3に減らすことができるうえ、重金属等有害物
質の溶出の防止や溶融スラグの再利用、最終埋立処分場
の延命等が可能になるからである。
2. Description of the Related Art In recent years, in order to reduce the volume and detoxify the incineration residue and fly ash discharged from a refuse incinerator, a melting and solidifying method such as incineration residue has attracted attention and has been put to practical use. .
The volume of incineration residue etc.
This is because it can be reduced to 2 to 1/3, and it is possible to prevent elution of harmful substances such as heavy metals, reuse molten slag, and extend the life of the final landfill disposal site.

【0003】而して、前記焼却残査等の被溶融物の溶融
固化処理方法には、アーク溶融炉やプラズマアーク炉、
電気抵抗炉等を使用し、電気エネルギーによって被溶融
物を溶融固化する方法と、表面溶融炉や旋回溶融炉、コ
ークスベッド炉等を使用し、燃料の燃焼エネルギーによ
って被溶融物を溶融固化する方法とが多く利用されてお
り、ごみ焼却設備に発電設備が併置されている場合に
は、前者の電気エネルギーを用いる方法が、また発電設
備が併置されていない場合には、後者の燃焼エネルギー
を用いる方法が夫々多く採用されている。
[0003] Thus, the melting and solidifying method for the material to be melted, such as the incineration residue, includes arc melting furnaces, plasma arc furnaces,
A method of melting and solidifying a material to be melted by electric energy using an electric resistance furnace, etc., and a method of melting and solidifying a material to be melted by combustion energy of fuel using a surface melting furnace, a swirling melting furnace, a coke bed furnace, etc. When the waste incineration facility and the power generation equipment are co-located, the former method of using electric energy is used, and when the power generation equipment is not co-located, the latter combustion energy is used. Each method is widely adopted.

【0004】図2は、従前の溶融炉における水砕スラグ
の生成の一例を示すものである。図2に於いて21は溶
融炉、22は落口、23はスラグ水冷槽、24は水砕ス
ラグ、25はスラグコンベア、26はスラグ受槽であ
り、溶融炉21内で被溶融物を溶融することにより生成
された溶融スラグは、落口22を経て冷却水を貯えたス
ラグ水冷槽23内へ落し込まれ、ここで水砕スラグ24
となる。また、生成された前記水砕スラグ24は、水冷
槽23内に設けたスラグコンベア25によりスラグ受槽
26内へ排出される。尚、前記スラグ受槽26内へ排出
された水砕スラグ24には通常3〜5wt%の水分が付
着しており、この付着水と蒸発により失なわれる蒸発水
とに相当する量の水が、水冷槽23内へ適宜に補充され
て行く。
FIG. 2 shows an example of generation of water granulated slag in a conventional melting furnace. In FIG. 2, 21 is a melting furnace, 22 is an outlet, 23 is a slag water cooling tank, 24 is water granulated slag, 25 is a slag conveyor, and 26 is a slag receiving tank, and melts a material to be melted in the melting furnace 21. The molten slag generated by this is dropped into the slag water cooling tank 23 storing the cooling water through the outlet 22, where the water granulated slag 24
Becomes The generated granulated slag 24 is discharged into the slag receiving tank 26 by the slag conveyor 25 provided in the water cooling tank 23. Incidentally, the water granulated slag 24 discharged into the slag receiving tank 26 usually has a water content of 3 to 5 wt%, and an amount of water corresponding to the water adhered and the evaporated water lost by evaporation is It is replenished into the water cooling tank 23 as appropriate.

【0005】前記のように、溶融炉内で溶融された被溶
融物(溶融スラグ)は、冷却水内へ投入することにより
急冷され、ガラス状の水砕スラグとなる。このようにし
て形成された水砕スラグ24内には、焼却残査内に存在
していた重金属類の一部が含有されているものの、これ
等の物質は物理的・化学的に一層安定した状態でスラグ
内に封入されており、その結果、水砕スラグ24からの
重金属類の溶出は大幅に抑制されることになる。例えば
産業廃棄物の陸上埋立基準に於いては、埋立で特に問題
となる重金属の鉛の溶出値を0.3mg/l以下に規制
しているが、水砕スラグ24はこの鉛に対する溶出値は
勿論のことその他の規制物質に対する溶出値について
も、規制値以下の値となっている。
As described above, the material to be melted (molten slag) melted in the melting furnace is rapidly cooled by being poured into the cooling water to become glassy granulated slag. The granulated slag 24 thus formed contains some of the heavy metals present in the incineration residue, but these substances are physically and chemically more stable. It is enclosed in the slag in the state, and as a result, the elution of heavy metals from the water granulated slag 24 is significantly suppressed. For example, the landfill standard for industrial waste regulates the elution value of lead, which is a heavy metal that is particularly problematic in landfill, to 0.3 mg / l or less, but the granulated slag 24 has an elution value for this lead. Of course, the elution values for other regulated substances are also below the regulated values.

【0006】ところで、前記水砕スラグ24は溶融のた
めに多量のエネルギーを消費して生成されたものであ
り、しかも硬度が極めて高いと云う特性を有している。
そのため、単に埋立により処分するだけでは経済性に欠
け、資源経済の点からも積極的にその有効利用を推進す
べきものであり、現実にコンクリートフィラー、路盤
材、盛土材、埋戻材、建築ブロック材等への応用につい
て、各方面に於いて研究・開発が行なわれている。
By the way, the water granulated slag 24 is produced by consuming a large amount of energy for melting and has a characteristic that the hardness is extremely high.
Therefore, it is not economical to simply dispose of by landfill, and it is necessary to actively promote its effective use from the viewpoint of resource economy. Actually, concrete filler, roadbed material, embankment material, backfill material, building block Research and development are being carried out in various fields regarding the application to materials and the like.

【0007】尚、前記水砕スラグ24をコンクリートフ
ィラーや路盤材等として利用する場合、その安全性を確
保すると云う観点から各用途毎の重金属類の溶出基準を
定めるのが望ましいが、現時点に於いては、未だ溶出基
準として定められたものは無い。しかし、これ等の用途
に於いては、水砕スラグ24の殆んどが土壌と直接に接
触する状態で使用されるものであるから、現行の土壌環
境基準を視野に入れてその溶出基準が定められ、これに
よって安全性の確保が担保されるものと考えられる。
When the water granulated slag 24 is used as a concrete filler or a roadbed material, it is desirable to determine the elution standard of heavy metals for each application from the viewpoint of ensuring its safety, but at this time, However, there is still no established elution standard. However, in these applications, most of the granulated slag 24 is used in a state of being in direct contact with the soil, and therefore the elution standard is set in view of the current soil environmental standard. It is stipulated that securement of safety is guaranteed by this.

【0008】一方、前記土壌環境基準では、例えば重金
属である鉛の溶出値は0.01mg/l以下に規制され
ており、極めて厳しい規制値となっている。これに対し
て、従来の溶融炉21で生成された水砕スラグ24は、
スラグ自体から重金属類、例えば鉛を現行の土壌環境基
準の規制値を越えて溶出するようなことは全く無く、且
つこのことは多くの溶出試験を通して実証されている。
しかし、水砕スラグ24に付着した冷却水(通常、前述
の通り3〜5wt%の量である)は、重金属類によって
相当に汚染されている。その結果、付着水に含まれてい
た鉛化合物等が水砕スラグ24の外表面から離脱溶出
し、基準値を越える土壌汚染を生ずることになる。
On the other hand, according to the soil environmental standards, the elution value of lead, which is a heavy metal, is regulated to 0.01 mg / l or less, which is an extremely strict regulation value. On the other hand, the granulated slag 24 produced in the conventional melting furnace 21 is
There is no case where heavy metals such as lead are leached from the slag itself in excess of the regulation values of the existing soil environmental standards, and this has been verified through many leaching tests.
However, the cooling water attached to the granulated slag 24 (usually in an amount of 3 to 5 wt% as described above) is considerably contaminated by heavy metals. As a result, lead compounds and the like contained in the adhered water are separated and eluted from the outer surface of the granulated slag 24, resulting in soil contamination exceeding the standard value.

【0009】従って、水砕スラグ4の有効利用を推進す
るためには、被溶融物を未溶融部分がないように完全に
溶融させ、これによって水砕スラグからの重金属類の溶
出を皆無にすると共に、水砕用冷却水による汚染にも留
意して、安全性に優れた良質の水砕スラグを安定して製
造することが重要となる。
Therefore, in order to promote the effective use of the water granulated slag 4, the material to be melted is completely melted so that there is no unmelted portion, thereby eliminating the elution of heavy metals from the water granulated slag. At the same time, it is important to keep in mind the contamination by the cooling water for water granulation and to stably manufacture high quality water granulation slag with excellent safety.

【0010】[0010]

【発明が解決しようとする課題】本発明は、従前の溶融
炉に於いて生成された水砕スラグに於ける上述の如き問
題、即ち水砕スラグ自体からの重金属類の溶出は防止さ
れるものの、付着した水砕用冷却水の汚染に起因する重
金属汚染を生ずる虞れがあると云う問題を解決せんとす
るものであり、重金属汚染の発生をほぼ皆無とすること
により、安全性に優れた高品質の水砕スラグを生成でき
るようにしたスラグ洗浄装置を備えた廃棄物溶融処理設
備とこれを用いた水砕スラグの製造方法を提供するもの
である。
SUMMARY OF THE INVENTION The present invention prevents the above-mentioned problems in water granulated slag produced in a conventional melting furnace, that is, the elution of heavy metals from the water granulated slag itself is prevented. The purpose is to solve the problem that heavy metal pollution may occur due to the pollution of cooling water for water granulation that has adhered, and by eliminating almost all the heavy metal pollution, excellent safety is achieved. The present invention provides a waste melting treatment facility equipped with a slag cleaning device capable of producing high-quality water granulated slag, and a method for producing water granulated slag using the same.

【0011】[0011]

【課題を解決するための手段】本願装置発明は、水砕ス
ラグを生成する廃棄物溶融処理設備に於いて、溶融スラ
グCを受け入れるスラグコンベア10を有するスラグ水
冷槽6と,前記スラグ水冷槽6からの水砕スラグD1
受け入れる水洗コンベア10を有するスラグ水洗槽9
と,前記スラグ水洗槽9のスラグ出口側近傍に設けら
れ、清水Eを噴射するスラグ2次洗浄水ノズル11と,
前記スラグ水冷槽6のスラグ出口側近傍に設けられ、前
記スラグ水洗槽9内の2次洗浄排水H1 を噴射する。ス
ラグ1次洗浄水ノズル12と,溶融排ガス冷却室5内に
設けられ、前記スラグ水冷槽6からの1次洗浄排水F1
を噴射する溶融排ガス冷却用水噴霧ノズル18とから構
成したことを発明の基本構成とするものである。
According to the present invention, in a waste melting treatment facility for producing granulated slag, a slag water cooling tank 6 having a slag conveyor 10 for receiving a molten slag C, and the slag water cooling tank 6 are provided. Slag washing tank 9 having a washing conveyor 10 for receiving water granulated slag D 1 from
And a slag secondary washing water nozzle 11 provided near the slag outlet side of the slag washing tank 9 for injecting fresh water E,
The secondary cleaning wastewater H 1 is provided in the slag water cooling tank 6 in the vicinity of the slag outlet side and the secondary cleaning waste water H 1 in the slag water cleaning tank 9 is injected. The slag primary cleaning water nozzle 12 and the primary cleaning drain F 1 from the slag water cooling tank 6 provided in the molten exhaust gas cooling chamber 5
It is a basic constitution of the invention that the water spray nozzle 18 for cooling the molten exhaust gas for injecting

【0012】また、本願方法発明は、水砕スラグを生成
する廃棄物溶融処理設備に於いて、スラグ水冷槽6から
引上げした水砕スラグD1 に1次洗浄水ノズル8から2
次洗浄排水H1 を噴射することにより前記水砕スラグD
1 を1次洗浄し、次に、前記スラグ水冷槽6から排出し
た水砕スラグD1 をスラグ水洗槽9内へ受け入れると共
に、スラグ水洗槽9から引上げした水砕スラグD2 に2
次洗浄ノズル11から清水Eを噴射し、水砕スラグD2
を清水Eにより対向流的に2次洗浄することを発明の基
本構成とするものである。
Further, the method invention of the present application, in the waste melting treatment facility for producing granulated slag, the granulated slag D 1 pulled up from the slag water cooling tank 6 is connected to the primary washing water nozzles 8 to 2
The granulated slag D is produced by injecting the next cleaning waste water H 1.
1 is first washed, and then the water granulated slag D 1 discharged from the slag water cooling tank 6 is received in the slag water washing tank 9 and the water granulated slag D 2 pulled up from the slag water washing tank 9
Fresh water E is sprayed from the next cleaning nozzle 11 to produce granulated slag D 2
It is the basic constitution of the invention to carry out the secondary washing with fresh water E in a countercurrent manner.

【0013】[0013]

【発明の実施の形態】図1は本発明の実施の形態の一例
を示すものである。図1に於いて1はごみ等の焼却炉、
2は焼却排ガス冷却室、3は焼却灰等の溶融炉、4は空
気予熱器、5は溶融排ガス冷却室、6はスラグ水冷槽、
7はスラグコンベア、8はスラグ1次洗浄水ノズル、9
はスラグ水洗槽、10は水洗コンベア、11はスラグ2
次洗浄水ノズル、12はスラグ2次洗浄排水槽、13は
スラグ1次洗浄水ポンプ、14はスラグ1次洗浄排水沈
澱槽、15はスラグ1次洗浄排水槽、16はスラグ1次
洗浄排水ポンプ、17は焼却排ガス冷却用水噴射ノズ
ル、18は溶融排ガス冷却用水噴射ノズル、19は汚泥
脱水機である。
FIG. 1 shows an example of an embodiment of the present invention. In FIG. 1, 1 is an incinerator for garbage,
2 is an incinerator exhaust gas cooling chamber, 3 is a melting furnace for incinerated ash, 4 is an air preheater, 5 is a molten exhaust gas cooling chamber, 6 is a slag water cooling tank,
7 is a slag conveyor, 8 is a slag primary cleaning water nozzle, 9
Is a slag washing tank, 10 is a washing conveyor, 11 is a slag 2
Secondary cleaning water nozzle, 12 slag secondary cleaning drainage tank, 13 slag primary cleaning drainage pump, 14 slag primary cleaning drainage settling tank, 15 slag primary cleaning drainage tank, 16 slag primary cleaning drainage pump Reference numeral 17 is a water injection nozzle for cooling incineration exhaust gas, 18 is a water injection nozzle for cooling molten exhaust gas, and 19 is a sludge dehydrator.

【0014】図1を参照して、ごみ焼却炉1内へ供給さ
れたごみAはここで焼却され、その排ガスは排ガス冷却
室2、廃棄回収ボイラ、排ガス処理装置、煙突(図示省
略)等を経て大気中へ放出されて行く。一方、焼却炉1
からの焼却灰(燃焼残査)Bは溶融炉内へ順次送られ、
ここで加熱溶融される。また、溶融炉3からの排ガスは
空気予熱器4、排ガス冷却室5、排ガス処理装置、煙突
(図示省略)等を経て大気中へ放出されて行く。
Referring to FIG. 1, the waste A supplied into the waste incinerator 1 is incinerated here, and its exhaust gas is discharged to an exhaust gas cooling chamber 2, a waste recovery boiler, an exhaust gas treatment device, a chimney (not shown), etc. After that, it is released into the atmosphere. On the other hand, incinerator 1
Incineration ash (combustion residue) B from the
It is heated and melted here. Further, the exhaust gas from the melting furnace 3 is discharged into the atmosphere through the air preheater 4, the exhaust gas cooling chamber 5, the exhaust gas treatment device, the chimney (not shown) and the like.

【0015】前記溶融炉3中で形成された溶融スラグC
は水を張ったスラグ水冷槽6内へ落口3aを通して落下
され、ここで水砕スラグD1 となったあと、水冷槽6内
に設けたスラグコンベア7によって水面上へ運び上げら
れる。尚、前記水砕スラグD1 の外表面には、水冷槽6
内の重金属で汚染されているスラグ冷却水Fが3〜5w
t%の割合で付着している。そのため、スラグコンベア
7の最上部近傍の水洗スラグD1 が水面上へ露出する位
置に於いて、1次洗浄水ノズル8から吹きつけた水(2
次洗浄排水H1 )によってこれを洗浄し、水砕スラグD
1 の外表面に付着している汚染されたスラグ冷却水Fを
洗い落とす。
Molten slag C formed in the melting furnace 3
Is dropped into the slag water cooling tank 6 filled with water through the outlet 3a, and becomes the granulated slag D 1 here, and is then carried up onto the water surface by the slag conveyor 7 provided in the water cooling tank 6. In addition, a water cooling tank 6 is provided on the outer surface of the granulated slag D 1.
Slag cooling water F contaminated with heavy metals inside is 3-5w
Adhered at a rate of t%. Therefore, at the position where the wash slag D 1 near the top of the slag conveyor 7 is exposed above the water surface, the water (2
This is washed with the next washing wastewater H 1 ) and granulated slag D
The contaminated slag cooling water F adhering to the outer surface of 1 is washed off.

【0016】前記水洗処理により表面に付着したスラグ
冷却水Fの大部分を洗い落とされた水砕スラグD1 は、
引き続きその下方に設けたスラグ水洗槽9内へ投入され
る。当該スラグ水洗槽9は、下部を水槽とし且つその上
方に傾斜した筒状体を設けたものであり、傾斜した筒状
体部分にはスクリューコンベア形式の水洗コンベア10
が配置されている。即ち、スラグ水洗槽9の下部水槽内
へ落下した水砕スラグD1 は、水洗コンベア10によっ
て上方へ運び上げられる間に、スラグ水洗槽9の最上部
に設けられた2次洗浄ノズル11からの新鮮な清水Eに
よって再洗浄され、これによって、前段階の1次洗浄で
残存した表面の付着汚水を完全に洗い流す。この合計2
段の水洗浄処理により、水砕スラグD2 は重金属汚染を
起こすことのない良質なスラグとなり、各種用途に有効
利用することが可能となる。
The granulated slag D 1 obtained by washing off most of the slag cooling water F adhering to the surface by the water washing treatment is
Then, it is thrown into the slag washing tank 9 provided below it. The slag water washing tank 9 has a lower part as a water tank and an inclined cylindrical body is provided above the water tank, and a screw conveyor type washing conveyor 10 is provided in the inclined cylindrical body portion.
Is arranged. That is, the water granulated slag D 1 dropped into the lower water tank of the slag water washing tank 9 is conveyed from the secondary washing nozzle 11 provided at the uppermost portion of the slag water washing tank 9 while being carried upward by the water washing conveyor 10. It is rewashed with fresh fresh water E, which completely rinses off the adhered dirty water on the surface remaining in the primary washing of the previous stage. This total 2
By the step water cleaning treatment, the granulated slag D 2 becomes a high quality slag that does not cause heavy metal contamination and can be effectively used for various purposes.

【0017】スラグ水洗槽9内で水砕スラグD1 の2次
洗浄に使用された2次洗浄水Hは、僅かに重金属で汚染
された付着水を含んだ形でスラグ水洗槽9から2次洗浄
排水槽12へ流下し、ここに貯えられるまた、排水槽1
2内へ貯えられた2次洗浄排水H1 は、1次洗浄水ポン
プ13によって1次洗浄ノズル8へ送られ、スラグ水洗
槽9の最上部から1次洗浄水として下方向へ向けて噴射
される。更に、噴射された1次洗浄水は水砕スラグD1
を洗浄しながらスラグ水冷槽6の下部に溜り、溶融炉3
からの溶融スラグCの冷却水Fとして利用される。
The secondary washing water H used for the secondary washing of the granulated slag D 1 in the slag washing tank 9 contains secondary water from the slag washing tank 9 in a form containing adhering water slightly contaminated with heavy metals. It flows down to the cleaning drainage tank 12 and is stored here.
The secondary cleaning waste water H 1 stored in 2 is sent to the primary cleaning nozzle 8 by the primary cleaning water pump 13 and jetted downward from the top of the slag water cleaning tank 9 as primary cleaning water. It Further, the injected primary cleaning water is granulated slag D 1
The slag water cooling tank 6 accumulates in the lower part of the melting furnace 3 while cleaning
Is used as the cooling water F for the molten slag C.

【0018】前記スラグ水冷槽6中の冷却水Fは、清水
Eを2段階に亘り対向流的に水砕スラグの洗浄に利用し
たあと、溶融スラグCの冷却用としても用いられるの
で、重金属による汚染度が増す。従って、本実施態様で
は2次洗浄水として供給された清水Eと等量の汚染され
たスラグ冷却水Fをスラグ水冷槽6より沈澱槽14に引
抜き、ここで上澄液と沈澱汚泥に分離する構成としてい
る。そして、沈澱槽14内で分離した前記上澄液(1次
洗浄排水)F1 は1次洗浄排水槽15に貯えられたあ
と、焼却排ガス冷却室2及び溶融排ガス冷却室5の冷却
用の噴射水として使用するため、1次洗浄排水ポンプ1
6によって、夫々水噴射ノズル17及び水噴射ノズル1
8へ供給される。また、沈澱槽14の下部に沈殿した汚
泥Jは脱水機19にて脱水したのち、ケーキJ1 は再び
溶融炉3へ投入され、且つ脱離液Kは排水処理(図示省
略)へ送られる。
The cooling water F in the slag water cooling tank 6 is made of heavy metal because it is used for cooling the molten slag C after the fresh water E is countercurrently used for washing the water granulated slag in two steps. The degree of pollution increases. Therefore, in this embodiment, the same amount of contaminated slag cooling water F as the fresh water E supplied as the secondary washing water is drawn from the slag water cooling tank 6 to the settling tank 14, where it is separated into a supernatant and a settling sludge. It is configured. The supernatant liquid (primary washing drainage) F 1 separated in the settling tank 14 is stored in the primary washing drainage tank 15 and then injected for cooling the incineration exhaust gas cooling chamber 2 and the molten exhaust gas cooling chamber 5. Primary wash drain pump 1 for use as water
6, water injection nozzle 17 and water injection nozzle 1 respectively
8 is supplied. The sludge J settled in the lower part of the settling tank 14 is dehydrated by the dehydrator 19, the cake J 1 is fed into the melting furnace 3 again, and the desorbed liquid K is sent to wastewater treatment (not shown).

【0019】尚、従前の溶融炉に於ける水砕スラグの生
成では、スラグ水冷槽6へスラグ冷却水Fを1回充満さ
せると、その後は蒸発による減少分と、汚染度が著しく
高くなった時の入れ替えに必要な量だけを補充すればよ
く、スラグ冷却水Fの必要供給量は比較的少なくてよ
い。これに対して、本発明に於いては、洗浄のために常
時清水Eを供給する必要があるため、スラグ冷却水Fに
限って見ると使用水量は増加する。しかし、従前の溶融
炉では、排ガス冷却室5内への水噴射のために大量の清
水を必要とするのに対して、本発明では前述の通り2次
洗浄水H、1次洗浄水H1及びスラグ冷却水Fとして活
用した後の清水Eを排ガス冷却室5の冷却水として噴射
する構成としているため、水の物質収支が従前の溶融炉
の場合に比して増加することはない。
In the conventional production of water granulated slag in the melting furnace, once the slag cooling water F was filled with the slag cooling water F once, the amount of pollution caused by evaporation and the degree of pollution increased significantly. It is sufficient to replenish only the amount necessary for time replacement, and the required supply amount of the slag cooling water F may be relatively small. On the other hand, in the present invention, since it is necessary to constantly supply the fresh water E for cleaning, the amount of water used increases when it is limited to the slag cooling water F. However, in the conventional melting furnace, a large amount of fresh water is required to inject water into the exhaust gas cooling chamber 5, whereas in the present invention, as described above, the secondary cleaning water H and the primary cleaning water H 1 Also, since the fresh water E that has been used as the slag cooling water F is injected as the cooling water for the exhaust gas cooling chamber 5, the mass balance of water does not increase as compared with the conventional melting furnace.

【0020】[0020]

【表1】 [Table 1]

【0021】表1は、1次洗浄ノズル8及び2次洗浄ノ
ズル11からの噴射を停止した状態で、スラグ水洗槽6
から引上げた水砕スラグ(試料1)(即ち、従前の溶融
炉に於いて生成した水砕スラグ)と、1次洗浄ノズル8
及び2次洗浄ノズル11から水噴射を行なった状態でス
ラグ水洗槽9の上方から取り出した水洗スラグ(試料
2)(即ち、本発明による2段洗浄を施した水砕スラグ
2 )との重金属の溶出試験結果を示すものである。
尚、試料1及び試料2は、夫々溶融量200kg/Hの
溶融炉2に於いて、溶融スラグCの最初の出滓から約1
0時間経過後にスラグコンベア7の上部及び水洗コンベ
ア10の出口に於いて夫々採取した水砕スラグであり、
また重金属類の溶出試験は環境庁告示第46号溶出試験
方法に規定する方法に従って実施したものである。更
に、試料2の採取時に於ける各洗浄ノズル8,11から
の放水量は、1次洗浄ノズル8が20l/mi、2次洗
浄ノズル11が20l/miであり且つ水砕スラグD1
のスラグコンベア37上に於ける平均洗浄時間は約6
分、水砕スラグD2 の水洗コンベア10上に於ける平均
洗浄時間は約3分であった。
Table 1 shows the slag washing tank 6 with the injection from the primary cleaning nozzle 8 and the secondary cleaning nozzle 11 stopped.
Granulated slag (Sample 1) pulled up from the above (that is, granulated slag produced in the conventional melting furnace) and the primary cleaning nozzle 8
And a heavy metal with the washing slag (Sample 2) (that is, the granulated slag D 2 subjected to the two-stage washing according to the present invention) taken out from above the slag washing tank 9 in a state where water is jetted from the secondary washing nozzle 11. The results of the dissolution test are shown.
Samples 1 and 2 are each about 1 from the first slag of molten slag C in the melting furnace 2 having a melting amount of 200 kg / H.
Granulated slag collected at the upper part of the slag conveyor 7 and the outlet of the water washing conveyor 10 after 0 hours,
The dissolution test for heavy metals was carried out according to the method specified in Environmental Agency Notification No. 46 Dissolution Test Method. Further, the amount of water discharged from each of the cleaning nozzles 8 and 11 when collecting the sample 2 is 20 l / mi for the primary cleaning nozzle 8 and 20 l / mi for the secondary cleaning nozzle 11 and the granulated slag D 1
The average cleaning time on the slag conveyor 37 is about 6
The average washing time of the water granulated slag D 2 on the washing conveyor 10 was about 3 minutes.

【0022】前記表1からも明らかなように、本件装置
発明を用いて生成された水砕スラグD2 (試料2)は、
何れも土壌環境基準に規定する重金属類の溶出値を完全
に下廻っており、極めて安全性に優れたものであること
が判る。また、前記表1の結果から、水砕スラグに付着
する汚染水を清水によって洗浄除去することにより、重
金属類の溶出値は規制値以下に減少し且つ水砕スラグ自
体の内部からの重金属類の溶出が全く無いことが判る。
As is clear from Table 1 above, the granulated slag D 2 (Sample 2) produced by using the present invention is as follows:
All of them are completely below the elution value of heavy metals specified in the soil environmental standards, and it can be seen that they are extremely safe. Further, from the results in Table 1 above, by washing away the contaminated water adhering to the water granulated slag with clean water, the elution value of heavy metals decreases below the regulation value and the heavy metal from the inside of the water granulated slag itself is removed. It can be seen that there is no elution.

【0023】尚、前記図1の実施態様に於いては、焼却
炉1としてストーカ式の焼却炉を採用しているが、焼却
炉そのものの型式は流動床式のものであっても、或いは
ロータリーキルン式のものであってもよい。同様に、溶
融炉3の方も、電気エネルギー式の炉であっても、或い
は化石燃料燃焼式の炉であってもよく、また、焼却と溶
融とが1体化された、例えば乾留熱分解溶融方式であっ
ても良い。更に、被溶融物も、都市ごみや各種産業廃棄
物の燃焼残査のみならず、飛灰や廃棄物それ自体であっ
ても良い。
In the embodiment shown in FIG. 1, a stoker type incinerator is used as the incinerator 1, but the incinerator itself may be a fluidized bed type or a rotary kiln. It may be of the formula. Similarly, the melting furnace 3 may also be an electric energy type furnace or a fossil fuel combustion type furnace, and, for example, dry distillation pyrolysis in which incineration and melting are integrated. A melting method may be used. Further, the material to be melted may be fly ash or the waste itself as well as the combustion residue of municipal waste and various industrial wastes.

【0024】また、前記図1の実施態様では、水砕スラ
グを所謂対向流式で2段階洗浄する方式としているが、
これは、2段階洗浄でもって当初の目的である水砕スラ
グ表面の付着汚染水をほぼ完全に且つ経済的に洗浄する
ことができたためであり、必要に応じて洗浄段階数を増
したり、或は洗浄方式を所謂並行流方式とすることも可
能である。
Further, in the embodiment shown in FIG. 1, the granulated slag is so-called counter-flow type which is cleaned in two stages.
This is because it was possible to almost completely and economically clean the contaminated water adhering to the surface of the granulated slag by the two-step cleaning, and the number of cleaning steps could be increased if necessary. The cleaning method can be a so-called parallel flow method.

【0025】[0025]

【発明の効果】本発明に於いては、スラグ水冷槽6に設
けたスラグコンベア7の末端部に於いて、1次洗浄ノズ
ル8からの噴射水により水冷槽6より引き上げた水砕ス
ラグを1次洗浄し、更に、前記1次洗浄をした水砕スラ
グを水洗コンベア10を備えたスラグ水洗槽9内へ放出
してこれを水洗コンベア10により洗浄すると共に、水
洗コンベア10の末端部に設けた2次洗浄ノズル11か
ら清水を噴射して水洗スラグを2次洗浄する構成として
いる。その結果、水洗スラグの外表面に付着したスラグ
水冷槽6内の重金属汚染水が完全に洗浄除去されること
になり、環境汚染を起生する虞れの全く無いクリーンな
良質の水砕スラグD2 を比較的経済的に生成することが
でき、水砕スラグの有効利用をより一層推進することが
可能となる。
According to the present invention, at the end of the slag conveyor 7 provided in the slag water cooling tank 6, the water granulated slag pulled up from the water cooling tank 6 by the water sprayed from the primary cleaning nozzle 1 Subsequent washing, and further, the granulated slag subjected to the primary washing is discharged into the slag washing tank 9 equipped with the washing conveyor 10 and washed by the washing conveyor 10 and provided at the end of the washing conveyor 10. The secondary cleaning nozzle 11 sprays clean water to secondary clean the cleaning slag. As a result, the heavy metal contaminated water in the slag water cooling tank 6 adhering to the outer surface of the washed slag is completely washed away, and there is absolutely no risk of causing environmental pollution. 2 can be generated relatively economically, and it becomes possible to further promote the effective use of granulated slag.

【0026】また、本発明に於いては、供給した清水E
を二次洗浄水、1次洗浄水及びスラグ冷却水の三回に亘
って使用すると共に、スラグ冷却水の一部をごみ焼却炉
や溶融炉の排ガス冷却室内へ冷却水として噴射する構成
としている。その結果、供給した清水Eはその殆んどが
有効利用されることになり、廃棄物溶融処理設備全体と
しての使用水量の増加を来たすことは全く無い。本発明
は上述の通り、設備全体の運転管理上の経済性を損なう
ことなく、安全で良質の水砕スラグを安定して生成する
ことができるものであり、優れた実用的効用を奏するも
のである。
Further, in the present invention, the supplied fresh water E
Is used for three times as secondary cleaning water, primary cleaning water and slag cooling water, and part of the slag cooling water is injected as cooling water into the exhaust gas cooling chamber of the refuse incinerator or melting furnace. . As a result, most of the supplied fresh water E is effectively used, and there is no increase in the amount of water used as the entire waste melting treatment facility. INDUSTRIAL APPLICABILITY As described above, the present invention is capable of stably producing water granulated slag that is safe and of high quality without impairing the economical efficiency of operation management of the entire facility, and exhibits excellent practical utility. is there.

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

【図1】本発明の実施態様を示すスラグ洗浄装置を備え
た廃棄物溶融処理設備の全体系統図である。
FIG. 1 is an overall system diagram of a waste melting treatment facility equipped with a slag cleaning device showing an embodiment of the present invention.

【図2】従前の溶融炉に於ける水砕スラグの生成を示す
概要説明図である。
FIG. 2 is a schematic explanatory view showing generation of water granulated slag in a conventional melting furnace.

【符号の説明】[Explanation of symbols]

A:ごみ、B:燃焼残査、C:溶融スラグ、D1
3 :水砕スラグ、E:清水、F:スラグ冷却水、
1 :1次洗浄排水、H:2次洗浄水、H1 :1次洗浄
水、J:分離汚泥、J1 :脱水ケーキ、K:脱離液、
1:焼却炉、2:焼却排ガス冷却室、3:溶融炉、3
a:落口、4:空気予熱器、5:溶融排ガス冷却室、
6:スラグ水冷槽、7:スラグコンベア、8:スラグ1
次洗浄水ノズル、9:スラグ水洗槽、10:水洗コンベ
ア、11:スラグ2次洗浄水ノズル、12:スラグ2次
洗浄排水槽、13:スラグ1次洗浄水ポンプ、14:ス
ラグ1次洗浄排水沈澱槽、15:スラグ1次洗浄排水
槽、16:スラグ1次洗浄排水ポンプ、17:焼却排ガ
ス冷却用水噴射ノズル、18:溶融排ガス冷却用水噴霧
ノズル、19:汚泥脱水機。
A: Garbage, B: Combustion residue, C: Molten slag, D 1 ~
D 3 : Granulated slag, E: Fresh water, F: Slag cooling water,
F 1 : primary cleaning waste water, H: secondary cleaning water, H 1 : primary cleaning water, J: separated sludge, J 1 : dehydrated cake, K: desorption liquid,
1: incinerator, 2: incinerator exhaust gas cooling chamber, 3: melting furnace, 3
a: outlet, 4: air preheater, 5: molten exhaust gas cooling chamber,
6: Slag water cooling tank, 7: Slag conveyor, 8: Slag 1
Next washing water nozzle, 9: Slag washing tank, 10: Washing conveyor, 11: Slag secondary washing water nozzle, 12: Slag secondary washing drainage tank, 13: Slag primary washing water pump, 14: Slag primary washing drainage Sedimentation tank, 15: Slag primary cleaning drainage tank, 16: Slag primary cleaning drainage pump, 17: Water injection nozzle for cooling incineration exhaust gas, 18: Water spray nozzle for cooling molten exhaust gas, 19: Sludge dehydrator.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 水砕スラグを生成する廃棄物溶融処理設
備に於いて、溶融スラグ(C)を受け入れるスラグコン
ベア(10)を有するスラグ水冷槽(6)と,前記スラ
グ水冷槽(6)からの水砕スラグ(D1 )を受け入れる
水洗コンベア(10)を有するスラグ水洗槽(9)と,
前記スラグ水洗槽(9)のスラグ出口側近傍に設けら
れ、清水(E)を噴射するスラグ2次洗浄水ノズル(1
1)と,前記スラグ水冷槽(6)のスラグ出口側近傍に
設けられ、前記スラグ水洗槽(9)からの2次洗浄排水
(H1 )を噴射するスラグ1次洗浄水ノズル(12)
と,溶融排ガス冷却室(5)内に設けられ、前記スラグ
水冷槽(6)からの1次洗浄排水(F1 )を噴射する溶
融排ガス冷却用水噴霧ノズル(18)とから構成したこ
とを特徴とするスラグ洗浄装置を備えた廃棄物溶融処理
設備。
1. A slag water cooling tank (6) having a slag conveyor (10) for receiving molten slag (C) in a waste melting treatment facility for producing water granulated slag, and from the slag water cooling tank (6). A slag washing tank (9) having a washing conveyor (10) for receiving the water granulated slag (D 1 ),
A slag secondary washing water nozzle (1) provided near the slag outlet side of the slag washing tank (9) for injecting fresh water (E)
1) and a slag primary cleaning water nozzle (12) which is provided near the slag outlet side of the slag water cooling tank (6) and injects secondary cleaning drainage (H 1 ) from the slag water cleaning tank (9).
And a molten-exhaust gas cooling water spray nozzle (18) which is provided in the molten-exhaust gas cooling chamber (5) and injects the primary cleaning wastewater (F 1 ) from the slag water cooling tank (6). Waste melting treatment equipment equipped with a slag cleaning device.
【請求項2】 廃棄物溶融処理設備を焼却炉(1)及び
溶融炉(3)を備えた構成とすると共に、スラグ水冷槽
(6)から引き抜いた1次洗浄排水(F1 )を沈澱分離
し、その上澄液を排ガス冷却用水として溶融排ガス冷却
用水噴霧ノズル(18)及び焼却炉(1)の焼却排ガス
冷却室(2)の焼却排ガス冷却用水噴霧ノズル(17)
へ供給する構成とした請求項1に記載のスラグ洗浄装置
を備えた廃棄物溶融処理設備。
2. The waste melting treatment facility comprises an incinerator (1) and a melting furnace (3), and the primary washing wastewater (F 1 ) drawn from the slag water cooling tank (6) is precipitated and separated. Then, the supernatant liquid is used as exhaust gas cooling water for melting exhaust gas cooling water spray nozzle (18) and incineration exhaust gas cooling water spray nozzle (17) for incinerator exhaust gas cooling chamber (2) of incinerator (1).
A waste melting treatment facility equipped with the slag cleaning device according to claim 1, which is configured to be supplied to the waste melting treatment facility.
【請求項3】 水砕スラグを生成する廃棄物溶融処理設
備に於いて、スラグ水冷槽(6)から引上げした水砕ス
ラグ(D1 )に1次洗浄水ノズル(8)から1次洗浄水
(H1 )を噴射することにより前記水砕スラグ(D1
を1次洗浄し、次に、前記スラグ水冷槽(6)から排出
した水砕スラグ(D1 )をスラグ水洗槽(9)内へ受け
入れると共に、スラグ水洗槽(9)から引上げした水砕
スラグ(D2 )に2次洗浄ノズル(11)から清水
(E)を噴射し、水砕スラグ(D2)を清水(E)によ
り対向流的に2次洗浄すると共に、スラグ水洗槽(9)
からの排水を前記1次洗浄水(H1 )とするようにした
ことを特徴とする水砕スラグの製造方法。
3. In a waste melting treatment facility for producing granulated slag, the granulated slag (D 1 ) pulled up from the slag water cooling tank (6) is supplied with primary cleaning water from a primary cleaning water nozzle (8). the slag by (H 1) for injecting (D 1)
Washed primary and then the conjunction accepting slag water-cooled tank granulated slag discharged from (6) (D 1) to the slag washing tank (9) in, granulated slag was pulled from the slag washing tank (9) Fresh water (E) is sprayed from ( 2 ) to the secondary cleaning nozzle (11) to carry out secondary cleaning of the granulated slag (D 2 ) with fresh water (E) in a countercurrent manner, and at the same time, a slag washing tank (9)
A method for producing granulated slag, characterized in that the waste water from the water is used as the primary washing water (H 1 ).
【請求項4】 スラグ水冷槽(6)から引き抜いた1次
洗浄排水(F1 )を溶融処理設備を形成する溶融炉
(3)及び又は焼却炉(1)の排ガス冷却用の噴射水と
して利用するようにした請求項3に記載の水砕スラグの
製造方法。
4. The primary cleaning waste water (F 1 ) drawn from the slag water cooling tank (6) is used as injection water for cooling exhaust gas of a melting furnace (3) and / or an incinerator (1) forming a melting treatment facility. The method for producing granulated slag according to claim 3, wherein the method is performed.
JP04778196A 1996-03-05 1996-03-05 Waste melting treatment equipment with slag cleaning device and method for producing granulated slag Expired - Fee Related JP3549135B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Cited By (5)

* Cited by examiner, † Cited by third party
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JP2007120842A (en) * 2005-10-27 2007-05-17 Mitsubishi Heavy Ind Ltd Method and its device for treating ash melting furnace granulation water
JP2009039669A (en) * 2007-08-10 2009-02-26 Hitachi Zosen Corp Settling method and apparatus of slurry, and waste incineration facility
CN112197588A (en) * 2020-10-30 2021-01-08 唐海燕 Environment-friendly garbage recycling device with rolling and purifying mechanism
CN114459248A (en) * 2022-01-18 2022-05-10 安徽华铂再生资源科技有限公司 Slag flushing process special for furnace
CN114953265A (en) * 2022-05-24 2022-08-30 张家港润盛科技材料有限公司 Low-carbon environment-friendly recycled aluminum notebook keyboard frame structure and processing method thereof

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007120842A (en) * 2005-10-27 2007-05-17 Mitsubishi Heavy Ind Ltd Method and its device for treating ash melting furnace granulation water
JP2009039669A (en) * 2007-08-10 2009-02-26 Hitachi Zosen Corp Settling method and apparatus of slurry, and waste incineration facility
CN112197588A (en) * 2020-10-30 2021-01-08 唐海燕 Environment-friendly garbage recycling device with rolling and purifying mechanism
CN112197588B (en) * 2020-10-30 2023-04-07 唐海燕 Environment-friendly garbage recycling device with rolling and purifying mechanism
CN114459248A (en) * 2022-01-18 2022-05-10 安徽华铂再生资源科技有限公司 Slag flushing process special for furnace
CN114459248B (en) * 2022-01-18 2023-07-18 安徽华铂再生资源科技有限公司 Slag flushing process special for kiln
CN114953265A (en) * 2022-05-24 2022-08-30 张家港润盛科技材料有限公司 Low-carbon environment-friendly recycled aluminum notebook keyboard frame structure and processing method thereof
CN114953265B (en) * 2022-05-24 2024-05-03 张家港润盛科技材料有限公司 Low-carbon environment-friendly recycled aluminum laptop keyboard frame structure and processing method thereof

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