JPH09324910A - Exhaust gas treatment apparatus for ash fusion furnace - Google Patents
Exhaust gas treatment apparatus for ash fusion furnaceInfo
- Publication number
- JPH09324910A JPH09324910A JP8142631A JP14263196A JPH09324910A JP H09324910 A JPH09324910 A JP H09324910A JP 8142631 A JP8142631 A JP 8142631A JP 14263196 A JP14263196 A JP 14263196A JP H09324910 A JPH09324910 A JP H09324910A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- gas
- ash
- furnace
- molten
- 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
Links
- 230000004927 fusion Effects 0.000 title abstract 3
- 238000010521 absorption reaction Methods 0.000 claims abstract description 27
- 239000000428 dust Substances 0.000 claims abstract description 19
- 239000007788 liquid Substances 0.000 claims abstract description 16
- 239000003595 mist Substances 0.000 claims abstract description 8
- 238000002844 melting Methods 0.000 claims description 36
- 239000000155 melt Substances 0.000 claims description 2
- 229910052751 metal Inorganic materials 0.000 abstract description 15
- 239000002184 metal Substances 0.000 abstract description 15
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 12
- 108060003095 GAS2 Proteins 0.000 abstract description 9
- 229910001385 heavy metal Inorganic materials 0.000 abstract description 7
- 230000005484 gravity Effects 0.000 abstract description 3
- 230000000694 effects Effects 0.000 abstract description 2
- 238000000926 separation method Methods 0.000 abstract 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 44
- 239000007789 gas Substances 0.000 description 28
- 239000002893 slag Substances 0.000 description 18
- 239000011780 sodium chloride Substances 0.000 description 16
- 150000003839 salts Chemical class 0.000 description 14
- VEXZGXHMUGYJMC-UHFFFAOYSA-N HCl Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 11
- 229910002091 carbon monoxide Inorganic materials 0.000 description 11
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 11
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 11
- OKTJSMMVPCPJKN-UHFFFAOYSA-N carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 10
- KEAYESYHFKHZAL-UHFFFAOYSA-N sodium Chemical compound [Na] KEAYESYHFKHZAL-UHFFFAOYSA-N 0.000 description 8
- 239000011734 sodium Substances 0.000 description 8
- 229910052708 sodium Inorganic materials 0.000 description 8
- KZBUYRJDOAKODT-UHFFFAOYSA-N chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 description 7
- QWPPOHNGKGFGJK-UHFFFAOYSA-N Hypochlorous acid Chemical compound ClO QWPPOHNGKGFGJK-UHFFFAOYSA-N 0.000 description 6
- KKCBUQHMOMHUOY-UHFFFAOYSA-N Sodium oxide Chemical compound [O-2].[Na+].[Na+] KKCBUQHMOMHUOY-UHFFFAOYSA-N 0.000 description 6
- 229910052799 carbon Inorganic materials 0.000 description 6
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 6
- 239000001301 oxygen Substances 0.000 description 6
- 229910052760 oxygen Inorganic materials 0.000 description 6
- MYMOFIZGZYHOMD-UHFFFAOYSA-N oxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 6
- 229910001948 sodium oxide Inorganic materials 0.000 description 6
- 150000001447 alkali salts Chemical class 0.000 description 5
- 230000005611 electricity Effects 0.000 description 5
- 238000010438 heat treatment Methods 0.000 description 5
- 229910002804 graphite Inorganic materials 0.000 description 4
- 239000010439 graphite Substances 0.000 description 4
- FAPWRFPIFSIZLT-UHFFFAOYSA-M sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- 238000001914 filtration Methods 0.000 description 3
- 159000000011 group IA salts Chemical class 0.000 description 3
- 229910052742 iron Inorganic materials 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate dianion Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 2
- 238000009835 boiling Methods 0.000 description 2
- 239000011449 brick Substances 0.000 description 2
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium monoxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 2
- 238000004891 communication Methods 0.000 description 2
- 239000004020 conductor Substances 0.000 description 2
- 238000004090 dissolution Methods 0.000 description 2
- 238000005868 electrolysis reaction Methods 0.000 description 2
- 239000000706 filtrate Substances 0.000 description 2
- 238000011017 operating method Methods 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- 239000002956 ash Substances 0.000 description 1
- 238000009933 burial Methods 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- CURLTUGMZLYLDI-UHFFFAOYSA-N carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- VYZAMTAEIAYCRO-UHFFFAOYSA-N chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 1
- 239000000571 coke Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000001784 detoxification Methods 0.000 description 1
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 238000010891 electric arc Methods 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 239000000945 filler Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 230000003100 immobilizing Effects 0.000 description 1
- 239000003350 kerosene Substances 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000006011 modification reaction Methods 0.000 description 1
- 239000010813 municipal solid waste Substances 0.000 description 1
- 230000003472 neutralizing Effects 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000001590 oxidative Effects 0.000 description 1
- 230000000149 penetrating Effects 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000006722 reduction reaction Methods 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 239000010801 sewage sludge Substances 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は都市ごみ焼却炉をは
じめ各種焼却炉から排出される灰を溶融処理する際に発
生する排ガスを無害化すると共に排ガス中に含まれる成
分を再利用しやすい形態にする灰溶融炉の排ガス処理装
置に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention makes harmless the exhaust gas generated when melting ash discharged from various incinerators including municipal waste incinerators and makes it easy to reuse the components contained in the exhaust gas. The present invention relates to an exhaust gas treatment device for an ash melting furnace.
【0002】[0002]
【従来の技術】都市ごみ、下水汚泥等の各種廃棄物は焼
却施設で焼却処理され、生じた焼却灰やばいじんは、従
来埋め立て処分されていた。しかし、埋め立て処分地枯
渇の問題や有害重金属類の溶出による地下水汚染の問題
があるため溶融による減量・減容化と無害化の必要性が
高まってきている。2. Description of the Related Art Various wastes such as municipal solid waste and sewage sludge have been incinerated in an incineration facility, and the resulting incinerated ash and dust have conventionally been disposed of in landfills. However, due to the problem of depletion of landfill sites and the problem of groundwater contamination due to elution of harmful heavy metals, the necessity for weight reduction, volume reduction, and detoxification by melting is increasing.
【0003】このような背景で灰中の残留炭素、コーク
ス、灯油、電力を熱源とした溶融処理方式が提案され、
一部で実処理が行われている。このうち、電力を熱源と
した溶融炉としてプラズマアーク加熱方式と抵抗加熱方
式とがある。プラズマアーク加熱方式の溶融炉は上部炉
蓋を貫通する中空黒鉛電極を設け、その先端を溶融スラ
グ上面近くに位置させ、電極の中空部分にArガスある
いはN2 ガスを上から流し、上部の黒鉛電極と炉底電極
との間に直流通電して、プラズマ化ガス流によりアーク
を継続し、灰を加熱溶融するものである。電極が長寿命
で溶融速度が大きく、炉をコンパクトにできるという特
徴がある反面、溶融に至る前に、焼却灰やばいじんがガ
ス流により飛散し、集塵機に大きな負担がかかるという
問題がある。[0003] Under such a background, a melting treatment method using a residual carbon in ash, coke, kerosene, and electric power as a heat source has been proposed.
Actual processing is performed in part. Among them, there are a plasma arc heating method and a resistance heating method as a melting furnace using electric power as a heat source. The melting furnace of the plasma arc heating system is provided with a hollow graphite electrode penetrating the upper furnace lid, the tip of which is located near the upper surface of the molten slag, and Ar gas or N 2 gas is caused to flow from above into the hollow portion of the electrode. A direct current is applied between the electrode and the bottom electrode of the furnace, and the arc is continued by the flow of the plasmaizing gas to heat and melt the ash. Although the electrodes have a long life and a high melting rate and can make the furnace compact, on the other hand, there is a problem that the incinerated ash and dust are scattered by the gas flow before the melting and the dust collector is heavily burdened.
【0004】抵抗加熱方式の灰溶融炉は溶融スラグ内に
対抗電極を配置し、直流または交流通電による電気抵抗
熱(ジユール熱)により灰を加熱溶融するものであり、
1)熱効率が高い、2)発生ガスが少ない、3)アーク
を生成しないためフリッカが発生しない、4)溶融スラ
グと溶融メタルとを分離した分割出滓ができる、という
特徴がある。In the resistance heating type ash melting furnace, a counter electrode is arranged in the molten slag and the ash is heated and melted by electric resistance heat (juule heat) due to direct current or alternating current.
1) High thermal efficiency, 2) Small amount of generated gas, 3) Flicker does not occur because arc is not generated, and 4) Molten slag and molten metal can be separated and separated separately.
【0005】かかる抵抗加熱方式の灰溶融処理方法とし
て特開平7−77318号に開示されたものがある。図
2は上記公報に開示されたもので灰溶融炉の断面および
前後設備のフローシートを示している。図においてaは
灰溶融炉、bは上部電極、cは炉底電極、dは電源装
置、eは溶融メタル層、fは溶融スラグ層、gは溶融塩
層、hはCOガス燃料炉、iは集塵機、jは集塵ファ
ン、kは煙突、mは電極埋没位置調節器である。上記発
明の特徴はごみ焼却施設より発生する焼却灰、ばいじん
あるいは二者の混合物からなる廃棄物を電気抵抗熱を熱
源として溶融処理する方法であって、上部電極の先端位
置を溶融塩層と溶融メタル層との間の溶融スラグ層中に
位置せしめ炉底電極との間に、直流通電もしくは交流2
相通電により垂直方向に通電することにより溶融塩を電
気分解することなく、溶融スラグ層fの上方に溶融塩層
gを安定的に形成し、有害な塩素ガス、塩化水素ガス等
の発生を防止しようとするものである。As such a resistance heating type ash melting treatment method, there is one disclosed in JP-A-7-77318. FIG. 2 discloses the cross section of the ash melting furnace and the flow sheet of the front and rear equipment as disclosed in the above publication. In the figure, a is an ash melting furnace, b is an upper electrode, c is a bottom electrode, d is a power supply device, e is a molten metal layer, f is a molten slag layer, g is a molten salt layer, h is a CO gas fuel furnace, and i is Is a dust collector, j is a dust collecting fan, k is a chimney, and m is an electrode burial position adjuster. A feature of the above invention is a method of melting incineration ash generated from a refuse incineration facility, waste consisting of dust or a mixture of the two by using electric resistance heat as a heat source, and melting the tip position of the upper electrode with a molten salt layer. It is positioned in the molten slag layer between the metal layer and the furnace bottom electrode, and direct current or alternating current 2
The molten salt layer g is stably formed above the molten slag layer f without electrolyzing the molten salt by energizing in the vertical direction by the phase energization to prevent generation of harmful chlorine gas, hydrogen chloride gas, etc Is what you are trying to do.
【0006】[0006]
【発明が解決しようとする課題】しかし、上述のように
灰溶融炉a内に溶融塩層gを形成させるような操業をす
ると、溶融塩は炉壁材を侵触する性質が極めて強いの
で、侵触を防ぐため高価な炉壁材料を使う必要がある。
また電気の良導性のよい溶融塩が炉壁中に浸透するの
で、短絡事故を起こしやすい。そこで本願出願人は、鋭
意研究の結果、炉底の陰極と炉蓋から挿入された陽極と
の間で通電して、電気抵抗熱により灰を溶融する際に、
食塩(NaCl)などのアルカリ塩を積極的に電気分解
する操業方法を採用することにした。かかる操業方法に
よれば例えば食塩は、塩素ガスと金属ナトリウムに電気
分解する。塩素ガスは水蒸気と反応して塩化水素と次亜
塩素酸になるが、次亜塩素酸は酸素を放出して塩化水素
になる。また金属ナトリウムは蒸発し酸化雰囲気中で酸
化ナトリウムとなる。そしてこれらの物質はすべて排ガ
ス中に含まれて、外部に放出される。なお、ナトリウム
は一部溶融メタル層eに残こる。However, when the operation for forming the molten salt layer g in the ash melting furnace a is carried out as described above, the molten salt has a very strong property of corroding the furnace wall material, so To prevent this, it is necessary to use expensive furnace wall material.
In addition, the molten salt, which has a good electric conductivity, penetrates into the furnace wall, which is likely to cause a short circuit accident. Therefore, the applicant of the present application, as a result of diligent research, energized between the cathode of the furnace bottom and the anode inserted from the furnace lid, when melting the ash by electric resistance heat,
We decided to adopt an operating method that positively electrolyzes alkaline salts such as sodium chloride (NaCl). According to this operating method, for example, salt is electrolyzed into chlorine gas and metallic sodium. Chlorine gas reacts with water vapor to become hydrogen chloride and hypochlorous acid, but hypochlorous acid releases oxygen to hydrogen chloride. Further, metallic sodium is evaporated and becomes sodium oxide in the oxidizing atmosphere. And all of these substances are contained in the exhaust gas and released to the outside. In addition, a part of sodium remains in the molten metal layer e.
【0007】しかし、これらの物質を含む排ガスを図2
に示すように乾式処理すると、これらの物質は吸湿性が
強く、吸湿するとバグフィルタや電気集塵機などの集塵
機iまたは途中の配管やダクトにダストと共に付着し、
払い落としが困難で目詰まりや性能劣化を起こしやす
い。また、塩化水素は乾式処理が困難である。However, the exhaust gas containing these substances is shown in FIG.
When the dry treatment is performed as shown in Fig. 2, these substances have strong hygroscopicity, and when they absorb moisture, they adhere to dust collectors i such as bag filters and electric dust collectors, or pipes and ducts in the middle, together with dust,
It is difficult to wipe off and it is easy to cause clogging and performance deterioration. Further, hydrogen chloride is difficult to dry process.
【0008】本発明は上述した問題点に鑑み案出された
もので、溶融塩の分解物質を含む排ガスを、目詰まりを
起こさずに安定的に処理すると共に有害な重金属を処理
しやすい形で取り出すことのできる灰溶融炉の排ガス処
理装置を提供することを目的とする。The present invention has been devised in view of the above-mentioned problems, and it is possible to stably treat exhaust gas containing a decomposed substance of a molten salt without causing clogging and to easily treat harmful heavy metals. An object is to provide an exhaust gas treatment device for an ash melting furnace that can be taken out.
【0009】[0009]
【課題を解決するための手段】上記目的を達成するため
本発明の灰溶融炉の排ガス処理装置は炉底に設けた陰極
と、炉蓋を貫通して挿入した陽極との間で通電し、電気
抵抗熱により灰を溶融する灰溶融炉から発生する排ガス
を導いて、吸収液にダストおよび可溶性成分を吸収させ
るガス吸収塔と、ガス吸収塔からの排ガスをミストセパ
レータを介して導き排ガス中のCOガスを燃焼させるC
O燃焼器とを有する。In order to achieve the above object, an exhaust gas treating apparatus for an ash melting furnace according to the present invention is energized between a cathode provided on a furnace bottom and an anode inserted through a furnace lid, Guide the exhaust gas generated from the ash melting furnace that melts ash by electric resistance heat, and the gas absorption tower that absorbs dust and soluble components in the absorbing liquid, and guide the exhaust gas from the gas absorption tower through the mist separator C that burns CO gas
O combustor.
【0010】次に本発明の作用を説明する。灰溶融炉は
直流電流を通電する直流溶融炉で、炉底側が陰極、炉蓋
を貫通して挿入される電極が陽極となっている。陽極と
陰極との間に通電すると発生するジュール熱により灰が
溶融する。なお、灰は固体の状態では電気の不良導体な
ので灰中に鉄などの金属粉を混ぜておき、初期通電す
る。初期通電により灰が溶融し、溶融スラグ層になると
電気の良導体となり、連続溶融が可能となる。灰溶融炉
中では比重差により、下部の鉄などの溶融メタル層と、
上部の溶融スラグ層に分離しており、それぞれ別に排出
する。灰中に含まれる食塩などの塩は溶融中に電気分解
し、陽極側で塩素ガス、陰極側で金属ナトリウムが発生
する。塩素ガスは炉上部のフリーボード中で水蒸気と反
応し、塩化水素と次亜塩素酸になるが、次亜塩素酸は酸
素を放出して塩化水素になる。Next, the operation of the present invention will be described. The ash melting furnace is a direct current melting furnace that applies a direct current, and the bottom side of the furnace is a cathode, and the electrode inserted through the furnace lid is an anode. The ash is melted by Joule heat generated when electricity is applied between the anode and the cathode. Since ash is a poor conductor of electricity when it is in a solid state, metal powder such as iron is mixed in the ash, and initial electricity is applied. When the ash is melted by the initial energization and becomes a molten slag layer, it becomes a good conductor of electricity and continuous melting becomes possible. In the ash melting furnace, due to the difference in specific gravity, the molten metal layer such as iron at the bottom,
Separated into the upper molten slag layer and discharged separately. Salts such as salt contained in the ash are electrolyzed during melting to generate chlorine gas on the anode side and metallic sodium on the cathode side. Chlorine gas reacts with water vapor in the freeboard in the upper part of the furnace to form hydrogen chloride and hypochlorous acid, but hypochlorous acid releases oxygen to hydrogen chloride.
【0011】金属ナトリウムは沸点が低いので直ちに一
部が蒸発し、炉上部のフリーボード中で酸化され酸化ナ
トリウムガスになる。塩化水素や酸化ナトリウムは水に
可溶な可溶性成分である。これらの可溶性成分とダスト
を含む排ガスは灰溶融炉から排出されて、ガス吸収塔に
導入される。なお、ガス吸収塔は上部から吸収液を散水
するスプレイ方式でもよいが、排ガスを吸収液中に潜ら
せるバブル方式でもよい。灰中には未然炭素、炭酸塩と
して含まれる炭素があり、陽極として使用される黒鉛も
炭素である。これらの炭素は、灰溶融炉のフリーボード
中では酸素が不足状態となっているので、燃焼して一酸
化炭素(CO)となる。従ってこれをそのまま外部に排
出させることはできないので、ガス吸収塔を出たガスは
ミストセパレータにより水滴を除去した後、CO燃焼器
により燃焼して炭酸ガスとした後外部に排出する。Since metallic sodium has a low boiling point, a portion thereof is immediately evaporated and oxidized in the freeboard in the upper part of the furnace to become sodium oxide gas. Hydrogen chloride and sodium oxide are soluble components that are soluble in water. Exhaust gas containing these soluble components and dust is discharged from the ash melting furnace and introduced into the gas absorption tower. The gas absorption tower may be of a spray type in which the absorbing liquid is sprinkled from the upper portion, or may be of a bubble type in which the exhaust gas is dipped in the absorbing liquid. There is carbon in the ash and carbon contained as a carbonate, and the graphite used as the anode is also carbon. These carbons are burned to carbon monoxide (CO) because oxygen is insufficient in the freeboard of the ash melting furnace. Therefore, this gas cannot be discharged to the outside as it is, so that the gas discharged from the gas absorption tower is subjected to a mist separator to remove water droplets and then burned by a CO combustor to form carbon dioxide gas, and then discharged to the outside.
【0012】このように排ガスを湿式処理するようにし
たので、排ガス中にアルカリ塩が電気分解した可溶性の
成分が含まれていても、排ガス処理装置の目詰まりを起
こすことがなくて、安定的な操業が可能である。Since the exhaust gas is wet-processed as described above, even if the exhaust gas contains a soluble component obtained by electrolyzing an alkali salt, the exhaust gas processing device is not clogged and is stable. Various operations are possible.
【0013】[0013]
【発明の実施の形態】以下本発明の1実施形態につい
て、図面を参照しつつ説明する。図1は本発明の灰溶融
炉の排ガス処理装置のフローシートである。図におい
て、1は直流式の灰溶融炉で炉底に陰極1a,炉蓋1i
を貫通して陽極1bがそれぞれ設けられている。なお、
陰極1aは導電性の煉瓦、陽極1bは黒鉛がそれぞれ用
いられている。1fは直流電源装置である。灰1jは炉
蓋1iを通して投入される。灰溶融炉1内では陽極1b
と陰極1a間で通電することにより電気抵抗熱(ジュー
ル熱)が発生し灰1jが溶融する。溶融した灰1jは比
重差により上部の溶融スラグ層1dと下部の溶融メタル
層1cに分離し、溶融スラグ層1dの上部には未溶融の
灰1jが浮遊した状態の灰カバー層1eが生じる。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS One embodiment of the present invention will be described below with reference to the drawings. FIG. 1 is a flow sheet of an exhaust gas treating apparatus for an ash melting furnace of the present invention. In the figure, 1 is a direct current type ash melting furnace, a cathode 1a and a furnace lid 1i on the furnace bottom.
Anodes 1b are respectively provided so as to penetrate through. In addition,
The cathode 1a is made of a conductive brick, and the anode 1b is made of graphite. 1f is a DC power supply device. The ash 1j is thrown in through the furnace lid 1i. In the ash melting furnace 1, the anode 1b
When electricity is applied between the cathode 1a and the cathode 1a, electric resistance heat (Joule heat) is generated and the ash 1j is melted. The molten ash 1j is separated into an upper molten slag layer 1d and a lower molten metal layer 1c due to a difference in specific gravity, and an ash cover layer 1e in which unmelted ash 1j is suspended is formed on the molten slag layer 1d.
【0014】陽極1bと陰極1aとの間に印加される電
圧は70〜80Vであり、溶融スラグ層1d内の温度は
1100°〜1200°Cに制御されている。溶融スラ
グ層1dの抵抗率ρ(Ω・cm)はρ=0.1〜0.5
であるのに対し、溶融メタル層1cの抵抗率はρ=10
-6〜10-8なのでジュール熱はほとんど全て溶融スラグ
層1d内で発生する。従って溶融メタル層1cは、上部
の表面のみが溶融した状態であり、内部は固体となって
おり、全体が陰極の役割をする。灰1j中に含まれる食
塩などのアルカリ塩は、溶融スラグ層内で電気分解さ
れ、アルカリ塩が食塩である場合には塩素ガスと金属ナ
トリウムになる。塩素ガスは陽極1b側で発生するが、
フリーボード1k中で水蒸気と反応し、塩化水素と次亜
塩素酸になる。次亜塩素酸は酸素を放出して塩化水素に
なる。金属ナトリウムは陰極側に発生するが陰極は沸点
(880°C)以上の温度となっているので一部は直ち
に蒸発する。蒸発した金属ナトリウムガスはフリーボー
ド1k中で酸素と反応し酸化ナトリウムになる。The voltage applied between the anode 1b and the cathode 1a is 70 to 80V, and the temperature in the molten slag layer 1d is controlled to 1100 to 1200 ° C. The resistivity ρ (Ω · cm) of the molten slag layer 1d is ρ = 0.1 to 0.5
On the other hand, the resistivity of the molten metal layer 1c is ρ = 10
Since it is -6 to 10 -8, almost all Joule heat is generated in the molten slag layer 1d. Therefore, in the molten metal layer 1c, only the upper surface is molten, the inside is solid, and the whole functions as a cathode. Alkaline salt such as salt contained in the ash 1j is electrolyzed in the molten slag layer, and becomes chlorine gas and metallic sodium when the alkali salt is salt. Chlorine gas is generated on the anode 1b side,
Reacts with water vapor in the freeboard 1k to form hydrogen chloride and hypochlorous acid. Hypochlorous acid releases oxygen to hydrogen chloride. Metallic sodium is generated on the cathode side, but since the cathode has a temperature above the boiling point (880 ° C.), part of it is immediately evaporated. The evaporated metallic sodium gas reacts with oxygen in the freeboard 1k to become sodium oxide.
【0015】2は排ガスであり、炉蓋1iに設けられた
排出口に接続された連絡配管13を通って炉外に排出さ
れる。排ガス2の中には上述の塩化水素や酸化ナトリウ
ムなどの水に可溶性の成分の外、ダストやCOガスが含
まれる。灰中に含まれる未燃炭素、陽極1bとして使用
される黒鉛棒、灰1j中に炭酸塩として存在する炭素な
どが、炉内では酸素不足状態なのでCOガスとなる。1
gは溶融スラグであり、1hは溶融メタルである。溶融
スラグの主成分はけい砂および酸化カルシウムであり、
溶融メタルの主成分は鉄である。溶融スラグは間歇的又
は連続的に排出される。溶融メタルは溶融スラグ排出
後、陽極1bと溶融メタル層1cとの間にアーク放電を
発生させ、メタルを溶融させて排出する。Reference numeral 2 denotes exhaust gas, which is discharged to the outside of the furnace through a connecting pipe 13 connected to a discharge port provided in the furnace lid 1i. The exhaust gas 2 contains dust and CO gas in addition to the above-described water-soluble components such as hydrogen chloride and sodium oxide. The unburned carbon contained in the ash, the graphite rod used as the anode 1b, the carbon present as the carbonate in the ash 1j, and the like become CO gas because oxygen is insufficient in the furnace. 1
g is molten slag, and 1h is molten metal. The main components of molten slag are silica sand and calcium oxide,
The main component of molten metal is iron. The molten slag is discharged intermittently or continuously. After the molten metal is discharged from the molten slag, arc discharge is generated between the anode 1b and the molten metal layer 1c to melt and discharge the metal.
【0016】3はガス吸収塔である。本実施形態ではス
プレイ式のものとして説明するが、吸収液中に排ガスを
潜らせるバブル式でもよい。排ガス2はガス吸収塔3下
方に設けられたガス入口3aから塔内に入り、上方に設
けられたガス出口3bから排出される。3cは吸収液を
噴出させるノズルである。吸収液は細かい水滴となって
塔内を下降するのに対し、排ガス2が塔内を上昇し、吸
収液の中にダストと共に可溶性成分が吸収される。排ガ
ス2はガス吸収塔3から連絡配管14を介してミストセ
パレータ4に導かれる。ミストセパレータ4内には邪魔
板や充填物などが設けられており、排ガス2をこれらに
衝突させて、水滴を分離する。ミストセパレータ4を出
た排ガス2は連絡配管15を経てCO燃焼器5に流入す
る。CO燃焼器は酸化触媒を担持したものやパイロット
バーナを有し、直接燃焼させるものなどがある。6は吸
引ファンであり連絡配管16を介してCO燃焼器に接続
されている。7は煙突である。Reference numeral 3 is a gas absorption tower. In this embodiment, the spray type is described, but a bubble type in which the exhaust gas is submerged in the absorbing liquid may be used. The exhaust gas 2 enters the tower through a gas inlet 3a provided below the gas absorption tower 3, and is discharged from a gas outlet 3b provided above. 3c is a nozzle for ejecting the absorbing liquid. The absorbing liquid becomes fine water droplets and descends in the tower, whereas the exhaust gas 2 rises in the tower and the soluble component is absorbed in the absorbing liquid together with dust. The exhaust gas 2 is guided from the gas absorption tower 3 to the mist separator 4 via the communication pipe 14. A baffle plate, a filler, and the like are provided in the mist separator 4, and the exhaust gas 2 is caused to collide with these to separate water droplets. The exhaust gas 2 exiting from the mist separator 4 flows into the CO combustor 5 via the connecting pipe 15. CO burners include those that carry an oxidation catalyst and those that have a pilot burner and burn directly. Reference numeral 6 denotes a suction fan, which is connected to the CO combustor via a communication pipe 16. 7 is a chimney.
【0017】8はガス吸収塔3からの吸収液を受け入れ
る吸収液タンクである。吸収液タンク8から吸収液の一
部は循環ポンプ9を経て吸収塔に循環し、残りは溶解槽
10に送られる。なお、17はメークアプ用の水であ
る。溶解槽10を出た吸収液は濾過槽11に送られ、こ
こで分離されてスラッジ18は灰溶融炉1に再び送ら
れ、濾液19は水処理装置12に送られる。水処理装置
は反応槽、濾過槽、沈殿槽などを有し、濾過槽11から
排出される吸収濾液19の中和や溶解している重金属
(鉛、亜鉛、水銀、クロームなど)の固定化を行う。Reference numeral 8 is an absorption liquid tank for receiving the absorption liquid from the gas absorption tower 3. A part of the absorption liquid from the absorption liquid tank 8 is circulated to the absorption tower via the circulation pump 9, and the rest is sent to the dissolution tank 10. In addition, 17 is water for make-up. The absorption liquid that has left the dissolution tank 10 is sent to the filtration tank 11, where it is separated, the sludge 18 is sent again to the ash melting furnace 1, and the filtrate 19 is sent to the water treatment device 12. The water treatment device has a reaction tank, a filtration tank, a precipitation tank, etc., and is used for neutralizing the absorption filtrate 19 discharged from the filtration tank 11 and immobilizing dissolved heavy metals (lead, zinc, mercury, chrome, etc.). To do.
【0018】次に本実施形態の作用を説明する。以上説
明したようにアルカリ塩の電気分解により生じた塩化水
素や酸化ナトリウムなどの可溶性の成分は排ガス2中に
ダストと共に含まれて炉外に排出される。ダストや可溶
性成分、さらに蒸発した重金属はすべて吸収塔で吸収液
中に吸収される。従って排ガスの乾式処理で起こるよう
な集塵機の目詰まりや性能の劣化は起こらず、安定した
操業が可能である。さらに重金属も吸収液に溶解してい
るので、不溶化して埋立処理するにしても、抽出して有
効利用するにしても取り扱いが容易となる。Next, the operation of this embodiment will be described. As described above, the soluble components such as hydrogen chloride and sodium oxide generated by the electrolysis of the alkali salt are included in the exhaust gas 2 together with the dust and are discharged out of the furnace. Dust, soluble components, and evaporated heavy metals are all absorbed in the absorption liquid in the absorption tower. Therefore, the dust collector is not clogged and the performance is not deteriorated as in the dry treatment of exhaust gas, and stable operation is possible. Further, since the heavy metal is also dissolved in the absorbing solution, it is easy to handle even if it is insolubilized for landfill treatment or extracted for effective use.
【0019】本発明は以上述べた実施形態に限られるも
のではなく、発明の要旨を逸脱しない範囲で種々の変更
が可能である。The present invention is not limited to the embodiments described above, and various modifications can be made without departing from the spirit of the invention.
【0020】[0020]
【発明の効果】以上述べたように本発明は灰溶融炉でア
ルカリ塩の電気分解を積極的に行って、排ガス中にアル
カリ塩の電気分解により発生する可溶性成分を含有さ
せ、その排ガスを湿式で処理するようにしたので、 (1)排ガスを乾式で処理する場合に比べて、目詰まり
などのトラブルが起きない。As described above, the present invention positively electrolyzes an alkali salt in an ash melting furnace so that the exhaust gas contains a soluble component generated by the electrolysis of the alkali salt, and the exhaust gas is wetted. Since (1) exhaust gas is processed dry, troubles such as clogging do not occur.
【0021】(2)アルカリ塩を積極的に電気分解する
ので、炉内には溶融塩層が存在せず、炉壁の煉互の材質
は特殊で高価なものを使用しなくてもよく、安価にな
る。 (3)排ガス中に含まれる重金属のガスは処理水に溶解
するので、不溶化して埋立処理するにしても、抽出して
再資源化するにしても、取り扱いが容易となる。(2) Since the alkaline salt is positively electrolyzed, there is no molten salt layer in the furnace, and it is not necessary to use a special and expensive material for the brick of the furnace wall. It will be cheaper. (3) Since the heavy metal gas contained in the exhaust gas is dissolved in the treated water, it is easy to handle whether insolubilized and landfilled or extracted and recycled.
【0022】などの優れた効果を有する。It has excellent effects such as
【図1】本実施例の灰溶融炉の排ガス処理装置の全体フ
ローシートである。FIG. 1 is an overall flow sheet of an exhaust gas treating apparatus for an ash melting furnace of this example.
【図2】従来の灰溶融炉および排ガス処理装置のフロー
シートである。FIG. 2 is a flow sheet of a conventional ash melting furnace and an exhaust gas treatment device.
1 灰溶融炉 1a 陰極 1b 陽極 2 排ガス 3 ガス吸収塔 4 ミストセパレータ 5 CO燃焼器 1 Ash melting furnace 1a Cathode 1b Anode 2 Exhaust gas 3 Gas absorption tower 4 Mist separator 5 CO combustor
───────────────────────────────────────────────────── フロントページの続き (72)発明者 松澤 克明 神奈川県横浜市磯子区新中原町1番地 石 川島播磨重工業株式会社技術研究所内 (72)発明者 安田 直明 東京都江東区豊洲二丁目1番1号 石川島 播磨重工業株式会社東京第一工場内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Katsuaki Matsuzawa 1 Shinshinarahara-cho, Isogo-ku, Yokohama-shi, Kanagawa Ishi Kawashima Harima Heavy Industries Co., Ltd. Technical Research Institute (72) Inventor Naoaki Yasuda 2-1-1 Toyosu, Koto-ku, Tokyo No. 1 Ishikawajima Harima Heavy Industries Ltd. Tokyo No. 1 factory
Claims (1)
入した陽極との間で通電し、電気抵抗熱により灰を溶融
する灰溶融炉から発生する排ガスを導いて、吸収液にダ
ストおよび可溶性成分を吸収させるガス吸収塔と、ガス
吸収塔からの排ガスをミストセパレータを介して導き排
ガス中のCOガスを燃焼させるCO燃焼器とを有するこ
とを特徴とする灰溶融炉の排ガス処理装置。1. An absorbing liquid is introduced by conducting an electric current between a cathode provided on the bottom of a furnace and an anode inserted through a furnace lid to guide exhaust gas generated from an ash melting furnace that melts ash by electric resistance heat. Gas absorption tower for absorbing dust and soluble components, and a CO combustor for guiding the exhaust gas from the gas absorption tower through a mist separator to burn the CO gas in the exhaust gas, the exhaust gas of an ash melting furnace Processing equipment.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP14263196A JP3567614B2 (en) | 1996-06-05 | 1996-06-05 | Exhaust gas treatment equipment for ash melting furnace |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP14263196A JP3567614B2 (en) | 1996-06-05 | 1996-06-05 | Exhaust gas treatment equipment for ash melting furnace |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH09324910A true JPH09324910A (en) | 1997-12-16 |
JP3567614B2 JP3567614B2 (en) | 2004-09-22 |
Family
ID=15319845
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JP14263196A Expired - Fee Related JP3567614B2 (en) | 1996-06-05 | 1996-06-05 | Exhaust gas treatment equipment for ash melting furnace |
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JP (1) | JP3567614B2 (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006023052A (en) * | 2004-07-09 | 2006-01-26 | Takuma Co Ltd | Exhaust gas processing method for ash melting furnace, and processing facility therefor |
JP2019515242A (en) * | 2016-05-12 | 2019-06-06 | ダニエリ コルス ベスローテン フェノーツハップDanieli Corus B.V. | Furnace plant and process for furnace gas processing |
-
1996
- 1996-06-05 JP JP14263196A patent/JP3567614B2/en not_active Expired - Fee Related
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006023052A (en) * | 2004-07-09 | 2006-01-26 | Takuma Co Ltd | Exhaust gas processing method for ash melting furnace, and processing facility therefor |
JP2019515242A (en) * | 2016-05-12 | 2019-06-06 | ダニエリ コルス ベスローテン フェノーツハップDanieli Corus B.V. | Furnace plant and process for furnace gas processing |
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