JPS5843332B2 - Oxidation tower for flue gas desulfurization gypsum recovery method - Google Patents
Oxidation tower for flue gas desulfurization gypsum recovery methodInfo
- Publication number
- JPS5843332B2 JPS5843332B2 JP52025100A JP2510077A JPS5843332B2 JP S5843332 B2 JPS5843332 B2 JP S5843332B2 JP 52025100 A JP52025100 A JP 52025100A JP 2510077 A JP2510077 A JP 2510077A JP S5843332 B2 JPS5843332 B2 JP S5843332B2
- Authority
- JP
- Japan
- Prior art keywords
- gypsum
- classification
- oxidation tower
- recovery method
- flue gas
- 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
Links
- 229910052602 gypsum Inorganic materials 0.000 title claims description 51
- 239000010440 gypsum Substances 0.000 title claims description 51
- 238000007254 oxidation reaction Methods 0.000 title claims description 25
- 230000003647 oxidation Effects 0.000 title claims description 24
- 238000000034 method Methods 0.000 title claims description 12
- 238000011084 recovery Methods 0.000 title claims description 12
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims description 10
- 239000003546 flue gas Substances 0.000 title claims description 10
- 238000006477 desulfuration reaction Methods 0.000 title claims description 9
- 230000023556 desulfurization Effects 0.000 title claims description 9
- 239000002002 slurry Substances 0.000 claims description 15
- 235000010261 calcium sulphite Nutrition 0.000 claims description 7
- 230000001590 oxidative effect Effects 0.000 claims description 7
- GBAOBIBJACZTNA-UHFFFAOYSA-L calcium sulfite Chemical compound [Ca+2].[O-]S([O-])=O GBAOBIBJACZTNA-UHFFFAOYSA-L 0.000 claims description 3
- 239000013078 crystal Substances 0.000 description 15
- 239000007789 gas Substances 0.000 description 5
- 239000002245 particle Substances 0.000 description 5
- 229910001868 water Inorganic materials 0.000 description 5
- 239000007788 liquid Substances 0.000 description 4
- 238000010521 absorption reaction Methods 0.000 description 3
- 239000002562 thickening agent Substances 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 2
- 238000002485 combustion reaction Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 229910052925 anhydrite Inorganic materials 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 229910000019 calcium carbonate Inorganic materials 0.000 description 1
- 235000010216 calcium carbonate Nutrition 0.000 description 1
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000000706 filtrate Substances 0.000 description 1
- 238000010304 firing Methods 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000002093 peripheral effect Effects 0.000 description 1
- 238000012805 post-processing Methods 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F11/00—Compounds of calcium, strontium, or barium
- C01F11/46—Sulfates
- C01F11/464—Sulfates of Ca from gases containing sulfur oxides
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F11/00—Compounds of calcium, strontium, or barium
- C01F11/46—Sulfates
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Inorganic Chemistry (AREA)
- Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
- Treating Waste Gases (AREA)
Description
【発明の詳細な説明】
本発明は良質の粗大粒の石膏のみの回収を可能とする排
煙脱硫石膏回収法用酸化塔に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an oxidation tower for a flue gas desulfurization gypsum recovery method that makes it possible to recover only high-quality coarse-grained gypsum.
排煙脱硫石膏回収法はボイラ等の燃焼排ガス中のSO2
ガスを石灰スラリーで吸収除去し、生成した亜硫酸カル
シウム(CaSO3・−!−H20)を酸化塔で空気を
送入して酸化して石膏(CaSO4・2H20)とし、
これを回収するものである。The flue gas desulfurization gypsum recovery method collects SO2 from combustion flue gas from boilers, etc.
The gas is absorbed and removed using lime slurry, and the generated calcium sulfite (CaSO3-!-H20) is oxidized by introducing air into an oxidation tower to form gypsum (CaSO4.2H20).
This is what is collected.
その反応は次の如くである。The reaction is as follows.
CaCO3+5O2−+CaSO3・−H2O・・・・
・・・・・SO2吸収1 l 2
CaS03−−H3O+−i:02→CaSO4”2H
20・・−・・−酸化この石膏回収法で得られる石膏の
粒径が小さいと、あと処理のシックナーや遠心分離機で
の水切れが悪く、従って付着水分が多くなる。CaCO3+5O2-+CaSO3・-H2O・・・・
...SO2 absorption 1 l 2 CaS03--H3O+-i:02→CaSO4"2H
20.--Oxidation If the particle size of the gypsum obtained by this gypsum recovery method is small, it is difficult to remove water in a post-processing thickener or centrifugal separator, and therefore, a large amount of moisture adheres to the gypsum.
付着水分が多くなると、石膏はべとついて運搬などを困
難とするばかりでなく、セメントとの混合、ボードの製
作時などにおいて熱量を余計に必要とし、熱経済上不利
であり、かつセメント、ボードなどの品質を低下させる
ので、使用に不適であり、また焼成時に固化することも
ある。If there is a lot of moisture attached, gypsum not only becomes sticky and difficult to transport, but also requires extra heat when mixing with cement and manufacturing boards, which is disadvantageous in terms of thermoeconomics. It is unsuitable for use because it deteriorates the quality of other materials, and it may solidify during firing.
従って、石膏回収法においては酸化塔で石膏粒径を大き
くし良質化する必要がある。Therefore, in the gypsum recovery method, it is necessary to increase the gypsum particle size and improve the quality using an oxidation tower.
しかしながら、従来の石膏回収法で使用している酸化塔
ではCaSO3・−HH2Oの酸化のみを行ない、結晶
粒径の大きい石膏を選択的に取り出すことは考えられて
いなかった。However, the oxidation tower used in the conventional gypsum recovery method only oxidizes CaSO3.--HH2O, and it has not been considered to selectively extract gypsum with large crystal grain sizes.
また従来の吸収塔での酸化率の犬なるときには石膏の結
晶粒が大きくできず、問題があった。Furthermore, when the oxidation rate in conventional absorption towers is low, the crystal grains of gypsum cannot be made large, which poses a problem.
本発明は上記の従来装置の欠点を解決し、良質の粗大粒
の石膏のみの回収を可能とする排煙脱硫石膏回収法酸化
塔を提供するもので、その要旨とするところは、亜硫酸
カルシウムを空気酸化して石膏とする排煙脱硫石膏回収
法用酸化塔において、酸化塔本体底部の周辺部に複数個
の酸化空気用気泡分散器を配設するとともに該底部中央
に設けた分級胴体内に分級用空気分散器を取り付け、か
つ該分級胴体内に石膏スラリー出口を設けたことを特徴
とする排煙脱硫石膏回収法用酸化塔、にある。The present invention solves the drawbacks of the conventional equipment described above and provides an oxidation tower for the flue gas desulfurization gypsum recovery method that makes it possible to recover only high-quality coarse-grained gypsum. In an oxidation tower for the flue gas desulfurization gypsum recovery method that oxidizes air to produce gypsum, a plurality of bubble dispersers for oxidizing air are arranged around the bottom of the oxidation tower main body, and a plurality of bubble dispersers for oxidizing air are installed in the classification body provided at the center of the bottom. An oxidation tower for flue gas desulfurization gypsum recovery method, characterized in that an air disperser for classification is attached and a gypsum slurry outlet is provided in the classification body.
次に、本発明を図面によって説明する。Next, the present invention will be explained with reference to the drawings.
第1図は本発明の一実施例の全体図、第2図は第1図の
実施例の要部詳細図、第3図aは第1図の実施例に使用
する気泡分散器の一例の縦断面図、同じくbはaのA−
A矢視図である。Fig. 1 is an overall view of an embodiment of the present invention, Fig. 2 is a detailed view of the main parts of the embodiment of Fig. 1, and Fig. 3a is an example of a bubble disperser used in the embodiment of Fig. 1. Longitudinal cross-sectional view, b is A- of a
It is a view from arrow A.
第1図および第2図において、本実施例は酸化塔本体1
底部の周辺部に複数個の酸化空気用気泡分散器15を配
設するとともに底部中央に設けた分級胴体17内に分級
用気泡分散器14を取り付けかつ分級胴体17内に石膏
スラリー出口3を設けた構成である。1 and 2, this embodiment shows the oxidation tower main body 1
A plurality of bubble dispersers 15 for oxidizing air are arranged around the bottom, and a bubble disperser 14 for classification is installed in the classification body 17 provided at the center of the bottom, and a gypsum slurry outlet 3 is provided in the classification body 17. The configuration is as follows.
この構成において、亜硫酸カルシウム(以下、Ca S
Osで示す)スラリー液人口2から酸化塔本体1内に
供給されたCaS Osスラリーは空気入口管16を通
り酸化空気用気泡分散器15から噴出される微細気泡に
よって酸化されて石膏となるのであるが、その際搭底部
中央に設けた分級胴体17と分級用気泡分散器14から
の微細気泡の上昇流に打ち勝って粗大結晶の石膏のみが
沈降し、この沈降した粗大結晶の石膏を分級胴体17内
に設けた石膏スラリー出口3から抜き出すのである。In this configuration, calcium sulfite (hereinafter, CaS
The CaS Os slurry supplied into the oxidation tower main body 1 from the slurry liquid population 2 (indicated by Os) passes through the air inlet pipe 16 and is oxidized by fine bubbles ejected from the oxidation air bubble disperser 15 to become gypsum. However, at this time, only the coarse crystal gypsum settles out by overcoming the upward flow of fine bubbles from the classification body 17 and the classification bubble disperser 14 provided at the center of the bottom of the tower, and the settled coarse crystal gypsum is transferred to the classification body 17. The gypsum slurry is extracted from the gypsum slurry outlet 3 provided inside.
すなわち、分級胴体17と分級用気泡分散器14からの
静かな微細気泡の上昇流によって石膏結晶粒の分級を可
能とするものである。That is, the gypsum crystal grains can be classified by the quiet upward flow of fine bubbles from the classification body 17 and the classification bubble disperser 14.
分級用気泡分散器14からの気泡は量的に少なく、酸化
効果は期待しないよう設計しており、従って送入空気量
は任意に調節でき、取り出すべき石膏結晶の状況に応じ
て適宜加減すればよい。The air bubbles from the air bubble disperser 14 for classification are small in quantity, and the design is such that no oxidation effect is expected.Therefore, the amount of air fed can be adjusted arbitrarily, and it can be adjusted as appropriate depending on the situation of the gypsum crystals to be taken out. good.
一方、酸化空気用気泡分散器15からの送入空気量は大
量であり、その微細気泡の上昇に伴い塔内の周辺部に上
昇流が起こると共に塔中央部では下降流が起こって塔内
に規則的な対流が発生する。On the other hand, the amount of air fed from the oxidizing air bubble disperser 15 is large, and as the fine bubbles rise, an upward flow occurs in the periphery of the column, and a downward flow occurs in the center of the column. Regular convection occurs.
その際、塔中央の分級用気泡分散器14からの空気は少
量であるのであまり抵抗にはならない。At this time, since the air from the classification bubble disperser 14 in the center of the column is small, it does not provide much resistance.
このように、酸化塔本体1内でCaSO3の空気酸化に
より生成した石膏結晶は、前述したように、塔周辺部の
酸化空気用気泡分散器15からの微細気泡の上昇流にの
って塔内を循環しつつ次第に成長してゆくが、そのうち
結晶粒の粗大化した石膏のみが分級用気泡分散器14か
らの微細気泡の上昇流に打ち勝って分級胴体17内に沈
降するので、同一酸化塔内で酸化、結晶粗大化、分級が
行なわれ、それによって良質の粗大粒の石膏のみを取り
出すことを可能とするものである。As described above, the gypsum crystals generated by air oxidation of CaSO3 in the oxidation tower main body 1 are carried inside the tower by the upward flow of fine bubbles from the oxidation air bubble disperser 15 in the peripheral area of the tower. However, only the gypsum with coarse crystal grains overcomes the upward flow of fine bubbles from the classification bubble disperser 14 and settles into the classification body 17. Oxidation, crystal coarsening, and classification are performed in the gypsum, which makes it possible to extract only high-quality, coarse-grained gypsum.
従って、従来例に見られるごとき石膏粒のポンプ羽根な
どによる破砕が起らない。Therefore, the gypsum particles are not crushed by the pump blades as seen in the conventional example.
石膏スラリー出口3から抜き出された粗大粒の石膏は次
いでシックナー11に導入され、さらに分級して所要粒
度の石膏結晶とするのであるが、その際該抜出量が多い
、ときは石膏スラリー循環配管弁4を調節してその一部
を酸化塔本体1に戻すこともできる。The coarse-grained gypsum extracted from the gypsum slurry outlet 3 is then introduced into the thickener 11, where it is further classified into gypsum crystals of the required particle size. At this time, if the amount extracted is large, the gypsum slurry is circulated. It is also possible to return a portion of it to the oxidation tower main body 1 by adjusting the piping valve 4 .
上記酸化空気用気泡分散器15と分級用気泡分散器14
は構造的に全く同一のものでもよく、従ってコストアッ
プにはならない。The oxidizing air bubble disperser 15 and the classification bubble disperser 14
may be structurally identical, so there will be no cost increase.
構造としては、たとえば第3図a、bに示すごときもの
でよい。The structure may be as shown in FIGS. 3a and 3b, for example.
この気泡分散器はすでに特願昭47−73569号明細
書において開示されている。This bubble disperser has already been disclosed in Japanese Patent Application No. 47-73569.
図において、18はローター、19はステーター、21
はロータ−18上部に放射状に取り付けた突起棒である
。In the figure, 18 is a rotor, 19 is a stator, 21
are protruding rods radially attached to the upper part of the rotor 18.
この構造のものは次の特徴、すなわち
(1)大きな攪拌羽根がないため、液を大きく流動させ
ることなく静かに微細気泡を発生させることができるこ
と、
(2)気体噴出部に析出した結晶による目づまりを起こ
すことがないこと、
を有するため、分級胴体との組合せによって、静かな微
細気泡の上昇流を発生させ、それによって上記の分級を
可能ならしめるものである。This structure has the following characteristics: (1) Since there is no large stirring blade, fine bubbles can be generated quietly without causing large liquid flow; (2) Eyes caused by crystals deposited at the gas jetting part. Because it does not cause clogging, when combined with the classification body, it generates a quiet upward flow of fine bubbles, thereby making the above classification possible.
実験によって、分級胴体内の空塔速度を3crfL/5
ec= 0.03 m/s以下とすると、70μ以上の
粗大化した石膏結晶が沈降し始めることが確認されたの
で、空気流量の加減によって比較的容易に石膏結晶を分
級することができる。Through experiments, the superficial velocity inside the classification fuselage was reduced to 3crfL/5.
It has been confirmed that when ec = 0.03 m/s or less, coarse gypsum crystals of 70 μm or more begin to settle, so the gypsum crystals can be classified relatively easily by adjusting the air flow rate.
本発明は燃焼排ガス中の酸素濃度が高い場合またはSO
2濃度の低い場合のごとく、吸収塔で生成したC aS
Oa・ΣH20の大部分が酸化してしまうようなガス側
条件の悪い場合に特に有効である。The present invention is suitable for cases where the oxygen concentration in the combustion exhaust gas is high or when SO
2 As in the case of low concentration, CaS produced in the absorption tower
This is particularly effective when the gas side conditions are so bad that most of Oa/ΣH20 is oxidized.
それは本発明によれば、残留する僅かなCa S Os
−HH2O分を有効に使って良質の粗大粒径の石膏結晶
をつくることができるからである。According to the invention, it is possible to reduce the residual amount of Ca SO
This is because -HH2O content can be effectively used to produce high-quality, coarse-grained gypsum crystals.
本発明の効果は次の通りである。The effects of the present invention are as follows.
(1)粒径の大きい石膏のみを回収できる。(1) Only gypsum with large particle size can be recovered.
特に、ガス側条件の悪い場合、たとえば02/SO2比
の大なる時に有効である。This is particularly effective when the gas side conditions are bad, for example when the 02/SO2 ratio is large.
(2)遠心分離機での水分の分離が容易となり、かつ石
膏の付着水分を少なくできるので品質の向上を可能とす
る。(2) Water can be easily separated using a centrifuge, and the amount of water adhering to gypsum can be reduced, making it possible to improve quality.
(3)従来装置とはあまり変らないので、設備費、維持
費の増加はきわめて少ない。(3) Since there is not much difference from conventional equipment, increases in equipment costs and maintenance costs are extremely small.
本発明は、以上のごとく、良質の粗大粒径の石膏のみの
回収を可能ならしめる排煙脱硫石膏回収法用酸化塔を提
供するもので、その工業的価値は大きい。As described above, the present invention provides an oxidation tower for a flue gas desulfurization gypsum recovery method that makes it possible to recover only high-quality, coarse-grained gypsum, and has great industrial value.
第1図は本発明の一実施例の全体図、第2図は第1図の
実施例の要部詳細図、第3図aは第1図の実施例に使用
する気泡分散器の一例の縦断面図、同じくbはaのA−
A矢視図である。
図において、1・・・・・・酸化塔本体、2・・・・・
・CaSO3スラリー液入口、3・・・・・・石膏スラ
リー出口、4・・・・・・石膏スラリー循環配管弁、5
・・・・・・石膏スラリ−抜出口、6・・・・・・空気
入口ヘッダー、7・・・・・・気泡分散器空気入口管調
節弁、8・・・・・・空気出口、9・・・・・・液面、
10・・・・・・スラリー用ポンプ、11・・・・・・
シックナー、12・・・・・・濃縮液出口、13・・・
・・・ろ液出口、14・・・・・・結晶分級用気泡分散
器、15・・・・・・酸化空気用気泡分散器、16・・
・・・・空気入口管、17・・・・・・分級胴体、18
・・・・・・ローター、19・・・・・・ステータ、2
0・・・・・・整流胴、21・・・・・・突起棒。Fig. 1 is an overall view of an embodiment of the present invention, Fig. 2 is a detailed view of the main parts of the embodiment of Fig. 1, and Fig. 3a is an example of a bubble disperser used in the embodiment of Fig. 1. Longitudinal cross-sectional view, b is A- of a
It is a view from arrow A. In the figure, 1... oxidation tower main body, 2...
・CaSO3 slurry liquid inlet, 3...Gypsum slurry outlet, 4...Gypsum slurry circulation piping valve, 5
...Gypsum slurry outlet, 6...Air inlet header, 7...Bubble disperser air inlet pipe control valve, 8...Air outlet, 9 ······Liquid surface,
10... Slurry pump, 11...
Thickener, 12... Concentrate outlet, 13...
... Filtrate outlet, 14... Bubble disperser for crystal classification, 15... Bubble disperser for oxidizing air, 16...
... Air inlet pipe, 17 ... Classification body, 18
...Rotor, 19 ...Stator, 2
0... Rectifier cylinder, 21... Protruding rod.
Claims (1)
硫石膏回収法用酸化塔において、酸化塔本体底部の周辺
部に複数個の酸化空気用気泡分散器を配設するとともに
該底部中央に設けた分級胴体内に分級用気泡分散器を取
り付け、かつ該分級胴体内に石膏スラリー出口を設けた
ことを特徴とする排煙脱硫石膏回収法用酸化塔。1. In an oxidation tower for flue gas desulfurization gypsum recovery method in which calcium sulfite is air-oxidized to gypsum, a plurality of bubble dispersers for oxidizing air are arranged around the bottom of the oxidation tower main body, and at the center of the bottom. An oxidation tower for flue gas desulfurization gypsum recovery method, characterized in that a bubble disperser for classification is installed in the classification body, and a gypsum slurry outlet is provided in the classification body.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP52025100A JPS5843332B2 (en) | 1977-03-08 | 1977-03-08 | Oxidation tower for flue gas desulfurization gypsum recovery method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP52025100A JPS5843332B2 (en) | 1977-03-08 | 1977-03-08 | Oxidation tower for flue gas desulfurization gypsum recovery method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS53109897A JPS53109897A (en) | 1978-09-26 |
| JPS5843332B2 true JPS5843332B2 (en) | 1983-09-26 |
Family
ID=12156498
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP52025100A Expired JPS5843332B2 (en) | 1977-03-08 | 1977-03-08 | Oxidation tower for flue gas desulfurization gypsum recovery method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5843332B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS59184718U (en) * | 1983-05-24 | 1984-12-08 | 株式会社日立ホームテック | heating thermal container |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7522963B2 (en) * | 2004-08-27 | 2009-04-21 | Alstom Technology Ltd | Optimized air pollution control |
| US7536232B2 (en) | 2004-08-27 | 2009-05-19 | Alstom Technology Ltd | Model predictive control of air pollution control processes |
| US9910413B2 (en) | 2013-09-10 | 2018-03-06 | General Electric Technology Gmbh | Automatic tuning control system for air pollution control systems |
-
1977
- 1977-03-08 JP JP52025100A patent/JPS5843332B2/en not_active Expired
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS59184718U (en) * | 1983-05-24 | 1984-12-08 | 株式会社日立ホームテック | heating thermal container |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS53109897A (en) | 1978-09-26 |
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