JP2000218131A - Treatment of organaochlorine compound-containing gas - Google Patents

Treatment of organaochlorine compound-containing gas

Info

Publication number
JP2000218131A
JP2000218131A JP11022349A JP2234999A JP2000218131A JP 2000218131 A JP2000218131 A JP 2000218131A JP 11022349 A JP11022349 A JP 11022349A JP 2234999 A JP2234999 A JP 2234999A JP 2000218131 A JP2000218131 A JP 2000218131A
Authority
JP
Japan
Prior art keywords
catalyst
treating
value
incineration
atomic ratio
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP11022349A
Other languages
Japanese (ja)
Inventor
Akinori Okusako
顕仙 奥迫
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.)
Sumitomo Chemical Co Ltd
Original Assignee
Sumitomo Chemical 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 Sumitomo Chemical Co Ltd filed Critical Sumitomo Chemical Co Ltd
Priority to JP11022349A priority Critical patent/JP2000218131A/en
Publication of JP2000218131A publication Critical patent/JP2000218131A/en
Pending legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To inexpensively and effectively treat organochlorine compd.-containing gas generated at a time of the incineration of urban garbage or industrial waste. SOLUTION: At a time of the incineration of waste in an incinerator, a multicomponent oxide type catalyst represented by the general formula; AaBbPcOd (wherein A is at least one element selected from a group consisting of lithium, sodium, potassium, cesium, rubidium, magnesium, calcium, barium, manganese, iron, cobalt, nickel, copper, silver, bismuth, aluminum, gallium, indium, tin, zinc, lanthanum, tungsten, tantalum and niobium, B is at least one element selected from a group consisting of sulfur, boron, silicon and germanium, P is phosphorus, O is oxyden and a, b, c and d are an atomic ratio of respective elements and, when a is set to 1, b is a value of 10 or less containing 0, c is a value of 30 or less not containing 0 and d is a value determined by valencies and an atomic ratio of respective elements) such as AlPO4, Ca3 (PO4) 2 or FePO4 is mixed with waste and the resulting mixture is baked at 200-600 deg.C.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明が属する技術分野】本発明は廃棄物の燃焼処理時
に発生するダイオキシン類等の有機塩素系化合物含有ガ
スの処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating a gas containing an organic chlorine-based compound such as dioxins generated during the combustion treatment of waste.

【0002】[0002]

【従来技術】都市ゴミや産業廃棄物焼却炉から発生する
排ガス中には通常、ダイオキシン類、PCB、その他こ
れらの前駆体と考えられる塩素化合物などの有害有機塩
素系化合物が含有されている。とりわけ、ダイオキシン
類は極微量であっても生物体に重大な影響を及ぼすとし
てその除去技術の確立が急務となってきている。
2. Description of the Related Art Exhaust gas generated from municipal garbage and industrial waste incinerators usually contains harmful organic chlorine-based compounds such as dioxins, PCBs, and chlorine compounds which are considered to be precursors of these. In particular, it is urgently necessary to establish a technology for removing dioxins from the view that they have a significant effect on living organisms even in very small amounts.

【0003】例えば、特開平10−128315号公報
にはダイオキシン類化合物含有廃水を、酸性白土または
活性白土を含む吸着剤に接触させ、上記廃水中のダイオ
キシン類化合物を吸着させる方法が提案されている。ま
た、特開平10−151342号公報には、表面が親水
性である無機多孔質物を含む粉体の排ガス処理剤吸着剤
を用いてダイオキシン類を吸着する焼却設備が提案され
ている。しかしこのような吸着処理方法は、ダイオキシ
ン類吸着後の吸着剤の処理が問題となる。
[0003] For example, Japanese Patent Application Laid-Open No. 10-128315 proposes a method in which dioxin compound-containing wastewater is brought into contact with an adsorbent containing acid clay or activated clay to adsorb the dioxin compounds in the wastewater. . In addition, Japanese Patent Application Laid-Open No. Hei 10-151342 proposes an incineration facility that adsorbs dioxins by using a powdery exhaust gas treating agent adsorbent containing an inorganic porous material having a hydrophilic surface. However, such an adsorption treatment method has a problem in treating the adsorbent after adsorbing dioxins.

【0004】また、特開平10−66829号公報、特
開平10−99646号公報、特開平10−23519
1号公報には、固定床でV−W−TiO2 系触媒を用い
た有機ハロゲン化合物の除去方法が提案されている。し
かしながら、これら固定床型触媒は、一日のゴミ焼却能
力が数百トン規模の大規模な焼却炉の場合、建設費が数
億円を越え、極めて高価な設備投資が要求されるとの問
題を有する。
Further, Japanese Patent Application Laid-Open Nos. 10-66829, 10-99646, and 10-23519
No. 1 proposes a method for removing an organic halogen compound using a VW-TiO 2 -based catalyst in a fixed bed. However, these fixed-bed catalysts have the problem that, in the case of a large-scale incinerator with a daily incineration capacity of several hundred tons, the construction cost exceeds several hundred million yen and extremely expensive capital investment is required. Having.

【0005】[0005]

【発明が解決しようとする課題】かかる事情下に鑑み、
本発明者等は、都市ゴミや産業廃棄物焼却時に発生する
有機塩素系化合物含有ガスを廉価に且つ効果的に処理し
得る方法を見出すべく鋭意検討した結果、特定の複合酸
化物系触媒を用いる場合には、廉価で効率よく燃焼排ガ
ス中の有機塩素系化合物を処理し得ることを見出し、本
発明を完成するに至った。
In view of such circumstances,
The present inventors have conducted intensive studies to find a method that can inexpensively and effectively treat an organic chlorine-based compound-containing gas generated during incineration of municipal garbage and industrial waste, and as a result, use a specific composite oxide-based catalyst. In such a case, it was found that the organic chlorine-based compound in the flue gas could be efficiently and inexpensively processed, and the present invention was completed.

【0006】[0006]

【課題を解決するための手段】すなわち、本発明は、焼
却時に発生する有機塩素系化合物含有ガスを触媒存在下
に酸素と接触させて処理する有機塩素系化合物含有ガス
の処理方法において、触媒として一般式AaBbPcO
d(式中のAはリチウム、ナトリウム、カリウム、セシ
ウム、ルビジウム、マグネシウム、カルシウム、バリウ
ム、マンガン、鉄、コバルト、ニッケル、銅、銀、ビス
マス、アルミニウム、ガリウム、インジウム、スズ、亜
鉛、ランタン、セリウム、タングステン、タンタル、ニ
オブからなる群より選ばれた少なくとも1種の元素を表
し、Bは硫黄、ホウ素、珪素、ゲルマニウムからなる群
より選ばれた少なくとも1種の元素、Pはリン、Oは酸
素を表し、また添字a、b、c及びdは各元素の原子比
を表し、a=1としたときbは0を含む10以下の値、
cは0を含まない30以下の値を表し、dは各元素の原
子価および原子比によって決まる値を表す。)で示され
る複合酸化物系触媒を用いることを特徴とする有機塩素
系化合物含有ガスの処理方法を提供するにある。
That is, the present invention relates to a method for treating an organochlorine compound-containing gas, which comprises treating an organochlorine compound-containing gas generated during incineration by contacting it with oxygen in the presence of a catalyst. General formula AaBbPcO
d (A in the formula is lithium, sodium, potassium, cesium, rubidium, magnesium, calcium, barium, manganese, iron, cobalt, nickel, copper, silver, bismuth, aluminum, gallium, indium, tin, zinc, lanthanum, cerium , Tungsten, tantalum, and niobium represent at least one element selected from the group consisting of sulfur, boron, silicon, and germanium; P is phosphorus, and O is oxygen. And the subscripts a, b, c and d represent the atomic ratio of each element, and when a = 1, b is a value of 10 or less including 0,
c represents a value of not more than 30 not including 0, and d represents a value determined by the valence and atomic ratio of each element. It is another object of the present invention to provide a method for treating a gas containing an organic chlorine-based compound, which comprises using the complex oxide-based catalyst represented by the formula (1).

【0007】[0007]

【発明の実施の形態】以下、本発明をさらに詳細に説明
する。本発明で処理の対象とする排ガスとしては例え
ば、都市ゴミや産業廃棄物等の有機塩素系化合物を含有
する燃焼排ガスが挙げられる。このような燃焼排ガスに
はダイオキシン類や、これらの前駆体となるクロロベン
ゼン類、クロロフェノール類等の有機塩素系化合物が含
まれる。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in more detail. Examples of the exhaust gas to be treated in the present invention include a combustion exhaust gas containing an organic chlorine-based compound such as municipal waste and industrial waste. Such combustion exhaust gas contains dioxins and organochlorine compounds such as chlorobenzenes and chlorophenols, which are precursors thereof.

【0008】本発明で使用される複合酸化物系触媒は、
一般式AaBbPcOd(式中の記号は前記と同じ)で
示される複合リン酸塩系触媒である。触媒成分Aとして
は、リチウム、ナトリウム、カリウム、セシウム、ルビ
ジウム、マグネシウム、カルシウム、バリウム、マンガ
ン、鉄、コバルト、ニッケル、銅、銀、ビスマス、アル
ミニウム、ガリウム、インジウム、スズ、亜鉛、ランタ
ン、セリウム、イットリウム、タングステン、タンタ
ル、ニオブからなる群より選ばれた少なくとも1種の元
素であるが、好ましくはリチウム、ナトリウム、カリウ
ム、マグネシウム、カルシウム、バリウム、マンガン、
コバルト、ニッケル、アルミニウム、ガリウム、インジ
ウム、スズ、亜鉛、ランタン、セリウムからなる群より
選ばれた少なくとも1種の元素である。特に有機塩素化
合物を含有する排ガスとの接触方法に於いて、特別の装
置を用いることなく、燃焼物質に混合し燃焼せしめる簡
単な方法で、かつ燃焼排ガス処理後の触媒を残灰と共に
埋立処理等に供しても問題なく、且つ廉価であることよ
り、触媒成分Aとしてナトリウム、カリウム、マグネシ
ウム、カルシウム、アルミニウムからなる群より選ばれ
た少なくとも1種の元素が使用された複合リン酸塩系触
媒の使用が推奨される。
The composite oxide catalyst used in the present invention is:
This is a composite phosphate catalyst represented by the general formula AaBbPcOd (the symbols in the formula are the same as described above). As the catalyst component A, lithium, sodium, potassium, cesium, rubidium, magnesium, calcium, barium, manganese, iron, cobalt, nickel, copper, silver, bismuth, aluminum, gallium, indium, tin, zinc, lanthanum, cerium, Yttrium, tungsten, tantalum, at least one element selected from the group consisting of niobium, preferably lithium, sodium, potassium, magnesium, calcium, barium, manganese,
It is at least one element selected from the group consisting of cobalt, nickel, aluminum, gallium, indium, tin, zinc, lanthanum, and cerium. Especially in the method of contacting with exhaust gases containing organic chlorine compounds, it is a simple method of mixing and burning with the combustion material without using special equipment, and the catalyst after the treatment of the combustion exhaust gas is landfilled together with residual ash. And at least one element selected from the group consisting of sodium, potassium, magnesium, calcium, and aluminum as the catalyst component A. Use is recommended.

【0009】触媒成分Bとしては、硫黄、ホウ素、珪
素、ゲルマニウムからなる群より選ばれた少なくとも1
種の元素が挙げられる。一般式中Pはリン、Oは酸素を
表し、また添字a、b、c及びdは各元素の原子比を表
し、a=1としたときbは0を含む10以下の値、cは
0を含まない30以下の値を表し、dは各元素の原子価
および原子比によって決まる値を表す。)で示される複
合酸化物系触媒である。添字で示す数値範囲が上記範囲
を外れる場合には、排ガス中の十分な有機性塩素化合物
の低減効果が得られない。
As the catalyst component B, at least one selected from the group consisting of sulfur, boron, silicon and germanium is used.
Species of elements. In the general formula, P represents phosphorus, O represents oxygen, and subscripts a, b, c, and d represent the atomic ratio of each element. When a = 1, b is a value of 10 or less including 0, and c is 0. And d represents a value determined by the valence and atomic ratio of each element. ). When the numerical range indicated by the subscript is out of the above range, a sufficient effect of reducing the amount of the organic chlorine compound in the exhaust gas cannot be obtained.

【0010】このような一般式を有する複合リン酸塩系
触媒としてはNa2 HPO4 、K2HPO4 、Cs2
PO4 、Rb2 HPO4 、MgHPO4 、CaHP
4 、Ca(H2 PO4 2 、Ca3 (PO4 2 、C
aP2 7 、BaHPO4 、FePO4 、Co3 (PO
4 2 、Ni3 (PO4 2 、Cu2 2 7 、AlP
4 、Al(H2 PO4 3 、AlH3 (PO4 2
Al4 (P2 7 3 、GaPO4 、InPO4 、Sn
3 (PO4 2 、Zn3 (PO4 2 、LaPO4、C
ePO4 等が具体的に挙げられる。就中、Ca3 (PO
4 2 、AlPO4、FePO4 の適用が推奨される。
[0010] The complex phosphate system having such a general formula
Na as a catalystTwoHPOFour, KTwoHPOFour, CsTwoH
POFour, RbTwoHPOFour, MgHPOFour, CaHP
OFour, Ca (HTwoPOFour)Two, CaThree(POFour)Two, C
aPTwoO7, BaHPOFour, FePOFour, CoThree(PO
Four)Two, NiThree(POFour)Two, CuTwoPTwoO7, AlP
O Four, Al (HTwoPOFour)Three, AlHThree(POFour)Two,
AlFour(PTwoO7)Three, GaPOFour, InPOFour, Sn
Three(POFour)Two, ZnThree(POFour)Two, LaPOFour, C
ePOFourAnd the like. Especially, CaThree(PO
Four)Two, AlPOFour, FePOFourIs recommended.

【0011】本発明に用いる触媒調製法に関しては特に
制限はなく、複合酸化物触媒を得る公知の方法により調
製できる。例えば、上記一般式中A、Bで表した元素の
酸化物、水酸化物、硝酸塩、アンモニウム塩、炭酸塩、
塩化物、有機酸塩、アルコキサイド、金属酸アンモニウ
ム塩等の少なくとも一種とリン酸アンモニウム、リン酸
水素二アンモニウム、リン酸二水素アンモニウム、85
%リン酸水溶液等のリン原料を混合し、これを蒸発乾
固、或いは固液分離、乾燥した後、焼成する方法等が挙
げられる。例えばアルミニウムおよびリンからなるリン
酸塩系触媒であれば、硝酸アルミニウム水溶液にリン酸
アンモニウム水溶液を添加し、蒸発乾固の後、焼成すれ
ばよい。
The method for preparing the catalyst used in the present invention is not particularly limited, and the catalyst can be prepared by a known method for obtaining a composite oxide catalyst. For example, oxides, hydroxides, nitrates, ammonium salts, carbonates of the elements represented by A and B in the above general formula,
At least one of a chloride, an organic acid salt, an alkoxide, an ammonium metal acid salt and the like, and ammonium phosphate, diammonium hydrogen phosphate, ammonium dihydrogen phosphate, 85
% Phosphoric acid aqueous solution or the like, and then evaporating to dryness, or solid-liquid separation, drying, and firing. For example, in the case of a phosphate catalyst composed of aluminum and phosphorus, an aqueous solution of ammonium phosphate may be added to an aqueous solution of aluminum nitrate, evaporated to dryness, and then fired.

【0012】触媒は単独で用いてもよいが、担体に担持
して、或いは希釈剤と混合して用いてもよい。担体や希
釈剤としては、例えばボリア、シリカ、アルミナ、シリ
カ−アルミナ、マグネシア、カルシア、セリア、ゼオラ
イト、ジルコニア、シリコン−カーバイト、粘土等が挙
げられる。担持量や希釈剤と触媒との希釈混合比に制限
はない。また、触媒は粉状で用いても、これを成形して
用いてもよい。成形して使用する場合にはハニカム状、
タブレット状、リング状、球状、柱状等の公知の形状の
ものが使用し得る。成型法は圧縮成形、押し出し成形、
噴霧乾燥造粒等公知の方法で行えばよい。
The catalyst may be used alone, but may be supported on a carrier or mixed with a diluent. Examples of the carrier and diluent include boria, silica, alumina, silica-alumina, magnesia, calcia, ceria, zeolite, zirconia, silicon-carbide, clay and the like. There is no limitation on the supported amount or the dilution mixture ratio between the diluent and the catalyst. Further, the catalyst may be used in the form of a powder or may be used after being molded. When molded and used, honeycomb shape,
Known shapes such as a tablet, a ring, a sphere, and a column can be used. The molding method is compression molding, extrusion molding,
A known method such as spray drying granulation may be used.

【0013】本発明の実施に際し、上記方法で得られた
触媒は、酸素存在下、焼却時に発生する有機塩素系化合
物含有ガスと接触させて有機塩素系化合物含有ガスを処
理するが、有機塩素系化合物含有ガスとの接触方法とし
て、固定床、移動床、流動床等を用いてもよく、さらに
廃棄物と供に焼却炉内に投入して使用してもよい。本発
明の触媒の使用温度については特に制限はないが、反応
温度が低すぎると十分な活性は得られず、また逆に使用
温度が高すぎると触媒が劣化してしまう恐れがある。そ
こで通常300〜1000℃の範囲で選択できるが、好
ましくは300〜800℃である。反応圧力は減圧から
加圧まで幅広く選べるが通常100〜400kPa、好
ましくは100〜200kPaの範囲である。
In practicing the present invention, the catalyst obtained by the above method is treated with an organic chlorine-based compound-containing gas by bringing it into contact with an organic chlorine-based compound-containing gas generated during incineration in the presence of oxygen. As a method of contacting with the compound-containing gas, a fixed bed, a moving bed, a fluidized bed, or the like may be used, and further, it may be put into an incinerator with waste and used. The use temperature of the catalyst of the present invention is not particularly limited. However, if the reaction temperature is too low, sufficient activity cannot be obtained, and if the use temperature is too high, the catalyst may be deteriorated. Therefore, the temperature can be usually selected in the range of 300 to 1000 ° C., preferably 300 to 800 ° C. The reaction pressure can be selected from a wide range from reduced pressure to increased pressure, but is usually in the range of 100 to 400 kPa, preferably 100 to 200 kPa.

【0014】[0014]

【発明の効果】以上詳述した本発明方法によれば、廉価
で効率よく燃焼排ガス中の有機塩素系化合物を処理する
ことが可能で、特にAlPO4 、Ca3 (PO4 2
FePO4 等よりなる複合リン酸系酸化物触媒を用いる
場合には、使用後の触媒も焼却残灰と共に埋め立てや、
或いは土木建築材料資材原料として使用することも可能
であることより、その産業上の効果は極めて大である。
According to the method of the present invention described in detail above, it is possible to efficiently and inexpensively treat organochlorine compounds in flue gas, especially AlPO 4 , Ca 3 (PO 4 ) 2 ,
When a composite phosphoric acid oxide catalyst made of FePO 4 or the like is used, the used catalyst is also buried together with the incineration residual ash,
Alternatively, since it can be used as a raw material for civil engineering and building materials, its industrial effect is extremely large.

【0015】[0015]

【実施例】次に実施例により本発明をさらに詳細に説明
するが、本発明はこれらに限定されるものではない。
尚、本発明に於いては有機塩素系化合物として、モノク
ロロベンゼンを用いた。モノクロロベンゼン(MCB)
の分解率(%)を次式で表す。 MCB分解率(%)=(入口のMCB濃度−出口のMC
B濃度)÷(入口のMCB濃度)×100
Next, the present invention will be described in more detail by way of examples, but the present invention is not limited to these examples.
In the present invention, monochlorobenzene was used as the organic chlorine compound. Monochlorobenzene (MCB)
Is expressed by the following equation. MCB decomposition rate (%) = (MCB concentration at inlet-MC at outlet)
B concentration) 濃度 (MCB concentration at inlet) × 100

【0016】実施例1 イオン交換水400mlに硝酸カルシウム(Ca(NO
3 2 ・4H2 O)141.70gを溶解し、均一な溶
液とした。この水溶液に85%リン酸水溶液46.16
gを攪拌しながら添加した後、25%アンモニア水を用
いpH≒9に調整した。このようにして得られたスラリ
ー溶液を濾過後、120℃で約20時間乾燥した。得ら
れた乾燥品を空気中500℃で3時間焼成して触媒を得
た。この触媒の元素分析を行った結果、リンとカルシウ
ムの比(モル比)はP/Ca=0.64であった〔Ca
3 (PO4 2 〕。この触媒を粉砕、篩別し22〜30
メシュの粒子を得た。このようにして得た触媒3gと#
14の信濃電気製錬(株)製シナノランダム(シリコン
カーバイド)18gを混合し、内径15mmのパイレッ
クスガラス製反応管に充填した。これにMCB/CO2
/酸素/窒素の割合(体積比)が100ppm/260
ppm/15%/85%からなる原料ガスを供給し活性
試験を行った。反応圧力は常圧、空間速度は5000/
hrとした。入口、出口それぞれのMCB濃度は液体ク
ロマトグラフィーを用いて分析した。分析は絶対検量線
法で行った。その結果、反応器壁温500℃においける
MCB分解率は100%であった。
EXAMPLE 1 Calcium nitrate (Ca (NO
3) was dissolved 2 · 4H 2 O) 141.70g, and a uniform solution. An aqueous 85% phosphoric acid solution 46.16 was added to this aqueous solution.
g was added with stirring, and the pH was adjusted to 9 using 25% aqueous ammonia. The slurry solution thus obtained was filtered and then dried at 120 ° C. for about 20 hours. The obtained dried product was calcined in air at 500 ° C. for 3 hours to obtain a catalyst. As a result of elemental analysis of this catalyst, the ratio (molar ratio) of phosphorus to calcium was P / Ca = 0.64 [Ca
3 (PO 4 ) 2 ]. This catalyst is pulverized and sieved to 22 to 30
Mesh particles were obtained. 3 g of the catalyst thus obtained and #
18 g of Shinano Random (silicon carbide) manufactured by Shinano Electric Smelting Co., Ltd. were mixed and filled into a Pyrex glass reaction tube having an inner diameter of 15 mm. MCB / CO 2
/ Oxygen / nitrogen ratio (volume ratio) is 100 ppm / 260
An activity test was performed by supplying a raw material gas consisting of ppm / 15% / 85%. Reaction pressure is normal pressure, space velocity is 5000 /
hr. The MCB concentration at each of the inlet and outlet was analyzed using liquid chromatography. The analysis was performed by the absolute calibration method. As a result, the MCB decomposition rate at a reactor wall temperature of 500 ° C. was 100%.

【0017】実施例2 イオン交換水400mlに硝酸セリウム(Ce(N
3 3 ・6H2 O)86.95gを溶解し均一な溶液
とした。この水溶液に85%リン酸水溶液23.09g
を攪拌しながら添加した後、25%アンモニア水を用い
pH≒9に調整した。このようにして得られたスラリー
溶液を濾過、乾燥後、空気中500℃で3時間焼成して
触媒を得た。この触媒の元素分析を行った結果、リンと
セリウムの比(モル比)はP/Ce=0.90であった
〔CePO4 〕。この触媒を粉砕、篩別し22〜30メ
シュの粒子を得た。この触媒を用い実施例1と同じ条件
で活性評価を行った。その結果、反応器壁温400℃に
於けるMCB分解率は94%であった。
Example 2 Cerium nitrate (Ce (N) was added to 400 ml of ion-exchanged water.
O 3) 3 · 6H 2 O ) was dissolved 86.95g to prepare a homogenous solution. 23.09 g of 85% phosphoric acid aqueous solution
Was added with stirring, and the pH was adjusted to 9 using 25% aqueous ammonia. The slurry solution thus obtained was filtered, dried, and then calcined in air at 500 ° C. for 3 hours to obtain a catalyst. As a result of elemental analysis of this catalyst, the ratio (molar ratio) of phosphorus to cerium was P / Ce = 0.90 [CePO 4 ]. The catalyst was pulverized and sieved to obtain 22-30 mesh particles. The activity was evaluated under the same conditions as in Example 1 using this catalyst. As a result, the MCB decomposition rate at a reactor wall temperature of 400 ° C. was 94%.

【0018】実施例3 イオン交換水800mlに硝酸アルミニウム(Al(N
3 3 ・9H2 O)150.02gを溶解し均一な溶
液とした。この水溶液に85%リン酸水溶液46.04
gを攪拌しながら添加した後、25%アンモニア水を用
いpH≒9に調整した。このようにして得られたスラリ
ー溶液を濾過、乾燥後、空気中500℃で3時間焼成し
て触媒を得た。この触媒の元素分析を行った結果、リン
とアルミニウムの比(モル比)はP/Al=0.99で
あった〔AlPO4 〕。この触媒を粉砕、篩別し22〜
30メシュの粒子を得た。この触媒を用い実施例1と同
じ条件で活性評価を行った。その結果、反応器壁温50
0℃に於けるMCB分解率は96%であった。
Example 3 Aluminum nitrate (Al (N
O 3) 3 · 9H 2 O ) was dissolved 150.02g was a uniform solution. An 85% phosphoric acid aqueous solution 46.04 was added to this aqueous solution.
g was added with stirring, and the pH was adjusted to 9 using 25% aqueous ammonia. The slurry solution thus obtained was filtered, dried, and then calcined in air at 500 ° C. for 3 hours to obtain a catalyst. As a result of an elemental analysis of this catalyst, the ratio (molar ratio) of phosphorus to aluminum was P / Al = 0.99 [AlPO 4 ]. This catalyst is pulverized and sieved to 22-
30 mesh particles were obtained. The activity was evaluated under the same conditions as in Example 1 using this catalyst. As a result, the reactor wall temperature 50
The MCB decomposition rate at 0 ° C. was 96%.

【0019】実施例4 イオン交換水400mlに硝酸鉄(Fe(NO3 3
9H2 O)80.86gを溶解し均一な溶液とした。こ
の水溶液に85%リン酸水溶液23.06gを攪拌しな
がら添加した後、25%アンモニア水を用いpH≒9に
調整した。このようにして得られたスラリー溶液を濾
過、乾燥後、空気中500℃で3時間焼成して触媒を得
た。この触媒の元素分析を行った結果、リンと鉄の比
(モル比)はP/Fe=0.98であった〔FeP
4 〕。この触媒を粉砕、篩別し22〜30メシュの粒
子を得た。この触媒を用い実施例1と同じ条件で活性評
価を行った。その結果、反応器壁温500℃におけるM
CB分解率は83%であった。
EXAMPLE 4 Iron nitrate (Fe (NO 3 ) 3.
80.86 g of (9H 2 O) was dissolved to obtain a uniform solution. 23.06 g of an 85% aqueous phosphoric acid solution was added to this aqueous solution with stirring, and the pH was adjusted to 9 using 25% aqueous ammonia. The slurry solution thus obtained was filtered, dried, and then calcined in air at 500 ° C. for 3 hours to obtain a catalyst. As a result of elemental analysis of this catalyst, the ratio (molar ratio) of phosphorus to iron was P / Fe = 0.98 [FeP
O 4 ]. The catalyst was pulverized and sieved to obtain 22-30 mesh particles. The activity was evaluated under the same conditions as in Example 1 using this catalyst. As a result, M at a reactor wall temperature of 500 ° C.
The CB decomposition rate was 83%.

【0020】比較例1 実施例1の方法に於いて、触媒としてCa3 (PO4
2 に代えて、平均粒子径22〜30メッシュの活性アル
ミナ(商品名BK−112:住友化学工業株式会社製)
を用いた他は同じ条件で活性評価を行った。その結果、
反応器壁温500℃におけるMCB分解率は67%であ
った。
Comparative Example 1 In the method of Example 1, the catalyst was Ca 3 (PO 4 )
In place of 2 , activated alumina having an average particle size of 22 to 30 mesh (trade name BK-112: manufactured by Sumitomo Chemical Co., Ltd.)
The activity was evaluated under the same conditions except for using. as a result,
The MCB decomposition rate at a reactor wall temperature of 500 ° C. was 67%.

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 2E191 BA12 BC01 BD13 4D048 AA11 AB03 BA01Y BA02X BA03X BA04Y BA06Y BA14Y BA15Y BA17Y BA19X BA20Y BA28Y BA34Y BA35Y BA36Y BA37Y BA38Y BA42X BA42Y BA44X BA44Y BB01 4G069 AA02 AA08 BB06A BB06B BC02A BC03A BC04A BC05A BC09A BC10A BC13A BC16A BC17A BC18A BC23A BC25A BC31A BC32A BC62A BC66A BC67A BC68A BD02A BD03A BD05A BD07A CA04 CA10 CA19 DA05 DA06 EA02Y ──────────────────────────────────────────────────続 き Continued on the front page F-term (reference) 2E191 BA12 BC01 BD13 4D048 AA11 AB03 BA01Y BA02X BA03X BA04Y BA06Y BA14Y BA15Y BA17Y BA19X BA20Y BA28Y BA34Y BA35Y BA36Y BA37Y BA38Y BA42X BA42Y BA44X BA44A03 BC03 BC03 A02A03 BC BC10A BC13A BC16A BC17A BC18A BC23A BC25A BC31A BC32A BC62A BC66A BC67A BC68A BD02A BD03A BD05A BD07A CA04 CA10 CA19 DA05 DA06 EA02Y

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】焼却時に発生する有機塩素系化合物含有ガ
スを触媒存在下に酸素と接触させて処理する有機塩素系
化合物含有ガスの処理方法において、触媒として一般式
AaBbPcOd(式中のAはリチウム、ナトリウム、
カリウム、セシウム、ルビジウム、マグネシウム、カル
シウム、バリウム、マンガン、鉄、コバルト、ニッケ
ル、銅、銀、ビスマス、アルミニウム、ガリウム、イン
ジウム、スズ、亜鉛、ランタン、セリウム、タングステ
ン、タンタル、ニオブからなる群より選ばれた少なくと
も1種の元素を表し、Bは硫黄、ホウ素、珪素、ゲルマ
ニウムからなる群より選ばれた少なくとも1種の元素、
Pはリン、Oは酸素を表し、また添字a、b、c及びd
は各元素の原子比を表し、a=1としたときbは0を含
む10以下の値、cは0を含まない30以下の値を表
し、dは各元素の原子価および原子比によって決まる値
を表す。)で示される複合酸化物系触媒を用いることを
特徴とする有機塩素系化合物含有ガスの処理方法。
1. A method for treating an organochlorine compound-containing gas, which comprises treating an organochlorine compound-containing gas generated at the time of incineration by bringing it into contact with oxygen in the presence of a catalyst, wherein the catalyst has the general formula AaBbPcOd (where A is lithium ,sodium,
Potassium, cesium, rubidium, magnesium, calcium, barium, manganese, iron, cobalt, nickel, copper, silver, bismuth, aluminum, gallium, indium, tin, zinc, lanthanum, cerium, tungsten, tantalum, niobium B represents at least one element selected from the group consisting of sulfur, boron, silicon, and germanium;
P represents phosphorus, O represents oxygen, and subscripts a, b, c, and d
Represents the atomic ratio of each element. When a = 1, b represents a value of 10 or less including 0, c represents a value of 30 or less not including 0, and d is determined by the valence and atomic ratio of each element. Represents a value. A method for treating a gas containing an organic chlorine-based compound, which comprises using the complex oxide-based catalyst represented by the formula (1).
【請求項2】一般式AaBbPcOdで示される複合酸
化物系触媒の触媒成分Aが、ナトリウム、カリウム、マ
グネシウム、カルシウム、バリウムおよびアルミニウム
からなる群より選ばれた少なくとも1種の元素よりなる
ことを特徴とする請求項1記載の有機塩素系化合物含有
ガスの処理方法。
2. The catalyst component A of the complex oxide-based catalyst represented by the general formula AaBbPcOd comprises at least one element selected from the group consisting of sodium, potassium, magnesium, calcium, barium and aluminum. The method for treating a gas containing an organic chlorine-based compound according to claim 1.
【請求項3】触媒が焼却炉中で焼却物質と共に混合攪拌
された状態で存在することを特徴とする請求項1記載の
有機塩素系化合物含有ガスの処理方法。
3. The method for treating a gas containing an organic chlorine-based compound according to claim 1, wherein the catalyst is present in a state of being mixed and stirred with the incineration material in the incinerator.
JP11022349A 1999-01-29 1999-01-29 Treatment of organaochlorine compound-containing gas Pending JP2000218131A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11022349A JP2000218131A (en) 1999-01-29 1999-01-29 Treatment of organaochlorine compound-containing gas

Publications (1)

Publication Number Publication Date
JP2000218131A true JP2000218131A (en) 2000-08-08

Family

ID=12080198

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2000218131A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100707039B1 (en) 2005-10-07 2007-04-13 에스케이 주식회사 Hydrothermally Stable Microporous Molecular Sieve Catalyst and Preparing Method Thereof
WO2007043742A1 (en) * 2005-10-07 2007-04-19 Sk Energy Co., Ltd. Hydrothermally stable microporous molecular sieve catalyst and preparation method thereof

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100707039B1 (en) 2005-10-07 2007-04-13 에스케이 주식회사 Hydrothermally Stable Microporous Molecular Sieve Catalyst and Preparing Method Thereof
WO2007043742A1 (en) * 2005-10-07 2007-04-19 Sk Energy Co., Ltd. Hydrothermally stable microporous molecular sieve catalyst and preparation method thereof
CN101282784B (en) * 2005-10-07 2012-07-18 Sk新技术株式会社 Hydrothermally stable microporous molecular sieve catalyst and preparation method thereof

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