JPS6262119A - Combustion method for liquid organic halides - Google Patents

Combustion method for liquid organic halides

Info

Publication number
JPS6262119A
JPS6262119A JP60202444A JP20244485A JPS6262119A JP S6262119 A JPS6262119 A JP S6262119A JP 60202444 A JP60202444 A JP 60202444A JP 20244485 A JP20244485 A JP 20244485A JP S6262119 A JPS6262119 A JP S6262119A
Authority
JP
Japan
Prior art keywords
organic halides
solid composition
liquid organic
oxygen
combustion
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
JP60202444A
Other languages
Japanese (ja)
Other versions
JPS648242B2 (en
Inventor
Yoshihiro Kagawa
香川 義博
Yoshimasa Igari
猪狩 俶将
Zensuke Inoue
井上 善介
Saburo Inoue
三郎 井上
Michio Mochizuki
望月 通生
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.)
CLEAN JAPAN CHEM KK
OOSAKASHI
National Institute of Advanced Industrial Science and Technology AIST
Osaka City
Original Assignee
CLEAN JAPAN CHEM KK
OOSAKASHI
Agency of Industrial Science and Technology
Osaka City
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 CLEAN JAPAN CHEM KK, OOSAKASHI, Agency of Industrial Science and Technology, Osaka City filed Critical CLEAN JAPAN CHEM KK
Priority to JP60202444A priority Critical patent/JPS6262119A/en
Publication of JPS6262119A publication Critical patent/JPS6262119A/en
Publication of JPS648242B2 publication Critical patent/JPS648242B2/ja
Granted legal-status Critical Current

Links

Abstract

PURPOSE:To completely decompose liquid organic halides such as PCB etc. to make them harmless, by making in advance liquid organic halides such as PCB etc. into a solid composition having specific composition, and then heating it to high temperature, causing vaporized organic halides being released to be burnt with oxygen. CONSTITUTION:Prior to burning treatment, liquid organic halides are in advance made to form a solid composition composed of liquid organic halides, calcium hydroxides and/or magnesium hydroxides, water-soluble polymers, organic acid metallic salts, silicates, and extending agents. The solid composition wherein liquid organic halides are fixed is heated to high temperatures in the presence of or in the absence of oxygen to cause vaporized organic halides to be released from said solid composition. When said vaporized organic halides are burnt at high temperatures with oxygen, they are completely decomposed, with the result that organic halides themselves can not be detected in the combustion flue gases and also can not be detected in the solid composition.

Description

【発明の詳細な説明】 〔技術分野〕 本発明は、PCB等の液状有機ハロゲン化物を無害化す
るための燃焼処理方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION [Technical Field] The present invention relates to a combustion treatment method for rendering liquid organic halides such as PCB harmless.

〔従来技術〕[Prior art]

PCB (ポリ塩素化ビフェニル)等の液状有機ハロゲ
ン化物は非常に安定な化合物であり、しかも有害性を有
することから、その廃棄処理には非常な困難が伴う。
Liquid organic halides such as PCB (polychlorinated biphenyls) are extremely stable compounds and are also toxic, making their disposal extremely difficult.

現在、液状pcnを保有する企業の一部では、使用禁止
となった当初、短期間の保管によって可急的にその処理
方法が確立され、処理が完了されるものとして、暫定的
保管のために、ドラム缶、薄鉄板槽、或はトランスのま
ま倉庫内等に保管されてきた。しかし、長年月を経るに
従い、ドラム缶、鉄板等の腐蝕から漏出したり、故鉄回
収業者に。
Currently, some companies that own liquid PCN, when its use was first banned, quickly established a treatment method for it by storing it for a short period of time, and assumed that the treatment would be completed, and for temporary storage. , drums, thin iron plate tanks, or transformers have been stored in warehouses, etc. However, over the years, it has leaked from corroded drums, iron plates, etc., and waste metal has been collected by waste iron recovery companies.

トランスがPCB入りのまま持ち込まれ、放置されてい
たものから漏出しているという状況も報道されている。
There have also been reports of transformers being brought in with their PCBs inside and leaking from abandoned items.

これらは、氷山の一角であり、末端での保管の実態は把
握できておらず、極めて憂慮すべき状況にある。その上
、保管施設に莫大な経費をかけた企業でも、地震等の天
災地変が生じた場合に、倒壊事故等による流出、汚染が
心配されている。
These are just the tip of the iceberg, and the actual state of storage at the end of the world is unknown, and the situation is extremely worrying. Furthermore, even companies that have spent a huge amount of money on storage facilities are concerned about leakage and contamination due to collapse, etc., in the event of a natural disaster such as an earthquake.

従来、PCBを無害化するために、各種の方法が提供さ
れているが、処理効率の点から、燃焼法が有利なものと
されている。しかし、燃焼法によってPCBを100%
分解し、完全に無害化することは困難で、この目的を達
成するには、例えば、3段階の燃焼工程、即ち、140
0℃以上での第1次燃焼、1500℃以上での第2次燃
焼及び1400℃以上での第3次燃焼の工程が必要であ
るとされている。
Conventionally, various methods have been provided to render PCB harmless, but the combustion method is considered to be advantageous in terms of processing efficiency. However, the combustion method eliminates 100% PCBs.
It is difficult to decompose and completely render harmless, and to achieve this goal, for example, a three-stage combustion process, namely 140
It is said that the steps of primary combustion at 0°C or higher, secondary combustion at 1500°C or higher, and tertiary combustion at 1400°C or higher are required.

〔目   的〕〔the purpose〕

本発明の目的は、前記PCB等の液状有機ハロゲン化物
を燃焼法により無害化する方法において、作業性がよく
かつ比較的簡単な方法により、確実に無害化する方法を
提供することにある。
An object of the present invention is to provide a method of detoxifying liquid organic halides such as PCBs by a combustion method, which is highly workable and relatively simple.

〔構  成〕〔composition〕

本発明によれば、液状有機ハロゲン化物を、あらかじめ
、該液状有機ハロゲン化物と、水酸化カルシウム及び/
又は水酸化マグネシウムと、水溶性高分子と、有機酸金
属塩と、珪酸塩と、増量剤とからなる固体状組成物とし
た後、該−棒状組成物を、酸素の存在又は不存在下、高
温に加熱すると共に、該固体状組成物から放出された蒸
気状有機ハロゲン化物を、酸素で燃焼させることを特徴
とする液状有機ハロゲン化物の燃焼処理方法が提供され
る。
According to the present invention, the liquid organic halide is mixed with calcium hydroxide and/or the liquid organic halide in advance.
Or, after forming a solid composition consisting of magnesium hydroxide, a water-soluble polymer, an organic acid metal salt, a silicate, and an extender, the rod-shaped composition is prepared in the presence or absence of oxygen, A method for combustion treatment of a liquid organic halide is provided, which comprises heating the solid composition to a high temperature and burning the vaporous organic halide released from the solid composition with oxygen.

本発明においては、燃焼処理に先ち、液状有機ハロゲン
化物を、あらかじめ、液状有機ハロゲン化物と、水酸化
力ルシーウム及び/又は水酸化マグネシウムと、水溶性
高分子と、有機酸金属塩と、珪酸塩と、増量剤とからな
る固体状組成物とする。
In the present invention, prior to the combustion treatment, the liquid organic halide is mixed with the liquid organic halide, lucium hydroxide and/or magnesium hydroxide, a water-soluble polymer, an organic acid metal salt, and a silicic acid. A solid composition is formed from a salt and a filler.

このような固体状組成物の製造は、酸化カルシウム及び
/又は酸化マグネシウムと水とを反応させるに際し、こ
の反応系に、液状有機ハロゲン化物と共に、水溶性高分
子、有機酸金属塩、珪酸塩及び増量剤を加えることによ
って行うことができる。
To produce such a solid composition, when calcium oxide and/or magnesium oxide is reacted with water, a water-soluble polymer, an organic acid metal salt, a silicate, and a liquid organic halide are added to the reaction system. This can be done by adding fillers.

この場合の酸化カルシウム及び/又は酸化マグネシウム
と水との反応では多大の発熱を生じ、酸化カルシウム及
び/又は酸化マグネシウムは、水酸化カルシウム及び/
又は水酸化マグネシウムに変換される。
In this case, the reaction between calcium oxide and/or magnesium oxide and water generates a large amount of heat, and calcium oxide and/or magnesium oxide reacts with calcium hydroxide and/or magnesium oxide.
Or converted to magnesium hydroxide.

水溶性高分子としては、従来公知の種々のものが用いら
れ、ポリビニルアルコール、デンプン及びその誘導体、
メトキシセルロース、ヒドロキシエチルセルロース、メ
チルセルロース、エチルセルロース、カルボキシメチル
セルロース等のセルロース誘導体、ポリアクリル酸ソー
ダ、アクリル酸アミド/アクリル酸エステル共重合体、
スチレン/無水マレイン酸共重合体アルカリ塩、アルギ
ン酸ソーダ、ゼラチン、カゼイン等がある。このような
水溶性高分子は、その分子中にカルボキシル基や水酸基
等の親木基を多数含み、アルカリ性条件下では有機ハロ
ゲン化物や珪酸塩と反応したり、あるいはゲル状物とな
り、最終的に水不溶性の物質に変換されるものと考えら
れる。
Various conventionally known water-soluble polymers are used, including polyvinyl alcohol, starch and its derivatives,
Cellulose derivatives such as methoxycellulose, hydroxyethylcellulose, methylcellulose, ethylcellulose, carboxymethylcellulose, sodium polyacrylate, acrylic amide/acrylic ester copolymer,
Examples include styrene/maleic anhydride copolymer alkali salt, sodium alginate, gelatin, and casein. Such water-soluble polymers contain many parent groups such as carboxyl groups and hydroxyl groups in their molecules, and under alkaline conditions they react with organic halides and silicates, or become gel-like substances, and eventually It is thought that it is converted into a water-insoluble substance.

有機酸金属塩としては、従来公知のカルボキシル基を持
つ脂肪族及び芳香族系の種々のものが使用され、例えば
、ステアリン酸、カプリン酸、ラウリン酸、ミリスチン
酸、パルミチン酸、リノール酸、リルン酸、オレイン酸
などの高級脂肪酸の金属塩の他、安息香酸、サリチル酸
、p−ヒドロキシ安息香酸、ナフトエ酸、タンニン酸等
の芳香族カルボン酸等が挙げられる。また、金属塩とし
ては、アルミニウム、マンガン、コバルト、カルシウム
、マグネシウム、鉄、亜鉛、ニッケル等が挙げられる。
As the organic acid metal salt, various conventionally known aliphatic and aromatic ones having a carboxyl group are used, such as stearic acid, capric acid, lauric acid, myristic acid, palmitic acid, linoleic acid, lylunic acid. , metal salts of higher fatty acids such as oleic acid, and aromatic carboxylic acids such as benzoic acid, salicylic acid, p-hydroxybenzoic acid, naphthoic acid, and tannic acid. Further, examples of metal salts include aluminum, manganese, cobalt, calcium, magnesium, iron, zinc, and nickel.

一般に、金属セッケンとして使用されている有機酸金属
塩の使用が好適である。このような有機酸金属塩は、水
不溶性であり、反応後に生じた生成物をサラサラとした
粉末状にする効果を有し、また有機ハロゲン化合物や前
記高分子とも配位結合等して、有機ハロゲン化物の不溶
化にも効果を有するものと考えられる。
In general, it is preferred to use organic acid metal salts that are used as metal soaps. Such organic acid metal salts are water-insoluble, have the effect of making the product produced after the reaction into a smooth powder, and also form coordination bonds with organic halogen compounds and the above-mentioned polymers, and form organic It is thought that it also has an effect on insolubilizing halides.

珪酸塩としては、珪酸ナトリウム、珪酸カルシウム、珪
酸マグネシウム、珪酸カルシウムナトリウム等が挙げら
れるが、珪酸マグネシウムカルシウムの使用が好ましい
。また、珪酸には、オルト珪酸やメタ珪酸が包含される
。このような珪酸塩は、天然に産出するものを有利に用
いることができる。このような珪酸塩は、有機ハロゲン
化物と反応してオルガノハロポリシロキサンを生じたり
、あるいは反応系に存在する各種金属元素と反応して、
水不溶性の化合物1例えば、ゲーレナイト等を形成した
りするものと考えられる。
Examples of the silicate include sodium silicate, calcium silicate, magnesium silicate, sodium calcium silicate, etc., and use of magnesium calcium silicate is preferred. Moreover, silicic acid includes ortho-silicic acid and meta-silicic acid. Naturally occurring silicates can be advantageously used as such silicates. Such silicates react with organic halides to produce organohalopolysiloxanes, or react with various metal elements present in the reaction system,
It is thought that water-insoluble compounds 1, such as gehlenite, are formed.

増量剤としては、各種の無機化合物や粘土鉱物が使用さ
れ、例えば、炭酸カルシウム、石コウ、シリカ、ゼオラ
イト、パーライト、セピオライト。
Various inorganic compounds and clay minerals are used as fillers, such as calcium carbonate, gypsum, silica, zeolite, perlite, and sepiolite.

白土、中性陶土、カオリン、ベントナイト、黄土等が挙
げられる。このような増量剤は1発熱反応を希釈する効
果を示す他、生成物を取扱いの容易な粉末固形状にする
等の効果を示す。
Examples include white clay, neutral china clay, kaolin, bentonite, and loess. Such extenders have the effect of diluting the exothermic reaction and also have the effect of converting the product into a powder solid that is easy to handle.

次に1本発明で用いる前記各成分の使用割合について述
べると、酸化カルシウム及び/又は酸化マグネシウムは
、40〜70重量%、水溶性高分子1.5〜10重量%
、有機酸金属塩2〜10重量%、珪酸塩5〜15重量%
、増量剤15〜30重量%である。
Next, to describe the proportions of each component used in the present invention, calcium oxide and/or magnesium oxide is 40 to 70% by weight, and water-soluble polymer is 1.5 to 10% by weight.
, organic acid metal salt 2-10% by weight, silicate 5-15% by weight
, 15-30% by weight of filler.

前記固体状組成物を好ましく製造するには、各成分をミ
キサーに添加し、均一に攪拌した後、水を添加し、攪拌
を行う。この操作により発熱反応が起り、温度が上昇す
るが、約120〜150℃で処理対象とする有機ハロゲ
ン化物を加えてさらに攪拌を続ける。この攪拌を通常1
〜5分間分間石屋と。
To preferably produce the solid composition, each component is added to a mixer and stirred uniformly, and then water is added and stirred. Although this operation causes an exothermic reaction and the temperature rises, the organic halide to be treated is added at about 120 to 150° C. and stirring is continued. This stirring is usually done for 1
~5 minutes with Ishiya.

粉状の処理物が得られる。この場合、種々の変更が可能
であり、例えば、各添加成分の混合に先立ち、水を先に
加えることができ、また、各成分の混合順序は任意であ
り、水溶性高分子をメタノール等の有機溶剤にあらかじ
め溶解して水に加えておき、これを他の添加成分と有機
ハロゲン化物との混合物に加えて反応を行うことができ
る。さらに、あらかじめ、各添加成分を均一な混合物と
しておき、現場において、この混合物と水と有機ハロゲ
ン化物を混合反応させることができる。このような混合
物の1例を次表に示す。
A powdered processed product is obtained. In this case, various changes are possible. For example, water can be added first before mixing each additive component, and the order of mixing each component can be arbitrary. The reaction can be carried out by dissolving it in an organic solvent in advance and adding it to water, and then adding this to a mixture of other additive components and the organic halide. Furthermore, it is possible to form a homogeneous mixture of each additive component in advance, and then mix and react this mixture, water, and organic halide on site. An example of such a mixture is shown in the table below.

表−1 前記反応は有機ハロゲン化物の沸点以下の温度で行われ
、PCBの場合、90〜145℃程度で行うのがよい。
Table 1 The reaction is carried out at a temperature below the boiling point of the organic halide, and in the case of PCB, it is preferably carried out at about 90 to 145°C.

反応温度の調節は、無機増量剤の添加量を加減すること
によって行うことができる。反応装置としては、密封型
のものが用いられる。有機ハロゲン化物に対する前記各
添加成分の使用割合は。
The reaction temperature can be adjusted by adjusting the amount of inorganic extender added. As the reactor, a sealed type is used. What is the usage ratio of each of the above additive components to the organic halide?

有機ハロゲン化物の種類や反応条件による変るが。It varies depending on the type of organic halide and reaction conditions.

一般的には、その添加成分の合計量で、有機ハロゲン化
物100重量部あたり、25〜200重量部程度である
。また水の使用割合は、酸化カルシウム及び/又は酸化
マグネシウム当り5〜100程度である。
Generally, the total amount of the added components is about 25 to 200 parts by weight per 100 parts by weight of the organic halide. The ratio of water used is about 5 to 100 parts per calcium oxide and/or magnesium oxide.

前記のようにして得られる生成物は、有機ハロゲン化物
の固定化されたものであり、固形物からの有機ハロゲン
化物の溶出は殆んど見られない。
The product obtained as described above is a product in which the organic halide is immobilized, and elution of the organic halide from the solid substance is hardly observed.

また、この生成物は、粉末状であるが、このものは、必
要に応じ、ペレット状、塊状等の任意の形状に成形する
ことができる。なお、本発明で用いるこのような組成物
については、特開昭60−139263号公報に記載さ
れている。
Further, although this product is in the form of a powder, it can be formed into any shape such as pellets or lumps, if necessary. Incidentally, such a composition used in the present invention is described in JP-A-60-139263.

本発明者らの研究によれば、前記の液状有機ハロゲン化
物の固定化された固体状組成“物は、これを酸素の存在
下又は不存在で高温に加熱して固体状組成物から蒸気状
有機ハロゲン化物を放出させ、この蒸気状有機ハロゲン
化物を酸素により高温燃焼させる時には、液状有機ハロ
ゲン化物は実質上完全に分解され、燃焼排ガス中には有
機ハロゲン化物自体の検出は見られず、また固体状組成
物中にもその検出は見られないことが見出された。この
ような熱処理により、液状有機ハロゲン化物が完全分解
される理由は明確に鮮明されていないが、固体状組成物
を加熱した時に、その固体状組成物には水酸化カルシウ
ム及び/又は水酸化マグネシウムや、有機酸金属塩、珪
酸塩等の金属化合物が含まれているため、これらの金属
化合物が液状有機ハロゲン化物の分解触媒的作用を示し
、固体状組成物から気化する有機ハロゲン化物は、部分
的に分解を受けた不安定な構造のもの、即ち、燃焼性の
高い構造のものに変換されることによるものと考えられ
る。
According to the research of the present inventors, the solid composition of the above-mentioned liquid organic halide can be converted into vapor by heating it to a high temperature in the presence or absence of oxygen. When an organic halide is released and the vaporized organic halide is burned at high temperature with oxygen, the liquid organic halide is virtually completely decomposed, and no organic halide itself is detected in the combustion exhaust gas. It was found that it was not detected even in solid compositions.The reason why liquid organic halides are completely decomposed by such heat treatment is not clearly understood, but When heated, the solid composition contains metal compounds such as calcium hydroxide and/or magnesium hydroxide, organic acid metal salts, and silicates. The organic halide that exhibits a decomposition catalytic action and vaporizes from the solid composition is partially decomposed and converted into an unstable structure, that is, a highly combustible structure. Conceivable.

本発明における液状有機ハロゲン化物の燃焼方法におい
ては、反応工程上では、加熱による固体状組成物からの
燃焼性の高められた蒸気状ハロゲン化物の放出工程と、
この放出された蒸気状ハロゲン化物の燃焼工程からなる
。従って、本発明を実施する場合、加熱室と燃焼室を備
えた燃焼炉を用いて実施することができ、加熱室と燃焼
室との条件を変化させることができる。この場合、固体
状組成物から蒸気状有機ハロゲン化物を放出させるため
の加熱では、800〜1500℃、好−ましくは850
〜1200℃の温度条件が採用され、またこの加熱にお
いては、酸素の存在は必ずしも必要とされないが、一般
には酸素の存在下で行われる。次に、固体状組成物から
の蒸気状有機ハロゲン化物の酸素による燃焼では、80
0〜1500℃、好ましくは900〜1300℃の温度
条件が採用される。蒸気状有機ハロゲン化物の燃焼は、
酸化触媒の存在下で行うことができ、この場合の酸化触
媒としては、従来公知のものが用いられ、銀、チタン、
マンガン、鉄、銅、ニッケル、コバルト等の金属及びそ
の酸化物等がある。
In the method for burning a liquid organic halide according to the present invention, the reaction step includes a step of releasing a vaporized halide with increased combustibility from a solid composition by heating;
It consists of a combustion process of the released vaporous halide. Therefore, when implementing the present invention, it can be implemented using a combustion furnace provided with a heating chamber and a combustion chamber, and the conditions of the heating chamber and the combustion chamber can be changed. In this case, the heating for releasing the vaporous organic halide from the solid composition is carried out at 800-1500°C, preferably at 850°C.
Temperature conditions of ˜1200° C. are employed, and this heating is generally carried out in the presence of oxygen, although the presence of oxygen is not necessarily required. Next, in the combustion of vaporous organic halides from solid compositions with oxygen, 80
Temperature conditions of 0 to 1500°C, preferably 900 to 1300°C are employed. The combustion of vaporous organic halides is
It can be carried out in the presence of an oxidation catalyst, and in this case, conventionally known oxidation catalysts are used, such as silver, titanium,
These include metals such as manganese, iron, copper, nickel, and cobalt, and their oxides.

本発明を工業的に実施する場合、そあ燃焼炉は、必ずし
も前記したように加熱室と燃焼室の2つの室に区画する
必要はなく、実際には、1つの燃焼室を備えたものを用
いて実施することができる。
When the present invention is carried out industrially, the combustion furnace does not necessarily need to be divided into two chambers, a heating chamber and a combustion chamber, as described above, and in fact, a combustion furnace with one combustion chamber may be used. It can be implemented using

即ち、この場合には、前記した固体状組成物の加熱によ
る蒸気状有機ハロゲン化物の放出と、その蒸気状有機ハ
ロゲン化物の酸素による燃焼は同一の燃焼室で行われる
。本発明を工業的に実施する場合の燃焼炉としては、縦
型及び横型のいずれの方式、好ましくは、ロータリーキ
ルン型のものが使用され、供給原料としての前記固体状
組成物は、粉体状、ペレット状、塊状等の任意の形状で
炉内に供給することができる。
That is, in this case, the above-described release of the vaporous organic halide by heating the solid composition and the combustion of the vaporous organic halide with oxygen are performed in the same combustion chamber. When the present invention is carried out industrially, a combustion furnace of either a vertical type or a horizontal type, preferably a rotary kiln type, is used, and the solid composition as a feedstock is in the form of a powder, It can be fed into the furnace in any form such as pellets or lumps.

実施例 (1)固体状組成物の調製 以下の表−2に示す配合量を有する成分の処理剤がPC
B入りトランスオイルの固定化処理に供された。
Example (1) Preparation of solid composition The processing agent containing the ingredients shown in Table 2 below is PC.
It was used for fixing B-containing transformer oil.

表−2 PCB人リトランスオイールの組成は表−3に記述する
ものであった。
Table 2 The composition of the PCB human retrans oil was as described in Table 3.

表−3 小型のミキサーに200グラムの表−2に示す処理剤を
投入し、水40ccを添加して攪拌し発熱反応を起させ
た。約20秒で142℃に達した後に、PCB入りトラ
ンスオイル100グラムを投入し、攪拌を継続した。約
2分後に温度を測定すると96°Cであった。
Table 3 200 grams of the processing agent shown in Table 2 was placed in a small mixer, and 40 cc of water was added and stirred to cause an exothermic reaction. After the temperature reached 142° C. in about 20 seconds, 100 grams of transformer oil containing PCB was added and stirring was continued. The temperature was measured after about 2 minutes and was 96°C.

温度測定後、更に1分間攪拌し、粉状となったものを取
り出した。この温度は82°Cであった。この粉状物を
風乾し、常温とした後、PCB A溶出試験を行った。
After measuring the temperature, the mixture was further stirred for 1 minute and the powdered mixture was taken out. This temperature was 82°C. After air-drying this powder and bringing it to room temperature, a PCBA elution test was conducted.

試験方法は昭和48年環境庁告示第13号(イ)に従っ
た。その結果、有機ハロゲン化物の溶出は見られなかっ
た。
The test method was in accordance with the Environment Agency Notification No. 13 (a) of 1972. As a result, no elution of organic halides was observed.

(2)固体状組成物の燃焼炉処理 燃焼炉としては、図面に示した構造のもの、即ち、長さ
1500mm、内径261nI11のアルミナ反応管1
の周囲に電熱コイルを巻成して形成した燃焼室a(長さ
700mm)と、その辷流側に同じく電熱コイルを巻成
して形成した加熱室b(長さ200mm)を有するもの
を用いた。
(2) Combustion furnace treatment of solid composition The combustion furnace has the structure shown in the drawing, that is, an alumina reaction tube 1 with a length of 1500 mm and an inner diameter of 261 nI11.
A combustion chamber A (length 700 mm) formed by winding an electric heating coil around the combustion chamber A and a heating chamber B (length 200 mm) formed by winding an electric heating coil on the flow side thereof is used. there was.

前記(1)で得た固体状組成物(粉体)の試料の熱処理
を行うために、先ず、燃焼室aを所定の温度まで昇温さ
せた後、加熱室す内に燃焼ボートに採取した試料を押込
む。次に空気を空気ボンベ8から流量計7及びライン6
を経て、蓋体4内に挿入した導管5の先端からアルミナ
反応管1の内部に、約5分間定速で吹込んだ後、加熱室
すの昇温を開始する。加熱室すを1000℃まで昇温し
、その温度を約10分間保持した後、空気を流しながら
、加熱室すと燃焼室aとを放冷する。この場合の熱処理
条件は表−4に示した通りで・ある。また、加熱室すの
平均昇温速度は15〜b 燃焼排ガス中からのPCBの捕集は、環境庁通達「気相
PCB測定要領J(1972)に準じて行った。即ち、
図面に示すように、アルミナ反応管lの先端から出た排
ガスを管9を通して空ビン11に導入した後、10%N
a011150mΩを入れた洗気ビン12に通気洗浄し
、次いで、n−ヘキサンをそれぞれ150m Q入れた
2本の洗気ビン13.14を順次通し、フロリジ力ル力
ラム15を通して大気に放出する。なお、各ビン11.
12、13及び14はいずれもウォーターバス(1〜5
℃)により冷却した。
In order to heat-treat the sample of the solid composition (powder) obtained in (1) above, first, the combustion chamber a was heated to a predetermined temperature, and then the sample was collected in a combustion boat inside the heating chamber. Push in the sample. Next, air is supplied from the air cylinder 8 to the flow meter 7 and the line 6.
After blowing into the alumina reaction tube 1 from the tip of the conduit 5 inserted into the lid 4 at a constant rate for about 5 minutes, the temperature of the heating chamber is started to rise. After raising the temperature of the heating chamber to 1000° C. and maintaining that temperature for about 10 minutes, the heating chamber and combustion chamber a are allowed to cool while flowing air. The heat treatment conditions in this case are as shown in Table 4. In addition, the average temperature increase rate of the heating chamber was 15~b. Collection of PCBs from combustion exhaust gas was carried out in accordance with the Environmental Agency's notification ``Gas phase PCB measurement procedure J (1972)''.
As shown in the drawing, the exhaust gas coming out from the tip of the alumina reaction tube 1 is introduced into the empty bottle 11 through the tube 9, and then 10% N
A0111150 mΩ is placed in the air washing bottle 12 for ventilation cleaning, then two air washing bottles 13 and 14 each containing 150 mQ of n-hexane are passed in sequence, and the air is discharged to the atmosphere through the Florigi force ram 15. Note that each bottle 11.
12, 13 and 14 are all water baths (1 to 5
℃).

(3) PCl3の分析 試料及び熱処理残渣をn−ヘキサン200m (1で2
4時間ソックスレー抽出処理し、これに下記に示す処理
式を施して被検試料液(A)を得る。
(3) PCl3 analysis sample and heat treatment residue were mixed with 200 m of n-hexane (1 in 2
A Soxhlet extraction treatment was performed for 4 hours, and the treatment formula shown below was applied to obtain a test sample solution (A).

また、燃焼排ガス中のPCBを捕集した前記洗気ビン1
2の10%Na0II溶液と、前記洗気ビン13.14
のn−ヘキサンを分岐ロートに集める。次に、これらの
3本の洗気ビンと、空の洗気ビン11をそれぞれn−ヘ
キサン50mαで3回洗浄し、その洗浄液を前記分液ロ
ートに合せる。この分液ロートからのヘキサン層を下記
に示す処理Aを施して被検試料液(B)を得る。
In addition, the air washing bin 1 that collects PCBs in the combustion exhaust gas
2 10% Na0II solution and the air washing bottle 13.14
of n-hexane is collected in a branch funnel. Next, these three air washing bottles and the empty air washing bottle 11 are each washed three times with 50 mα of n-hexane, and the washing liquid is added to the separating funnel. The hexane layer from this separating funnel is subjected to treatment A shown below to obtain a test sample solution (B).

〔処理A〕[Processing A]

n−ヘキサン層を精製水200m Qで2回洗浄し、無
水硫酸ナトリウムで脱水後、KD濃縮器で約5mQ以下
に濃縮する。この濃縮n−ヘキサン層を25m Qの試
験管に採り、IN −KOH・エタノール5mQを加え
、はげしく振とうした後、−昼夜放置する。これにエタ
ノールの3倍量の精製水を加え、振とう静置後、上層の
n−ヘキサンを分取する。このn−ヘキサン層を0.I
NKOI+及び精製水で洗浄後、フロリジ力ル力ラムを
通してクリーンアップする。次に、このカラムをエチル
エーテルで溶出し、溶出したエチルエーテル・ヘキサン
層をにD濃縮器で3+nQまで濃縮する。
The n-hexane layer is washed twice with 200 mQ of purified water, dehydrated with anhydrous sodium sulfate, and concentrated to about 5 mQ or less using a KD concentrator. This concentrated n-hexane layer was taken into a 25 mQ test tube, 5 mQ of IN-KOH/ethanol was added thereto, and after vigorous shaking, it was left to stand for days and nights. Purified water in an amount three times that of ethanol is added to this, and after shaking and standing, the upper layer of n-hexane is separated. This n-hexane layer was I
After washing with NKOI+ and purified water, clean up by passing through a Floridian power ram. Next, this column is eluted with ethyl ether, and the eluted ethyl ether/hexane layer is concentrated to 3+nQ using a D concentrator.

前記のようにして得た被検試料液を’tcp −GC分
析にかけてその中に含まれるPCBを測定した。
The test sample solution obtained as described above was subjected to 'tcp-GC analysis to measure PCBs contained therein.

また、前記分液ロートから得た10%Na1l1層に含
まれる塩素分をJISに0102に従って測定した。
Further, the chlorine content contained in the 10% Na11 layer obtained from the separating funnel was measured according to JIS 0102.

(4)実験結果 前記pcnの測定結果を前記表−4に示した実験番号に
対応させて表−5に示す。
(4) Experimental Results The measurement results of the pcn are shown in Table 5 in correspondence with the experiment numbers shown in Table 4 above.

表−5 また、前記塩素分析の結果を、前記表−4の実験番号と
対応させて表−6に示す。なお、表−6の排ガス中の塩
素値の後にカッコで示した数値は、その塩素分の試料中
全塩素に対する割合(%)を示す。
Table 5 The results of the chlorine analysis are shown in Table 6 in correspondence with the experiment numbers in Table 4. Note that the numerical value shown in parentheses after the chlorine value in the exhaust gas in Table 6 indicates the ratio (%) of the chlorine content to the total chlorine in the sample.

なお、この実験では、加熱温度を1000〜1200℃
で滞留時間2〜5秒の条件で行ったが、滞留時間を長く
とることによって、その加熱温度を低下させることがで
きる。
In addition, in this experiment, the heating temperature was set at 1000 to 1200°C.
Although the heating was carried out under conditions of a residence time of 2 to 5 seconds, the heating temperature can be lowered by increasing the residence time.

表−6 〔効  果〕 前記表−5に示された結果かられかるように、本発明に
よれば、PCBは完全分解されて無害化されることが明
らかである。しかも、本発明の場合。
Table 6 [Effects] As can be seen from the results shown in Table 5 above, it is clear that according to the present invention, PCBs are completely decomposed and rendered harmless. Moreover, in the case of the present invention.

その実施は容易であり、従来、PCBの元金分解が燃焼
処理法で非常に困難であったことを考えると。
It is easy to implement, considering that conventionally it has been extremely difficult to decompose PCBs into their original form using combustion treatment methods.

本発明の産業的意義は多大である。The industrial significance of the present invention is enormous.

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

図面は本発明を実施する場合に用いた装置系統図を示す
。 1・・・アルミナ反応管、2,3・・・電熱コイル、7
・・・流量計、8・・・空気ボンベ、a・・・燃焼室、
b・・・加熱室。 指定代理人 工業技術院化学技術研究所長藤堂尚之
The drawings show a system diagram of an apparatus used to carry out the present invention. 1... Alumina reaction tube, 2, 3... Electric heating coil, 7
...flow meter, 8...air cylinder, a...combustion chamber,
b...Heating chamber. Designated Agent: Naoyuki Todo, Director, Institute of Chemical Technology, Agency of Industrial Science and Technology

Claims (1)

【特許請求の範囲】[Claims] (1)液状有機ハロゲン化物を、あらかじめ、該液状有
機ハロゲン化物と、水酸化カルシウム及び/又は水酸化
マグネシウムと、水溶性高分子と、有機酸金属塩と、珪
酸塩と、増量剤とからなる固体状組成物とした後、該固
体状組成物を、酸素の存在又は不存在下、高温に加熱す
ると共に、該固体状組成物から放出された蒸気状有機ハ
ロゲン化物を、酸素で燃焼させることを特徴とする液状
有機ハロゲン化物の燃焼処理方法。
(1) A liquid organic halide is prepared in advance from the liquid organic halide, calcium hydroxide and/or magnesium hydroxide, a water-soluble polymer, an organic acid metal salt, a silicate, and an extender. After forming the solid composition, heating the solid composition to a high temperature in the presence or absence of oxygen, and burning the vaporous organic halide released from the solid composition with oxygen. A method for combustion treatment of liquid organic halides, characterized by:
JP60202444A 1985-09-12 1985-09-12 Combustion method for liquid organic halides Granted JPS6262119A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60202444A JPS6262119A (en) 1985-09-12 1985-09-12 Combustion method for liquid organic halides

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60202444A JPS6262119A (en) 1985-09-12 1985-09-12 Combustion method for liquid organic halides

Publications (2)

Publication Number Publication Date
JPS6262119A true JPS6262119A (en) 1987-03-18
JPS648242B2 JPS648242B2 (en) 1989-02-13

Family

ID=16457624

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60202444A Granted JPS6262119A (en) 1985-09-12 1985-09-12 Combustion method for liquid organic halides

Country Status (1)

Country Link
JP (1) JPS6262119A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01131676A (en) * 1987-08-11 1989-05-24 Yonezawa Kagaku Kogyo Kk Treatment method for making organic halide compound harmless
WO1995014509A1 (en) * 1993-11-29 1995-06-01 Eimatsu Kanzaki Detoxifying method for polychlorobiphenyl
JP2009513480A (en) * 2005-08-26 2009-04-02 クナツプ,ジヨン・エル Energy generation method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01131676A (en) * 1987-08-11 1989-05-24 Yonezawa Kagaku Kogyo Kk Treatment method for making organic halide compound harmless
WO1995014509A1 (en) * 1993-11-29 1995-06-01 Eimatsu Kanzaki Detoxifying method for polychlorobiphenyl
JP2009513480A (en) * 2005-08-26 2009-04-02 クナツプ,ジヨン・エル Energy generation method

Also Published As

Publication number Publication date
JPS648242B2 (en) 1989-02-13

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