JPH10263504A - Method for solidifying material to be treated and solidified material - Google Patents
Method for solidifying material to be treated and solidified materialInfo
- Publication number
- JPH10263504A JPH10263504A JP9069392A JP6939297A JPH10263504A JP H10263504 A JPH10263504 A JP H10263504A JP 9069392 A JP9069392 A JP 9069392A JP 6939297 A JP6939297 A JP 6939297A JP H10263504 A JPH10263504 A JP H10263504A
- Authority
- JP
- Japan
- Prior art keywords
- treated
- chlorine
- temperature
- dechlorinating agent
- treated product
- 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
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Landscapes
- Processing Of Solid Wastes (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は廃棄物等の処理物を
加熱して固形化処理する方法、およびこの方法により形
成された固形化物に関し、特に、処理物に脱塩素剤を混
入して固形化処理する方法および固形化物に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for heating and treating solidified products such as wastes, and a solidified product formed by this method. The present invention relates to a method of performing a chemical conversion treatment and a solidified product.
【0002】[0002]
【従来の技術】都市ゴミ等の処理物は年々その量が増加
し、その処理が問題となっている。都市ゴミは一般的
に、一般家庭とかオフィス等から処理物として排出され
可燃性のものが主となっている。最近ではこの可燃性の
処理物を単に焼却処理するのではなく、資源として有効
に利用することが考えられ、一旦処理物を固形化し、こ
れを燃料として再利用することも行われている。しか
し、処理物の中には、近年多種多様な化学物質、例え
ば、塩化ビニル樹脂を多く含んだプラスチック類や、オ
フィスで使用される紙の塩素漂白剤のように、多量の塩
素成分を含んだ物質が混入しているため、単に固形化し
ただけでは、燃料として使用し燃焼される際、有害な塩
素系ガスが発生し、そのまま大気に放出すると大気汚染
をきたし、環境上好ましくない結果をもたらす。従っ
て、高効率でクリーンなエネルギー資源としての再利用
には問題があり、これに対処した技術の開発が重要な課
題となっている。2. Description of the Related Art The amount of processed waste such as municipal garbage increases year by year, and its disposal has become a problem. In general, municipal garbage is mainly discharged from general households or offices as flammable waste. Recently, it has been considered that this flammable treated material is not simply incinerated, but is effectively used as a resource, and the treated material is once solidified and reused as fuel. However, some of the processed materials contain a large amount of chlorine components in recent years, such as a wide variety of chemical substances, for example, plastics containing a large amount of vinyl chloride resin and chlorine bleach for office paper. Due to the inclusion of substances, simply solidifying will generate harmful chlorine-based gas when used and burned as fuel, and if released directly into the atmosphere, it will cause air pollution and have undesirable environmental consequences . Therefore, there is a problem in reusing as a high-efficiency and clean energy resource, and development of a technology corresponding to this problem has become an important issue.
【0003】[0003]
【発明が解決しようとする課題】処理物を加熱処理する
際に問題となるのは、処理物中に含まれる塩素成分の処
理であり、焼却過程でガス化した塩素系ガス(塩化水
素、塩素ガス)は、フィルタ等で吸着処理して大気中に
塩素系ガスが排出されないようにしている。A problem that arises when heat-treating a treated product is the treatment of chlorine components contained in the treated product, and the chlorine-based gas (hydrogen chloride, chlorine chloride) gasified in the incineration process. Gas) is subjected to an adsorption treatment with a filter or the like so that chlorine-based gas is not discharged into the atmosphere.
【0004】一方、加熱過程でガス化しなかった塩素成
分は処理灰と結合してしまい、高濃度の塩素成分を含有
した処理灰となる。[0004] On the other hand, chlorine components that have not been gasified during the heating process are combined with the treated ash, resulting in treated ash containing a high concentration of chlorine components.
【0005】このように処理灰に塩素成分が含有してい
ると、処理灰を燃料資源として再利用することは困難で
あり、もっぱら地中に埋設することで処理されている。[0005] If the treated ash contains a chlorine component as described above, it is difficult to reuse the treated ash as a fuel resource, and the ash is treated only by burying it in the ground.
【0006】そのため、処理灰を再利用する場合には、
事前に処理物を分別して塩素系ガスの発生の少ない処理
物のみ選別して焼却処理し、その処理灰(残渣)を燃料
として又はブロック等に固形化して再利用することが行
われている。Therefore, when reusing the treated ash,
Processed materials are separated in advance, only processed materials that generate less chlorine-based gas are selected and incinerated, and the processed ash (residue) is solidified as fuel or in a block or the like and reused.
【0007】しかし、処理物の分別を行うことは効率が
悪く、しかも、資源回収率も低いことから、塩素成分を
効果的に除去する技術の確立が望まれている。[0007] However, since the separation of the treated material is inefficient and the resource recovery rate is low, it is desired to establish a technique for effectively removing the chlorine component.
【0008】また、処理物(ゴミ)を固形化して燃料と
して利用することも行われているが、現状では、単に可
燃性の処理物を圧縮固形化する程度のものであり、ある
程度の減量化は達成できるが、燃料として使用する場合
は、前記と同様に、有害な塩素系ガスを発生し、その対
策が必要となっている。[0008] Further, it is also practiced to solidify the processed material (garbage) and use it as a fuel. However, at present, the flammable processed material is simply compressed and solidified. Can be achieved, but when used as a fuel, harmful chlorine-based gas is generated in the same manner as described above, and countermeasures are required.
【0009】本発明はこのような課題に鑑みなされたも
ので、その目的は燃焼させても塩素系ガス(塩化水素、
塩素ガス)を発生させない処理物の固形化処理方法と、
その固形化物を提供するにある。SUMMARY OF THE INVENTION The present invention has been made in view of the above problems, and its object is to produce a chlorine-based gas (hydrogen chloride,
A solidification treatment method for a treated material that does not generate chlorine gas);
It is to provide the solidified product.
【0010】[0010]
【課題を解決するための手段】本願の発明者らは、数々
の実験調査の結果、処理物に含まれる塩素成分と、アル
カリ金属水酸化物を脱塩素剤として処理物に適量混入
し、所定の温度で加熱処理すると、所定の温度で塩素成
分が分解して有害な塩素系ガスを発生し、この有害な塩
素系ガスと脱塩素剤とが反応して無害な塩化物を生成
し、ガスおよび残渣中には有害な塩素系ガス成分が残存
しないことを見い出した。As a result of numerous experimental investigations, the inventors of the present application have found that a proper amount of a chlorine component and an alkali metal hydroxide contained in a treated material is mixed into the treated material as a dechlorinating agent, When the heat treatment is performed at a temperature of, the chlorine component is decomposed at a predetermined temperature to generate harmful chlorine-based gas, and the harmful chlorine-based gas reacts with the dechlorinating agent to generate harmless chloride, and the gas is removed. It was also found that no harmful chlorine-based gas components remained in the residue.
【0011】また、加熱処理時に脱塩素剤を添加して処
理することで、脱塩素効果をねらった処理をしているこ
とに着目し、燃料として使用される固形化物(ペレッ
ト)を製作する際に、脱塩素剤を混入して製作すること
に着目した。Attention is also paid to the fact that a dechlorinating agent is added during the heat treatment to perform a treatment aimed at the dechlorination effect. In addition, we focused on manufacturing by mixing a dechlorinating agent.
【0012】発明者らは、まず、脱塩素効果のある物質
の探索をし、且つ同物質をペレットに混入して焼却した
場合の効果を調査した。[0012] The inventors first searched for a substance having a dechlorination effect, and investigated the effect of mixing the substance into pellets and burning it.
【0013】本発明はこれらの実験調査に基づいてなさ
れたもので、脱塩素剤を混入して処理物を固形化して、
これを燃料として焼却したとき、有害な塩素系ガスを発
生させない固形化燃料を得ることができた。The present invention has been made based on these experimental investigations, in which a treated product is solidified by mixing a dechlorinating agent,
When this was incinerated as a fuel, a solidified fuel that did not generate harmful chlorine-based gas could be obtained.
【0014】本発明において、処理物を固形化する処理
方法は、処理物と、塩素系ガスと反応するアルカリ金属
水酸化物の脱塩素剤とを混合して複数温度域で加熱処理
し、生成された生成物を加圧成形してペレット状に固形
化することを特徴とするものである。[0014] In the present invention, the treatment method for solidifying the treated material is to mix the treated material with a dechlorinating agent for an alkali metal hydroxide that reacts with a chlorine-based gas and heat-treat the mixture in a plurality of temperature ranges to produce The obtained product is subjected to pressure molding and solidified into a pellet.
【0015】このときの加熱処理時の温度は、塩素系ガ
スの析出が始まる温度(200〜300℃)以下で前処
理し、ついで300〜500℃で塩素系ガスを析出させ
ると共に脱塩素剤と反応させて無害な塩化物を生成させ
る。At this time, the temperature at the time of the heat treatment is not more than the temperature (200 to 300 ° C.) at which the precipitation of the chlorine-based gas starts, and then the chlorine-based gas is precipitated at 300 to 500 ° C. Reacts to produce harmless chloride.
【0016】そして、生成物を造粒機により圧縮成型し
て固形化物(ペレット)を形成する。または、生成物に
さらに脱塩素剤を添加してペレットを形成する。The product is compression-molded by a granulator to form a solidified product (pellet). Alternatively, a dechlorinating agent is further added to the product to form pellets.
【0017】本発明に使用される脱塩素剤としては、 (1)アルカリ金属水酸化物の単体、2種類以上の単
体、2種類以上の単体の混合物から選択したもの。As the dechlorinating agent used in the present invention, (1) an alkali metal hydroxide selected from a simple substance, two or more simple substances, and a mixture of two or more simple substances.
【0018】(2)水酸化ナトリウム、水酸化カリウ
ム、水酸化リチウム、水酸化ルビジウム、水酸化セシウ
ムから選択した単体、2種類以上の単体、2種類以上の
単体の混合物から適宜選択して使用する。(2) A simple substance selected from sodium hydroxide, potassium hydroxide, lithium hydroxide, rubidium hydroxide, and cesium hydroxide, a mixture of two or more simple substances, and a mixture of two or more simple substances are appropriately used. .
【0019】添加量は、処理される処理物と当量又は5
〜30重量%、又は発生する塩素系ガスに対して0.5
〜1.5モルを添加する。The amount of addition is equivalent to the processed material to be treated or 5 equivalents.
To 30% by weight, or 0.5 to the generated chlorine-based gas
Add ~ 1.5 mol.
【0020】また、固形物を製造する際の加圧力は、加
圧力が小さいと固形化が困難であり、加圧が大きいと設
備が大がかりとなる等の理由から10〜1000kg/
cm2が好適である。The pressing force for producing a solid is 10 to 1000 kg / kg for reasons such as solidification is difficult if the pressing force is small, and the equipment becomes large if the pressing force is large.
cm 2 is preferred.
【0021】以上の条件により処理物中に脱塩素剤を添
加して加熱処理すると、例えば、水酸化ナトリウム(N
aOH)を添加した場合には、塩化水素(HCl)と反
応して、次のようになる。When a dechlorinating agent is added to the treated product under the above-mentioned conditions and heat treatment is performed, for example, sodium hydroxide (N
When aOH) is added, it reacts with hydrogen chloride (HCl) to give:
【0022】 (NaOH)+(HCl)→(NaCl)+(H2O) このように塩化水素は水酸化ナトリウムと反応して、残
渣の一部となる塩化ナトリウム(NaCl)と、水分
(H2 O)になり、ダイオキシンの原因の一因となる塩
素水素ガスを生成することはなく、排ガスおよび残渣の
無害化が実現できる。(NaOH) + (HCl) → (NaCl) + (H 2 O) As described above, hydrogen chloride reacts with sodium hydroxide to form sodium chloride (NaCl), which is a part of the residue, and water (H). 2 O) and does not generate chlorine-hydrogen gas, which is a cause of dioxin, and can achieve detoxification of exhaust gas and residues.
【0023】一方、残渣にも有害な塩素系ガス成分は含
まれておらず、しかもNaClは水などの溶液で簡単に
溶解除去できるので、洗浄後に残った炭化物質は燃料等
として有効利用できる。On the other hand, no harmful chlorine-based gas components are contained in the residue, and NaCl can be easily dissolved and removed with a solution such as water, so that the carbonized material remaining after washing can be effectively used as fuel or the like.
【0024】なお、洗浄後の処理液には、有害な塩素系
ガス成分はほとんど含有していないので、そのまま、又
は塩素成分以外の別の有害物質の除去後に河川、海洋に
排出することが可能となる。Since the treated liquid after cleaning contains almost no harmful chlorine-based gas components, it can be discharged to rivers and oceans as it is or after removing other harmful substances other than chlorine components. Becomes
【0025】[0025]
【発明の実施の形態】以下、本発明の実施の形態を図面
によって説明する。Embodiments of the present invention will be described below with reference to the drawings.
【0026】図1は本発明の実施の形態の概念図で、1
は処理物供給部、2は混合機、3は脱塩素剤供給部を示
す。4は加熱手段で、混合機2内の処理物を加熱する。
この加熱手段4は、ガス加熱、電気加熱又は燃焼加熱,
マイクロ波加熱,誘導加熱等のいずれの加熱手段でもよ
い。FIG. 1 is a conceptual diagram of an embodiment of the present invention.
Denotes a processing material supply unit, 2 denotes a mixer, and 3 denotes a dechlorinating agent supply unit. Reference numeral 4 denotes a heating means for heating the processed material in the mixer 2.
The heating means 4 includes gas heating, electric heating or combustion heating,
Any heating means such as microwave heating and induction heating may be used.
【0027】5は造粒機で外部に加熱手段6を有し、内
部には加圧ローラ等から成るプレス手段を備えている。
7は造粒機5で成形された固形化物(ペレット)を示
す。Reference numeral 5 denotes a granulator having a heating means 6 on the outside and a press means comprising a pressure roller and the like inside.
Reference numeral 7 denotes a solidified product (pellet) formed by the granulator 5.
【0028】ペレットを製造する手順は、まず、処理物
を処理物供給部1に投入し、脱塩素剤供給部3に脱塩素
剤を収容して、これらを所定の割合で混合機2に供給す
る。混合機2では、処理物と脱塩素剤と混合しながら、
加熱処理手段4で加熱(乾留)処理する。(加熱処理は
造粒機内で行ってもよい)加熱処理は少なくとも加熱温
度域の異なる2段階以上で行い。前段よりも後段の温度
域を高くする。The procedure for manufacturing the pellets is as follows. First, the processed material is charged into the processed material supply unit 1, the dechlorinating agent is stored in the dechlorinating agent supply unit 3, and these are supplied to the mixer 2 at a predetermined ratio. I do. In the mixing machine 2, while mixing the processed material and the dechlorinating agent,
The heating (dry distillation) treatment is performed by the heating means 4. (The heat treatment may be performed in a granulator.) The heat treatment is performed in at least two or more stages having different heating temperature ranges. The temperature range of the latter stage is made higher than that of the former stage.
【0029】加熱処理は、まず、図2に示すように、3
00℃以下、好ましくは150℃〜250℃の温度で外
気を遮断した状態で10分間加熱処理(乾留)する。次
いで、前行程より高温の300〜600℃(好ましくは
400〜500℃)で加熱処理して処理物から塩素系ガ
スを析出させ、且つ添加した脱塩素剤と反応されて無害
な塩化物を生成させる。As shown in FIG.
A heat treatment (dry distillation) is performed at a temperature of 00 ° C. or less, preferably 150 ° C. to 250 ° C., with the outside air shut off for 10 minutes. Next, a heat treatment is performed at 300 to 600 ° C. (preferably 400 to 500 ° C.), which is higher than that in the previous step, to precipitate a chlorine-based gas from the processed product, and to react with the added dechlorinating agent to produce harmless chloride. Let it.
【0030】次に、混合機2の開閉扉2bを開き、混合
物を造粒機5に供給し、この造粒機5で混合物を前記と
同様の温度条件で加熱しながらプレス手段で圧縮成形
し、ペレット7を形成する。なお、混合機2に破砕機能
を付加してもよい。Next, the opening / closing door 2b of the mixer 2 is opened, the mixture is supplied to the granulator 5, and the mixture is compression-molded by press means while heating the mixture under the same temperature conditions as described above. Then, a pellet 7 is formed. The crushing function may be added to the mixer 2.
【0031】上記の行程において処理物内にプラスチッ
ク類が混入していると、プラスチック類は軟化した状態
で処理物と混合され、そして成形されるので、処理物間
の接着剤(バインダ)としての役目を果し、製造された
パレットは安定した固体形状を維持する。In the above process, if plastics are mixed in the processed material, the plastics are mixed with the processed material in a softened state, and are molded, so that the plastics serve as an adhesive (binder) between the processed materials. Acting, the pallets produced maintain a stable solid form.
【0032】プレス手段としては、例えば、混合物を送
り出す送り回転ローラと圧縮成形する絞り回転ローラ
(加熱ローラとしてもよい)とを備え、送り回転ローラ
間の間隔を調整して加圧力を100〜1000kg/c
m2に調整する。この加圧力が小さいと固形化が困難と
なり、また大きすぎると設備が大がかりとなる。The pressing means includes, for example, a feed rotary roller for feeding out the mixture and a squeezing rotary roller (which may be a heating roller) for compression molding. / C
to adjust to the m 2. If the pressure is small, solidification is difficult, and if it is too large, the equipment becomes large.
【0033】このように圧縮成形することにより、ペレ
ットの体積比は次のように減量化される。By performing the compression molding in this manner, the volume ratio of the pellet is reduced as follows.
【0034】[0034]
【表1】 [Table 1]
【0035】以上の処理方法で固形化処理した処理物を
燃料として使用し、燃焼させる処理物が含有する塩素成
分は次に示す実験の結果、発生するであろう有害な塩素
系ガスは無害な塩化物を生成して、排ガス及び残渣には
有害な塩素系ガス成分は含まれていないことが判明し
た。Using the processed material solidified by the above-described processing method as a fuel, the chlorine component contained in the processed material to be burned is determined to be harmless by the following experiment. Chloride was generated, and it was found that the exhaust gas and the residue did not contain harmful chlorine-based gas components.
【0036】実験は、排気管付きで、開閉扉を有する密
閉容器にて低酸素雰囲気を作り、この密閉容器に試料を
入れ、電気炉にて加熱し、250℃から600℃まで5
0℃間隔で各温度にて5分間保持し、昇温時、キープ時
で塩化水素ガス(HCl)濃度(ppm)を測定する。In the experiment, a low-oxygen atmosphere was created in a closed vessel having an exhaust pipe and an opening / closing door.
Hold at each temperature for 5 minutes at intervals of 0 ° C., and measure the concentration (ppm) of hydrogen chloride gas (HCl) at the time of temperature rise and at the time of keep.
【0037】ガス濃度の測定は、JIS−K0804に
規定されている検知管によって測定した。The gas concentration was measured with a detector tube specified in JIS-K0804.
【0038】表1にこの測定結果を示す。表1におい
て、塩化水素ガス濃度は実験10回における測定値で実
施例1および2は最高値、比較例1〜比較例4は最低値
を示す。Table 1 shows the measurement results. In Table 1, the concentration of hydrogen chloride gas is a measured value in ten experiments, Examples 1 and 2 show the highest values, and Comparative Examples 1 to 4 show the lowest values.
【0039】なお“ND”は“検出されず”を表し、1
0回の実験でいずれも検出されなかったことを示す。Note that "ND" represents "not detected" and 1
It shows that none was detected in 0 experiments.
【0040】[0040]
【表2】 [Table 2]
【0041】実験は、先ず塩素成分を多量に含有するポ
リ塩化ビニリデンのみを処理物として予備実験を行っ
た。表1中の比較例1と比較例2は同じ処理物の各1
g,4gに脱塩素剤を添加しない予備実験用の試料とし
た。In the experiment, first, a preliminary experiment was conducted using only polyvinylidene chloride containing a large amount of a chlorine component as a treated material. Comparative Example 1 and Comparative Example 2 in Table 1 are each 1
g and 4 g were used as samples for preliminary experiments in which no dechlorinating agent was added.
【0042】比較例3は同じ処理物4gに従来の脱塩素
剤である消石灰の粉末20gを添加した試料、比較例4
は同じ処理物4gに脱塩素剤として炭酸カルシウムを添
加した試料とした。Comparative Example 3 is a sample obtained by adding 20 g of slaked lime powder as a conventional dechlorinating agent to 4 g of the same treated product.
Was a sample obtained by adding calcium carbonate as a dechlorinating agent to 4 g of the same treated product.
【0043】次に本発明による脱塩素処理の実施例とし
て、処理物としてのポリ塩化ビニリデン4gに脱塩素剤
として粉砕した水酸化ナトリウム20gを添加した試料
を実施例1とし、同じ処理物に脱塩素剤として粉砕した
水酸化カリウム20gを添加した試料を実施例2とし
た。脱塩素剤として平均粒径が100μmの粉体を用い
た。Next, as an example of the dechlorination treatment according to the present invention, a sample in which 20 g of pulverized sodium hydroxide was added as a dechlorinating agent to 4 g of polyvinylidene chloride as a processed material was referred to as Example 1, and the sample was subjected to dechlorination. A sample to which 20 g of ground potassium hydroxide was added as a chlorine agent was used as Example 2. Powder having an average particle size of 100 μm was used as a dechlorinating agent.
【0044】表1に示した実験結果から以下のように考
察される。The following is considered from the experimental results shown in Table 1.
【0045】先ず、塩素成分を多量に含んでいるポリ塩
化ビニリデンのみを用いて予備試験を行った結果、比較
例1,2に示すように、熱処理により塩化水素が多量に
発生している。First, a preliminary test was conducted using only polyvinylidene chloride containing a large amount of a chlorine component. As a result, as shown in Comparative Examples 1 and 2, a large amount of hydrogen chloride was generated by the heat treatment.
【0046】次に、従来の脱塩素剤である消石灰及び炭
酸カルシウムを添加した比較例3,4は、比較例1,2
に較べて塩化水素の発生がかなり抑制されてはいるもの
の、まだ十分であるとは言えない。Next, Comparative Examples 3 and 4, in which slaked lime and calcium carbonate, which are conventional dechlorinating agents, were added, Comparative Examples 1 and 2 were used.
However, although the generation of hydrogen chloride is considerably suppressed, it is still not sufficient.
【0047】これに対して上記処理物に、脱塩素剤とし
てアルカリ金属水酸化物である水酸化ナトリウムと水酸
化カリウムを添加した実施例1,2は、実施例1におけ
る温度が350℃及び450℃における昇温時と、実施
例2における温度が450℃の5分キープ時に僅かな塩
化水素ガスの発生が見られたが、全温度範囲に渡って塩
化水素ガスが検出されず、きわめて良好な結果が得られ
た。従って本実施例によれば、比較例1〜4に較べ非常
に良好な結果が得られた。On the other hand, in Examples 1 and 2 in which sodium hydroxide and potassium hydroxide as alkali metal hydroxides were added as dechlorinating agents to the above treated products, the temperatures in Example 1 were 350 ° C. and 450 ° C. Although slight generation of hydrogen chloride gas was observed when the temperature was raised at 5 ° C. and when the temperature in Example 2 was kept at 450 ° C. for 5 minutes, hydrogen chloride gas was not detected over the entire temperature range, and it was very good. The result was obtained. Therefore, according to this example, very good results were obtained as compared with Comparative Examples 1 to 4.
【0048】なお、600℃以上1000℃の温度にお
いても同様の効果が得られた。The same effect was obtained at a temperature between 600 ° C. and 1000 ° C.
【0049】水酸化ナトリウムが塩素系ガスと反応する
と、ガスおよび残渣の無害化が実現できる理由は、次の
ように有害な塩化系ガスが無害な塩化物に置換生成され
ることによる。When sodium hydroxide reacts with chlorine-based gas, detoxification of gas and residue can be realized because harmful chloride-based gas is replaced with harmless chloride as follows.
【0050】ここで水酸化ナトリウム(NaOH)を脱
塩素剤として用いて処理物中に添加した場合の反応は、
前記したように水酸化ナトリウムが塩化水素(HCl)
との間で以下の反応式が進行する。Here, when sodium hydroxide (NaOH) is used as a dechlorinating agent and added to the processed product, the reaction is as follows:
As described above, sodium hydroxide is converted to hydrogen chloride (HCl).
The following reaction formula proceeds between and.
【0051】 (NaOH)+(HCl)→(NaCl)+(H2 O) このように水酸化ナトリウムは塩化水素と反応して無害
な塩化ナトリウムと水を生成する。(NaOH) + (HCl) → (NaCl) + (H 2 O) Thus, sodium hydroxide reacts with hydrogen chloride to produce harmless sodium chloride and water.
【0052】水酸化カリウム(KOH)を用いた場合の
反応式は、 (KOH)+(HCl)→(KCl)+(H2 O) として水酸化カリウムは塩化水素と反応して無害な塩化
カリウムと水になる。When potassium hydroxide (KOH) is used, the reaction formula is as follows: (KOH) + (HCl) → (KCl) + (H 2 O) Potassium hydroxide reacts with hydrogen chloride and is harmless potassium chloride And become water.
【0053】一方、反応により生成したNaClは無害
な塩化物であり、このNaClは水などの溶液により洗
浄処理することにより効果的に除去できる。On the other hand, NaCl produced by the reaction is a harmless chloride, and this NaCl can be effectively removed by washing with a solution such as water.
【0054】図3はこの処理灰を洗浄処理する説明図
で、処理灰を水槽に入れ、所定時間(約30分間)撹拌
して塩化ナトリウム(NaCl)を水に溶解し、処理灰
から取り除く、次に、これを脱水、乾燥して固形化す
る。洗浄後は有益な炭化物質が残る。FIG. 3 is an explanatory view for washing the treated ash. The treated ash is put into a water tank, and stirred for a predetermined time (about 30 minutes) to dissolve sodium chloride (NaCl) in water and to remove it from the treated ash. Next, this is dehydrated and dried to be solidified. After cleaning, valuable carbonized material remains.
【0055】以上のことから、該脱塩素剤中に塩素成分
と反応して無害な塩化物を生成するアルカリ金属水酸化
物が存在すれば塩化ナトリウムとか塩化カリウムとして
残渣の一部となり、ダイオキシンの発生原因の1つであ
る塩化水素が生成することがなく、これらの残渣と排ガ
スの無害化をはかることができる。上記以外の脱塩素剤
である水酸化リチウム、水酸化ルビジウム、水酸化セシ
ウムを使用しても同様な結果が得られる。From the above, if an alkali metal hydroxide that reacts with a chlorine component to form harmless chlorides in the dechlorinating agent is present, it becomes a part of the residue as sodium chloride or potassium chloride, and dioxin Hydrogen chloride, which is one of the causes, is not generated, and the residue and exhaust gas can be made harmless. Similar results can be obtained by using other dechlorinating agents such as lithium hydroxide, rubidium hydroxide and cesium hydroxide.
【0056】このことから、脱塩素剤としては、上記と
同様の反応を示す次の物質が使用できる。From the above, the following substances showing the same reaction as described above can be used as the dechlorinating agent.
【0057】(1)アルカリ金属水酸化物の単体、2種
類以上の単体、2種類以上の単体の混合物から選択した
もの。(1) An alkali metal hydroxide selected from a simple substance, two or more simple substances, and a mixture of two or more simple substances.
【0058】(2)水酸化ナトリウム、水酸化カリウ
ム、水酸化リチウム、水酸化ルビジウム、水酸化セシウ
ムから選択した単体、2種類以上の単体、2種類以上の
単体の混合物から選択したもの。(2) A simple substance selected from sodium hydroxide, potassium hydroxide, lithium hydroxide, rubidium hydroxide and cesium hydroxide, a mixture of two or more simple substances, and a mixture of two or more simple substances.
【0059】一方、反応によりNaClとかKClが生
成されるが、生成したNaCl,KClは無害な塩化物
であり、水などの溶液による洗浄処理により効果的に除
去でき、洗浄後には、再利用可能な炭化物質が残る。こ
れを造粒機でペレット状に形成すれば、燃料として有効
利用が可能となる。On the other hand, NaCl and KCl are produced by the reaction, and the produced NaCl and KCl are harmless chlorides, which can be effectively removed by washing treatment with a solution such as water, and can be reused after washing. The remaining carbonized material remains. If this is formed into pellets by a granulator, it can be effectively used as fuel.
【0060】また、残渣の特性により、残渣を分離手段
等により各物質に分離し、分離後の物質を乾燥し固形化
して燃料又はその他有効に活用することができる。Further, depending on the characteristics of the residue, the residue can be separated into various substances by a separation means or the like, and the separated substance can be dried and solidified to be used as fuel or other effectively.
【0061】なお、洗浄後の処理液には、有害な物質は
ほとんど含まれていないので、そのまま河川又は海洋に
放流することができる。Since the treatment liquid after washing contains almost no harmful substances, it can be discharged to rivers or oceans as it is.
【0062】なお、残渣中の残留塩素成分をイオンクロ
マトグラフィで測定した結果、比較例1〜4では、10
00ppm以上あったものが、本発明では確認されず、
無害な塩化物(NaCl)が確認された。The residual chlorine component in the residue was measured by ion chromatography.
What was not less than 00 ppm was not confirmed in the present invention,
Harmless chloride (NaCl) was identified.
【0063】[0063]
【発明の効果】以上のように本発明は、処理物に脱塩素
剤を混合して、まず、塩素系ガスが析出する温度以下の
低温で熱処理し、次いで、高温に加熱処理し、これを加
圧して固形化物(ペレット)を形成するようにしたの
で、 (1)固形化物を燃焼したときに塩素系ガス(塩化水
素、塩素ガス)の発生がない安全なペレットが得られ
る。As described above, according to the present invention, a treated product is mixed with a dechlorinating agent, first heat-treated at a low temperature below the temperature at which chlorine-based gas is precipitated, and then heat-treated at a high temperature. Since the solidified material (pellet) is formed by pressurizing, (1) a safe pellet free of generation of chlorine-based gas (hydrogen chloride, chlorine gas) when burning the solidified material is obtained.
【0064】(2)ペレットの製造過程においても、発
生するガス中の有害な塩素系ガスは脱塩素剤と反応して
無害な塩化物に生成されるので、排気ガス中の有害な塩
素系物質は効果的に除去でき、排ガスはそのまま大気中
に放出してもダイオキンの発生は防止される。(2) Even in the process of producing pellets, harmful chlorine-based gas in the exhaust gas is generated because harmful chlorine-based gas in the generated gas reacts with the dechlorinating agent to form harmless chloride. Can be effectively removed, and the generation of Diokin is prevented even if the exhaust gas is directly discharged into the atmosphere.
【0065】(3)以上の理由により、取り扱いの便利
な固形化燃料として有効に再利用できる。(3) For the above reasons, it can be effectively reused as a solidified fuel which is convenient to handle.
【0066】等の効果を奏する。The following effects are obtained.
【図1】本発明の実施の形態の概念図。FIG. 1 is a conceptual diagram of an embodiment of the present invention.
【図2】本発明の処理方法の説明図。FIG. 2 is an explanatory diagram of a processing method of the present invention.
【図3】処理灰の処理説明図。FIG. 3 is an explanatory diagram of the processing of the processing ash.
1…処理物供給部 2…混合機 3…脱塩素剤供給部 4,6…加熱手段 5…造粒機 7…ペレット DESCRIPTION OF SYMBOLS 1 ... Process supply part 2 ... Mixer 3 ... Dechlorinating agent supply part 4, 6 ... Heating means 5 ... Granulator 7 ... Pellets
Claims (13)
リ金属水酸化物の脱塩素剤とを混合して複数温度域で加
熱処理し、生成された生成物をペレット状に固形化する
ことを特徴とする処理物の固形化処理方法。1. A process wherein a treated product and a dechlorinating agent for an alkali metal hydroxide that reacts with a chlorine-based gas are mixed and heat-treated in a plurality of temperature ranges, and the produced product is solidified into pellets. A method for solidifying a treated product, characterized by the following.
域を高くし、前段の温度域は、塩素系ガスの析出が始ま
る温度とし、該温度を所定時間保持することを特徴とす
る請求項1記載の処理物の固形化処理方法。2. The heat treatment temperature range is set higher in a temperature range in a latter stage than in a former stage, and the temperature range in a former stage is a temperature at which chlorine-based gas starts to be deposited, and the temperature is maintained for a predetermined time. Item 6. A method for solidifying a treated product according to Item 1.
300℃としたことを特徴とする請求項1又は2に記載
の処理物の固形化処理方法。3. The temperature range before the heat treatment is 200 ° C.
The method according to claim 1, wherein the temperature is set to 300 ° C. 4.
域を高くし、後段の温度域は析出した塩素系ガスが脱塩
素剤に固定される温度とし、該温度を所定時間保持する
ことを特徴とする請求項1記載の処理物の固形化処理方
法。4. The heat treatment temperature range is set higher in the latter stage than in the former stage, and the latter temperature range is set to a temperature at which the deposited chlorine-based gas is fixed to the dechlorinating agent, and the temperature is maintained for a predetermined time. The method for solidifying a treated product according to claim 1, wherein:
〜500℃としたことを特徴とする請求項1又は4に記
載の処理物の固形化処理方法。5. The temperature range of the latter stage of the heat treatment is 300 ° C.
The method for solidifying a treated product according to claim 1 or 4, wherein the temperature is set to 500C.
を特徴とする請求項1ないし5のいずれか1項に記載の
処理物の固形化処理方法。6. The method according to claim 1, wherein the heat treatment is performed in a low oxygen atmosphere.
体、2種類以上の単体、2種類以上の単体の混合物から
選択したことを特徴とする請求項1記載の処理物の固形
化処理方法。7. The solidification treatment of a treated product according to claim 1, wherein the dechlorinating agent is selected from a simple substance of an alkali metal hydroxide, a mixture of two or more simple substances, and a mixture of two or more simple substances. Method.
カリウム、水酸化リチウム、水酸化ルビジウム、水酸化
セシウムから選択した単体、2種類以上の単体、2種類
以上の単体の混合物から選択したことを特徴とする請求
項1記載の処理物の固形化処理方法。8. The dechlorinating agent is selected from a simple substance selected from sodium hydroxide, potassium hydroxide, lithium hydroxide, rubidium hydroxide and cesium hydroxide, a mixture of two or more simple substances, and a mixture of two or more simple substances. The method for solidifying a treated product according to claim 1, wherein:
粉体状、溶液、懸濁液の何れかで形成したことを特徴と
する請求項1,7,8のいずれか1項に記載の処理物の
固形化処理方法。9. The dechlorinating agent may be in the form of a block, a plate, a porous,
The solidification treatment method for a treated product according to any one of claims 1, 7, and 8, wherein the treatment product is formed in the form of a powder, a solution, or a suspension.
物の5〜30重量%であることを特徴とする請求項1,
7,8,9のいずれか1項に記載の処理物の固形化処理
方法。10. The method according to claim 1, wherein the amount of the dechlorinating agent is 5 to 30% by weight of the processed material.
The solidification treatment method for a treated product according to any one of 7, 8, and 9.
分量に対して0.5〜1.5モルであることを特徴とす
る請求項1,7,8,9のいずれか1項に記載の処理物
の固形化処理方法。11. The method according to claim 1, wherein the dechlorinating agent is added in an amount of 0.5 to 1.5 mol based on the amount of the generated chlorine component. 3. A method for solidifying a treated product according to item 1.
kg/cm2としたことを特徴とする請求項1記載の処
理物の固形化処理方法。12. The pressure for pressure molding is 100 to 1000.
2. The method for solidifying a treated product according to claim 1, wherein the solid content is set to kg / cm 2 .
カリ金属水酸化物の脱塩素剤とを混合して複数温度域で
熱処理し、生成された生成物を加圧成形してペレット状
に固形化したことを特徴とする処理物の固形化物。13. A mixture of a treated product and a dechlorinating agent for an alkali metal hydroxide which reacts with a chlorine-based gas, heat-treated in a plurality of temperature ranges, and press-formed the resulting product into pellets. A solidified processed product characterized by being solidified.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9069392A JPH10263504A (en) | 1997-03-24 | 1997-03-24 | Method for solidifying material to be treated and solidified material |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9069392A JPH10263504A (en) | 1997-03-24 | 1997-03-24 | Method for solidifying material to be treated and solidified material |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH10263504A true JPH10263504A (en) | 1998-10-06 |
Family
ID=13401295
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP9069392A Pending JPH10263504A (en) | 1997-03-24 | 1997-03-24 | Method for solidifying material to be treated and solidified material |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH10263504A (en) |
-
1997
- 1997-03-24 JP JP9069392A patent/JPH10263504A/en active Pending
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP2000015635A (en) | Method for dechlorination of waste and method and apparatus for producing dechlorinated fuel | |
JPH10235313A (en) | Solidification treatment of object to be treated and solidified matter | |
JPH10263504A (en) | Method for solidifying material to be treated and solidified material | |
JPH10263503A (en) | Method of solidifying material to be treated and solidified material | |
CN115947977A (en) | Method for degrading plastics | |
JPH10244237A (en) | Solidifying method for material to be treated and solidified material | |
JP2008207044A (en) | Detoxification method of solid containing organohalogen compound | |
JPH10263502A (en) | Solidifying treatment of treating product and solidified product | |
KR100341551B1 (en) | Noxious Component Removal Process and Noxious Component Removal Agent Therefor | |
JP2933047B2 (en) | Solidification treatment method of treated material | |
JPH1110109A (en) | Method for solidification treatment of treating material and solidified material | |
JP2985819B2 (en) | Solidification of waste | |
JP2003260438A (en) | Method for treating molten slag, apparatus therefor and inorganic structural material | |
JPH1110108A (en) | Method for solidification of material to be treated and solidified material | |
JPH10235310A (en) | Solidification treatment of object to be treated and solidified matter | |
JPH1110110A (en) | Method for solidification treatment of material to be treated and solidified matter | |
JP2002274900A (en) | Method of producing cement raw material and the cement raw material | |
JP2000303084A (en) | Method for treating chlorine-containing plastic waste | |
JP3497056B2 (en) | Solidification treatment method of treated material | |
JPH11116979A (en) | Solid fuel and its manufacture | |
JP2001270962A (en) | Method for manufacturing dechlorinated resin and refining method | |
JPH10235187A (en) | Dechlorination agent | |
JP2000044970A (en) | Method for solidifying matter to be treated, and solidified matter | |
JP3090056B2 (en) | Waste dechlorination method | |
JP6651900B2 (en) | Treatment method for chlorine-containing incinerated ash |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20040827 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20040831 |
|
A02 | Decision of refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A02 Effective date: 20050111 |