JPH0249775B2 - - Google Patents
Info
- Publication number
- JPH0249775B2 JPH0249775B2 JP57047119A JP4711982A JPH0249775B2 JP H0249775 B2 JPH0249775 B2 JP H0249775B2 JP 57047119 A JP57047119 A JP 57047119A JP 4711982 A JP4711982 A JP 4711982A JP H0249775 B2 JPH0249775 B2 JP H0249775B2
- Authority
- JP
- Japan
- Prior art keywords
- cement
- exhaust gas
- powder
- gas
- hardened
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
Landscapes
- Treating Waste Gases (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Description
本発明は活性廃棄物または下水汚泥を焼却処理
する際排出する酸性物質含有の排ガス、あるいは
通常の工業用燃焼炉からの排ガス中より酸性物質
を乾式で除去する除去方法に関するものである。
生活廃棄物または下水汚泥は従来埋立用、海洋
投棄または焼却などにより廃棄処理されていた
が、近時埋立用地の不足または海洋汚染防止など
のために、これらの処理は次第に困難になつて来
た。それ故これらの処理は焼却するより他に手段
がなくなつて来た。しかるに廃棄物や下水汚泥を
焼却すれば、SO2,SO3,Cl2,HCl,HFおよび
H2Sなどの酸性ガスが発生し、これらのガスに起
因する公害問題が問題となるので、これらのガス
の除去を行う必要がある。またエネルギー源の不
足から硫黄含有量の多い燃料の使用を余儀なくさ
れているので、排ガス中の脱硫処理は益々必要に
なつて来た。従つて安価で簡便に実施できる排ガ
ス中の酸性物質の除去方法の開発が急務になつて
いる。
本発明者は排ガス中の酸性物質を乾式で除去せ
んとして除去剤について種々研究した結果、セメ
ントと石灰石粉及び/又はドロマイト粉との混合
物に水を添加して硬化体を造り、これを所望の粒
度に破砕するか、あるいはセメントと石灰石粉及
び/又はドロマイト粉との混合物を水を媒体とし
てパンペレタイザー、押し出し成形機等で所望の
粒度に、造粒し、その後加湿条件下で養生して造
つた硬化体は接触界面が大きく、その硬化体の構
成鉱物は主としてCaO―SiO2―H2O系ゲル、Ca
(OH)2および未反応粒子であつて、CaO―SiO2
―H2O系ゲルおよびCa(OH)2は100〜600℃に加
熱されると分解し、多孔質の非晶質物および遊離
のCaOとになり、生成した遊離のCaOおよび非晶
質物は化学的に優れた活性を示すので、比較的低
温な排ガス中の酸性物質に対しても除去性能が大
であり、更にセメントにより石灰石粉、ドロマイ
ト粉を分散硬化させた酸性物質除去剤は高温での
排ガス中の酸性物質の除去性能が特に大であるこ
とを知見した。
次に本発明を実験例に基いて説明する。
普通ポルトランドセメント、珪石粉(径0.5mm
以下)、石灰石粉(径0.5mm以下)、ドロマイト粉
(径0.5mm以下)を使用し、次表に記した割合に混
合し、水を加えて硬化せしめ、養生温度20±3
℃、養生湿度(R.H.%)80%以上で7日間養生
し、セメント硬化体(40×40×160mm)を造つた。
The present invention relates to a method for dry removal of acidic substances from exhaust gas containing acidic substances discharged when activated waste or sewage sludge is incinerated, or from exhaust gas from a normal industrial combustion furnace. Domestic waste or sewage sludge has traditionally been disposed of by landfilling, ocean dumping, or incineration, but these treatments have become increasingly difficult in recent years due to lack of landfill space and efforts to prevent marine pollution. . Therefore, there is now no other way to dispose of these materials other than incineration. However, if waste and sewage sludge are incinerated, SO 2 , SO 3 , Cl 2 , HCl, HF and
Acidic gases such as H 2 S are generated and pollution problems caused by these gases become a problem, so it is necessary to remove these gases. Furthermore, because fuels with high sulfur content have been forced to be used due to lack of energy sources, desulfurization treatment of exhaust gas has become increasingly necessary. Therefore, there is an urgent need to develop a method for removing acidic substances from exhaust gas that is inexpensive and easy to implement. As a result of various researches on removal agents in an attempt to remove acidic substances in exhaust gas by dry method, the present inventor added water to a mixture of cement and limestone powder and/or dolomite powder to create a hardened material, and this was used to form a hardened material. Either by crushing to a desired particle size, or by granulating a mixture of cement and limestone powder and/or dolomite powder to the desired particle size using a pan pelletizer, extruder, etc. using water as a medium, and then curing it under humidified conditions. The ivy hardened body has a large contact interface, and the constituent minerals of the hardened body are mainly CaO-SiO 2 -H 2 O gel, Ca
(OH) 2 and unreacted particles, CaO―SiO 2
- When H 2 O gel and Ca(OH) 2 are heated to 100-600℃, they decompose into porous amorphous material and free CaO, and the generated free CaO and amorphous material are chemically As it shows excellent activity, it has great removal performance even for acidic substances in exhaust gas at relatively low temperatures.Furthermore, acidic substance removers made by dispersing and hardening limestone powder and dolomite powder with cement are effective at high temperatures. It was found that the removal performance of acidic substances in exhaust gas is particularly high. Next, the present invention will be explained based on experimental examples. Ordinary Portland cement, silica powder (diameter 0.5mm
(below), limestone powder (diameter 0.5 mm or less), and dolomite powder (diameter 0.5 mm or less) are mixed in the proportions shown in the table below, hardened by adding water, and cured at a temperature of 20 ± 3.
C. and curing humidity (RH%) of 80% or higher for 7 days to produce a hardened cement body (40 x 40 x 160 mm).
【表】
上記硬化体を10mm以下に破砕後、110℃で24時
間乾燥し、ついで破砕して0.59〜1.19mmの粒子に
調整した。このようにして造つた硬化体の破砕物
100gを固定床に充填し、SO2ガスを含有する下
記組成のガスの脱硫試験を行つた。なお、比較の
ため、石灰石及びドロマイトをそれぞれ上記硬化
体の破砕物と同一粒度に破砕・粒調したものを用
いて同様な試験を行つた。これらは実験番号5及
び6とする。
ガス組成:SO2700ppm、O25%
CO212%、残りN2
ガス流量:25/min
固定床断面積:56.7cm2
ガス温度:600℃、900℃
脱硫酸(%)は
入口SO2濃度−出口SO2濃度/入口SO2濃度×100で求めた
この実験結果を添付図面に示す。
図より了解されるように、本発明品(実験番号
3、4)は同日に出願したセメントクリンカを水
中養生した酸性物質除去剤よりも脱硫性能が優れ
ていることが認められ、800〜1000℃特に900℃で
の脱硫性能が一層向上することが認められた。こ
れに較べ、石灰石粒(実験番号5)、ドロマイト
粒(実験番号6)では脱硫率は短時間で低下して
しまう。これは、セメントにより分散硬化させた
多孔質の石灰石粉、ドロマイト粉硬化体とは異な
り、密実な粒であるため、表層のみしか反応が進
まないためと考えられる。なお、セメントと珪酸
粉を使用した実験番号2のものはセメントのみの
もの(実験番号1)よりも600、800、900℃のい
ずれの温度でも脱硫率が小さいことが分る。
本発明はこれらの知見に基づくものであつて、
その構成は、セメントと、石灰石粉及び/又はド
ロマイト粉との混合物を水の存在下で硬化せしめ
て得た硬化体を破砕したものに、又は上記混合物
を水を媒体として造粒し、硬化させた硬化体に、
800〜1000℃の排ガスを接触させることを特徴と
する。
本発明において、セメントとしては普通ポルト
ランドセメント、早強ポルトランドセメント等の
各種ポルトランドセメント、または高炉セメン
ト、シリカセメント、フライアツシユセメント等
の混合セメントが使用される。
なお、800〜1000℃の排ガスを処理するにはセ
メント:石灰石粉及び/又はドロマイト粉の重量
比は1:1〜1:5が好ましい。上記重量比が5
が越えるとき急激に硬化体の強度が低下するので
好ましくない。
次に使用する石灰石粉及び/又はドロマイト粉
は本発明の除去剤の製造方法、処理すべきガスの
組成等により異なるが、一般には0.5mm以下が好
ましい。特に押し出し成形機により造粒するとき
は0.1mm以下にすることが好ましい。
なお、上記実験例では排ガス中のSO2ガスの除
去の場合のみを記載したが、SO3,Cl2,HCl,
HFおよびH2Sなどの酸性ガスが含有されている
場合にもSO2ガスと同様に除去することができ
る。
本発明の方法に用いる硬化体、すなわち酸性物
質除去剤は安価であり、除去効果が大であつて長
期間の使用に耐えるので、本発明の工業的価値は
非常に大である。[Table] The cured product was crushed into particles of 10 mm or less, dried at 110°C for 24 hours, and then crushed to obtain particles of 0.59 to 1.19 mm. Crushed hardened material made in this way
A fixed bed was filled with 100 g of the gas, and a desulfurization test was conducted using a gas having the following composition containing SO 2 gas. For comparison, similar tests were conducted using limestone and dolomite, each of which had been crushed to the same particle size as the crushed material of the above-mentioned hardened material. These will be experiment numbers 5 and 6. Gas composition: SO 2 700ppm, O 2 5% CO 2 12%, remaining N 2 Gas flow rate: 25/min Fixed bed cross-sectional area: 56.7cm 2 Gas temperature: 600℃, 900℃ Desulfation (%) is inlet SO 2 The results of this experiment, determined by concentration - outlet SO 2 concentration / inlet SO 2 concentration x 100, are shown in the attached drawing. As can be seen from the figure, the products of the present invention (experiment numbers 3 and 4) were found to have better desulfurization performance than the acidic substance remover for cement clinker cured in water, which was applied on the same day. In particular, it was observed that the desulfurization performance at 900°C was further improved. In comparison, the desulfurization rate decreases in a short time with limestone grains (experiment number 5) and dolomite grains (experiment number 6). This is thought to be because, unlike porous limestone powder and hardened dolomite powder, which are dispersed and hardened with cement, the particles are dense, so the reaction progresses only in the surface layer. In addition, it can be seen that the desulfurization rate of Experiment No. 2 using cement and silicate powder was lower than that of cement only (Experiment No. 1) at all temperatures of 600, 800, and 900°C. The present invention is based on these findings, and
Its composition is made by curing a mixture of cement and limestone powder and/or dolomite powder in the presence of water and crushing the hardened material, or by granulating the above mixture using water as a medium and hardening it. To the cured body,
It is characterized by contacting exhaust gas at 800 to 1000℃. In the present invention, as the cement, various Portland cements such as ordinary Portland cement and early strength Portland cement, or mixed cements such as blast furnace cement, silica cement, and fly ash cement are used. In addition, in order to treat exhaust gas at 800 to 1000°C, the weight ratio of cement:limestone powder and/or dolomite powder is preferably 1:1 to 1:5. The above weight ratio is 5
is not preferable because the strength of the cured product decreases rapidly when it exceeds. The limestone powder and/or dolomite powder to be used next varies depending on the method for producing the removing agent of the present invention, the composition of the gas to be treated, etc., but is generally preferably 0.5 mm or less. In particular, when granulating using an extrusion molding machine, it is preferable that the particle size is 0.1 mm or less. In addition, in the above experimental example, only the case of removing SO 2 gas from exhaust gas was described, but SO 3 , Cl 2 , HCl,
Even if acidic gases such as HF and H 2 S are contained, they can be removed in the same way as SO 2 gas. The cured product used in the method of the present invention, that is, the acidic substance removing agent, is inexpensive, has a large removal effect, and can be used for a long period of time, so the present invention has great industrial value.
図面は本発明の酸性物質除去剤を使用して種々
の温度における排ガスの脱硫試験を行なつた結果
を表わすもので、脱硫時間と脱硫率との関係を示
すものである。
The drawings show the results of exhaust gas desulfurization tests at various temperatures using the acidic substance remover of the present invention, and show the relationship between desulfurization time and desulfurization rate.
Claims (1)
粉との混合物を水の存在下で硬化せしめて得た硬
化体を破砕したものに、又は上記混合物を水を媒
体として造粒し、硬化させた硬化体に、800〜
1000℃の排ガスを接触させることを特徴とする排
ガス中の酸性物質除去方法。1 A hardened product obtained by curing a mixture of cement and limestone powder and/or dolomite powder in the presence of water, or a hardened product obtained by granulating the above mixture using water as a medium and hardening it. From 800 to
A method for removing acidic substances from exhaust gas, which is characterized by contacting exhaust gas at 1000°C.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57047119A JPS58166932A (en) | 1982-03-26 | 1982-03-26 | Removing agent for acidic material in waste gas |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57047119A JPS58166932A (en) | 1982-03-26 | 1982-03-26 | Removing agent for acidic material in waste gas |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS58166932A JPS58166932A (en) | 1983-10-03 |
| JPH0249775B2 true JPH0249775B2 (en) | 1990-10-31 |
Family
ID=12766268
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57047119A Granted JPS58166932A (en) | 1982-03-26 | 1982-03-26 | Removing agent for acidic material in waste gas |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS58166932A (en) |
Families Citing this family (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6297640A (en) * | 1985-10-25 | 1987-05-07 | Hokkaido Electric Power Co Inc:The | Manufacturing method of desulfurization and denitrification agent |
| JPS61209038A (en) * | 1985-03-13 | 1986-09-17 | Hokkaido Electric Power Co Inc:The | Preparation of absorbent for desulfurization and denitration |
| GB2172277B (en) * | 1985-03-13 | 1989-06-21 | Hokkaido Electric Power | Preparation process of desulfurizing and denitrating agents |
| DE3611769A1 (en) * | 1986-04-08 | 1987-10-15 | Ytong Ag | METHOD AND DEVICE FOR PURIFYING EXHAUST GASES |
| JPS62254824A (en) * | 1986-04-28 | 1987-11-06 | Hokkaido Electric Power Co Inc:The | Production of treating agent for flue gas |
| JPH0655256B2 (en) * | 1986-07-02 | 1994-07-27 | 三菱重工業株式会社 | Dry exhaust gas treatment method |
| JPH0655257B2 (en) * | 1988-12-05 | 1994-07-27 | 三菱重工業株式会社 | Dry exhaust gas treatment method |
| JP2629042B2 (en) * | 1989-03-14 | 1997-07-09 | 北海道電力 株式会社 | Method for producing exhaust gas treating agent |
| US5403808A (en) * | 1993-07-07 | 1995-04-04 | Case Western Reserve University | Sorbents for flue gas desulfurization |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS56158249A (en) * | 1980-05-09 | 1981-12-05 | Kaou Kueekaa Kk | Acidic gas capturing material in gas produced from mold |
-
1982
- 1982-03-26 JP JP57047119A patent/JPS58166932A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS58166932A (en) | 1983-10-03 |
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