JP5434149B2 - Highly reactive and low adhesion slaked lime and method for producing the same - Google Patents

Highly reactive and low adhesion slaked lime and method for producing the same Download PDF

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JP5434149B2
JP5434149B2 JP2009052626A JP2009052626A JP5434149B2 JP 5434149 B2 JP5434149 B2 JP 5434149B2 JP 2009052626 A JP2009052626 A JP 2009052626A JP 2009052626 A JP2009052626 A JP 2009052626A JP 5434149 B2 JP5434149 B2 JP 5434149B2
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雅典 佐藤
英子 明石
礼佳 岡田
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Yoshizawa Lime Industry Co Ltd
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Description

本発明は、主としてゴミ焼却場で排ガスから酸性ガスを吸収除去するために使用する消石灰であって、とくに反応性が高く、しかも、消石灰を輸送する配管やバグフィルター濾布などの機器への付着性が低いものに関し、その製造方法にも関する。 The present invention is slaked lime mainly used for absorbing and removing acidic gas from exhaust gas at a garbage incineration plant, and is particularly reactive, and adheres to equipment such as piping and bag filter filter cloth for transporting slaked lime. It relates also to the manufacturing method with respect to the thing with low property.

ゴミ焼却場から出る排ガス中の、塩化水素や硫黄酸化物などの酸性ガスを吸着除去する目的で、煙道に反応性の高い消石灰を吹き込む処理が行なわれている。この消石灰としては、JIS特号が広く使用されているが、消石灰の使用量を低減し、かつ発生する飛灰の量を低減するため、比表面積を高めるとともに細孔容積を増大して、酸性ガスとの反応性を高めたものが要望されている。 For the purpose of adsorbing and removing acidic gases such as hydrogen chloride and sulfur oxides in the exhaust gas from the garbage incineration plant, a highly reactive slaked lime is blown into the flue. As this slaked lime, JIS special name is widely used. In order to reduce the amount of slaked lime used and to reduce the amount of fly ash generated, the specific surface area is increased and the pore volume is increased. What has improved the reactivity with gas is desired.

この要望にこたえて、いわゆる「高反応性消石灰」が提供されているが、反応性の高い消石灰に関しては、流動性が悪い、輸送配管に付着しやすい、バグフィルターにおける差圧上昇が著しい、などの問題がしばしば発生している。そこで、高反応性消石灰のもつこのような特性が引き起こすトラブルを解消することを意図して、つぎに挙げるような種々の試みがなされている。 In response to this request, so-called “high-reactivity slaked lime” has been provided, but for highly reactive slaked lime, the fluidity is poor, it tends to adhere to transport piping, the differential pressure rise in the bag filter is significant, etc. The problem often occurs. Therefore, various attempts as described below have been made with the intention of eliminating the trouble caused by such characteristics of highly reactive slaked lime.

その一つは消石灰に付着性を低減する物質を混合することであって、「低付着性消石灰およびそれに改質する方法」(特許文献1)は、消石灰に生石灰を重量で98:2〜70:30の割合で混合し、グリコール類、グリコールエーテル類またはエタノールアミン類から選んだ少なくとも1種の添加剤を特定量添加することを開示している。 One of them is mixing slaked lime with a substance that reduces adhesion, and “low adhesion slaked lime and a method for modifying it” (Patent Document 1) is 98: 2 to 70 by weight of quick lime. : Mixing at a ratio of 30 and adding a specific amount of at least one additive selected from glycols, glycol ethers or ethanolamines.

同じ発明の名称を冠して提案されたいまひとつの技術(特許文献2)は、消石灰に対し、生石灰に加えてパルプ類を添加すること、および添加により得られた混合物を、電磁マイクロ波の照射により加熱処理することを提案している。 Another technique (Patent Document 2) proposed with the title of the same invention is that, in addition to quick lime, pulp is added to slaked lime, and the mixture obtained by addition is irradiated with electromagnetic microwaves. It is proposed to heat-treat.

さらに、やはり同じ発明の名称をになう提案(特許文献3)は、上記いずれかの消石灰組成物に対して、マイクロ波を照射して1〜30分間加熱することにより、付着性のいっそうの改善ができることを教示している。 Furthermore, the proposal (patent document 3) which also becomes the name of the same invention is still more adhesive by irradiating one of the above slaked lime compositions with microwaves and heating for 1 to 30 minutes. Teaching that improvements can be made.

これらとは別の改良策として、「付着性改善消石灰」(特許文献4)は、消石灰に重量で1〜5%のパーライト粉末を添加することを開示している。パーライト粉末は、平均粒径が50μm以下のものが好ましいという。この技術は、有機物の添加が消石灰の用途を制限する、という問題に対処できることが取り柄であるという。 As an improvement measure different from these, "Adhesion-improving slaked lime" (Patent Document 4) discloses that 1 to 5% by weight of pearlite powder is added to slaked lime. The pearlite powder preferably has an average particle size of 50 μm or less. The technology is said to be able to cope with the problem that the addition of organic substances limits the use of slaked lime.

原料となる生石灰に注目した対策は、「付着抑制型消石灰」(特許文献5)として、活性度が20〜150mL、好ましくは40〜100mLの生石灰を消化したものを提案している。この活性度は、粒度10〜3mmの生石灰50gを、指示薬としてフェノールフタレインを加えた水2リットル中に投入し、撹拌しながら4Nの塩酸を滴下しながら、溶液が僅かに赤色を呈する状態を維持して、5分間経過したときの塩酸消費量(mL)であらわす。
特開平8−73216 特開平8−73217 特開平8−109016 特開2003−252621 特開2006−273600
The countermeasure which paid attention to the quick lime used as a raw material has proposed what digested quick lime whose activity is 20-150 mL, Preferably 40-100 mL as "adhesion suppression type | mold slaked lime" (patent document 5). The activity is such that 50 g of quick lime having a particle size of 10 to 3 mm is put into 2 liters of water to which phenolphthalein is added as an indicator, and 4N hydrochloric acid is added dropwise with stirring, so that the solution is slightly red. It is expressed as the hydrochloric acid consumption (mL) after 5 minutes.
JP-A-8-73216 JP-A-8-73217 JP-A-8-109016 JP 2003-252621 A JP 2006-273600 A

しかし、上記した対応策は、その効果はかならずしも高いとはいえないし、コスト的に現実的とはいえないものもある、といった難点がある。さらに、高反応性消石灰の使用に伴う諸問題は、当然なことではあるが、個々のゴミ焼却場の設備や操業の条件と密接な関係があり、ある工場では問題がなくても、別の工場では大きな支障があるということが経験された。 However, the countermeasures described above are not necessarily highly effective, and there are drawbacks that some of them are not realistic in terms of cost. In addition, the problems associated with the use of highly reactive slaked lime are, of course, closely related to the facilities and operating conditions of individual garbage incineration plants. It was experienced that there was a big hindrance at the factory.

本発明の目的は、酸性ガスとの高い反応性を維持したまま、消石灰を輸送する配管やバグフィルター濾布などの機器への付着性が軽減され、どのようなゴミ焼却場においてもトラブルを生じることなく排ガス処理に使用できる、高反応性で付着性の低い消石灰を提供することにある。そのような消石灰を製造する方法を提供することもまた、本発明の目的に含まれる。ここで、消石灰の「輸送」は、乾式の気送と、湿式のスラリー液送の両方を包含する。 The object of the present invention is to reduce the adhesion to equipment such as piping and bag filter filter cloth for transporting slaked lime while maintaining high reactivity with acid gas, and causes troubles in any garbage incineration plant An object of the present invention is to provide slaked lime that is highly reactive and has low adhesion, which can be used for exhaust gas treatment without any problems. Providing a method for producing such slaked lime is also included in the object of the present invention. Here, “transport” of slaked lime includes both dry air feeding and wet slurry liquid feeding.

本発明の高反応性で付着性が低い消石灰は、炭酸化反応試験において、pH11に達する時間が10分以上、20分以下であることを特徴とする、炭酸化反応性が比較的低い消石灰である。炭酸化反応試験は、製品である消石灰と炭酸ガスとの反応性を調べるために出願人が確立した試験方法であって、消石灰を水に分散させて5重量%のスラリーを形成し、このスラリーを6,000rpmの高速で撹拌しつつ、そこに炭酸ガスを640mL/分の速度で吹き込み、pHが11に低下するまでの時間(分)を測定することからなる。この時間が短いほど、その消石灰は炭酸ガスとの反応性が高く、長いほど反応性が低い。一方、あまりに炭酸化反応性が低い消石灰は、炭酸ガス以外の酸性ガスとの反応性も低くなってしまうので、高反応性を維持するという観点から、20分以下という限界を設けた。 The slaked lime having high reactivity and low adhesion according to the present invention is a slaked lime with relatively low carbonation reactivity, characterized in that the time to reach pH 11 is 10 minutes or more and 20 minutes or less in the carbonation reaction test. is there. The carbonation reaction test is a test method established by the applicant for investigating the reactivity between slaked lime as a product and carbon dioxide gas, and slaked lime is dispersed in water to form a 5% by weight slurry. Is stirred at a high speed of 6,000 rpm, carbon dioxide gas is blown into it at a speed of 640 mL / min, and the time (min) until the pH drops to 11 is measured. The shorter this time, the higher the reactivity of the slaked lime with carbon dioxide, and the lower the time, the lower the reactivity. On the other hand, slaked lime with too low carbonation reactivity has low reactivity with acidic gases other than carbon dioxide gas, so a limit of 20 minutes or less is provided from the viewpoint of maintaining high reactivity.

高反応性で付着性が低い消石灰を製造する本発明の方法は、原料として、ASTM C110により定められた測定法(以下「ASTM法」と略称する)による水和活性度試験において30秒値が60℃以下であり、かつ、△T=180秒値−30秒値が15℃以上である生石灰を使用し、これを、連続消化装置に供給し、水にアルコール類およびエタノールアミン類からなるグループから選んだ1種または2種以上の添加剤を、消石灰100重量部に対して0.1〜5重量部の割合で添加したものを消化水として加えることを特徴とする製造方法である。 The method of the present invention for producing highly reactive and low adhesive slaked lime has a 30 second value as a raw material in a hydration activity test according to a measurement method defined by ASTM C110 (hereinafter abbreviated as “ASTM method”). Quick lime having a temperature of 60 ° C. or less and ΔT 2 = 180 seconds value−30 seconds value of 15 ° C. or more is used, and this is supplied to a continuous digester and consists of alcohols and ethanolamines in water. It is a manufacturing method characterized by adding one or two or more additives selected from a group at a ratio of 0.1 to 5 parts by weight with respect to 100 parts by weight of slaked lime as digestive water.

本発明の高反応性で付着性が低い消石灰を使用すれば、ゴミ焼却場の排ガスに含まれる酸性ガスを除去する性能として現われる高い反応性を維持したまま、使用時に、消石灰を輸送する配管やバグフィルター濾布などの機器に付着する度合が低く、配管閉塞やバグフィルター差圧の過度の上昇による操業停止などのトラブルを引き起こすことが少ないという利点が、確実に得られる。 If slaked lime with high reactivity and low adhesion of the present invention is used, piping that transports slaked lime at the time of use while maintaining the high reactivity that appears as the ability to remove acidic gas contained in the exhaust gas of the garbage incineration plant, The degree of adhesion to equipment such as bag filter cloth is low, and it is possible to surely obtain the advantage that troubles such as piping blockage and operation stoppage due to excessive increase of the bag filter differential pressure are less likely to occur.

本発明の高反応性で付着性が低い消石灰の製造方法によれば、炭酸化反応試験においてpH11に達する時間が10分以上、20分以下である性質を示す消石灰を、確実に製造することができる。本発明の消石灰は、圧縮空気にのせる気送の場合も、またスラリーにして液送する場合も、低い付着性を示すことが、実際のゴミ焼却場の運転において確認されている。 According to the method for producing slaked lime having high reactivity and low adhesion according to the present invention, it is possible to reliably produce slaked lime having a property that the time to reach pH 11 in the carbonation reaction test is 10 minutes or more and 20 minutes or less. it can. The slaked lime of the present invention has been confirmed in the operation of an actual incineration plant to exhibit low adhesion, both when it is put on compressed air and when it is sent as a slurry.

以下、本発明の完成に至る経過を述べて、上記の限定理由を説明するとともに、好適な実施態様を示す。まず、配管の閉塞トラブルを生じたゴミ焼却場から配管に固着した消石灰を入手して分析したところ、使用前に比べて、COの含有量が著しく増加していることがわかった。そこで発明者らは、消石灰の付着性とCOとの反応性に関係があると推測し、高反応性消石灰と、COとの反応性の関連を調べた。手順はつぎのとおりである。
1)水380gに消石灰20gを分散させ、5%水スラリーをつくる。
2)温度20℃で、この水スラリーを高速(6,000rpm)撹拌しながら、その中へ、COガスを、640mL/分の速度で吹き込む。
3)pH(スラリー形成時は12.0〜12.9)の径時変化を記録し、pHが11に低下するまでの時間(分)を記録する。その時間が短い方が、COとの反応性が高いことになる。(この試験方法が、前記した炭酸化反応試験にほかならない。)
In the following, the process leading to the completion of the present invention will be described, the reasons for limitation will be explained, and preferred embodiments will be shown. First, when obtaining and analyzing slaked lime fixed to a pipe from a garbage incineration site that caused a pipe clogging trouble, it was found that the content of CO 2 was remarkably increased compared to before use. Therefore inventors speculated to be related to the reactivity of the adhesion and CO 2 of slaked lime was investigated and highly reactive calcium hydroxide, the association of reactivity with CO 2. The procedure is as follows.
1) Disperse 20 g of slaked lime in 380 g of water to make a 5% water slurry.
2) While stirring the water slurry at a high temperature (6,000 rpm) at a temperature of 20 ° C., CO 2 gas is blown into the water slurry at a speed of 640 mL / min.
3) Record the change with time of pH (12.0 to 12.9 at the time of slurry formation) and record the time (minutes) until the pH drops to 11. The shorter the time, the higher the reactivity with CO 2 . (This test method is nothing but the carbonation reaction test described above.)

結果は図1に示すとおりであって、配管の閉塞が生じやすかった消石灰1種は「炭酸化反応性」が高い、すなわち炭酸化反応試験におけるpH低下時間が8分以下であり、一方、閉塞が生じにくかった消石灰2種は、11分以上と、明確な差が認められた。結局、上記した推測が当たっていたわけであって、配管の閉塞を招くことなく排ガスの処理を行なうためには、炭酸化反応試験におけるpH低下時間が10分以上である消石灰を使用すべきであることがわかった。 The results are as shown in FIG. 1, and one kind of slaked lime that is likely to cause clogging of the piping has a high “carbonation reactivity”, that is, the pH reduction time in the carbonation reaction test is 8 minutes or less, while clogging occurs. There was a clear difference between the two types of slaked lime that were difficult to produce, 11 minutes or longer. In the end, the above assumption was true, and slaked lime with a pH reduction time of 10 minutes or more in the carbonation reaction test should be used in order to treat exhaust gas without causing blockage of the piping. I understood it.

さらに発明者らは、消石灰の炭酸化反応性と固着性との関係を確認するために、つぎの実験を行なった。高反応性の消石灰100gずつをCOガスまたは加湿したCOガスにさらして炭酸化させた後(加湿したガスを使用するのは、炭酸化を促進するためである)、それから15gをとって径40mmの型に入れ、24.5×10Paの圧力をかけて押し固め、得られた成形体について、木屋式硬度計を利用した、3点荷重による破断強度の測定を行なった。一部のサンプルは低温乾燥機で乾燥したのちに押し固め、乾燥の前後における破断強度を比較した。この低温乾燥は、煙道ガスとの接触による乾燥のシミュレーションである。それぞれの場合の圧縮強度と、CO含有量および水分含有量の値を下記の表1に示す。 Furthermore, the inventors conducted the following experiment in order to confirm the relationship between the carbonation reactivity and fixation of slaked lime. Highly reactive after carbonated slaked lime 100g by the exposed to CO 2 gas or humidified CO 2 gas (to use the humidified gas is to promote carbonation), taking it from 15g The mold was put into a 40 mm diameter mold and pressed under a pressure of 24.5 × 10 6 Pa, and the resulting molded body was measured for breaking strength by a three-point load using a Kiyama hardness tester. Some samples were dried after being dried in a low-temperature drier, and then compared for breaking strength before and after drying. This low temperature drying is a simulation of drying by contact with flue gas. Table 1 below shows the compressive strength and the values of CO 2 content and water content in each case.

表1

Figure 0005434149
Table 1
Figure 0005434149

押し固めた消石灰サンプルがもつ圧縮強度は、炭酸化による固着の進行の尺度であって、配管や機器に付着した消石灰が剥落しにくくなる機構を示すものと解される。この面からも、消石灰の付着性、さらには付着した消石灰の固着性に対して、炭酸化反応性が重要であることがわかる。 The compressive strength of the compacted slaked lime sample is a measure of the progress of fixation due to carbonation, and is understood to indicate a mechanism that makes it difficult for slaked lime attached to piping and equipment to fall off. Also from this aspect, it can be seen that the carbonation reactivity is important for the adhesion of slaked lime and the adhesion of slaked lime.

一方、ゴミ焼却場の排ガス処理に使用したときに酸性ガスの除去率が高く、かつ、高反応性で少量の使用で済む高活性を有する、この用途にとって好適な消石灰は、比表面積が広く、しかも細孔の容積が大きいものであることが知られている。そして、そのような消石灰は、石灰石を焼成する度合からいえば、硬焼よりは比較的軟焼の、したがって水和活性度も高い生石灰を原料にしたときに得られることも知られている。そうなると、上述した、炭酸化反応性が低い消石灰を得るには水和活性度が低い生石灰から出発すべきであるとの知見と、これらの常識との折り合いが必要であり、原料生石灰の水和活性度を適切に選択する必要がある、との結論に至る。 On the other hand, slaked lime suitable for this application, which has a high acid gas removal rate when used for waste gas treatment at a garbage incineration plant, and is highly reactive and requires only a small amount of use, has a wide specific surface area, Moreover, it is known that the pore volume is large. And it is also known that such slaked lime can be obtained when raw lime is used as a raw material in terms of the degree of calcining of limestone. Then, the above-mentioned knowledge that starting with quick lime with low hydration activity should be obtained in order to obtain slaked lime with low carbonation reactivity, and these common senses need to be balanced. The conclusion is reached that the activity needs to be selected appropriately.

そこで発明者らは、高反応性でありながら炭酸化反応性が低い消石灰を与える原料生石灰を追求した。消化により得た消石灰の炭酸化反応性に対して、消化原料である生石灰の、水和反応性で表される活性度が影響するのではないかと考え、「t60値」で知られる水和活性度が、24秒から62秒に至るさまざまな値をもつ11種の生石灰を消化し、得られた消石灰の炭酸化反応性を調べた。よく知られているとおり、t60値は、粒度を−210μmに調製した生石灰150gを20±0.5℃の水600mLに投入し、300rpmの速度で撹拌しながら、水温が60℃に到達するまでの時間(秒)を記録したものであって、この時間が短いほど、その生石灰は水和活性度が高く、長いほど低いということになる。 Thus, the inventors have sought raw lime that gives slaked lime that has high reactivity but low carbonation reactivity. Hydration known as “t 60 value” because the activity expressed by hydration reactivity of quick lime, which is the raw material for digestion, may affect the carbonation reactivity of slaked lime obtained by digestion. Eleven kinds of quicklime with various activities ranging from 24 seconds to 62 seconds were digested, and the carbonation reactivity of the obtained slaked lime was examined. As is well known, the t 60 value indicates that the water temperature reaches 60 ° C. while stirring 150 g of quick lime having a particle size of −210 μm into 600 mL of water at 20 ± 0.5 ° C. and stirring at a speed of 300 rpm. The shorter the time, the quicker the hydration activity, and the shorter the time, the lower the time.

実験の結果、t60値が低い、すなわち水和活性度が高い生石灰を消化して得た消石灰ほど、炭酸化反応性が高いという関係が確認できた。前述の、炭酸化反応試験の値が10分以上である消石灰を与える生石灰は、t60値にして50秒以上の、水和反応活性がやや低いものであることがわかった。 The results of the experiment, t 60 value is low, that is, as slaked lime hydration activity is obtained by digesting a high quicklime, relations of a high carbonation reaction could be confirmed. Described above, quicklime value of carbonation reaction test gives slaked lime is at least 10 minutes, more than 50 seconds in the t 60 value, hydration activity was found to be one rather low.

ところでt60値は、水和反応の初期の状況を示す指標であって、中期以降の状況は、これだけではわからない。しかし発明者らは、炭酸化反応性を抑制しつつ高反応性を維持した消石灰を得るためには、原料生石灰の水和に関して、中期以降の反応性もまた重要であろうと予測したので、水和特性を初期のみならず中期以降についても知ることができるASTM法により、原料生石灰の規定をすることとした。その結果得られたのが、前記した「ASTM法による水和活性度試験において30秒値が60℃以下であり、かつ、△T=180秒値−30秒値が15℃以上である生石灰」という限定である。これを一口でいえば、水和に関して「初期反応は若干遅いが、その後の反応の伸びが大きい生石灰」である。 By the way, the t 60 value is an index indicating the initial state of the hydration reaction, and the state after the middle period cannot be understood by itself. However, the inventors have predicted that the reactivity after the middle period will also be important for the hydration of raw quicklime in order to obtain slaked lime that maintains high reactivity while suppressing carbonation reactivity. The raw quicklime was defined by the ASTM method which can know the sum characteristics not only in the initial period but also in the middle period and thereafter. As a result, “the quick lime whose 30 second value is 60 ° C. or lower and ΔT 2 = 180 second value−30 second value is 15 ° C. or higher in the hydration activity test by the ASTM method described above was obtained. Is the limitation. Speaking of this, it is “quick lime whose initial reaction is a little slow, but the subsequent reaction is large” regarding hydration.

当業者にはよく知られているように、ASTM法による水和活性度試験は、デュワー瓶に入れた水に生石灰を投入し、温度上昇曲線を記録するものであって、水和反応開始30秒後の水温は、初期反応の速度を表わす。この温度が60℃を超える生石灰は、あまりに初期反応性が高いため、良好な消石灰を与えない。一方、△T=180秒値−30秒値は、その後の反応の伸びを示すもので、この値が小さすぎる生石灰は、初期の水和反応性が高すぎるか、または中期以降の水和反応性が低く、いずれにせよ好ましい消石灰を与えない。30秒値が60℃以下であってもその差が15℃に達しない生石灰は、焼成度が高すぎて水和反応が遅く、消化が適切に行えないことが多いし、得られた消石灰の酸性ガスとの反応性が不満足である。 As is well known to those skilled in the art, the hydration activity test by the ASTM method is a method in which quick lime is put into water placed in a Dewar bottle and a temperature rise curve is recorded. The water temperature after a second represents the rate of the initial reaction. Quick lime whose temperature exceeds 60 ° C. does not give good slaked lime because its initial reactivity is so high. On the other hand, ΔT 2 = 180 seconds value−30 seconds value indicates the elongation of the subsequent reaction, and quick lime whose value is too small has too high initial hydration reactivity or hydration after the middle period. Reactivity is low and in any case does not give the preferred slaked lime. The quick lime whose difference does not reach 15 ° C. even if the value for 30 seconds is 60 ° C. or less, the firing degree is too high, the hydration reaction is slow, and digestion cannot often be performed properly. Reactivity with acid gas is unsatisfactory.

消化に当たっては、生石灰に対する消化水の割合を、HO/CaO=0.8〜1.2(重量比)の範囲とすることが好ましい。この消化水の量は、消化に必要な理論量の水に対して約2.5〜3.7倍に相当する。高反応性の消石灰を得るには、比較的多量の消化水を使用して、生石灰と水との混合物が、なるべく高含水状態であるようにする必要がある。0.8に達しない水量比では消化水の量が不足であり、一方、消化水の量がある限度を超えると、消化機の撹拌負荷が大きくなり、工業的な連続生産には不適当になる上、消化後に過剰の水分を乾燥させるためのエネルギー消費が過大になるという問題がある。製品消石灰に期待できる性能と、製造コストの調和をはかって、上記の消化水量比0.8〜1.2を選択した。 In digestion, the ratio of digested water to quicklime is preferably in the range of H 2 O / CaO = 0.8 to 1.2 (weight ratio). This amount of digested water corresponds to about 2.5 to 3.7 times the theoretical amount of water required for digestion. In order to obtain highly reactive slaked lime, it is necessary to use a relatively large amount of digested water so that the mixture of quicklime and water is as high as possible. If the water ratio does not reach 0.8, the amount of digestion water is insufficient. On the other hand, if the amount of digestion water exceeds a certain limit, the agitation load of the digester increases, which is inappropriate for industrial continuous production. In addition, there is a problem that energy consumption for drying excess water after digestion becomes excessive. The above-mentioned digestion water amount ratio of 0.8 to 1.2 was selected in consideration of the performance expected from the product slaked lime and the production cost.

アルコール類およびエタノールアミン類からなるグループから選んだ1種または2種以上の添加剤は、製品消石灰が広い比表面積と大きな細孔容積を有し、それによって、処理すべき排ガス中の酸性ガスの除去率を高く得る上で、効果的である。アルコール類は、メタノールやエタノールのような一価アルコールから、ジエチレングリコールやジプロピレングリコールのような多価アルコールに至る、多種類のアルコールが使用できる。エタノールアミン類は、モノエタノールアミン、ジエタノールアミン、トリエタノールアミンが使用できるが、トリエタノールアミンが好適である。 One or more additives selected from the group consisting of alcohols and ethanolamines, the product slaked lime has a large specific surface area and a large pore volume, so that the acid gas in the exhaust gas to be treated It is effective in obtaining a high removal rate. As the alcohols, various kinds of alcohols from monohydric alcohols such as methanol and ethanol to polyhydric alcohols such as diethylene glycol and dipropylene glycol can be used. As the ethanolamine, monoethanolamine, diethanolamine, and triethanolamine can be used, and triethanolamine is preferable.

消化は、消化機の出口における温度が70℃以下となる条件で実施することが好ましい。この温度は、消化機に熟成機が付設されている場合は、もちろん熟成機の出口における温度をいう。出口温度70℃以下の条件は、消化が十分に行なわれることを保証するものであって、十分な消化は、製品消石灰の酸性ガス除去性能を高く維持し、結果として、排ガス処理における使用消石灰の原単位の向上に寄与する。消化に要する時間、つまり消化機内部での滞留時間は、消化機の(熟成機が付設されていれば、それを含めた)容積によって決定される。十分な滞留時間を確保すれば水和反応が完了するので、消化物の温度は出口側ほど低くなるが、生産量を増強しようとすれば、当然に滞留時間が短縮されるため、消化物の出口側温度は高くなる。高い温度で消化機を出た消石灰は、消化が不完全であり、凝集性が高く、したがって使用時の分散性が悪いことが経験された。このような凝集は、酸性ガスと反応する表面積を見掛け上減少させ、消石灰原単位の増大につながるおそれがある。実機による高反応性消石灰使用の実績から、上記の消化機出口における消石灰の温度が70℃以下となるような消化を行なうことの有用性が確認された。 Digestion is preferably carried out under conditions where the temperature at the outlet of the digester is 70 ° C or lower. This temperature is, of course, the temperature at the outlet of the aging machine when an aging machine is attached to the digester. Conditions at an outlet temperature of 70 ° C. or less ensure that digestion is sufficiently performed. Sufficient digestion maintains the acid gas removal performance of product slaked lime high, and as a result, the use of slaked lime used in exhaust gas treatment Contributes to the improvement of basic unit. The time required for digestion, that is, the residence time inside the digester, is determined by the volume of the digester (including the aging machine if included). If sufficient residence time is secured, the hydration reaction will be completed, so the digest temperature will be lower on the outlet side, but if you try to increase production, the residence time will naturally be shortened, so The outlet side temperature increases. It has been experienced that slaked lime leaving the digester at high temperatures is incompletely digested and highly cohesive and therefore poorly dispersible when used. Such agglomeration apparently reduces the surface area that reacts with the acid gas, which may lead to an increase in slaked lime unit. The utility of performing digestion so that the temperature of the slaked lime at the outlet of the digester is 70 ° C. or less was confirmed from the results of the use of highly reactive slaked lime with an actual machine.

本発明の消石灰は、粒度分布の観点からは、45μm以上の径を有する粒子の存在率が10重量%以下であることが好ましい。比較的大径の粒子は、水平配管たとえば煙道内で沈降して堆積しやすい傾向があるので、その割合を低く抑えることによって、堆積が引き起こす閉塞を防止できるという利益が得られる。 In the slaked lime of the present invention, the abundance of particles having a diameter of 45 μm or more is preferably 10% by weight or less from the viewpoint of particle size distribution. Since particles of relatively large diameter tend to settle and accumulate in horizontal piping, for example in a flue, keeping the proportion low can provide the benefit of preventing clogging caused by deposition.

表2に示すような水和反応の特性を持つ生石灰を原料として使用し、CaOに対して1重量%に相当するジエチレングリコールを含有する消化水を、水の重量比1.0となるように加えて消化を行なった。得られた消石灰の炭酸化反応の状況を調べて、図2に示す結果を得た。測定された炭酸化速度を、表2に合わせて示す。実施例の消石灰2種は、原料に用いた生石灰のASTM試験の30秒値が60℃以下であるとともに、△Tが15℃以上という条件を満たすものであって、かつ、炭酸化速度が10分以上という条件を満たしている Using quick lime having hydration reaction characteristics as shown in Table 2 as a raw material, digestion water containing 1% by weight of diethylene glycol with respect to CaO is added so that the weight ratio of water becomes 1.0. And digested. The situation of carbonation reaction of the obtained slaked lime was examined, and the result shown in FIG. 2 was obtained. The measured carbonation rate is shown in Table 2 together. The two types of slaked lime in the examples satisfy the condition that the 30 second value of the ASTM test of quick lime used as a raw material is 60 ° C. or less and ΔT 2 is 15 ° C. or more, and the carbonation rate is Meet the condition of 10 minutes or more

表2

Figure 0005434149
Table 2
Figure 0005434149

得られた消石灰を、ゴミ焼却場の排ガスを処理して酸性ガスを除去する目的に使用し、設備に必要な清掃のインターバルが何日になるかを調べた。その結果を、表2に合わせて示す。本発明の消石灰を使用することにより、機器や配管への消石灰の付着が著しく減り、メンテナンスの負担が軽くなることが実証された。 The obtained slaked lime was used for the purpose of treating the exhaust gas from the garbage incineration plant to remove acid gas, and the number of cleaning intervals required for the equipment was examined. The results are also shown in Table 2. By using the slaked lime of the present invention, it has been proved that adhesion of slaked lime to equipment and piping is remarkably reduced and the maintenance burden is reduced.

本発明の成立過程で行なった実験のデータであって、排ガス処理に使用したときに配管への付着性が高い消石灰と、低い消石灰との炭酸化反応試験の結果を示すグラフ。It is the data of the experiment conducted in the formation process of this invention, Comprising: The graph which shows the result of the carbonation reaction test of slaked lime with high adhesiveness to piping, when used for exhaust gas treatment, and low slaked lime. 本発明の実施例で製造し、使用した消石灰について、炭酸化反応試験の結果を示す、図1と同様なグラフ。The graph similar to FIG. 1 which shows the result of a carbonation reaction test about the slaked lime manufactured and used in the Example of this invention.

Claims (5)

ASTM C110に定める水和活性度試験において30秒値が60℃以下であり、かつ、△T =180秒値−30秒値が15℃以上である生石灰を消化してなり、炭酸化反応試験(消石灰を水に分散させて5重量%のスラリーを形成し、このスラリーを6,000rpmの高速で撹拌しつつ、そこに炭酸ガスを640mL/分の速度で吹き込み、pHが11に低下するまでの時間を測定する。単位「分」)において、pH11に達する時間が10分以上、20分以下であることを特徴とする高反応性で付着性が低い消石灰。 Carbonation reaction test by digesting quick lime whose 30 second value is 60 ° C. or less and ΔT 2 = 180 second value −30 second value is 15 ° C. or more in the hydration activity test defined in ASTM C110 (Slaked lime is dispersed in water to form a 5% by weight slurry, and while stirring the slurry at a high speed of 6,000 rpm, carbon dioxide gas is blown into it at a speed of 640 mL / min until the pH drops to 11. A highly reactive and low adherence slaked lime characterized in that the time to reach pH 11 is 10 minutes or more and 20 minutes or less in the unit “minute”). 45μm以上の径を有する粒子の存在率が10重量%以下である請求項1の消石灰。 The slaked lime according to claim 1, wherein the abundance of particles having a diameter of 45 µm or more is 10% by weight or less. 原料として、ASTM C110に定める水和活性度試験において30秒値が60℃以下であり、かつ、△T=180秒値−30秒値が15℃以上である生石灰を使用し、これを連続消化装置に供給し、アルコール類およびエタノールアミン類からなるグループから選んだ1種または2種以上の添加剤を、消石灰100重量部に対して0.1〜5重量部の割合で添加した水を消化水として加えることを特徴とする高反応性で付着性が低い消石灰の製造方法。 As a raw material, quick lime having a 30 second value of 60 ° C. or lower and a ΔT 2 = 180 second value−30 second value of 15 ° C. or higher in a hydration activity test defined in ASTM C110 is used. The water which supplied to the digester and added 1 or 2 or more types of additives selected from the group consisting of alcohols and ethanolamines at a ratio of 0.1 to 5 parts by weight with respect to 100 parts by weight of slaked lime. A method for producing slaked lime that is highly reactive and has low adhesion, which is added as digestive water. 生石灰に対する消化水の割合を、HO/CaO=0.8〜1.2(重量比)の範囲として実施する請求項3の消石灰の製造方法。 The percentage of digested water for quicklime, H 2 O / CaO = 0.8~1.2 slaked lime manufacturing method of claim 3 implemented as (weight ratio). 消化機の出口の温度が70℃以下となる条件で消化を実施する請求項3の消石灰の製造方法。 The method for producing slaked lime according to claim 3, wherein the digestion is performed under a condition that the temperature at the outlet of the digester is 70 ° C or lower.
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