JP3144499B2 - PH adjustment method of water using shell quicklime - Google Patents
PH adjustment method of water using shell quicklimeInfo
- Publication number
- JP3144499B2 JP3144499B2 JP35646291A JP35646291A JP3144499B2 JP 3144499 B2 JP3144499 B2 JP 3144499B2 JP 35646291 A JP35646291 A JP 35646291A JP 35646291 A JP35646291 A JP 35646291A JP 3144499 B2 JP3144499 B2 JP 3144499B2
- Authority
- JP
- Japan
- Prior art keywords
- shell
- lime
- water
- quicklime
- adjusting
- 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
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 title claims description 105
- 239000000292 calcium oxide Substances 0.000 title claims description 55
- 235000012255 calcium oxide Nutrition 0.000 title claims description 55
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims description 42
- 238000000034 method Methods 0.000 title claims description 34
- 238000010979 pH adjustment Methods 0.000 title 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 41
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 41
- 239000004571 lime Substances 0.000 claims description 41
- 230000029087 digestion Effects 0.000 claims description 26
- 238000010304 firing Methods 0.000 claims description 11
- 239000002994 raw material Substances 0.000 claims description 11
- 235000015170 shellfish Nutrition 0.000 claims description 8
- 239000002245 particle Substances 0.000 claims description 7
- 230000035484 reaction time Effects 0.000 claims description 4
- 238000000691 measurement method Methods 0.000 claims description 2
- 230000009257 reactivity Effects 0.000 claims description 2
- 238000001816 cooling Methods 0.000 description 20
- 230000002378 acidificating effect Effects 0.000 description 17
- 230000003472 neutralizing effect Effects 0.000 description 17
- 238000001354 calcination Methods 0.000 description 15
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 13
- 239000000920 calcium hydroxide Substances 0.000 description 13
- 235000011116 calcium hydroxide Nutrition 0.000 description 13
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 13
- 235000019738 Limestone Nutrition 0.000 description 11
- 239000006028 limestone Substances 0.000 description 11
- 238000005065 mining Methods 0.000 description 11
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 10
- 238000006386 neutralization reaction Methods 0.000 description 9
- 239000003795 chemical substances by application Substances 0.000 description 6
- 238000002407 reforming Methods 0.000 description 6
- 229910000019 calcium carbonate Inorganic materials 0.000 description 5
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 4
- 230000008859 change Effects 0.000 description 4
- 238000002485 combustion reaction Methods 0.000 description 4
- 238000010586 diagram Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 238000010583 slow cooling Methods 0.000 description 4
- 239000004094 surface-active agent Substances 0.000 description 4
- 241000237509 Patinopecten sp. Species 0.000 description 3
- 239000002253 acid Substances 0.000 description 3
- 150000007513 acids Chemical class 0.000 description 3
- 239000011248 coating agent Substances 0.000 description 3
- 238000000576 coating method Methods 0.000 description 3
- 238000003780 insertion Methods 0.000 description 3
- 230000037431 insertion Effects 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 244000005700 microbiome Species 0.000 description 3
- 235000020637 scallop Nutrition 0.000 description 3
- 238000005245 sintering Methods 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- 238000009360 aquaculture Methods 0.000 description 2
- 244000144974 aquaculture Species 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- -1 etc. Substances 0.000 description 2
- 230000036571 hydration Effects 0.000 description 2
- 238000006703 hydration reaction Methods 0.000 description 2
- 230000009545 invasion Effects 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 241000251468 Actinopterygii Species 0.000 description 1
- 241000237502 Ostreidae Species 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 125000000129 anionic group Chemical group 0.000 description 1
- 239000003945 anionic surfactant Substances 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- 210000000988 bone and bone Anatomy 0.000 description 1
- 239000011449 brick Substances 0.000 description 1
- 239000003093 cationic surfactant Substances 0.000 description 1
- 239000011247 coating layer Substances 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 230000020169 heat generation Effects 0.000 description 1
- 238000007654 immersion Methods 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000006396 nitration reaction Methods 0.000 description 1
- 239000002736 nonionic surfactant Substances 0.000 description 1
- 235000020636 oyster Nutrition 0.000 description 1
- 238000003908 quality control method Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000010420 shell particle Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Description
【0001】[0001]
【産業上の利用分野】本発明は、産業廃棄物として大量
に発生する貝殻を焼成して得られる貝殻生石灰を用い
た、河川、湖沼、養殖漁場等の水のpHを調整する方法
に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for adjusting the pH of water in rivers, lakes, marshes, aquaculture and fishing grounds using shell lime obtained by firing shells generated in large quantities as industrial waste. is there.
【0002】[0002]
【従来の技術】河川、湖沼、養殖漁場等の水は、自然界
に存在する酸、人為的要因による酸、あるいは魚が排出
するアンモニアの微生物の作用による硝酸化等の種々酸
が溶け込むことにより、弱酸性からpH2〜3程度の強
酸性を示すものがある。このように酸性を示す水(以
下、酸性水という。)をそのままにしておくと生物の生
態系や環境の破壊に繋がるため、従来より鉱物質の石灰
石(炭酸カルシウム)やこれを焼成して得られる生石灰
(酸化カルシウム)、あるいは生石灰を消化して得られ
る消石灰(水酸化カルシウム)等が中和剤として酸性水
の中和改質に用いられている。2. Description of the Related Art Water from rivers, lakes and marshes, aquaculture and fishing grounds dissolves with various acids such as acids existing in nature, acids caused by man-made factors, or nitration caused by the action of microorganisms of ammonia emitted by fish. Some exhibit weak acidity to strong acidity of about pH 2 to 3. Leaving such acidic water (hereinafter referred to as acidic water) as it is leads to the destruction of the ecosystem and environment of living organisms. Quick lime (calcium oxide), slaked lime (calcium hydroxide) obtained by digesting quick lime, and the like are used as neutralizing agents for neutralizing and reforming acidic water.
【0003】このような酸性水の中和作用を有する技術
として、例えば炭酸カルシウムを用いる技術は、特定地
域に産出する水質改良に適した成分を有する貝化石を用
いて排水等の中和を行なわしめる方法(特開平2−26
8882公報、特開平2−268884公報)、接触曝
気式の汚水処理装置において微生物等を保持せしめるた
めの接触濾材として籠状中空体内部に貝殻等を入れ中性
化させる方法(特公平2−2635公報)等が知られて
いる。また酸化カルシウムを用いる技術は、貝、骨、石
灰石等を焼成して得られる酸化カルシウム粉末、水及び
油の3者を混合したアルカリ剤を用いて主として酸性の
廃油、廃液を脱酸させる技術(特公平2−32208公
報)等が知られている。[0003] As a technique having a neutralizing action of such acidic water, for example, a technique using calcium carbonate performs neutralization of wastewater or the like using shell fossils produced in specific areas and having components suitable for improving water quality. Squeezing method (JP-A-2-26)
No. 8882, Japanese Unexamined Patent Publication No. 2-268884), a method of neutralizing a shell-like hollow body as a contact filter medium for retaining microorganisms in a contact aeration type sewage treatment apparatus (Japanese Patent Publication No. Hei 2-2635). Gazettes) are known. The technique using calcium oxide is a technique for deoxidizing mainly acidic waste oil and waste liquid using an alkaline agent obtained by mixing calcium oxide powder obtained by firing shellfish, bone, limestone, etc., water and oil ( Japanese Patent Publication No. 2-32208) is known.
【0004】このように石灰石、生石灰あるいは消石灰
は材料の入手もたやすくまた経済的にも適した材料であ
るため、酸性水の中和材として多用されている。しかし
ながら、例えば石灰石等の炭酸カルシウムを用いる方法
では、塊状で用いうるという利点はあるものの、生石灰
や消石灰に比べてpH調整能力が小さいため、酸性水の
中和に多くの量を必要とする。一方、生石灰や消石灰は
pH調整能力が大きいため使用量は石灰石に比べて少な
い量ですむが水中で粉状化、白濁するという問題があ
る。また、酸性水を中和改質する場合、単に中和のみの
処理であれば中和能力が大きくて、中和速度が早い生石
灰や消石灰を所定量添加して急速に中和する方法等を採
用できるが、河川や湖沼等のように生物の生態系を保持
しながら中和する必要がある場合は前記のような方法は
好ましい方法とはいえない。一方、石灰石等の炭酸カル
シウムを用いれば生石灰や消石灰に比べて中和は概して
穏やかではあるが、逆に中和に要する時間がかかりすぎ
たり、石灰石表面に微生物が付着したり汚泥等が堆積し
たりしてその表面が覆われるため、中和能力が低下する
という問題がある。また、消化速度を調整した生石灰を
用いて酸性水を中和改質する方法も考えられが、生石灰
の消化速度を調整する方法として、水圏生態系成因によ
る炭酸カルシウムを原料として、これを焼成後、ノニオ
ン性、アニオン性及びカチオン性の界面活性剤の存在下
で、生石灰の粉砕と界面活性剤による生石灰表面の被覆
を単一操作で施し、その被覆層の厚みを調整することに
より生石灰の消化速度を調整する方法が知られている
(特開平2−258656公報)。しかしながら、この
ように界面活性剤を生石灰に被覆して消化速度を調節し
た生石灰を用いて酸性水を中和改質する方法では、生石
灰の製造において界面活性剤を被覆させる工程が必要で
あることに加えて、界面活性剤の存在下で、生石灰の粉
砕を行っているため、生石灰粉末が流出して白濁化しや
すく、それを防止するための工夫を必要とする。As described above, limestone, quicklime or slaked lime is a material which is easily available and economically suitable, and is therefore frequently used as a neutralizing material for acidic water. However, for example, a method using calcium carbonate such as limestone has an advantage that it can be used in a lump, but has a small pH adjusting ability as compared with quick lime or slaked lime, and therefore requires a large amount for neutralization of acidic water. On the other hand, quicklime and slaked lime have a large pH adjusting ability, so that they can be used in a smaller amount than limestone, but have a problem that they become powdery and cloudy in water. In addition, in the case of neutralizing and reforming acidic water, a method of neutralizing rapidly by adding a predetermined amount of quicklime or slaked lime which has a large neutralization capacity if the treatment is only neutralization and has a high neutralization speed. Although it can be adopted, when it is necessary to neutralize while maintaining the biological ecosystem such as a river or a lake, the above method is not a preferable method. On the other hand, when calcium carbonate such as limestone is used, neutralization is generally milder than quick lime or slaked lime, but on the contrary, it takes too long to neutralize, microorganisms adhere to the limestone surface, and sludge accumulates. The surface is covered, and the neutralization ability is reduced. In addition, a method of neutralizing and reforming acidic water using quicklime whose digestion rate has been adjusted is also conceivable.However, as a method of adjusting the quicklime digestion rate, calcium carbonate produced by aquatic ecosystem origin is used as a raw material, and after calcining In the presence of nonionic, anionic and cationic surfactants, grinding of quicklime and coating of quicklime surface with surfactant in a single operation, and adjusting the thickness of the coating layer to digest quicklime A method for adjusting the speed is known (JP-A-2-258656). However, in the method of neutralizing and modifying acidic water using quicklime coated with quicklime and adjusting the digestion rate by coating a surfactant in this way, a step of coating the quicklime with a surfactant is required. In addition, since quicklime is pulverized in the presence of a surfactant, quicklime powder is likely to flow out and become cloudy, and a device for preventing it is required.
【0005】[0005]
【発明が解決しようとする課題】本発明は、酸性水の中
和改質に中和剤として酸化カルシウムを用いる方法にお
いて、従来の生石灰を使用した際の問題点を解決し、生
物の生態系を保持しながら中和することのできる水のp
H調整(中和改質)方法を提供することを目的とする。SUMMARY OF THE INVENTION The present invention solves the problem of using conventional quick lime in a method of using calcium oxide as a neutralizing agent in the neutralization and reforming of acidic water, and solves the problem of the ecosystem of living organisms. Of water that can be neutralized while maintaining
An object of the present invention is to provide an H adjustment (neutralization reforming) method.
【0006】[0006]
【課題を解決するための手段】本発明者は、水のpH調
整方法について鋭意検討を重ねた結果、特定の方法によ
り製造した生石灰を用いることにより上記目的が達成で
きることを見いだし、本発明を完成した。 即ち、本発
明は、貝殻を原料として製造した消化速度の遅い貝殻生
石灰を用いて水のpHを調整することを特徴とする水の
pH調整方法である。貝殻を焼成する装置として、従来
よりロ−タリ−キルンや竪型生石灰焼成炉等が用いられ
ている。これらの装置は一般に焼成物を急冷するタイプ
であるため得られる貝殻生石灰は消化速度の早いものが
多い。本発明の方法では、貝殻を原料として製造した、
後述の測定法方で測定した全消化反応時間が60分以上
の貝殻生石灰を使用することを特徴とする。本発明で用
いることができる貝殻生石灰は、次のような方法により
得ることができる。従来の竪型石灰焼成炉(図3)にお
いて、原料投入管1の炉内挿入部分2をなくし、排鉱機
部5の回転シ−ル部及びシュ−ト部6を外気の侵入を防
止できる構造とするとともに、空気量を調節できる冷却
用配管10を排鉱機部5に設けた構造に改良された竪型
石灰焼成炉を用いて、冷却用空気量を調節して焼成物の
冷却速度を調節することで、本発明で用いることができ
る貝殻生石灰を得ることができる。改良された竪型石灰
焼成炉(以下、単に炉という。)の全体断面概略図を図
4に示す。Means for Solving the Problems As a result of intensive studies on the method of adjusting the pH of water, the present inventor has found that the above object can be achieved by using quicklime produced by a specific method, and has completed the present invention. did. That is, the present invention is a method for adjusting the pH of water, wherein the pH of the water is adjusted using quick-lime shell lime produced from shells and having a low digestion rate. Rotary kilns, vertical quicklime calcination furnaces, and the like have been used as apparatuses for baking shells. Since these devices are generally of the type in which the calcined product is rapidly cooled, the quick lime obtained from the shell often has a high digestion rate. In the method of the present invention, the shell was produced as a raw material,
It is characterized by using quick lime of a shell having a total digestion reaction time of 60 minutes or more as measured by a measurement method described later. Shell quicklime that can be used in the present invention can be obtained by the following method. In the conventional vertical lime sintering furnace (FIG. 3), the insertion portion 2 of the raw material charging pipe 1 in the furnace is eliminated, and the invasion of the outside air into the rotary seal portion and the shunt portion 6 of the mining machine 5 can be prevented. The cooling rate of the calcined material is adjusted by using a vertical lime calciner having an improved structure in which a cooling pipe 10 capable of adjusting the amount of air is provided in the ore removing unit 5 while adjusting the amount of cooling air. By adjusting the value, quick shell lime that can be used in the present invention can be obtained. FIG. 4 shows a schematic overall sectional view of an improved vertical lime burning furnace (hereinafter simply referred to as a furnace).
【0007】前記炉を用いて貝殻生石灰を製造する場合
の概略の製造工程は次のとおりである。まず、炉へ装入
する貝殻の粒度は2〜60mm程度が良く、ホタテ貝、
カキ殻、アワビ殻等の大きなものは、予め適当な粉砕機
を用いて粒度を前記範囲、好ましくは30〜50mm程
度の大きさに粉砕して粒度を調整する。このように貝殻
の粒度を調整することにより、炉への装入を容易にする
とともに、貝殻の炉内装填嵩密度を大きくし、炉内堆積
部の空気抵抗を大きくして、燃焼空気の制御が容易とな
る。貝殻片の大きさが60mmを超えると炉内装填嵩密
度が小さくなり、空気抵抗が小さくなるため焼成管理が
難しくなり、また2mm未満では飛散しやくなり、排ガ
スとともに炉外へ流出する量が多くなるため好ましくな
い。[0007] The outline of the production process in the case of producing shell lime using the above furnace is as follows. First, the particle size of the shell charged into the furnace is preferably about 2 to 60 mm.
Large oyster shells, abalone shells and the like are previously crushed to a particle size within the above range, preferably about 30 to 50 mm, using a suitable crusher to adjust the particle size. By adjusting the shell particle size in this way, charging into the furnace is facilitated, the shell interior filling bulk density is increased, and the air resistance of the furnace deposition area is increased to control combustion air. Becomes easier. If the size of shell pieces exceeds 60 mm, the bulk density inside the furnace will be low, and the air resistance will be low, making it difficult to manage the baking. If it is less than 2 mm, it will be liable to fly and will flow out of the furnace together with the exhaust gas. Is not preferred.
【0008】粒度調整された貝殻(以下、単に貝殻とい
う。)は原料投入管1より装入され炉内の棚部3に一時
堆積されるが、原料投入管炉内挿入部2が撤去されてい
るため、棚部3の天井まで貝殻が装入でき、炉内の燃焼
空気が棚部外側にある排ガス通路7へ容易に逃げないよ
うになる。このため棚部3の空気抵抗が大きくなり、燃
焼空気が逃げていきにくくなり安定した焼成雰囲気を保
持できる。[0008] Shells (hereinafter simply referred to as shells) whose grain size has been adjusted are charged from a raw material charging pipe 1 and temporarily deposited on a shelf 3 in the furnace. Therefore, shells can be inserted into the ceiling of the shelf 3 so that combustion air in the furnace does not easily escape to the exhaust gas passage 7 outside the shelf. For this reason, the air resistance of the shelf 3 increases, and the combustion air does not easily escape, and a stable firing atmosphere can be maintained.
【0009】次いで、棚部3に一時堆積された貝殻は焼
成帯4に順次落とされ焼成される。貝殻の焼成は、通常
焼成帯4の温度を1,100℃〜1,250℃程度に保
持して行なうことができるが、温度と保持時間は所望と
する貝殻生石灰の焼成度合、即ち貝殻生石灰の酸化カル
シウム含有量に応じて適宜設定すればよい。ここで、焼
成の管理は主として燃料と燃焼空気の使用量の制御によ
り行なうが、炉内への外気の侵入があると焼成管理が困
難となり、いわゆる焼けむらといった品質のばらつきを
生じやすく貝殻生石灰の品質管理が困難となる。従来の
竪型石灰焼成炉における外気の主な侵入経路はシュ−ト
部6と排鉱機部5の回転シ−ル部である。特にシュ−ト
部6は、焼成された貝殻生石灰の主な冷却用空気の取り
入れ口となっているが、外気に開放されているため取り
入れる空気の量を調節することが困難であり、過剰の空
気が炉内へ取り入れられるというような構造であった。
まず、外気の侵入を防ぐ手段としは、従来の排鉱機部5
の回転シ−ル部(図5)を二重シ−ル構造(図6)とし
て排鉱機部5の回転シ−ル部からの外気の侵入を防ぎ、
また従来の冷却用空気の主な取り入れ口でもあるシュ−
ト部6に、例えばエアシリンダ−で駆動するようなダン
パ−9を二重に取り付けた構造としてダンパ−を交互に
作動させて貝殻生石灰を排出しシュ−ト部6からの外気
の侵入を防ぐ等の方法があげられる。また、冷却用の空
気を取り入れる手段としては、図7及び図8に示すよう
に、排鉱機部5に冷却用空気を取り入れるための冷却用
配管10を設けて、排鉱機部5内部に所望とする貝殻の
消化速度に応じて冷却用空気を調整しながら送り込み、
貝殻生石灰を冷却する等の方法があげられる。Next, the shells temporarily deposited on the shelf 3 are sequentially dropped into the firing zone 4 and fired. The calcination of the shell can be usually carried out while maintaining the temperature of the calcination zone 4 at about 1,100 ° C. to 1,250 ° C., and the temperature and the holding time are the desired degree of calcination of the shell quick lime, ie, the shell lime. What is necessary is just to set suitably according to calcium oxide content. Here, firing is controlled mainly by controlling the amount of fuel and combustion air used, but if there is outside air entering the furnace, it becomes difficult to control firing, and quality fluctuations such as so-called unevenness in burning are likely to occur, resulting in the calcination of shell lime. Quality control becomes difficult. The main path of the outside air in the conventional vertical lime calcination furnace is the rotating section of the shut section 6 and the mining machine section 5. In particular, the shut portion 6 serves as a main cooling air intake for the calcined shell quicklime, but since it is open to the outside air, it is difficult to control the amount of air to be taken in. The structure was such that air was taken into the furnace.
First, as means for preventing the invasion of outside air, the conventional mining machine 5
The rotary seal portion (FIG. 5) of FIG. 5 has a double seal structure (FIG. 6) to prevent intrusion of outside air from the rotary seal portion of the mining machine portion 5,
In addition, the shoe which is the main intake of the conventional cooling air
For example, a damper 9 which is driven by an air cylinder is attached to the start portion 6 in a double structure, and the dampers are alternately operated to discharge the shell lime and prevent outside air from entering the shoot portion 6. And the like. As means for taking in cooling air, as shown in FIGS. 7 and 8, a cooling pipe 10 for taking in cooling air is provided in the mining machine section 5, and inside the mining machine section 5. Adjusting the cooling air according to the desired shellfish digestion rate and sending it in,
Examples of such methods include cooling shell lime.
【0010】このように焼成された貝殻生石灰の冷却速
度を調節することで、貝殻生石灰の消化速度(水和速
度)を調節できる。冷却速度は、所望とする生石灰の消
化速度に応じて調節すればよい。貝殻生石灰の消化速度
を遅くするには、冷却速度を遅く(徐冷)すればよく、
また焼成温度を高めに設定すれば更に効果がある。徐冷
することにより生石灰の消化速度が遅くなるのは、徐冷
により結晶が粗大化し消化速度が遅くなるものと思われ
る。The digestion rate (hydration rate) of the shell lime can be adjusted by adjusting the cooling rate of the shell lime thus calcined. The cooling rate may be adjusted according to the desired quick lime digestion rate. To slow down the rate of shellfish lime digestion, slow down the cooling rate (slow cooling),
Further, if the firing temperature is set higher, there is a further effect. The reason why the slow cooling slows down the quicklime digestion rate is thought to be that the slow cooling causes the crystals to become coarse and the digestion rate to slow down.
【0011】酸性水を中和改質するには、例えば前記炉
を用いて焼成して得られた貝殻生石灰から、粉末化して
いる部分を除去したものを容器に入れて、酸性水と接触
させればよい。貝殻生石灰を入れる容器は、貝殻生石灰
と酸性水が容易に接触できるような構造を有し、アルカ
リや水で容易に腐食されないような材質のものであれば
特に限定はなく、また形状も使用目的に応じた任意な形
状としてよい。このような容器として、例えば図1に示
すような網目の小さいネットや布袋等をあげることがで
きる。また貝殻生石灰を入れた容器は、酸性水中に適当
な方法により固定しておけばよく、固定する方法や固定
する容器の数等は、特に限定されるものではない。In order to neutralize and reform the acidic water, for example, the powdered portion of the calcined lime obtained by calcination using the above-mentioned furnace is removed and put into a container, and the lime is brought into contact with the acidic water. Just do it. There is no particular limitation on the container in which the shellfish lime is to be placed, as long as it has a structure that allows the shellfish lime to easily come into contact with acidic water and is not easily corroded by alkali or water. Any shape may be used according to the conditions. Examples of such a container include a net having a small mesh and a cloth bag as shown in FIG. Further, the container containing the shell lime may be fixed in an acidic water by an appropriate method, and the fixing method, the number of containers to be fixed, and the like are not particularly limited.
【0012】このように酸性水の中和改質に、消化速度
の遅い貝殻生石灰を用いることにより、従来の石灰石を
焼成して得られる生石灰が水との接触により発熱しなが
ら直ちに粉状化して白濁化するといった現象に対して、
消化が穏やかに進行するため、発熱も少なく、消化され
て生成した消石灰による白濁化も極めて少なく、また河
川や湖沼等の生物の生態系を保持しながら酸性水を中和
改質できる。[0012] As described above, by using shell lime having a slow digestion rate for neutralizing and reforming acidic water, quick lime obtained by calcining conventional limestone is immediately powdered while generating heat due to contact with water. For the phenomenon of cloudiness,
Since digestion proceeds gently, there is little heat generation, very little clouding due to slaked lime generated by digestion, and it is possible to neutralize and reform acidic water while maintaining ecosystems of living organisms such as rivers and lakes.
【実施例】以下、実施例により本発明の貝殻生石灰を用
いた水の中和改質方法を詳細に説明する。EXAMPLES Hereinafter, the method for neutralizing and modifying water using quick lime of the present invention will be described in detail with reference to examples.
【0013】(実施例1)ホタテ貝貝殻を50mm以下
の粒度に破砕したものを貝殻生石灰製造用原料とした。
この原料を原料投入管1より、竪型石灰焼成炉に投入
し、焼成帯4の温度1,100℃、1時間で焼成した。
焼成後、貝殻生石灰は冷却空気量及び貝殻生石灰排出速
度等を調節して、8時間程度の時間をかけて100℃以
下程度まで徐冷しながら冷却した。得られた貝殻生石灰
の焼成度合(CaO含有量)は、90%であった。な
お、貝殻生石灰の製造には、従来の竪型石灰焼成炉を次
に示すような例に改良した竪型石灰焼成炉を用いた。即
ち、原料貝殻の投入管1の炉内挿入部分2をなくすとと
もに、排鉱機部5の回転シ−ル部を二重シ−ル構造と
し、またシュ−ト部6にエアシリンダ−で作動するダン
パ−9を二重に取り付け、ダンパ−を交互に作動させて
貝殻生石灰を取り出し外気の炉内への侵入を防ぐ構造と
するとともに、焼成された貝殻生石灰の冷却速度を調節
できる冷却用配管10を排鉱機部5に取り付けた竪型石
灰焼成炉に改良した。(Example 1) Scallop shells crushed to a particle size of 50 mm or less were used as raw materials for the production of quick lime.
This raw material was put into a vertical lime calcination furnace from a raw material charging pipe 1 and baked at a temperature of 1,100 ° C. in a calcination zone 4 for 1 hour.
After calcining, the shell quicklime was cooled while gradually cooling to about 100 ° C. or less over about 8 hours by adjusting the amount of cooling air, the shell quicklime discharging speed, and the like. The calcined degree (CaO content) of the obtained quick lime was 90%. For the production of shellfish lime, a vertical lime calcination furnace obtained by improving a conventional vertical lime calcination furnace to the following example was used. That is, while eliminating the insertion portion 2 of the raw material shell input pipe 1 in the furnace, the rotary seal portion of the mining machine unit 5 has a double seal structure, and the shut unit 6 is operated by an air cylinder. A double damper 9 is installed, and the dampers are alternately operated to take out the shell lime so as to prevent the outside air from entering the furnace, and to control the cooling rate of the fired shell shell lime. 10 was improved to a vertical lime sintering furnace attached to the mining unit 5.
【0014】次に、貝殻生石灰の消化状況を調査するた
めに、常温まで冷却した前記貝殻生石灰を大きさ30m
m程度の粒度に揃えたもの、約500gを網目状のネッ
ト入れ、これを100lの水に浸漬した状態で20日間
放置した。この後、水中より前記ネットを取り出し個々
の貝殻生石灰の消化状況を調査した結果、水に浸漬する
前の貝殻生石灰の状態と比べて約1/3程度が粉状化し
ていた。また、形を保って残っている約2/3のものの
成分を分析した結果、消石灰が約75%程度であり、残
りの成分は炭酸カルシウムであった。Next, in order to investigate the digestion state of the shell lime, the shell lime cooled to room temperature was sized 30 m.
Approximately 500 g of a net having a particle size of about m was put into a mesh net, and the net was left immersed in 100 l of water for 20 days. Thereafter, the net was taken out of the water, and the digestion state of the individual shell lime was examined. As a result, it was found that about 1/3 of the state of the shell lime before immersion in water was powdered. Further, as a result of analyzing about 2/3 of the components remaining in shape, about 75% of slaked lime was found, and the remaining components were calcium carbonate.
【0015】(実施例2、比較例1、2)表1に示す条
件で生石灰を調製して、生石灰の消化速度を調査した。
得られた結果を合わせて表1に示す。この結果から、徐
冷して得られる貝殻生石灰は消化速度が遅く、また消化
に伴う発熱も少ないことがわかる。なお、実施例2の貝
殻生石灰は、ホタテ貝貝殻を実施例1の操作に準じて、
改良された竪型石灰焼成炉で焼成して得たものであり、
比較例1及び2の生石灰は、それぞれホタテ貝貝殻及び
石灰石を用いて、電気炉で1,000℃、2時間の条件
で焼成後、大気中に取り出し急冷して調製したものであ
る。また、生石灰の消化速度は、アメリカ材料規格協会
の定めるASTM C110−76aに準じて測定し
た。この方法の概要は次のとおりである。消化反応性試
験装置を用いて、水温40℃の水380mlに、3.3
5mmふるい通過試料生石灰を手早く調製し、室温にな
るまで気密容器の中に入れていた生石灰76gを入れ、
温度計の読みが3回続けて0.5℃以内の変化になるま
で温度を読み取り、この3回の読みの最初の時間を全消
化反応時間とし、このときの温度を最終反応温度とみな
し、この最終反応温度からはじめの温度を差し引いて全
上昇温度を得る方法である。(Example 2, Comparative Examples 1 and 2) Quicklime was prepared under the conditions shown in Table 1 and the digestion rate of quicklime was investigated.
Table 1 shows the obtained results. From this result, it can be understood that the quicklime of the shell obtained by slow cooling has a slow digestion rate and also generates less heat due to the digestion. In addition, the quicklime of the shell of Example 2 was obtained by using the scallop shell according to the operation of Example 1.
It is obtained by firing in an improved vertical lime firing furnace,
The quicklime of Comparative Examples 1 and 2 was prepared by sintering the scallop shell and limestone in an electric furnace at 1,000 ° C. for 2 hours, then taking out into the atmosphere and rapidly cooling. The quick lime digestion rate was measured according to ASTM C110-76a defined by the American Society for Standards for Materials. The outline of this method is as follows. Using a digestion reactivity test apparatus, 3.3 ml of 380 ml of water at a water temperature of 40 ° C.
5 mm sieve passing sample quicklime was quickly prepared, and 76 g of quicklime placed in an airtight container until room temperature was reached,
The temperature was read until the reading of the thermometer was changed continuously within 0.5 ° C. three times, and the first time of the three readings was taken as the total digestion reaction time, and the temperature at this time was regarded as the final reaction temperature. In this method, the initial temperature is subtracted from the final reaction temperature to obtain a total temperature increase.
【0016】(実施例3)実施例1で得られた貝殻生石
灰を大きさ10〜50mmの粒度に選別したもの、大き
さ30mmの消石灰及び大きさ2〜5mmの石灰石を中
和剤として用い、それぞれの中和剤ごとにpH値を2.
5程度に調製した水10lに中和剤50gを添加し、1
回/日の頻度で適宜撹拌した後放置し、適当な間隔でp
Hを測定した。時間の経過(横軸)に対するpH値の変
化(縦軸)を測定した結果を図2に示す。図2で、前記
消石灰、貝殻生石灰及び石灰石のpH値の変化をそれぞ
れ、11、12及び13で示している。この結果から、
水和速度が遅い貝殻生石灰であっても、消石灰とほぼ同
等の中和能力があることがわかる。(Example 3) Shell lime obtained in Example 1 was sorted to a particle size of 10 to 50 mm, slaked lime having a size of 30 mm and limestone having a size of 2 to 5 mm were used as neutralizing agents. The pH value for each neutralizer is 2.
50 g of a neutralizing agent was added to 10 l of water adjusted to about 5, and 1
After stirring appropriately at a frequency of twice a day, the mixture is allowed to stand, and p
H was measured. FIG. 2 shows the results of measuring the change in the pH value (vertical axis) with the passage of time (horizontal axis). In FIG. 2, changes in pH values of the slaked lime, shell quicklime and limestone are indicated by 11, 12 and 13, respectively. from this result,
It can be seen that even shellfish lime having a low hydration rate has a neutralizing ability substantially equal to slaked lime.
【図1】 貝殻生石灰を入れた概略例図。FIG. 1 is a schematic diagram showing a case in which quicklime is added to a shell.
【図2】 中和剤別の中和能力を示すグラフ。FIG. 2 is a graph showing the neutralizing ability of each neutralizing agent.
【図3】 従来の竪型石灰焼成炉全体断面概略図。FIG. 3 is a schematic cross-sectional view of an entire conventional vertical lime calcination furnace.
【図4】 改良された竪型石灰焼成炉全体断面概略図。FIG. 4 is a schematic cross-sectional view of the entire improved vertical lime burning furnace.
【図5】 従来の排鉱機部回転シ−ル部。FIG. 5 is a conventional rotary seal unit of a mining machine unit.
【図6】 排鉱機部回転シ−ル部の改良概略図。FIG. 6 is an improved schematic diagram of a rotary seal part of a mining machine part.
【図7】 シュ−ト部改良及び冷却用配管概略図。FIG. 7 is a schematic diagram of a pipe for improving a shout portion and cooling.
【図8】 シュ−ト部側からみた冷却用配管概略図。FIG. 8 is a schematic diagram of a cooling pipe as viewed from a shout portion side.
1 原料投入管 2 原料投入管炉内挿入部 3 棚部 4 焼成帯 5 排鉱機部 6 シュ−ト部 7 排ガス通路 8 天井レンガ磨耗部 9 ダンパ− 10 冷却用配管 11 消石灰によるpH値の変化状況 12 貝殻生石灰によるpH値の変化状況 13 石灰石によるpH値の変化状況 REFERENCE SIGNS LIST 1 raw material introduction pipe 2 raw material introduction tube furnace insertion section 3 shelf 4 firing zone 5 mining machine section 6 shout section 7 exhaust gas passage 8 ceiling brick wear section 9 damper 10 cooling pipe 11 pH change due to slaked lime Situation 12 Change in pH value due to shell lime 13 Change in pH value due to limestone
【表1】 [Table 1]
───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) C02F 1/66 C04B 2/00 ──────────────────────────────────────────────────続 き Continued on front page (58) Field surveyed (Int. Cl. 7 , DB name) C02F 1/66 C04B 2/00
Claims (3)
用いて水のpHを調整する水のpH調整方法であって、
消化反応性試験装置を用いて、水温40℃の水380m
lに、3.35mmふるい通過試料生石灰を手早く調製
し、室温になるまで気密容器の中に入れていた生石灰7
6gを入れ、温度計の読みが3回続けて0.5℃以内の
変化になるまで温度を読み取り、この3回の読みの最初
の時間を全消化反応時間とする、アメリカ材料規格協会
の定めるASTM C110−76aに準ずる測定方法
で測定した、前記貝殻生石灰の全消化反応時間が60分
以上であることを特徴とする水のpH調整方法。Claims 1. A shell lime manufactured from a shell as a raw material.
A method of adjusting the pH of water using the method of adjusting the pH of water,
Using a digestion reactivity test device, 380 m of water at a water temperature of 40 ° C.
Quickly prepare 3.35mm sieve passing sample quicklime in l
And quicklime 7 which was put in the airtight container until it reached room temperature
6 g, and the reading of the thermometer is within 0.5 ° C for 3 consecutive times.
Read the temperature until it changes, the first of these three readings
Time is defined as the total digestion reaction time.
Measurement method according to ASTM C110-76a specified by
60 minutes total digestion reaction time of the shell quicklime measured in
A method for adjusting the pH of water characterized by the above .
0〜1250℃の温度で焼成して製造した貝殻生石灰でShell quicklime manufactured by firing at a temperature of 0 to 1250 ° C
ある請求項1に記載の水のpH調整方法。The method for adjusting the pH of water according to claim 1.
る請求項1に記載の水のpH調整方法。The method for adjusting the pH of water according to claim 1.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP35646291A JP3144499B2 (en) | 1991-12-25 | 1991-12-25 | PH adjustment method of water using shell quicklime |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP35646291A JP3144499B2 (en) | 1991-12-25 | 1991-12-25 | PH adjustment method of water using shell quicklime |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH05169069A JPH05169069A (en) | 1993-07-09 |
| JP3144499B2 true JP3144499B2 (en) | 2001-03-12 |
Family
ID=18449135
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP35646291A Expired - Lifetime JP3144499B2 (en) | 1991-12-25 | 1991-12-25 | PH adjustment method of water using shell quicklime |
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| Country | Link |
|---|---|
| JP (1) | JP3144499B2 (en) |
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|---|---|---|---|---|
| JPH09187775A (en) * | 1996-01-05 | 1997-07-22 | Ube Chem Ind Co Ltd | Hard-to-disintegrate magnesia ph adjustor for improving water quality and bottom quality |
| KR100385280B1 (en) * | 2001-03-23 | 2003-05-23 | 린나이코리아 주식회사 | Porous counteragent for disposing condensed water from gas boiler and a method for manufacturing the same |
| KR101648075B1 (en) * | 2016-01-29 | 2016-08-23 | 대구대학교 산학협력단 | Appararus and Method for anti-scaling on membrane using Carbon dioxide |
| KR101681151B1 (en) * | 2016-03-17 | 2016-12-01 | 한국건설기술연구원 | Water corrosiveness improvement system using granular alkaline chemical and water corrosiveness improvement method using the same |
| CA3167941A1 (en) * | 2020-02-14 | 2021-08-19 | Collidion, Inc. | Compositions, kits, methods and uses for cleaning, disinfecting, sterilizing and/or treating |
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1991
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