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JPS632891B2 - - Google Patents
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JPS632891B2 - - Google Patents

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Publication number
JPS632891B2
JPS632891B2 JP14189079A JP14189079A JPS632891B2 JP S632891 B2 JPS632891 B2 JP S632891B2 JP 14189079 A JP14189079 A JP 14189079A JP 14189079 A JP14189079 A JP 14189079A JP S632891 B2 JPS632891 B2 JP S632891B2
Authority
JP
Japan
Prior art keywords
slaked lime
tank
water
aqueous solution
constant
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
Application number
JP14189079A
Other languages
Japanese (ja)
Other versions
JPS5669223A (en
Inventor
Sadao Kojima
Masaaki Shimada
Kunio Sakai
Katsuo Horie
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kureha Corp
Original Assignee
Kureha Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kureha Corp filed Critical Kureha Corp
Priority to JP14189079A priority Critical patent/JPS5669223A/en
Priority to US06/134,051 priority patent/US4366142A/en
Priority to CA000348568A priority patent/CA1160427A/en
Priority to GB8010397A priority patent/GB2048107B/en
Priority to US06/223,286 priority patent/US4389376A/en
Publication of JPS5669223A publication Critical patent/JPS5669223A/en
Publication of JPS632891B2 publication Critical patent/JPS632891B2/ja
Granted legal-status Critical Current

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  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)

Description

【発明の詳細な説明】 本発明は上水道水のPH調整及び水道管の保護を
目的として水道水に注入する消石灰水溶液を連続
的かつ必要に応じて断続的に製造する装置に関す
るものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an apparatus for continuously and, if necessary, intermittently producing a slaked lime aqueous solution to be injected into tap water for the purpose of adjusting the pH of tap water and protecting water pipes.

従来上水道において管路に錆などが生じ赤水を
生じることがあり、その防止が必要となつてい
る。また水道施設経費の大部分を占める管路の寿
命は場所によつてまちまちであり、80年近く使用
しても殆んど錆の生じないところもあれば、一方
わずか2年ほどで管路を交換せばならない所もあ
る。このような管路の耐久性の相異は水道水の水
質によるもので、アルカリ度が高く腐蝕性の小さ
い水ほど管路の寿命が長いことが知られている。
Conventionally, in waterworks, rust etc. may occur in the pipes, producing red water, and there is a need to prevent this. Furthermore, the lifespan of pipes, which account for the majority of water facility costs, varies depending on the location; in some places, there is almost no rust even after nearly 80 years of use; There are some parts that need to be replaced. Such differences in the durability of pipes are due to the quality of tap water, and it is known that water with higher alkalinity and less corrosiveness has a longer lifespan.

管路の寿命を延ばし、水道水の赤水を防止する
ためには水道水のPHを調整することが必要であ
り、このため苛性ソーダ、ソーダ灰、消石灰など
の注入が行なわれており、最近では取扱いが容易
であるとの理由から苛性ソーダが多く使われてい
る。しかし苛性ソーダが単にPH調整機能しか有し
ないのに対し、消石灰を使用するときは管壁に炭
酸カルシウムの被膜をつくり、管路の腐蝕を防止
する機能をも有することで消石灰の使用がより望
ましいものである。それにもかかわらず消石灰が
あまり使用されないのは、溶けにくく溶液で貯蔵
するのに大きなタンクを要すること、粉末注入で
は連続計量注入が難しく溶け残りが底に沈積、付
着等を生ずること、またスラリーで注入すると途
中の管路内に沈積し易くまた消石灰に含有される
不溶物(例えばMgO、SiO2、Fe2O3等)が水道
水に混入するなどの理由によるものである。
In order to extend the life of pipes and prevent red water from forming in tap water, it is necessary to adjust the pH of tap water.For this purpose, caustic soda, soda ash, slaked lime, etc. are injected into the water. Caustic soda is often used because it is easy to use. However, while caustic soda only has the function of adjusting pH, when using slaked lime, it creates a calcium carbonate film on the pipe wall, which also has the function of preventing corrosion of pipes, making it more desirable to use slaked lime. It is. Despite this, slaked lime is not often used because it is difficult to dissolve and requires a large tank to store as a solution, it is difficult to continuously meter and pour powder, and the undissolved residue settles and sticks to the bottom, and because it is not used as a slurry. This is because when it is injected, it tends to deposit in the pipes along the way, and insoluble substances (for example, MgO, SiO 2 , Fe 2 O 3, etc.) contained in slaked lime mix into tap water.

最近消石灰注入による上述の不都合を解消する
ものとして槽の下部に金網を設け上下に仕切り、
該金網上に消石灰の堆積層を形成させ水を張つた
消石灰貯留溶解槽の下側より別に設けた定圧水槽
の水を一定流速で送入し、上部より消石灰飽和水
を取り出す方法が提案されている。
Recently, in order to solve the above-mentioned inconvenience caused by slaked lime injection, a wire mesh was installed at the bottom of the tank to divide it into upper and lower parts.
A method has been proposed in which a deposited layer of slaked lime is formed on the wire mesh, water is fed from a separate constant pressure water tank at a constant flow rate from the bottom of the slaked lime storage and dissolution tank filled with water, and slaked lime saturated water is taken out from the top. There is.

この方法によればストツク消石灰はそのままで
あり、溶液貯蔵に比べタンクは極めて小さくてす
み、また注入量だけ溶かすから溶解槽も小さくて
すみ全体として装置がコンパクトになると云われ
ている。
According to this method, the stock slaked lime remains as it is, and the tank is extremely small compared to solution storage, and since only the amount to be injected is dissolved, the dissolution tank is also small, and the overall apparatus is said to be compact.

しかしながら本発明者等の研究によれば、上記
方法においては最初の数時間は期待通りの濃度の
消石灰水溶液を取り出すことができるが、次第に
消石灰の濃度を低下してくる。
However, according to research conducted by the present inventors, in the above method, a slaked lime aqueous solution with an expected concentration can be taken out for the first few hours, but the concentration of slaked lime gradually decreases.

これは消石灰の堆積層に水の通路となる孔がで
き、時間の経過とともに孔が大きくなり、局部的
に消石灰の堆積層のない部分を水が通過し水と消
石灰の接触が良好に行なわれなくなることによ
る。また従来より提案されている金網上で消石灰
の堆積層を形成させる方式の場合は数カ月の短期
間では問題ないとしても数年間の長期の連続使用
では金網の目詰りが発生し、水の通路を閉塞させ
ることになる。即ち消石灰に含有する別量の砂若
しくは不溶物、または水道水に含有される鉄若し
くはその他微量の不溶物等により金網の目詰りを
発生させる。更に水中に存在している遊離炭酸は
Ca(OH)2の存在下ではCaCO3に転化する故、ス
ケーリングをおこし金網の目詰りを発生させる。
こうした不都合を完全に解消し消石灰飽和水を安
定して長時間連続して得ることについて本発明者
等が種々の研究を重ねた結果、溶解層内部に金網
を使用することなく安定して長期間連続的に消石
灰飽和水溶液を得る本発明に至つた。
This is because pores are formed in the slaked lime deposit layer, and as time passes, the pores become larger, allowing water to locally pass through areas where there is no slaked lime deposit, allowing good contact between water and slaked lime. By disappearing. In addition, in the case of the conventionally proposed method of forming a deposited layer of slaked lime on a wire mesh, although there may be no problem in a short period of several months, the wire mesh will become clogged if used continuously for several years, and the water passage will become blocked. It will cause a blockage. That is, the wire mesh is clogged by a separate amount of sand or insoluble matter contained in slaked lime, or by iron or other minute amounts of insoluble matter contained in tap water. Furthermore, the free carbonic acid present in water is
In the presence of Ca(OH) 2 , it is converted to CaCO 3 , causing scaling and clogging of the wire mesh.
As a result of various studies conducted by the present inventors to completely eliminate these inconveniences and obtain slaked lime saturated water stably and continuously for a long period of time, we have found that it is possible to obtain slaked lime-saturated water stably and continuously for a long period of time without using a wire mesh inside the dissolved layer. The present invention has been achieved to continuously obtain a saturated aqueous solution of slaked lime.

本発明は消石灰溶解槽として円筒または角筒の
筒型或は下部が逆截頭円錐型または逆截頭角錐型
(以下単に逆截頭錐型と記す)をなし該錐体の最
大径の部分が筒型をなす上部と連結してなる竪型
槽を用い、該槽上面に消石灰供給口を、又該槽上
端部に消石灰水溶液取出管を有する溢流液受部を
設け、かつこの槽の底部に給水口および垂直方向
に回転する1個または2個以上の撹拌翼を設け、
該撹拌翼を回転させながら底部の給水口より水を
一定または略一定の速度で送入して消石灰を流動
溶解させながら槽上部より連続的に消石灰水溶液
を取り出す装置に関する。
The present invention provides a slaked lime dissolving tank having a cylindrical or rectangular tube shape, or a lower part of which is an inverted truncated conical shape or an inverted truncated pyramidal shape (hereinafter simply referred to as an inverted truncated pyramidal shape), and the largest diameter portion of the cone. A vertical tank is used, in which a slaked lime supply port is provided on the top surface of the tank, and an overflow liquid receiving part with a slaked lime aqueous solution extraction pipe is provided at the top end of the tank. A water supply port and one or more stirring blades rotating vertically are provided at the bottom,
The present invention relates to a device that continuously takes out a slaked lime aqueous solution from the upper part of the tank while rotating the stirring blade and feeding water at a constant or substantially constant speed from the water supply port at the bottom to fluidize and dissolve the slaked lime.

本発明において消石灰溶解槽は上下の断面積が
同じである筒型であつてもよいが、槽の上部と底
部とで断面積の異なる少なくとも下部が逆截頭錐
型をなす槽を用いるのが好ましい。この底部から
水を供給するとき水流速は上部に行くに従つて低
下するから、断面積の小さい下部で撹拌するとき
消石灰粒子の流動する高さは比較的低く抑えるこ
とができる。即ち消石灰粒子の流動する高さの割
には強い撹拌力を与えることができるため、撹拌
翼は供給水を溶解槽内に均一に供給させるデイス
トリビユーターの役目をすると同時に、消石灰と
水との接触を効果的に行なわせ、水中の遊離炭酸
により生成する炭酸カルシウムや消石灰中に存在
する酸化マグネシウムより生成する水酸化マグネ
シウムが消石灰粒子表面を被覆して溶解困難とさ
せる現象を防止することが可能となり、未溶解消
石灰が殆んどなくなるまで長期間に亘り、略均一
な濃度の消石灰水溶液を得ることができる。
In the present invention, the slaked lime dissolving tank may have a cylindrical shape with the upper and lower cross-sectional areas being the same; however, it is preferable to use a tank in which the upper and lower sections have different cross-sectional areas and at least the lower part is in the shape of an inverted truncated cone. preferable. When water is supplied from the bottom, the water flow rate decreases toward the top, so when stirring at the bottom, where the cross-sectional area is small, the height at which the slaked lime particles flow can be kept relatively low. In other words, the stirring blades can provide a strong stirring force considering the height at which the slaked lime particles flow, so the stirring blades act as a distributor to uniformly supply the water into the dissolution tank, and at the same time, they also serve as a distributor to uniformly supply water into the dissolution tank. It is possible to prevent the phenomenon that calcium carbonate produced by free carbonic acid in water and magnesium hydroxide produced from magnesium oxide present in slaked lime coat the surface of slaked lime particles and make it difficult to dissolve. This makes it possible to obtain a slaked lime aqueous solution with a substantially uniform concentration over a long period of time until almost all undissolved dissolved lime disappears.

従つて消石灰溶解槽は撹拌翼の存在する下部に
対し上部の断面積が大なる逆截頭錐型をなす槽を
用いるのが好ましい。また撹拌翼としては垂直方
向に回転するものを用い、例えば水平に配置され
た回転軸に切欠き翼を複数個取付けた撹拌機が用
いられ、撹拌機は消石灰溶解槽底にある消石灰の
撹拌できない部分が生じないように撹拌翼を配置
する。このためには撹拌機は1個でよい場合もあ
るが、多くの場合槽の大きさに応じて複数個を適
宜組合せて設けられる。撹拌機に取付けられる翼
の長さは多くの場合10〜30cm程度のものが用いら
れる。
Therefore, it is preferable to use an inverted truncated cone-shaped slaked lime dissolving tank in which the cross-sectional area of the upper part is larger than that of the lower part where the stirring blades are present. In addition, stirring blades that rotate vertically are used, for example, a stirrer with multiple notched blades attached to a horizontally arranged rotating shaft, and the stirrer cannot stir the slaked lime at the bottom of the slaked lime dissolution tank. Arrange the stirring blades so that no lumps occur. For this purpose, a single stirrer may be sufficient in some cases, but in many cases a plurality of stirrers may be provided in appropriate combinations depending on the size of the tank. The blades attached to the stirrer are often about 10 to 30 cm long.

撹拌翼として垂直方向に回転させることによつ
て、従来の回転軸が槽上面から下部に貫通して水
平方向に撹拌翼が回転するものに比し、槽上部の
消石灰の沈降部には回転軸のような回転体がなく
なるので、槽内液の上昇流が乱されることなく、
消石灰粒子の分離が容易になる。さらに、槽内に
挿入する回転軸を短かくすることができるように
よつて回転軸を支持する架台も小規模のものとす
ることができるので好都合である。また槽底部か
ら回転軸を槽内に垂直に貫入させる手段もある
が、この場合には槽底に存在する固体消石灰粒子
や不溶解物のため液洩れのない回転シールの使用
には技術上の困難を伴なう。本発明の側壁から回
転軸を水平に槽内に貫入させる場合には上記垂直
に貫入する場合に比し比較的回転シールの使用は
容易となる利点がある。
By rotating the stirring blade vertically, the rotating shaft penetrates from the top of the tank to the bottom and the stirring blade rotates horizontally. Since there is no rotating body, the upward flow of the liquid in the tank is not disturbed.
Separation of slaked lime particles becomes easier. Furthermore, since the rotating shaft inserted into the tank can be shortened, the pedestal supporting the rotating shaft can also be made smaller, which is advantageous. There is also a method of vertically penetrating the rotating shaft into the tank from the bottom of the tank, but in this case, due to the solid slaked lime particles and undissolved substances present at the bottom of the tank, it is difficult to use a rotary seal that does not leak. accompanied by difficulties. When the rotary shaft of the present invention penetrates horizontally into the tank from the side wall, there is an advantage that the use of the rotary seal is relatively easier than when the rotary shaft penetrates vertically.

撹拌機は運転の初期より回転させるが、用いる
消石灰が溶解し易い微細粒子を多量に含むときは
撹拌するまでもなく槽上部より飽和濃度に近い消
石灰水溶液が得られる。従つてこのような場合消
石灰微細粒子が殆んど溶解し、得られる消石灰水
溶液の濃度が低下し始める頃より撹拌機を回転さ
せればよい。勿論運転の最初から撹拌機を回転さ
せても何ら支障はない。
The stirrer is rotated from the beginning of operation, but when the slaked lime used contains a large amount of easily soluble fine particles, an aqueous slaked lime solution with a near saturated concentration can be obtained from the upper part of the tank without stirring. Therefore, in such a case, the stirrer may be rotated from the time when most of the slaked lime fine particles are dissolved and the concentration of the obtained slaked lime aqueous solution begins to decrease. Of course, there is no problem in rotating the agitator from the beginning of the operation.

撹拌機の回転速度は撹拌により流動する消石灰
粒子が槽の上端より溢流しない範囲であればよい
が、撹拌速度があまり高速のときはそれだけ消石
灰粒子が高くまで流動するため溶解槽高を徒らに
高くする必要が生じ、また消費動力も高くなるの
で好ましくない。
The rotational speed of the stirrer should be within a range where the slaked lime particles flowing through stirring do not overflow from the top of the tank, but if the stirring speed is too high, the slaked lime particles will flow to a higher height, making it difficult to increase the height of the dissolution tank. This is not preferable because it requires a higher power consumption and the power consumption also increases.

次に本発明で用いる装置を附図により説明す
る。
Next, the apparatus used in the present invention will be explained with reference to the accompanying drawings.

第1図は本発明で用いる装置の具体例であり、
消石灰溶解槽1の上面に消石灰供給口2、該槽1
の上端部に消石灰水溶液取出口3を有する溢流液
受部4を設け、かつ該槽1の底部に給水管5およ
び1個または2個以上の撹拌機6を設けてなる。
該撹拌機6は槽下部側面より取付けられ槽内にお
いて水平軸端に撹拌翼が垂直回転するよう設けら
れる。給水管5はその開口部を好ましくは下向き
とし、消石灰スラリーの逆流を防止する。また給
水管5の開口部は複数個に分割されていてもよ
い。また槽1の上流部は液が溢流するとき槽内の
流動を乱さないよう溢流部を水平にする必要があ
り、好ましくは切り欠きノツチを設ける。
FIG. 1 shows a specific example of the device used in the present invention,
A slaked lime supply port 2 on the top surface of the slaked lime dissolving tank 1, the tank 1
An overflow receiver 4 having an aqueous slaked lime solution outlet 3 is provided at the upper end of the tank 1, and a water supply pipe 5 and one or more stirrers 6 are provided at the bottom of the tank 1.
The stirrer 6 is attached from the side of the lower part of the tank, and is provided within the tank so that the stirring blade rotates vertically at the end of a horizontal shaft. The opening of the water supply pipe 5 is preferably directed downward to prevent backflow of the slaked lime slurry. Further, the opening of the water supply pipe 5 may be divided into a plurality of parts. Further, the upstream part of the tank 1 needs to be horizontal so as not to disturb the flow in the tank when the liquid overflows, and preferably a notch is provided.

このような装置において消石灰溶解槽1へ消石
灰供給口2より所定量の消石灰を投入し、給水管
5より新たな水を一定または略一定速度で供給す
る。新たな水を一定または略一定の速度で供給す
るには、例えば定圧水槽7を設け、管8より新た
な水を導入し、溢流管9により定圧水槽7の水位
を一定に保持させながら給水管10、流量計11
を通して給水管5より槽1に供給する。このとき
水の流速が槽の上部で2mm/sec以下となるよう
にするのが好ましい。
In such an apparatus, a predetermined amount of slaked lime is put into the slaked lime dissolving tank 1 from the slaked lime supply port 2, and fresh water is supplied from the water supply pipe 5 at a constant or substantially constant rate. To supply new water at a constant or substantially constant rate, for example, a constant pressure water tank 7 is provided, new water is introduced through a pipe 8, and water is supplied while maintaining the water level in the constant pressure water tank 7 constant through an overflow pipe 9. Pipe 10, flow meter 11
The water is supplied to the tank 1 from the water supply pipe 5 through the water supply pipe 5. At this time, it is preferable that the flow rate of water be 2 mm/sec or less at the top of the tank.

このように撹拌機により消石灰を流動溶解させ
ながら新たな水を供給するとき、消石灰が殆んど
なくなるまで濃度約1500〜1800ppm(水温により
異なる)の消石灰水溶液が溢流液受部を経て消石
灰水溶液取出口3より連続して得られる。消石灰
水溶液の濃度を気温にかかわらず一定にするには
定圧水槽内にヒーターを設け、給水の温度を一定
にコントロールすればよい。尚12は不溶物取出
管である。
When fresh water is supplied while slaked lime is fluidized and dissolved by the stirrer, the slaked lime aqueous solution with a concentration of approximately 1500 to 1800 ppm (depending on the water temperature) passes through the overflow liquid receiver until the slaked lime is almost gone. It can be obtained continuously from the outlet 3. In order to keep the concentration of the slaked lime aqueous solution constant regardless of the temperature, a heater may be installed in the constant pressure water tank to control the temperature of the water supply to be constant. Note that 12 is an insoluble matter removal tube.

また本発明の実施に際しては第2図に示す如く
2個の消石灰溶解槽1,1′を互いの消石灰水溶
液取出口3,3′が切換えバルブ13,13′によ
り他の溶解槽の給水管5,5′に連結するように
設け、一方の溶解槽より得られる液の消石灰濃度
が低下しはじめたとき、この水溶液を更に他方の
溶解槽に通して直列に使用し高濃度の消石灰水溶
液を連続して得るのが原料消石灰を略完全に利用
することができて好ましい。
In addition, when carrying out the present invention, as shown in FIG. , 5', and when the concentration of slaked lime in the solution obtained from one dissolution tank begins to decrease, this aqueous solution is further passed through the other dissolution tank and used in series to continuously provide a high concentration slaked lime aqueous solution. It is preferable to obtain the slaked lime by substantially completely utilizing the raw material slaked lime.

即ち最初の溶解槽1より流出する液は、消石灰
が溶解槽内に充分存在するときは殆んど飽和水溶
液であり、敢えて第2の溶解槽1′に導入する必
要はなく、そのまま消石灰水溶液取出管3より取
り出してもよい。しかし長期間運転していると溶
解槽1内の消石灰が少なくなり、次第に消石灰水
溶液取出管3より得られる消石灰水溶液の濃度が
低下してくる。少なくともこの消石灰水溶液の濃
度が低下しはじめる前より、第1の溶解槽1より
得られる溶液を切換えバルブ13により第2の溶
解槽1′に導入する。このようにすることにより
第1の溶解槽1の消石灰を略完全に利用しながら
消石灰飽和水溶液を連続して得ることができる。
第1の溶解槽1の消石灰を消費した後に定圧水槽
7よりの給水を切換えバルブ14により第2の溶
解槽1′に切換える。このとき第2溶解槽1′中に
は充分消石灰が存在し、消石灰水溶液取出管3′
より得られる水溶液は約1500〜1800ppmの濃度で
得られる。この間に第1の溶解槽1の中の不溶物
を不溶物取出管12より除去し、新たに消石灰を
所定量入れ水を張つておく。そして第2の溶解槽
1′により得られる消石灰水溶液の濃度が低下し
はじめる前に切換えバルブ13′により第2の溶
解槽より水溶液を第1の溶解槽に導入し、同様に
運転して第1の溶解槽の水溶液取出管3より消石
灰水溶液を得る。このように逐次切換え使用する
ことにより原料消石灰を略完全に利用しながら消
石灰水溶液を製造することができる。
That is, the liquid flowing out from the first dissolving tank 1 is almost a saturated aqueous solution when there is sufficient slaked lime in the dissolving tank, and there is no need to introduce it into the second dissolving tank 1', and the slaked lime aqueous solution can be taken out as it is. It may also be taken out from tube 3. However, when operating for a long period of time, the amount of slaked lime in the dissolution tank 1 decreases, and the concentration of the slaked lime aqueous solution obtained from the slaked lime aqueous solution extraction pipe 3 gradually decreases. At least before the concentration of the slaked lime aqueous solution begins to decrease, the solution obtained from the first dissolution tank 1 is introduced into the second dissolution tank 1' by the switching valve 13. By doing so, the slaked lime saturated aqueous solution can be continuously obtained while substantially completely utilizing the slaked lime in the first dissolution tank 1.
After the slaked lime in the first dissolving tank 1 is consumed, the water supply from the constant pressure water tank 7 is switched to the second dissolving tank 1' by the switching valve 14. At this time, there is sufficient slaked lime in the second dissolution tank 1', and the slaked lime aqueous solution extraction pipe 3'
The resulting aqueous solution has a concentration of about 1500-1800 ppm. During this time, the insoluble matter in the first dissolution tank 1 is removed from the insoluble matter removal pipe 12, and a predetermined amount of slaked lime is added to the tank and water is filled. Then, before the concentration of the slaked lime aqueous solution obtained in the second dissolution tank 1' begins to decrease, the aqueous solution is introduced from the second dissolution tank into the first dissolution tank using the switching valve 13', and the operation is continued in the same manner. A slaked lime aqueous solution is obtained from the aqueous solution take-out pipe 3 of the dissolution tank. By sequentially switching and using the slaked lime in this manner, the slaked lime aqueous solution can be produced while making almost complete use of the raw slaked lime.

実施例 底部内径334mmφ、上部内径625mmφ、高さ2800
mmの下部逆截頭円錐部の高さが1400mmで、上部が
円筒である第1図に示す溶解装置で、該装置円錐
部側壁に支持され、且つ水平に貫入された回転軸
の周りに垂直方向に回転する外径175mmφのター
ビン形撹拌翼を持つ装置を用いた。この溶解槽に
水を張り消石灰20Kg(63μ以下の微細粒子80重量
%含む)(約4日連続運転相当量)を投入し、定
圧水槽で一定圧力に保持した水道水を、底部の内
径334mmφの部分の流速が0.4〜0.8mm/secで送入
し、かつ撹拌機を周速0.5〜1.0m/secで回転さ
せ、槽の上端部の取出管より消石灰水溶液を連続
的に取り出した。得られた水溶液は未溶解消石灰
が殆んどなくなるまで1500〜1800ppmで約一定濃
度の消石灰水溶液であつた。尚このときの消石灰
粒子の流動層部分の高さは1600〜1800mmであつ
た。
Example Bottom inner diameter 334mmφ, top inner diameter 625mmφ, height 2800
The melting apparatus shown in Fig. 1 has a lower inverted truncated conical part with a height of 1400 mm and a cylindrical upper part. A device with a turbine-type stirring blade with an outer diameter of 175 mmφ that rotates in the same direction was used. This dissolution tank was filled with water, 20kg of slaked lime (containing 80% by weight of fine particles of 63μ or less) (equivalent to about 4 days of continuous operation) was added, and tap water maintained at a constant pressure in a constant pressure water tank was poured into a tank with an inner diameter of 334mmφ at the bottom. The slaked lime aqueous solution was continuously taken out from the take-out pipe at the upper end of the tank by feeding the tank at a flow rate of 0.4 to 0.8 mm/sec and rotating the stirrer at a circumferential speed of 0.5 to 1.0 m/sec. The resulting aqueous solution was a slaked lime aqueous solution with a constant concentration of 1,500 to 1,800 ppm until almost all undissolved dissolved lime disappeared. The height of the fluidized bed portion of the slaked lime particles at this time was 1600 to 1800 mm.

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

第1図は本発明装置の1例を示す要領図であ
り、第2図は本発明の他の実施態様を示す要領図
である。 1,1′……消石灰溶解槽、2……消石灰供給
口、3,3′……消石灰水溶液取出管、4……溢
流液受部、5,5′……給水管、6……撹拌機、
7……定圧水槽、9……溢流管、10……給水
管、11……流量計、12……不溶物取出管、1
3,13′,14……切換えバルブ。
FIG. 1 is a schematic diagram showing one example of the apparatus of the present invention, and FIG. 2 is a schematic diagram showing another embodiment of the present invention. 1, 1'... Slaked lime dissolving tank, 2... Slaked lime supply port, 3, 3'... Slaked lime aqueous solution extraction pipe, 4... Overflow liquid receiver, 5, 5'... Water supply pipe, 6... Stirring machine,
7... Constant pressure water tank, 9... Overflow pipe, 10... Water supply pipe, 11... Flow meter, 12... Insoluble matter removal pipe, 1
3, 13', 14...Switching valve.

Claims (1)

【特許請求の範囲】[Claims] 1 消石灰溶解槽が筒型または下部が逆截頭錐型
をなし該錐体の最大径の部分が筒型をなす上部と
連結してなり、該槽上面に消石灰供給口を、又該
槽上端部に消石灰水溶液取出管を有する溢流液受
部を設けた消石灰溶解槽1個または互いの消石灰
水溶液取出管が切換バルブにより他の槽の給水導
管に連結するように配設した消石灰溶解槽2個よ
りなり、かつ該槽底部に給水口および垂直方向に
回転する1個または2個以上の撹拌機を設けてな
り、定圧水槽の水位を一定に保持しながら一定ま
たは略一定の速度で水道水を該消石灰溶解槽に送
入する手段を接続してなることを特徴とする消石
灰水溶液の連続製造装置。
1 The slaked lime dissolving tank has a cylindrical shape or an inverted truncated cone shape at the bottom, and the largest diameter part of the cone is connected to the cylindrical upper part, and a slaked lime supply port is provided on the top surface of the tank, and a slaked lime supply port is provided at the top of the tank. One slaked lime dissolving tank equipped with an overflow liquid receiving part with a slaked lime aqueous solution extraction pipe in the section, or two slaked lime dissolving tanks arranged so that each slaked lime aqueous solution extraction pipe is connected to the water supply pipe of the other tank by a switching valve. The water tank is equipped with a water inlet and one or more agitators rotating in the vertical direction at the bottom of the tank, and tap water is supplied at a constant or almost constant speed while maintaining a constant water level in the constant pressure water tank. 1. An apparatus for continuously producing a slaked lime aqueous solution, characterized in that the slaked lime aqueous solution is connected to a means for feeding the slaked lime aqueous solution into the slaked lime dissolving tank.
JP14189079A 1979-03-28 1979-11-01 Preparation of aqueous solution of slaked line and its device Granted JPS5669223A (en)

Priority Applications (5)

Application Number Priority Date Filing Date Title
JP14189079A JPS5669223A (en) 1979-11-01 1979-11-01 Preparation of aqueous solution of slaked line and its device
US06/134,051 US4366142A (en) 1979-03-28 1980-03-26 Method and apparatus for the preparation of slaked lime solution
CA000348568A CA1160427A (en) 1979-03-28 1980-03-27 Method and apparatus for the preparation of slaked lime solution
GB8010397A GB2048107B (en) 1979-03-28 1980-03-27 Method and apparatus for the continuous preparation of slaked lime solution
US06/223,286 US4389376A (en) 1979-03-28 1981-01-08 Apparatus for the preparation of slaked lime solution

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14189079A JPS5669223A (en) 1979-11-01 1979-11-01 Preparation of aqueous solution of slaked line and its device

Publications (2)

Publication Number Publication Date
JPS5669223A JPS5669223A (en) 1981-06-10
JPS632891B2 true JPS632891B2 (en) 1988-01-21

Family

ID=15302539

Family Applications (1)

Application Number Title Priority Date Filing Date
JP14189079A Granted JPS5669223A (en) 1979-03-28 1979-11-01 Preparation of aqueous solution of slaked line and its device

Country Status (1)

Country Link
JP (1) JPS5669223A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2678718B2 (en) * 1992-12-25 1997-11-17 呉羽化学工業株式会社 Method for forming protective coating in tap water pipe

Also Published As

Publication number Publication date
JPS5669223A (en) 1981-06-10

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