JPH04310285A - Treatment of undissolved matter generated in process for manufacturing aqueous solution of slaked lime - Google Patents

Treatment of undissolved matter generated in process for manufacturing aqueous solution of slaked lime

Info

Publication number
JPH04310285A
JPH04310285A JP10306691A JP10306691A JPH04310285A JP H04310285 A JPH04310285 A JP H04310285A JP 10306691 A JP10306691 A JP 10306691A JP 10306691 A JP10306691 A JP 10306691A JP H04310285 A JPH04310285 A JP H04310285A
Authority
JP
Japan
Prior art keywords
slaked lime
carbon dioxide
undissolved matter
undissolved
calcium carbonate
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP10306691A
Other languages
Japanese (ja)
Inventor
Norimasa Nonaka
規正 野中
Tadaaki Tomari
泊り 忠昭
Kazuo Isono
磯野 一男
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.)
DICK DEGUREMON KK
Original Assignee
DICK DEGUREMON KK
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 DICK DEGUREMON KK filed Critical DICK DEGUREMON KK
Priority to JP10306691A priority Critical patent/JPH04310285A/en
Publication of JPH04310285A publication Critical patent/JPH04310285A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To subject the undissolved matter generated when an aqueous slaked lime solution is prepared to neutralization treatment. CONSTITUTION:The undissolved matter in a dissolving tank 5 is transferred to a reaction tank 11 through an undissolved matter withdrawing pipe 19 and carbon dioxide is sent in the reaction tank 11 from a carbon dioxide cylinder 15 through a gassifier 16 and a diffusing pipe 12. Slaked lime contained in the undissolved matter is reacted with carbon dioxide in the reaction tank 11 to be precipitated as water-insoluble calcium carbonate. At this time, when pH is adjusted to 9.5-11.0 by carbon dioxide, the amount of formed calcium carbonate becomes max. A separated liquid being a supernatant is further transferred to a neutralizing tank 13 to be reacted with carbon dioxide sent from the carbon dioxide cylinder 15 through the gassifier 16 and the diffusing pipe 12. Since a small amount of calcium carbonate contained in the separated liquid is dissolved as calcium bicarbonate and pH is suppressed to about 7, treated water can be discharged. Calcium carbonate formed in the reaction tank 11 is withdrawn to be reutilized.

Description

【発明の詳細な説明】[Detailed description of the invention]

【0001】0001

【産業上の利用分野】本発明は、消石灰水溶液の製造過
程で発生する未溶解物の処理方法、特に上水道水のpH
調整に用いる消石灰水溶液を製造する際に発生する不溶
解物の処理方法に関する。
[Industrial Application Field] The present invention relates to a method for treating undissolved substances generated during the production process of slaked lime aqueous solution, and in particular,
This invention relates to a method for treating insoluble matter generated when producing a slaked lime aqueous solution used for adjustment.

【0002】0002

【従来の技術】上水道水のpH調整に消石灰を利用する
ことは、赤水抑制の効果があり、また健康上有益なこと
がよく知られている。しかし、消石灰の粉体をそのまま
注入することは、投入時に粉塵が飛び散り作業環境を悪
化させるばかりでなく、添加量の調整が難しく、また消
石灰中の不溶解物がろ過池を閉塞させたり、給水濁度を
上昇させたりするので好ましくない。かかる観点から、
上水道水のpH調整、アルカリ度の調整には消石灰の飽
和溶液が用いられている。
BACKGROUND OF THE INVENTION It is well known that the use of slaked lime to adjust the pH of tap water has the effect of suppressing red water and is also beneficial for health. However, injecting slaked lime powder as it is not only causes dust to scatter when it is added, worsening the working environment, but it is also difficult to adjust the amount added, and insoluble matter in the slaked lime may clog the filter or water supply. This is not preferable because it increases turbidity. From this point of view,
A saturated solution of slaked lime is used to adjust the pH and alkalinity of tap water.

【0003】従来、上記目的のためにヨーロッパにおい
ては、サチュレーター(溶解槽)と称する上向流ブラン
ケットタイプの消石灰連続溶解装置が使用されている。 また、わが国においても特公昭62−23634号、特
公昭63−2890号、特公昭63−2891号、特公
昭63−35574号、特公昭63−58762号及び
特公昭63−58763号公報に見られるように種々の
溶解槽が開発されている。
[0003] Conventionally, an upflow blanket type continuous slaked lime dissolving device called a saturator (dissolving tank) has been used in Europe for the above purpose. In addition, in Japan, it can be found in Japanese Patent Publication No. 62-23634, Special Publication No. 63-2890, Special Publication No. 63-2891, Special Publication No. 35574-1980, Special Publication No. 63-58762, and Special Publication No. 63-58763. Various types of dissolution tanks have been developed.

【0004】0004

【発明が解決しようとする課題】しかしながら、サチュ
レーターは、消石灰中に含まれる不純物であるマグネシ
ア、ケイ酸、酸化鉄や、その他消石灰が炭酸ガスと反応
して生じた炭酸カルシウムなどの不溶解物を除くために
、常に一定量の未溶解物を取り出さなければならない。 この未溶解物中には、未溶解の消石灰を多く含み、pH
値も12〜13と高いため、水質汚濁防止法上、そのま
ま河川に排出することには問題がある。そこで、未溶解
物を酸で中和して放流しているが、この場合、安価な硫
酸を使用すると、反応で生ずる硫酸カルシウムの溶解度
が小さいため、反応時間が30分以上かかり、更にpH
の安定性が悪いため、正確なpHの調整に多くの労力と
時間を要する。塩酸で中和する場合には、かかる問題は
解決されるが、浄水場は公共的な場所でもあるため、塩
酸の運搬、取り扱い、貯蔵に危険が伴う。さらに酸の過
剰注入の虞があり、アルカリ注入設備が必要となるなど
の問題が生じる。
[Problems to be Solved by the Invention] However, saturators do not remove impurities contained in slaked lime, such as magnesia, silicic acid, iron oxide, and other insoluble substances such as calcium carbonate produced when slaked lime reacts with carbon dioxide gas. A certain amount of undissolved material must always be removed for removal. This undissolved material contains a large amount of undissolved slaked lime, and the pH
Since the value is as high as 12 to 13, it is problematic to discharge it directly into rivers under the Water Pollution Control Act. Therefore, the undissolved substances are neutralized with acid and discharged. However, in this case, if cheap sulfuric acid is used, the reaction time will be longer than 30 minutes due to the low solubility of calcium sulfate produced in the reaction, and the pH will increase further.
Because of its poor stability, it takes a lot of effort and time to accurately adjust the pH. Neutralization with hydrochloric acid solves this problem, but since water treatment plants are also public places, there are risks associated with transporting, handling, and storing hydrochloric acid. Furthermore, there is a risk of excessive injection of acid, which causes problems such as the need for alkali injection equipment.

【0005】また、特公昭62─23634号公報にお
いては、取り出した未溶解物を更に水で溶解してpH1
0以下の消石灰水溶液を消石灰飽和溶液と共に上水道水
のpH調整に用いている。この方法では未溶解物の中和
という問題は緩和されるが、微量の不純物が上水道水に
混入するため、水質上問題がある。また、未溶解物の溶
解には多量の水が必要となり、消石灰水溶液のpH値も
一定しないため、消石灰水溶液の注入量を最適に制御す
ることが難しい。
[0005] Furthermore, in Japanese Patent Publication No. 62-23634, the undissolved material taken out is further dissolved with water and the pH is adjusted to 1.
A slaked lime aqueous solution with a concentration of 0 or less is used together with a slaked lime saturated solution to adjust the pH of tap water. Although this method alleviates the problem of neutralization of undissolved substances, it causes water quality problems because trace amounts of impurities are mixed into tap water. Further, a large amount of water is required to dissolve undissolved substances, and the pH value of the slaked lime aqueous solution is not constant, so it is difficult to optimally control the injection amount of the slaked lime aqueous solution.

【0006】更に、特公昭63−2890号、特公昭6
3−2891号、特公昭63−35574号、特公昭6
3−58762号及び特公昭63−58763号公報に
おいては、不溶解物を溶解槽より取り出すことが示され
ているが、その処理方法については何の記載もないので
、前記サチュレーターのような問題が生じる。
[0006] Furthermore, Special Publication No. 63-2890, Special Publication No. 63-2890,
No. 3-2891, Special Publication No. 63-35574, Special Publication No. 1983
No. 3-58762 and Japanese Patent Publication No. 63-58763 disclose that undissolved matter is taken out from the dissolving tank, but there is no description of how to dispose of the undissolved matter, so problems like the saturator mentioned above may not occur. arise.

【0007】したがって、以前より上水道水のpH調整
に消石灰の飽和水溶液が望ましいとされながらも、上記
問題に対する効果的な解決方法がなく、消石灰の上水道
水における利用が制限され、処理法の早期開発が望まれ
ていた。
Therefore, although a saturated aqueous solution of slaked lime has long been considered desirable for adjusting the pH of tap water, there is no effective solution to the above problem, and the use of slaked lime in tap water is limited, leading to the early development of treatment methods. was desired.

【0008】[0008]

【課題を解決するための手段】上記要望に答えるため、
本発明者等は溶解槽から取り出した未溶解物の中和方法
について種々検討した結果、消石灰水溶液を製造する溶
解槽から未溶解物を引き出し、その未溶解物を炭酸ガス
で反応させると、不溶解の炭酸カルシウムとなって沈降
するので、中和後のpH上昇も防げ、安全で、着実なp
H調整が行えることを見出した。特に、炭酸ガスで中和
するときは、第1段階で未溶解物をpH9.5〜11.
0に中和し、炭酸カルシウムを生成沈澱させた後、更に
その分離液を炭酸ガスで中和することが望ましい。
[Means for solving the problem] In order to meet the above request,
As a result of various studies on methods for neutralizing the undissolved matter taken out from the dissolution tank, the present inventors found that if the undissolved matter was extracted from the dissolution tank for producing a slaked lime aqueous solution and the undissolved matter was reacted with carbon dioxide gas, the undissolved matter could be neutralized. Since it becomes dissolved calcium carbonate and settles, it prevents the pH from increasing after neutralization, and provides a safe and steady pH.
It was discovered that H adjustment can be performed. In particular, when neutralizing with carbon dioxide gas, the undissolved matter is removed at pH 9.5 to 11 in the first step.
After neutralizing to 0 and precipitating calcium carbonate, it is desirable to further neutralize the separated liquid with carbon dioxide gas.

【0009】[0009]

【作用】一般に、懸濁物質を含む飽和濃度以上の消石灰
溶解液をpH7に中和して放置すると、懸濁物質の再溶
解などにより、pHが上昇する現象が認められる。例え
ば、溶解槽から取り出した未溶解物を硫酸で中和すると
、中和に要する時間が特定できないばかりでなく、pH
7で酸の添加を中止しても、2〜3時間の間、pHの上
昇が認められる。
[Function] Generally, when a slaked lime solution containing suspended matter at a saturation concentration or higher is neutralized to pH 7 and left to stand, a phenomenon is observed in which the pH increases due to redissolution of the suspended matter. For example, when undissolved substances taken out from a dissolution tank are neutralized with sulfuric acid, not only the time required for neutralization cannot be determined, but also the pH
Even if acid addition is stopped at 7, an increase in pH is observed for 2 to 3 hours.

【0010】一方、このような中和に炭酸ガスを用いる
と、pH9.5〜11.0(望ましくはpH10.0前
後)まで中和された時点で、残存している消石灰が容易
に炭酸カルシウムとなって沈澱し、未溶解物中に含まれ
る炭酸カルシウムとともに回収が可能となる。したがっ
て、沈澱物を回収した後、分離液を再度炭酸ガスにより
中和すれば、pH値5.8〜8.6に容易に調整でき、
しかもわずかに残存する炭酸カルシウムが重炭酸塩とな
って溶解するので、水質汚濁防止法に定める基準に適合
させることができる。過剰の炭酸ガスを供給した場合で
も、pHは6.3以下になることはなく、塩酸などの酸
を過剰に用いた場合のように、アルカリ注入の必要がな
い。したがって、溶解槽から取り出した未溶解物を炭酸
ガスで中和することにより、安全で、着実なpH調整が
行える。また、本発明を実施することにより上水道水に
連続して消石灰飽和溶液を注入することが可能になる。 一方、回収した炭酸カルシウムは、ゴム、プラスチック
、肥料工業等に直接利用可能であり、また、生石灰、消
石灰の原料ともなるため、利用範囲も広く資源の無駄が
ない。
On the other hand, when carbon dioxide gas is used for such neutralization, the remaining slaked lime is easily converted to calcium carbonate once the pH is neutralized to 9.5 to 11.0 (preferably around pH 10.0). It precipitates and can be recovered together with the calcium carbonate contained in the undissolved matter. Therefore, after collecting the precipitate, if the separated liquid is neutralized again with carbon dioxide gas, the pH value can be easily adjusted to 5.8 to 8.6.
Moreover, since the slight remaining calcium carbonate becomes bicarbonate and dissolves, it can meet the standards set by the Water Pollution Control Law. Even when an excess of carbon dioxide gas is supplied, the pH does not fall below 6.3, and there is no need to inject alkali, unlike when an excess of acid such as hydrochloric acid is used. Therefore, by neutralizing the undissolved matter taken out from the dissolution tank with carbon dioxide gas, safe and steady pH adjustment can be performed. Further, by implementing the present invention, it becomes possible to continuously inject a slaked lime saturated solution into tap water. On the other hand, the recovered calcium carbonate can be directly used in the rubber, plastic, fertilizer industries, etc., and can also be used as a raw material for quicklime and slaked lime, so it can be used in a wide range of applications and does not waste resources.

【0011】[0011]

【実施例】次に、図1を参照して、本発明にかかる処理
方法を詳しく説明する。図1において1は消石灰の予備
溶解槽であり、ここに投入された消石灰は水に溶解され
スラリー化される。その濃度は、一般には、5〜15%
の範囲の濃度の値に調整される。前記濃度に調整された
消石灰スラリーは、消石灰スラリー移送ポンプ3により
、溶解槽(サチュレーター)5の中に垂直に配置された
消石灰スラリー供給管6に供給される。溶解槽5は、好
ましくは図示するようにスラリー供給管6と連通する攪
拌チューブ7、攪拌機9及びドラフトチューブ10を備
えることが望ましい。溶解槽5に供給された消石灰スラ
リーは、図示する給水管18よりフローメーター4で調
整されて一定速度で供給される水と共に攪拌混合されな
がら攪拌チューブ7内を上昇し、次いでドラフトチュー
ブ10の中を下降する。未溶解の消石灰や不溶解物は、
溶解槽5の下部でブランケットゾーンを形成するが、攪
拌機9の吸引力により、消石灰スラリー供給管6により
連続して供給される消石灰スラリーと供給管18により
同じく連続して供給される水と共に、攪拌チューブ7及
びドラフトチューブ10の中を流動循環する。このよう
に、消石灰スラリーを流動循環させながら水を供給する
ことにより、消石灰粒子の流出を抑え、連続して飽和濃
度に近い消石灰水溶液を得ることが可能となる。 このときの消石灰水溶液の濃度は、温度により異なるが
約0.1%〜0.18%であり、この濃度は、更に供給
管18により供給される水の供給速度と消石灰スラリー
供給管6により供給される消石灰スラリーの供給速度に
よって変動する。消石灰水溶液は溶解槽5の上部に設け
られた三角ノッチ状の越流堰を溢流してトラフ8に集め
られ、そこから注入点17に導かれる。
EXAMPLE Next, the processing method according to the present invention will be explained in detail with reference to FIG. In FIG. 1, reference numeral 1 denotes a slaked lime preliminary dissolution tank, in which slaked lime is dissolved in water and made into a slurry. Its concentration is generally 5-15%
is adjusted to a concentration value in the range of . The slaked lime slurry adjusted to the above concentration is supplied by a slaked lime slurry transfer pump 3 to a slaked lime slurry supply pipe 6 vertically arranged in a dissolution tank (saturator) 5. The dissolution tank 5 preferably includes a stirring tube 7 communicating with the slurry supply pipe 6, a stirrer 9, and a draft tube 10 as shown in the figure. The slaked lime slurry supplied to the dissolution tank 5 rises in the stirring tube 7 while being stirred and mixed with water that is supplied at a constant rate from the water supply pipe 18 shown in the figure, adjusted by the flow meter 4, and then rises in the draft tube 10. descend. Undissolved slaked lime and insoluble matter are
A blanket zone is formed at the bottom of the dissolution tank 5, and due to the suction force of the agitator 9, the slaked lime slurry is continuously supplied through the slaked lime slurry supply pipe 6, and the water is also continuously supplied through the supply pipe 18, and the mixture is stirred. The fluid circulates through the tube 7 and draft tube 10. In this way, by supplying water while fluidly circulating the slaked lime slurry, it is possible to suppress the outflow of slaked lime particles and to continuously obtain a slaked lime aqueous solution with a concentration close to saturation. The concentration of the slaked lime aqueous solution at this time varies depending on the temperature, but is approximately 0.1% to 0.18%. It varies depending on the supply rate of slaked lime slurry. The slaked lime aqueous solution overflows a triangular notch-shaped overflow weir provided at the top of the dissolution tank 5, is collected in a trough 8, and is guided to an injection point 17 from there.

【0012】一方、溶解槽5の下部でブランケットゾー
ンを形成している、未溶解の消石灰や炭酸カルシウムは
、溶解槽5の底部に設けられた未溶解物引き抜き管19
により反応槽11に導入される。未溶解物の引き抜きは
、好ましくはタイマーにより時間を設定し、一定時間毎
に行うことが望ましい。反応槽11には炭酸ガスボンベ
15から気化器16及びガス供給管もしくは散気管12
を介して炭酸ガスが供給される。反応槽11に導入され
た未溶解の消石灰は液中に分散された炭酸ガスと反応し
て炭酸カルシウムとなり沈降する。この時のpHを9.
5〜11.0、望ましくはpH10.0に調整すること
により、生成する炭酸カルシウムの量が最大となる。反
応槽11で生成した炭酸カルシウムや不溶解物は溶液か
ら分離して沈澱するので、上澄みの分離液は、さらに中
和槽13に導かれる。中和槽13には同じく炭酸ガスボ
ンベ15からガス供給管もしくは散気管14を介して炭
酸ガスが供給される。中和槽13内の分離液は液中に分
散される炭酸ガスによりpH7近辺に中和される。反応
槽11の上澄み液は少量の炭酸カルシウムを含んでいる
が、中和槽13で炭酸ガスと反応することにより、重炭
酸塩となり完全に溶解する。また、過剰の炭酸ガスが中
和槽13に供給された場合でも、放流水21のpHは約
6.3以下となることはなく、放流水のpH値を調整す
るためにアルカリ剤の添加を必要としない。反応槽11
で生成した炭酸カルシウムと少量の不溶解物である不純
物は引き抜き管20により引き抜かれ、ゴムなどの副資
材、肥料、あるいは生石灰製造の原料として再利用する
ことが可能である。
On the other hand, the undissolved slaked lime and calcium carbonate forming the blanket zone at the bottom of the dissolution tank 5 are removed by an undissolved matter drawing pipe 19 provided at the bottom of the dissolution tank 5.
is introduced into the reaction tank 11 by. It is desirable that the undissolved matter be drawn out at regular intervals, preferably by setting a time using a timer. The reaction tank 11 is connected from a carbon dioxide gas cylinder 15 to a vaporizer 16 and a gas supply pipe or aeration pipe 12.
Carbon dioxide gas is supplied via. The undissolved slaked lime introduced into the reaction tank 11 reacts with the carbon dioxide gas dispersed in the liquid to turn into calcium carbonate and precipitate. The pH at this time was 9.
By adjusting the pH to 5 to 11.0, preferably 10.0, the amount of calcium carbonate produced is maximized. Since calcium carbonate and undissolved substances generated in the reaction tank 11 are separated from the solution and precipitated, the supernatant separated liquid is further led to the neutralization tank 13. Carbon dioxide gas is similarly supplied to the neutralization tank 13 from a carbon dioxide gas cylinder 15 via a gas supply pipe or an aeration pipe 14 . The separated liquid in the neutralization tank 13 is neutralized to pH around 7 by carbon dioxide gas dispersed in the liquid. The supernatant liquid in the reaction tank 11 contains a small amount of calcium carbonate, but when it reacts with carbon dioxide gas in the neutralization tank 13, it becomes bicarbonate and is completely dissolved. Furthermore, even if excess carbon dioxide gas is supplied to the neutralization tank 13, the pH of the effluent water 21 will not be lower than approximately 6.3, and an alkaline agent must be added to adjust the pH value of the effluent water. do not need. Reaction tank 11
Calcium carbonate and a small amount of undissolved impurities produced in the above are extracted by a drawing tube 20 and can be reused as auxiliary materials such as rubber, fertilizers, or raw materials for producing quicklime.

【0013】[0013]

【発明の効果】このように、溶解槽から引き抜いた未溶
解物を炭酸ガスで中和することにより、酸を使用した場
合に比べて、安全、着実なpH調整が可能となる。また
、アルカリ注入設備も必要としないし、中和後、取り出
される生成物は酸で処理した場合に比べて用途範囲が広
く利用価値が高い。更に、本発明を上水道水のpH調整
用の消石灰水溶液を製造する装置に用いれば、不純物の
少ない消石灰水溶液を得ることができ、しかも不溶解物
を連続して処理できるので、従来例に見られるように複
数の装置を設置しなくとも消石灰水溶液を上水道水に連
続して注入することができる。
[Effects of the Invention] As described above, by neutralizing the undissolved matter extracted from the dissolution tank with carbon dioxide gas, it is possible to adjust the pH more safely and steadily than when using an acid. Further, no alkali injection equipment is required, and the product taken out after neutralization has a wider range of uses and higher utility value than when treated with acid. Furthermore, if the present invention is used in an apparatus for producing a slaked lime aqueous solution for adjusting the pH of tap water, it is possible to obtain a slaked lime aqueous solution with few impurities, and in addition, insoluble matter can be continuously treated, which is different from conventional examples. Thus, the slaked lime aqueous solution can be continuously injected into tap water without installing multiple devices.

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

【図1】本発明の実施に使用される装置の概略図である
。5  溶解槽 11  反応槽 12  散気管 13  中和槽 14  散気管 15  炭酸ガスボンベ 16  気化器 19  未溶解物引き出し管 21  放流水
FIG. 1 is a schematic diagram of the apparatus used to implement the invention. 5 Dissolution tank 11 Reaction tank 12 Aeration pipe 13 Neutralization tank 14 Aeration pipe 15 Carbon dioxide cylinder 16 Vaporizer 19 Undissolved matter withdrawal pipe 21 Discharge water

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】  消石灰水溶液を製造する溶解槽から未
溶解物を引き出し、その引き出した未溶解物を炭酸ガス
で中和することを特徴とする消石灰水溶液の製造過程で
発生する未溶解物の処理方法。
Claim 1: Treatment of undissolved matter generated in the process of producing a slaked lime aqueous solution, characterized by drawing out undissolved matter from a dissolution tank for producing the slaked lime aqueous solution, and neutralizing the drawn out undissolved matter with carbon dioxide gas. Method.
【請求項2】  前記炭酸ガスで中和するにあたり、第
1段階で未溶解物を炭酸ガスでpH9.5〜11.0に
中和し、炭酸カルシウムを生成沈澱させた後、更にその
分離液を炭酸ガスで中和することを特徴とする請求項1
記載の消石灰水溶液の製造過程で発生する未溶解物の処
理方法。
2. In the neutralization with carbon dioxide gas, in the first step, undissolved substances are neutralized with carbon dioxide gas to a pH of 9.5 to 11.0, calcium carbonate is produced and precipitated, and then the separated liquid is Claim 1 characterized in that the is neutralized with carbon dioxide gas.
A method for treating undissolved substances generated during the manufacturing process of the slaked lime aqueous solution described above.
JP10306691A 1991-04-08 1991-04-08 Treatment of undissolved matter generated in process for manufacturing aqueous solution of slaked lime Pending JPH04310285A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10306691A JPH04310285A (en) 1991-04-08 1991-04-08 Treatment of undissolved matter generated in process for manufacturing aqueous solution of slaked lime

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10306691A JPH04310285A (en) 1991-04-08 1991-04-08 Treatment of undissolved matter generated in process for manufacturing aqueous solution of slaked lime

Publications (1)

Publication Number Publication Date
JPH04310285A true JPH04310285A (en) 1992-11-02

Family

ID=14344297

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10306691A Pending JPH04310285A (en) 1991-04-08 1991-04-08 Treatment of undissolved matter generated in process for manufacturing aqueous solution of slaked lime

Country Status (1)

Country Link
JP (1) JPH04310285A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2010040999A2 (en) * 2008-10-06 2010-04-15 Siltbuster Limited Apparatus and method for treating alkaline water
JP2011073892A (en) * 2009-09-29 2011-04-14 Nippon Paper Industries Co Ltd Method for producing calcium carbonate
JP2013087013A (en) * 2011-10-18 2013-05-13 Mitsubishi Paper Mills Ltd Method for producing calcium carbonate
CN105836921B (en) * 2016-05-04 2019-06-25 浙江闰土研究院有限公司 A kind of processing method of dye wash waste water

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2010040999A2 (en) * 2008-10-06 2010-04-15 Siltbuster Limited Apparatus and method for treating alkaline water
WO2010040999A3 (en) * 2008-10-06 2010-07-15 Siltbuster Limited Apparatus and method for treating alkaline water
GB2464141B (en) * 2008-10-06 2013-06-26 Siltbuster Ltd Portable apparatus and method for treatment of alkaline water reaction with carbon dioxide
AU2009300918B2 (en) * 2008-10-06 2014-06-05 Siltbuster Limited Portable apparatus and method for treatment of alkaline water by reaction with carbon dioxide
JP2011073892A (en) * 2009-09-29 2011-04-14 Nippon Paper Industries Co Ltd Method for producing calcium carbonate
JP2013087013A (en) * 2011-10-18 2013-05-13 Mitsubishi Paper Mills Ltd Method for producing calcium carbonate
CN105836921B (en) * 2016-05-04 2019-06-25 浙江闰土研究院有限公司 A kind of processing method of dye wash waste water

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