JPS63141696A - Production of mineralized water - Google Patents

Production of mineralized water

Info

Publication number
JPS63141696A
JPS63141696A JP28859086A JP28859086A JPS63141696A JP S63141696 A JPS63141696 A JP S63141696A JP 28859086 A JP28859086 A JP 28859086A JP 28859086 A JP28859086 A JP 28859086A JP S63141696 A JPS63141696 A JP S63141696A
Authority
JP
Japan
Prior art keywords
water
value
index
stage
saturation
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
JP28859086A
Other languages
Japanese (ja)
Inventor
Shinji Morita
森田 真二
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.)
Sasakura Engineering Co Ltd
Original Assignee
Sasakura Engineering Co Ltd
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 Sasakura Engineering Co Ltd filed Critical Sasakura Engineering Co Ltd
Priority to JP28859086A priority Critical patent/JPS63141696A/en
Publication of JPS63141696A publication Critical patent/JPS63141696A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To attain a prescribed saturation index by measuring the temp. pH value, Ca concn. and dissolved carbon dioxide concn. of mineralized water, calculating the saturation index and/or stability index thereof and subjecting an aq. alkaline soln. to injection control. CONSTITUTION:Gaseous CO2 is injected to pure water in a 1st stage. The water is brought into contact with a Ca-contg. material to form the water contg. Ca<2+> ion and HCO3<-> ion in a 2nd stage. The aq. alkaline water is injected to the water in a 3rd stage. The pH value of the water obtd. in the 2nd stage is measured and the injection rate of the gaseous CO2 is adjusted at this time. The temp., pH value, Ca concn. and dissolved carbon dioxide concn. of the water obtd. in the 3rd stage are measured and the saturation index and/or stability index are computed. The injection rate of the aq. alkaline soln. is thereby controlled so as to have the saturation index and/or stability index within the prescribed range. Ca<2+> and HCO3<-> are dissolved in the pure water to about the extent considered to be saturation or slightly supersaturation to maintain the less corrosive condition in this method.

Description

【発明の詳細な説明】 産業上の利用分野: 本発明は、純水に、カルシウム・マグネシウム・アルカ
リ金属などを炭酸塩・酸性炭酸塩などの形にして溶Ps
させるミネラル水の製造方法に関するものである。
Detailed Description of the Invention Field of Industrial Application: The present invention involves dissolving Ps in pure water by dissolving calcium, magnesium, alkali metals, etc. in the form of carbonates, acidic carbonates, etc.
The present invention relates to a method for producing mineral water.

ここで、純水とは、蒸留法(通常蒸留法・フラッシュ蒸
留法を含む。〕、逆浸透法などにより純化した水、ミネ
ラル水とは、無機成分と含む水のことである。
Here, pure water refers to water purified by a distillation method (including normal distillation method and flash distillation method), reverse osmosis method, etc., and mineral water refers to water containing inorganic components.

・R景技術: 純水は、飲料として無味で好ましくない。また、鋼管・
鋼容器などで輸送する場合、鉄がm4し易いため、それ
らの減肉速度が速く、かつ水が赤色tiび易い。コンク
リート・アスベストなど金・U・容器の材料とした場合
にも、可溶成分が溶出し易く耐久性を劣化する。
・R-scape technology: Pure water is tasteless and undesirable as a beverage. In addition, steel pipes
When transporting in steel containers, iron tends to become m4, so the rate of thinning is fast, and water tends to turn red. Even when it is used as a material for metal, U, or containers such as concrete or asbestos, soluble components tend to leach out and the durability deteriorates.

この欠点を予防するため、従来、純水に002ガスを注
入しt後、石灰石・ドロフィトなど炭酸7Iフルシウム
・炭酸マグネシウム金倉む粒状固本(硬化剤)を接触さ
せ、Ca  金主体として浴出させ、その後、さらに、
NaOH,Ca(OH)2などの水溶液(アルカリ剤)
を加えて処理済水のpHを調節する方法が知られていた
(!#開昭61−572j2号、同61−57293号
、同61−97098号各公報記載など。)。
In order to prevent this drawback, conventionally, after injecting 002 gas into pure water, it is brought into contact with granular solids (curing agent) such as limestone, dolphite, etc. containing 7I fulsium carbonate and magnesium carbonate, and the Ca is extracted as a main body of gold. , then further,
Aqueous solutions (alkaline agents) such as NaOH, Ca(OH)2, etc.
A method was known for adjusting the pH of treated water by adding (described in Japanese Patent Publications No. 61-572j2, No. 61-57293, No. 61-97098, etc.).

また、Larson ラ(Journal −Amer
ican Waterworks As5ociati
on 、 Vol −84+ 1667 + 1944
)に代表される取扱では、 f(20ヰHゝ+Od−・・・・・・・・・・・・・・
・・・・・・・・・・・・・・・・(1)KW = (
)f”X0f(−) 、 Kw’ = (:)I”) 
(OH−)CO,+H20=M、Co8= H” 十H
co; −−−−−−−旧・−・−(2)HCO,; 
= H” + COニー 叫・団・・旧・・・旧旧旧旧
・・(3)ただし、〔〕はアクティビティ、〔〕は濃度
を表θす。アクティビティ係数の推定に、Debye 
−Hucke l  J) % a法則を用いて、炭酸
カルシウムで飽和した状態のpH(! t−pH5で示
すとpf(a=logKs/に!−1og(Ca”つ−
1og(alk) +9.80+(2,5カー)/(1
+ 5.8σ+5.5μ) ・・・・・・・・・(4)
ただし、μはイオン強度を示し、alkは(5)式によ
って定義されるアルカリ度(全アルカリ度、Mアルカリ
度)で、メチルオレンジを指示薬として測定し得る値で
ある。
Also, Larson La (Journal-Amer
ican Waterworks As5ociati
on, Vol -84+ 1667 + 1944
), f(20ヰHゝ+Od−・・・・・・・・・・・・・・・・
・・・・・・・・・・・・・・・・・・(1) KW = (
)f"X0f(-), Kw' = (:)I")
(OH-)CO, +H20=M, Co8=H” 10H
co; --------old・-・-(2)HCO,;
= H" + CO knee Shouting, group, old... old old old old... (3) However, [] represents activity, and [] represents concentration θ. Debye is used to estimate the activity coefficient.
- Huckel J) % Using the a law, the pH of a state saturated with calcium carbonate (!
1og(alk) +9.80+(2,5 car)/(1
+5.8σ+5.5μ) ・・・・・・・・・(4)
However, μ indicates ionic strength, and alk is alkalinity (total alkalinity, M alkalinity) defined by equation (5), which is a value that can be measured using methyl orange as an indicator.

(a l k) + (H” ) = 2(COニー 
、l + (HCOa ) + (OH−〕・” (5
)ただし、(Ca  )はCaとして、(alk、]は
CtCOaとして表したppm値である。
(a l k) + (H”) = 2(CO knee
, l + (HCOa) + (OH-]・” (5
) However, (Ca) is a ppm value expressed as Ca, and (alk, ] is a ppm value expressed as CtCOa.

以上の4に1、KW、K8 の値を第1表に示す。Table 1 shows the values of 1, KW, and K8 in 4 above.

第  1  表 飽和指数(Langellier指数)L−1,は(p
Ha −pds )、安全指数(dyzner指数)S
、1.は(2P。
Table 1 Saturation index (Langellier index) L-1, is (p
Ha-pds), safety index (dyzner index) S
, 1. (2P.

−pHa )で示され、スケール生成、装置腐食の観点
カラ有用とされティる( gyzner : Jour
nal −American water works
 As5ociation 、Vo135 。
-pHa) and is considered to be useful from the perspective of scale formation and equipment corrosion (gyzner: Jour
nal-American water works
As5ocation, Vo135.

P、472〜486 、1944 )。P, 472-486, 1944).

さて、上記し九ミネラル化水を望ましいし・■。Now, the above-mentioned 9 mineralized water is desirable.■.

値、S、I・値に維持するため、純水にCOzガスを注
入し、6解したCO2を測定して、この測定値と所望基
準値に11tlI御する方法が、前記%開昭61−57
292号、同61−57298号に記載されており、ま
た生成ミネラル化水の電導度を測定して、所望値に制御
する方法が知られている(特開昭61−46298号)
In order to maintain the value, S, and I value, there is a method of injecting COz gas into pure water, measuring the dissolved CO2, and controlling this measured value and the desired reference value by 11tlI. 57
No. 292 and No. 61-57298, and a method of measuring the conductivity of produced mineralized water and controlling it to a desired value is known (Japanese Patent Laid-Open No. 61-46298).
.

解決しようとする問題点: しかしながら純水中に注入した場合の浴解CO2((2
)弐K 必要’k CO2(!: 過gJIJCO2ト
t 含tr o ) (D tau定値は不安定な欠点
があり、ミネラル化水の濯導度を測定する方法は、電導
度の温度依存性が犬で温度補正をしなければならない。
Problem to be solved: However, when injected into pure water, the solution of CO2 in the bath ((2
)2K Necessary'k CO2 (!: Excess gJIJCO2t t tro ) (D The tau constant value has the disadvantage of being unstable, and the method of measuring the rinsing conductivity of mineralized water has the disadvantage that the temperature dependence of the conductivity is The dog must be used to compensate for the temperature.

問題点を解決する手段: 不発明では、純水にCO2ガスを注入する第一工程と、
第一工程で得られたCO2を含んだ水を含カルシウム物
質と接触させ、Ca!“イオンとaCO;イオンを含む
水にする第二工程と、第二工程によって得らルた水にア
ルカリ性水溶液を注入する第三工程とからなるミネラル
化水の製造方法に2いて、第二工程で得られた水のpH
@を測定してCO,ガスの注入量を調整する段階と、第
三工程で得られた水の温度、Pi(II!、カルシウム
濃度、2よび溶存炭酸ガス濃度を測定して、飽和指数お
よび/または安定度指数を演算することにより、所定の
飽和指数2よび/または安定度I¥Iaの範囲になるよ
うに前記アルカリ性水溶液の注入量を制御することを特
徴とするものである。すなわち、ミネラル化水の温度、
pH値、カルシウム濃度、および溶存炭酸ガス濃度を測
定して、まず、自動演算によりnco8@度を求め、 pHs=log(Ks/Kg)−1og(Ca  )−
1og(f(CO;J+ 9.80 + 2.5σ/(
1+5.3σ−5,5μ)・・・・・・(6)((6)
式中、KSlに2、〔Ca2+〕、μは(4)式のとお
り: (HCO;)は2イオンモルのUCO;を1モル
のCaCOBとして、ppm CaCO3テ表わしりH
CO;ノ濃度) によジ、pf(sを算出し、実測pH値(pHaで示す
Means for solving the problem: In the non-invention, the first step is to inject CO2 gas into pure water,
The water containing CO2 obtained in the first step is brought into contact with a calcium-containing substance, and Ca! “Ions and aCO: A method for producing mineralized water consisting of a second step of making water containing ions, and a third step of injecting an alkaline aqueous solution into the water obtained in the second step. The pH of the water obtained in
The step of adjusting the injection amount of CO and gas by measuring The method is characterized in that the injection amount of the alkaline aqueous solution is controlled to be in the range of a predetermined saturation index 2 and/or stability I\Ia by calculating a stability index. temperature of mineralized water,
Measure the pH value, calcium concentration, and dissolved carbon dioxide concentration, and first calculate nco8@degree by automatic calculation, pHs=log(Ks/Kg)−1og(Ca)−
1og(f(CO; J+ 9.80 + 2.5σ/(
1+5.3σ-5,5μ)・・・・・・(6)((6)
In the formula, KSl is 2, [Ca2+], and μ are as shown in formula (4): (HCO;) is expressed as ppm CaCO3, where 2 ion moles of UCO; are 1 mole of CaCOB.
CO; concentration), pf(s) was calculated, and the measured pH value (expressed in pHa).

)トノ関係が、飽和指数(pHa −p)is ) =
 Q−0,5力ツナ定度指数(2pH5−pHa ) 
= 6〜7になるように、アルカリ性水溶液の添加量を
調整するようにしたものである。
) The relationship is the saturation index (pHa - p) is ) =
Q-0,5 power tuna constant index (2pH5-pHa)
The amount of the alkaline aqueous solution added is adjusted so that the ratio is 6 to 7.

作用: 本発明の構成は、前記特開昭61−57292号、同6
1−57298号公報に記載のものと、CO2の検出位
置が異なる。すなわち、同刊行物に記載の方法では、カ
ルシウム溶解槽より上流位置でCO2の測定を行うに対
し、本発明ではカルシウム溶解槽より下流でpH測定を
行う。
Effect: The structure of the present invention is as described in the above-mentioned JP-A-61-57292 and JP-A-61-57292.
The CO2 detection position is different from that described in Japanese Patent No. 1-57298. That is, in the method described in the same publication, CO2 is measured at a position upstream from the calcium dissolution tank, whereas in the present invention, pH is measured at a position downstream from the calcium dissolution tank.

炭酸ガスの注入量とミネラル化水中のpi(値との相関
関係を、試験装置で調べた結果の1例1r:第2表に示
す。
An example of the results of examining the correlation between the amount of carbon dioxide gas injected and the pi value in mineralized water using a test device is shown in Table 2.

第2表 すなわち、CO!注入盪とpH値との間に逆相関関係が
あるから、調整が0T能である。
Table 2, namely CO! Adjustment is possible because there is an inverse relationship between injection temperature and pH value.

次に、(4)式を(6)式に変えた理由、すなわち、〔
alk)を(HCO;)  に変えた理由は、p)I 
= 7〜8.5の場合(したがって、フェノールフタレ
ンを指示薬としたアルカリ度、すなわちPアルカリ度が
零の場合)、本明細Jでいうアルカリ度alk (メチ
ルナレンジを指示薬としたアルカリ度でMアルカリ度と
も言う。)はf(Co; (ppm CaCO3として
表示)と同値となることによる。第3表に、Pアルカリ
度、Mアルカリ度、(oH−)、(Coニー、l、(t
[X)−間の関係を示す。
Next, we will discuss the reason for changing equation (4) to equation (6), that is, [
The reason for changing alk) to (HCO;) is p)I
= 7 to 8.5 (therefore, when the alkalinity using phenolphthalene as an indicator, that is, the P alkalinity is zero), the alkalinity referred to in this specification J (alkalinity using methylnadi as an indicator, M alkalinity) ) is the same as f(Co; (expressed as ppm CaCO3). Table 3 shows P alkalinity, M alkalinity, (oH-), (Coney, l, (t
Indicates the relationship between [X)-.

isa表 本発明ではpH= 7〜8.5の範囲にて通用するため
上表のPアルカリ度=Oすなわちアルカリ度は全てHC
L)、と考え得る。
isa table In the present invention, the pH is valid in the range of 7 to 8.5, so the P alkalinity in the above table = O, that is, the alkalinity is all HC
L).

さらに、(f(CO;)は(2)式よりCO2#度を測
定して計算rζて求める事が出来る。
Further, (f(CO;) can be obtained by measuring CO2# degree and calculating rζ from equation (2).

−また水中のCO2濃度は隔lIA電極法により簡単に
求める事が田米、市販のもので充分使用に1討える。C
a  測定はイオンamlcで行ないこれも市販のもの
で十分である。
-Also, the CO2 concentration in water can be easily determined using the 1IA electrode method, and commercially available products are sufficient for use. C
a The measurement is carried out using an ion AMLC, and a commercially available one is sufficient.

実施例: 第1図に示した実施例において、純水は、先づCO2ガ
ス源から供給されるCO2ガスの注入上受けた後、カル
シウム溶解塔に至り H2O+ CO2+ CaCOB = Ca ” + 
胆; ・・・・” ”・・” ” (7)に代表される
反応により溶解する(硬化反応と呼ぶ。)。
Example: In the example shown in FIG. 1, pure water is first injected with CO2 gas supplied from a CO2 gas source, and then reaches the calcium dissolution tower to form H2O+ CO2+ CaCOB = Ca '' +
Bile; ...""..."" Dissolves by the reaction represented by (7) (referred to as hardening reaction).

カルシウム溶解槽内で起こる(7)反応は、一般に終結
することなく、CO2は水中に溶解した形で残り、pH
を下げるので、さらにアルカリ性吻質Na0)I、 C
a(OH)2flどの水?Il’[を加えて、PHを所
望値に上昇させる。図中(1)はアルカリ水溶液送入口
、(2)はミネラル化水のpi(測定部で、測定pHを
所定値例えば8ならしめる九めに、f14節弁(3)を
自動操作して、位ffi (1)で送入されるアルカリ
水溶液量1に調節する。カルシウム溶解塔(5)での処
理を終った水中のCa は、位置(4)でサンプリング
されpHを測定し所望値に近づけるために、自動調節弁
(5)を自動操作する。また位置(4)でサンプリング
された水中の全炭酸量は別に自動測定され、 L、1.
、S、1.の計算に用い、計算されたり、1.、S・工
・は制御目的値の決定に用いられる。
The reactions that take place in the calcium dissolution tank (7) generally do not terminate and the CO2 remains in dissolved form in the water and the pH
Since it lowers the alkaline rostral Na0) I, C
a(OH) 2 fl Which water? Add Il'[ to raise the PH to the desired value. In the figure, (1) is the alkaline aqueous solution inlet, (2) is the mineralized water pi (measuring unit, and at the ninth stage when the measured pH is set to a predetermined value, for example 8, the f14 control valve (3) is automatically operated. The amount of alkaline aqueous solution fed at position ffi (1) is adjusted to 1. Ca in the water that has been treated in the calcium dissolution tower (5) is sampled at position (4), and the pH is measured and brought close to the desired value. For this purpose, the automatic control valve (5) is automatically operated.In addition, the total amount of carbon dioxide in the water sampled at position (4) is automatically measured separately, and L, 1.
,S,1. It is used in the calculation of 1. , S・engineering is used to determine the control objective value.

カルシウム溶解塔は、石灰石・ドロマイトなどの含カル
シウム粒体を充填材とした充填塔構造のものが便利で、
水の流れは上方から下方に向つものでも、下方から上方
に向うものでも良い。
A convenient calcium dissolution tower is one with a packed tower structure using calcium-containing particles such as limestone or dolomite as a filler.
The flow of water may be from above to below or from below to above.

発明の効果: 本発明のミネラル化水の製造方法では、純水にCa”ゝ
、HCOHを飽和ないし、若干過飽和と思われる程度(
L、I・=θ〜0.5)に溶解せしめ、かつ、腐食性の
少ない状d(S、1.=6〜8)を維持するように運転
可能である。しかして、〔Ca〕、(Heo;)の測定
が容易かつ連続に、安唾に行える利点がある。それゆえ
、広く一般の使用に適し、産業上の利用性は大きい。
Effects of the invention: In the method for producing mineralized water of the present invention, pure water contains Ca'' and HCOH to an extent that is considered to be saturated or slightly supersaturated (
L, I.=θ~0.5), and can be operated so as to maintain a less corrosive state d(S, 1.=6~8). Therefore, there is an advantage that [Ca] and (Heo;) can be easily and continuously measured. Therefore, it is suitable for wide general use and has great industrial applicability.

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

第1図は、流れ図として示した本発明の実施例に、イン
ストルメンテーション・オートメーションを施こしたも
のである。 A・・・カルシウム溶解槽
FIG. 1 shows an embodiment of the invention shown as a flowchart, with instrumentation automation applied. A... Calcium dissolution tank

Claims (1)

【特許請求の範囲】 1 純水にCO_2ガスを注入する第一工程と、第一工
程で得られたCO_2を含んだ水を含カルシウム物質と
接触させ、Ca^2^+イオンとHCO^−_3イオン
を含む水にする第二工程と、第二工程によつて得られた
水にアルカリ性水溶液を注入する第三工程とからなるミ
ネラル化水の製造方法において、 前記第二工程で得られた水のpH値を測定してCO_2
ガスの注入量を調整する段階と、前記第三工程で得られ
た水の温度、pH値、カルシウム濃度、および溶存炭酸
ガス濃度を測定して、飽和指数および/または安定度指
数を演算することにより、所定の飽和指数および/また
は安定度指数の範囲になるように前記アルカリ性水溶液
の注入量を制御することを含むミネラル化水の製造方法
[Claims] 1. A first step of injecting CO_2 gas into pure water, and bringing the water containing CO_2 obtained in the first step into contact with a calcium-containing substance to form Ca^2^+ ions and HCO^-. _3 A method for producing mineralized water comprising a second step of making water containing ions and a third step of injecting an alkaline aqueous solution into the water obtained in the second step, Measuring the pH value of water and CO_2
adjusting the amount of gas to be injected, and calculating the saturation index and/or stability index by measuring the temperature, pH value, calcium concentration, and dissolved carbon dioxide concentration of the water obtained in the third step. A method for producing mineralized water, comprising controlling the injection amount of the alkaline aqueous solution so that it falls within a predetermined saturation index and/or stability index range.
JP28859086A 1986-12-02 1986-12-02 Production of mineralized water Pending JPS63141696A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP28859086A JPS63141696A (en) 1986-12-02 1986-12-02 Production of mineralized water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP28859086A JPS63141696A (en) 1986-12-02 1986-12-02 Production of mineralized water

Publications (1)

Publication Number Publication Date
JPS63141696A true JPS63141696A (en) 1988-06-14

Family

ID=17732225

Family Applications (1)

Application Number Title Priority Date Filing Date
JP28859086A Pending JPS63141696A (en) 1986-12-02 1986-12-02 Production of mineralized water

Country Status (1)

Country Link
JP (1) JPS63141696A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05138180A (en) * 1991-11-13 1993-06-01 Kureha Chem Ind Co Ltd Treatment of city water
JPH05293476A (en) * 1992-04-22 1993-11-09 Kureha Chem Ind Co Ltd Preventing method for red water in city water
WO2001000507A1 (en) * 1999-06-25 2001-01-04 Abiogen Pharma S.P.A. Preparation and metering of components mixed with co¿2?
JP2018509283A (en) * 2015-01-29 2018-04-05 オムヤ インターナショナル アーゲー Method for producing alkaline earth metal bicarbonate solution

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6146293A (en) * 1984-08-10 1986-03-06 Mitsubishi Heavy Ind Ltd Method for converting freshwater into drinking water
JPS6197098A (en) * 1984-10-19 1986-05-15 Mitsubishi Heavy Ind Ltd Manufacture of potable water

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6146293A (en) * 1984-08-10 1986-03-06 Mitsubishi Heavy Ind Ltd Method for converting freshwater into drinking water
JPS6197098A (en) * 1984-10-19 1986-05-15 Mitsubishi Heavy Ind Ltd Manufacture of potable water

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05138180A (en) * 1991-11-13 1993-06-01 Kureha Chem Ind Co Ltd Treatment of city water
JPH05293476A (en) * 1992-04-22 1993-11-09 Kureha Chem Ind Co Ltd Preventing method for red water in city water
WO2001000507A1 (en) * 1999-06-25 2001-01-04 Abiogen Pharma S.P.A. Preparation and metering of components mixed with co¿2?
JP2018509283A (en) * 2015-01-29 2018-04-05 オムヤ インターナショナル アーゲー Method for producing alkaline earth metal bicarbonate solution

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