JPH07109585A - Treatment of circulating water - Google Patents
Treatment of circulating waterInfo
- Publication number
- JPH07109585A JPH07109585A JP25166593A JP25166593A JPH07109585A JP H07109585 A JPH07109585 A JP H07109585A JP 25166593 A JP25166593 A JP 25166593A JP 25166593 A JP25166593 A JP 25166593A JP H07109585 A JPH07109585 A JP H07109585A
- Authority
- JP
- Japan
- Prior art keywords
- water
- corrosion
- calcium carbonate
- carbon dioxide
- dioxide gas
- 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
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F5/00—Softening water; Preventing scale; Adding scale preventatives or scale removers to water, e.g. adding sequestering agents
- C02F5/08—Treatment of water with complexing chemicals or other solubilising agents for softening, scale prevention or scale removal, e.g. adding sequestering agents
- C02F5/083—Mineral agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/008—Control or steering systems not provided for elsewhere in subclass C02F
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/02—Non-contaminated water, e.g. for industrial water supply
- C02F2103/023—Water in cooling circuits
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/06—Controlling or monitoring parameters in water treatment pH
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/08—Corrosion inhibition
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Preventing Corrosion Or Incrustation Of Metals (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は循環水の処理方法に関す
る。更に詳しくは、炭酸カルシウムの析出が予想される
水循環系統に使用される金属の防食及びスケール防止の
ための水処理方法に関する。FIELD OF THE INVENTION The present invention relates to a method for treating circulating water. More specifically, it relates to a water treatment method for corrosion prevention and scale prevention of metals used in a water circulation system in which precipitation of calcium carbonate is expected.
【0002】[0002]
【従来の技術】水の濃縮を伴う冷却水系や鉄鋼工場で使
用される集塵水系では、水中の塩類濃度の増加により腐
食やスケールを生じやすくなる。例えば水中の塩化物イ
オンや硫酸イオンなど腐食性イオンの増加は、水循環系
統に使用される金属の腐食を加速し、漏水事故や設備寿
命の低下などの問題を引き起こす。また、集塵水や濃縮
した冷却水中のカルシウムイオンや重炭酸イオンは、ス
ケール生成の原因となり、配管の詰まりや熱交換器の熱
交換効率低下などの問題を引き起こす。このため、従
来、冷却水系では、スケールによる障害を防止するため
に、水の濃縮を極力避けて、冷却水水質を管理する対策
がとられたり、腐食やスケール生成を防止する効果を有
するポリマーを含む水処理剤が添加されたりしている
(特公昭55−6439号公報など)。2. Description of the Related Art In cooling water systems accompanied by water concentration and in dust collection water systems used in steel factories, corrosion and scale are likely to occur due to an increase in salt concentration in water. For example, an increase in corrosive ions such as chloride ions and sulfate ions in water accelerates the corrosion of metals used in the water circulation system, causing problems such as water leakage accidents and shortened equipment life. Moreover, calcium ions and bicarbonate ions in the collected water and the concentrated cooling water cause scale formation, which causes problems such as clogging of pipes and reduction of heat exchange efficiency of the heat exchanger. For this reason, in the conventional cooling water system, in order to prevent damage due to scale, measures are taken to avoid water concentration as much as possible and control the quality of the cooling water, or to use a polymer that has the effect of preventing corrosion and scale formation. A water treatment agent containing it is sometimes added (Japanese Patent Publication No. 55-6439).
【0003】[0003]
【発明が解決しようとする課題】ところが、前者の方法
では、腐食による障害は防止できず、また、水を大量に
必要とするなどの難点がある。However, the former method has drawbacks in that it cannot prevent damage due to corrosion and requires a large amount of water.
【0004】他方、前記のポリマーを含む水処理剤の添
加によってスケールや腐食による障害を防止する方法は
極めて効率の良い方法であり、広く適用されているが、
ポリマーを使用する点で日常の薬注管理等が煩雑とな
り、経済的にも高価であるという欠点がある。On the other hand, the method of preventing damage due to scale and corrosion by adding the water treatment agent containing the above-mentioned polymer is an extremely efficient method and is widely applied.
Since the polymer is used, daily drug administration and the like are complicated and economically expensive.
【0005】このようなことから、日常管理が容易で、
安価な循環水の処理方法が望まれていた。Because of this, daily management is easy,
An inexpensive method of treating circulating water has been desired.
【0006】本発明は上記従来の実情に鑑みてなされた
ものであって、循環水系の腐食及びスケールに起因する
障害を防止して水資源の有効利用を図る容易かつ安価な
循環水の処理方法を提供することを目的とする。The present invention has been made in view of the above-mentioned conventional circumstances, and is an easy and inexpensive method for treating circulating water for effectively utilizing water resources by preventing damages caused by corrosion and scale of the circulating water system. The purpose is to provide.
【0007】[0007]
【課題を解決するための手段】本発明の循環水の処理方
法は、炭酸カルシウムが析出傾向にある循環水に炭酸ガ
スを添加することを特徴とする。The method for treating circulating water according to the present invention is characterized by adding carbon dioxide gas to circulating water in which calcium carbonate tends to precipitate.
【0008】以下、図面を参照して本発明の実施例につ
いて詳細に説明する。Embodiments of the present invention will be described in detail below with reference to the drawings.
【0009】図1は本発明の循環水の処理方法の一実施
例方法を示す系統図である。FIG. 1 is a system diagram showing a method of an embodiment of the method for treating circulating water according to the present invention.
【0010】図中、1は冷却塔であり、冷却塔1で冷却
された水は、ポンプPを備える配管2から、配管2A,
2Bを経て、各熱交換器3A,3Bに送給され、熱交換
を行なう。熱交換により温度が上昇した水は、それぞれ
配管4A,4Bを経て、配管4より冷却塔に返送して再
冷却し、循環再使用する。なお、熱交換器は2個に限ら
ず、3個以上設けられる場合もある。In the figure, 1 is a cooling tower, and the water cooled in the cooling tower 1 is supplied from a pipe 2 equipped with a pump P to a pipe 2A,
After passing through 2B, they are fed to the heat exchangers 3A and 3B for heat exchange. The water whose temperature has risen due to heat exchange is returned to the cooling tower from the pipe 4 via the pipes 4A and 4B, recooled, and reused by circulation. Note that the number of heat exchangers is not limited to two and may be three or more.
【0011】本実施例においては、冷却水の供給配管2
に炭酸ガスの吹き込み用配管5を設け、熱交換器に流入
する冷却水中に炭酸ガスの吹き込みを行なう。6は手動
バルブ、7は電磁バルブであり、冷却塔1内の冷却水中
に設けたpHセンサー8Aの測定値に基き、pHコント
ローラ8に連動して開閉するように構成されている。In this embodiment, the cooling water supply pipe 2
A carbon dioxide gas blowing pipe 5 is provided at the position to blow carbon dioxide gas into the cooling water flowing into the heat exchanger. Reference numeral 6 is a manual valve, and 7 is an electromagnetic valve, which is configured to open and close in conjunction with the pH controller 8 based on the measured value of the pH sensor 8A provided in the cooling water in the cooling tower 1.
【0012】即ち、本発明においては、後述の作用の項
で述べるように、処理対象水系の最高使用温度におい
て、炭酸カルシウムが未飽和となるように、炭酸ガスを
添加することが重要である。このような炭酸ガス添加量
の制御は、当該水系のpH調節により行なうことがで
き、pHが7〜9となるように炭酸ガスの添加量を制御
すれば良い。That is, in the present invention, it is important to add carbon dioxide gas so that the calcium carbonate becomes unsaturated at the maximum operating temperature of the water system to be treated, as will be described later in the section of action. Such control of the carbon dioxide gas addition amount can be performed by adjusting the pH of the aqueous system, and the carbon dioxide gas addition amount may be controlled so that the pH becomes 7 to 9.
【0013】このため、本実施例においては、pHセン
サー8Aの測定pHが炭酸カルシウムが未飽和となるよ
うに、pHコントローラ8により電磁バルブ7の開閉を
制御して、炭酸ガス吹き込み量の調節を行なう。なお、
9はチャッキ弁である。For this reason, in this embodiment, the opening and closing of the electromagnetic valve 7 is controlled by the pH controller 8 so that the pH measured by the pH sensor 8A becomes unsaturated, and the amount of carbon dioxide gas blown is adjusted. To do. In addition,
9 is a check valve.
【0014】このようにして、炭酸カルシウムの析出が
予想される循環冷却水中に、炭酸ガスを吹き込むことに
より、スケールの生成及び金属の腐食が有効に防止され
る。In this way, by blowing carbon dioxide into the circulating cooling water in which precipitation of calcium carbonate is expected, scale formation and metal corrosion are effectively prevented.
【0015】図1に示す方法は、炭酸ガスの吹き込みを
pHによる自動制御で行なうものであるが、本発明の方
法は、図2に示す如く、pHセンサー(図示せず)の測
定値に基いて手動バルブ6で炭酸ガスの吹き込み量を制
御することもできる。なお、図2に示す方法は、炭酸ガ
ス吹き込み配管にpHコントローラと連動する電磁バル
ブを設けていない点のみが図1に示す方法と異なり、そ
の他、同一機能を奏する部材には同一符号を付してあ
る。In the method shown in FIG. 1, blowing of carbon dioxide gas is automatically controlled by pH, but the method of the present invention is based on the measured value of a pH sensor (not shown) as shown in FIG. In addition, the amount of carbon dioxide gas blown in can be controlled by the manual valve 6. Note that the method shown in FIG. 2 is different from the method shown in FIG. 1 only in that the carbon dioxide blowing pipe is not provided with an electromagnetic valve interlocking with the pH controller, and other members having the same function are denoted by the same reference numerals. There is.
【0016】いずれの方法においても、既存の設備の適
当な箇所に炭酸ガス吹き込み配管を設けるという極めて
簡易な改造工事により、本発明の方法を容易に実施する
ことができ、良好な効果を達成することができる。In any of the methods, the method of the present invention can be easily carried out by a very simple remodeling work in which a carbon dioxide gas blowing pipe is provided in an appropriate place of the existing equipment, and a good effect is achieved. be able to.
【0017】なお、本発明の方法は、図1,2に示す循
環冷却水系に限らず、炭酸カルシウムが析出する傾向に
ある水系であれば有効に適用することができ、例えば、
鉄鋼工場で使用される集塵水系等に適用して良好な効果
を得ることができる。また、炭酸ガスの添加方法にも特
に制限はなく、貯槽内の水にバブリングする方法などを
採用することもできる。The method of the present invention is not limited to the circulating cooling water system shown in FIGS. 1 and 2, but can be effectively applied to any water system in which calcium carbonate tends to precipitate.
Good effects can be obtained by applying it to dust collection water systems used in steel factories. The method of adding carbon dioxide gas is not particularly limited, and a method of bubbling water in the storage tank or the like can also be adopted.
【0018】なお、用いる炭酸ガスとしては、高純度の
炭酸ガスに限らず、場合によっては各種工場内で発生す
る炭酸ガスを多く含む廃ガスなどを利用することもでき
る。この場合には工場の廃ガス排出量の低減が図れ、有
利である。The carbon dioxide gas used is not limited to high-purity carbon dioxide gas, and waste gas containing a large amount of carbon dioxide gas generated in various factories may be used in some cases. In this case, the amount of waste gas emitted from the factory can be reduced, which is advantageous.
【0019】[0019]
【作用】本発明の循環水の処理方法は、水中のカルシウ
ムイオンや重炭酸イオンなどの防食性イオンを有効に利
用して、系内の金属表面に保護皮膜を形成させて防食す
るとともに、水と炭酸ガスとを接触させることによって
水中の炭酸カルシウムを未飽和な状態に維持し、炭酸カ
ルシウム系スケールの生成を防止するという原理に基づ
くものである。The method of treating circulating water according to the present invention effectively utilizes anticorrosive ions such as calcium ions and bicarbonate ions in water to form a protective film on the metal surface in the system to prevent corrosion. It is based on the principle that calcium carbonate in water is maintained in an unsaturated state by contacting with the carbon dioxide gas and the formation of calcium carbonate-based scale is prevented.
【0020】以下に本発明の循環水の処理方法の作用効
果について詳細に説明する。The effects of the circulating water treatment method of the present invention will be described in detail below.
【0021】 スケールの防止効果 炭酸カルシウムの飽和溶液については下記(1)式の関
係があり、また、炭酸イオンと炭酸水素イオンとは下記
(2)式の平衡関係にある。Scale Preventive Effect A saturated solution of calcium carbonate has a relationship of the following formula (1), and a carbonate ion and a hydrogen carbonate ion have an equilibrium relationship of the following formula (2).
【0022】[0022]
【化1】 [Chemical 1]
【0023】炭酸カルシウムの飽和又は過飽和溶液に炭
酸ガスを吹き込むと、水のpHが低下(H+ が増加)
し、上記(2)の平衡反応は左(←)に進む結果、炭酸
カルシウムの構成に必要なCO3 2- が減少するため、炭
酸カルシウムを未飽和(溶解状態)に維持することがで
きる。即ち、炭酸カルシウム系スケールの析出を防止す
ることができる。When carbon dioxide gas is blown into a saturated or supersaturated solution of calcium carbonate, the pH of water decreases (H + increases).
However, as a result of the equilibrium reaction of the above (2) proceeding to the left (←), CO 3 2− necessary for the composition of calcium carbonate is reduced, so that calcium carbonate can be maintained in an unsaturated state (dissolved state). That is, it is possible to prevent the precipitation of the calcium carbonate-based scale.
【0024】 防食効果 金属、例えば鉄表面での腐食反応では、鉄の溶出反応
(アノード反応)と酸素の還元反応が下記(3),
(4)式に従って起こる。Anticorrosion Effect In the corrosion reaction on the surface of metal such as iron, the elution reaction of iron (anode reaction) and the reduction reaction of oxygen are as follows (3),
It occurs according to the equation (4).
【0025】[0025]
【化2】 [Chemical 2]
【0026】上記アノード、カソードの各反応は各々別
々の鉄表面で起こる。これら(3),(4)式のいずれ
か一方又は両方の反応を抑制することにより防食が可能
である。上記(4)式より明らかなように、カソード反
応の起こっている場所では、pHが上昇(OH- が増
加)しており、例え炭酸ガスを吹き込んでいたとして
も、前記(2)式の反応が右側(→)に進む結果、炭酸
カルシウムの析出が起こる。析出した炭酸カルシウム
は、バルク状ではなく、スケールとは異なる極めて薄い
膜として鉄表面を覆う。カソード反応の起こっている鉄
表面にこのような炭酸カルシウムの皮膜が形成される
と、酸素の拡散が阻害されるため、(4)式は起こりに
くくなる。その結果、腐食を防止できる。The above anode and cathode reactions occur on different iron surfaces. Corrosion can be prevented by suppressing the reaction of either or both of the expressions (3) and (4). As is clear from the above formula (4), the pH is rising (OH − is increasing) at the place where the cathode reaction is occurring, and even if carbon dioxide gas is blown in, the reaction of the above formula (2) Results in precipitation of calcium carbonate. The precipitated calcium carbonate covers the iron surface not as a bulk but as an extremely thin film different from the scale. When such a calcium carbonate film is formed on the iron surface where the cathodic reaction is occurring, the diffusion of oxygen is hindered, so that the equation (4) becomes difficult to occur. As a result, corrosion can be prevented.
【0027】本発明の方法は、防食剤及びスケール防止
剤を使用する方法に比べて日常管理が容易であり、かつ
安価に実施できる。しかも、炭酸ガスを用いるものであ
り、塩酸や硫酸などの酸によるpH調整と異なり、腐食
性イオンの増加の問題もない。The method of the present invention is easier to carry out on a daily basis and can be carried out at a lower cost than the method using an anticorrosive agent and a scale inhibitor. Moreover, since carbon dioxide gas is used, unlike the pH adjustment with acids such as hydrochloric acid and sulfuric acid, there is no problem of increasing corrosive ions.
【0028】[0028]
【実施例】以下に実施例及び比較例を挙げて本発明をよ
り具体的に説明する。EXAMPLES The present invention will be described more specifically with reference to Examples and Comparative Examples below.
【0029】実施例1、比較例1,2 表1に示す水質の工業用水のpHが7.0〜8.0の範
囲を維持するように45℃,大気開放静置の条件で炭酸
ガスを1〜5ml/分の割合で吹き込みながら濃縮さ
せ、濃縮倍数に対する水中のカルシウム硬度の変化を調
べた(実施例1)。比較のため、炭酸ガスを吹き込まな
かった場合(比較例1)及び市販の冷却水処理剤(スケ
ール防止剤並びに防食剤配合:商標クリロイヤル526
1 栗田工業(株)商品)を所定量添加した場合(比較
例2)についても試験した。なお、濃縮倍数は、濃縮に
要した水の量を濃縮後の水の量で除した値を用いた。Example 1, Comparative Examples 1 and 2, carbon dioxide gas was added under the conditions of 45 ° C. and open to the atmosphere so that the pH of the industrial water having the water quality shown in Table 1 was maintained in the range of 7.0 to 8.0. The mixture was concentrated while being blown at a rate of 1 to 5 ml / min, and the change in calcium hardness in water with respect to the concentration multiple was examined (Example 1). For comparison, when carbon dioxide gas was not blown (Comparative Example 1) and a commercial cooling water treatment agent (scale inhibitor and anticorrosive compounded: trademark Kuriroyal 526)
1 A test was also performed when a predetermined amount of Kurita Water Industries Co., Ltd.) was added (Comparative Example 2). As the concentration multiple, a value obtained by dividing the amount of water required for concentration by the amount of water after concentration was used.
【0030】結果を図3に示す。図3より、炭酸ガスを
吹き込まなかった場合には、濃縮倍数3倍以上になると
炭酸カルシウムの析出によりカルシウム硬度が理論値よ
り低下してくるのに対して、炭酸ガスを吹き込んだ場合
には、市販の冷却水処理剤を添加した場合と同様にほぼ
理論値通りカルシウム硬度が水中に維持されていること
がわかる。The results are shown in FIG. From FIG. 3, when the carbon dioxide gas was not blown, the calcium hardness becomes lower than the theoretical value due to the precipitation of calcium carbonate when the concentration factor becomes 3 times or more, whereas when the carbon dioxide gas is blown, It can be seen that the calcium hardness was maintained in water almost in accordance with the theoretical value as in the case of adding the commercially available cooling water treatment agent.
【0031】本実施例により、濃縮水と炭酸ガスとの接
触によって、水中の炭酸カルシウムの析出が有効に防止
され、本発明の方法はスケールの生成防止に有効である
ことが明らかである。According to this example, it is apparent that the contact of the concentrated water with the carbon dioxide gas effectively prevents the precipitation of calcium carbonate in the water, and that the method of the present invention is effective in preventing the formation of scale.
【0032】[0032]
【表1】 [Table 1]
【0033】実施例2、比較例3,4 実施例1で調整した5倍濃縮水に鉄の金属試験片を浸漬
し、水温45℃の条件下で、金属の重量変化量の経時変
化を調べた(実施例2)。なお、試験期間中も炭酸ガス
の濃縮水中への吹き込みを5ml/分の割合で継続し
た。比較のため、比較例1で調整した5倍濃縮水(比較
例3)及び比較例2で調整した5倍濃縮水(比較例4)
についても同様に試験を行なった。Example 2, Comparative Examples 3 and 4 A metal test piece of iron was immersed in the 5-fold concentrated water prepared in Example 1 and the change with time of the weight change amount of the metal was examined under the condition of the water temperature of 45 ° C. (Example 2). During the test period, the blowing of carbon dioxide gas into the concentrated water was continued at a rate of 5 ml / min. For comparison, the 5-fold concentrated water prepared in Comparative Example 1 (Comparative Example 3) and the 5-fold concentrated water prepared in Comparative Example 2 (Comparative Example 4)
Was similarly tested.
【0034】結果を図4に示す。図4より明らかなよう
に、実施例2では、初期の腐食減量は炭酸ガスを吹き込
まない比較例3と変わらないものの、一定時間経過後に
腐食減量はほぼ一定となった。これは、鉄表面に炭酸カ
ルシウムの保護皮膜形成が形成され、腐食が防止されて
いることを示している。炭酸ガスを吹き込まなかった比
較例3の場合も本発明による実施例2とほぼ同様に時間
経過とともに腐食減量の増加速度が低下する傾向を示し
たが、本発明による実施例2に比べると腐食の低下傾向
は緩慢であった。The results are shown in FIG. As is clear from FIG. 4, in Example 2, although the initial corrosion weight loss was the same as that of Comparative Example 3 in which carbon dioxide gas was not blown in, the corrosion weight loss became substantially constant after a certain period of time. This indicates that a protective film of calcium carbonate was formed on the iron surface to prevent corrosion. In the case of Comparative Example 3 in which carbon dioxide gas was not blown, the rate of increase in corrosion weight loss tended to decrease with time almost similarly to Example 2 according to the present invention. The declining trend was slow.
【0035】一方、市販の冷却水処理剤を添加した比較
例4では、初期の腐食減量は実施例2より少ないもの
の、一定時間経過後の腐食減量の増加量は、実施例2と
ほとんど変わらなかった。この結果は、本発明による実
施例2で保護皮膜を形成した後は、防食剤を使用した場
合に匹敵する防食効果が期待できることを示している。
従って、本発明の方法は、水中の金属の防食に有効であ
ることが明らかである。On the other hand, in Comparative Example 4 in which a commercially available cooling water treatment agent was added, the initial corrosion weight loss was smaller than that in Example 2, but the increase in corrosion weight loss after a certain period of time was almost the same as in Example 2. It was This result shows that, after forming the protective film in Example 2 according to the present invention, an anticorrosion effect comparable to the case where an anticorrosive agent is used can be expected.
Therefore, it is clear that the method of the present invention is effective for corrosion protection of metals in water.
【0036】以上の結果から、炭酸ガスの吹き込みを行
わない場合には、腐食防止には有効であっても、スケー
ル防止はできないのに対し、炭酸ガスの吹き込みを行う
本発明の方法では、スケール防止剤及び防食剤を使用し
た場合に匹敵するスケール防止効果及び防食効果を達成
できることが明らかである。From the above results, when the carbon dioxide gas is not blown, the scale cannot be prevented even though it is effective in preventing corrosion, whereas the method of the present invention in which the carbon dioxide gas is blown in does not scale. It is clear that comparable scale inhibition and anticorrosion effects can be achieved with the use of inhibitors and anticorrosion agents.
【0037】[0037]
【発明の効果】以上詳述した通り、本発明の循環水の処
理方法によれば、炭酸カルシウムの析出が予想される水
に炭酸ガスを接触させるという極めて簡易な操作によっ
て、スケールの生成防止及び金属の腐食防止を、容易か
つ効率的に、しかも安価に実現することが可能になっ
た。As described in detail above, according to the method for treating circulating water of the present invention, scale formation can be prevented and prevented by a very simple operation of bringing carbon dioxide into contact with water in which calcium carbonate is expected to precipitate. It has become possible to easily, efficiently and inexpensively prevent metal corrosion.
【0038】本発明によれば、腐食やスケールといった
障害を生じることなく、水の高度利用を図ることがで
き、工業的、経済的に極めて有利である。According to the present invention, it is possible to make advanced use of water without causing damage such as corrosion and scale, which is extremely advantageous industrially and economically.
【図1】本発明の循環水の処理方法の一実施例方法を示
す系統図である。FIG. 1 is a system diagram showing a method of an embodiment of a method for treating circulating water according to the present invention.
【図2】本発明の循環水の処理方法の他の実施例方法を
示す系統図である。FIG. 2 is a system diagram showing another embodiment method of the circulating water treatment method of the present invention.
【図3】実施例1及び比較例1,2における濃縮倍数と
水中のカルシウム硬度との関係を示すグラフである。FIG. 3 is a graph showing the relationship between concentration factor and calcium hardness in water in Example 1 and Comparative Examples 1 and 2.
【図4】実施例2及び比較例3,4における腐食減量の
経時変化を示すグラフである。FIG. 4 is a graph showing changes over time in corrosion weight loss in Example 2 and Comparative Examples 3 and 4.
1 冷却塔 3A,3B 熱交換器 6 手動バルブ 7 電磁バルブ 8 pHコントローラ 8A pHセンサー 1 Cooling Tower 3A, 3B Heat Exchanger 6 Manual Valve 7 Electromagnetic Valve 8 pH Controller 8A pH Sensor
Claims (1)
に炭酸ガスを添加することを特徴とする循環水の処理方
法。1. A method for treating circulating water, which comprises adding carbon dioxide gas to circulating water in which calcium carbonate tends to precipitate.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP25166593A JPH07109585A (en) | 1993-10-07 | 1993-10-07 | Treatment of circulating water |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP25166593A JPH07109585A (en) | 1993-10-07 | 1993-10-07 | Treatment of circulating water |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH07109585A true JPH07109585A (en) | 1995-04-25 |
Family
ID=17226203
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP25166593A Pending JPH07109585A (en) | 1993-10-07 | 1993-10-07 | Treatment of circulating water |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH07109585A (en) |
Cited By (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001070987A (en) * | 1999-09-03 | 2001-03-21 | Katayama Chem Works Co Ltd | Water treatment method |
JP2007209942A (en) * | 2006-02-13 | 2007-08-23 | Fujita Corp | Obtaining method of variation of concentration of dissolved calcium |
JP2010078239A (en) * | 2008-09-26 | 2010-04-08 | Tokyo Electric Power Co Inc:The | Water heater and method of preventing scale deposition |
EP2213630A1 (en) * | 2009-01-12 | 2010-08-04 | L'Air Liquide Société Anonyme pour l'Etude et l'Exploitation des Procédés Georges Claude | Method to inhibit scale formation in cooling circuits using carbon dioxide |
JP2010223525A (en) * | 2009-03-25 | 2010-10-07 | Osaka Gas Co Ltd | Method and device of removing scale attached to piping of heat exchanger |
JP2012179601A (en) * | 2012-05-11 | 2012-09-20 | Fujita Corp | Obtaining method of variation of concentration of dissolved calcium |
WO2014096845A1 (en) * | 2012-12-20 | 2014-06-26 | Linde Aktiengesellschaft | Cooling process |
CN104071890A (en) * | 2014-06-27 | 2014-10-01 | 重庆大学 | Method for removing calcium carbonate scales by using microbial extracellular carbonic anhydrase |
NL2010885C2 (en) * | 2013-05-29 | 2014-12-02 | Stichting Dienst Landbouwkundi | Cooling water. |
CN110028145A (en) * | 2019-04-23 | 2019-07-19 | 李卫 | A kind of thermal power plant indirect air cooling unit Circulating Water Corrosion control system and method |
WO2024203967A1 (en) * | 2023-03-24 | 2024-10-03 | 住友重機械工業株式会社 | Condenser and boiler system comprising condenser |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS61220793A (en) * | 1985-03-25 | 1986-10-01 | Sasakura Eng Co Ltd | Method for monitoring and controlling water quality |
-
1993
- 1993-10-07 JP JP25166593A patent/JPH07109585A/en active Pending
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
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JPS61220793A (en) * | 1985-03-25 | 1986-10-01 | Sasakura Eng Co Ltd | Method for monitoring and controlling water quality |
Cited By (14)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001070987A (en) * | 1999-09-03 | 2001-03-21 | Katayama Chem Works Co Ltd | Water treatment method |
JP2007209942A (en) * | 2006-02-13 | 2007-08-23 | Fujita Corp | Obtaining method of variation of concentration of dissolved calcium |
JP2010078239A (en) * | 2008-09-26 | 2010-04-08 | Tokyo Electric Power Co Inc:The | Water heater and method of preventing scale deposition |
EP2213630A1 (en) * | 2009-01-12 | 2010-08-04 | L'Air Liquide Société Anonyme pour l'Etude et l'Exploitation des Procédés Georges Claude | Method to inhibit scale formation in cooling circuits using carbon dioxide |
US8153010B2 (en) | 2009-01-12 | 2012-04-10 | American Air Liquide, Inc. | Method to inhibit scale formation in cooling circuits using carbon dioxide |
JP2010223525A (en) * | 2009-03-25 | 2010-10-07 | Osaka Gas Co Ltd | Method and device of removing scale attached to piping of heat exchanger |
JP2012179601A (en) * | 2012-05-11 | 2012-09-20 | Fujita Corp | Obtaining method of variation of concentration of dissolved calcium |
WO2014096845A1 (en) * | 2012-12-20 | 2014-06-26 | Linde Aktiengesellschaft | Cooling process |
US10527370B2 (en) | 2012-12-20 | 2020-01-07 | Linde Aktiengesellschaft | Cooling process |
NL2010885C2 (en) * | 2013-05-29 | 2014-12-02 | Stichting Dienst Landbouwkundi | Cooling water. |
WO2014193230A1 (en) * | 2013-05-29 | 2014-12-04 | Stichting Dienst Landbouwkundig Onderzoek | Cooling water |
CN104071890A (en) * | 2014-06-27 | 2014-10-01 | 重庆大学 | Method for removing calcium carbonate scales by using microbial extracellular carbonic anhydrase |
CN110028145A (en) * | 2019-04-23 | 2019-07-19 | 李卫 | A kind of thermal power plant indirect air cooling unit Circulating Water Corrosion control system and method |
WO2024203967A1 (en) * | 2023-03-24 | 2024-10-03 | 住友重機械工業株式会社 | Condenser and boiler system comprising condenser |
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