JPH1133565A - Method for preventing corrosion of water heat storage apparatus - Google Patents

Method for preventing corrosion of water heat storage apparatus

Info

Publication number
JPH1133565A
JPH1133565A JP9208444A JP20844497A JPH1133565A JP H1133565 A JPH1133565 A JP H1133565A JP 9208444 A JP9208444 A JP 9208444A JP 20844497 A JP20844497 A JP 20844497A JP H1133565 A JPH1133565 A JP H1133565A
Authority
JP
Japan
Prior art keywords
water
slaked lime
index
carbon dioxide
heat storage
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
JP9208444A
Other languages
Japanese (ja)
Inventor
Isao Funahashi
勲 舟橋
Kiwamu Yamamoto
究 山本
Yoshio Shimada
喜夫 島田
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
Kureha Engineering Co Ltd
Original Assignee
Kureha Corp
Kureha 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 Kureha Corp, Kureha Engineering Co Ltd filed Critical Kureha Corp
Priority to JP9208444A priority Critical patent/JPH1133565A/en
Priority to KR1019980028813A priority patent/KR19990013931A/en
Publication of JPH1133565A publication Critical patent/JPH1133565A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F5/00Softening water; Preventing scale; Adding scale preventatives or scale removers to water, e.g. adding sequestering agents
    • C02F5/08Treatment of water with complexing chemicals or other solubilising agents for softening, scale prevention or scale removal, e.g. adding sequestering agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/08Corrosion 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

PROBLEM TO BE SOLVED: To prevent the corrosion of the piping, heat exchanger or the like of a water heat storage system without largely lowering the heat conductivity of the heat exchange part of the heat storage system by using slaked lime and carbon dioxide to respectively adjust the pH, Langelier index and Larson index of circulating water to specified ranges. SOLUTION: When a heat storage system is filled with water, the total alkalinity, calcium hardness, concn. of sulfate ions and concn. of chlorine ions of raw water used in filling are analyzed not only to determine an injection ratio of slaked lime setting a Langelier index to -0.5 to +0.2 and a Larson index to 0.05 to 0.2 but also to adjust the pH of intake water to 7.5 to 9. In this case, the raw water is sent to a mixing adjusting tank 4 from a filling water flow rate regulator 7 and a carbonated water making apparatus 3 and slaked lime is sent to the mixing adjusting tank 4 as a slaked lime aq. soln. by a slaked lime aq. soln. making apparatus 1 so that the amt. thereof becomes a predetermined water filling control slaked lime injection ratio by the filling water flow rate regulator 7. A carbon dioxide flow rate regulating valve 9 is controlled so that a pH value becomes a water filling control pH value.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明が属する技術分野】本発明は水蓄熱システムの腐
食防止方法に関する。さらに詳しくは水蓄熱システムの
水配管や接続機器等の循環水と接触する金属の表面の腐
食を防止する方法に関する。
The present invention relates to a method for preventing corrosion of a water heat storage system. More particularly, the present invention relates to a method for preventing corrosion of a metal surface that comes into contact with circulating water such as a water pipe or a connection device of a water heat storage system.

【0002】[0002]

【従来の技術】深夜電力、河川の熱エネルギーや都市の
排熱エネルギーなどを有効に利用し、地域の冷暖房に使
用する蓄熱システムは、省エネルギーや炭酸ガスを放出
しないシステムとして、近年益々その設置が拡大してい
る。水蓄熱システムは、水を熱輸送媒体として使用し、
蓄熱部と熱使用部の間に冷水や温水を循環させ地域の冷
暖房を行う熱循環システムである。この水蓄熱システム
は、蓄熱槽、熱交換部、水ポンプ、配管、熱利用部の熱
交換部(銅フィンコイル)などからなり、蓄熱槽でつく
られた冷水や温水が熱利用部へ送られ熱交換部で熱交換
をして利用され、蓄熱システムの蓄熱槽へ戻ってくる。
2. Description of the Related Art In recent years, a heat storage system for effectively utilizing midnight power, river heat energy, urban waste heat energy, and the like for cooling and heating in a region has been increasingly installed as a system that does not emit energy or emit carbon dioxide. It is expanding. Water heat storage systems use water as a heat transport medium,
This is a heat circulation system that circulates cold or hot water between the heat storage unit and the heat use unit to cool and heat the area. This water heat storage system consists of a heat storage tank, a heat exchange unit, a water pump, piping, and a heat exchange unit (copper fin coil) for the heat utilization unit. Cold water and hot water created in the heat storage tank are sent to the heat utilization unit. It is used after heat exchange in the heat exchange section, and returns to the heat storage tank of the heat storage system.

【0003】蓄熱槽の構造材料が、コンクリートやモル
タル材であった時には、蓄熱システムの水中の遊離炭酸
が構造材料中の消石灰と反応してpHの上昇や炭酸水素
カルシウムの生成により水質改善が行われ、水は非腐食
性となっていた。しかし、最近の蓄熱槽は、コンクリー
トの上にエポキシ樹脂などの合成樹脂をコーティングし
たものが多くなってきており、上記の水質改善が行われ
ず、そのため水配管や利用者側の熱交換部の腐食が激し
くなっている。
When the structural material of the heat storage tank is concrete or mortar material, the free carbonic acid in the water of the heat storage system reacts with the slaked lime in the structural material to increase the pH and to improve the water quality by generating calcium bicarbonate. The water was non-corrosive. However, in recent heat storage tanks, concrete has been coated with a synthetic resin such as epoxy resin on concrete, and the above-mentioned water quality improvement has not been carried out. Therefore, corrosion of water pipes and heat exchange parts on the user side has occurred. Is getting more intense.

【0004】低硬度、低炭酸の水道水の防錆を目的とし
て水道水に消石灰と炭酸ガスを注入してランゲリア指数
を改善する方法(例えば特開平2−194893号公報
参照。)は、最近自治体水道やビル・マンションなどで
広く使用されている。この方法は、水に消石灰と炭酸ガ
スを注入し、鉄等の水配管の内面に炭酸カルシウムを主
体とする保護皮膜を形成させ、腐食を防止するものであ
る。
[0004] A method of improving the Langelia index by injecting slaked lime and carbon dioxide into tap water for the purpose of preventing rust of low-hardness, low-carbonate tap water (for example, see Japanese Unexamined Patent Publication (Kokai) No. 2-194893) has recently been proposed by local governments. Widely used in water supply, buildings and condominiums. In this method, slaked lime and carbon dioxide gas are injected into water to form a protective film mainly composed of calcium carbonate on the inner surface of a water pipe made of iron or the like, thereby preventing corrosion.

【0005】しかし、水蓄熱システムにおいては熱交換
器の材質としては銅が主に用いられている。熱交換器の
銅フィンコイル等の表面に保護皮膜が厚く形成されると
熱伝導度が低下し熱交換器の効率が低下する。また銅フ
ィンコイル等の腐食も問題となっている。
However, in the water heat storage system, copper is mainly used as a material of the heat exchanger. If a thick protective film is formed on the surface of the copper fin coil or the like of the heat exchanger, the thermal conductivity is reduced, and the efficiency of the heat exchanger is reduced. Corrosion of copper fin coils and the like is also a problem.

【0006】[0006]

【発明が解決しようとする課題】本発明は、水蓄熱シス
テムの熱交換部の熱伝導度を大きく低下させることな
く、該蓄熱システムの配管、熱交換器等の腐食を防止す
る方法を提供することを目的とする。
SUMMARY OF THE INVENTION The present invention provides a method for preventing corrosion of pipes, heat exchangers and the like of a heat storage system without greatly reducing the thermal conductivity of a heat exchange section of the water storage system. The purpose is to:

【0007】[0007]

【課題を解決するための手段】本発明は、消石灰及び炭
酸ガスを用い、循環水のpHを7.5〜9、ランゲリア
指数を−0.5〜+0.2、ラーソン指数を0.05〜
0.2とすることを特徴とする水蓄熱システムの腐食防
止方法である。
The present invention uses slaked lime and carbon dioxide gas, has a circulating water pH of 7.5 to 9, a Langerian index of -0.5 to +0.2, and a Larson index of 0.05 to 0.05.
0.2 is a method for preventing corrosion of a water heat storage system, which is set to 0.2.

【0008】また本発明は、水蓄熱システムに水を張り
込む際に、張り込みに使用する原水の総アルカリ度、カ
ルシウム硬度、硫酸イオン濃度、塩素イオン濃度を予め
測定し、張り込む水のランゲリア指数を−0.5〜+
0.2、ラーソン指数を0.05〜0.2に改善するに
必要な消石灰注入率および張り込む水のpHを求め、前
記原水に前記消石灰注入率になるように消石灰を注入
し、更に炭酸ガスを注入し、消石灰及び炭酸ガス注入後
のpHが前記pHになるように炭酸ガス注入量を制御す
ることを特徴とする水蓄熱システムの腐食防止方法であ
る。
Further, the present invention measures the total alkalinity, calcium hardness, sulfate ion concentration, and chloride ion concentration of raw water used for filling when water is poured into the water heat storage system, and determines the Langerian index of the filled water. From -0.5 to +
0.2, the slaked lime injection rate and the pH of the impregnated water required to improve the Larson index to 0.05 to 0.2 are determined, and slaked lime is injected into the raw water so as to have the slaked lime injection rate. A method for preventing corrosion of a water heat storage system, characterized by injecting a gas and controlling an injection amount of a carbon dioxide gas so that pH after injecting slaked lime and carbon dioxide gas becomes the above-mentioned pH.

【0009】更に、本発明は、水蓄熱システムの循環水
のpH、総アルカリ度、Pアルカリ度又は総酸度、カル
シウム硬度、硫酸イオン濃度、塩素イオン濃度及び溶解
固形分を定期的に測定し、ランゲリア指数及びラーソン
指数を求め、該ランゲリア指数及び該ラーソン指数がラ
ンゲリア指数−0.5〜+0.2、ラーソン指数0.0
5〜0.2の間に設定した目標値からはずれた場合は、
循環水のランゲリア指数及びラーソン指数を目標値に復
帰させるために必要な消石灰及び炭酸ガスの総注入量を
計算又は実験で求め、次いで循環水の一部に消石灰及び
炭酸ガスを両者の総注入量比で一定の注入率で注入した
場合のpHの値を計算又は実験により求め、循環水の一
部に前記一定の注入率で消石灰を注入し、更に炭酸ガス
を注入し、消石灰及び炭酸ガス注入後のpHが前記pH
になるように炭酸ガス注入量を制御し、先に求めた消石
灰の総注入量を注入した時点で消石灰及び炭酸ガスの注
入を停止することを特徴とする水蓄熱システムの腐食防
止方法である。
Further, the present invention is to periodically measure pH, total alkalinity, P alkalinity or total acidity, calcium hardness, sulfate ion concentration, chloride ion concentration and dissolved solid content of circulating water of the water heat storage system, The Langerian index and the Larson index are determined, and the Langerian index and the Larson index are calculated as follows: the Langerian index -0.5 to +0.2, the Larson index 0.0
If it deviates from the target value set between 5 and 0.2,
Calculate or experiment the total amount of slaked lime and carbon dioxide necessary to return the Langerian index and Larson index to the target values of the circulating water, and then add the slaked lime and carbon dioxide to a part of the circulating water The value of pH when injected at a constant injection rate is calculated or experimented, slaked lime is injected at a certain injection rate into a part of the circulating water, carbon dioxide gas is further injected, and slaked lime and carbon dioxide gas are injected. After the pH is above the pH
A method for preventing corrosion of a water heat storage system, characterized in that the injection amount of slaked lime and carbon dioxide gas is stopped when the previously injected slaked lime total injection amount is injected so that the injection amount of carbon dioxide gas is controlled so as to be as follows.

【0010】ここに、ランゲリア指数、ラーソン指数と
は以下のように定義されるものである。 ランゲリア指数=pH−pHs =pH−8.313+log[Ca2+]+log[A]−s (1) ラーソン指数=(2[SO42-]+[Cl-])/[HCO3 -] (2) ここに、 pH:水の実際のpH値 pHs:理論上のpH値 log[Ca2+]:カルシウムイオン濃度の対数 log[A]:総アルカリ度の対数 s:補正値 [SO42-]:硫酸イオン濃度 [Cl-]:塩素イオン濃度 [HCO3 -]:炭酸水素イオン濃度 を表す。
Here, the Langeria index and Larson index are defined as follows. Langelier index = pH-pHs = pH-8.313 + log [Ca 2+] + log [A] -s (1) Larson Index = (2 [SO4 2-] + [Cl -]) / [HCO 3 -] (2 Here, pH: actual pH value of water pHs: theoretical pH value log [Ca 2+ ]: logarithm of calcium ion concentration log [A]: logarithm of total alkalinity s: correction value [SO4 2− ] : sulfate ion concentration [Cl -]: chloride ion concentration [HCO 3 -] - represents bicarbonate ion concentration.

【0011】本発明は、消石灰及び炭酸ガスを用いて、
水蓄熱システムの循環水のpH、ランゲリア指数、ラー
ソン指数を上記範囲に保つことにより、鉄部材の表面に
炭酸カルシウムを主成分とする緻密な保護膜を形成し腐
食を防止し、銅部材の表面には保護膜が過剰に形成され
ることを抑制しかつ銅部材の腐食を防止するものであ
る。
[0011] The present invention uses slaked lime and carbon dioxide gas,
By keeping the pH of the circulating water of the water heat storage system, the Langeria index, and the Larson index within the above ranges, a dense protective film containing calcium carbonate as a main component is formed on the surface of the iron member to prevent corrosion, and the surface of the copper member is prevented. The purpose of the present invention is to prevent the protection film from being formed excessively and to prevent corrosion of the copper member.

【0012】本発明者らは、水温15℃、pH6.8、
カルシウム硬度30mg/L、アルカリ度30mg/
L、遊離炭酸11mg/L、塩素イオン濃度10mg/
L、硫酸イオン濃度10mg/Lで、ランゲリア指数−
2.2、ラーソン指数0.8の水に消石灰を99mg/
L炭酸ガスを116mg/L注入し、pH7.7カルシ
ウム硬度166mg/L、アルカリ度163mg/L、
遊離炭酸7mg/Lランゲリア指数0、ラーソン指数
0.15の水に改善した。この水を内径20mm、長さ
150mmの炭素鋼鋼管とこれと電気的に絶縁した同じ
寸法の銅管に流した。2カ月後に管を切断して内面を調
べたところ、炭素鋼鋼管には約150μmの炭酸カルシ
ウムを主体とする皮膜の形成がみられた。一方銅管には
約1μmの皮膜しか形成されていなかった。
The present inventors have found that the water temperature is 15 ° C., the pH is 6.8,
Calcium hardness 30mg / L, alkalinity 30mg / L
L, free carbonic acid 11 mg / L, chloride ion concentration 10 mg / L
L, at a sulfate ion concentration of 10 mg / L, the
2.2 99 g of slaked lime in water with Larson index of 0.8
L carbon dioxide gas is injected at 116 mg / L, pH 7.7 calcium hardness is 166 mg / L, alkalinity is 163 mg / L,
The water content was improved to 7 mg / L of free carbonic acid and water with a Langeria index of 0 and a Larson index of 0.15. This water was passed through a carbon steel pipe having an inner diameter of 20 mm and a length of 150 mm and a copper pipe of the same dimensions electrically insulated therefrom. Two months later, the pipe was cut and the inner surface thereof was examined. As a result, a coating mainly composed of calcium carbonate of about 150 μm was formed on the carbon steel pipe. On the other hand, only a film of about 1 μm was formed on the copper tube.

【0013】鉄と銅の標準電極電位(水素電極基準)
は、鉄が−0.44V、銅が+0.34Vである。金属
面への炭酸カルシウムの皮膜形成の機構は、 金属面の陽極部:M → M++e (A) 金属面の陰極部:e+1/2H2O+1/4O2 → OH- (B) OH-+Ca2++HCO3 - → CaCO3+H2O (C) と考えられる。(A)式で示される電子を放出しやす
い、即ち電極電位が銅よりも卑な鉄の方が、(B)、
(C)式で示される炭酸カルシウムの皮膜が形成されや
すいものと考えられる。このことより上述の実験で鋼管
の表面への皮膜形成が銅管のそれよりも150倍と大き
かったことが納得される。
Standard electrode potential of iron and copper (based on hydrogen electrode)
Is -0.44V for iron and + 0.34V for copper. Mechanism of film formation of calcium carbonate to the metal surface, the anode portion of the metal surface: cathode part of M → M + + e (A ) metal surface: e + 1 / 2H 2 O + 1 / 4O 2 → OH - (B) OH - + Ca 2 ++ HCO 3 → CaCO 3 + H 2 O (C) It is easy to emit the electrons represented by the formula (A), that is, iron whose electrode potential is lower than that of copper is (B),
It is considered that the calcium carbonate film represented by the formula (C) is easily formed. From this, it can be understood that the film formation on the surface of the steel pipe was 150 times larger than that of the copper pipe in the above-described experiment.

【0014】[0014]

【発明の実施の形態】図1、2に本発明の実施の一形態
を示した。図1及び2を参照しながら本発明の実施の形
態を詳細に説明する。図1は蓄熱システムへの初期水張
用の設備図である。該設備は消石灰水溶液製造装置
(1)、炭酸ガス装置(2)、炭酸水製造装置(3)、
混合調整槽(4)、調整水移送ポンプ(5)などから構
成されている。蓄熱システムに水を張り込む際に、張り
込みに使用する原水(6)は、予め総アルカリ度、カル
シウム硬度、硫酸イオン濃度、塩素イオン濃度が分析さ
れ、張り込む水のランゲリア指数を−0.5〜+0.
2、ラーソン指数を0.05〜0.2に改善するに必要
な消石灰注入率(以下「水張込用管理消石灰注入率」と
呼ぶことがある。)及び張り込む水のpH(以下「水張
込用管理pH値」と呼ぶことがある。)が決定される。
原水(6)は、張込水用流量調節器(7)で所定流量と
なる様に調整され、炭酸水製造装置(3)を通って混合
調整槽(4)へ送られる。消石灰は、低速攪拌機付消石
灰水溶液製造装置(1)で濃度約1600mg/Lの消
石灰水溶液とし、混合調整槽(4)へ送るが、張込水用
流量調節器(7)からの流量信号を受け、この流量に対
して上述のようにして求めた水張込用管理消石灰注入率
となる量が送られる。消石灰水溶液製造装置(1)は溢
流型の槽であり、多量の消石灰粉末が投入され低速攪拌
機で攪拌されているが、消石灰水溶液製造用の水は給水
流量調節器(8)を通って消石灰水溶液製造装置(1)
の下部から張込水の流量に見合った量が供給され消石灰
水灰溶液(14)となって消石灰水溶液製造装置(1)
から溢流して、混合調整槽(4)へ送られる。炭酸ガス
は流量調節弁(9)を通って炭酸水製造装置(3)へ送
られ原水(6)と混合されて炭酸水(13)となり、混
合調整槽(4)へ送られるが、混合調整槽(4)に設置
してあるpH調節器(10)で測定されるpH値が水張
込用管理pH値となる様に流量調節弁(9)で制御して
送られる。混合調整槽(4)には仕切壁(11)と攪拌
機(12)が設置してあり、炭酸水(13)と消石灰水
溶液(14)は攪拌混合されて所定水質に調整され、調
整水移送ポンプ(5)を経て水蓄熱システムへ送られ
る。
1 and 2 show an embodiment of the present invention. An embodiment of the present invention will be described in detail with reference to FIGS. FIG. 1 is an equipment diagram for initial filling of the heat storage system. The equipment includes slaked lime aqueous solution production equipment (1), carbon dioxide gas equipment (2), carbonated water production equipment (3),
It comprises a mixing adjustment tank (4), an adjustment water transfer pump (5) and the like. When water is injected into the heat storage system, the raw water (6) used for the injection is analyzed in advance for total alkalinity, calcium hardness, sulfate ion concentration, and chloride ion concentration, and the Langerian index of the injected water is -0.5. ~ + 0.
2. The slaked lime injection rate necessary for improving the Larson index to 0.05 to 0.2 (hereinafter sometimes referred to as “managed slaked lime injection rate for water impregnation”) and the pH of the impregnated water (hereinafter “water”). It may be referred to as “management pH value for intrusion.”).
The raw water (6) is adjusted so as to have a predetermined flow rate by a flow rate controller (7) for filling water, and is sent to a mixing adjustment tank (4) through a carbonated water producing device (3). Slaked lime is made into a slaked lime aqueous solution having a concentration of about 1600 mg / L by a slaked lime aqueous solution manufacturing device (1) equipped with a low-speed stirrer, and sent to the mixing adjustment tank (4). The slaked lime receives a flow signal from the flow controller (7). Then, an amount that becomes the water sludge management slaked lime injection rate determined as described above with respect to this flow rate is sent. The slaked lime aqueous solution production apparatus (1) is an overflow type tank, and a large amount of slaked lime powder is charged and stirred by a low-speed stirrer. Water for producing slaked lime aqueous solution passes through a feedwater flow rate controller (8) and is slaked lime. Aqueous solution production equipment (1)
An amount corresponding to the flow rate of the spilled water is supplied from the lower part of the apparatus to form a slaked lime ash solution (14), and a slaked lime aqueous solution production device (1)
And overflows to the mixing adjustment tank (4). The carbon dioxide gas is sent to the carbonated water production device (3) through the flow control valve (9) and mixed with the raw water (6) to become carbonated water (13) and sent to the mixing adjustment tank (4). The water is controlled and controlled by a flow rate control valve (9) so that the pH value measured by a pH controller (10) installed in a tank (4) becomes a control pH value for water impregnation. A partition wall (11) and a stirrer (12) are installed in the mixing adjustment tank (4), and the carbonated water (13) and the slaked lime aqueous solution (14) are stirred and mixed to adjust to a predetermined water quality. It is sent to the water heat storage system via (5).

【0015】なお、本発明においては水蓄熱システムへ
送られる水のランゲリア指数は−0.5〜+0.2の間
に調整されるが、ランゲリア指数が+0.2以上となる
と形成される炭酸カルシウムを主体とする保護皮膜の結
晶の粒子が荒くなり緻密な保護膜とならず腐食防止の効
果が低下する。ランゲリア指数が−0.5以下では保護
皮膜の形成が不充分となる。またラーソン指数は0.0
5〜0.02の範囲とするが、ラーソン指数が0.05
以下では溶解無機炭酸が多くなりすぎ銅の溶解が増大
し、0.2以上では銅の腐食(孔食)抑制効果が小さ
い。また、蓄熱システムへ送られる水は、pHが7.5
〜9、総アルカリ度が60〜175mg/L、好ましく
は75〜150mg/L、カルシウム硬度が60〜17
5mg/L、好ましくは75〜150mg/Lであるこ
とが望ましい。水蓄熱システムへの水の張り込みが長時
間にわたり、途中で原水の水質が変化するおそれがある
ときは、時々原水の総アルカリ度、カルシウム硬度、硫
酸イオン濃度、塩素イオン濃度を測定し、水張込用管理
消石灰注入率及び水張込用管理pH値を設定し直す。
In the present invention, the Langerian index of the water sent to the water heat storage system is adjusted between -0.5 and +0.2. The particles of the crystal of the protective film mainly composed of are roughened, so that the protective film does not become dense and the effect of preventing corrosion is reduced. When the Langeria index is -0.5 or less, formation of the protective film becomes insufficient. The Larson index is 0.0
The Larson index is 0.05 to 0.05.
Below, the amount of dissolved inorganic carbonic acid becomes too large, and the dissolution of copper increases, and above 0.2, the effect of suppressing corrosion (pitting) of copper is small. The water sent to the heat storage system has a pH of 7.5.
-9, total alkalinity 60-175 mg / L, preferably 75-150 mg / L, calcium hardness 60-17
It is desirably 5 mg / L, preferably 75 to 150 mg / L. If the water quality of the raw water changes during the long period of time when the water is immersed in the water heat storage system, measure the total alkalinity, calcium hardness, sulfate ion concentration, and chloride ion concentration of the raw water from time to time. Reset the management slaked lime injection rate and the water filling management pH value.

【0016】図2は、水蓄熱システムの水質維持用の設
備図である。該設備は消石灰水溶液製造装置(1)、炭
酸ガス装置(2)、炭酸水製造装置(3)、混合調整槽
(4)、調整水移送ポンプ(5)、消石灰水溶液移送ポ
ンプ(15)、蓄熱槽(21)、蓄熱槽水移送ポンプ
(22)、蓄熱槽水抜出ポンプ(23)、ヒートポンプ
(24)などから構成されている。水蓄熱システムの循
環水は、蓄熱槽水移送ポンプ(22)で客先の熱交換装
置へ移送されて利用され、再び蓄熱槽(21)へ戻って
くる。水蓄熱システムの水は長期間循環し、運転してい
ると循環水中のカルシウムが槽壁や管壁などに析出した
り、沈殿物となって循環水中から分離されたり、水蓄熱
システムのポンプグランド等からの水漏れに対する低カ
ルシウム硬度水の補給によりカルシウム硬度が低下して
くる。カルシウム硬度の値は、循環水を採取してカルシ
ウム硬度をキレート滴定分析法で手分析したり、カルシ
ウムイオン濃度計を循環水中に設置することで測定する
ことができる。カルシウム硬度が低下すると(1)式の
[Ca2+]の値が低下するので、ランゲリア指数は低下
し、目的の水質値から逸脱してしまうことになる。循環
水中で消石灰と炭酸は次式の様に反応していると考えら
れる。 Ca(HCO32は不安定な物質であり、温度上昇によ
り Ca(HCO32 → CaCO3↓+CO2↑+H2O となり、HCO3を分解して炭酸ガスを放出し、炭酸カ
ルシウムを沈殿する。また、Ca(HCO32は金属表
面等の陰極部で生成するOH-により Ca(HCO32+OH- → CaCO3↓+HCO3 -
+H2O となり、炭酸カルシウムを沈殿し、HCO3を分解す
る。従って(2)式の[HCO3 -]値が低下し、ラーソ
ン指数は増大して目的の水質値から逸脱してしまうこと
になる。
FIG. 2 is an equipment diagram for maintaining the water quality of the water heat storage system. The equipment includes slaked lime aqueous solution production equipment (1), carbon dioxide gas equipment (2), carbonated water production equipment (3), mixing adjustment tank (4), regulated water transfer pump (5), slaked lime aqueous solution transfer pump (15), heat storage It comprises a tank (21), a heat storage tank water transfer pump (22), a heat storage tank water extraction pump (23), a heat pump (24) and the like. The circulating water of the water heat storage system is transferred to the heat exchange device at the customer by the heat storage tank water transfer pump (22) and used, and returns to the heat storage tank (21) again. Water in the water heat storage system circulates for a long time, and during operation, calcium in the circulating water precipitates on the tank wall or tube wall, separates from the circulating water as sediment, or the pump ground of the water heat storage system Replenishment of low-calcium hardness water against water leakage from the water lowers the calcium hardness. The value of the calcium hardness can be measured by collecting the circulating water and manually analyzing the calcium hardness by chelate titration analysis, or by installing a calcium ion concentration meter in the circulating water. When the calcium hardness decreases, the value of [Ca 2+ ] in the expression (1) decreases, so that the Langeria index decreases and deviates from the target water quality value. It is considered that slaked lime and carbonic acid react in the circulating water as shown in the following equation. Ca (HCO 3 ) 2 is an unstable substance, and becomes Ca (HCO 3 ) 2 → CaCO 3 ↓ + CO 2 ↑ + H 2 O due to a rise in temperature, decomposes HCO 3 to release carbon dioxide gas, and releases calcium carbonate. Settles. In addition, Ca (HCO 3 ) 2 is converted into Ca (HCO 3 ) 2 + OH → CaCO 3 ↓ + HCO 3 by OH generated at a cathode portion such as a metal surface.
+ H 2 O to precipitate calcium carbonate and decompose HCO 3 . Therefore, the [HCO 3 ] value in the equation (2) decreases, and the Larson index increases, deviating from the target water quality value.

【0017】水蓄熱システムの水質管理は、蓄熱システ
ムの循環水の水質を定期的に分析して水質変化を監視
し、水質が管理目標値から外れた場合は、その差と蓄熱
システム保有水量から補充するべきカルシウム量及び炭
酸ガス量を計算し水質維持装置によって補給する。具体
的には、定期的に蓄熱システムの循環水のpH、総アル
カリ度、Pアルカリ度又は総酸度、カルシウム硬度、硫
酸イオン濃度、塩素イオン濃度及び溶解固形分等を測定
し、ランゲリア指数及びラーソン指数を求める。該ラン
ゲリア指数及び該ラーソン指数がランゲリア指数−0.
5〜+0.2、ラーソン指数0.05〜0.2の間に設
定した目標値からはずれた場合は、循環水のランゲリア
指数及びラーソン指数を目標値に復帰させるために必要
な消石灰及び炭酸ガスの総注入量を、水蓄熱システムの
総保有水量を考慮して計算又は実験で求め、次いで循環
水の一部に消石灰及び炭酸ガスを両者の総注入量比で一
定の注入率で注入した場合のpHの値(以下「水質維持
用管理pH値」と呼ぶことがある。)を計算又は実験に
より求め、循環水の一部に前記一定の注入率で消石灰を
注入し、更に炭酸ガスを注入し、消石灰及び炭酸ガス注
入後のpHが水質維持用管理pH値になるように炭酸ガ
ス注入量を制御する。即ち、消石灰水溶液製造装置
(1)から出る消石灰水溶液の濃度は、ほぼ一定の16
00mg/Lであるからカルシウム所要補充量から総消
石灰水溶液注入量を計算し、この値を消石灰水溶液製造
装置(1)の給水流量積算計(16)に運転終了ポイン
トとしてセットする。水蓄熱システムから蓄熱槽水抜出
ポンプ(23)によって一定流量の水を抜き出し、これ
に炭酸ガスを注入して混合調整槽(4)に送る。この蓄
熱槽水抜出ポンプ(23)からの水に対して先に設定し
た一定注入率になる様に消石灰水溶液製造装置(1)か
ら消石灰水溶液移送ポンプ(15)によって消石灰水溶
液を混合調整槽(4)に送る。混合調整槽(4)には攪
拌機(12)を備えて各溶液を均一に混合しpH調節器
(10)によってpHを測定する。炭酸ガスの注入は、
pH調節器(10)で測定される値が水質維持用管理p
H値になる様に流量調節弁(9)を制御して行う。この
様にして調整された水は調整水移送ポンプ(5)によっ
て水蓄熱システムへ戻す。熱交換器へのスケーリング等
に対する安全を考慮して水質調整用水の抜き出しは、熱
交換器から蓄熱槽中央部方向へ水が流れる時のみ自動的
に運転し、戻した水が直ちに再び汲み上げられることが
無い様に汲み出し口の下流側に戻す。この様にして先に
セットした給水流量積算計(16)の設定値が運転終了
ポイントに達したとき消石灰及び炭酸ガスの注入を停止
し水質調整は完了する。
Water quality management of the water heat storage system is performed by periodically analyzing the water quality of the circulating water of the heat storage system and monitoring the change in water quality. If the water quality deviates from the management target value, the difference and the water storage amount of the heat storage system are used. The amount of calcium and carbon dioxide to be replenished is calculated and replenished by the water quality maintenance device. Specifically, the pH, total alkalinity, P alkalinity or total acidity, calcium hardness, sulfate ion concentration, chloride ion concentration, dissolved solid content, etc. of the circulating water of the heat storage system are periodically measured, and the Langerier index and Larson index are measured. Find the index. The Langerian index and the Larson index are calculated as follows:
If the values deviate from the target values set between 5 and +0.2 and the Larson index between 0.05 and 0.2, slaked lime and carbon dioxide required to return the Langerian index and Larson index of the circulating water to the target values are obtained. The total injection amount of the water is calculated or experimented in consideration of the total water storage capacity of the water heat storage system, and then slaked lime and carbon dioxide gas are injected into a part of the circulating water at a fixed injection ratio based on the total injection ratio of both. (Hereinafter sometimes referred to as "water quality maintenance management pH value") is calculated or experimented, slaked lime is injected into a part of the circulating water at the above constant injection rate, and carbon dioxide gas is further injected. Then, the amount of carbon dioxide gas injected is controlled so that the pH after injecting slaked lime and carbon dioxide gas becomes the management pH value for maintaining water quality. That is, the concentration of the slaked lime aqueous solution coming out of the slaked lime aqueous solution production apparatus (1) is approximately constant 16
Since it is 00 mg / L, the total slaked lime aqueous solution injection amount is calculated from the required calcium replenishment amount, and this value is set as an operation end point in the feedwater flow rate integrator (16) of the slaked lime aqueous solution manufacturing apparatus (1). A constant flow rate of water is extracted from the water heat storage system by a heat storage tank water extraction pump (23), carbon dioxide gas is injected into the water, and sent to the mixing adjustment tank (4). The slaked lime aqueous solution is mixed by the slaked lime aqueous solution transfer pump (15) from the slaked lime aqueous solution manufacturing apparatus (1) so that the water from the heat storage tank water extraction pump (23) has a predetermined injection rate. ). The mixing tank (4) is provided with a stirrer (12) to uniformly mix each solution, and the pH is measured by a pH controller (10). Carbon dioxide injection
The value measured by the pH controller (10) is the water quality management p
The control is performed by controlling the flow rate control valve (9) so that the H value is obtained. The conditioned water is returned to the water heat storage system by the conditioned water transfer pump (5). In consideration of safety against scaling to the heat exchanger, the water for water quality adjustment is automatically drained only when water flows from the heat exchanger toward the center of the heat storage tank, and the returned water is immediately pumped up again. Return to the downstream side of the pumping outlet so that there is no When the set value of the feedwater flow rate integrator (16) set earlier reaches the operation end point, the injection of slaked lime and carbon dioxide gas is stopped, and the water quality adjustment is completed.

【0018】なお、水蓄熱システムへ戻される水は、p
H7.5〜9、ランゲリア指数−0.5〜+0.2、ラ
ーソン指数0.05〜0.02、総アルカリ度60〜1
75mg/L、好ましくは75〜150mg/L、カル
シウム硬度60〜175mg/L、好ましくは75〜1
50mg/Lの範囲にあることが望ましい。従って、水
蓄熱システムの循環水のランゲリア指数及びラーソン指
数の目標値及び水質維持装置を運転する時期を決定する
該目標値からの偏差は水蓄熱システムへ戻す水の水質が
上記範囲に入るように設定することが好ましい。
The water returned to the water heat storage system is p
H7.5-9, Langeria index -0.5- + 0.2, Larson index 0.05-0.02, total alkalinity 60-1
75 mg / L, preferably 75 to 150 mg / L, calcium hardness 60 to 175 mg / L, preferably 75 to 1
It is desirable to be in the range of 50 mg / L. Accordingly, deviations from the target values of the Langerian index and Larson index of the circulating water of the water heat storage system and the target values that determine when to operate the water quality maintenance device are set so that the quality of the water returned to the water heat storage system falls within the above range. It is preferable to set.

【0019】[0019]

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明を実施するための装置の一例を示す構成
図である。
FIG. 1 is a configuration diagram illustrating an example of an apparatus for implementing the present invention.

【図2】本発明を実施するための装置の一例を示す構成
図である。
FIG. 2 is a configuration diagram illustrating an example of an apparatus for implementing the present invention.

【0020】[0020]

【符号の説明】[Explanation of symbols]

1.消石灰水溶液製造装置 2.炭酸ガス装置 3.炭酸水製造装置 4.混合調整槽 5.調整水移送ポンプ 6.原水 7.張込水用流量調節器 8.給水流量調節器 9.流量調節弁 10.pH測定器 11.仕切板 12.撹拌機 13.炭酸水 14.消石灰水溶液 15.消石灰水溶液移送ポンプ 16.給水流量積算計 21.蓄熱槽 22.蓄熱槽水移送ポンプ 23.蓄熱糟水抜出ポンプ 24.ヒートポンプ 1. Slaked lime aqueous solution production equipment 2. Carbon dioxide device 3. Carbonated water production equipment 4. Mixing adjustment tank 5. Regulated water transfer pump 6. Raw water 7. 7. Flow rate controller for seawater Water supply flow controller 9. Flow control valve 10. pH meter 11. Partition plate 12. Stirrer 13. Carbonated water 14. Slaked lime aqueous solution 15. Slaked lime aqueous solution transfer pump 16. Feed water flow meter 21. Thermal storage tank 22. Heat storage tank water transfer pump 23. Heat storage tank drainage pump 24. heat pump

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 消石灰及び炭酸ガスを用い、循環水のp
Hを7.5〜9、ランゲリア指数を−0.5〜+0.
2、ラーソン指数を0.05〜0.2とすることを特徴
とする水蓄熱システムの腐食防止方法。
1. Using slaked lime and carbon dioxide gas, p of circulating water
H is 7.5 to 9, and the Langeria index is -0.5 to +0.
2. A method for preventing corrosion of a water heat storage system, wherein the Larson index is 0.05 to 0.2.
【請求項2】 水蓄熱システムに水を張り込む際に、張
り込みに使用する原水の総アルカリ度、カルシウム硬
度、硫酸イオン濃度、塩素イオン濃度を予め測定し、張
り込む水のランゲリア指数を−0.5〜+0.2、ラー
ソン指数を0.05〜0.2に改善するに必要な消石灰
注入率および張り込む水のpHを求め、前記原水に前記
消石灰注入率になるように消石灰を注入し、更に炭酸ガ
スを注入し、消石灰及び炭酸ガス注入後のpHが前記p
Hになるように炭酸ガス注入量を制御することを特徴と
する水蓄熱システムの腐食防止方法。
2. When water is poured into a water heat storage system, the total alkalinity, calcium hardness, sulfate ion concentration, and chloride ion concentration of raw water used for the filling are measured in advance, and the Langerian index of the filled water is set to −0. The slaked lime injection rate and the pH of the impregnated water required to improve the Larson index to 0.05 to 0.2 are determined, and slaked lime is injected into the raw water so as to have the slaked lime injection rate. And further inject carbon dioxide gas, and the pH after injecting slaked lime and carbon dioxide
A method for preventing corrosion of a water heat storage system, wherein the amount of carbon dioxide gas injected is controlled so as to be H.
【請求項3】 水蓄熱システムの循環水のpH、総アル
カリ度、Pアルカリ度又は総酸度、カルシウム硬度、硫
酸イオン濃度、塩素イオン濃度及び溶解固形分を定期的
に測定し、ランゲリア指数及びラーソン指数を求め、該
ランゲリア指数及び該ラーソン指数がランゲリア指数−
0.5〜+0.2、ラーソン指数0.05〜0.2の間
に設定した目標値からはずれた場合は、循環水のランゲ
リア指数及びラーソン指数を目標値に復帰させるために
必要な消石灰及び炭酸ガスの総注入量を計算又は実験で
求め、次いで循環水の一部に消石灰及び炭酸ガスを両者
の総注入量比で一定の注入率で注入した場合のpHの値
を計算又は実験により求め、循環水の一部に前記一定の
注入率で消石灰を注入し、更に炭酸ガスを注入し、消石
灰及び炭酸ガス注入後のpHが前記pHになるように炭
酸ガス注入量を制御し、先に求めた消石灰の総注入量を
注入した時点で消石灰及び炭酸ガスの注入を停止するこ
とを特徴とする水蓄熱システムの腐食防止方法。
3. The pH, total alkalinity, total alkalinity, total alkalinity or total acidity, calcium hardness, sulfate ion concentration, chloride ion concentration and dissolved solid content of the circulating water of the water heat storage system are periodically measured, and the Langerier index and Larson's index are measured. An index is obtained, and the Langerian index and the Larson index are calculated as
If the values deviate from the target values set between 0.5 to +0.2 and the Larson index of 0.05 to 0.2, slaked lime required for returning the circulating water to the target values of the Langeria index and the Larson index are obtained. Calculate or experiment the total injection amount of carbon dioxide gas, and then calculate or experiment the pH value when slaked lime and carbon dioxide gas are injected into a part of the circulating water at a constant injection rate at the total injection ratio of both. Injecting slaked lime at a certain injection rate into a part of the circulating water, further injecting carbon dioxide gas, controlling the amount of carbon dioxide gas injected so that the pH after slaked lime and carbon dioxide gas injection becomes the above pH, A method for preventing corrosion of a water heat storage system, wherein the injection of slaked lime and carbon dioxide gas is stopped when the obtained total amount of slaked lime is injected.
JP9208444A 1997-07-16 1997-07-16 Method for preventing corrosion of water heat storage apparatus Pending JPH1133565A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP9208444A JPH1133565A (en) 1997-07-16 1997-07-16 Method for preventing corrosion of water heat storage apparatus
KR1019980028813A KR19990013931A (en) 1997-07-16 1998-07-16 Corrosion Prevention Method of Shrinkage Heat System

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9208444A JPH1133565A (en) 1997-07-16 1997-07-16 Method for preventing corrosion of water heat storage apparatus

Publications (1)

Publication Number Publication Date
JPH1133565A true JPH1133565A (en) 1999-02-09

Family

ID=16556320

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9208444A Pending JPH1133565A (en) 1997-07-16 1997-07-16 Method for preventing corrosion of water heat storage apparatus

Country Status (2)

Country Link
JP (1) JPH1133565A (en)
KR (1) KR19990013931A (en)

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* Cited by examiner, † Cited by third party
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JP2010137224A (en) * 2010-02-12 2010-06-24 Kureha Engineering Co Ltd Method for cleaning water
JP2011183247A (en) * 2010-03-04 2011-09-22 Kobelco Eco-Solutions Co Ltd Water treatment apparatus and water treatment method

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010137224A (en) * 2010-02-12 2010-06-24 Kureha Engineering Co Ltd Method for cleaning water
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