JP2021188884A - Pipe cleaning method - Google Patents

Pipe cleaning method Download PDF

Info

Publication number
JP2021188884A
JP2021188884A JP2020097867A JP2020097867A JP2021188884A JP 2021188884 A JP2021188884 A JP 2021188884A JP 2020097867 A JP2020097867 A JP 2020097867A JP 2020097867 A JP2020097867 A JP 2020097867A JP 2021188884 A JP2021188884 A JP 2021188884A
Authority
JP
Japan
Prior art keywords
cleaning
pipe
ppm
water
cleaning liquid
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.)
Granted
Application number
JP2020097867A
Other languages
Japanese (ja)
Other versions
JP7453065B2 (en
Inventor
孝典 田中
Takanori Tanaka
信司 泉山
Shinji Izumiyama
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.)
Kao Corp
Original Assignee
Kao Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kao Corp filed Critical Kao Corp
Priority to JP2020097867A priority Critical patent/JP7453065B2/en
Publication of JP2021188884A publication Critical patent/JP2021188884A/en
Application granted granted Critical
Publication of JP7453065B2 publication Critical patent/JP7453065B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Cleaning By Liquid Or Steam (AREA)

Abstract

To provide a pipe cleaning method capable of efficiently and reliably cleaning dirt derived from the biofilm of pipes, such as a pipe connected to a facility such as a bathtub, and also capable of suppressing foaming during cleaning and rinsing of pipes.SOLUTION: A pipe cleaning method comprises, after contacting dirt adhering to the inside of a pipe with a cleaning solution containing (a) percarbonate, (b) reducing agent and water for a predetermined time, rinsing the inside of the pipe with water having more than twice the total capacity of the pipe.SELECTED DRAWING: None

Description

本発明は、配管の洗浄方法に関する。 The present invention relates to a method for cleaning pipes.

病院、入居施設、温泉旅館、銭湯などで使用されている大型の浴槽は、浴槽水(温水)を有効利用するために、一般に、循環浄化処理が行われている。浴槽水の循環は、例えば、浴槽の底面や側面に穿設した2つの通水口を循環配管で接続し循環ポンプを使用して行われている。ポンプや配管などで構成される循環経路には、毛髪、タオル布屑、ゴミなどの異物を除去するフィルタ(ヘアキャッチャー)、濾過器、熱交換器などが設けられる。また、レジオネラ属菌などの病原性細菌の増殖を抑制するために、塩素消毒が行われることもある。 Large bathtubs used in hospitals, occupancy facilities, hot spring inns, public baths, etc. are generally subjected to circulation purification treatment in order to effectively use bathtub water (hot water). The circulation of bathtub water is performed, for example, by connecting two water passages bored in the bottom surface or the side surface of the bathtub with a circulation pipe and using a circulation pump. Filters (hair catchers), filters, heat exchangers, etc. that remove foreign substances such as hair, towel cloth, and dust are provided in the circulation path composed of pumps and pipes. In addition, chlorine disinfection may be performed to suppress the growth of pathogenic bacteria such as Legionella spp.

循環経路に配置された配管は、一般に狭い機械室に設置されており、洗浄がしにくく、また、浴槽のように頻繁に洗浄できないために、配管内に付着したスライムやスケールが成長しやすい。配管内でのスライムやスケールの付着は雑菌の発生につながるため、衛生的な環境を整備するためにも、効率的な洗浄が望まれている。 The pipes arranged in the circulation path are generally installed in a narrow machine room, are difficult to wash, and cannot be washed frequently like a bathtub, so slime and scale adhering to the inside of the pipes tend to grow. Adhesion of slime and scale in the pipe leads to the generation of germs, so efficient cleaning is desired to maintain a hygienic environment.

特許文献1には、用水系の機器、装置、配管などの内面に付着したスケールおよびスライムを無機酸あるいは有機酸の水溶液で処理する工程、および前記工程で使用した液を系から排出することなくこれに過酸化ナトリウム、過炭酸ナトリウムあるいは安定化二酸化塩素水に過炭酸ナトリウムを溶解した溶液を添加混合する工程からなる、スケールおよびスライムの化学的除去方法が開示されている。
特許文献2には、酸または酸性塩と過炭酸塩とからなる風呂釜洗浄剤が開示されている。
特許文献3には、配管内を洗浄する方法において、配管の内側を過硫酸塩又は過硫酸塩と界面活性剤を含有する水溶液に接触させた後、過硫酸塩、界面活性剤及び過炭酸アルカリ塩を含有する水溶液に接触させる配管洗浄方法が開示されている。
特許文献4には、所定の無機過酸化物、カチオン系殺菌剤、炭酸塩もしくは重炭酸塩と固体酸とからなる発泡剤を含有する、殺菌性能を有する硬質表面用固形洗浄剤組成物が開示されている。
Patent Document 1 describes a step of treating scales and slimes adhering to the inner surface of water-based equipment, devices, pipes, etc. with an aqueous solution of an inorganic acid or an organic acid, and without discharging the liquid used in the step from the system. A method for chemically removing scale and slime is disclosed, which comprises a step of adding and mixing a solution of sodium percarbonate in sodium peroxide, sodium percarbonate or stabilized chlorine dioxide water.
Patent Document 2 discloses a bath kettle cleaning agent composed of an acid or an acid salt and a percarbonate.
In Patent Document 3, in a method for cleaning the inside of a pipe, the inside of the pipe is brought into contact with a persulfate or an aqueous solution containing a persulfate and a surfactant, and then the persulfate, a surfactant and an alkali percarbonate are described. A method for cleaning a pipe in contact with an aqueous solution containing salt is disclosed.
Patent Document 4 discloses a solid cleaning composition for a hard surface having bactericidal activity, which contains a predetermined inorganic peroxide, a cationic bactericide, a carbonate or a foaming agent composed of a bicarbonate or a solid acid, and has bactericidal performance. Has been done.

特開昭51−037870号公報Japanese Unexamined Patent Publication No. 51-037870 特開昭61−207500号公報Japanese Unexamined Patent Publication No. 61-207500 特開2006−110213号公報Japanese Unexamined Patent Publication No. 2006-110213 特開平11−035987号公報Japanese Unexamined Patent Publication No. 11-035987

本発明は、配管、例えば浴槽などの設備に接続された配管のバイオフィルムに由来する汚れに対して、効率よく、かつ確実に洗浄でき、また、配管の洗浄中やすすぎの際の発泡を抑制することができる配管の洗浄方法を提供する。 INDUSTRIAL APPLICABILITY The present invention can efficiently and reliably clean pipes, for example, stains derived from biofilms of pipes connected to equipment such as bathtubs, and suppress foaming during cleaning and rinsing of pipes. Provide a method of cleaning pipes that can be used.

本発明は、配管内に付着した汚れに(a)過炭酸塩、(b)還元剤及び水を含有する洗浄液〔以下、本発明の洗浄液ともいう〕を所定時間接触させた後、前記配管の総容量の2倍以上の量の水で前記配管内をすすぐ、配管の洗浄方法に関する。 In the present invention, a cleaning liquid containing (a) a percarbonate, (b) a reducing agent and water [hereinafter, also referred to as a cleaning liquid of the present invention] is brought into contact with the dirt adhering to the inside of the pipe for a predetermined time, and then the above-mentioned pipe is used. The present invention relates to a method of cleaning the pipe by rinsing the inside of the pipe with an amount of water more than twice the total capacity.

また、本発明は、(a)過炭酸塩〔以下、(a)成分という〕及び(b)還元剤〔以下、(b)成分という〕を含有し、前記本発明の洗浄方法に用いられる、配管用洗浄剤組成物に関する。 Further, the present invention contains (a) a percarbonate [hereinafter referred to as (a) component] and (b) a reducing agent [hereinafter referred to as (b) component], and is used in the cleaning method of the present invention. Regarding the cleaning agent composition for piping.

本発明によれば、配管、例えば浴槽などの設備に接続された配管のバイオフィルムに由来する汚れに対して、効率よく、かつ確実に洗浄でき、また、配管の洗浄中やすすぎの際の発泡を抑制することができる配管の洗浄方法及びこれに用いる配管用洗浄剤組成物が提供される。
本発明では、配管のバイオフィルムを効率よく洗浄できる上に、配管の洗浄中やすすぎの際の発泡を抑制できるため、過剰な発泡によるバイオフィルムに由来する汚れへの洗浄性の低下や循環装置のエアーロック等の作業性の低下等の不利益が低減され、例えば、すすぎ回数を減らすことが可能となる。
According to the present invention, dirt derived from biofilm of pipes, for example, pipes connected to equipment such as bathtubs, can be efficiently and surely washed, and foaming during washing and rinsing of pipes. A method for cleaning a pipe and a composition for cleaning a pipe used for the method are provided.
In the present invention, the biofilm of the pipe can be efficiently washed, and foaming during cleaning and rinsing of the pipe can be suppressed. Disadvantages such as deterioration of workability such as air lock are reduced, and for example, the number of rinses can be reduced.

本発明の配管の洗浄方法を行う循環風呂システムの一例を示す概略図Schematic diagram showing an example of a circulation bath system for cleaning the piping of the present invention.

(a)成分は、過炭酸塩である。(a)成分は、バイオフィルムに由来する汚れへの洗浄性(以下、洗浄性ともいう)及び作業時の発泡の抑制(以下、発泡抑制性ともいう)の観点から、過炭酸アルカリ金属塩が好ましい。(a)成分は、過炭酸ナトリウムがより好ましい。 The component (a) is a percarbonate. The component (a) is a percarbonate alkali metal salt from the viewpoint of detergency against stains derived from biofilm (hereinafter, also referred to as detergency) and suppression of foaming during work (hereinafter, also referred to as foaming inhibitory property). preferable. As the component (a), sodium percarbonate is more preferable.

本発明の洗浄液中の(a)成分の濃度は、洗浄性及び発泡抑制性の観点から、好ましくは100ppm以上、より好ましくは200ppm以上、更に好ましくは500ppm以上、より更に好ましくは800ppm以上、そして、好ましくは10000ppm以下、より好ましくは8000ppm以下、更に好ましくは6000ppm以下、より更に好ましくは4000ppm以下である。 The concentration of the component (a) in the cleaning liquid of the present invention is preferably 100 ppm or more, more preferably 200 ppm or more, still more preferably 500 ppm or more, still more preferably 800 ppm or more, and from the viewpoint of detergency and foaming inhibitory property. It is preferably 10000 ppm or less, more preferably 8000 ppm or less, still more preferably 6000 ppm or less, still more preferably 4000 ppm or less.

(b)成分は、還元剤である。本発明でいう還元剤は、遷移金属の還元作用を有する化合物であってよい。
(b)成分としては、(b1)エンジオール構造を有する化合物、例えばアスコルビン酸又はその塩、ビタミンC、タンニン酸、エリソルビン酸又はその塩、(b2)ヒドロキシルアミン、例えばN,N−ジエチルヒドロキシルアミン、(b3)フェノール系還元剤、例えば没食子酸、メチルヒドロキノン、ジメチルヒドロキノン、トリメチルヒドロキノン、t−ブチルヒドロキノン、メトキシヒドロキノン、クロロヒドロキノン、及び(b4)その他の還元剤、例えばアスコルビン酸誘導体又はその塩、ハイドロサルファイト、ピロ亜硫酸塩、亜硫酸塩、亜硫酸水素塩、チオ硫酸塩、二酸化チオ尿素、から選ばれる還元剤が挙げられる。
(b)成分は、洗浄性、発泡抑制性及び製品化での適用容易性の観点から、アスコルビン酸及びその塩、並びにビタミンCから選ばれる1種以上の化合物が好ましい。
(B) The component is a reducing agent. The reducing agent referred to in the present invention may be a compound having a reducing action of a transition metal.
The component (b) includes (b1) a compound having an endiol structure, for example, ascorbic acid or a salt thereof, vitamin C, tannic acid, erythorbic acid or a salt thereof, and (b2) a hydroxylamine, for example, N, N-diethylhydroxylamine. , (B3) phenolic reducing agents such as gallic acid, methylhydroquinone, dimethylhydroquinone, trimethylhydroquinone, t-butylhydroquinone, methoxyhydroquinone, chlorohydroquinone, and (b4) other reducing agents such as ascorbic acid derivatives or salts thereof. Examples thereof include a reducing agent selected from hydrosulfite, pyrosulfite, sulfite, hydrogen sulfite, thiosulfate, and thiourea dioxide.
As the component (b), ascorbic acid and a salt thereof, and one or more compounds selected from vitamin C are preferable from the viewpoints of detergency, foaming inhibitory property, and ease of application in commercialization.

本発明の洗浄液中の(b)成分の濃度は、洗浄性及び発泡抑制性の観点から、好ましくは10ppm以上、より好ましくは50ppm以上、更に好ましくは100ppm以上、より更に好ましくは300ppm以上、より更に好ましくは500ppm以上、より更に好ましくは1000ppm以上、より更に好ましくは2500ppm以上、そして、好ましくは100000ppm以下、より好ましくは50000ppm以下、更に好ましくは30000ppm以下、より更に好ましくは10000ppm以下、より更に好ましくは5000ppm以下である。 The concentration of the component (b) in the cleaning liquid of the present invention is preferably 10 ppm or more, more preferably 50 ppm or more, still more preferably 100 ppm or more, still more preferably 300 ppm or more, still more, from the viewpoint of detergency and foaming inhibitory property. It is preferably 500 ppm or more, more preferably 1000 ppm or more, still more preferably 2500 ppm or more, and preferably 100,000 ppm or less, more preferably 50,000 ppm or less, still more preferably 30,000 ppm or less, still more preferably 10,000 ppm or less, still more preferably 5000 ppm. It is as follows.

本発明の洗浄液は、洗浄性及び発泡抑制性の観点から、更に(c)有機酸及びその塩から選ばれる1種以上の化合物〔以下(c)成分という〕を含有することが好ましい。(c)成分としては、マロン酸、リンゴ酸、3−ヒドロキシプロピオン酸、コハク酸、乳酸、酒石酸、グリコール酸、マレイン酸、フマル酸が挙げられる。(c)成分としては、洗浄性及び発泡抑制性の観点から、酒石酸、コハク酸、リンゴ酸及びこれらの塩から選ばれる1種以上の化合物が好ましい。 From the viewpoint of detergency and foaming inhibitory property, the cleaning liquid of the present invention preferably further contains (c) one or more compounds selected from organic acids and salts thereof [hereinafter referred to as (c) component]. Examples of the component (c) include malonic acid, malic acid, 3-hydroxypropionic acid, succinic acid, lactic acid, tartrate acid, glycolic acid, maleic acid, and fumaric acid. As the component (c), one or more compounds selected from tartaric acid, succinic acid, malic acid and salts thereof are preferable from the viewpoint of detergency and foaming inhibitory property.

本発明の洗浄液が(c)成分を含有する場合、該洗浄液中の(c)成分の濃度は、洗浄性の観点から、好ましくは100ppm以上、より好ましくは500ppm以上、更に好ましくは1000ppm以上、より更に好ましくは2500ppm以上、そして、発泡抑制性の観点から、好ましくは10000ppm以下、より好ましくは8000ppm以下、更に好ましくは6000ppm以下、より更に好ましくは4000ppm以下である。 When the cleaning liquid of the present invention contains the component (c), the concentration of the component (c) in the cleaning liquid is preferably 100 ppm or more, more preferably 500 ppm or more, still more preferably 1000 ppm or more, and more, from the viewpoint of cleaning property. It is more preferably 2500 ppm or more, and from the viewpoint of foaming inhibitory property, it is preferably 10000 ppm or less, more preferably 8000 ppm or less, still more preferably 6000 ppm or less, still more preferably 4000 ppm or less.

本発明の洗浄液は、本発明の効果を阻害しない範囲で、(a)成分、(b)成分、(c)成分以外に、例えば、界面活性剤、キレート剤、酵素、消泡剤などの成分を含有することができる。 In addition to the components (a), (b), and (c), the cleaning solution of the present invention contains, for example, components such as a surfactant, a chelating agent, an enzyme, and an antifoaming agent, as long as the effects of the present invention are not impaired. Can be contained.

本発明の洗浄液のpHは、洗浄性及び発泡抑制性の観点から、好ましくは3以上、より好ましくは3.5以上、更に好ましくは3.8以上、そして、好ましくは11以下、より好ましくは6以下、更に好ましくは5以下である。 The pH of the cleaning solution of the present invention is preferably 3 or more, more preferably 3.5 or more, still more preferably 3.8 or more, and preferably 11 or less, more preferably 6 from the viewpoint of detergency and foaming inhibitory property. Below, it is more preferably 5 or less.

本発明の洗浄液の温度は、好ましくは20℃以上、より好ましくは35℃以上、そして、好ましくは60℃以下、より好ましくは45℃以下である。 The temperature of the cleaning liquid of the present invention is preferably 20 ° C. or higher, more preferably 35 ° C. or higher, and preferably 60 ° C. or lower, more preferably 45 ° C. or lower.

本発明の洗浄方法では、配管内に付着した汚れに本発明の洗浄液を所定時間接触させる。汚れはバイオフィルムを含む汚れであってよい。従って、本発明の洗浄方法は、配管内に付着したバイオフィルムを含む汚れに本発明の洗浄液を所定時間接触させる洗浄方法であってよい。前記所定時間、すなわち本発明の洗浄液を汚れに接触させる時間は、洗浄性及び発泡抑制性の観点から、好ましくは5分以上、より好ましくは10分以上、より更に好ましくは20分以上、そして、好ましくは100分以下、より好ましくは60分以下、更に好ましくは45分以下である。 In the cleaning method of the present invention, the cleaning liquid of the present invention is brought into contact with the dirt adhering to the inside of the pipe for a predetermined time. The stain may be a stain containing a biofilm. Therefore, the cleaning method of the present invention may be a cleaning method in which the cleaning liquid of the present invention is brought into contact with the dirt containing the biofilm adhering to the inside of the pipe for a predetermined time. The predetermined time, that is, the time for contacting the cleaning liquid of the present invention with the dirt is preferably 5 minutes or more, more preferably 10 minutes or more, still more preferably 20 minutes or more, and from the viewpoint of detergency and foaming inhibitory property. It is preferably 100 minutes or less, more preferably 60 minutes or less, still more preferably 45 minutes or less.

本発明の洗浄方法では、洗浄後の洗浄液をpH5超、更に6以上、そして、9以下、更に8以下に調整してから配管から排出することが好ましい。 In the cleaning method of the present invention, it is preferable that the cleaning liquid after cleaning is adjusted to pH 5 or more, further 6 or more, 9 or less, and further 8 or less, and then discharged from the pipe.

本発明の洗浄方法では、例えば、排液槽や浴槽等に連結された配管の場合、洗浄液のpHを好ましくは3以上6以下、更に好ましくは3以上5以下として配管と接触させた後、配管から流出させて排液槽や浴槽等に貯め、当該洗浄排出液のpHを好ましくは5超9以下、より好ましくは6以上8以下に調整してから排出することが好ましい。この方法では、初期段階で配管内の汚れが洗浄水中に溶解し、次いでpH調整により溶解した汚れが適度な大きさの水不溶物として析出することで、汚れが配管中に残留しにくく、又、配管外に排出されやすくなり、洗浄効率がより向上するうえ、排出液から汚れ部分をスラッジとして分離等の後処理が容易となり、環境への負荷も低減できるものと考えられる。 In the cleaning method of the present invention, for example, in the case of a pipe connected to a drainage tank, a bathtub, or the like, the pH of the cleaning liquid is preferably 3 or more and 6 or less, more preferably 3 or more and 5 or less, and then the pipe is brought into contact with the pipe. It is preferable that the washing drainage liquid is discharged from the water and stored in a drainage tank, a bathtub, or the like, and the pH of the washing drainage liquid is preferably adjusted to 5 or more and 9 or less, more preferably 6 or more and 8 or less, and then discharged. In this method, the dirt in the pipe is dissolved in the washing water at the initial stage, and then the dirt dissolved by adjusting the pH is deposited as a water-insoluble matter of an appropriate size, so that the dirt is less likely to remain in the pipe, and the dirt is less likely to remain in the pipe. It is considered that the waste can be easily discharged to the outside of the pipe, the cleaning efficiency can be further improved, the post-treatment such as separating the dirty portion from the discharged liquid as sludge can be facilitated, and the load on the environment can be reduced.

本発明の洗浄方法では、洗浄対象の配管内に付着した汚れに本発明の洗浄液を所定時間接触させた後、前記配管の総容量の2倍以上の量の水で前記配管内をすすぐ。すすぎは、複数回行うことが好ましい。配管の洗浄後、例えば、循環浴槽では、運転を再開させるにあたって、次亜塩素酸塩等を低濃度で維持して浴槽水を消毒しながら操業する。その際、本発明の洗浄液が過剰に残留したまま運転すると、次亜塩素酸塩の効果を低下させるため、次亜塩素酸塩の効果に影響を及ぼさない程度まですすぎを行う必要がある。本発明の洗浄方法において、洗浄液の発泡が抑えられることは、一定量の水を用いてすすぎを行う場合に生じる過剰な起泡の抑制につながり、すすぎ回数が増えてもすすぎ効率を損なうことがない。
本発明では、すすぎを複数回行い、1回あたりのすすぎに用いる水の量が、発泡抑制性の観点から、配管の総容量の1倍以上、更に2倍以上、更に3倍以上、そして、4倍以下、更に5倍以下であることが好ましい。
すすぎを行う水の温度は、洗浄性及び発泡抑制性の観点から、例えば、5℃以上60℃以下とすることができる。
In the cleaning method of the present invention, the cleaning liquid of the present invention is brought into contact with the dirt adhering to the inside of the pipe to be cleaned for a predetermined time, and then the inside of the pipe is rinsed with water in an amount of at least twice the total capacity of the pipe. Rinsing is preferably performed multiple times. After cleaning the pipes, for example, in a circulating bathtub, when restarting the operation, the operation is performed while maintaining a low concentration of hypochlorite or the like and disinfecting the bathtub water. At that time, if the operation is performed with the cleaning solution of the present invention remaining excessively, the effect of hypochlorite is reduced, so it is necessary to rinse until the effect of hypochlorite is not affected. In the cleaning method of the present invention, suppressing foaming of the cleaning liquid leads to suppression of excessive foaming that occurs when rinsing with a certain amount of water, and even if the number of rinses increases, the rinsing efficiency may be impaired. No.
In the present invention, rinsing is performed a plurality of times, and the amount of water used for each rinsing is 1 times or more, further 2 times or more, further 3 times or more the total capacity of the pipe from the viewpoint of foaming inhibition, and It is preferably 4 times or less, and more preferably 5 times or less.
The temperature of the water to be rinsed can be, for example, 5 ° C. or higher and 60 ° C. or lower from the viewpoint of detergency and foaming inhibitory property.

本発明の洗浄液、すすぎ水に用いる水は、特に限定されるものではないが、水道水、地下水、温泉水、イオン交換水、蒸留水等を用いることができる。 The water used for the cleaning liquid and the rinsing water of the present invention is not particularly limited, but tap water, groundwater, hot spring water, ion-exchanged water, distilled water and the like can be used.

配管は、循環経路の少なくとも一部を形成していてよい。
循環経路は、配管と接続する浴槽を含んでいてよい。
循環経路は、配管と接続する熱交換器を含んでいてよい。
循環経路は、配管と接続する集塵手段及び/又はろ過手段を含んでいてよい。
これら、浴槽、熱交換器、集塵手段、ろ過手段は、それぞれ、給湯システムなどで用いられている公知のものを採用することができる。
The piping may form at least part of the circulation path.
The circulation path may include a bathtub connected to the pipe.
The circulation path may include a heat exchanger connected to the piping.
The circulation path may include dust collecting means and / or filtering means connected to the pipe.
As these bathtubs, heat exchangers, dust collecting means, and filtering means, known ones used in hot water supply systems and the like can be adopted.

本発明の洗浄方法では、配管が循環経路の少なくとも一部を形成し、洗浄液を循環させて接触させることができる。更に、配管が循環経路の少なくとも一部を形成し、洗浄液を循環させて接触させた後、洗浄液を配管から排出してからすすぎを行うことができる。 In the cleaning method of the present invention, the piping forms at least a part of the circulation path, and the cleaning liquid can be circulated and brought into contact with each other. Further, after the pipe forms at least a part of the circulation path and the cleaning liquid is circulated and brought into contact with the pipe, the cleaning liquid can be discharged from the pipe and then rinsed.

図1を参照して本発明を説明する。図1は、本発明の配管の洗浄方法を行う循環風呂システムの一例を示す概略図である。図1中、1は配管、2は浴槽、3は熱交換器、4はろ過器、5はヘアキャチャー、6は封止栓であり、7は必要に応じて設置される分離装置(例えば、ろ過器、遠心分離機等)であり、矢印は洗浄水又はすすぎのための水(以下、すすぎ水ともいう)の進行方向を示している。図1のシステムでは、配管1と浴槽2は接続して循環経路を構成している。循環経路には配管と接続する熱交換器3、ろ過器4、集塵手段であるヘアキャッチャー5が配置されている。図1のシステムでは、図示しないポンプにより、洗浄水やすすぎ水を送り出すように設定されている。図1では、洗浄水は、配管1から浴槽2に搬送され、更に浴槽2から排出されて配管1に搬送されて、循環経路を矢印の方向に移動して配管の洗浄を行う。循環時間を接触時間であってよく、前記の範囲から選択できる。洗浄液のpH、温度は前記の範囲から選択できる。本発明では、循環させる洗浄液のpHは3以上5以下が好ましい。洗浄液は、所定時間接触を終えた後、循環を止めて、必要に応じてpH調整剤を添加してpHを5超9以下に調整した後、封止栓6を解放して、析出する固形分を浴槽2から排出する経路で、例えば、必要に応じて分離装置7で、ろ過等で除いた後、このシステムから排出される。洗浄液が排出された後、配管1の総容量の2倍以上の量のすすぎ水を循環経路に供給して配管1、浴槽2などのすすぎを行う。図1のように配管が循環経路を形成する場合、すすぎ水の供給を開始する地点から、配管1の総容量に相当する量が供給された時点でいったんすすぎ水の供給を停止し、すすぎ水を循環させて所定時間すすぎを行えばよい。この1回の循環すすぎは、配管1の総容量の1倍の量の水ですすぎを行ったものに相当する。所定時間の循環すすぎが終了した後、そのすすぎ水を排出し、同じ要領で、1回以上すすぎを追加で行うことで、配管1の総容量の2倍以上の量の水で配管のすすぎが行われる。すすぎ水は、水道水などを用いることができる。すすぎ水の温度は特に限定されないが、例えば、5℃以上60℃以下とすることができる。図1では、配管1の斜線部分が総容量となる。すすぎ水を循環させる場合は、封止栓6は閉じておく。 The present invention will be described with reference to FIG. FIG. 1 is a schematic view showing an example of a circulation bath system that performs the method for cleaning pipes of the present invention. In FIG. 1, 1 is a pipe, 2 is a bathtub, 3 is a heat exchanger, 4 is a filter, 5 is a hair catcher, 6 is a sealing plug, and 7 is a separating device installed as needed (for example, Filters, centrifuges, etc.), and the arrows indicate the direction of travel of wash water or water for rinsing (hereinafter, also referred to as rinse water). In the system of FIG. 1, the pipe 1 and the bathtub 2 are connected to form a circulation path. A heat exchanger 3 connected to a pipe, a filter 4, and a hair catcher 5 as a dust collecting means are arranged in the circulation path. In the system of FIG. 1, a pump (not shown) is set to send out wash water and rinse water. In FIG. 1, the washing water is conveyed from the pipe 1 to the bathtub 2, further discharged from the bathtub 2 and conveyed to the pipe 1, and moves along the circulation path in the direction of the arrow to wash the pipe. The circulation time may be the contact time and can be selected from the above range. The pH and temperature of the cleaning solution can be selected from the above ranges. In the present invention, the pH of the circulating cleaning liquid is preferably 3 or more and 5 or less. After the cleaning liquid has been contacted for a predetermined time, the circulation is stopped, a pH adjuster is added as necessary to adjust the pH to more than 5 and 9 or less, and then the sealing stopper 6 is released to precipitate a solid. Minutes are discharged from the bathtub 2, for example, removed by filtration or the like with a separator 7 if necessary, and then discharged from this system. After the cleaning liquid is discharged, the amount of rinse water that is at least twice the total capacity of the pipe 1 is supplied to the circulation path to rinse the pipe 1, the bathtub 2, and the like. When the pipes form a circulation path as shown in FIG. 1, the supply of the rinse water is temporarily stopped when the amount corresponding to the total capacity of the pipe 1 is supplied from the point where the supply of the rinse water is started, and the rinse water is supplied. It may be circulated and rinsed for a predetermined time. This one-time circulation rinsing corresponds to rinsing with an amount of water that is once the total capacity of the pipe 1. After the circulation rinsing for a predetermined time is completed, the rinse water is discharged, and by performing an additional rinse at least once in the same manner, the pipe can be rinsed with more than twice the total capacity of the pipe 1. Will be done. As the rinse water, tap water or the like can be used. The temperature of the rinse water is not particularly limited, but can be, for example, 5 ° C. or higher and 60 ° C. or lower. In FIG. 1, the shaded portion of the pipe 1 is the total capacity. When the rinse water is circulated, the sealing stopper 6 is closed.

<実施例1>
(1)洗浄液
洗浄液として、
(a)過炭酸ナトリウム1000ppm
(b)アスコルビン酸 1000ppm
(c)酒石酸 1000ppm
を含有する洗浄液(残部は水、pH4.1)を用いた。
<Example 1>
(1) Cleaning liquid As a cleaning liquid
(A) Sodium percarbonate 1000ppm
(B) Ascorbic acid 1000ppm
(C) Tartaric acid 1000ppm
A cleaning solution containing water (the balance is water, pH 4.1) was used.

(2)バイオフィルム除去試験(配管モデル)
洗浄液又はコントロール(超純水)5mLを入れた6wellプレートにバイオフィルムが形成されたテストピースを浸し、40℃、60rpmで所定の時間振とうした(TAITEC製、BioShaker BR−43FL)。振とう時間を、表1では洗浄時間として示した。振とう後の洗浄液の中和には、炭酸ナトリウムを用い、pH7に調整した。なお、本発明のpHは、ガラス電極を用いたpHメーターによって測定した値である。
洗浄液を1mL残し、超純水を2mL添加後、60rpmで5分間振とうすることですすぎ1回とした。この1回のすすぎは、配管の総容量の1倍の量の水によるすすぎに相当する。この試験は、ここでの全体容量の3/5が配管の総容量、同全体容量の2/5が浴槽容量に相当し、1回の排水で全体容量の1/5の洗浄液又はすすぎ水が系中に残留するような実機設備を想定した配管モデルで実施したものである。
1回のすすぎが終了したごとにすすぎ水を捨てて、新たな超純水を用いて、表1に示す回数まですすぎを繰り返した。2回目以降のすすぎは、すすぎ水を1mLずつ残し、そこに新たな超純水2mLを添加して実施した。所定回数のすすぎを終えた後、各テストピースを0.1%クリスタルバイオレット溶液中に浸し、バイオフィルムを染色した後、過剰となるクリスタルバイオレットをすべて除去するために超純水で洗浄した後、1mLのエタノールでテストピースのバイオフィルムと結合して染色していたクリスタルバイオレット染料を抽出し、吸光度(OD570)を測定し、バイオフィルムの残存量を求めた。
測定したOD570をもとに、下記式に従ってバイオフィルム除去率を測定した。結果を表1に示した。
バイオフィルム除去率(%)={(コントロールOD570−ブランクOD570)−(実施例のOD570−ブランクOD570)}×100/(コントロールOD570−ブランクOD570)
尚、コントロールはバイオフィルムが形成されたテストピースの洗浄操作を行わずにクリスタルバイオレット処理を行ったものであり、ブランクはエタノールのOD570を指す。
(2) Biofilm removal test (piping model)
A test piece on which a biofilm was formed was immersed in a 6-well plate containing 5 mL of a cleaning solution or control (ultrapure water) and shaken at 40 ° C. and 60 rpm for a predetermined time (BioShaker BR-43FL manufactured by TAITEC). The shaking time is shown as the washing time in Table 1. Sodium carbonate was used to neutralize the washing liquid after shaking, and the pH was adjusted to 7. The pH of the present invention is a value measured by a pH meter using a glass electrode.
After leaving 1 mL of the cleaning solution and adding 2 mL of ultrapure water, it was rinsed once by shaking at 60 rpm for 5 minutes. This single rinse corresponds to rinsing with water in an amount of 1 times the total capacity of the pipe. In this test, 3/5 of the total capacity here corresponds to the total capacity of the piping, and 2/5 of the total capacity corresponds to the bathtub capacity. This was carried out using a piping model that assumes actual equipment that remains in the system.
After each rinse, the rinse water was discarded, and fresh ultrapure water was used to repeat the rinse up to the number shown in Table 1. The second and subsequent rinses were carried out by leaving 1 mL of rinse water and adding 2 mL of fresh ultrapure water to it. After a predetermined number of rinses, each test piece is immersed in a 0.1% crystal violet solution, stained with a biofilm, washed with ultrapure water to remove any excess crystal violet, and then washed with ultrapure water. The crystal violet dye that had been stained by binding to the biofilm of the test piece was extracted with 1 mL of ethanol, and the absorbance (OD570) was measured to determine the residual amount of the biofilm.
Based on the measured OD570, the biofilm removal rate was measured according to the following formula. The results are shown in Table 1.
Biofilm removal rate (%) = {(Control OD570-Blank OD570)-(Example OD570-Blank OD570)} x 100 / (Control OD570-Blank OD570)
The control is a crystal violet treatment without cleaning the test piece on which the biofilm is formed, and the blank refers to ethanol OD570.

Figure 2021188884
Figure 2021188884

<実施例2>
実施例1と同様に、ただし処理条件を表2の通りとして、バイオフィルム除去試験を行った。また、表2の洗浄液について、以下の方法で発泡抑制性を評価した。また、バイオフィルム除去試験で行った最後のすすぎのすすぎ水について、次亜塩素酸ナトリウムとの反応性(表では、「次亜塩素酸Naとの反応性」と表示した)を以下の方法で評価した。結果を表2に示した。
<Example 2>
The biofilm removal test was carried out in the same manner as in Example 1, except that the treatment conditions were as shown in Table 2. In addition, the foaming inhibitory properties of the cleaning liquids shown in Table 2 were evaluated by the following methods. In addition, the reactivity with sodium hypochlorite (indicated as "reactivity with Na hypochlorite" in the table) of the rinse water for the final rinse performed in the biofilm removal test was determined by the following method. evaluated. The results are shown in Table 2.

*発泡抑制性評価
50mL遠沈管に洗浄液を30mL加え、20往復激しく振とう後の泡体積を遠沈管の目盛りより算出した。
泡体積(mL)=(泡からなる層の最上部の目盛り)−(液状部分と泡状部分の境界部の目盛り)
* Evaluation of foaming inhibitory property 30 mL of cleaning solution was added to a 50 mL centrifuge tube, and the foam volume after vigorous shaking for 20 reciprocations was calculated from the scale of the centrifuge tube.
Foam volume (mL) = (scale at the top of the layer consisting of bubbles)-(scale at the boundary between the liquid part and the foam part)

*すすぎ水の次亜塩素酸ナトリウムとの反応性評価
最後のすすぎのすすぎ水1mLに、次亜塩素酸ナトリウム水溶液を2ppmとなるように加えた。全塩素濃度をDPD法で測定し、1.9ppm以上であれば次亜塩素酸ナトリウムと反応性がないと判断し、表2には○で示した。前記濃度が1.9ppm未満の場合は反応性があると判断し、表2には×で示した。すなわち、ジ亜塩素酸ナトリウムとの反応性がない場合(評価として〇と表した場合)とは、すすぎが良好に行われていることを示している。
* Evaluation of reactivity of rinse water with sodium hypochlorite To 1 mL of rinse water for the final rinse, an aqueous solution of sodium hypochlorite was added so as to be 2 ppm. The total chlorine concentration was measured by the DPD method, and if it was 1.9 ppm or more, it was judged that there was no reactivity with sodium hypochlorite, and it is indicated by ◯ in Table 2. When the concentration was less than 1.9 ppm, it was judged to be reactive, and is indicated by x in Table 2. That is, when there is no reactivity with sodium dichlorite (when it is expressed as 〇 as an evaluation), it indicates that rinsing is performed well.

Figure 2021188884
Figure 2021188884

<実施例3>
実施例2と同様に、ただし条件を表3の通りとして、バイオフィルム除去試験を行った。その際、洗浄後の中和の有無による汚れの析出の様子を目視観察した。なお、中和を行う場合は、振とう後の洗浄液に、炭酸ナトリウムを添加して、pH7になるように調整して行った。結果を表3に示した。
<Example 3>
A biofilm removal test was performed in the same manner as in Example 2, but with the conditions as shown in Table 3. At that time, the state of precipitation of stains due to the presence or absence of neutralization after cleaning was visually observed. In the case of neutralization, sodium carbonate was added to the washing liquid after shaking to adjust the pH to 7. The results are shown in Table 3.

Figure 2021188884
Figure 2021188884

<実施例4及び比較例4>
表4に示す組成の洗浄液を表4に示す条件で用いて、実施例1と同様にバイオフィルム除去試験を行った。また、表4の洗浄液について、実施例2と同様の方法で発泡抑制性を評価した。結果を表4に示した。
<Example 4 and Comparative Example 4>
A biofilm removal test was carried out in the same manner as in Example 1 using the cleaning solution having the composition shown in Table 4 under the conditions shown in Table 4. Moreover, about the cleaning liquid of Table 4, the foaming inhibitory property was evaluated by the same method as in Example 2. The results are shown in Table 4.

Figure 2021188884
Figure 2021188884

Claims (18)

配管内に付着した汚れに(a)過炭酸塩、(b)還元剤及び水を含有する洗浄液を所定時間接触させた後、前記配管の総容量の2倍以上の量の水で前記配管内をすすぐ、配管の洗浄方法。 After contacting the dirt adhering to the inside of the pipe with a cleaning liquid containing (a) a percarbonate, (b) a reducing agent and water for a predetermined time, the inside of the pipe is filled with water in an amount of at least twice the total capacity of the pipe. How to rinse and clean the pipes. 前記所定時間は10分以上である、請求項1に記載の配管の洗浄方法。 The method for cleaning pipes according to claim 1, wherein the predetermined time is 10 minutes or more. 配管が循環経路の少なくとも一部を形成する、請求項1又は2に記載の配管の洗浄方法。 The method for cleaning a pipe according to claim 1 or 2, wherein the pipe forms at least a part of a circulation path. 配管が循環経路の少なくとも一部を形成し、洗浄液を循環させて接触させた後、洗浄液を配管から排出してからすすぎを行う、請求項1〜3の何れか1項に記載の配管の洗浄方法。 The cleaning of the pipe according to any one of claims 1 to 3, wherein the pipe forms at least a part of the circulation path, the cleaning liquid is circulated and brought into contact with the pipe, and then the cleaning liquid is discharged from the pipe and then rinsed. Method. 循環経路は、配管と接続する浴槽を含む、請求項3又は4に記載の配管の洗浄方法。 The method for cleaning pipes according to claim 3 or 4, wherein the circulation route includes a bathtub connected to the pipes. すすぎを複数回行い、1回あたりのすすぎに用いる水の量が、配管の総容量の1倍以上である、請求項1〜5の何れか1項に記載の配管の洗浄方法。 The method for cleaning a pipe according to any one of claims 1 to 5, wherein the rinsing is performed a plurality of times and the amount of water used for each rinsing is 1 times or more the total capacity of the pipe. (a)成分が、過炭酸ナトリウムである、請求項1〜6の何れか1項に記載の配管の洗浄方法。 (A) The method for cleaning a pipe according to any one of claims 1 to 6, wherein the component is sodium percarbonate. 洗浄液中の(a)成分の濃度が100ppm以上3000ppm以下である、請求項1〜7の何れか1項に記載の配管の洗浄方法。 The method for cleaning a pipe according to any one of claims 1 to 7, wherein the concentration of the component (a) in the cleaning liquid is 100 ppm or more and 3000 ppm or less. (b)成分が、アスコルビン酸及びその塩、並びにビタミンCから選ばれる1種以上の化合物である、請求項1〜8の何れか1項に記載の配管の洗浄方法。 (B) The method for cleaning a pipe according to any one of claims 1 to 8, wherein the component is ascorbic acid and a salt thereof, and one or more compounds selected from vitamin C. 洗浄液中の(b)成分の濃度が100ppm以上3000ppm以下である、請求項1〜9の何れか1項に記載の配管の洗浄方法。 The method for cleaning a pipe according to any one of claims 1 to 9, wherein the concentration of the component (b) in the cleaning liquid is 100 ppm or more and 3000 ppm or less. 洗浄液が、更に(c)有機酸及びその塩から選ばれる1種以上の化合物〔以下(c)成分という〕を含有する、請求項1〜10の何れか1項に記載の配管の洗浄方法。 The method for cleaning a pipe according to any one of claims 1 to 10, wherein the cleaning liquid further contains (c) one or more compounds selected from an organic acid and a salt thereof [hereinafter referred to as (c) component]. (c)成分が、酒石酸、コハク酸、リンゴ酸及びこれらの塩から選ばれる1種以上の化合物である、請求項11に記載の配管の洗浄方法。 The method for cleaning a pipe according to claim 11, wherein the component (c) is one or more compounds selected from tartaric acid, succinic acid, malic acid and salts thereof. 洗浄液中の(c)成分の濃度が100ppm以上3000ppm以下である、請求項11又は12に記載の配管の洗浄方法。 The method for cleaning a pipe according to claim 11 or 12, wherein the concentration of the component (c) in the cleaning liquid is 100 ppm or more and 3000 ppm or less. 洗浄液のpHが3以上5以下である、請求項1〜13の何れか1項に記載の配管の洗浄方法。 The method for cleaning a pipe according to any one of claims 1 to 13, wherein the pH of the cleaning liquid is 3 or more and 5 or less. 洗浄後の洗浄液のpHを5超9以下に調整してから配管から排出する、請求項1〜14の何れか1項に記載の配管の洗浄方法。 The method for cleaning a pipe according to any one of claims 1 to 14, wherein the pH of the cleaning liquid after cleaning is adjusted to 5 or more and 9 or less, and then discharged from the pipe. 汚れがバイオフィルムを含む、請求項1〜15の何れか1項に記載の配管の洗浄方法。 The method for cleaning a pipe according to any one of claims 1 to 15, wherein the dirt contains a biofilm. (a)過炭酸塩及び(b)還元剤を含有し、請求項1〜16の何れか1項に記載の洗浄方法に用いられる、配管用洗浄剤組成物。 A cleaning agent composition for piping, which contains (a) a percarbonate and (b) a reducing agent, and is used in the cleaning method according to any one of claims 1 to 16. 更に(c)有機酸及びその塩から選ばれる1種以上の化合物を含有する、請求項17に記載の配管用洗浄剤組成物。 (C) The cleaning agent composition for piping according to claim 17, further comprising (c) one or more compounds selected from an organic acid and a salt thereof.
JP2020097867A 2020-06-04 2020-06-04 How to clean pipes Active JP7453065B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2020097867A JP7453065B2 (en) 2020-06-04 2020-06-04 How to clean pipes

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2020097867A JP7453065B2 (en) 2020-06-04 2020-06-04 How to clean pipes

Publications (2)

Publication Number Publication Date
JP2021188884A true JP2021188884A (en) 2021-12-13
JP7453065B2 JP7453065B2 (en) 2024-03-19

Family

ID=78849188

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2020097867A Active JP7453065B2 (en) 2020-06-04 2020-06-04 How to clean pipes

Country Status (1)

Country Link
JP (1) JP7453065B2 (en)

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61207500A (en) * 1985-03-08 1986-09-13 大阪瓦斯株式会社 Bath furnace detergent
JPH09118993A (en) * 1995-07-04 1997-05-06 Ebara Kogyo Senjo Kk Method and device for chemical cleaning of plant
JPH11262459A (en) * 1998-03-17 1999-09-28 Toto Ltd Bathroom washing device
JP2002003899A (en) * 2000-06-19 2002-01-09 Kansai Koso Kk Fume inhibitor for detergent and detergent composition
JP2003320325A (en) * 2002-04-30 2003-11-11 Kurita Engineering Co Ltd Sludge discharge method for petroleum refining apparatus
JP2007077202A (en) * 2005-09-12 2007-03-29 Shikoku Chem Corp Colored oxidizing agent composition
JP2008039368A (en) * 2006-08-10 2008-02-21 Nippon Soda Co Ltd Bath boiler cleaning method
JP2008075976A (en) * 2006-09-21 2008-04-03 Nippon Soda Co Ltd Bathtub water circulation pipe washing tool and bathtub water circulation pipe washing method

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61207500A (en) * 1985-03-08 1986-09-13 大阪瓦斯株式会社 Bath furnace detergent
JPH09118993A (en) * 1995-07-04 1997-05-06 Ebara Kogyo Senjo Kk Method and device for chemical cleaning of plant
JPH11262459A (en) * 1998-03-17 1999-09-28 Toto Ltd Bathroom washing device
JP2002003899A (en) * 2000-06-19 2002-01-09 Kansai Koso Kk Fume inhibitor for detergent and detergent composition
JP2003320325A (en) * 2002-04-30 2003-11-11 Kurita Engineering Co Ltd Sludge discharge method for petroleum refining apparatus
JP2007077202A (en) * 2005-09-12 2007-03-29 Shikoku Chem Corp Colored oxidizing agent composition
JP2008039368A (en) * 2006-08-10 2008-02-21 Nippon Soda Co Ltd Bath boiler cleaning method
JP2008075976A (en) * 2006-09-21 2008-04-03 Nippon Soda Co Ltd Bathtub water circulation pipe washing tool and bathtub water circulation pipe washing method

Also Published As

Publication number Publication date
JP7453065B2 (en) 2024-03-19

Similar Documents

Publication Publication Date Title
US12024451B2 (en) Methods and apparatus for controlling water hardness
EP2144986B1 (en) Water treatment system and downstream cleaning methods
US9896364B2 (en) Synergistic interaction of weak cation exchange resin and magnesium oxide
CA2475443C (en) Method for sterilisation and cleaning of water supply systems, in particular in swimming and bathing pool units and device for carrying out the same
CN106630011A (en) Combined cleaning method of water reuse reverse osmosis system for printing and dyeing wastewater
JP4498981B2 (en) Washing water recycling apparatus and method
JP3163041B2 (en) Cleaning towel and disinfection cleaning device for towel
JP2021188884A (en) Pipe cleaning method
JP2576033B2 (en) Endoscope cleaning method and apparatus
JP2006043695A (en) Cleaning method
JP2007319801A (en) Washing method of circulating water-purifying system, and circulating water-purifying system
JP2001254096A (en) Cleaning fluid and washing apparatus using the same
KR101182990B1 (en) Cleaning method
JP4653476B2 (en) Filter medium washing method and filtration system
JPH07133493A (en) Sustaining germicidal detergent
JP2007152077A (en) Washing method
JP2024006494A (en) Chlorine concentration control method, cleaning system for water treatment apparatus, program, and water circulation type water treatment apparatus
JP2576033C (en)
Vaughn Successful CIP Cleaning
JP2004154627A (en) Method for washing/sterilizing milking parlor and apparatus therefor
JP2022007825A (en) Automatic tableware cleaning method
JP2005130939A (en) Cleaning method of circulation type bathtub
JPH06254518A (en) Water-based precision cleaning system
KR20110081437A (en) Cleaning method of water treatment apparatus

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20230310

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20231122

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20231205

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20240125

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20240305

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20240307

R151 Written notification of patent or utility model registration

Ref document number: 7453065

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R151