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JPH0151520B2 - - Google Patents
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JPH0151520B2 - - Google Patents

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Publication number
JPH0151520B2
JPH0151520B2 JP55112677A JP11267780A JPH0151520B2 JP H0151520 B2 JPH0151520 B2 JP H0151520B2 JP 55112677 A JP55112677 A JP 55112677A JP 11267780 A JP11267780 A JP 11267780A JP H0151520 B2 JPH0151520 B2 JP H0151520B2
Authority
JP
Japan
Prior art keywords
caustic
hydrogen peroxide
caustic soda
weight
water
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.)
Expired
Application number
JP55112677A
Other languages
Japanese (ja)
Other versions
JPS5738900A (en
Inventor
Kunio Inoguchi
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.)
NITSUHON TEIIHOORU KK
Original Assignee
NITSUHON TEIIHOORU KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by NITSUHON TEIIHOORU KK filed Critical NITSUHON TEIIHOORU KK
Priority to JP11267780A priority Critical patent/JPS5738900A/en
Publication of JPS5738900A publication Critical patent/JPS5738900A/en
Publication of JPH0151520B2 publication Critical patent/JPH0151520B2/ja
Granted legal-status Critical Current

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  • Cleaning In General (AREA)
  • Detergent Compositions (AREA)

Description

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

この発明は、固脂状物質、厨芥類、スライム等
によつて閉塞もしくは流れが悪くなつた排水管、
或いは油溜め等の清掃剤組成物に関するものであ
る。 従来固脂、厨芥類、スライム等によつて閉塞も
しくは流れが悪くなつた排水管等の閉塞を解除す
る目的等に使用する清掃剤組成物としては酸性物
質としてスルフアミン酸を主体とするもの、アル
カリ性物質として珪酸ソーダ、苛性ソーダ、苛性
カリ等を主体とするもの、酸化剤として次亜塩素
酸ソーダを主体とするもの等が市販されており、
特に苛性ソーダ、苛性カリなど苛性アルカリ類を
主体とするものが広く使用されている。 これら苛性アルカリ類を主体とする清掃剤は、
苛性アルカリ類の水溶時の溶解熱で固脂等の油脂
分を溶融鹸化するとともに、厨芥、毛髪、スライ
ム等を軟化又は溶解することによつて閉塞を解消
するものであるが、これら苛性アルカリ類を主体
とするものにも欠点がある。 即ち苛性アルカリ類のうち苛性ソーダは冷水中
に投入しただけでは完全に溶解せず、撹拌するこ
とによつてはじめて完全に溶解させることができ
るが、このように完全に溶解しない場合には沈澱
した苛性ソーダが固結し、却つて排水管を固く閉
塞してしまう結果となる。 したがつて閉塞した排水管の冷水を湯水に置換
した後に苛性ソーダを投入しなければならないと
いう欠点がある。 更に大きな欠点としては、苛性ソーダが溶解し
ている部分のみが溶解熱のために高温になり、湯
水の温度及び苛性ソーダの添加量によつては突沸
する危険があり、また温度上昇によりプラスチツ
ク製排水管の変形、破損を招く危険がある。 一方苛性アルカリ類として苛性カリを使用する
場合には苛性カリは冷水中でも急速に溶解し、局
部的に温度が上昇する。 第1表は、500mlのメスシリンダーに水300mlを
採り、これにフレーク苛性カリを投入して投入30
秒後、2分後、10分後の温度をメスシリンダーの
底部と液面部とで測定した結果を示すものであ
る。
This invention deals with drain pipes that are clogged or have poor flow due to solid fat substances, kitchen waste, slime, etc.
Alternatively, the present invention relates to a composition for cleaning oil sumps and the like. Conventionally, cleaning compositions used for the purpose of unblocking drain pipes, etc. that are clogged or have poor flow due to solid fats, kitchen waste, slime, etc., include those containing mainly sulfamic acid as an acidic substance, and alkaline ones. There are commercially available products that mainly contain sodium silicate, caustic soda, and caustic potash as substances, and those that contain sodium hypochlorite as an oxidizing agent.
In particular, those based on caustic alkalis such as caustic soda and caustic potash are widely used. These cleaning agents mainly contain caustic alkalis,
The heat of dissolution when caustic alkalis is dissolved in water melts and saponifies fats and oils such as solid fats, and also dissolves blockages by softening or dissolving kitchen waste, hair, slime, etc. These caustic alkalis There are also drawbacks to those that are based on In other words, among caustic alkalis, caustic soda does not dissolve completely just by adding it to cold water, and can only be completely dissolved by stirring. However, if it does not dissolve completely in this way, the precipitated caustic soda will solidify, resulting in a solid blockage of the drain pipe. Therefore, there is a drawback that caustic soda must be added after the cold water in the blocked drain pipe has been replaced with hot water. An even bigger drawback is that only the part where the caustic soda is dissolved becomes hot due to the heat of dissolution, and depending on the temperature of the hot water and the amount of caustic soda added, there is a risk of bumping. There is a risk of deformation or damage. On the other hand, when caustic potash is used as the caustic alkali, it dissolves rapidly even in cold water, causing a local temperature rise. Table 1 shows that 300ml of water is taken into a 500ml graduated cylinder, and the flaked caustic potash is poured into it.
This figure shows the results of measuring the temperature at the bottom of the graduated cylinder and at the liquid level after 2 seconds, 2 minutes, and 10 minutes.

【表】 以上の結果より明らかなように苛性カリの添加
量によつては100℃以上に上昇するので、プラス
チツク製排水管は危険にさらされる。また多量に
添加した場合は冷水中でも突沸の危険性がある。 この発明は上記実情に鑑み苛性ソーダ、苛性カ
リ等の苛性アルカリ類が適当な速度で均質に溶解
するような排水管等の清掃剤組成物を提案するも
のである。 この発明の組成は基本的には固形苛性ソーダ、
苛性カリ等の固形苛性アルカリ類と固形であつて
水と接触することにより或いは更に加熱されるこ
とにより酸素を発生する過酸化水素付加物等の酸
素発生化合物を配合してなるものである。 即ち上記組成中固形苛性アルカリ類として苛性
ソーダを使用した場合には、苛性ソーダとともに
水中に投入された過酸化水素付加物は分解して酸
素を発生するが、苛性ソーダの溶解熱でこの分解
は促進される。 そこで多量の気泡が発生して上昇し、水溶液中
に激しい対流が起り、この結果苛性ソーダの表面
は絶えず低濃度の水溶液で洗われるので溶解が促
進されるし、温度も全体に拡散されるので局部的
に高温とならない。 また過酸化水素付加物の分解の際の発熱によつ
て苛性ソーダの溶解は一層促進されると同時に、
苛性ソーダの溶解熱で酸素発生化合物の分解も促
進される。即ち連鎖発熱によつて苛性ソーダ、過
酸化水素付加物の溶解が促進される。その結果、
突沸の危険性或いは苛性ソーダの固結の虞れが無
い状態で排水管等の清掃を行なうことができるの
である。 一方固形苛性アルカリとし苛性カリを使用した
場合について述べると、苛性カリ単独でも無撹拌
下で完全に溶解するので、苛性ソーダのように固
結する虞れがないが、突沸の危険性及びプラスチ
ツク排水管の損傷の危険性はある。しかし苛性カ
リと酸素発生化合物との組合せによる本発明によ
れば過酸化水素付加物から発生した酸素によつて
対流が生じ、これにより水溶液全体に熱が拡散す
るので、突沸の危険を回避することができ、同時
に苛性カリの溶解している部分の高温度化を防止
できる。これによりプラスチツク排水管の損傷を
回避することができる。 固形苛性アルカリ類として苛性ソーダと苛性カ
リとの併用した場合には次のような利点がある。 即ち、苛性ソーダの形状が大きい場合又は分厚
い場合、更には水の温度が低い場合は酸素発生化
合物が共存しても苛性ソーダの溶解が遅かつた
り、或いは完全溶解しない場合があるが、苛性カ
リを配合することによつて急速に完全溶解させる
ことができる。 過酸化水素付加物を配合することの第2の特徴
は、酸素発生によつて種々の汚れを壁面から剥離
し易くすることである。 即ち、排水管の内壁及び油溜め底、側壁に付着
している固脂状物質は、殆んどが脂肪からなつて
いるので温度上昇によつて溶融するが、中には溶
融しない固脂状物質がある。固脂状物質が溶融し
ないのは脂肪ばかりでなく蛋白質、澱粉質その他
の種々の物質からなるためと推定される。これに
対して本発明の組成物は排水管等に付着した固脂
状物質を容易に剥離することができる。これは固
脂状物質と排水管壁面の間隙に過酸化水素付加物
の分解により発生した酸素が介入して剥離を促進
するものと推定される。 使用する固形苛性アルカリは、フレーク状、タ
ブレツト状、小球状、顆粒状等種々あるが、その
うち何れを使用してもよい。 但し、一包装単位の総てを水中に投入する場合
は何等問題はないが、一包装単位を分割して使用
する場合は各成分の分級が大きな問題となる。即
ち分級すると本発明組成物の特徴を発揮できず各
成分個有の欠点、例えば苛性ソーダであれば固
結、苛性カリであれば突沸、局部的高温等の欠点
が顕われるためである。 特に過酸化水素付加物は粒状又は顆粒状、小粒
状の市販品が殆んどである現状ではフレーク状の
苛性アルカリを高率配合することは直ちに分級に
つながる。 粉状又は顆粒状過酸化水素付加物60%と、一例
としてタイラー篩4メツシユ(孔眼寸法4.699mm)
オン90%以上の大きさの市販のフレーク状苛性ア
ルカリを40%まで配合しても分級は発生しない
が、同じフレーク状苛性アルカリ50%と過酸化水
素付加物50%の配合では分級が目立つてくる。 タイラー篩4メツシユアンダー90%以上のフレ
ーク状苛性アルカリの粗砕品であれば、該フレー
ク状苛性アルカリ50%と過酸化水素付加物50%の
配合でも分級は目立たない。更にタイラー篩7メ
ツシユ(孔眼寸法2.794mm)アンダー90%以上の
小さなフレーク状苛性ソーダになれば、該苛性ソ
ーダ80%と過酸化水素付加物20%の配合でも分級
は目立たない。タイラー篩24メツシユ(孔眼寸法
0.71mm)アンダー90%以上の顆粒状苛性ソーダで
あれば、過酸化水素付加物との間には如何なる割
合でも分級は見られず、しかもこの混合物70%に
4メツシユオン90%以上のフレーク状苛性カリ30
%を配合しても分級は目立たない。 要は苛性アルカリの大きさが小さければ小さい
程、過酸化水素付加物との分級を避けながら苛性
アルカリの配合率を高めることができる。一般的
に酸素発生化合物の配合率が低い程、即ち苛性ア
ルカリの配合率が高い程、単位重量当りの発熱量
が大であるために経済的である。 苛性アルカリの配合率は20〜95重量%であり、
好ましくは50〜80重量%である。20重量%以下で
は発熱量が少ないので、特に苛性ソーダの溶解及
び過酸化水素付加物の溶解にも長時間を要し、実
用性に乏しい。一方95重量%以上では過酸化水素
付加物の配合率が低くなるので、ガス発生量が少
なく水溶液の対流が弱くなる。特に苛性ソーダで
は溶解を充分に促進することができず、また苛性
カリでは突沸し易い状態となり危険である。 本発明に使用する過酸化水素付加物としては過
炭酸ソーダ(2Na2CO3・3H2O2)、過硼酸ソーダ
(NaBO3 H2O2・3H2O)、過酸化硫酸ソーダ、過
酸化ピロリン酸ソーダのような重合りん酸塩過酸
化水素付加物、過酸化尿素等が主たるものであ
る。このうち特に過炭酸ソーダ、過硼酸ソーダは
廉価であり、取扱い易く、且つ安全性が高く貯蔵
容易である。 これらの酸素発生化合物は粉末、小結晶又は顆
粒状として市販されており、溶解し易さの点から
もこの種の形状が好ましい。これら過酸化水素付
加物の単独又は2種以上の併用の配合率は5〜80
重量%である。5重量%以下では水溶液の対流が
弱くなり、苛性ソーダの溶解を充分に促進するこ
とができず、未溶解苛性ソーダが残つて固結する
こともあり、苛性カリの場合は突沸を招く場合も
生ずる。80重量%以上では組成物の発熱量が少な
いので、特に苛性ソーダの溶解及び過酸化水素付
加物の溶解に長時間を要し、実用性に乏しい。し
たがつて好ましい配合率は20〜50重量%である。 なお過酸化水素付加物配合の効果としては上述
以外に、分解して発生した酸素の作用により排水
管内の殺菌が行われ、同時に臭い成分が分解され
て消臭効果があるなどを挙げることができる。ま
た上記組成物は使用直前に配合してもよいが、あ
らかじめ配合しておいても良い。後者の場合組成
中の過酸化水素付加物は製造工程中及び商品在庫
中の吸湿によつて分解し、実際に使用する場合に
は酸素の発生が少くなるか、皆無になつてしまう
こともある。 更に過酸化水素付加物では、分解によつて生成
する水のために分解の進行と共に組成物全体が次
第にケーキングを生成する。 この現象を防止するためには分解抑制剤の配合
が効果的であり、本発明は固形苛性アルカリ20〜
95重量%と、固形の過酸化水素付加物5〜80重量
%と、過酸化水素付加物に対する分解抑制剤0.2
〜10重量%を最初から配合して長期間の貯蔵中で
も安定に保存でき、且つ取扱い易い排水管、油溜
め等の清掃剤組成物を提供するものである。 分解抑制剤としては無水珪酸類、酸化マグネシ
ウム、リン酸マグネシウム、珪酸マグネシウム等
のマグネシウム化合物の1種又は2種以上で構成
する。 無水珪酸の作用は、商品在庫中において苛性ア
ルカリと過酸化水素付加物との直接接触が妨げら
れるためであると推定される。したがつて無水珪
酸の粒径は細かい方が単位重量当りの苛性アルカ
リ、過酸化水素付加物の表面被覆面積が大となる
ので好ましい。無水珪酸の配合率は0.2〜10重量
%が好ましく、0.2重量%以下では過酸化水素付
加物の分解を防ぐことができず、10重量%以上で
は絶対発熱量が少なくなるので好ましくない。 無水珪酸の種類については微粉末無定形無水珪
酸、乾燥力を有している合成無水珪酸、石英粉の
ような天然無水珪酸等が好ましい。 珪石粉は無水珪酸以外の鉱物例えばアルミニウ
ムを含む鉱物が微量混入しているため、合成無水
珪酸に比べて過酸化水素付加物の分解抑制力が多
少低下する。 因みにアルミニウム、カルシウム等を含むアル
ミノ珪酸ソーダ、合成ゼオライト、カオリン、酸
性白土等は分解抑制力がない。 なおマグネシウム化合物については十分な分解
抑制力を有する。 以上排水管の清掃効果について説明したが、本
発明の組成物は排水中に混じつて流れてくる油脂
類を、溜め池のように流れの緩い場所に導いて浮
上せしめ、溜めておく所謂油溜め(グリーストラ
ツプ)の清掃剤としても使用することができる。 即ち、グリーストラツプからの油脂類の流出は
グリーストラツプから先の排水管壁に油脂類が付
着して次第に排水を悪くして遂には閉塞させてし
まうことになるため厨房等におけるグリーストラ
ツプからの油の回収が重要な問題となつている。
しかしグリーストラツプの厨房等における位置は
流し台の下、或いは床下深い場所等にあることが
多く、油の回収は極めて困難な場合が多く、油ば
かりでなく同時に多量の水をもすくい出している
実情である。 従来苛性アルカリ類を主成分とする排水管清浄
がグリーストラツプの清掃にも使用されている。
しかしこの場合苛性アルカリ類によつて油脂類が
鹸化されても鹸化物は水中に分散したり、或いは
沈澱し、未鹸化油の多い所謂部分鹸化物のみが表
面に浮上して完全回収は困難である。 一方本発明の組成物をグリーストラツプ内に投
入すると、油脂類が鹸化物になると同時に、過酸
化水素付加物の分解によつて発生する気泡に随伴
して水中に分散している鹸化物、汚物、或いは底
や周壁から剥離された種々の汚れが浮上してく
る。しかも気泡は多くの有機物を吸着しているた
め極めて安定で破壊し難い泡である。そこで固状
鹸化物、未鹸化油脂、その他の汚物が上記のよう
に安定した固い泡によつて押し上げられる。した
がつて金網等ですくい出せば、安定な固い泡の上
の鹸化物、未鹸化油脂、その他の汚物はそのまま
すくい上げることができ、作業能率が極めて良好
となる。 なお本発明は排水管、油溜めの外にこれ等の類
似物の清掃に使用することができることは勿論で
ある。 以下、この発明の実施例を示す。 実施例 1 500mlメスシリンダーに300mlの水を入れ、これ
に表−2の各実験の配合物100gを投入し、液面
部と底部の温度を測定した。また投入10分後の未
溶解物の有無及び未溶解物があつた場合はその状
態を観察した。 この結果を表−2に示す。
[Table] As is clear from the above results, depending on the amount of caustic potash added, the temperature can rise to over 100℃, which puts plastic drain pipes at risk. Furthermore, if a large amount is added, there is a risk of bumping even in cold water. In view of the above circumstances, the present invention proposes a composition for cleaning drain pipes, etc., in which caustic alkalis such as caustic soda and caustic potash are dissolved homogeneously at an appropriate rate. The composition of this invention basically consists of solid caustic soda,
It is a mixture of a solid caustic alkali such as caustic potash and an oxygen generating compound such as a hydrogen peroxide adduct which is solid and generates oxygen when it comes into contact with water or is further heated. That is, when caustic soda is used as the solid caustic alkali in the above composition, the hydrogen peroxide adduct added to the water together with the caustic soda decomposes to generate oxygen, but this decomposition is accelerated by the heat of dissolution of the caustic soda. . There, a large number of bubbles are generated and rise, causing intense convection in the aqueous solution.As a result, the surface of the caustic soda is constantly washed with a low concentration aqueous solution, promoting dissolution, and the temperature is also diffused throughout, causing localized areas. does not reach high temperatures. In addition, the dissolution of caustic soda is further accelerated by the heat generated during the decomposition of the hydrogen peroxide adduct, and at the same time,
The heat of dissolution of caustic soda also accelerates the decomposition of oxygen-generating compounds. That is, the chain heat generation promotes the dissolution of the caustic soda and hydrogen peroxide adducts. the result,
Drain pipes, etc. can be cleaned without the risk of bumping or caking of caustic soda. On the other hand, when using caustic potash as a solid caustic alkali, since caustic potash alone dissolves completely without stirring, there is no risk of caking like with caustic soda, but there is a risk of bumping and damage to plastic drain pipes. There is a risk of However, according to the present invention, which uses a combination of caustic potash and an oxygen-generating compound, the oxygen generated from the hydrogen peroxide adduct causes convection, which diffuses heat throughout the aqueous solution, thereby avoiding the risk of bumping. At the same time, it is possible to prevent the temperature of the part where caustic potash is dissolved from becoming high. This avoids damage to the plastic drain pipe. When caustic soda and caustic potash are used together as solid caustic alkalis, there are the following advantages. In other words, if the caustic soda is large or thick, or if the water temperature is low, the dissolution of the caustic soda may be slow or may not completely dissolve even if an oxygen-generating compound is present, but caustic potash may be added. This allows rapid and complete dissolution. The second feature of blending the hydrogen peroxide adduct is that it makes it easier to remove various stains from the wall surface by generating oxygen. In other words, most of the solid and fat substances adhering to the inner wall of the drain pipe, the bottom of the oil sump, and the side walls are made up of fat and will melt as the temperature rises, but there are some solid and fat substances that do not melt. There is a substance. It is presumed that the reason why solid fat substances do not melt is that they are composed not only of fat but also of protein, starch, and various other substances. On the other hand, the composition of the present invention can easily peel off solid fat substances adhering to drain pipes and the like. It is presumed that this is because oxygen generated by the decomposition of the hydrogen peroxide adduct intervenes in the gap between the solid substance and the drain pipe wall surface, promoting peeling. There are various types of solid caustic alkali to be used, such as flakes, tablets, small spheres, and granules, and any of them may be used. However, there is no problem when the entire package is put into water, but when the package is divided and used, classification of each component becomes a big problem. That is, when classified, the characteristics of the composition of the present invention cannot be exhibited, and disadvantages inherent to each component, such as caking in the case of caustic soda and bumping and localized high temperatures in the case of caustic potash, appear. In particular, since most hydrogen peroxide adducts are commercially available in the form of granules, granules, or small particles, incorporating a high percentage of flaky caustic alkali immediately leads to classification. Powdered or granular hydrogen peroxide adduct 60% and, for example, 4 mesh Tyler sieves (hole size 4.699 mm)
Even if you mix up to 40% of commercially available flake caustic alkali with a size of 90% or more, no classification will occur, but if you mix 50% of the same flake caustic alkali and 50% hydrogen peroxide adduct, classification will be noticeable. come. If the flaky caustic alkali is coarsely crushed with a Tyler sieve 4 mesh under 90% or more, the classification will not be noticeable even if the flaky caustic alkali is 50% mixed with the hydrogen peroxide adduct at 50%. Furthermore, if the small flakes of caustic soda are 90% or more under the Tyler sieve 7 mesh (hole size 2.794 mm), the classification will not be noticeable even if the caustic soda is 80% and the hydrogen peroxide adduct is 20%. Tyler sieve 24 mesh (hole size)
0.71mm) If the powder is 90% or more of granular caustic soda, no classification will be observed between it and the hydrogen peroxide adduct at any ratio, and 70% of this mixture contains 4 meshes of flake caustic soda with 90% or more.
Classification is not noticeable even if % is mixed. In short, the smaller the size of the caustic alkali, the higher the blending ratio of the caustic alkali can be while avoiding classification with the hydrogen peroxide adduct. Generally, the lower the blending ratio of the oxygen-generating compound, that is, the higher the blending ratio of the caustic alkali, the greater the calorific value per unit weight, and therefore it is more economical. The compounding ratio of caustic alkali is 20 to 95% by weight,
Preferably it is 50 to 80% by weight. If it is less than 20% by weight, the calorific value is small, so it takes a long time to dissolve caustic soda and the hydrogen peroxide adduct, which is impractical. On the other hand, if it is 95% by weight or more, the blending ratio of the hydrogen peroxide adduct becomes low, so the amount of gas generated is small and the convection of the aqueous solution becomes weak. In particular, caustic soda cannot sufficiently promote dissolution, and caustic potash tends to cause bumping, which is dangerous. Hydrogen peroxide adducts used in the present invention include sodium percarbonate (2Na 2 CO 3・3H 2 O 2 ), sodium perborate (NaBO 3 H 2 O 2・3H 2 O), sodium peroxide sulfate, and peroxide. The main ones include hydrogen peroxide adducts of polymerized phosphates such as sodium pyrophosphate, and urea peroxide. Among these, sodium percarbonate and sodium perborate are particularly inexpensive, easy to handle, highly safe, and easy to store. These oxygen-generating compounds are commercially available in the form of powder, small crystals, or granules, and these types of shapes are preferred from the viewpoint of ease of dissolution. The blending ratio of these hydrogen peroxide adducts alone or in combination is 5 to 80
Weight%. If it is less than 5% by weight, the convection of the aqueous solution becomes weak and the dissolution of caustic soda cannot be sufficiently promoted, and undissolved caustic soda may remain and solidify, which may lead to bumping in the case of caustic potash. If the composition exceeds 80% by weight, the calorific value of the composition is low, so that it takes a long time to dissolve the caustic soda and the hydrogen peroxide adduct, making it impractical. Therefore, the preferred blending ratio is 20 to 50% by weight. In addition to the above-mentioned effects, the addition of hydrogen peroxide adducts also has the effect of sterilizing the inside of the drain pipe due to the action of oxygen generated by the decomposition, and at the same time decomposing odor components and having a deodorizing effect. . Further, the above composition may be blended immediately before use, or may be blended in advance. In the latter case, the hydrogen peroxide adduct in the composition will decompose due to moisture absorption during the manufacturing process and in product inventory, resulting in less or no oxygen generation during actual use. . Furthermore, in the case of hydrogen peroxide adducts, the entire composition gradually forms a caking as the decomposition progresses due to the water produced by the decomposition. In order to prevent this phenomenon, it is effective to incorporate a decomposition inhibitor, and the present invention is effective in preventing this phenomenon.
95% by weight, 5-80% by weight of solid hydrogen peroxide adduct, and 0.2% decomposition inhibitor for hydrogen peroxide adduct.
The present invention provides a cleaning agent composition for drain pipes, oil sump, etc., which is formulated from the beginning in an amount of ~10% by weight, can be stably stored even during long-term storage, and is easy to handle. The decomposition inhibitor is composed of one or more magnesium compounds such as silicic anhydride, magnesium oxide, magnesium phosphate, and magnesium silicate. The effect of silicic anhydride is presumed to be that direct contact between caustic alkali and hydrogen peroxide adduct is prevented during product inventory. Therefore, it is preferable that the particle size of the anhydrous silicic acid is smaller because the surface coverage area of the caustic alkali and hydrogen peroxide adduct per unit weight becomes larger. The blending ratio of silicic anhydride is preferably 0.2 to 10% by weight; if it is less than 0.2% by weight, decomposition of the hydrogen peroxide adduct cannot be prevented, and if it is more than 10% by weight, the absolute calorific value decreases, which is not preferred. Regarding the type of silicic anhydride, finely powdered amorphous silicic anhydride, synthetic silicic anhydride having drying power, natural silicic anhydride such as quartz powder, etc. are preferable. Since silica powder contains trace amounts of minerals other than silicic anhydride, such as minerals containing aluminum, its ability to suppress the decomposition of hydrogen peroxide adducts is somewhat lower than that of synthetic silicic anhydride. Incidentally, sodium aluminosilicate, synthetic zeolite, kaolin, acid clay, etc. containing aluminum, calcium, etc. do not have the ability to inhibit decomposition. Note that magnesium compounds have sufficient decomposition suppressing power. The cleaning effect of drain pipes has been explained above, but the composition of the present invention guides the oils and fats mixed with wastewater and flows to a place where the flow is slow, such as a reservoir, and floats them to a so-called oil reservoir where they are stored. It can also be used as a cleaning agent for (grease traps). In other words, when oils and fats leak from the grease trap, the oil and fats adhere to the wall of the drain pipe beyond the grease trap, gradually impairing the drainage and eventually causing a blockage. recovery has become an important issue.
However, grease traps are often located in kitchens, etc., under sinks or deep under the floor, making it extremely difficult to collect the oil. It is. Traditionally, drain cleaners based on caustic alkalis have also been used to clean grease traps.
However, in this case, even if oils and fats are saponified by caustic alkalis, the saponified products are dispersed in water or precipitated, and only so-called partially saponified products containing a large amount of unsaponified oil float to the surface, making complete recovery difficult. be. On the other hand, when the composition of the present invention is put into a grease trap, oils and fats become saponified products, and at the same time, saponified products and filth are dispersed in water accompanied by bubbles generated by decomposition of hydrogen peroxide adducts. , or various dirt peeled off from the bottom or peripheral wall come to the surface. Moreover, since the bubbles adsorb many organic substances, they are extremely stable and difficult to destroy. There, solid saponified substances, unsaponified fats and oils, and other impurities are pushed up by the stable hard foam as described above. Therefore, by scooping out with a wire mesh or the like, saponified substances, unsaponified fats and oils, and other impurities on stable, hard foam can be scooped up as they are, resulting in extremely high work efficiency. It goes without saying that the present invention can be used to clean drain pipes, oil sumps, and other similar objects. Examples of this invention will be shown below. Example 1 300 ml of water was placed in a 500 ml graduated cylinder, 100 g of each experimental formulation shown in Table 2 was added thereto, and the temperatures at the liquid surface and bottom were measured. In addition, the presence or absence of undissolved substances and the state of undissolved substances, if any, were observed 10 minutes after the addition. The results are shown in Table-2.

【表】 上記表−2から明らかなように実験No.1〜4
(比較例)では苛性ソーダ単独の場合は形状、大
きさに拘わらず30℃以下では未溶解物が固結し、
また40℃では不溶解が僅かに残り、固結するよう
なことはなかつたが、底部の温度が90℃以上に達
するので、プラスチツク製排水管は破損の危険を
生じた。 実験No.5〜7では過炭酸ソーダ配合率5%、苛
性ソーダ、苛性カリ配合率95%で実験を行なつ
た。この結果水温20℃では未溶解物が可成り残つ
たが(実験No.5)、水温40℃では未溶解物は残ら
ず(実験No.6)、苛性カリを使用した場合には軽
く突沸した(実験No.7)。したがつて上記配合率
が限界領域であることが認められた。 一方過炭酸ソーダ配合率80%、苛性ソーダ配合
率20%では水温が20℃のような低温の場合には温
度上昇は見られず過炭酸ソーダが未溶解状態で残
つた(実験No.11)。更に上記配合率及び水温では
溶解し易い苛性カリを使用した場合においても温
度上昇が見られず、過炭酸ソーダも可成り残ると
ころから過炭酸ソーダ配合率の上限は80%である
と認められた。 なお苛性カリ80%と過炭酸ソーダ20%の好まし
い配合範囲では未溶解物、突沸とも見られなかつ
た(実験No.9)。 しかし大きなフレーク状の苛性ソーダ50%と過
炭酸ソーダ50%を配合した場合には未溶解物が少
し残つた(実験No.10)。 これより大きなフレーク状苛性ソーダの混入は
好ましくない場合もあることが明らかとなつた。
なお小さなフレーク状苛性ソーダ25%と苛性カリ
70%を併用した場合は突沸することなく、未溶解
物も残らなかつた(実験No.8)。これより苛性ソ
ーダと苛性カリの併用が好ましい結果をもたらす
ことは明らかである。苛性ソーダと苛性カリの併
用が好ましいことは実験No.12〜16にも示されてお
り、特に実験No.15とNo.16は各成分の分級もなく、
総ての面で好ましい状態であると認められる。 実施例 2 タイラー篩24メツシユパス90%以上の顆粒状苛
性ソーダ70重量%、フレーク状苛性カリ10重量
%、顆粒状過炭酸ソーダ20重量%からなるベース
に、下記の各種物質を添加して厚さ0.1mmのポリ
エチレン袋に入れてヒートシールし、これにピン
ホール1ケあけて相対湿度70%、37℃の恒温恒湿
器に入れて30日間放置した。30日後に取出してケ
ーキングの状態を観察し、更に有効酸素を測定し
た。この結果を表−3に示す。
[Table] As is clear from Table-2 above, Experiments No. 1 to 4
(Comparative Example) When using caustic soda alone, undissolved matter solidifies at temperatures below 30°C regardless of its shape and size.
At 40°C, a small amount of undissolved material remained and no solidification occurred, but as the temperature at the bottom reached 90°C or higher, there was a risk of damage to the plastic drain pipe. In Experiment Nos. 5 to 7, experiments were conducted with a sodium percarbonate blending ratio of 5% and a caustic soda and caustic potash blending ratio of 95%. As a result, a considerable amount of undissolved matter remained at a water temperature of 20°C (Experiment No. 5), but no undissolved matter remained at a water temperature of 40°C (Experiment No. 6), and slight bumping occurred when caustic potash was used ( Experiment No. 7). Therefore, it was recognized that the above blending ratio was in the limit range. On the other hand, when the sodium percarbonate ratio was 80% and the caustic soda ratio was 20%, no temperature increase was observed when the water temperature was as low as 20°C, and the sodium percarbonate remained undissolved (Experiment No. 11). Furthermore, at the above blending ratio and water temperature, no temperature rise was observed even when caustic potash, which is easily soluble, was used, and a considerable amount of soda percarbonate remained, so it was recognized that the upper limit of the sodium percarbonate blending ratio was 80%. In addition, in the preferred blending range of 80% caustic potassium and 20% sodium percarbonate, neither undissolved matter nor bumping was observed (Experiment No. 9). However, when large flakes of 50% caustic soda and 50% sodium percarbonate were mixed, a small amount of undissolved matter remained (Experiment No. 10). It has become clear that the inclusion of larger flakes of caustic soda may be undesirable.
25% small flakes of caustic soda and caustic potash.
When 70% was used in combination, there was no bumping and no undissolved matter remained (Experiment No. 8). From this, it is clear that the combination of caustic soda and caustic potash brings about favorable results. Experiments No. 12 to 16 also show that the combination of caustic soda and caustic potash is preferable, and in particular, experiments No. 15 and No. 16 do not require classification of each component.
It is recognized that the situation is favorable in all aspects. Example 2 The following various substances were added to a base consisting of 70% by weight of granular caustic soda, 10% by weight of flaky caustic potassium, and 20% by weight of granular sodium percarbonate with a Tyler sieve 24 mesh pass of 90% or more, and a thickness of 0.1 mm was added. The material was placed in a polyethylene bag, heat-sealed, one pinhole was made in it, and the material was placed in a constant temperature and humidity chamber at 70% relative humidity and 37°C for 30 days. After 30 days, the cake was taken out, the state of caking was observed, and the amount of available oxygen was measured. The results are shown in Table-3.

【表】 上記した表−3において、実験番号26,27,28
は参考例である。 上記表−3より明らかなように、珪酸マグネシ
ウムとエアロジルは約0.2重量%の配合率で有効
であり、合成シリカゲルは1重量%で有効であつ
た。しかしアルミノ珪酸カルシウム、アルミノ珪
酸ソーダ、カオリン等には効果が見られなかつ
た。 実施例 3 1メスシリンダーに20℃の水1000mlを入れ、
これに下記実験No.32の組成物を所定量添加し、5
分後の温度を記録した。5分後の結果は表−4の
通りであつた。 実験No.32の組成 タイラー篩24メツシユアンダー 90%以上顆粒状苛性ソーダ 40重量% フレーク状苛性カリ 30重量% 過炭酸ソーダ 29.7重量% フアインシール 0.3重量%
[Table] In Table 3 above, experiment numbers 26, 27, 28
is a reference example. As is clear from Table 3 above, magnesium silicate and Aerosil were effective at a blending ratio of about 0.2% by weight, and synthetic silica gel was effective at a blending ratio of 1% by weight. However, no effect was observed with calcium aluminosilicate, sodium aluminosilicate, kaolin, etc. Example 3 1Pour 1000ml of water at 20℃ into a graduated cylinder,
A predetermined amount of the composition of Experiment No. 32 below was added to this, and 5
The temperature was recorded after minutes. The results after 5 minutes were as shown in Table 4. Composition of Experiment No. 32 Tyler sieve 24 mesh Under 90% or more Granular caustic soda 40% by weight Flaked caustic potash 30% by weight Soda percarbonate 29.7% by weight Fine Seal 0.3% by weight

【表】 表−4の結果は下記の関係式で表わされる直線
となる。 △t=0.135G ……(1) △t;水1000mlの上昇温度(℃) G;水1000mlに対するNo.32の投入量(g) 即ち、例えば1000mlの水を14℃上昇させたいと
きにはNo.32の組成物を100g投入すればよい。こ
のように上昇する温度の上限を計算によつて求め
ることができるので極めて安全である。 実施例 4 風呂の排水に極めて長時間かかるようになつた
ホテルの排水管(硬質塩化ビニル製、内径25mm、
垂直の長さ1.2m)を実施例3のNo.32で清掃作業
を行なつた。 排水管の曲り角部分に詰つているものと推定し
て水量を0.6と推定した。硬質塩化ビニル製管
は60℃までは絶対に完全であり、圧力をかけなけ
れば70℃でも安全であるので、上限温度を70℃と
した。水温は24℃であつたので、これらの数値を
上記(1)式に代入し、No.32の必要量を次のようにし
て求めた。 (70−24)=0.135×G G=341g 水0.6に対しては341g×0.6=205g、次に排水
管に水を一杯に張り、直ちにNo.32を200g投入し
た。投入5分後の温度は68℃であり、ほぼ予想通
りであつた。 投入12分後に激しい音をたてながら一気に水が
流れて排水管は開通した。 実施例 5 川崎市の某工場の厨房では、残菜をデイスポー
ザーで粉砕し、水と共に鉄パイプ排水管(長さ
27m直径100mm)で脱水装置まで流体輸送してい
る。 この排水管はよく詰り、その度毎にフランジを
外して清掃している。 排水管の出口から手を入れて調べたところ、管
壁にほゞ2cmの厚さで油脂、残菜などが付着して
いて固結化していた。従つて排水管の容積は60mm
φとして計算して76とした。 調製した湯の温度は43℃、上昇目標温度を80℃
として下記の計算から実施例No.3のNo.32の必要量
は22Kgとした。 (80−43)=0.13G G=284(g) 284g×76()=21.6(Kg)≒22Kg 排水管出口のコツクを閉じ、排水管入口から43
℃の湯と共にNo.32の組成物を徐々に投入し、管内
が充満した後更に10分間放置した。出口のコツク
を開くと同時に残菜及び剥離した固脂が多量に排
出されてきた。 実施例 6 100のグリーストラツプに、実施例No.3のNo.
32を2Kg投入して撹拌棒で軽くかきまわした。過
炭酸ソーダの分解によつて発生した泡と一緒に、
グリーストラツプの底に沈んでいたり或いは側壁
に付着していたりしている腐敗進行中の油脂類も
浮上してきた。この泡はグリーストラツプ中の有
機物が吸着しているため、極めて安定であり、油
脂類はこれらの泡に持ち上げられ、水面上に安定
な油脂膜が形成された。そのまま30分間放置した
後金網ですくいあげて観察してみた。油脂膜の殆
んどが石鹸のように固くなつており、しかもその
下には厚さ約1cmの固いスポンジ状の泡の層がで
きており、その固さは金網ですくいあげてもこわ
れない程度であつた。腐敗進行中の油脂類には遊
離脂肪酸が多く含有されているので容易に鹸化さ
れて石鹸になつたものと考えられる。グリースト
ラツプの水には多くの有機物が含まれているの
で、過炭酸ソーダの分解が激しく短時間に多量の
泡を発生して、生成したばかりの石鹸をも吸着し
て固い泡になるものと思われる。そこで石鹸をす
くい出し、極めて能率的にグリーストラツプの清
掃をおこなうことができた。
[Table] The result in Table 4 is a straight line expressed by the following relational expression. △t=0.135G...(1) △t; Temperature increase in 1000ml of water (℃) G; Amount of No. 32 added to 1000ml of water (g) In other words, for example, if you want to raise the temperature of 1000ml of water by 14℃, No. 100g of the composition No. 32 should be added. It is extremely safe because the upper limit of the temperature increase can be determined by calculation. Example 4 A hotel drain pipe (made of hard vinyl chloride, inner diameter 25 mm,
Cleaning work was carried out using No. 32 of Example 3 (vertical length 1.2 m). The amount of water was estimated to be 0.6, assuming that the blockage was in the corner of the drain pipe. Hard vinyl chloride pipes are absolutely perfect up to 60°C, and are safe even at 70°C if no pressure is applied, so we set the upper temperature limit to 70°C. Since the water temperature was 24°C, these values were substituted into the above equation (1), and the required amount of No. 32 was determined as follows. (70-24) = 0.135 x G G = 341g For 0.6 of water, 341g x 0.6 = 205g.Next, the drain pipe was filled with water and 200g of No. 32 was immediately added. The temperature 5 minutes after the addition was 68°C, which was almost as expected. Twelve minutes after the water was added, the water flowed out all at once, making a loud sound, and the drain pipe opened. Example 5 In the kitchen of a certain factory in Kawasaki City, leftover vegetables are crushed in a disposer and put together with water into an iron pipe drainage pipe (long
27m (diameter: 100mm) to transport fluid to the dehydration equipment. This drain pipe often gets clogged, and I have to remove the flange and clean it every time. When I inserted my hand into the outlet of the drain pipe and inspected it, I found that oil, fat, leftovers, etc. had adhered to the pipe wall to a thickness of about 2 cm and had solidified. Therefore, the volume of the drain pipe is 60mm.
It was calculated as φ and was set to 76. The temperature of the prepared hot water is 43℃, and the target temperature is 80℃.
Based on the calculation below, the required amount of No. 32 of Example No. 3 was determined to be 22 kg. (80−43) = 0.13G G = 284 (g) 284g x 76 () = 21.6 (Kg) ≒ 22Kg Close the drain pipe outlet and 43
Composition No. 32 was gradually added together with hot water at ℃, and after the inside of the tube was filled, it was left for another 10 minutes. As soon as the outlet was opened, a large amount of leftover food and peeled solid fat was discharged. Example No. 6 No. 1 of Example No. 3 was added to the 100 grease trap.
2 kg of 32 was added and stirred lightly with a stirring rod. Together with the bubbles generated by the decomposition of soda percarbonate,
The decomposing fats and oils that had sunk to the bottom of the grease trap or adhered to the side walls also came to the surface. These bubbles were extremely stable because the organic matter in the grease trap was adsorbed, and the oils and fats were lifted up by these bubbles, forming a stable oil and fat film on the water surface. After leaving it for 30 minutes, I scooped it up with a wire mesh and observed it. Most of the oil film is hard like soap, and underneath it is a layer of hard sponge-like foam about 1 cm thick, which is so hard that it won't break even if you scoop it up with a wire mesh. It was hot. Since the fats and oils in the process of decay contain a large amount of free fatty acids, it is thought that they are easily saponified and turned into soap. Grease trap water contains a lot of organic matter, so the soda percarbonate decomposes rapidly and generates a large amount of foam in a short period of time, which also absorbs the soap that has just been generated and becomes hard foam. Seem. I scooped out the soap and was able to clean the grease trap very efficiently.

Claims (1)

【特許請求の範囲】[Claims] 1 固形苛性アルカリ20〜95重量%と、固形の過
酸化水素付加物5〜80重量%と、無水珪酸、無機
マグネシウム化合物の一種又は二種以上からなる
上記過酸化水素付加物に対する分解抑制剤0.2〜
10重量%とを配合してなる排水管、油溜め等の清
掃剤組成物。
1 Decomposition inhibitor for the hydrogen peroxide adduct consisting of 20-95% by weight of solid caustic alkali, 5-80% by weight of solid hydrogen peroxide adduct, and one or more of silicic anhydride and inorganic magnesium compound 0.2 ~
A composition for cleaning drain pipes, oil sumps, etc., containing 10% by weight.
JP11267780A 1980-08-18 1980-08-18 Cleaner composition for drainpipe, oil sink or like Granted JPS5738900A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11267780A JPS5738900A (en) 1980-08-18 1980-08-18 Cleaner composition for drainpipe, oil sink or like

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11267780A JPS5738900A (en) 1980-08-18 1980-08-18 Cleaner composition for drainpipe, oil sink or like

Publications (2)

Publication Number Publication Date
JPS5738900A JPS5738900A (en) 1982-03-03
JPH0151520B2 true JPH0151520B2 (en) 1989-11-02

Family

ID=14592706

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11267780A Granted JPS5738900A (en) 1980-08-18 1980-08-18 Cleaner composition for drainpipe, oil sink or like

Country Status (1)

Country Link
JP (1) JPS5738900A (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60144400A (en) * 1983-12-30 1985-07-30 サンポール株式会社 Exothermic detergent composition
JPS60260699A (en) * 1984-06-07 1985-12-23 栗田工業株式会社 Detergent compostion
DE19858189A1 (en) * 1998-08-24 2000-06-21 Ophardt Product Gmbh & Co Kg Mixing tank
JP5330682B2 (en) * 2007-12-18 2013-10-30 宇部マテリアルズ株式会社 Slimming peeling remover and slime peeling removing method
JP5535518B2 (en) * 2008-05-01 2014-07-02 宇部マテリアルズ株式会社 Removal method of slime and aqueous slime remover preparation kit

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3968048A (en) * 1975-02-14 1976-07-06 The Drackett Company Drain cleaning compositions

Also Published As

Publication number Publication date
JPS5738900A (en) 1982-03-03

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