JPH10151466A - Waste water purifying method and washing waste water treatment apparatus - Google Patents

Waste water purifying method and washing waste water treatment apparatus

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Publication number
JPH10151466A
JPH10151466A JP31455396A JP31455396A JPH10151466A JP H10151466 A JPH10151466 A JP H10151466A JP 31455396 A JP31455396 A JP 31455396A JP 31455396 A JP31455396 A JP 31455396A JP H10151466 A JPH10151466 A JP H10151466A
Authority
JP
Japan
Prior art keywords
wastewater
anode
waste water
cathode
precipitate
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
JP31455396A
Other languages
Japanese (ja)
Inventor
Yasuhito Takahashi
康仁 高橋
Kunihito Mori
國人 森
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.)
Panasonic Holdings Corp
Original Assignee
Matsushita Electric Industrial 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 Matsushita Electric Industrial Co Ltd filed Critical Matsushita Electric Industrial Co Ltd
Priority to JP31455396A priority Critical patent/JPH10151466A/en
Publication of JPH10151466A publication Critical patent/JPH10151466A/en
Pending legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a washing waste water treatment method reduced in cost without using a filter when org. waste water such as washing waste water is treated with an electrochemical technique and an apparatus therefor. SOLUTION: Waste water 2 is introduced into an electrolytic treatment tank having an electrode 5 consisting of an anode 7 and a cathode 8 and a current is allowed to flow across the anode 7 and the cathode 8 to form a precipitate 9 of a substance constituting one of the anode 7 and the cathode 8 and an ionic substance in waste water 2 and the precipitate 9 is removed by a liquid cyclone 4 by utilizing the specific gravity difference between the waste water and the precipitate 9.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は家庭の洗濯排水、商
業クリーニング排水、織物類の洗濯排水、およびメッキ
液等の排水内のイオン性物質を取り除く方法及びその装
置に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for removing ionic substances from wastewater such as household wastewater, commercial cleaning wastewater, textile wastewater, and plating solution.

【0002】[0002]

【従来の技術】従来、有機スルホン酸を含む酸性メッキ
液、洗浄液またはそれらの廃液は、水酸化ナトリウム等
によって中和処理を施し、生じる錫または鉛の水酸化物
を分離し、コンクリート等で固めた後、埋め立てられて
いた。一方、有機スルホン酸のナトリウム塩を含む廃液
は、公害を発生しないことを確認した後に、一般排水と
して河川または海洋に廃棄されていた。
2. Description of the Related Art Conventionally, acidic plating solutions containing organic sulfonic acid, cleaning solutions or their waste liquids are subjected to a neutralization treatment with sodium hydroxide or the like, and the resulting tin or lead hydroxide is separated and solidified with concrete or the like. After that, it was landfilled. On the other hand, a waste liquid containing a sodium salt of an organic sulfonic acid has been discarded in a river or ocean as general wastewater after confirming that no pollution occurs.

【0003】また、特開平5ー23673号公報にも記
載されているように、洗浄排水、染色排水、洗米排水ま
たは洗車排水等の有機性排水を電気化学的手法により処
理する際には、陽極として不溶性陽極および溶性陽極を
使用して、不溶性陽極により有機成分の分解を行い、分
解成分を溶性陽極の溶解により生ずる微粒子とともにフ
ロック化することにより凝集あるいは沈降を促進して分
解生成物の分離を行い、フィルタによりろ過した後、放
流されていた。
As described in Japanese Patent Application Laid-Open No. Hei 5-23673, when an organic wastewater such as washing wastewater, dyeing wastewater, rice washing wastewater or car washing wastewater is treated by an electrochemical method, an anode is used. Insoluble anodes and soluble anodes are used as a component to decompose organic components with the insoluble anodes, and floculate the decomposed components together with fine particles produced by dissolving the soluble anodes to promote aggregation or sedimentation to separate decomposition products. It was discharged after filtration by a filter.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、上記し
た従来の技術には次のような問題がある。
However, the above-mentioned prior art has the following problems.

【0005】まず第1に、廃液の安全確認および廃棄に
は多額のコストがかかり非常に不経済である。第2に、
溶性陽極の溶解により生ずる微粒子とともにフロック化
して凝集あるいは沈降物をフィルタによりろ過する際、
多量に処理しようとすると、フィルタが目詰まりを起こ
すために、たびたびフィルタの交換あるいは掃除をしな
ければならず、処理が煩雑になる。
First, safety confirmation and disposal of waste liquids are very costly and costly. Second,
When flocculating together with the fine particles generated by dissolving the soluble anode and filtering the aggregates or sediment with a filter,
If a large amount of processing is to be performed, the filter must be replaced or cleaned frequently to cause clogging of the filter, which complicates the processing.

【0006】そこで、本発明は、上記の課題を解決すべ
く、フィルタ等を用いることなく、かつ、コストのかか
らない排水の処理方法及び洗濯排水処理装置を提供する
ことを目的とする。
Accordingly, an object of the present invention is to provide a wastewater treatment method and a washing wastewater treatment device which do not use a filter or the like and which does not require a cost, in order to solve the above-mentioned problems.

【0007】[0007]

【課題を解決するための手段】上記目的を達成するため
に本発明は、家庭洗濯排水、商業クリーニング排水、織
物類の洗濯排水、およびメッキ液等の排水内のイオン性
物質をフィルタ等を用いることなく、Alからなる陽極
および陰極が対向してなる電極を有する電解処理タンク
内にこれらの排水を入れ、陽極および陰極間に電流を流
し、陽極および/または陰極近傍において、電極から溶
出したAlイオンと排水内のイオン性物質で非溶解性の
沈殿物を形成し、沈殿物を含む排水を電解処理タンクの
外部に導き、ポンプを介して液体サイクロン内に導入し
て沈殿物を取り除いた後、再び電解処理タンク内に戻
し、循環を繰り返すことによって、排水中に含まれるイ
オン性物質を取り除く排水の浄化方法を提供する。
SUMMARY OF THE INVENTION In order to achieve the above object, the present invention uses a filter or the like to filter ionic substances in wastewater such as household laundry wastewater, commercial cleaning wastewater, textile laundry wastewater, and plating solution. Without draining these wastewaters into an electrolytic treatment tank having an electrode in which an anode and a cathode made of Al face each other, a current is passed between the anode and the cathode, and Al eluted from the electrodes near the anode and / or the cathode. After forming insoluble precipitates by the ions and the ionic substances in the wastewater, the wastewater containing the precipitates is led to the outside of the electrolytic treatment tank, and introduced into the liquid cyclone via a pump to remove the precipitates. The present invention provides a method for purifying wastewater by removing the ionic substance contained in the wastewater by returning the wastewater to the electrolytic treatment tank again and repeating the circulation.

【0008】[0008]

【発明の実施の形態】以下本発明に実施の形態における
排水方法について、図面を参照しながら説明することと
する。但し、本実施の形態では、本発明の排水処理方法
を洗濯排水に適用した場合について説明する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS A drainage method according to an embodiment of the present invention will be described below with reference to the drawings. However, in the present embodiment, a case where the wastewater treatment method of the present invention is applied to washing wastewater will be described.

【0009】図1は、本発明の排水の浄化方法を実施す
るための浄化装置の概要を示す概略図である。図1に示
した浄化装置の構成について説明すると、電解処理タン
ク1内には、例えば洗濯機からの洗濯排水2が入れられ
ており、この洗濯排水2はポンプ3を介して液体サイク
ロン4に入り、再び電解処理タンク1に戻り、繰り返し
循環するようになっている。
FIG. 1 is a schematic diagram showing an outline of a purification apparatus for carrying out the method for purifying wastewater of the present invention. To explain the configuration of the purification device shown in FIG. 1, for example, washing wastewater 2 from a washing machine is put in an electrolytic treatment tank 1, and the washing wastewater 2 enters a liquid cyclone 4 via a pump 3. Then, it returns to the electrolytic treatment tank 1 and circulates repeatedly.

【0010】また、電解処理タンク1の内部には、アル
ミニウム(以下Alと記す)からなる電極5が電解処理
タンク1と電気的に絶縁された状態で挿入され、電極間
に電流を流す手段としての電解電源6から直流が通電さ
れるようになっている。ここで電極5は、例えば、陽極
7および陰極8として縦50cm、横25cmの大きさ
のAlを使用し、陰極ー陽極ー陰極ー陽極ー陰極ー陽極
ー陰極といった具合に対向して配置されている。なお、
図1に示すように、陽極7が陰極8に挟まれるように配
置しているのは、陽極7の両面を有効に利用するためで
ある。
An electrode 5 made of aluminum (hereinafter, referred to as Al) is inserted into the electrolytic processing tank 1 in a state of being electrically insulated from the electrolytic processing tank 1, and serves as a means for flowing a current between the electrodes. Is supplied with a direct current from the electrolysis power supply 6 of FIG. Here, the electrode 5 uses, for example, Al having a size of 50 cm in length and 25 cm in width as the anode 7 and the cathode 8, and is arranged so as to face the cathode-anode-cathode-anode-cathode-anode-cathode. I have. In addition,
As shown in FIG. 1, the anode 7 is disposed so as to be sandwiched between the cathodes 8 in order to effectively use both surfaces of the anode 7.

【0011】次に以下では、上記の図1に示す浄化装置
を用いた排水の浄化方法について説明を行う。
Next, a method of purifying waste water using the purifying apparatus shown in FIG. 1 will be described below.

【0012】電極に通電することによって、投入した電
気量に応じて陽極7表面からAlイオンが溶出する。洗
濯排水2には、主に陰イオン性界面活性剤として直鎖ア
ルキルベンゼンスルホン酸ナトリウムが含まれる。これ
は、水溶液中では、直鎖アルキルベンゼンスルホン酸イ
オン(以下LASイオンと記す)とナトリウムイオンに
電離しており、電極5に電解電源6から直流を通電する
ことにより、LASイオンは陽極7にナトリウムイオン
は陰極8に引き寄せられる。陽極7表面からは上記した
ように、Alイオンが溶液中に溶出しており、LASイ
オンと結合して非溶解性の沈澱物9が形成される。この
ときの反応の様子を図2に示す。
By energizing the electrodes, Al ions elute from the surface of the anode 7 in accordance with the amount of electricity supplied. Washing wastewater 2 mainly contains sodium linear alkylbenzene sulfonate as an anionic surfactant. This is because, in an aqueous solution, linear alkylbenzene sulfonic acid ions (hereinafter, referred to as LAS ions) and sodium ions are ionized, and when a direct current is applied to the electrode 5 from the electrolytic power supply 6, the LAS ions are The ions are attracted to the cathode 8. As described above, Al ions are eluted into the solution from the surface of the anode 7 and combine with the LAS ions to form a non-soluble precipitate 9. The state of the reaction at this time is shown in FIG.

【0013】またこの時、陽極7には水酸(OH)基も
引き寄せられ、非溶解性のAl(OH)3も形成される
ことになるが、通常水酸基に比べてLASイオンの濃度
が非常に大きいため、反応のほとんどがLASイオンと
の結合の反応になる。
At this time, a hydroxyl (OH) group is also attracted to the anode 7 and insoluble Al (OH) 3 is formed. However, the concentration of LAS ions is much higher than that of the hydroxyl group. Most of the reaction is a reaction of bonding with LAS ions.

【0014】この後、図1に示す沈澱物9を含んだ水溶
液はポンプ3を介して液体サイクロン4に入れられる。
ここでいう液体サイクロンとは水等の液体を流入させて
旋回流を起こさせ、その液体中に含まれる異相分子遠心
力を作用させて液体から分離捕捉する装置のことを指し
ている。この液体サイクロン4において生じる旋回流に
より洗濯排水2と沈澱物9とが比重差により分離され、
比重の小さい洗濯排水2は液体サイクロン4の上部から
排出され、沈澱物9が下方から排出される。なお、ここ
では、液体サイクロン4により沈殿物の除去を行った
が、比重差を利用して沈殿物と排水とを分離することが
できる装置であればよい。
Thereafter, the aqueous solution containing the precipitate 9 shown in FIG. 1 is put into the hydrocyclone 4 via the pump 3.
The term "hydrocyclone" as used herein refers to a device that causes a liquid such as water to flow therein to generate a swirling flow, and applies a centrifugal force of a different-phase molecule contained in the liquid to separate and capture the liquid from the liquid. Due to the swirling flow generated in the hydrocyclone 4, the washing wastewater 2 and the precipitate 9 are separated by a specific gravity difference,
The washing wastewater 2 having a low specific gravity is discharged from the upper part of the liquid cyclone 4, and the precipitate 9 is discharged from the lower part. Here, the sediment is removed by the liquid cyclone 4, but any device capable of separating the sediment from the wastewater by utilizing the difference in specific gravity may be used.

【0015】従って、液体サイクロン4の上部に排出さ
れた洗濯排水2を再び電解処理タンク1に戻され、再び
電解処理されてイオン性物質が沈澱物9となって液体サ
イクロン4に供給される。そして、液体サイクロン4で
は、洗濯排水2と沈澱物9が分離されて、洗濯排水2は
液体サイクロン4の上部から排出されて再び電解処理タ
ンク1に戻される。
Therefore, the washing drainage 2 discharged to the upper part of the liquid cyclone 4 is returned to the electrolytic treatment tank 1 again, and is subjected to electrolytic treatment again, and the ionic substance is supplied to the liquid cyclone 4 as a precipitate 9. Then, in the liquid cyclone 4, the washing wastewater 2 and the precipitate 9 are separated, and the washing wastewater 2 is discharged from the upper part of the liquid cyclone 4 and returned to the electrolytic treatment tank 1 again.

【0016】上記の過程を繰り返すことにより、洗濯排
水2からイオン性物質が取り除かれる。尚、液体サイク
ロン4の下方には、沈澱物12が溜まり、また、衣類に
付いた砂埃、土なども液体サイクロン4で分離されて沈
澱物12と一緒に液体サイクロン4の下方に溜まる。従
って、処理が終了すれば沈殿物12を別途処分すればよ
く、イオン性物質が取り除かれるとバルブ10を開けて
排水処理すればよい。
By repeating the above process, the ionic substances are removed from the washing wastewater 2. The sediment 12 accumulates below the hydrocyclone 4, and dust and dirt attached to clothes are also separated by the hydrocyclone 4 and accumulate below the hydrocyclone 4 together with the sediment 12. Therefore, when the treatment is completed, the precipitate 12 may be separately disposed, and when the ionic substance is removed, the valve 10 may be opened to perform the drainage treatment.

【0017】なお、本発明は、洗濯排水についてのみ適
用できるものではなく、その他幅広く排水処理に用いる
ことができ、その具体例としては、商業クリーニング排
水、織物類の排水、メッキ液等の排水、および洗車排水
等が挙げられる。
The present invention can be applied not only to washing wastewater but also to a wide range of other wastewater treatments. Specific examples thereof include commercial cleaning wastewater, textile wastewater, plating liquid wastewater, and the like. And car wash drainage.

【0018】[0018]

【発明の効果】以上説明したように本発明によれば、洗
濯排水中に含まれるイオン性物質取り除くために陽極お
よび陰極からなる電極を有する電解処理タンク内に排水
を入れ、陽極および陰極間に電流を流し、陽極や陰極近
傍において陽極や陰極物質と排水内のイオン性物質で沈
殿物を形成し、排水とともに液体サイクロンへ供給し、
この液体サイクロン内で生じる旋回流によって、比重の
差を利用して比重の異なる沈殿物と排水を分離し、沈殿
物が取り除かれた排水は上方から排出して再び電解処理
タンクへ戻し、沈殿物は下方へ排出させることができる
ため、連続した分離作用を行わせることができ、フィル
タ等を用いる必要性がなくなり、目詰まりの心配もなく
効率良く排水の浄化を行うことができる。
As described above, according to the present invention, in order to remove ionic substances contained in washing wastewater, the wastewater is put into an electrolytic treatment tank having an electrode composed of an anode and a cathode, and the wastewater is placed between the anode and the cathode. When an electric current is passed, a precipitate is formed between the anode and cathode materials and the ionic substance in the wastewater in the vicinity of the anode and the cathode, and is supplied to the liquid cyclone with the wastewater,
Due to the swirling flow generated in this hydrocyclone, the sediment with different specific gravity and wastewater are separated by utilizing the difference in specific gravity, and the wastewater from which sediment is removed is discharged from above and returned to the electrolytic treatment tank again, and the sediment is removed. Can be discharged downward, so that a continuous separation action can be performed, so that there is no need to use a filter or the like, and it is possible to efficiently purify wastewater without fear of clogging.

【0019】従って、本発明は工業的価値のみならず地
球環境の保全に大きく貢献するものである。
Therefore, the present invention greatly contributes not only to industrial value but also to conservation of the global environment.

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

【図1】本発明の排水浄化装置の構成を示す概略図FIG. 1 is a schematic diagram showing a configuration of a wastewater purification device of the present invention.

【図2】電極近傍でのイオンの動きを示す図FIG. 2 is a diagram showing the movement of ions near an electrode.

【符号の説明】[Explanation of symbols]

1 電解処理タンク 2 洗濯排水 3 ポンプ 4 液体サイクロン 5 電極 6 電解電源 7 陽極 8 陰極 9 沈殿物 10 バルブ 11 排水 Reference Signs List 1 electrolytic treatment tank 2 washing drainage 3 pump 4 liquid cyclone 5 electrode 6 electrolytic power supply 7 anode 8 cathode 9 sediment 10 valve 11 drainage

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 陽極および陰極からなる電極を有する電
解処理タンク内に排水を入れる工程と、前記陽極と前記
陰極との間に電流を流し、少なくとも前記陽極または前
記陰極の一方を構成する物質と前記排水内のイオン性物
質との沈殿物を形成する工程と、前記排水と前記沈殿物
との比重差を利用して前記排水内の前記沈殿物を取り除
く工程とを有する排水の浄化方法。
1. A step of draining an electrolytic treatment tank having an electrode comprising an anode and a cathode, and supplying a current between the anode and the cathode to form at least one of the anode and the cathode. A method for purifying wastewater, comprising: a step of forming a precipitate with an ionic substance in the wastewater; and a step of removing the precipitate in the wastewater by using a specific gravity difference between the wastewater and the precipitate.
【請求項2】 Alからなる陽極および陰極が対向して
なる電極を有する電解処理タンク内に排水を入れる工程
と、前記陽極と前記陰極との間に電流を流し、前記電極
から溶出したAlイオンと前記排水内のイオン性物質で
非溶解性の沈殿物を形成する工程と、前記沈殿物を含む
排水を前記電解処理タンクの外部に導き、ポンプを介し
て液体サイクロン内に導入して前記沈殿物を取り除いた
後、再び前記電解処理タンク内に戻し、循環を繰り返す
ことによって、前記排水中に含まれるイオン性物質を取
り除く工程とを有する排水の浄化方法。
2. A step of draining water into an electrolytic treatment tank having an electrode in which an anode and a cathode made of Al are opposed to each other, and flowing an electric current between the anode and the cathode to cause Al ions eluted from the electrode. Forming a non-soluble precipitate with the ionic substance in the wastewater, guiding the wastewater containing the precipitate to the outside of the electrolytic treatment tank, and introducing the precipitate into a liquid cyclone via a pump. Removing the matter, returning the wastewater to the electrolytic treatment tank again, and repeating the circulation to remove ionic substances contained in the wastewater.
【請求項3】 陽極および陰極が対向してなる電極と、
内部に洗濯後の排水を入れる電解処理タンクと、前記陽
極および陰極間に電流を流す手段と、前記電極から溶出
したイオンと前記排水内に含有されているイオン性物質
で形成された非溶解性の沈殿物を比重差を利用して除去
する手段とを有する洗濯排水処理装置。
3. An electrode having an anode and a cathode facing each other,
An electrolytic treatment tank for putting waste water after washing therein, a means for flowing an electric current between the anode and the cathode, and an insoluble material formed by ions eluted from the electrode and ionic substances contained in the waste water. And a means for removing the sediment of the waste water by utilizing a difference in specific gravity.
JP31455396A 1996-11-26 1996-11-26 Waste water purifying method and washing waste water treatment apparatus Pending JPH10151466A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP31455396A JPH10151466A (en) 1996-11-26 1996-11-26 Waste water purifying method and washing waste water treatment apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP31455396A JPH10151466A (en) 1996-11-26 1996-11-26 Waste water purifying method and washing waste water treatment apparatus

Publications (1)

Publication Number Publication Date
JPH10151466A true JPH10151466A (en) 1998-06-09

Family

ID=18054678

Family Applications (1)

Application Number Title Priority Date Filing Date
JP31455396A Pending JPH10151466A (en) 1996-11-26 1996-11-26 Waste water purifying method and washing waste water treatment apparatus

Country Status (1)

Country Link
JP (1) JPH10151466A (en)

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KR100500370B1 (en) * 2003-03-04 2005-07-14 이재복 The electrolytic sludge conditioning system and method
KR100930466B1 (en) 2007-12-21 2009-12-08 주식회사 포스코 Iron removal system generated in electrolytic clean line and iron removal method accordingly
KR101054351B1 (en) * 2008-09-03 2011-08-04 주식회사 씨플러스 Wastewater Treatment System
KR101060008B1 (en) * 2008-12-01 2011-08-29 삼성중공업 주식회사 Ballast water supply system and the vessel on which it is installed
WO2012088867A1 (en) * 2010-12-30 2012-07-05 波鹰(厦门)科技有限公司 Nano catalytic electrolysis and flocculation apparatus
US8603344B2 (en) 2005-10-31 2013-12-10 Sumitomo Osaka Cement Co., Ltd. Method and apparatus for removing metal from waste water
RU2800672C1 (en) * 2022-10-12 2023-07-25 Федеральное государственное бюджетное образовательное учреждение высшего образования "Российский государственный геологоразведочный университет имени Серго Орджоникидзе" Method for purification of oily wastewater in convective flows

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100341208B1 (en) * 2002-01-04 2002-06-22 장영호 Apparatus and method for removing pollutants in outflow water of abandoned mine by surface electrochemical reaction
KR100500370B1 (en) * 2003-03-04 2005-07-14 이재복 The electrolytic sludge conditioning system and method
US8603344B2 (en) 2005-10-31 2013-12-10 Sumitomo Osaka Cement Co., Ltd. Method and apparatus for removing metal from waste water
KR100930466B1 (en) 2007-12-21 2009-12-08 주식회사 포스코 Iron removal system generated in electrolytic clean line and iron removal method accordingly
KR101054351B1 (en) * 2008-09-03 2011-08-04 주식회사 씨플러스 Wastewater Treatment System
KR101060008B1 (en) * 2008-12-01 2011-08-29 삼성중공업 주식회사 Ballast water supply system and the vessel on which it is installed
WO2012088867A1 (en) * 2010-12-30 2012-07-05 波鹰(厦门)科技有限公司 Nano catalytic electrolysis and flocculation apparatus
RU2800672C1 (en) * 2022-10-12 2023-07-25 Федеральное государственное бюджетное образовательное учреждение высшего образования "Российский государственный геологоразведочный университет имени Серго Орджоникидзе" Method for purification of oily wastewater in convective flows

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