JP2011206637A - Method and apparatus for treatment of waste liquid containing acid or base and hydrogen peroxide - Google Patents

Method and apparatus for treatment of waste liquid containing acid or base and hydrogen peroxide Download PDF

Info

Publication number
JP2011206637A
JP2011206637A JP2010074592A JP2010074592A JP2011206637A JP 2011206637 A JP2011206637 A JP 2011206637A JP 2010074592 A JP2010074592 A JP 2010074592A JP 2010074592 A JP2010074592 A JP 2010074592A JP 2011206637 A JP2011206637 A JP 2011206637A
Authority
JP
Japan
Prior art keywords
waste liquid
hydrogen peroxide
irradiation
concentration
accelerator
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
JP2010074592A
Other languages
Japanese (ja)
Other versions
JP5581090B2 (en
Inventor
Etsuji Tachiki
悦二 立木
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 Corp
Original Assignee
Panasonic 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 Panasonic Corp filed Critical Panasonic Corp
Priority to JP2010074592A priority Critical patent/JP5581090B2/en
Publication of JP2011206637A publication Critical patent/JP2011206637A/en
Application granted granted Critical
Publication of JP5581090B2 publication Critical patent/JP5581090B2/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Photosensitive Polymer And Photoresist Processing (AREA)
  • Physical Water Treatments (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a treatment method for waste liquid which removes hydrogen peroxide contained in waste liquid containing acids or bases and hydrogen peroxide without distillation or neutralization treatment.SOLUTION: The treatment method includes: an irradiation process where ultraviolet rays are irradiated to the waste liquid to decompose the hydrogen peroxide contained therein; a measurement process where the hydrogen peroxide concentration of the waste liquid having been subjected to the irradiation process is measured; and a control process where the hydrogen peroxide concentration measured in the measurement process is compared with a reference value of the hydrogen peroxide concentration and when the measured concentration exceeds the reference value, at least one step selected from the following (a), (b) and (c) is performed: (a) starting to return the waste liquid having been subjected to the irradiation process and mix the returned waste liquid with the waste liquid before the irradiation process, or increasing the returning amount and mixing amount; (b) changing an ultraviolet irradiation condition to the waste liquid in the irradiation process to one where the decomposition of the hydrogen peroxide is accelerated; and (c) starting to add an accelerator for accelerating the decomposition of the hydrogen peroxide by the ultraviolet rays to the waste liquid before the irradiation process, or increasing the amount of added accelerator.

Description

本発明は、酸または塩基と過酸化水素とを含む廃液の処理方法および処理装置に関する。   The present invention relates to a treatment method and a treatment apparatus for waste liquid containing an acid or base and hydrogen peroxide.

半導体素子の製造工程から、酸または塩基と過酸化水素とを含む廃液が排出される。代表的な当該廃液は、硫酸、塩酸、フッ酸またはアンモニアに過酸化水素を加えた硫酸過水(SPM)、塩酸過水(HPM)、フッ酸過水(FPM)またはアンモニア過水(APM)を含む廃液である。酸または塩基と過酸化水素とを含む廃液は、一般に、当該酸または塩基の中和処理を経た後、触媒、酵素剤、還元剤などを用いた過酸化水素の分解処理を経て放流される。   A waste liquid containing an acid or base and hydrogen peroxide is discharged from the manufacturing process of the semiconductor element. Typical examples of the waste liquid include sulfuric acid / hydrochloric acid / hydrofluoric acid / ammonia hydrogen peroxide-added hydrogen peroxide (SPM), hydrochloric acid / hydrogen peroxide (HPM), hydrofluoric acid / hydrogen peroxide (FPM), or ammonia / hydrogen peroxide (APM). It is a waste liquid containing. A waste liquid containing an acid or base and hydrogen peroxide is generally discharged through a decomposition treatment of hydrogen peroxide using a catalyst, an enzyme agent, a reducing agent, etc. after neutralizing the acid or base.

廃液に含まれる酸および塩基は、再利用が望まれる。しかし、過酸化水素が廃液に含まれる場合、これを除去する必要があるため、その前に酸または塩基の中和処理が必須となる。中和処理を経た廃液から、酸および塩基の再利用はできない。このため、中和処理を実施することなく、廃液に含まれる過酸化水素を除去する方法の実現が望まれる。   It is desirable to reuse the acid and base contained in the waste liquid. However, when hydrogen peroxide is contained in the waste liquid, it is necessary to remove it, so that an acid or base neutralization treatment is essential before that. Acid and base cannot be reused from waste liquid that has undergone neutralization. For this reason, realization of the method of removing hydrogen peroxide contained in a waste liquid is desired, without performing neutralization processing.

硫酸を含むSPMは、半導体素子の製造工程において150℃程度の高温で使用されることもあって、これまで、多量の水で希釈された状態で製造装置から排出されている。近年、製造装置が改良され、多量の水で希釈されることなく、すなわち有効酸濃度が高い状態で、装置から排出されるようになってきている。有効酸(塩基)濃度が高い廃液から、有効酸(塩基)濃度が高いまま酸(塩基)を再利用することは、半導体素子の製造コストの観点からも、環境保全の観点からも、非常に待ち望まれる技術である。   SPM containing sulfuric acid is used at a high temperature of about 150 ° C. in the manufacturing process of semiconductor elements, and has been discharged from the manufacturing apparatus in a state diluted with a large amount of water. In recent years, the production apparatus has been improved and discharged from the apparatus without being diluted with a large amount of water, that is, in a state where the effective acid concentration is high. Recycling acid (base) from waste liquid with high effective acid (base) concentration while maintaining high effective acid (base) concentration is very important both from the viewpoint of semiconductor device manufacturing cost and environmental protection. This is a long-awaited technology.

特許文献1(特開平6-127908号公報)には、レジスト剥離装置から排出された、レジスト系有機物および過酸化水素を含む廃硫酸を硫酸に再生する硫酸再生装置が開示されている。特許文献1は、再生後の硫酸への有機物の混入を防ぐために、廃硫酸に含まれる有機物を除去することを課題としており、当該装置は、酸化剤および/または紫外線を用いて有機物を分解除去する有機物分解装置を備える。特許文献1には、当該再生装置において、過酸化水素などの酸化剤を廃硫酸に積極的に添加することによって、有機物を分解することが記載されている。   Patent Document 1 (Japanese Patent Laid-Open No. 6-127908) discloses a sulfuric acid regenerating apparatus that regenerates waste sulfuric acid containing a resist organic material and hydrogen peroxide discharged from a resist stripping apparatus into sulfuric acid. Patent document 1 makes it a subject to remove the organic substance contained in a waste sulfuric acid in order to prevent mixing of the organic substance in the sulfuric acid after reproduction | regeneration, The said apparatus decomposes and removes an organic substance using an oxidizing agent and / or an ultraviolet-ray. An organic matter decomposition device is provided. Patent Document 1 describes that in the regenerator, an organic substance is decomposed by positively adding an oxidizing agent such as hydrogen peroxide to waste sulfuric acid.

特許文献1の再生装置において、廃硫酸に最初から含まれる過酸化水素ならびに有機物分解装置において添加された過酸化水素は、再生後の硫酸への混入を防ぐために、硫酸の沸点以下での蒸留(第1の蒸留塔)により除去される。第1の蒸留塔を経た硫酸は、より高温での蒸留(第2の蒸留塔)により純度が高められ、硫酸供給管を通してレジスト剥離装置に再供給される。すなわち、特許文献1の装置は第1および第2の二つの蒸留塔を備えるが、これは、有機物分解のために過酸化水素を積極的に添加することを前提としているためと、レジスト剥離装置および硫酸再生装置を含む硫酸の再生循環路を構築することにより、レジスト剥離工程に再生硫酸を連続的に供給するためと考えられる。特許文献1の装置は、特定の工程に再生硫酸を連続的に供給する目的のためには非常に優れた性能を発揮する。しかし、一方で、廃液中の酸および塩基の再生および再利用を、バッチで、あるいは再生循環路を構築することなく別の装置または場所において行う場合には、少なくとも二つの蒸留塔を備える当該装置の製造コストおよび運転コストが不必要に大きいことから、特許文献1の装置は不適である。そもそも、酸または塩基の沸点が過酸化水素の沸点よりも十分に大きくなければ、特許文献1の装置により、酸または塩基と過酸化水素とを含む廃液から過酸化水素を除去した後に、当該酸または塩基を再利用できない。   In the regenerator of Patent Document 1, hydrogen peroxide initially contained in the waste sulfuric acid and hydrogen peroxide added in the organic matter decomposing apparatus are distilled below the boiling point of sulfuric acid in order to prevent mixing into the sulfuric acid after regeneration ( The first distillation column). The purity of the sulfuric acid that has passed through the first distillation column is increased by distillation at a higher temperature (second distillation column), and is re-supplied to the resist stripping device through the sulfuric acid supply pipe. That is, the apparatus of Patent Document 1 includes first and second distillation columns, which are based on the premise that hydrogen peroxide is positively added to decompose organic matter, and a resist stripping apparatus. It is considered that the regenerated sulfuric acid is continuously supplied to the resist stripping step by constructing a sulfuric acid recycle circuit including a sulfuric acid regenerator. The apparatus of Patent Document 1 exhibits extremely excellent performance for the purpose of continuously supplying regenerated sulfuric acid to a specific process. However, on the other hand, if the regeneration and reuse of acids and bases in the waste liquid is carried out in batch or in another device or place without building a regeneration circuit, the device comprising at least two distillation columns Since the manufacturing cost and the operating cost are unnecessarily large, the device of Patent Document 1 is not suitable. In the first place, if the boiling point of the acid or base is not sufficiently larger than the boiling point of hydrogen peroxide, after removing the hydrogen peroxide from the waste liquid containing the acid or base and hydrogen peroxide by the apparatus of Patent Document 1, Or the base cannot be reused.

特開平6-127908号公報JP-A-6-127908

このような事情を考慮し、本発明は、酸または塩基と過酸化水素とを含む廃液の処理方法および処理装置であって、過酸化水素の沸点に対する当該酸または塩基の沸点の関係によらないとともに、当該酸または塩基の中和処理を実施することなく、廃液に含まれる過酸化水素を分解、除去する処理方法および処理装置の提供を目的とする。   In view of such circumstances, the present invention is a method and apparatus for treating a waste liquid containing an acid or base and hydrogen peroxide, and does not depend on the relationship of the boiling point of the acid or base to the boiling point of hydrogen peroxide. Another object is to provide a treatment method and a treatment apparatus for decomposing and removing hydrogen peroxide contained in the waste liquid without performing the neutralization treatment of the acid or base.

本発明の処理方法は、酸または塩基と過酸化水素とを含む廃液の処理方法であって、酸または塩基と過酸化水素とを含む廃液に紫外線を照射して、前記廃液に含まれる過酸化水素を分解する照射工程と、前記照射工程を経た前記廃液における過酸化水素の濃度を測定する測定工程と、前記測定工程において測定された前記過酸化水素の濃度と、当該濃度の基準値とを対比して、前記測定された濃度が前記基準値を超える場合に、以下の(a)、(b)および(c)から選ばれる少なくとも一つを実施する、制御工程とを含む。(a)前記照射工程を経た前記廃液の少なくとも一部の環流と、前記照射工程が実施される前の前記廃液に対する、環流させた前記廃液の混合とを開始する、または前記環流および混合が既に行われているときに、前記照射工程を経た前記廃液の当該環流および混合の量を増加させる。(b)前記照射工程における前記廃液への紫外線の照射条件を、当該廃液に含まれる過酸化水素の分解が促進される方向に変化させる。(c)前記照射工程が実施される前の前記廃液に対して、紫外線の照射による過酸化水素の分解を促進する促進剤の添加を開始する、または前記添加が既に行われているときに、前記照射工程が実施される前の前記廃液に対する前記促進剤の添加の量を増加させる。   The treatment method of the present invention is a treatment method of a waste liquid containing an acid or base and hydrogen peroxide, wherein the waste liquid containing an acid or base and hydrogen peroxide is irradiated with ultraviolet rays, and the peroxidation contained in the waste liquid. An irradiation step for decomposing hydrogen, a measurement step for measuring the concentration of hydrogen peroxide in the waste liquid that has undergone the irradiation step, a concentration of the hydrogen peroxide measured in the measurement step, and a reference value for the concentration In contrast, when the measured concentration exceeds the reference value, a control step is performed in which at least one selected from the following (a), (b) and (c) is performed. (A) Start at least part of the reflux of the waste liquid that has undergone the irradiation step and mixing of the waste liquid that has been refluxed with respect to the waste liquid before the irradiation step is performed, or the reflux and mixing are already When being performed, the amount of the reflux and mixing of the waste liquid that has undergone the irradiation step is increased. (B) The irradiation condition of the ultraviolet light to the waste liquid in the irradiation step is changed in a direction in which the decomposition of hydrogen peroxide contained in the waste liquid is promoted. (C) To start the addition of an accelerator that promotes the decomposition of hydrogen peroxide by ultraviolet irradiation with respect to the waste liquid before the irradiation step is performed, or when the addition has already been performed, The amount of the accelerator added to the waste liquid before the irradiation step is performed is increased.

本発明の処理装置は、酸または塩基と過酸化水素とを含む廃液の処理装置であって、酸または塩基と過酸化水素とを含む廃液に紫外線を照射する紫外線照射機構と、前記紫外線を照射した後の前記廃液における過酸化水素の濃度を測定する測定機構と、以下の(A)、(B)および(C)から選ばれる少なくとも一つとを備える。(A)前記紫外線を照射した後の前記廃液の少なくとも一部を環流させて、前記紫外線が照射される前の前記廃液に混合する環流機構、ならびに前記測定機構において測定された前記過酸化水素の濃度と、当該濃度の基準値とを対比して、前記測定された濃度が前記基準値を超える場合に、前記環流機構による前記環流および混合を開始するか、または前記環流および混合が既に行われているときに前記環流および混合させる前記廃液の量を増加させる、環流制御機構。(B)前記測定機構において測定された前記過酸化水素の濃度と、当該濃度の基準値とを対比して、前記測定された濃度が前記基準値を超える場合に、前記紫外線照射機構による前記廃液への紫外線の照射条件を、当該廃液に含まれる過酸化水素の分解が促進される方向に変化させる紫外線制御機構。(C)前記紫外線が照射される前の前記廃液に対して、紫外線の照射による過酸化水素の分解を促進する促進剤を添加する促進剤添加機構、ならびに前記測定機構において測定された前記過酸化水素の濃度と、当該濃度の基準値とを対比して、前記測定された濃度が前記基準値を超える場合に、前記促進剤添加機構による前記促進剤の添加を開始するか、または前記促進剤の添加が既に行われているときに前記促進剤を添加する量を増加させる、促進剤制御機構。   The treatment apparatus of the present invention is a waste liquid treatment apparatus containing an acid or base and hydrogen peroxide, and an ultraviolet irradiation mechanism for irradiating the waste liquid containing an acid or base and hydrogen peroxide with ultraviolet light, and the ultraviolet light irradiation. And a measurement mechanism for measuring the concentration of hydrogen peroxide in the waste liquid after the operation, and at least one selected from the following (A), (B), and (C). (A) A reflux mechanism for circulating at least a part of the waste liquid after irradiation with the ultraviolet light and mixing with the waste liquid before the ultraviolet light irradiation, and the hydrogen peroxide measured in the measurement mechanism. When the measured concentration exceeds the reference value by comparing the concentration with the reference value of the concentration, the recirculation and mixing by the recirculation mechanism is started or the recirculation and mixing has already been performed. A recirculation control mechanism for increasing the amount of the recirculation and the waste liquid to be mixed. (B) When the concentration of the hydrogen peroxide measured in the measurement mechanism is compared with a reference value of the concentration and the measured concentration exceeds the reference value, the waste liquid by the ultraviolet irradiation mechanism An ultraviolet ray control mechanism that changes the irradiation condition of ultraviolet rays to the direction in which the decomposition of hydrogen peroxide contained in the waste liquid is accelerated. (C) an accelerator addition mechanism for adding an accelerator that promotes decomposition of hydrogen peroxide by irradiation of ultraviolet rays to the waste liquid before being irradiated with the ultraviolet rays, and the peroxidation measured in the measurement mechanism When the concentration of hydrogen is compared with the reference value of the concentration and the measured concentration exceeds the reference value, the addition of the accelerator by the accelerator addition mechanism is started, or the accelerator A promoter control mechanism that increases the amount of the promoter added when the addition of is already done.

本発明の処理方法および処理装置は、蒸留塔なしに、すなわち、過酸化水素の沸点に対する酸または塩基の沸点の関係によることなく、酸または塩基と過酸化水素とを含む廃液に含まれる過酸化水素を分解し、除去できる。これにより、本発明の処理方法および処理装置は、過酸化水素に比べて非常に高い沸点を有する硫酸だけではなく、過酸化水素と沸点が同程度以下である塩酸、フッ酸またはアンモニアを含む廃液にも適用できる。   The treatment method and treatment apparatus of the present invention provide a peroxidation contained in a waste liquid containing an acid or base and hydrogen peroxide without a distillation column, that is, without depending on the relationship of the boiling point of the acid or base to the boiling point of hydrogen peroxide. Hydrogen can be decomposed and removed. As a result, the treatment method and treatment apparatus of the present invention are not limited to sulfuric acid having a very high boiling point compared to hydrogen peroxide, but also waste liquid containing hydrochloric acid, hydrofluoric acid or ammonia having a boiling point equal to or less than that of hydrogen peroxide. It can also be applied to.

本発明の処理方法および処理装置は、触媒、酵素剤、還元剤などを用いて過酸化水素を分解する処理方法ならびに当該方法を採用する処理装置とは異なり、酸または塩基の中和処理を実施することなく、酸または塩基と過酸化水素とを含む廃液に含まれる過酸化水素を分解し、除去できる。   The treatment method and treatment apparatus of the present invention, unlike a treatment method that decomposes hydrogen peroxide using a catalyst, an enzyme agent, a reducing agent, or the like and a treatment device that employs the method, carry out neutralization treatment of acid or base. Without decomposing, hydrogen peroxide contained in the waste liquid containing acid or base and hydrogen peroxide can be decomposed and removed.

本発明の処理方法および処理装置によれば、廃液に含まれる過酸化水素の低コストでの除去が可能となり、廃液に含まれる酸または塩基の再利用が低コストで実現される。さらに、本発明の処理方法によれば、有効酸(塩基)濃度を保ったまま、廃液に含まれる過酸化水素を除去できる。すなわち、本発明の処理方法は、有効酸(塩基)濃度が高い廃液から、当該濃度が高いまま酸または塩基を再利用する場合に、特に有利となる。   According to the treatment method and the treatment apparatus of the present invention, it is possible to remove hydrogen peroxide contained in the waste liquid at low cost, and reuse of the acid or base contained in the waste liquid is realized at low cost. Furthermore, according to the treatment method of the present invention, hydrogen peroxide contained in the waste liquid can be removed while maintaining the effective acid (base) concentration. That is, the treatment method of the present invention is particularly advantageous when the acid or base is reused from a waste liquid having a high effective acid (base) concentration while the concentration is high.

本発明の処理方法および処理装置は、廃液に含まれる酸または塩基を再利用しない場合、例えば、処理後の廃液を放流する場合、にも好適に適用され、このときにも、当該廃液の処理が低コストとなる。   The treatment method and treatment apparatus of the present invention are also suitably applied to the case where the acid or base contained in the waste liquid is not reused, for example, when the waste liquid after treatment is discharged, and also at this time, the treatment of the waste liquid Is low cost.

本発明の処理装置の一例を示す模式図である。It is a schematic diagram which shows an example of the processing apparatus of this invention. 本発明の処理装置において、廃液に紫外線を照射する処理槽の一例を示す模式図である。In the processing apparatus of this invention, it is a schematic diagram which shows an example of the processing tank which irradiates a waste liquid with an ultraviolet-ray. 本発明の処理装置において、廃液に紫外線を照射する処理槽の別の一例を示す模式図である。In the processing apparatus of this invention, it is a schematic diagram which shows another example of the processing tank which irradiates a waste liquid with an ultraviolet-ray. 本発明の処理装置の別の一例を示す模式図である。It is a schematic diagram which shows another example of the processing apparatus of this invention. 本発明の処理装置のまた別の一例を示す模式図である。It is a schematic diagram which shows another example of the processing apparatus of this invention. 本発明の処理装置のさらにまた別の一例を示す模式図である。It is a schematic diagram which shows another example of the processing apparatus of this invention. 本発明の処理装置の上記とは別の一例を示す模式図である。It is a schematic diagram which shows an example different from the above of the processing apparatus of this invention. 本発明の処理装置の上記とはまた別の一例を示す模式図である。It is a schematic diagram which shows an example different from the above of the processing apparatus of this invention.

以下、本発明の処理装置(酸または塩基と過酸化水素とを含む廃液の処理装置)を図面に示しながら、当該装置および本発明の処理方法(酸または塩基と過酸化水素とを含む廃液の処理方法)を説明する。   Hereinafter, while showing the treatment apparatus of the present invention (treatment apparatus for waste liquid containing acid or base and hydrogen peroxide) in the drawings, the apparatus and the treatment method of the present invention (for waste liquid containing acid or base and hydrogen peroxide) Processing method) will be described.

図1に示す装置51は、酸または塩基と過酸化水素とを含む廃液1を、処理前に一時的に貯留する貯留槽12と、貯留槽12に廃液1を導入する導入管11と、廃液1に紫外線を照射する処理槽14と、廃液1を貯留槽12から処理槽14に送る配管13およびポンプPと、廃液1を処理槽14から装置51外に排出する排出管15と、排出管15の途中に設けられ、処理槽14を経た廃液1における過酸化水素の濃度を測定する測定装置18と、制御装置31と、を備える。制御装置31は、測定装置18で測定した当該濃度と当該濃度の基準値とを対比して、測定された濃度が基準値を超える場合に、処理槽14における廃液1への紫外線の照射条件を、廃液1に含まれる過酸化水素の分解が促進される方向に変化させる。装置51は、紫外線照射機構として処理槽14と、測定機構として測定装置18と、上記(B)の紫外線制御機構として制御装置31と、を備える。   An apparatus 51 shown in FIG. 1 includes a storage tank 12 that temporarily stores waste liquid 1 containing an acid or base and hydrogen peroxide, an introduction pipe 11 that introduces the waste liquid 1 into the storage tank 12, and a waste liquid. 1, a treatment tank 14 for irradiating ultraviolet rays, a pipe 13 and a pump P for sending the waste liquid 1 from the storage tank 12 to the treatment tank 14, a discharge pipe 15 for discharging the waste liquid 1 from the treatment tank 14 to the outside of the apparatus 51, and a discharge pipe 15, a measuring device 18 that measures the concentration of hydrogen peroxide in the waste liquid 1 that has passed through the treatment tank 14, and a control device 31 are provided. The control device 31 compares the concentration measured by the measurement device 18 with the reference value of the concentration, and when the measured concentration exceeds the reference value, the irradiation condition of the ultraviolet light to the waste liquid 1 in the treatment tank 14 is determined. Then, the hydrogen peroxide contained in the waste liquid 1 is changed in a direction that promotes decomposition. The apparatus 51 includes a processing tank 14 as an ultraviolet irradiation mechanism, a measuring apparatus 18 as a measurement mechanism, and a control device 31 as the ultraviolet control mechanism (B).

廃液1は、導入管11を通して貯留槽12に送られた後、ポンプPにより、配管13を通して処理槽14に送られる。処理槽14では、廃液1に紫外線を照射して当該廃液に含まれる過酸化水素を分解する工程(照射工程)が実施される。照射工程を経た廃液1は、排出管15を通して装置51外に送り出される。その際、排出管15の途中に設けられた測定装置18によって、照射工程を経た廃液1における過酸化水素の濃度が測定される(測定工程)。制御装置31は、測定装置18で測定した過酸化水素の濃度と当該濃度の基準値とを対比して、測定された濃度が基準値を超える場合に、処理槽14における廃液1への紫外線の照射条件を、廃液1に含まれる過酸化水素の分解が促進される方向に変化させる(制御工程)。   The waste liquid 1 is sent to the storage tank 12 through the introduction pipe 11 and then sent to the treatment tank 14 through the pipe 13 by the pump P. In the treatment tank 14, a step (irradiation step) of irradiating the waste liquid 1 with ultraviolet rays to decompose hydrogen peroxide contained in the waste liquid is performed. The waste liquid 1 that has undergone the irradiation process is sent out of the apparatus 51 through the discharge pipe 15. At that time, the concentration of hydrogen peroxide in the waste liquid 1 that has undergone the irradiation process is measured by a measuring device 18 provided in the middle of the discharge pipe 15 (measuring process). The control device 31 compares the concentration of hydrogen peroxide measured by the measuring device 18 with the reference value of the concentration, and when the measured concentration exceeds the reference value, the ultraviolet light to the waste liquid 1 in the treatment tank 14 is The irradiation conditions are changed in a direction in which the decomposition of hydrogen peroxide contained in the waste liquid 1 is promoted (control process).

装置51ならびに装置51において実施される上記処理方法では、廃液1に含まれる過酸化水素の分解・除去効率が向上する。さらに、この装置および方法では、処理すべき廃液1に含まれる過酸化水素の濃度が経時的に変化する場合にも、過酸化水素を安定して分解・除去できる。なお、排出管15を通して装置51から送り出された廃液1は、当業者が自由に取り扱うことができ、例えば、必要に応じてさらなる処理が施された後、貯蔵、再利用あるいは放流される。以降の図に示す装置52〜56においても同様である。   In the apparatus 51 and the processing method implemented in the apparatus 51, the decomposition / removal efficiency of hydrogen peroxide contained in the waste liquid 1 is improved. Furthermore, in this apparatus and method, hydrogen peroxide can be stably decomposed and removed even when the concentration of hydrogen peroxide contained in the waste liquid 1 to be treated changes with time. In addition, the waste liquid 1 sent out from the apparatus 51 through the discharge pipe 15 can be freely handled by those skilled in the art. For example, the waste liquid 1 is stored, reused or discharged after further processing is performed as necessary. The same applies to the devices 52 to 56 shown in the following figures.

制御装置31(制御工程)で対比される「基準値」は、装置51のユーザーが任意に設定できる。基準値は、例えば、廃液1からの酸または塩基の再利用時、あるいは廃液1の放流時に要求される過酸化水素の上限濃度である。上限濃度は、再利用時について、例えば100ppm、放流時について、例えば20ppmである。   The “reference value” to be compared in the control device 31 (control process) can be arbitrarily set by the user of the device 51. The reference value is, for example, the upper limit concentration of hydrogen peroxide required when the acid or base from the waste liquid 1 is reused or when the waste liquid 1 is discharged. The upper limit concentration is, for example, 100 ppm when reused, and, for example, 20 ppm when discharged.

装置51ならびに装置51において実施される上記処理方法では、測定装置18によって測定された、照射工程を経た廃液1の過酸化水素の濃度が基準値を超える場合に、制御装置31によって、過酸化水素の分解が促進される方向に紫外線の照射条件を変化させる。ここで、装置51の具体的な構成によっては、紫外線の照射条件が変化してから実際にその効果が得られるまで、より具体的には、測定装置18によって測定される過酸化水素の濃度が下がり始め、基準値以下となるまでに、タイムラグが生じることがある。このようなときに、基準値を上記上限濃度に設定していると、一時的に当該上限濃度を超える過酸化水素濃度を有する廃液が装置51から排出されることがある。このような排出が問題となる場合には、上記上限濃度から一定の値を差し引いた濃度を、基準値としてもよい。   In the apparatus 51 and the processing method implemented in the apparatus 51, when the concentration of hydrogen peroxide in the waste liquid 1 that has been subjected to the irradiation process measured by the measuring apparatus 18 exceeds a reference value, the control apparatus 31 performs hydrogen peroxide. The irradiation condition of ultraviolet rays is changed in the direction in which the decomposition of is promoted. Here, depending on the specific configuration of the device 51, more specifically, the concentration of hydrogen peroxide measured by the measuring device 18 is changed until the effect is actually obtained after the irradiation condition of the ultraviolet rays changes. There may be a time lag when it starts to fall and falls below the reference value. In such a case, if the reference value is set to the upper limit concentration, waste liquid having a hydrogen peroxide concentration that temporarily exceeds the upper limit concentration may be discharged from the apparatus 51. When such discharge becomes a problem, a concentration obtained by subtracting a certain value from the upper limit concentration may be used as a reference value.

制御装置31は、測定装置18において測定された廃液1における過酸化水素の濃度が当該濃度の基準値以下となった場合、処理槽14における廃液1への紫外線の照射条件を、廃液1に含まれる過酸化水素の分解が穏やかになる方向に変化させてもよい。   When the concentration of hydrogen peroxide in the waste liquid 1 measured by the measuring device 18 is equal to or lower than the reference value of the concentration, the control device 31 includes the waste liquid 1 in the waste liquid 1 under the irradiation condition of the ultraviolet light to the waste liquid 1 in the treatment tank 14. It may be changed in a direction in which decomposition of hydrogen peroxide generated becomes gentle.

制御する紫外線の照射条件は、例えば、単位量の廃液1に対する紫外線の照射量である。当該照射量は、例えば、廃液1が処理槽14を通過する時間を変化させたり、処理槽14において廃液1に照射する紫外線の強度を変化させたりすることで調整される。   The ultraviolet irradiation condition to be controlled is, for example, the ultraviolet irradiation amount with respect to the unit amount of the waste liquid 1. The amount of irradiation is adjusted by, for example, changing the time for which the waste liquid 1 passes through the treatment tank 14 or changing the intensity of the ultraviolet rays applied to the waste liquid 1 in the treatment tank 14.

具体的には、上記制御工程において、測定工程で測定した過酸化水素の濃度と当該濃度の基準値とを対比して、測定された濃度が基準値を超える場合に、照射工程における単位量の廃液1に対する紫外線の照射量を多くする。制御装置31は、測定装置18で測定した過酸化水素の濃度と当該濃度の基準値とを対比して、測定された濃度が基準値を超える場合に、処理槽14による、単位量の廃液1への紫外線の照射量を多くする。   Specifically, in the above control step, the concentration of hydrogen peroxide measured in the measurement step is compared with the reference value of the concentration, and when the measured concentration exceeds the reference value, the unit amount of the irradiation step Increasing the amount of ultraviolet irradiation to the waste liquid 1. The control device 31 compares the concentration of hydrogen peroxide measured by the measuring device 18 with the reference value of the concentration, and when the measured concentration exceeds the reference value, the unit amount of the waste liquid 1 by the treatment tank 14. Increase the amount of UV irradiation to the.

装置51ならびに装置51において実施される上記方法では、測定工程において(測定装置18において)、照射工程を経た(処理槽14を経た)廃液1における過酸化水素の濃度を連続的に測定し、制御工程において(制御装置31において)、測定された当該濃度と基準値とを連続的に対比して、上述した紫外線の照射条件の変化を連続的に実施してもよい。この場合、廃液1に含まれる過酸化水素の分解・除去効率がさらに向上する。また、処理すべき廃液1に含まれる過酸化水素の濃度が経時的に変化する場合にも、当該変化に対する処理の追従性が向上し、過酸化水素のさらに安定した分解・除去が可能となる。   In the apparatus 51 and the above method implemented in the apparatus 51, in the measurement process (in the measurement apparatus 18), the concentration of hydrogen peroxide in the waste liquid 1 that has undergone the irradiation process (through the treatment tank 14) is continuously measured and controlled. In the process (in the control device 31), the measured concentration and the reference value may be continuously compared, and the above-described change in the ultraviolet irradiation condition may be continuously performed. In this case, the decomposition and removal efficiency of hydrogen peroxide contained in the waste liquid 1 is further improved. Further, even when the concentration of hydrogen peroxide contained in the waste liquid 1 to be treated changes with time, the followability of the treatment with respect to the change is improved, and hydrogen peroxide can be more stably decomposed and removed. .

本発明の処理方法および処理装置の対象となる廃液1は、酸または塩基と過酸化水素とを含む。廃液1は、例えば、半導体素子の製造工程、より具体的には、基板の洗浄工程またはレジスト剥離工程から排出される廃液である。廃液1は、半導体素子の製造装置から排出された後、直接、または一度貯留された後に、導入管11を通して貯留槽12に送られる。   The waste liquid 1 which is the target of the treatment method and treatment apparatus of the present invention contains an acid or base and hydrogen peroxide. The waste liquid 1 is, for example, a waste liquid discharged from a semiconductor element manufacturing process, more specifically, a substrate cleaning process or a resist stripping process. The waste liquid 1 is discharged from the semiconductor device manufacturing apparatus, directly or once stored, and then sent to the storage tank 12 through the introduction pipe 11.

廃液1が含む酸は、例えば、硫酸、塩酸またはフッ酸である。廃液1が含む塩基は、例えば、アンモニアである。廃液1は、例えば、硫酸過水(SPM)、塩酸過水(HPM)、フッ酸過水(FPM)またはアンモニア過水(APM)を含む廃液である。   The acid contained in the waste liquid 1 is, for example, sulfuric acid, hydrochloric acid, or hydrofluoric acid. The base contained in the waste liquid 1 is, for example, ammonia. The waste liquid 1 is a waste liquid containing, for example, sulfuric acid / hydrogen peroxide (SPM), hydrochloric acid / hydrogen peroxide (HPM), hydrofluoric acid / hydrogen peroxide (FPM), or ammonia / hydrogen peroxide (APM).

処理槽14および照射工程では、廃液1に紫外線(UV)が照射され、以下の式(1)に示す過酸化水素の分解反応が進行する。式(1)における「・OH」は、ヒドロキシラジカルである。   In the treatment tank 14 and the irradiation step, the waste liquid 1 is irradiated with ultraviolet rays (UV), and the decomposition reaction of hydrogen peroxide represented by the following formula (1) proceeds. “.OH” in the formula (1) is a hydroxy radical.

22 +(UV照射)→ 2(・OH) → ・OH+1/2(H22) (1) H 2 O 2 + (UV irradiation) → 2 (.OH) → OH + 1/2 (H 2 O 2 ) (1)

式(1)に示すように、廃液1に紫外線が照射されると、当該廃液1に含まれる過酸化水素が分解してヒドロキシラジカルが発生する。発生したヒドロキシラジカルのうち、およそ半分のヒドロキシラジカルは過酸化水素に戻るが、残りのヒドロキシラジカルは、当該ラジカル同士あるいは廃液中に含まれる物質と反応し、消滅する。紫外線の照射により、当該反応と式(1)に示す分解反応とが繰り返されることで、過酸化水素は、最終的に水と酸素とに分解される。廃液中に有機物、例えばレジスト剥離工程から排出されたレジスト材料、が含まれる場合、ヒドロキシラジカルが当該有機物を分解して、炭酸ガスがさらに発生することがある。   As shown in Formula (1), when the waste liquid 1 is irradiated with ultraviolet rays, the hydrogen peroxide contained in the waste liquid 1 is decomposed to generate hydroxy radicals. Approximately half of the generated hydroxy radicals return to hydrogen peroxide, but the remaining hydroxy radicals react with each other or with substances contained in the waste liquid and disappear. The hydrogen peroxide is finally decomposed into water and oxygen by repeating the reaction and the decomposition reaction represented by the formula (1) by irradiation with ultraviolet rays. When the waste liquid contains an organic substance, for example, a resist material discharged from the resist stripping process, the hydroxy radical may decompose the organic substance to further generate carbon dioxide gas.

廃液1に照射する紫外線の波長は、100〜280nmが好ましい。この波長域の紫外線の光源には、例えば、水銀灯、エキシマレーザー、発光ダイオード(LED)を利用できる。   As for the wavelength of the ultraviolet-ray irradiated to the waste liquid 1, 100-280 nm is preferable. For example, a mercury lamp, excimer laser, or light emitting diode (LED) can be used as the ultraviolet light source in this wavelength range.

照射工程における廃液1の温度は、限定されない。廃液1に含まれる酸または塩基の種類によって調整でき、例えば酸が硫酸である場合、10〜50℃程度が好ましい。   The temperature of the waste liquid 1 in the irradiation process is not limited. For example, when the acid is sulfuric acid, the temperature is preferably about 10 to 50 ° C.

処理槽14の構造は、当該槽14内の廃液1に紫外線を照射できる限り限定されない。処理槽14の例を、図2,3に示す。   The structure of the treatment tank 14 is not limited as long as the waste liquid 1 in the tank 14 can be irradiated with ultraviolet rays. An example of the treatment tank 14 is shown in FIGS.

図2に示す処理槽14Aは、最も単純な構造を有する処理槽の一種である。処理槽14Aの内部は、配管13を通して処理槽14Aに送られた廃液1が滞留する空間になっている。廃液1は、処理槽14Aの内部で、設定された高さの液面を保っている。処理槽14A内の上部、廃液1の液面から露出した位置に、紫外線の光源41が配置されている。処理槽14Aの内部には隔壁43が配置されており、隔壁43の配置によって、廃液1の処理槽14Aへの滞留時間を長くするとともに、廃液1にできるだけ均一に紫外線が照射されるように工夫されている。配管13を通して処理槽14Aに送られた廃液1は、処理槽14Aの内部に滞留する間に光源41からの紫外線の照射を受けた後、処理槽14Aに接続された排出管15を通して当該槽14Aから送り出される。このような処理槽14Aを備える装置51は、低コストで構築できる。なお、処理槽14Aの内壁面は、紫外線を効率よく反射する処理、例えば鏡面処理、が施されていることが好ましい。   The processing tank 14A shown in FIG. 2 is a kind of processing tank having the simplest structure. The interior of the treatment tank 14A is a space in which the waste liquid 1 sent to the treatment tank 14A through the pipe 13 is retained. The waste liquid 1 maintains a liquid level with a set height inside the treatment tank 14A. An ultraviolet light source 41 is disposed in the upper part of the treatment tank 14 </ b> A, at a position exposed from the liquid level of the waste liquid 1. A partition wall 43 is arranged inside the treatment tank 14A. By arranging the partition wall 43, the residence time of the waste liquid 1 in the treatment tank 14A is lengthened, and the waste liquid 1 is irradiated with ultraviolet rays as uniformly as possible. Has been. The waste liquid 1 sent to the treatment tank 14A through the pipe 13 is irradiated with ultraviolet rays from the light source 41 while it stays in the treatment tank 14A, and then passes through the discharge pipe 15 connected to the treatment tank 14A. Sent out. The apparatus 51 provided with such a processing tank 14A can be constructed at low cost. Note that the inner wall surface of the treatment tank 14A is preferably subjected to a treatment that efficiently reflects ultraviolet rays, for example, a mirror treatment.

処理槽14Aにおいて、廃液1への紫外線の照射条件は、例えば、以下のように制御できる:廃液1が処理槽14Aを通過する時間を調整する。この調整は、ポンプPの出力を変化させることで実行できる;廃液1に照射する紫外線の強度を変化させる。例えば、2以上の光源41を有する処理槽14Aとし、点灯させる光源41の数を変化させる;処理槽14A内における廃液1の液面の高さを調整する。この調整は、処理槽14Aに送り込む廃液1の量と、処理槽14Aから送り出す廃液1の量とのバランスを変化させることで実行できる。   In the treatment tank 14A, the irradiation condition of the ultraviolet light to the waste liquid 1 can be controlled, for example, as follows: The time for the waste liquid 1 to pass through the treatment tank 14A is adjusted. This adjustment can be performed by changing the output of the pump P; it changes the intensity of the ultraviolet rays irradiated to the waste liquid 1. For example, the processing tank 14A having two or more light sources 41 is used, and the number of light sources 41 to be turned on is changed; the height of the liquid level of the waste liquid 1 in the processing tank 14A is adjusted. This adjustment can be performed by changing the balance between the amount of the waste liquid 1 sent to the treatment tank 14A and the amount of the waste liquid 1 sent from the treatment tank 14A.

図3に示す処理槽14Bは、廃液1が流通する配管42を内部に備える。配管42の一方の端部は、廃液1を処理槽14Bに送る配管13に接続されている。配管42の他方の端部は、紫外線照射後の廃液1を処理槽14Bから送り出す排出管15に接続されている。さらに、処理槽14Bは、配管42の外壁面に沿うように複数配置された紫外線の光源41を備える。配管42は、紫外線を透過する材料、例えばポリテトラフルオロエチレン、から構成されている。   The processing tank 14B shown in FIG. 3 includes a pipe 42 through which the waste liquid 1 flows. One end of the pipe 42 is connected to the pipe 13 that sends the waste liquid 1 to the treatment tank 14B. The other end of the pipe 42 is connected to a discharge pipe 15 that sends out the waste liquid 1 after ultraviolet irradiation from the treatment tank 14B. Furthermore, the processing tank 14 </ b> B includes a plurality of ultraviolet light sources 41 arranged along the outer wall surface of the pipe 42. The pipe 42 is made of a material that transmits ultraviolet rays, for example, polytetrafluoroethylene.

配管13を通して処理槽14Bに送られた廃液1は、そのまま処理槽14Bの配管42内を流れる。その際、光源41からの紫外線が配管42を透過して廃液1に照射され、廃液1に含まれる過酸化水素が分解される。その後、廃液1は、配管42に接続された排出管15を通して処理槽14Bから送り出される。処理槽14Bでは、紫外線の光源41と廃液1との距離を小さく保つことができるため、廃液1に含まれる過酸化水素を分解する効率が高くなる。これに加えて、配管42の径および形状、光源41の種類および配置の形態ならびに処理槽14B内における配管42の経路を適切に選択、設計することにより、廃液1に含まれる過酸化水素を分解する効率がさらに向上する。   The waste liquid 1 sent to the processing tank 14B through the pipe 13 flows in the pipe 42 of the processing tank 14B as it is. At that time, the ultraviolet light from the light source 41 passes through the pipe 42 and is irradiated to the waste liquid 1, and the hydrogen peroxide contained in the waste liquid 1 is decomposed. Thereafter, the waste liquid 1 is sent out from the treatment tank 14 </ b> B through the discharge pipe 15 connected to the pipe 42. In the treatment tank 14B, since the distance between the ultraviolet light source 41 and the waste liquid 1 can be kept small, the efficiency of decomposing hydrogen peroxide contained in the waste liquid 1 is increased. In addition to this, hydrogen peroxide contained in the waste liquid 1 is decomposed by appropriately selecting and designing the diameter and shape of the pipe 42, the type and arrangement of the light source 41, and the path of the pipe 42 in the treatment tank 14B. Efficiency is further improved.

処理槽14Bにおいて、廃液1への紫外線の照射条件は、例えば、以下のように制御できる:廃液1が処理槽14Bを通過する時間を調整する。この調整は、ポンプPの出力を変化させたり、バルブなどを用いて廃液1が通過する配管42の長さを変化させることで実行できる;廃液1に照射する紫外線の強度を変化させる。例えば、2以上の光源41を有する処理槽14Bとし、点灯させる光源41の数を変化させる。   In the treatment tank 14B, the irradiation condition of the ultraviolet light to the waste liquid 1 can be controlled, for example, as follows: The time for the waste liquid 1 to pass through the treatment tank 14B is adjusted. This adjustment can be performed by changing the output of the pump P or changing the length of the pipe 42 through which the waste liquid 1 passes using a valve or the like; the intensity of the ultraviolet rays irradiated to the waste liquid 1 is changed. For example, the processing tank 14B has two or more light sources 41, and the number of light sources 41 to be turned on is changed.

配管42は、通常、図3に示すように、屈曲した状態で処理槽14B内に配置される。これにより、処理槽14Bのコンパクト化を図ることができる。さらに、光源41の配置の形態によっては、1つの光源41によって、複数の配管42を流れる廃液1に同時に紫外線を照射できる。   As shown in FIG. 3, the pipe 42 is usually arranged in the treatment tank 14 </ b> B in a bent state. Thereby, the processing tank 14B can be made compact. Furthermore, depending on the arrangement of the light sources 41, the single liquid source 41 can simultaneously irradiate the waste liquid 1 flowing through the plurality of pipes 42 with ultraviolet rays.

処理槽14Bでは、配管42を構成する材料の種類を適切に選択することによって、廃液1に含まれる酸または塩基による処理槽14Bの腐食が抑えられ、廃液1の処理コストおよび装置51のメンテナンスコストが低くなる。これに加えて、処理槽14Bの腐食による廃液1への不純物の混入が減り、純度が高い酸または塩基の再利用が容易となる。酸および塩基のなかでも硫酸の腐食性が特に強いため、処理槽14Bは、廃液1が硫酸を含む場合に好適である。硫酸を含む廃液1を処理する場合、配管42は、紫外線を透過する樹脂、例えばポリテトラフルオロエチレン、により構成されることが好ましい。   In the treatment tank 14B, by appropriately selecting the type of material constituting the pipe 42, corrosion of the treatment tank 14B due to the acid or base contained in the waste liquid 1 is suppressed, and the treatment cost of the waste liquid 1 and the maintenance cost of the apparatus 51 are reduced. Becomes lower. In addition, the contamination of the waste liquid 1 due to the corrosion of the treatment tank 14B is reduced, and the reuse of the acid or base having a high purity is facilitated. Among acids and bases, the corrosiveness of sulfuric acid is particularly strong, so that the treatment tank 14B is suitable when the waste liquid 1 contains sulfuric acid. When processing the waste liquid 1 containing sulfuric acid, it is preferable that the piping 42 is comprised with resin which permeate | transmits an ultraviolet-ray, for example, polytetrafluoroethylene.

処理槽14Bの内壁面に対して、紫外線を効率よく反射する処理、例えば鏡面処理、が施されていることが好ましい。   It is preferable that the inner wall surface of the treatment tank 14B is subjected to a treatment that efficiently reflects ultraviolet rays, for example, a mirror treatment.

本発明の処理方法における照射工程は、廃液1への紫外線の照射によって廃液1に含まれる過酸化水素が分解できる限り、任意の装置を用い、必要に応じて当該装置を組み合わせて、実施できる。当該装置は、図2,3に示す処理槽14A,14Bに限定されない。   As long as the hydrogen peroxide contained in the waste liquid 1 can be decomposed by irradiation of the waste liquid 1 with ultraviolet rays, the irradiation step in the treatment method of the present invention can be carried out using any apparatus and combining the apparatuses as necessary. The said apparatus is not limited to processing tank 14A, 14B shown to FIG.

測定装置18は、例えば、過酸化水素センサーである。   The measuring device 18 is, for example, a hydrogen peroxide sensor.

本発明の処理方法における測定工程は、溶液中の過酸化水素の濃度を測定する公知の方法、例えば、滴定法、UV吸収法、近赤外吸収法を応用して実施できる。硫酸を含む廃液あるいはアンモニアを含む廃液の場合、過酸化水素の濃度を直接測定するだけではなく、廃液1の化学的酸素要求量(COD)を測定し、測定したCOD値を換算して過酸化水素の濃度としてもよい。   The measurement step in the treatment method of the present invention can be carried out by applying a known method for measuring the concentration of hydrogen peroxide in the solution, for example, a titration method, a UV absorption method, or a near infrared absorption method. In the case of a waste liquid containing sulfuric acid or a waste liquid containing ammonia, not only the concentration of hydrogen peroxide is directly measured, but also the chemical oxygen demand (COD) of waste liquid 1 is measured, and the measured COD value is converted into peroxidation. The concentration of hydrogen may be used.

測定装置18および制御装置31を用いた紫外線の照射条件の制御は、当業者であれば、適宜、構築できる。   A person skilled in the art can appropriately control the control of the ultraviolet irradiation conditions using the measuring device 18 and the control device 31.

図4に、本発明の処理装置の別の一例を示す。図4に示す装置52は、酸または塩基と過酸化水素とを含む廃液1を、処理前に一時的に貯留する貯留槽12と、貯留槽12に廃液1を導入する導入管11と、廃液1に紫外線を照射する処理槽14と、廃液1を貯留槽12から処理槽14に送る配管13およびポンプPと、廃液1を処理槽14から装置51外に排出する排出管15と、排出管15の途中に設けられ、処理槽14を経た廃液1における過酸化水素の濃度を測定する測定装置18と、排出管15の途中に設けられ、処理槽14を経た廃液1の少なくとも一部を排出管15から分岐させるバルブ16と、バルブ16において分岐させた廃液1を貯留槽12に環流させ、紫外線が照射される前の廃液1に混合する環流管17と、制御装置32と、を備える。制御装置32は、測定装置18で測定した当該濃度と当該濃度の基準値とを対比して、測定された濃度が基準値を超える場合に、バルブ16の作動を制御し、処理槽14を経た廃液1を環流管17を通して貯留槽12に環流させ、貯留槽12内の廃液1に混合させる量を制御する。より具体的には、当該場合に、バルブ16および環流管17による当該環流および混合を開始するか、または、当該環流および混合が既に行われているときに当該環流および混合させる廃液1の量を増加させる。装置52は、紫外線照射機構として処理槽14と、測定機構として測定装置18と、上記(A)の環流機構としてバルブ16および環流管17と、上記(A)の環流制御機構として制御装置32と、を備える。   FIG. 4 shows another example of the processing apparatus of the present invention. An apparatus 52 shown in FIG. 4 includes a storage tank 12 that temporarily stores waste liquid 1 containing an acid or base and hydrogen peroxide, an introduction pipe 11 that introduces the waste liquid 1 into the storage tank 12, and a waste liquid. 1, a treatment tank 14 for irradiating ultraviolet rays, a pipe 13 and a pump P for sending the waste liquid 1 from the storage tank 12 to the treatment tank 14, a discharge pipe 15 for discharging the waste liquid 1 from the treatment tank 14 to the outside of the apparatus 51, and a discharge pipe 15, a measuring device 18 for measuring the concentration of hydrogen peroxide in the waste liquid 1 that has passed through the treatment tank 14, and at least a part of the waste liquid 1 that has been provided in the middle of the discharge pipe 15 and has passed through the treatment tank 14. A valve 16 that branches off from the pipe 15, a reflux pipe 17 that circulates the waste liquid 1 branched off in the valve 16 to the storage tank 12 and mixes it with the waste liquid 1 before being irradiated with ultraviolet rays, and a control device 32 are provided. The control device 32 compares the concentration measured by the measuring device 18 with the reference value of the concentration, and controls the operation of the valve 16 when the measured concentration exceeds the reference value, and passes through the treatment tank 14. The waste liquid 1 is circulated to the storage tank 12 through the reflux pipe 17, and the amount mixed with the waste liquid 1 in the storage tank 12 is controlled. More specifically, in this case, the recirculation and mixing by the valve 16 and the recirculation pipe 17 are started, or the amount of the waste liquid 1 to be recirculated and mixed when the recirculation and mixing are already performed. increase. The apparatus 52 includes a treatment tank 14 as an ultraviolet irradiation mechanism, a measurement apparatus 18 as a measurement mechanism, a valve 16 and a circulation pipe 17 as the circulation mechanism (A), and a control device 32 as the circulation control mechanism (A). .

廃液1は、導入管11を通して貯留槽12に送られた後、ポンプPにより、配管13を通して処理槽14に送られる。処理槽14では、廃液1に紫外線を照射して当該廃液に含まれる過酸化水素を分解する工程(照射工程)が実施される。照射工程を経た廃液1は、排出管15を通して装置51外に送り出される。その際、排出管15の途中に設けられた測定装置18によって、照射工程を経た廃液1における過酸化水素の濃度が測定される(測定工程)。制御装置32は、上述した制御を行う(制御工程)。   The waste liquid 1 is sent to the storage tank 12 through the introduction pipe 11 and then sent to the treatment tank 14 through the pipe 13 by the pump P. In the treatment tank 14, a step (irradiation step) of irradiating the waste liquid 1 with ultraviolet rays to decompose hydrogen peroxide contained in the waste liquid is performed. The waste liquid 1 that has undergone the irradiation process is sent out of the apparatus 51 through the discharge pipe 15. At that time, the concentration of hydrogen peroxide in the waste liquid 1 that has undergone the irradiation process is measured by a measuring device 18 provided in the middle of the discharge pipe 15 (measuring process). The control device 32 performs the above-described control (control process).

装置52の起動時、あるいは貯留槽12内の廃液1に含まれる過酸化水素の濃度が高くなった場合に、処理槽14における過酸化水素の分解・除去が、望むレベルにまで達しないことがある。このとき、装置52ならびに装置52において実施される上記処理方法では、バルブ16を作動させて、処理槽14から送り出された廃液の少なくとも一部を貯留槽12に環流させ、貯留槽12内の廃液1における過酸化水素の濃度を低減させるとともに、環流させた廃液1に対して再度の照射工程を実施できる。すなわち、廃液1に含まれる過酸化水素の分解がより確実になる。   When the apparatus 52 is started up or when the concentration of hydrogen peroxide contained in the waste liquid 1 in the storage tank 12 becomes high, decomposition / removal of hydrogen peroxide in the treatment tank 14 may not reach a desired level. is there. At this time, in the processing method implemented in the device 52 and the device 52, the valve 16 is operated to circulate at least a part of the waste liquid sent out from the processing tank 14 to the storage tank 12, and the waste liquid in the storage tank 12 is returned. The concentration of hydrogen peroxide in 1 can be reduced, and the irradiation process can be performed again on the circulated waste liquid 1. That is, the decomposition of hydrogen peroxide contained in the waste liquid 1 becomes more reliable.

制御装置32(制御工程)で対比される「基準値」は、装置52のユーザーが任意に設定できる。基準値は、例えば、廃液1からの酸または塩基の再利用時、あるいは廃液1の放流時に要求される過酸化水素の上限濃度である。   The “reference value” to be compared in the control device 32 (control process) can be arbitrarily set by the user of the device 52. The reference value is, for example, the upper limit concentration of hydrogen peroxide required when the acid or base from the waste liquid 1 is reused or when the waste liquid 1 is discharged.

装置52ならびに装置52において実施される上記処理方法では、測定装置18によって測定された、照射工程を経た廃液1の過酸化水素の濃度が基準値を超える場合に、制御装置32によって、環流機構による廃液1の環流・混合が始まるか、あるいは廃液1の環流・混合量が増加させられる。ここで、装置52の具体的な構成によっては、廃液1の環流・混合が始まってから、あるいは廃液1の環流・混合量が増加してから実際にその効果が得られるまで、より具体的には、測定装置18によって測定される過酸化水素の濃度が下がり始め、基準値以下となるまでに、タイムラグが生じることがある。このようなときに、基準値を上記上限濃度に設定していると、一時的に当該上限濃度を超える過酸化水素濃度を有する廃液が装置52から排出されることがある。このような排出が問題となる場合には、上記上限濃度から一定の値を差し引いた濃度を、基準値としてもよい。   In the apparatus 52 and the processing method implemented in the apparatus 52, when the concentration of hydrogen peroxide in the waste liquid 1 after the irradiation process measured by the measuring apparatus 18 exceeds the reference value, the controller 32 causes the circulation mechanism to The recirculation / mixing of the waste liquid 1 starts or the recirculation / mixing amount of the waste liquid 1 is increased. Here, depending on the specific configuration of the device 52, more specifically, from the start of the recirculation / mixing of the waste liquid 1 or from the increase of the recirculation / mixing amount of the waste liquid 1 until the effect is actually obtained. In this case, a time lag may occur until the concentration of hydrogen peroxide measured by the measuring device 18 starts to decrease and falls below the reference value. In such a case, if the reference value is set to the upper limit concentration, waste liquid having a hydrogen peroxide concentration that temporarily exceeds the upper limit concentration may be discharged from the device 52. When such discharge becomes a problem, a concentration obtained by subtracting a certain value from the upper limit concentration may be used as a reference value.

制御装置32は、測定装置18において測定された廃液1における過酸化水素の濃度が当該濃度の基準値以下となった場合、環流機構による廃液1の環流・混合量を減少させてもよく、環流・混合を停止してもよい。   When the concentration of hydrogen peroxide in the waste liquid 1 measured by the measuring device 18 is equal to or less than the reference value of the concentration, the control device 32 may reduce the amount of reflux / mixing of the waste liquid 1 by the reflux mechanism. -Mixing may be stopped.

装置52ならびに装置52において実施される上記方法では、環流機構による廃液1の環流・混合量はゼロでありうるし、常に環流・混合が行われてもよい。   In the apparatus 52 and the above-described method implemented in the apparatus 52, the reflux / mixing amount of the waste liquid 1 by the reflux mechanism may be zero, or the reflux / mixing may always be performed.

装置52ならびに装置52において実施される上記方法では、測定工程において(測定装置18において)、照射工程を経た(処理槽14を経た)廃液1における過酸化水素の濃度を連続的に測定し、制御工程において(制御装置32において)、測定された当該濃度と基準値とを連続的に対比して、上述した廃液1の環流・混合を連続的に制御してもよい。この場合、処理すべき廃液1に含まれる過酸化水素の濃度が経時的に変化する場合にも、当該変化に対する処理の追従性が向上し、過酸化水素のさらに安定した分解・除去が可能となる。   In the apparatus 52 and the above method implemented in the apparatus 52, in the measurement process (in the measurement apparatus 18), the concentration of hydrogen peroxide in the waste liquid 1 that has undergone the irradiation process (through the treatment tank 14) is continuously measured and controlled. In the process (in the control device 32), the reflux and mixing of the waste liquid 1 described above may be continuously controlled by continuously comparing the measured concentration and the reference value. In this case, even when the concentration of hydrogen peroxide contained in the waste liquid 1 to be treated changes with time, the followability of the treatment to the change is improved, and hydrogen peroxide can be more stably decomposed and removed. Become.

環流機構は、図4に示すバルブ16および環流管17に限定されない。廃液1の環流先は貯留槽12に限定されない。照射工程が実施される前の廃液1に、環流した廃液1を混合すればよい。   The reflux mechanism is not limited to the valve 16 and the reflux pipe 17 shown in FIG. The return destination of the waste liquid 1 is not limited to the storage tank 12. The recycled waste liquid 1 may be mixed with the waste liquid 1 before the irradiation process is performed.

測定装置18および制御装置32を用いた廃液1の環流量の制御は、当業者であれば、適宜、構築できる。   A person skilled in the art can appropriately construct control of the ring flow rate of the waste liquid 1 using the measuring device 18 and the control device 32.

図5に、本発明の処理装置の別の一例を示す。図5に示す装置53は、酸または塩基と過酸化水素とを含む廃液1を、処理前に一時的に貯留する貯留槽12と、貯留槽12に廃液1を導入する導入管11と、廃液1に紫外線を照射する処理槽14と、廃液1を貯留槽12から処理槽14に送る配管13およびポンプPと、廃液1を処理槽14から装置51外に排出する排出管15と、排出管15の途中に設けられ、処理槽14を経た廃液1における過酸化水素の濃度を測定する測定装置18と、紫外線の照射による過酸化水素の分解を促進する促進剤2を、紫外線が照射される前の廃液1に添加する促進剤槽21と、促進剤2の添加量を調整するバルブ19と、制御装置33と、を備える。制御装置33は、測定装置18で測定した当該濃度と当該濃度の基準値とを対比して、測定された濃度が基準値を超える場合に、バルブ19の作動を制御し、廃液1への促進剤2の添加量を制御する。より具体的には、当該場合に、バルブ19および促進剤槽21による促進剤2の添加を開始するか、または、当該添加が既に行われているときに廃液1への促進剤2の添加量を増加させる。促進剤槽21は貯留槽12に接続されており、促進剤2は、貯留槽12内の廃液1に添加される。装置53は、紫外線照射機構として処理槽14と、測定機構として測定装置18と、上記(C)の促進剤添加機構としてバルブ19および促進剤槽21と、上記(C)の促進剤制御機構として制御装置33と、を備える。   FIG. 5 shows another example of the processing apparatus of the present invention. An apparatus 53 shown in FIG. 5 includes a storage tank 12 that temporarily stores waste liquid 1 containing acid or base and hydrogen peroxide, an introduction pipe 11 that introduces the waste liquid 1 into the storage tank 12, and a waste liquid. 1, a treatment tank 14 for irradiating ultraviolet rays, a pipe 13 and a pump P for sending the waste liquid 1 from the storage tank 12 to the treatment tank 14, a discharge pipe 15 for discharging the waste liquid 1 from the treatment tank 14 to the outside of the apparatus 51, and a discharge pipe 15, ultraviolet light is irradiated to a measuring device 18 that measures the concentration of hydrogen peroxide in the waste liquid 1 that has passed through the treatment tank 14 and an accelerator 2 that promotes the decomposition of hydrogen peroxide by ultraviolet irradiation. The accelerator tank 21 to be added to the previous waste liquid 1, the valve 19 for adjusting the addition amount of the accelerator 2, and the controller 33 are provided. The control device 33 compares the concentration measured by the measuring device 18 with the reference value of the concentration, and controls the operation of the valve 19 when the measured concentration exceeds the reference value, and promotes to the waste liquid 1. The amount of agent 2 added is controlled. More specifically, in this case, the addition of the accelerator 2 by the valve 19 and the accelerator tank 21 is started, or the addition amount of the accelerator 2 to the waste liquid 1 when the addition has already been performed. Increase. The accelerator tank 21 is connected to the storage tank 12, and the accelerator 2 is added to the waste liquid 1 in the storage tank 12. The apparatus 53 includes a treatment tank 14 as an ultraviolet irradiation mechanism, a measurement apparatus 18 as a measurement mechanism, a valve 19 and a promoter tank 21 as the accelerator addition mechanism (C), and a promoter control mechanism (C). And a control device 33.

廃液1は、導入管11を通して貯留槽12に送られた後、ポンプPにより、配管13を通して処理槽14に送られる。処理槽14では、廃液1に紫外線を照射して当該廃液に含まれる過酸化水素を分解する工程(照射工程)が実施される。貯留槽12において廃液1に促進剤2が添加されていれば、促進剤2が混合した廃液1に対して照射工程が実施される。照射工程を経た廃液1は、排出管15を通して装置51外に送り出される。その際、排出管15の途中に設けられた測定装置18によって、照射工程を経た廃液1における過酸化水素の濃度が測定される(測定工程)。制御装置33は、上述した制御を行う(制御工程)。   The waste liquid 1 is sent to the storage tank 12 through the introduction pipe 11 and then sent to the treatment tank 14 through the pipe 13 by the pump P. In the treatment tank 14, a step (irradiation step) of irradiating the waste liquid 1 with ultraviolet rays to decompose hydrogen peroxide contained in the waste liquid is performed. If the accelerator 2 is added to the waste liquid 1 in the storage tank 12, an irradiation process is implemented with respect to the waste liquid 1 which the accelerator 2 mixed. The waste liquid 1 that has undergone the irradiation process is sent out of the apparatus 51 through the discharge pipe 15. At that time, the concentration of hydrogen peroxide in the waste liquid 1 that has undergone the irradiation process is measured by a measuring device 18 provided in the middle of the discharge pipe 15 (measuring process). The control device 33 performs the above-described control (control process).

装置53の起動時、あるいは貯留槽12内の廃液1に含まれる過酸化水素の濃度が高くなった場合に、処理槽14における過酸化水素の分解・除去が、望むレベルにまで達しないことがある。このとき、装置53ならびに装置53において実施される上記処理方法では、バルブ19を作動させて、促進剤槽21から促進剤2を廃液1に添加し、促進剤2が混合した廃液1に紫外線を照射して、照射工程を実施できる。すなわち、廃液1に含まれる過酸化水素の分解がより確実になる。   When the apparatus 53 is started up or when the concentration of hydrogen peroxide contained in the waste liquid 1 in the storage tank 12 becomes high, decomposition / removal of hydrogen peroxide in the treatment tank 14 may not reach a desired level. is there. At this time, in the apparatus 53 and the processing method implemented in the apparatus 53, the valve 19 is operated, the accelerator 2 is added from the accelerator tank 21 to the waste liquid 1, and the waste liquid 1 mixed with the accelerator 2 is irradiated with ultraviolet rays. Irradiation can be performed. That is, the decomposition of hydrogen peroxide contained in the waste liquid 1 becomes more reliable.

制御装置33(制御工程)で対比される「基準値」は、装置53のユーザーが任意に設定できる。基準値は、例えば、廃液1からの酸または塩基の再利用時、あるいは廃液1の放流時に要求される過酸化水素の上限濃度である。   The “reference value” to be compared in the control device 33 (control process) can be arbitrarily set by the user of the device 53. The reference value is, for example, the upper limit concentration of hydrogen peroxide required when the acid or base from the waste liquid 1 is reused or when the waste liquid 1 is discharged.

装置53ならびに装置53において実施される上記処理方法では、測定装置18によって測定された、照射工程を経た廃液1の過酸化水素の濃度が基準値を超える場合に、制御装置33によって、促進剤添加機構による促進剤2の添加が始まるか、あるいは促進剤2の添加量が増加させられる。ここで、装置53の具体的な構成によっては、促進剤2の添加が始まってから、あるいは促進剤2の添加量が増加してから実際にその効果が得られるまで、より具体的には、測定装置18によって測定される過酸化水素の濃度が下がり始め、基準値以下となるまでに、タイムラグが生じることがある。このようなときに、基準値を上記上限濃度に設定していると、一時的に当該上限濃度を超える過酸化水素濃度を有する廃液が装置53から排出されることがある。このような排出が問題となる場合には、上記上限濃度から一定の値を差し引いた濃度を、基準値としてもよい。   In the apparatus 53 and the processing method implemented in the apparatus 53, when the concentration of hydrogen peroxide in the waste liquid 1 after the irradiation process measured by the measuring apparatus 18 exceeds the reference value, the controller 33 adds the accelerator. Addition of accelerator 2 by the mechanism begins or the amount of accelerator 2 added is increased. Here, depending on the specific configuration of the device 53, more specifically, until the effect is actually obtained after the addition of the accelerator 2 is started or the amount of the accelerator 2 is increased. There may be a time lag until the concentration of hydrogen peroxide measured by the measuring device 18 starts to decrease and falls below the reference value. In such a case, if the reference value is set to the upper limit concentration, waste liquid having a hydrogen peroxide concentration that temporarily exceeds the upper limit concentration may be discharged from the apparatus 53. When such discharge becomes a problem, a concentration obtained by subtracting a certain value from the upper limit concentration may be used as a reference value.

装置53ならびに装置53において実施される上記方法では、促進剤2の添加量はゼロでありうるし、常に促進剤2の添加が行われてもよい。   In the apparatus 53 and the above-described method performed in the apparatus 53, the amount of the accelerator 2 added may be zero, and the accelerator 2 may always be added.

装置53ならびに装置53において実施される上記方法では、測定工程において(測定装置18において)、照射工程を経た(処理槽14を経た)廃液1における過酸化水素の濃度を連続的に測定し、制御工程において(制御装置33において)、測定された当該濃度と基準値とを連続的に対比して、上述した促進剤2の添加を連続的に制御してもよい。この場合、処理すべき廃液1に含まれる過酸化水素の濃度が経時的に変化する場合にも、当該変化に対する処理の追従性が向上し、過酸化水素のさらに安定した分解・除去が可能となる。   In the apparatus 53 and the method implemented in the apparatus 53, in the measurement process (in the measurement apparatus 18), the concentration of hydrogen peroxide in the waste liquid 1 that has undergone the irradiation process (through the treatment tank 14) is continuously measured and controlled. In the process (in the control device 33), the addition of the accelerator 2 described above may be continuously controlled by continuously comparing the measured concentration with a reference value. In this case, even when the concentration of hydrogen peroxide contained in the waste liquid 1 to be treated changes with time, the followability of the treatment to the change is improved, and hydrogen peroxide can be more stably decomposed and removed. Become.

促進剤2は、特に限定されない。促進剤2は、過酸化水素を消費する物質、または紫外線の照射によって過酸化水素が分解して生じたヒドロキシラジカル(・OH)を消費する物質を含む。促進剤2は、例えばオゾンである。オゾンは、ヒドロキシラジカルを消費する。   The accelerator 2 is not particularly limited. The accelerator 2 includes a substance that consumes hydrogen peroxide, or a substance that consumes hydroxy radicals (.OH) generated by the decomposition of hydrogen peroxide by irradiation with ultraviolet rays. The accelerator 2 is, for example, ozone. Ozone consumes hydroxy radicals.

紫外線の照射によって過酸化水素が分解して生じたヒドロキシラジカル(・OH)は有機物を分解する。すなわち、有機物によっても、ヒドロキシラジカル(・OH)は消費される。このため、促進剤2は、有機物を含んでいてもよく、具体的には、有機物を含む溶液であってもよい。有機物は、例えば、有機溶剤、樹脂であり、樹脂には、半導体素子の製造工程から排出されるレジスト材料が含まれる。   Hydroxy radicals (.OH) generated by decomposition of hydrogen peroxide by ultraviolet irradiation decompose organic substances. That is, hydroxy radicals (.OH) are consumed also by organic substances. For this reason, the accelerator 2 may contain an organic substance, specifically, a solution containing an organic substance. The organic substance is, for example, an organic solvent or a resin, and the resin includes a resist material discharged from the semiconductor element manufacturing process.

促進剤2が有機物を含む場合、廃液1に含まれる酸または塩基の再利用を考慮すると、当該有機物の量は、照射工程においてヒドロキシラジカルとの反応によってほぼ消費される程度の量が好ましい。当該量は、濃度にして数ppm程度である。処理すべき廃液1がレジスト剥離工程から排出された廃液であるなど、最初から有機物を含む場合、有機物を含む促進剤2を添加した後の廃液1における有機物の濃度に注意することが好ましい。もちろん、本発明の処理方法または処理装置を経た廃液に有機物が含まれることが問題とならない場合には、単にヒドロキシラジカルを消費して過酸化水素の分解を促進させることに着目して、有機物を含む促進剤2を用いうる。   When the accelerator 2 contains an organic substance, considering the reuse of the acid or base contained in the waste liquid 1, the amount of the organic substance is preferably such that it is almost consumed by the reaction with the hydroxy radical in the irradiation step. The amount is about several ppm in terms of concentration. When the waste liquid 1 to be treated contains an organic substance from the beginning such as a waste liquid discharged from the resist stripping process, it is preferable to pay attention to the concentration of the organic substance in the waste liquid 1 after the addition of the accelerator 2 containing the organic substance. Of course, when it does not matter that organic matter is contained in the waste liquid that has passed through the treatment method or treatment apparatus of the present invention, paying attention to simply accelerating the decomposition of hydrogen peroxide by consuming hydroxy radicals, Including accelerator 2 may be used.

促進剤2は、廃液1への紫外線の照射が完了する前の任意の時点で、処理すべき廃液1に添加できる。例えば、図6に示す装置54では、貯留槽12と処理槽14との間において、廃液1に促進剤2が添加される。図7に示す装置55では、処理槽14内の廃液1に促進剤2が添加される。   The accelerator 2 can be added to the waste liquid 1 to be treated at any point before the irradiation of the waste liquid 1 with ultraviolet rays is completed. For example, in the apparatus 54 shown in FIG. 6, the accelerator 2 is added to the waste liquid 1 between the storage tank 12 and the processing tank 14. In the apparatus 55 shown in FIG. 7, the accelerator 2 is added to the waste liquid 1 in the treatment tank 14.

本発明の処理方法は、上記(a)〜(c)の各々を実施する制御工程を、任意の組み合わせで含んでもよい。本発明の処理方法は、上記(a)〜(c)の全てを実施する制御工程を含んでもよい。このような処理方法を実施する本発明の処理装置の一例を図8に示す。図8の装置56は、紫外線照射機構と、測定機構と、上記(A)〜(C)の全ての機構と、を備える。図8の符号34は、環流制御機構、紫外線制御機構および促進剤制御機構を兼ねる制御装置である。   The processing method of the present invention may include control steps for performing each of the above (a) to (c) in any combination. The treatment method of the present invention may include a control step for performing all of the above (a) to (c). An example of the processing apparatus of the present invention for carrying out such a processing method is shown in FIG. The apparatus 56 of FIG. 8 includes an ultraviolet irradiation mechanism, a measurement mechanism, and all the mechanisms (A) to (C). Reference numeral 34 in FIG. 8 is a control device that also serves as a reflux control mechanism, an ultraviolet light control mechanism, and an accelerator control mechanism.

本発明の処理装置は、上記(A)〜(C)の機構を、任意の組み合わせで備えてもよい。   The processing apparatus of this invention may be equipped with the mechanism of said (A)-(C) in arbitrary combinations.

本発明の処理方法および処理装置は、酸または塩基と過酸化水素とを含む廃液における過酸化水素を分解・除去して、当該酸または塩基の再利用を可能とする。本発明の処理方法および処理装置により、例えば、半導体素子の製造コストの低減および環境保全を図ることができる。   The treatment method and the treatment apparatus of the present invention make it possible to decompose and remove hydrogen peroxide in a waste liquid containing an acid or base and hydrogen peroxide and to reuse the acid or base. With the processing method and processing apparatus of the present invention, for example, the manufacturing cost of semiconductor elements can be reduced and the environment can be protected.

1 廃液
2 促進剤
11 導入管
12 貯留槽
13 配管
14、14A、14B 処理槽
15 排出管
16 バルブ
17 環流管
18 測定装置
19 バルブ
21 促進剤槽
31,32,33,34 制御装置
41 (紫外線の)光源
42 配管
51,52,53,54,55,56 (廃液処理)装置
DESCRIPTION OF SYMBOLS 1 Waste liquid 2 Promoter 11 Introducing pipe 12 Storage tank 13 Piping 14, 14A, 14B Treatment tank 15 Discharge pipe 16 Valve 17 Recirculation pipe 18 Measuring device 19 Valve 21 Promoter tank 31, 32, 33, 34 Control device 41 (ultraviolet light ) Light source 42 Piping 51, 52, 53, 54, 55, 56 (Waste liquid treatment) device

Claims (10)

酸または塩基と過酸化水素とを含む廃液に紫外線を照射して、前記廃液に含まれる過酸化水素を分解する照射工程と、
前記照射工程を経た前記廃液における過酸化水素の濃度を測定する測定工程と、
前記測定工程において測定された前記過酸化水素の濃度と、当該濃度の基準値とを対比して、前記測定された濃度が前記基準値を超える場合に、以下の(a)、(b)および(c)から選ばれる少なくとも一つを実施する、制御工程と、
を含む、酸または塩基と過酸化水素とを含む廃液の処理方法。
(a)前記照射工程を経た前記廃液の少なくとも一部の環流と、前記照射工程が実施される前の前記廃液に対する、環流させた前記廃液の混合と、を開始する、または
前記環流および混合が既に行われているときに、前記照射工程を経た前記廃液の当該環流および混合の量を増加させる、
(b)前記照射工程における前記廃液への紫外線の照射条件を、当該廃液に含まれる過酸化水素の分解が促進される方向に変化させる、
(c)前記照射工程が実施される前の前記廃液に対して、紫外線の照射による過酸化水素の分解を促進する促進剤の添加を開始する、または
前記添加が既に行われているときに、前記照射工程が実施される前の前記廃液に対する前記促進剤の添加の量を増加させる。
An irradiation step of irradiating a waste liquid containing an acid or base and hydrogen peroxide with ultraviolet rays to decompose hydrogen peroxide contained in the waste liquid;
A measuring step of measuring the concentration of hydrogen peroxide in the waste liquid that has undergone the irradiation step;
When the concentration of hydrogen peroxide measured in the measurement step is compared with the reference value of the concentration, and the measured concentration exceeds the reference value, the following (a), (b) and A control step of performing at least one selected from (c);
A method for treating a waste liquid containing acid or base and hydrogen peroxide.
(A) starting at least a part of the reflux of the waste liquid that has undergone the irradiation step and mixing of the waste liquid that has been refluxed with respect to the waste liquid before the irradiation step is performed, or Increasing the amount of the reflux and mixing of the waste liquid that has undergone the irradiation step when already done,
(B) changing the irradiation condition of the ultraviolet light to the waste liquid in the irradiation step in a direction in which the decomposition of hydrogen peroxide contained in the waste liquid is promoted;
(C) To start the addition of an accelerator that promotes the decomposition of hydrogen peroxide by ultraviolet irradiation with respect to the waste liquid before the irradiation step, or when the addition has already been performed, The amount of the accelerator added to the waste liquid before the irradiation step is performed is increased.
前記(b)が、
前記照射工程において、単位量の前記廃液に対する紫外線の照射量を多くする、である請求項1に記載の処理方法。
(B)
The processing method according to claim 1, wherein, in the irradiation step, the irradiation amount of ultraviolet light with respect to the waste liquid of unit amount is increased.
前記促進剤が、有機物を含む溶液またはオゾンである請求項1に記載の処理方法。   The processing method according to claim 1, wherein the accelerator is a solution containing organic matter or ozone. 前記酸が、硫酸、塩酸またはフッ酸である請求項1に記載の処理方法。   The treatment method according to claim 1, wherein the acid is sulfuric acid, hydrochloric acid, or hydrofluoric acid. 前記塩基が、アンモニアである請求項1に記載の処理方法。   The processing method according to claim 1, wherein the base is ammonia. 酸または塩基と過酸化水素とを含む廃液に紫外線を照射する紫外線照射機構と、
前記紫外線を照射した後の前記廃液における過酸化水素の濃度を測定する測定機構と、
以下の(A)、(B)および(C)から選ばれる少なくとも一つと、を備える、酸または塩基と過酸化水素とを含む廃液の処理装置。
(A)前記紫外線を照射した後の前記廃液の少なくとも一部を環流させて、前記紫外線が照射される前の前記廃液に混合する環流機構、ならびに
前記測定機構において測定された前記過酸化水素の濃度と、当該濃度の基準値とを対比して、前記測定された濃度が前記基準値を超える場合に、
前記環流機構による前記環流および混合を開始するか、または前記環流および混合が既に行われているときに前記環流および混合させる前記廃液の量を増加させる、環流制御機構、
(B)前記測定機構において測定された前記過酸化水素の濃度と、当該濃度の基準値とを対比して、前記測定された濃度が前記基準値を超える場合に、
前記紫外線照射機構による前記廃液への紫外線の照射条件を、当該廃液に含まれる過酸化水素の分解が促進される方向に変化させる紫外線制御機構、
(C)前記紫外線が照射される前の前記廃液に対して、紫外線の照射による過酸化水素の分解を促進する促進剤を添加する促進剤添加機構、ならびに
前記測定機構において測定された前記過酸化水素の濃度と、当該濃度の基準値とを対比して、前記測定された濃度が前記基準値を超える場合に、
前記促進剤添加機構による前記促進剤の添加を開始するか、または前記促進剤の添加が既に行われているときに前記促進剤を添加する量を増加させる、促進剤制御機構。
An ultraviolet irradiation mechanism for irradiating the waste liquid containing acid or base and hydrogen peroxide with ultraviolet rays;
A measurement mechanism for measuring the concentration of hydrogen peroxide in the waste liquid after irradiation with the ultraviolet light;
A waste liquid treatment apparatus comprising an acid or a base and hydrogen peroxide, comprising at least one selected from the following (A), (B), and (C).
(A) A reflux mechanism that circulates at least a part of the waste liquid after irradiation with the ultraviolet rays and mixes with the waste liquid before the ultraviolet irradiation, and the hydrogen peroxide measured in the measurement mechanism When the measured concentration exceeds the reference value by comparing the concentration with the reference value of the concentration,
A recirculation control mechanism that initiates the recirculation and mixing by the recirculation mechanism or increases the amount of the waste liquid to be recirculated and mixed when the recirculation and mixing are already performed;
(B) When the concentration of the hydrogen peroxide measured by the measurement mechanism is compared with a reference value of the concentration, and the measured concentration exceeds the reference value,
An ultraviolet ray control mechanism for changing the irradiation condition of the ultraviolet ray to the waste liquid by the ultraviolet ray irradiation mechanism in a direction in which decomposition of hydrogen peroxide contained in the waste liquid is promoted;
(C) an accelerator addition mechanism for adding an accelerator that promotes decomposition of hydrogen peroxide by irradiation of ultraviolet rays to the waste liquid before being irradiated with the ultraviolet rays, and the peroxidation measured in the measurement mechanism When the measured concentration exceeds the reference value by comparing the concentration of hydrogen with the reference value of the concentration,
An accelerator control mechanism that starts the addition of the accelerator by the accelerator addition mechanism or increases the amount of the accelerator added when the accelerator is already added.
前記紫外線の照射条件が、単位量の前記廃液に対する紫外線の照射量であり、
前記紫外線制御機構は、前記測定された濃度が前記基準値を超える場合に、前記紫外線照射機構による当該紫外線の照射量を多くする、請求項6に記載の処理装置。
The irradiation condition of the ultraviolet ray is an irradiation amount of the ultraviolet ray for the unit amount of the waste liquid,
The processing apparatus according to claim 6, wherein the ultraviolet ray control mechanism increases an amount of irradiation of the ultraviolet ray by the ultraviolet ray irradiation mechanism when the measured concentration exceeds the reference value.
前記促進剤が、有機物を含む溶液またはオゾンである請求項6に記載の処理装置。   The processing apparatus according to claim 6, wherein the accelerator is a solution containing organic matter or ozone. 前記酸が、硫酸、塩酸またはフッ酸である請求項6に記載の処理装置。   The processing apparatus according to claim 6, wherein the acid is sulfuric acid, hydrochloric acid, or hydrofluoric acid. 前記塩基が、アンモニアである請求項6に記載の処理装置。
The processing apparatus according to claim 6, wherein the base is ammonia.
JP2010074592A 2010-03-29 2010-03-29 Method and apparatus for treating waste liquid containing acid or base and hydrogen peroxide Expired - Fee Related JP5581090B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2010074592A JP5581090B2 (en) 2010-03-29 2010-03-29 Method and apparatus for treating waste liquid containing acid or base and hydrogen peroxide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2010074592A JP5581090B2 (en) 2010-03-29 2010-03-29 Method and apparatus for treating waste liquid containing acid or base and hydrogen peroxide

Publications (2)

Publication Number Publication Date
JP2011206637A true JP2011206637A (en) 2011-10-20
JP5581090B2 JP5581090B2 (en) 2014-08-27

Family

ID=44938347

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2010074592A Expired - Fee Related JP5581090B2 (en) 2010-03-29 2010-03-29 Method and apparatus for treating waste liquid containing acid or base and hydrogen peroxide

Country Status (1)

Country Link
JP (1) JP5581090B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013158722A (en) * 2012-02-07 2013-08-19 Sharp Corp Pipe member for sterilization and sterilizing apparatus with the same
WO2015125739A1 (en) * 2014-02-24 2015-08-27 倉敷紡績株式会社 Hydroxyl radical-containing water supply device and hydroxyl radical-containing water supply method

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0971405A (en) * 1995-09-04 1997-03-18 Mitsubishi Gas Chem Co Inc Purification of hydrogen peroxide
JPH10151451A (en) * 1996-11-21 1998-06-09 Akira Fujishima Method for removing hydrogen peroxide by photocatalyst and light irradiation
JP2000015196A (en) * 1998-06-30 2000-01-18 Nec Corp Washing of substrate and device for washing substrate
JP2004275969A (en) * 2003-03-18 2004-10-07 Kurabo Ind Ltd Apparatus and method for treating wastewater

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0971405A (en) * 1995-09-04 1997-03-18 Mitsubishi Gas Chem Co Inc Purification of hydrogen peroxide
JPH10151451A (en) * 1996-11-21 1998-06-09 Akira Fujishima Method for removing hydrogen peroxide by photocatalyst and light irradiation
JP2000015196A (en) * 1998-06-30 2000-01-18 Nec Corp Washing of substrate and device for washing substrate
JP2004275969A (en) * 2003-03-18 2004-10-07 Kurabo Ind Ltd Apparatus and method for treating wastewater

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013158722A (en) * 2012-02-07 2013-08-19 Sharp Corp Pipe member for sterilization and sterilizing apparatus with the same
WO2015125739A1 (en) * 2014-02-24 2015-08-27 倉敷紡績株式会社 Hydroxyl radical-containing water supply device and hydroxyl radical-containing water supply method
JPWO2015125739A1 (en) * 2014-02-24 2017-03-30 倉敷紡績株式会社 Hydroxyl radical-containing water supply device and hydroxyl radical-containing water supply method

Also Published As

Publication number Publication date
JP5581090B2 (en) 2014-08-27

Similar Documents

Publication Publication Date Title
WO2018092832A1 (en) Water treatment method and device
WO2018092831A1 (en) Water treatment method and device
KR20130012886A (en) Photocatalytic reactor and treatment method for pollutant using thereof
JPH1133567A (en) Ozone decomposing method and apparatus
JP5581090B2 (en) Method and apparatus for treating waste liquid containing acid or base and hydrogen peroxide
JP4224817B2 (en) Method for treating 1,4-dioxane
JP2004241726A (en) Method and device for treating resist
JPH1199394A (en) Method for removing organic matter in water
EP0242941B1 (en) Process and apparatus for the deodorization of air
JP2007021290A (en) Method and apparatus for treating exhaust gas
JP2003266088A (en) Ozone accelerated oxidation water treatment system together using ultraviolet rays
JP2006082081A (en) Accelerated oxidation treatment apparatus using ozone and photocatalyst
JP2017202474A (en) Ozone dissolved water production apparatus
JP2000263072A (en) Method and apparatus for treating wastewater
JP4569884B2 (en) Method and apparatus for treating organic matter in water
JP2008173617A (en) Water treatment apparatus and water treating method
WO2003051777A1 (en) Method and apparatus for treating waste ozone water and apparatus for treatment with ozone
JP5755590B2 (en) Water treatment method
WO2017104370A1 (en) Cleaning method and cleaning device
KR101250811B1 (en) Ozone on-line injector
JP2002307083A (en) Accelerated oxidation treatment apparatus
US20220119294A1 (en) System and method for treating contaminated water
KR100479321B1 (en) System for device treating organic materials
RU94562U1 (en) DEVICE FOR TREATMENT OF LIQUIDS BY UV RADIATION
JP2009112953A (en) Method and apparatus for treating water

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20130214

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20140219

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20140225

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20140408

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20140430

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20140616

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: 20140708

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20140714

R151 Written notification of patent or utility model registration

Ref document number: 5581090

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R151

LAPS Cancellation because of no payment of annual fees