WO2017033825A1 - Water treatment agent composition for cyanogen-containing waste water - Google Patents

Water treatment agent composition for cyanogen-containing waste water Download PDF

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Publication number
WO2017033825A1
WO2017033825A1 PCT/JP2016/074086 JP2016074086W WO2017033825A1 WO 2017033825 A1 WO2017033825 A1 WO 2017033825A1 JP 2016074086 W JP2016074086 W JP 2016074086W WO 2017033825 A1 WO2017033825 A1 WO 2017033825A1
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water treatment
agent composition
treatment agent
cyanide
water
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PCT/JP2016/074086
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French (fr)
Japanese (ja)
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平嶋英則
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株式会社片山化学工業研究所
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Priority claimed from JP2016120147A external-priority patent/JP6797370B2/en
Application filed by 株式会社片山化学工業研究所 filed Critical 株式会社片山化学工業研究所
Priority to CN201680048702.4A priority Critical patent/CN107922225B/en
Priority to KR1020187007286A priority patent/KR102526222B1/en
Publication of WO2017033825A1 publication Critical patent/WO2017033825A1/en

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds

Definitions

  • the present disclosure relates to a water treatment composition for cyanide-containing wastewater and a method for treating cyanide-containing wastewater.
  • cyan Since cyan has a strong adverse effect on the ecosystem, cyanate-containing wastewater cannot be released into nature as it is.
  • drainage standards are established based on the Water Pollution Control Law, and cyan removal processing is performed to satisfy this standard (1 mg / L or less), and wastewater cannot be discharged unless it is detoxified wastewater. ing.
  • additional drainage standards that are even lower than the above-mentioned drainage standards due to regulations.
  • Patent Document 1 discloses a reaction equivalent with cyanide in waste water without substantially adding zinc and ozone treatment to waste water containing free cyanide and cyanate complex salt. Disclosed is a treatment method characterized by adding the above divalent copper salt and a reducing agent to form a hardly soluble precipitate and separating it.
  • Patent Document 2 discloses that after adding a ferric salt and a cuprous salt in an amount capable of removing cyan contained in cyanine-containing wastewater in a weight ratio of 16: 1 to 1: 1, Disclosed is a method for treating cyanide-containing wastewater, characterized in that the pH of the wastewater is adjusted to 6 to 8, the generated water-insoluble salt is removed from the wastewater, and cyan in the wastewater is removed.
  • JP-A-2-48315 Japanese Patent No. 4639309
  • cyan-containing waste liquid It is a monovalent copper salt that forms a hardly soluble precipitate with cyanide in a waste liquid containing free cyanide and cyanate complex salt (hereinafter referred to as “cyan-containing waste liquid”). Therefore, when a water treatment agent composition containing a monovalent copper salt was prepared in order to easily treat wastewater containing cyanide, precipitation, dust, or both occurred, and stability improvement was necessary as a formulation. The problem of being was found.
  • the present disclosure provides a water treatment agent composition for cyanide-containing wastewater containing a monovalent copper salt with improved stability in one or more embodiments.
  • the present disclosure in one aspect, is a water treatment composition for cyanide-containing wastewater, (A) cuprous chloride, (B) at least one selected from the group consisting of alkali metal chlorides, alkali metal bromides, alkaline earth metal chlorides, and alkaline earth metal bromides, and (C) contains an inorganic acid and / or an organic acid,
  • the water treatment agent composition wherein the content of the (C) inorganic acid and / or organic acid in the water treatment agent composition is 10% by weight or less, and the pH of the water treatment agent composition is 2 or less.
  • the water treatment agent composition according to the present disclosure is added to cyanide-containing wastewater so as to have cuprous chloride having a reaction equivalent to or higher than cyanide in the wastewater.
  • the present invention relates to a method for treating cyanogen-containing wastewater, which comprises producing a soluble substance and separating the hardly soluble substance.
  • the water treatment agent composition for cyanide-containing wastewater of the present disclosure can exhibit an effect that precipitation and turbidity are suppressed and stability as a preparation is improved. In one or a plurality of embodiments, the water treatment agent composition for cyanide-containing wastewater of the present disclosure can further exhibit an effect that handling properties are improved.
  • FIG. 1 is a schematic diagram showing an example of a cyan-containing wastewater treatment apparatus used in a method for treating cyan-containing wastewater.
  • the problem that turbidity and precipitation occur when a preparation containing cuprous salt is prepared to treat cyanide-containing wastewater is solved by adding a predetermined amount of alkali metal chloride and acid. Based on the knowledge that it can.
  • Cyanide wastewater examples of the cyanate-containing wastewater to be treated in the present disclosure include wastewater discharged from an iron factory, a chemical factory, a plating factory, a coke manufacturing factory, a metal surface treatment factory, and the like. Cyan-containing wastewater containing a cyanide compound, cyanide, cyanide complex salt, cyano complex ion and the like can be mentioned.
  • the water treatment agent composition according to the present disclosure can suitably perform treatment of cyanide-containing wastewater having a strong buffering action such as coke oven wastewater.
  • Component A in the water treatment agent composition according to the present disclosure is cuprous chloride.
  • Monovalent copper ions come into contact with free cyanide, cyanide complex salts, and the like in wastewater to form hardly soluble substances.
  • the poorly soluble material is a precipitate in one or more embodiments. By removing the hardly soluble substance, cyan can be removed from the wastewater.
  • the content of component A in the water treatment agent composition according to the present disclosure is preferably 1.5% by weight or more, more preferably 5% by weight, from the viewpoint of improving the stability of the composition. % To 15% by weight.
  • Component B in the water treatment agent composition according to the present disclosure is at least one selected from the group consisting of alkali metal chlorides, alkali metal bromides, alkaline earth metal chlorides, and alkaline earth metal bromides. Examples include sodium chloride, calcium chloride, magnesium chloride, sodium bromide, and magnesium bromide. Component B may be one type or two or more types. In one or a plurality of embodiments, Component B in the water treatment agent composition according to the present disclosure is selected from the group consisting of alkali metal chlorides and alkaline earth metal chlorides from the viewpoint of improving the stability of the composition. At least one is preferred. Alkali metal chlorides and alkaline earth metal chlorides include sodium chloride, calcium chloride, and magnesium chloride in one or more embodiments.
  • the content of Component B in the water treatment agent composition according to the present disclosure is preferably 1% by weight or more and 45% by weight or less, more preferably, from the viewpoint of improving the stability of the composition. 1% by weight or more and 35% by weight or less.
  • Component C in the water treatment agent composition according to the present disclosure is an inorganic acid, an organic acid, or a combination of an inorganic acid and an organic acid.
  • Component C may be one type or two or more types.
  • the inorganic acid include hydrochloric acid, nitric acid, and sulfuric acid in one or a plurality of embodiments.
  • the organic acid include, in one or a plurality of embodiments, an oxycarboxylic acid, a polyvalent carboxylic acid, an aminopolycarboxylic acid, And amino acids.
  • the content of Component C in the water treatment agent composition according to the present disclosure is preferably such that the pH of the water treatment agent composition is 2 or less from the viewpoint of improving the stability of the composition. Is the amount.
  • the content of component C in the water treatment agent composition according to the present disclosure is preferably a concentration that is not designated as a deleterious substance, more preferably from the viewpoint of improving the handleability of the composition. It is 10 wt% or less, more preferably 5 wt% or less, and even more preferably 1 wt% or less.
  • the water treatment agent composition according to the present disclosure is a compound that forms sodium sulfite as a component D or sodium sulfite in an aqueous solution (such as sodium bisulfite) from the viewpoint of improving the stability of the composition. ) May be contained.
  • the content of component D in the water treatment agent composition according to the present disclosure is preferably 1% by weight or less, more preferably 0.1% by weight, from the viewpoint of improving the stability of the composition. % Or less, more preferably 0.01% by weight or less, and still more preferably 0.005% by weight or less.
  • the water treatment composition according to the present disclosure may be water (component E) other than the components A to C or A to D described above.
  • the water industrial water, tap water, distilled water, ion-exchanged water, ultrapure water, or the like can be used.
  • the water treatment agent composition according to the present disclosure may include the following other components in addition to the components A to E within a range not impairing the stability of the composition.
  • the water treatment agent composition according to the present disclosure may be used in combination with known agents such as a rust inhibitor, a corrosion inhibitor, a scale dispersant, and a slime control agent as long as the effects of the present invention are not impaired.
  • the water treatment agent composition according to the present disclosure has a pH of 2 or less, preferably 1.7 or less, from the viewpoint of improving the stability of the composition.
  • the water treatment composition according to the present disclosure may be distributed as a concentrate in one or a plurality of embodiments.
  • the concentrate of the water treatment composition according to the present disclosure can be used by diluting the components A to D so as to have the above-described content at the time of use.
  • the water treatment composition according to the present disclosure can be prepared by mixing the above components A to E.
  • a bubbling treatment with nitrogen gas may be performed in order to obtain a more stable water treatment agent composition.
  • the water treatment agent composition according to the present disclosure may be stored in a container such as a polytank, or may be used in a state stored in a storage tank or container. .
  • a container such as a polytank
  • the space in the container may be purged (replaced) with an inert gas such as nitrogen or argon.
  • positioned in the container purged with the inert gas as one or some embodiment of the water treatment agent composition which concerns on this indication is mentioned.
  • the water treatment agent composition according to the present disclosure is introduced into a storage tank, a container, or the like from the viewpoint of being usable in a state where the stability is maintained for a longer period of time by putting it in a storage tank, a container, etc. After that, the space in the storage tank or container may be brought into a slightly pressurized state (1 to 5 kPa) from the atmospheric pressure with an inert gas such as nitrogen or argon.
  • the slightly pressurized state can be maintained by attaching a regulator (precision pressure regulator) and a flow meter with a needle valve to an inert gas cylinder arranged in a storage tank or a container. Therefore, the form arrange
  • the present disclosure relates, in one aspect, to a method for preparing a water treatment agent composition for cyanide-containing wastewater, which comprises mixing the above components A to C and optionally component D and / or component E.
  • a method for preparing a water treatment agent composition according to the present disclosure includes arranging a mixed composition in a container such as a polytank, and purging the container in which the composition is arranged with an inert gas. May include.
  • the method for preparing a water treatment agent composition according to the present disclosure is a composition obtained by mixing the above components A to C and, if necessary, the component D and / or the component E.
  • the inside of a space such as a storage tank or a container in which is placed may be made to be slightly pressurized from the atmospheric pressure by an inert gas.
  • Examples of the slightly pressurized state include, in one or a plurality of embodiments, a state in which 1 to 5 kPa or 2 to 5 kPa is pressurized from atmospheric pressure.
  • the water treatment agent composition according to the present disclosure can be used for cyan removal treatment of cyanide-containing wastewater. Accordingly, in one aspect, the present disclosure is a method for treating cyan-containing wastewater, and the water treatment according to the present disclosure is such that the cyan-containing wastewater has cuprous chloride having a reaction equivalent to or higher than cyan in the wastewater. Adding an agent composition to form a hardly soluble substance of cyanide and separating the hardly soluble substance.
  • the content of cyan in the cyan-containing wastewater to be treated in the treatment method according to the present disclosure is not particularly limited, but wastewater having a total cyan concentration of 2 to 100 mg / L can be suitably treated.
  • the water treatment agent composition according to the present disclosure is converted to cyanide-containing wastewater so as to be cuprous chloride having a reaction equivalent to or higher than cyanide.
  • the water treatment agent composition according to the present disclosure may be added to the cyanide-containing waste water so that cuprous chloride is 4 to 1000 mg / L, preferably 10 to 100 mg / L. Can be mentioned.
  • the water treatment method according to the present disclosure is configured such that a storage tank or a container into which the water treatment agent composition according to the present disclosure has been introduced is brought into a slightly pressurized state from an atmospheric pressure by an inert gas. In this state, the water treatment agent composition according to the present disclosure may be added to the cyanide-containing wastewater.
  • the cyan-containing wastewater treatment method according to the present disclosure will be specifically described with reference to a schematic diagram (FIG. 1) illustrating an example of a cyan wastewater treatment apparatus, but this aspect does not limit the present invention.
  • Cyanide wastewater to be treated (indicated by solid arrows in the figure) is measured for cyan concentration at point A, sent to the reaction treatment tank 1, and based on the measured values such as cyan concentration, the treating agent composition tank From 2 the water treatment agent composition according to the present disclosure is added.
  • the cyan-containing wastewater is stirred for a predetermined time while stirring in the reaction treatment tank 1, the cyan-containing wastewater containing the generated poorly water-soluble salt is sent to the thickener 3 from below the reaction treatment tank 1.
  • the solid content is recovered from below the thickener 3 by being precipitated by a formation reaction of a poorly water-soluble salt.
  • the supernatant is discharged from above the thickener 3, the cyan concentration of the supernatant is measured at point B, and it is confirmed that the measured value is the drainage standard value or the added drainage standard value or less. Drain the water. In addition, there is no problem in reusing the treated waste water.
  • the cyanide-containing wastewater treatment apparatus that can be used in the method for treating cyanide-containing wastewater according to the present disclosure basically includes an additive tank for adding the water treatment agent composition according to the present disclosure, a poorly water-soluble salt. It consists of a reaction tank for generating, a precipitation tank for recovering the poorly water-soluble salt, piping connecting them, stirring means, a pump, and the like. The reaction tank and the precipitation tank can also be used together. In such a case, an apparatus such as a thickener can be used.
  • the water treatment agent compositions of Examples were colored but transparent without precipitation or turbidity.
  • the concentration of cuprous chloride was 2% by weight or less, the clogging of the pump Turbidity and precipitation, which are feared to be insufficient in concentration, occurred, and some cuprous chlorides were hardly dissolved.
  • the composition was practically unusable.
  • the total cyanide concentration is 1 mg / L or less based on the drainage standard based on the Water Pollution Control Law. I was able to.

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  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
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Abstract

Provided is a water treatment agent composition for cyanogen-containing waste water, the water treatment agent composition having improved stability and containing a monovalent copper salt in one or a plurality of embodiments. The present invention relates to a water treatment agent composition for cyanogen-containing waste water, the water treatment agent composition containing: (A) cuprous chloride; (B) at least one selected from the group consisting of an alkali metal chloride, an alkali metal bromide, an alkaline earth metal chloride, and an alkaline earth metal bromide; and (C) inorganic acids and/or organic acids. The content of the (C) inorganic acids and/or organic acids in the water treatment agent composition is 10 weight% or less, and the pH of the water treatment agent composition is 2 or less.

Description

シアン含有廃水用の水処理剤組成物Water treatment composition for cyanide-containing wastewater
 本開示は、シアン含有廃水用の水処理剤組成物、及び、シアン含有処理廃水の処理方法に関する。 The present disclosure relates to a water treatment composition for cyanide-containing wastewater and a method for treating cyanide-containing wastewater.
 シアンは生態系に強い悪影響を及ぼすため、シアン含有廃水を自然界にそのまま放出することはできない。シアンについては水質汚濁防止法に基づき排水基準が定められており、この基準(1mg/L以下)を満たすようにシアン除去処理を行い、無害化した廃水でなければ下水などに排出できないことになっている。また、条例により、上記排水基準値よりもさらに低い上乗せ排水基準を定めている地域も数多くある。 Since cyan has a strong adverse effect on the ecosystem, cyanate-containing wastewater cannot be released into nature as it is. For cyanide, drainage standards are established based on the Water Pollution Control Law, and cyan removal processing is performed to satisfy this standard (1 mg / L or less), and wastewater cannot be discharged unless it is detoxified wastewater. ing. In addition, there are many areas that have established additional drainage standards that are even lower than the above-mentioned drainage standards due to regulations.
 シアン含有廃水中のシアンの除去処理方法として、特許文献1は、遊離シアン及びシアン錯塩を含有する廃水に、実質的に亜鉛の添加及びオゾン処理を行うことなく、廃水中のシアンとの反応当量以上の2価の銅塩及び還元剤を添加し、難溶性の沈殿を生成させて分離することを特徴とする処理方法を開示する。 As a method for removing cyan in waste water containing cyanide, Patent Document 1 discloses a reaction equivalent with cyanide in waste water without substantially adding zinc and ozone treatment to waste water containing free cyanide and cyanate complex salt. Disclosed is a treatment method characterized by adding the above divalent copper salt and a reducing agent to form a hardly soluble precipitate and separating it.
 また、特許文献2は、シアン含有廃水に、該廃水に含まれるシアンを除去し得る量の第二鉄塩及び第一銅塩を16:1~1:1の重量割合で添加した後、該廃水のpHを6~8に調整し、生成した水不溶性塩を廃水から除去して、該廃水中のシアンを除去することを特徴とするシアン含有廃水の処理方法を開示する。 Patent Document 2 discloses that after adding a ferric salt and a cuprous salt in an amount capable of removing cyan contained in cyanine-containing wastewater in a weight ratio of 16: 1 to 1: 1, Disclosed is a method for treating cyanide-containing wastewater, characterized in that the pH of the wastewater is adjusted to 6 to 8, the generated water-insoluble salt is removed from the wastewater, and cyan in the wastewater is removed.
特開平2-48315号公報JP-A-2-48315 特許第4639309号公報Japanese Patent No. 4639309
 遊離シアン及びシアン錯塩を含有する廃液(以下、「シアン含有廃液」という)で、シアンと難溶性の沈殿を形成するのは、一価の銅塩である。そこで、シアン含有廃水を簡便に処理するために、一価の銅塩を含有する水処理剤組成物を調製したところ、沈殿、にごり、又はその両方が発生し、製剤として安定性の向上が必要であるという問題が見出された。 It is a monovalent copper salt that forms a hardly soluble precipitate with cyanide in a waste liquid containing free cyanide and cyanate complex salt (hereinafter referred to as “cyan-containing waste liquid”). Therefore, when a water treatment agent composition containing a monovalent copper salt was prepared in order to easily treat wastewater containing cyanide, precipitation, dust, or both occurred, and stability improvement was necessary as a formulation. The problem of being was found.
 本開示は、一又は複数の実施形態において、安定性が向上した、一価の銅塩を含有するシアン含有廃水用の水処理剤組成物を提供する。 The present disclosure provides a water treatment agent composition for cyanide-containing wastewater containing a monovalent copper salt with improved stability in one or more embodiments.
 本開示は、一態様において、シアン含有廃水用の水処理剤組成物であって、
 (A)塩化第一銅、
 (B)アルカリ金属塩化物、アルカリ金属臭化物、アルカリ土類金属塩化物、及びアルカリ土類金属臭化物からなる群から選ばれる少なくとも1つ、並びに、
 (C)無機酸及び/又は有機酸
 を含有し、
 前記(C)無機酸及び/又は有機酸の前記水処理剤組成物における含有量が、10重量%以下であり、かつ、前記水処理剤組成物のpHが2以下である水処理剤組成物(以下、「本開示に係る水処理剤組成物」ともよぶ)に関する。
The present disclosure, in one aspect, is a water treatment composition for cyanide-containing wastewater,
(A) cuprous chloride,
(B) at least one selected from the group consisting of alkali metal chlorides, alkali metal bromides, alkaline earth metal chlorides, and alkaline earth metal bromides, and
(C) contains an inorganic acid and / or an organic acid,
The water treatment agent composition wherein the content of the (C) inorganic acid and / or organic acid in the water treatment agent composition is 10% by weight or less, and the pH of the water treatment agent composition is 2 or less. (Hereinafter also referred to as “water treatment agent composition according to the present disclosure”).
 本開示は、その他の一態様において、シアン含有廃水に、該廃水中のシアンとの反応当量以上の塩化第一銅となるように本開示に係る水処理剤組成物を添加し、シアンの難溶性物質を生成させ該難溶性物質を分離することを含む、シアン含有廃水の処理方法に関する。 In another aspect of the present disclosure, the water treatment agent composition according to the present disclosure is added to cyanide-containing wastewater so as to have cuprous chloride having a reaction equivalent to or higher than cyanide in the wastewater. The present invention relates to a method for treating cyanogen-containing wastewater, which comprises producing a soluble substance and separating the hardly soluble substance.
 本開示のシアン含有廃水用の水処理剤組成物は、一又は複数の実施形態において、沈殿及び濁りが抑制され、製剤としての安定性が向上するという効果を奏しうる。本開示のシアン含有廃水用の水処理剤組成物は、一又は複数の実施形態において、さらに、取扱性が向上するという効果を奏し得る。 In one or a plurality of embodiments, the water treatment agent composition for cyanide-containing wastewater of the present disclosure can exhibit an effect that precipitation and turbidity are suppressed and stability as a preparation is improved. In one or a plurality of embodiments, the water treatment agent composition for cyanide-containing wastewater of the present disclosure can further exhibit an effect that handling properties are improved.
図1は、シアン含有廃水の処理方法に用いられるシアン含有廃水の処理装置の一例を示す概略模式図である。FIG. 1 is a schematic diagram showing an example of a cyan-containing wastewater treatment apparatus used in a method for treating cyan-containing wastewater.
 本開示は、シアン含有廃水を処理するために第一銅塩を含有する製剤を調製した場合に濁りや沈殿が発生するという問題が、アルカリ金属塩化物及び酸を所定量含有させることにより解消されうるという知見に基づく。 In the present disclosure, the problem that turbidity and precipitation occur when a preparation containing cuprous salt is prepared to treat cyanide-containing wastewater is solved by adding a predetermined amount of alkali metal chloride and acid. Based on the knowledge that it can.
 [シアン含有廃水]
 本開示において処理対象となるシアン含有廃水としては、製鉄工場、化学工場、メッキ工場、コークス製造工場、金属表面処理工場などから排出される廃水が挙げられ、一又は複数の実施形態において、金属のシアン化合物、シアンイオン、シアン錯塩、シアノ錯イオンなどを含むシアン含有廃水が挙げられる。本開示に係る水処理剤組成物は、一又は複数の実施形態において、コークス炉廃水のような緩衝作用の強いシアン含有廃水の処理をも好適に行なうことができる。
[Cyanide wastewater]
Examples of the cyanate-containing wastewater to be treated in the present disclosure include wastewater discharged from an iron factory, a chemical factory, a plating factory, a coke manufacturing factory, a metal surface treatment factory, and the like. Cyan-containing wastewater containing a cyanide compound, cyanide, cyanide complex salt, cyano complex ion and the like can be mentioned. In one or a plurality of embodiments, the water treatment agent composition according to the present disclosure can suitably perform treatment of cyanide-containing wastewater having a strong buffering action such as coke oven wastewater.
 [成分A:塩化第一銅]
 本開示に係る水処理剤組成物における成分Aは、塩化第一銅である。一価の銅イオンは、廃水中の遊離シアンやシアン錯塩等と接触して難溶性物質を形成する。該難溶性物質は、一又は複数の実施形態において、沈殿である。該難溶性物質を除去することで、廃水中からシアンを除去できる。
[Component A: Cuprous chloride]
Component A in the water treatment agent composition according to the present disclosure is cuprous chloride. Monovalent copper ions come into contact with free cyanide, cyanide complex salts, and the like in wastewater to form hardly soluble substances. The poorly soluble material is a precipitate in one or more embodiments. By removing the hardly soluble substance, cyan can be removed from the wastewater.
 本開示に係る水処理剤組成物における成分Aの含有量は、一又は複数の実施形態において、該組成物の安定性向上の点から、好ましくは1.5重量%以上、より好ましくは5重量%以上15重量%以下である。 In one or more embodiments, the content of component A in the water treatment agent composition according to the present disclosure is preferably 1.5% by weight or more, more preferably 5% by weight, from the viewpoint of improving the stability of the composition. % To 15% by weight.
 [成分B:アルカリ金属塩化物等]
 本開示に係る水処理剤組成物における成分Bは、アルカリ金属塩化物、アルカリ金属臭化物、アルカリ土類金属塩化物、及びアルカリ土類金属臭化物からなる群から選ばれる少なくとも1つであり、例えば、塩化ナトリウム、塩化カルシウム、塩化マグネシウム、臭化ナトリウム、及び臭化マグネシウムなどが挙げられる。成分Bは一種類であってもよく、二種類以上であってもよい。本開示に係る水処理剤組成物における成分Bは、一又は複数の実施形態において、該組成物の安定性向上の点から、アルカリ金属塩化物及びアルカリ土類金属塩化物からなる群から選ばれる少なくとも1つであることが好ましい。アルカリ金属塩化物及びアルカリ土類金属塩化物としては、一又は複数の実施形態において、塩化ナトリウム、塩化カルシウム、及び塩化マグネシウムが挙げられる。
[Component B: Alkali metal chloride, etc.]
Component B in the water treatment agent composition according to the present disclosure is at least one selected from the group consisting of alkali metal chlorides, alkali metal bromides, alkaline earth metal chlorides, and alkaline earth metal bromides. Examples include sodium chloride, calcium chloride, magnesium chloride, sodium bromide, and magnesium bromide. Component B may be one type or two or more types. In one or a plurality of embodiments, Component B in the water treatment agent composition according to the present disclosure is selected from the group consisting of alkali metal chlorides and alkaline earth metal chlorides from the viewpoint of improving the stability of the composition. At least one is preferred. Alkali metal chlorides and alkaline earth metal chlorides include sodium chloride, calcium chloride, and magnesium chloride in one or more embodiments.
 本開示に係る水処理剤組成物における成分Bの含有量は、一又は複数の実施形態において、該組成物の安定性向上の点から、好ましくは1重量%以上45重量%以下、より好ましくは1重量%以上35重量%以下である。 In one or more embodiments, the content of Component B in the water treatment agent composition according to the present disclosure is preferably 1% by weight or more and 45% by weight or less, more preferably, from the viewpoint of improving the stability of the composition. 1% by weight or more and 35% by weight or less.
 [成分C:酸]
 本開示に係る水処理剤組成物における成分Cは、無機酸、有機酸、又は無機酸及び有機酸の組み合わせである。成分Cは一種類であってもよく、二種類以上であってもよい。無機酸としては、一又は複数の実施形態において、塩酸、硝酸、及び硫酸が挙げられ、有機酸としては、一又は複数の実施形態において、オキシカルボン酸、多価カルボン酸、アミノポリカルボン酸、及びアミノ酸が挙げられる。
[Component C: Acid]
Component C in the water treatment agent composition according to the present disclosure is an inorganic acid, an organic acid, or a combination of an inorganic acid and an organic acid. Component C may be one type or two or more types. Examples of the inorganic acid include hydrochloric acid, nitric acid, and sulfuric acid in one or a plurality of embodiments. Examples of the organic acid include, in one or a plurality of embodiments, an oxycarboxylic acid, a polyvalent carboxylic acid, an aminopolycarboxylic acid, And amino acids.
 本開示に係る水処理剤組成物における成分Cの含有量は、一又は複数の実施形態において、該組成物の安定性向上の点から、好ましくは該水処理剤組成物のpHが2以下となる量である。本開示に係る水処理剤組成物における成分Cの含有量は、一又は複数の実施形態において、該組成物の取扱性向上の点から、好ましくは劇物に指定されない濃度であり、より好ましくは10重量%以下、さらに好ましくは5重量%以下、さらにより好ましくは1重量%以下である。 In one or more embodiments, the content of Component C in the water treatment agent composition according to the present disclosure is preferably such that the pH of the water treatment agent composition is 2 or less from the viewpoint of improving the stability of the composition. Is the amount. In one or a plurality of embodiments, the content of component C in the water treatment agent composition according to the present disclosure is preferably a concentration that is not designated as a deleterious substance, more preferably from the viewpoint of improving the handleability of the composition. It is 10 wt% or less, more preferably 5 wt% or less, and even more preferably 1 wt% or less.
 [成分D:亜硫酸ナトリウム]
 本開示に係る水処理剤組成物は、一又は複数の実施形態において、該組成物の安定性向上の点から、成分Dとして亜硫酸ナトリウム又は水溶液中で亜硫酸ナトリウムを生成する化合物(重亜硫酸ナトリウムなど)を含有してもよい。
[Component D: Sodium sulfite]
In one or a plurality of embodiments, the water treatment agent composition according to the present disclosure is a compound that forms sodium sulfite as a component D or sodium sulfite in an aqueous solution (such as sodium bisulfite) from the viewpoint of improving the stability of the composition. ) May be contained.
 本開示に係る水処理剤組成物における成分Dの含有量は、一又は複数の実施形態において、該組成物の安定性向上の点から、好ましくは1重量%以下、より好ましくは0.1重量%以下、さらに好ましくは0.01重量%以下、さらにより好ましくは0.005重量%以下である。 In one or more embodiments, the content of component D in the water treatment agent composition according to the present disclosure is preferably 1% by weight or less, more preferably 0.1% by weight, from the viewpoint of improving the stability of the composition. % Or less, more preferably 0.01% by weight or less, and still more preferably 0.005% by weight or less.
 [成分E:水]
 本開示に係る水処理剤組成物は、上述の成分A~C又はA~D以外は水(成分E)であってよい。水は、工業用水、水道水、蒸留水、イオン交換水、又は超純水等が使用され得る。あるいは、本開示に係る水処理剤組成物は、該組成物の安定性を阻害しない範囲で、成分A~E以外に下記のその他の成分を含んでもよい。
[Component E: Water]
The water treatment composition according to the present disclosure may be water (component E) other than the components A to C or A to D described above. As the water, industrial water, tap water, distilled water, ion-exchanged water, ultrapure water, or the like can be used. Alternatively, the water treatment agent composition according to the present disclosure may include the following other components in addition to the components A to E within a range not impairing the stability of the composition.
 [その他の成分]
 本開示に係る水処理剤組成物は、本発明の効果を阻害しない範囲で、防錆剤、腐食防止剤、スケール分散剤、スライムコントロール剤などの公知の薬剤を併用してもよい。
[Other ingredients]
The water treatment agent composition according to the present disclosure may be used in combination with known agents such as a rust inhibitor, a corrosion inhibitor, a scale dispersant, and a slime control agent as long as the effects of the present invention are not impaired.
 [pH]
 本開示に係る水処理剤組成物は、該組成物の安定性向上の点から、pHが2以下であり、好ましくは1.7以下である。
[PH]
The water treatment agent composition according to the present disclosure has a pH of 2 or less, preferably 1.7 or less, from the viewpoint of improving the stability of the composition.
 本開示に係る水処理組成物は、一又は複数の実施形態において、濃縮物として流通してもよい。本開示に係る水処理組成物の濃縮物は、一又は複数の実施形態において、使用時に上記成分A~Dが上述した含有量になるように希釈して使用することができる。 The water treatment composition according to the present disclosure may be distributed as a concentrate in one or a plurality of embodiments. In one or a plurality of embodiments, the concentrate of the water treatment composition according to the present disclosure can be used by diluting the components A to D so as to have the above-described content at the time of use.
 [水処理剤組成物の調製]
 本開示に係る水処理剤組成物は、上記成分A~Eを混合することで調製できる。本開示に係る水処理剤組成物の調製の一又複数の実施形態において、より安定性の高い水処理剤組成物を得るために、窒素ガスによるバブリング処理をしてもよい。
[Preparation of water treatment composition]
The water treatment composition according to the present disclosure can be prepared by mixing the above components A to E. In one or more embodiments of the preparation of the water treatment agent composition according to the present disclosure, a bubbling treatment with nitrogen gas may be performed in order to obtain a more stable water treatment agent composition.
 本開示に係る水処理剤組成物は、一又は複数の実施形態において、ポリタンク等の容器内に入れて保管してもよいし、貯蔵タンクやコンテナ等に入れてその状態で使用してもよい。
 一又は複数の実施形態において、ポリタンク等の容器内でより長期間安定性を保った状態で保管可能にする観点から、本開示に係る水処理剤組成物をポリタンク等の容器に導入した後、容器の空間内を窒素又はアルゴン等の不活性ガスでパージ(置換)してもよい。よって、本開示に係る水処理剤組成物の一又は複数の実施形態として、不活性ガスでパージされた容器に配置された形態が挙げられる。
 一又は複数の実施形態において、貯蔵タンクやコンテナ等に入れてより長期間安定性を保った状態で使用可能にする観点から、本開示に係る水処理剤組成物を貯蔵タンクやコンテナ等に導入した後、窒素又はアルゴン等の不活性ガスによって貯蔵タンクやコンテナの空間内を大気圧よりも微加圧状態(1~5kPa)にしてもよい。微加圧状態は、一又は複数の実施形態において、貯蔵タンクやコンテナに配置した不活性ガスボンベにレギュレーター(精密圧力調整器)及びニードルバルブ付き流量計を取り付けることにより維持することができる。よって、本開示に係る水処理剤組成物の一又は複数の実施形態として、微加圧状態に維持された容器に配置された形態が挙げられる。
In one or a plurality of embodiments, the water treatment agent composition according to the present disclosure may be stored in a container such as a polytank, or may be used in a state stored in a storage tank or container. .
In one or a plurality of embodiments, after introducing the water treatment agent composition according to the present disclosure into a container such as a polytank from the viewpoint of being able to be stored in a state where stability is maintained for a longer period in a container such as a polytank, The space in the container may be purged (replaced) with an inert gas such as nitrogen or argon. Therefore, the form arrange | positioned in the container purged with the inert gas as one or some embodiment of the water treatment agent composition which concerns on this indication is mentioned.
In one or a plurality of embodiments, the water treatment agent composition according to the present disclosure is introduced into a storage tank, a container, or the like from the viewpoint of being usable in a state where the stability is maintained for a longer period of time by putting it in a storage tank, a container, etc. After that, the space in the storage tank or container may be brought into a slightly pressurized state (1 to 5 kPa) from the atmospheric pressure with an inert gas such as nitrogen or argon. In one or a plurality of embodiments, the slightly pressurized state can be maintained by attaching a regulator (precision pressure regulator) and a flow meter with a needle valve to an inert gas cylinder arranged in a storage tank or a container. Therefore, the form arrange | positioned in the container maintained in the slightly pressurized state as one or some embodiment of the water treatment agent composition which concerns on this indication is mentioned.
 本開示は、一態様において、上記成分A~C、必要に応じて成分D及び/又は成分Eを混合することを含む、シアン含有廃水用の水処理剤組成物の調製方法に関する。本開示に係る水処理剤組成物の調製方法は、一又は複数の実施形態において、混合した組成物をポリタンク等の容器に配置すること、及び組成物を配置した容器内を不活性ガスでパージすることを含んでいてもよい。また、本開示に係る水処理剤組成物の調製方法は、一又は複数の実施形態において、上記成分A~C、必要に応じて成分D及び/又は成分Eを混合して得られた組成物が配置された貯蔵タンク又はコンテナ等の空間内を、不活性ガスによって大気圧よりも微加圧状態にすることを含んでいてもよい。微加圧状態としては、一又は複数の実施形態において、大気圧よりも1~5kPa又は2~5kPa加圧した状態が挙げられる。 The present disclosure relates, in one aspect, to a method for preparing a water treatment agent composition for cyanide-containing wastewater, which comprises mixing the above components A to C and optionally component D and / or component E. In one or a plurality of embodiments, a method for preparing a water treatment agent composition according to the present disclosure includes arranging a mixed composition in a container such as a polytank, and purging the container in which the composition is arranged with an inert gas. May include. In addition, in one or a plurality of embodiments, the method for preparing a water treatment agent composition according to the present disclosure is a composition obtained by mixing the above components A to C and, if necessary, the component D and / or the component E. The inside of a space such as a storage tank or a container in which is placed may be made to be slightly pressurized from the atmospheric pressure by an inert gas. Examples of the slightly pressurized state include, in one or a plurality of embodiments, a state in which 1 to 5 kPa or 2 to 5 kPa is pressurized from atmospheric pressure.
 [シアン含有廃水の処理方法]
 本開示に係る水処理剤組成物は、シアン含有廃水のシアン除去処理に使用できる。したがって、本開示は、一態様において、シアン含有廃水の処理方法であって、シアン含有廃水に、該廃水中のシアンとの反応当量以上の塩化第一銅となるように本開示に係る水処理剤組成物を添加し、シアンの難溶性物質を生成させ該難溶性物質を分離することを含む。
[Treatment method of wastewater containing cyanide]
The water treatment agent composition according to the present disclosure can be used for cyan removal treatment of cyanide-containing wastewater. Accordingly, in one aspect, the present disclosure is a method for treating cyan-containing wastewater, and the water treatment according to the present disclosure is such that the cyan-containing wastewater has cuprous chloride having a reaction equivalent to or higher than cyan in the wastewater. Adding an agent composition to form a hardly soluble substance of cyanide and separating the hardly soluble substance.
 本開示に係る処理方法おいて処理対象となるシアン含有廃水におけるシアンの含有量は、特に限定されないが、全シアン濃度で2~100mg/Lの廃水を好適に処理することができる。このようなシアン含有廃水を処理する場合には、一又は複数の実施形態において、シアンとの反応当量以上の塩化第一銅となるように本開示に係る水処理剤組成物をシアン含有廃水に添加することが挙げられ、あるいは、塩化第一銅を4~1000mg/L、好ましくは10~100mg/Lとなるように、本開示に係る水処理剤組成物をシアン含有廃水に添加することが挙げられる。 The content of cyan in the cyan-containing wastewater to be treated in the treatment method according to the present disclosure is not particularly limited, but wastewater having a total cyan concentration of 2 to 100 mg / L can be suitably treated. In the case of treating such cyanide-containing wastewater, in one or a plurality of embodiments, the water treatment agent composition according to the present disclosure is converted to cyanide-containing wastewater so as to be cuprous chloride having a reaction equivalent to or higher than cyanide. Alternatively, the water treatment agent composition according to the present disclosure may be added to the cyanide-containing waste water so that cuprous chloride is 4 to 1000 mg / L, preferably 10 to 100 mg / L. Can be mentioned.
 本開示に係る水処理方法は、一又は複数の実施形態において、本開示に係る水処理剤組成物が導入された貯蔵タンク又はコンテナ内を、不活性ガスによって大気圧よりも微加圧状態とし、その状態で本開示に係る水処理剤組成物をシアン含有廃水に添加することを含んでいてもよい。 In one or a plurality of embodiments, the water treatment method according to the present disclosure is configured such that a storage tank or a container into which the water treatment agent composition according to the present disclosure has been introduced is brought into a slightly pressurized state from an atmospheric pressure by an inert gas. In this state, the water treatment agent composition according to the present disclosure may be added to the cyanide-containing wastewater.
 本開示に係るシアン含有廃水の処理方法を、シアン廃水の処理装置の一例を示す概略模式図(図1)を用いて具体的に説明するが、この態様は本発明を限定するものではない。
 処理対象となるシアン含有廃水(図中、実線矢印で示す)は、A点においてシアン濃度が測定され、反応処理槽1に送られ、シアン濃度等の測定値に基づいて、処理剤組成物槽2から本開示に係る水処理剤組成物が添加される。反応処理槽1においてシアン含有廃水を撹拌しつつ、所定時間滞留させた後、生成した水難溶性塩を含むシアン含有廃水を、反応処理槽1の下方からシックナー3に送る。シックナー3では、水難溶性塩の生成反応により沈降させて、シックナー3の下方から固形分を回収する。一方、シックナー3の上方から上澄液を排出させ、B点において上澄液のシアン濃度を測定し、測定値が排水基準値あるいは上乗せ排水基準値以下であることを確認した後、上澄液を排水する。なお、上記の処理排水を再利用することは、何ら差し支えない。
The cyan-containing wastewater treatment method according to the present disclosure will be specifically described with reference to a schematic diagram (FIG. 1) illustrating an example of a cyan wastewater treatment apparatus, but this aspect does not limit the present invention.
Cyanide wastewater to be treated (indicated by solid arrows in the figure) is measured for cyan concentration at point A, sent to the reaction treatment tank 1, and based on the measured values such as cyan concentration, the treating agent composition tank From 2 the water treatment agent composition according to the present disclosure is added. After the cyan-containing wastewater is stirred for a predetermined time while stirring in the reaction treatment tank 1, the cyan-containing wastewater containing the generated poorly water-soluble salt is sent to the thickener 3 from below the reaction treatment tank 1. In the thickener 3, the solid content is recovered from below the thickener 3 by being precipitated by a formation reaction of a poorly water-soluble salt. On the other hand, the supernatant is discharged from above the thickener 3, the cyan concentration of the supernatant is measured at point B, and it is confirmed that the measured value is the drainage standard value or the added drainage standard value or less. Drain the water. In addition, there is no problem in reusing the treated waste water.
 すなわち、本開示に係るシアン含有廃水の処理方法に用いることができるシアン含有廃水の処理装置は、基本的に本開示に係る水処理剤組成物を添加するための添加剤槽、水難溶性塩を生成させるための反応槽、前記水難溶性塩を回収するための沈殿槽及びこれらを連結する配管、撹拌手段、ポンプなどからなる。前記の反応槽と沈殿槽とを兼用することもでき、このような場合にはシックナーなどの装置を用いることができる。 That is, the cyanide-containing wastewater treatment apparatus that can be used in the method for treating cyanide-containing wastewater according to the present disclosure basically includes an additive tank for adding the water treatment agent composition according to the present disclosure, a poorly water-soluble salt. It consists of a reaction tank for generating, a precipitation tank for recovering the poorly water-soluble salt, piping connecting them, stirring means, a pump, and the like. The reaction tank and the precipitation tank can also be used together. In such a case, an apparatus such as a thickener can be used.
 この発明を実施例により具体的に説明するが、この発明はこれらの実施例により限定されるものではない。 The present invention will be specifically described with reference to examples, but the present invention is not limited to these examples.
 [水処理剤組成物の調製と外観評価確認試験]
 200ミリリットル容のビーカーに水を加え、表2記載のアルカリ(土類)金属の塩化物又は臭化物、酸、また必要に応じて亜硫酸ナトリウム又はヨウ化カリウムの順に所定量となるように加えて水溶液とし、窒素バブリングを行いながらスターラーで10分間撹拌した。その後、塩化第一銅を加えて30分間の撹拌を行なったものを水処理剤組成物とした。得られた水処理剤組成物をガラス瓶に移し替えてから1時間保管後の外観の観察を行なった。外観の評価は下記表1の基準とした。なお表2中の各成分の数字はすべて重量%で、残部は水である。
[Preparation of water treatment agent composition and appearance evaluation confirmation test]
Add water to a 200 milliliter beaker and add an aqueous solution by adding a predetermined amount in the order of chlorides or bromides of alkali (earth) metal, acid, and sodium sulfite or potassium iodide as required. And stirring with a stirrer for 10 minutes while carrying out nitrogen bubbling. Then, the thing which added cuprous chloride and stirred for 30 minutes was made into the water treating agent composition. After the obtained water treatment composition was transferred to a glass bottle, the appearance after storage for 1 hour was observed. The evaluation of appearance was based on the criteria shown in Table 1 below. The numbers for each component in Table 2 are all by weight and the balance is water.
Figure JPOXMLDOC01-appb-T000001
Figure JPOXMLDOC01-appb-T000001
Figure JPOXMLDOC01-appb-T000002
Figure JPOXMLDOC01-appb-T000002
 表2の結果から、実施例の水処理剤組成物(実施例1~14)においては、色みを帯びているが、沈殿や濁りもなく透明であった。これに対し、比較例の水処理剤組成物(比較例1~11)の水処理剤組成物においては、塩化第一銅の濃度が2重量%以下であるにもかかわらず、ポンプの詰まりや濃度不足が懸念される濁りや沈殿が生じ、塩化第一銅をほとんど溶解しないものもあり、実質的に使用できない組成物であった。 From the results in Table 2, the water treatment agent compositions of Examples (Examples 1 to 14) were colored but transparent without precipitation or turbidity. In contrast, in the water treatment agent compositions of the comparative water treatment agent compositions (Comparative Examples 1 to 11), although the concentration of cuprous chloride was 2% by weight or less, the clogging of the pump Turbidity and precipitation, which are feared to be insufficient in concentration, occurred, and some cuprous chlorides were hardly dissolved. Thus, the composition was practically unusable.
 [容器内における水処理剤組成物の安定化確認試験]
 実施例9の水処理剤組成物を、容量200mlの密閉ポリ瓶にそれぞれ100mlずつ加え、容器の空間内に窒素ガスでパージしたものを、表3に示す温度で50日間静置した。50日後にガラス瓶に移して水処理剤組成物の外観の観察を行なった。その結果を表3に示す。
[Stabilization confirmation test of water treatment agent composition in container]
100 ml each of the water treating agent composition of Example 9 was added to a sealed plastic bottle having a capacity of 200 ml, and the one purged with nitrogen gas in the space of the container was allowed to stand at the temperature shown in Table 3 for 50 days. After 50 days, it was transferred to a glass bottle and the appearance of the water treatment agent composition was observed. The results are shown in Table 3.
Figure JPOXMLDOC01-appb-T000003
Figure JPOXMLDOC01-appb-T000003
 表3の結果から、50日間保管後の水処理剤組成物は、いずれの保管温度においても、保管前と同様の外観が維持され、製剤として長期間安定した状態を保っていたことが確認できた。
 また、窒素パージを行わなかった以外は、上記と同様に保管及び外観の観察を行った。その結果、容器を窒素パージして保管することによって、窒素パージを行わず保管した場合と比較して、より長期間安定した状態で保管できることが確認できた。
 さらに、NaSO(成分D)を含まない水処理剤組成物で同様の確認試験を行ったところ、NaSOを含まない水処理剤組成物においても同様の結果が得られた。
From the results in Table 3, it can be confirmed that the water treatment composition after storage for 50 days maintained the same appearance as before storage at any storage temperature and maintained a stable state as a preparation for a long time. It was.
Moreover, storage and appearance observation were performed in the same manner as described above except that nitrogen purging was not performed. As a result, it was confirmed that by storing the container after purging with nitrogen, it was possible to store the container in a stable state for a longer period of time than when storing without performing the nitrogen purge.
Furthermore, when the same confirmation test was performed with the water treatment agent composition not containing Na 2 SO 3 (component D), the same result was obtained in the water treatment agent composition not containing Na 2 SO 3 .
 [貯蔵タンクにおける水処理剤組成物の安定化確認試験]
 実施例9の水処理剤組成物を、1000Lの貯蔵タンクに750L加えて貯蔵タンクの空間内を窒素ガスでパージした後、さらに窒素により微加圧状態(3kPa)を保ちながら、当該水処理剤組成物を100L/日の流量で引き抜き使用した(7日間)。
[Stabilization confirmation test of water treatment agent composition in storage tank]
After adding 750 L of the water treatment agent composition of Example 9 to a 1000 L storage tank and purging the space of the storage tank with nitrogen gas, the water treatment agent was further maintained while maintaining a slightly pressurized state (3 kPa) with nitrogen. The composition was withdrawn and used at a flow rate of 100 L / day (7 days).
 その結果、7日間、良好な状態でタンクから引き抜き使用することができた。また、引き抜き使用終了後(引き抜き使用開始から7日後)、貯蔵タンク内の水処理剤組成物の外観を確認したところ、使用開始前と同様の褐色の透明液であった。
 また、貯蔵タンクに(空気)穴を開けて微加圧状態としなかった以外は、上記と同様に使用した。その結果、微加圧状態で使用することによって、微加圧状態にしなかった場合と比較して、水処理剤組成物の安定性に優れ、かつ良好に使用できることが確認できた。
 また、NaSO(成分D)を含まない水処理剤組成物で同様の試験を行ったところ、NaSOを含まない水処理剤組成物においても同様の結果が得られた。
As a result, it was able to be pulled out from the tank and used in good condition for 7 days. Moreover, when the external appearance of the water treatment agent composition in a storage tank was confirmed after completion | finish of extraction use (seven days after the start of extraction use), it was the same brown transparent liquid as before use start.
Moreover, it was used in the same manner as described above, except that a (air) hole was made in the storage tank so as not to be in a slightly pressurized state. As a result, it was confirmed that the water treatment agent composition was excellent in stability and can be used satisfactorily when used in a slightly pressurized state as compared with the case where the slightly pressurized state was not used.
Moreover, when the same test was performed with the water treatment agent composition not containing Na 2 SO 3 (component D), the same result was obtained in the water treatment agent composition not containing Na 2 SO 3 .
 [シアンの除去効果の確認]
 実施例2及び9の水処理剤組成物につき、下記条件でシアン除去実験を行った。
[Confirmation of cyan removal effect]
For the water treatment agent compositions of Examples 2 and 9, a cyan removal experiment was conducted under the following conditions.
 (シアン除去実験の条件)
 某製鉄所の2系統のコークス炉廃水ラインより採取したシアン含有廃液A(遊離シアン;1.6mg/L)およびシアン含有廃液B(遊離シアン;1.3mg/L)を用いた。1000mL容のビーカーに、それぞれシアン含有廃液を1000mL分注し、所定の薬剤濃度(Cu濃度)になるように実施例2及び実施例9の水処理剤組成物を添加し、130rpmにて30分間スターラーで撹拌した。その後1時間静置し、上澄液の全シアン濃度をJIS K0102に準拠して測定した。測定結果を表4に示す。
(Conditions for cyan removal experiment)
Cyan-containing waste liquid A (free cyan; 1.6 mg / L) and cyan-containing waste liquid B (free cyan; 1.3 mg / L) collected from two coke oven waste water lines at Sakai Steel Works were used. Into a 1000 mL beaker, 1000 mL each of the cyan-containing waste liquid was dispensed, and the water treatment agent compositions of Example 2 and Example 9 were added so as to have a predetermined chemical concentration (Cu + concentration), and 30 rpm at 130 rpm. Stir with a stirrer for minutes. Thereafter, the mixture was allowed to stand for 1 hour, and the total cyan density of the supernatant was measured according to JIS K0102. Table 4 shows the measurement results.
Figure JPOXMLDOC01-appb-T000004
Figure JPOXMLDOC01-appb-T000004
 表4に示すように、製鉄所のシアン廃水に対して実施例2及び実施例9の水処理剤組成物で処理することにより、全シアン濃度を水質汚濁防止法に基づく排水基準1mg/L以下にすることができた。 As shown in Table 4, by treating the cyanide wastewater of the steelworks with the water treatment composition of Example 2 and Example 9, the total cyanide concentration is 1 mg / L or less based on the drainage standard based on the Water Pollution Control Law. I was able to.
1 反応処理槽
2 処理剤組成物槽
3 シックナー
1 Reaction Treatment Tank 2 Treatment Agent Composition Tank 3 Thickener

Claims (6)

  1.  シアン含有廃水用の水処理剤組成物であって、
     (A)塩化第一銅、
     (B)アルカリ金属塩化物、アルカリ金属臭化物、アルカリ土類金属塩化物、及びアルカリ土類金属臭化物からなる群から選ばれる少なくとも1つ、並びに、
     (C)無機酸及び/又は有機酸
     を含有し、
     前記(C)無機酸及び/又は有機酸の前記水処理剤組成物における含有量が、10重量%以下であり、かつ、前記水処理剤組成物のpHが2以下である、水処理剤組成物。
    A water treatment composition for cyanide-containing wastewater,
    (A) cuprous chloride,
    (B) at least one selected from the group consisting of alkali metal chlorides, alkali metal bromides, alkaline earth metal chlorides, and alkaline earth metal bromides, and
    (C) contains an inorganic acid and / or an organic acid,
    The water treatment agent composition in which the content of the (C) inorganic acid and / or organic acid in the water treatment agent composition is 10% by weight or less, and the pH of the water treatment agent composition is 2 or less. object.
  2.  前記(A)塩化第一銅の前記水処理剤組成物における含有量が、1.5重量%以上である、請求項1記載の水処理剤組成物。 The water treatment agent composition according to claim 1, wherein the content of the (A) cuprous chloride in the water treatment agent composition is 1.5% by weight or more.
  3.  前記(B)アルカリ金属塩化物、アルカリ金属臭化物、アルカリ土類金属塩化物、及びアルカリ土類金属臭化物からなる群から選ばれる少なくとも1つの前記水処理剤組成物における含有量が、1重量%以上45重量%以下である、請求項1又は2記載の水処理剤組成物。 The content in at least one water treatment agent composition selected from the group consisting of (B) alkali metal chloride, alkali metal bromide, alkaline earth metal chloride, and alkaline earth metal bromide is 1% by weight or more. The water treatment agent composition of Claim 1 or 2 which is 45 weight% or less.
  4.  前記水処理剤組成物が、さらに、(D)亜硫酸ナトリウムを含有する、請求項1から3のいずれかに記載の水処理剤組成物。 The water treatment agent composition according to any one of claims 1 to 3, wherein the water treatment agent composition further comprises (D) sodium sulfite.
  5.  前記(D)亜硫酸ナトリウムの前記水処理剤組成物における含有量が、0.05重量%未満である、請求項4記載の水処理剤組成物。 The water treatment agent composition according to claim 4, wherein a content of the (D) sodium sulfite in the water treatment agent composition is less than 0.05% by weight.
  6.  シアン含有廃水に、該廃水中のシアンとの反応当量以上の塩化第一銅となるように請求項1から5のいずれかに記載の水処理剤組成物を添加し、シアンの難溶性物質を生成させ該難溶性物質を分離することを含む、シアン含有処理排水の処理方法。 The water-treating agent composition according to any one of claims 1 to 5 is added to cyanide-containing wastewater so as to have cuprous chloride having a reaction equivalent to or higher than that of cyanide in the wastewater. A method for treating cyanide-containing treated wastewater, comprising producing and separating the hardly soluble substance.
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Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58210892A (en) * 1982-05-31 1983-12-08 Katayama Chem Works Co Ltd Treating agent of waste water containing cyan and/or thiocyan
JPH01210096A (en) * 1988-02-18 1989-08-23 Sumitomo Metal Mining Co Ltd Removal of iron cyanide complex
JP2013123655A (en) * 2011-12-13 2013-06-24 Nippon Steel & Sumikin Eco-Tech Corp Method for treating cyanide-containing wastewater
JP2013146696A (en) * 2012-01-20 2013-08-01 Katayama Chem Works Co Ltd Method for treating cyanide-containing wastewater
JP2013226510A (en) * 2012-04-25 2013-11-07 Kurita Water Ind Ltd Treating method and treating agent of cyanogen-containing wastewater

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58210892A (en) * 1982-05-31 1983-12-08 Katayama Chem Works Co Ltd Treating agent of waste water containing cyan and/or thiocyan
JPH01210096A (en) * 1988-02-18 1989-08-23 Sumitomo Metal Mining Co Ltd Removal of iron cyanide complex
JP2013123655A (en) * 2011-12-13 2013-06-24 Nippon Steel & Sumikin Eco-Tech Corp Method for treating cyanide-containing wastewater
JP2013146696A (en) * 2012-01-20 2013-08-01 Katayama Chem Works Co Ltd Method for treating cyanide-containing wastewater
JP2013226510A (en) * 2012-04-25 2013-11-07 Kurita Water Ind Ltd Treating method and treating agent of cyanogen-containing wastewater

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