JP2011126933A - Heavy metal-treating agent and method for treating heavy metal by using the same - Google Patents

Heavy metal-treating agent and method for treating heavy metal by using the same Download PDF

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JP2011126933A
JP2011126933A JP2009283900A JP2009283900A JP2011126933A JP 2011126933 A JP2011126933 A JP 2011126933A JP 2009283900 A JP2009283900 A JP 2009283900A JP 2009283900 A JP2009283900 A JP 2009283900A JP 2011126933 A JP2011126933 A JP 2011126933A
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heavy metal
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piperazine
sodium
aqueous solution
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JP5493804B2 (en
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Yoshinori Ayama
義則 阿山
Hideki Hikita
英樹 疋田
Toshitaka Nagamine
利登 長嶺
Mitsuaki Yoshimitsu
満明 吉光
Yasuyuki Nagai
康行 長井
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Tosoh Corp
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Abstract

<P>PROBLEM TO BE SOLVED: To solve the problems wherein an aqueous solution of sodium carbodithionate of piperazine easily precipitates crystals when the aqueous solution is formed into a high concentration, although the aqueous solution of the carbodithionate of the piperazine has high heavy metal-immobilizing ability and is excellent heavy metal-treating agent hardly causing harmful gas when treating he heavy metal. <P>SOLUTION: The high-concentration aqueous solution exceeding 25 wt.% at room temperature (25°C) is obtained in the aqueous solution of the sodium piperazine-N, N'-biscarbodithionate containing a dissimilar metal cation, and the precipitation of the crystal is not caused. The molar ratio of the sodium cation to the dissimilar cation is preferably from 99:1 to 80:20, and the dissimilar cation is preferably potassium cation. <P>COPYRIGHT: (C)2011,JPO&INPIT

Description

本発明は、重金属を含有する固体廃棄物、例えば、ゴミ焼却場から排出される焼却灰及び飛灰、重金属に汚染された土壌、排水処理後に生じる汚泥等に含有する鉛、水銀、クロム、カドミウム、亜鉛及び銅等の有害な重金属を簡便に固定化し、不溶出化することを可能にする重金属処理剤に関するものであり、特に高濃度で他の汎用重金属処理剤との混合によって固形物の析出がないピペラジンジ−N,N’−ビスカルボジチオ酸ナトリウム水溶液からなる重金属処理剤に関するものである。   The present invention relates to solid waste containing heavy metals, for example, incineration ash and fly ash discharged from garbage incineration plants, soil contaminated with heavy metals, lead contained in sludge generated after wastewater treatment, mercury, chromium, cadmium It relates to a heavy metal treatment agent that makes it possible to easily fix and elute harmful heavy metals such as zinc and copper, and in particular, precipitation of solids by mixing with other general-purpose heavy metal treatment agents at a high concentration The present invention relates to a heavy metal treating agent comprising an aqueous solution of piperazine di-N, N′-biscarbodithioate without water.

都市ゴミ焼却工場などから排出される飛灰は重金属含有率が高く、重金属の溶出を抑制する処理を施すことが必要である。その様な処理方法のひとつとして薬剤処理法があり、キレート系薬剤などの重金属処理剤を添加して重金属を処理する方法が用いられている。   Fly ash discharged from municipal waste incineration plants and the like has a high heavy metal content and needs to be treated to suppress elution of heavy metals. As one of such treatment methods, there is a drug treatment method, and a method of treating a heavy metal by adding a heavy metal treatment agent such as a chelate-type drug is used.

キレート系薬剤としてはアミン誘導体のカルボジチオ酸塩が主に用いられている。特にピペラジンのカルボジチオ酸塩は他のアミン誘導体のカルボジチオ酸塩とは異なり硫化水素、二硫化炭素等の有害ガス発生が少ないという特徴を有するため、重金属処理剤として広く用いられている(例えば特許文献1参照)。   As chelating agents, carbodithioates of amine derivatives are mainly used. In particular, carbodithioate of piperazine is widely used as a heavy metal treating agent because it has a feature that less harmful gases such as hydrogen sulfide and carbon disulfide are generated unlike carbodithioate of other amine derivatives (for example, patent documents). 1).

現在、重金属処理剤として用いられているピペラジンのカルボジチオ酸塩の水溶液はカリウム塩が用いられているが、ピペラジンのカルボジチオ酸カリウム塩水溶液では他の汎用の重金属処理剤と混合した際に固形物が析出するという問題もあった。   Currently, potassium salt is used as an aqueous solution of piperazine carbodithioate used as a heavy metal treating agent, but when mixed with other general-purpose heavy metal treating agents, piperazine carbodithioic acid potassium salt aqueous solution contains solids. There was also a problem of precipitation.

一方、ピペラジンのカルボジチオ酸ナトリウム塩は、カリウム塩と同様に重金属固定化能が高く、なおかつ熱的に安定で有害ガスの発生がない優れた基本性能を有するものであるが、高濃度の水溶液ではナトリウム塩の結晶が析出するという問題があった。   On the other hand, carbodithioic acid sodium salt of piperazine has a high ability to immobilize heavy metals like potassium salt, and has excellent basic performance that is thermally stable and does not generate harmful gases. There was a problem that crystals of sodium salt were precipitated.

これまでピペラジン−N,N’−ビスカルボジチオ酸塩、特にカリウム塩の水溶液からの結晶析出(特に低温での結晶析出)を抑止するために、特定の範囲のアルカリ水酸化物を添加する方法が提案されている(例えば特許文献2〜3参照)。しかし、アルカリ水酸化物を添加量を制御しただけでは、ピペラジン−N,N’−ビスカルボジチオ酸ナトリウムの高濃度溶液からの結晶析出は抑止することはできなかった。   A method of adding an alkali hydroxide in a specific range in order to suppress crystal precipitation from an aqueous solution of piperazine-N, N′-biscarbodithioate, particularly potassium salt (particularly crystal precipitation at low temperature). Has been proposed (see, for example, Patent Documents 2 to 3). However, crystal precipitation from a high-concentration solution of piperazine-N, N′-biscarbodithioate could not be suppressed only by controlling the amount of alkali hydroxide added.

ピペラジン−N,N’−ビスカルボジチオ酸ナトリウムの溶解度は室温で約20重量%、加温した場合にも25重量%までであり、室温(25℃)で25重量%を超える高濃度で結晶析出のない高濃度ピペラジン−N,N’−ビスカルボジチオ酸ナトリウム水溶液は得られていなかった。   The solubility of piperazine-N, N′-biscarbodithioate sodium is about 20% by weight at room temperature, and even when heated, it is up to 25% by weight. Crystals at high concentrations exceeding 25% by weight at room temperature (25 ° C.) A high-concentration piperazine-N, N′-biscarbodithioate aqueous solution without precipitation was not obtained.

特許第3391173号Japanese Patent No. 3391173 特開2006−316183JP 2006-316183 A 特開2008−184470JP2008-184470

ピペラジン−N,N’−ビスカルボジチオ酸ナトリウム水溶液は高濃度水溶液とした場合に室温で結晶が析出するという問題があった。本発明は、高濃度のピペラジン−N,N’−ビスカルボジチオ酸ナトリウム水溶液、特に室温(25℃)で25重量%を超える高濃度の水溶液を提供するものである。   When the aqueous solution of piperazine-N, N′-biscarbodithioate is a high-concentration aqueous solution, there is a problem that crystals precipitate at room temperature. The present invention provides a high-concentration aqueous solution of piperazine-N, N'-biscarbodithioate, particularly a high-concentration aqueous solution exceeding 25% by weight at room temperature (25 ° C.).

本発明者等は上記の課題を解決すべく鋭意検討を重ねた結果、ピペラジン−N,N’−ビスカルボジチオ酸と塩を形成するカウンターカチオンとしてナトリウムカチオン以外の異種カチオン、特にカリウムカチオンを混合して用いることにより、結晶析出のないピペラジン−N,N’−ビスカルボジチオ酸ナトリウムの高濃度水溶液が得られることを見出し、本発明を完成するに到ったものである。   As a result of intensive studies to solve the above problems, the present inventors have mixed piperazine-N, N′-biscarbodithioic acid with a different cation other than sodium cation, particularly potassium cation, as a counter cation that forms a salt. As a result, it was found that a high-concentration aqueous solution of piperazine-N, N′-biscarbodithioate without crystal precipitation can be obtained, and the present invention has been completed.

以下、本発明について詳細に説明する。   Hereinafter, the present invention will be described in detail.

本発明の重金属処理剤は、室温(25℃)においてピペラジン−N,N’−ビスカルボジチオ酸ナトリウムの濃度が25重量%を超える水溶液からなるものである。ピペラジン−N,N’−ビスカルボジチオ酸ナトリウムの濃度は高い方が好ましく、27重量%以上が好ましい。   The heavy metal treating agent of the present invention comprises an aqueous solution in which the concentration of sodium piperazine-N, N′-biscarbodithioate exceeds 25% by weight at room temperature (25 ° C.). The concentration of piperazine-N, N'-biscarbodithioic acid sodium is preferably higher, and preferably 27% by weight or more.

一方、重金属処理剤は重金属含有物へ均一に分散させるために水で希釈して用いられるため、ピペラジン−N,N’−ビスカルボジチオ酸ナトリウムの濃度は30重量%を超えない範囲で十分である。   On the other hand, since the heavy metal treating agent is diluted with water to be uniformly dispersed in the heavy metal-containing material, the concentration of piperazine-N, N′-biscarbodithioic acid sodium does not exceed 30% by weight. is there.

本発明の高濃度のピペラジン―N,N’−ビスカルボジチオ酸ナトリウム水溶液が室温において結晶の析出がなく安定化されるのは、ピペラジン−N,N’−ビスカルボジチオ酸と塩を形成するカチオンとしてナトリウム単独ではなく、ナトリウム以外の異種カチオンとの混合カチオンとすることによって達成される。   The aqueous piperazine-N, N′-biscarbodithioate aqueous solution of the present invention is stabilized without precipitation of crystals at room temperature, and forms a salt with piperazine-N, N′-biscarbodithioic acid. This is achieved by using a mixed cation with a different cation other than sodium as a cation, not sodium alone.

混合カチオンとすることによって高濃度水溶液が安定化する理由は必ずしも定かではないが、例えば以下のメカニズムが考えられる。ピペラジン−N,N’−ビスカルボジチオ酸は金属錯体を形成するカウンターカチオン(金属カチオン種)によってはピペラジン−N,N’−ビスカルボジチオ酸分子の両末端の官能基と金属カチオンの配位結合を介して高分子構造となる場合があると言われている。ピペラジン−N,N’−ビスカルボジチオ酸ナトリウムの結晶が針状結晶であることから類推して、当該塩もピペラジン−N,N’−ビスカルボジチオ酸分子が一定方向に規則的に配列(会合)して結晶化が進んでいることが推定される。そのため、その様な規則的な配列して高分子化することを阻害する異種カチオンを混合して用いることにより、分子の会合及び結晶形成が阻害され、高濃度水溶液が安定に得られるのではないかと考えられる。   The reason why the high-concentration aqueous solution is stabilized by using mixed cations is not necessarily clear, but for example, the following mechanism can be considered. Piperazine-N, N'-biscarbodithioic acid is a coordinator between the functional group at both ends of the piperazine-N, N'-biscarbodithioic acid molecule and the metal cation, depending on the counter cation (metal cation species) forming the metal complex. It is said that a polymer structure may be formed through a bond. By analogy that the crystal of piperazine-N, N′-biscarbodithioate sodium is a needle-like crystal, the salt of this salt is also regularly arranged in a certain direction in the piperazine-N, N′-biscarbodithioate molecule ( It is estimated that crystallization is progressing. For this reason, the use of a mixture of different cations that inhibits such a regular arrangement and polymerisation will inhibit molecular association and crystal formation, and a high-concentration aqueous solution cannot be obtained stably. It is thought.

一方、ピペラジン−N,N’−ビスカルボジチオ酸カリウム塩では、異種カチオンの導入によってはその溶解度の顕著な向上は見られない。   On the other hand, in the case of piperazine-N, N′-biscarbodithioic acid potassium salt, the solubility is not significantly improved by introduction of different cations.

ナトリウムカチオンに対して導入される異種カチオンは、モル比で1〜20モル%(ナトリウムカチオンと異種カチオンのモル比99:1〜80:20)であり、特に3〜20モル%、さらに5〜10モル%の範囲が好ましい。1モル%未満では、高濃度水溶液の安定化効果(結晶析出抑止効果)が十分でない。一方、20モル%を超えた場合、ピペラジン−N,N’−ビスカルボジチオ酸カリウム塩の比率が高くなり、ナトリウム塩としての特徴、例えば他の汎用重金属処理剤と混合した際の固形物析出抑止効果が失われ易い。   The different cation introduced with respect to the sodium cation is 1 to 20 mol% (molar ratio of sodium cation to different cation 99: 1 to 80:20), particularly 3 to 20 mol%, A range of 10 mol% is preferred. If it is less than 1 mol%, the stabilization effect (crystal precipitation inhibiting effect) of the high-concentration aqueous solution is not sufficient. On the other hand, when it exceeds 20 mol%, the ratio of piperazine-N, N′-biscarbodithioic acid potassium salt is increased, and the characteristics as a sodium salt, for example, solid precipitation when mixed with other general-purpose heavy metal treating agents The deterrent effect is easily lost.

ピペラジン−N,N’−ビスカルボジチオ酸ナトリウムに導入する異種カチオン種はナトリウムカチオン以外のカチオン種類であれば特に限定はないが、それ自身がピペラジン−N,N’−ビスカルボジチオ酸と不溶性塩錯体を形成しないカリウムカチオンが特に好ましい。   There is no particular limitation on the different cation species to be introduced into piperazine-N, N′-biscarbodithioate sodium as long as it is a cation species other than sodium cation, but itself is insoluble in piperazine-N, N′-biscarbodithioate. A potassium cation that does not form a salt complex is particularly preferred.

本発明の重金属処理剤では、さらに異種アミンのカルボジチオ酸塩を混合して用いてもよい。   In the heavy metal treating agent of the present invention, carbodithioates of different amines may be further mixed and used.

本発明の重金属処理剤には、本発明の効果を損なわない範囲で他の成分を含んでもよい。例えばピペラジン−N−カルボジチオ酸ナトリウムはピペラジン−N,N’−ビスカルボジチオ酸ナトリウムを製造する際の副生物として生成し易いものである。ピペラジン−N−カルボジチオ酸ナトリウムは重金属を固定化する官能基を1つのみ有し、単位重量当たりの重金属処理能力が低いため、その含有量は低いことが好ましく、特に1重量%未満とすることが好ましい。   The heavy metal treating agent of the present invention may contain other components as long as the effects of the present invention are not impaired. For example, sodium piperazine-N-carbodithioate is likely to be generated as a by-product in the production of sodium piperazine-N, N'-biscarbodithioate. Piperazine-N-carbodithioic acid sodium has only one functional group for immobilizing heavy metals, and its ability to treat heavy metals per unit weight is low, so its content is preferably low, especially less than 1% by weight Is preferred.

次に本発明の重金属処理剤の製造法を説明する。   Next, the manufacturing method of the heavy metal processing agent of this invention is demonstrated.

本発明の重金属処理剤は、ピペラジン−N,N’−ビスカルボジチオ酸ナトリウムの水溶液に異種カチオンを有するものであればよく、その製造方法は限定されないが、特にピペラジン水溶液に二硫化炭素と水酸化ナトリウムを混合してピペラジン−N,N’−ビスカルボジチオ酸ナトリウムを製造する方法において、異種カチオンを含有する水酸化ナトリウムを混合することにより、ピペラジン−N,N’−ビスカルボジチオ酸ナトリウム分子の生成段階から混合カチオン系として製造することが好ましい。   The heavy metal treating agent of the present invention is not limited as long as it has a different cation in the aqueous solution of piperazine-N, N′-biscarbodithioate, and its production method is not limited. Piperazine-N, N′-biscarbodithioate sodium by mixing sodium hydroxide containing different cations in a method for producing sodium piperazine-N, N′-biscarbodithioate by mixing sodium oxide It is preferable to produce a mixed cationic system from the molecular production stage.

水溶液中でのピペラジン−N,N’−ビスカルボジチオ酸ナトリウムに、さらに異種アミンのカルボジチオ酸塩を混合して用いる場合には、最初からピペラジンと異種アミンの混合水溶液に二硫化炭素、アルカリ金属水酸化物を添加して反応させることが好ましい。   When piperazine-N, N′-biscarbodithioate in aqueous solution is mixed with carbodithioate of different amines, carbon disulfide and alkali metal are first added to the mixed aqueous solution of piperazine and different amines. It is preferable to add a hydroxide to react.

次に本発明の重金属処理剤を用いた重金属処理方法について説明する。   Next, the heavy metal processing method using the heavy metal processing agent of this invention is demonstrated.

本発明の重金属処理剤は重金属汚染物質と混合することによって重金属汚染物質を処理、即ち重金属汚染物質中の重金属を不溶化することができる。   The heavy metal treating agent of the present invention can treat heavy metal contaminants by mixing with heavy metal contaminants, that is, insolubilize heavy metals in the heavy metal contaminants.

重金属汚染物質は限定されないが、飛灰、土壌、スラッジ等が例示でき、処理される重金属としては鉛、カドミウム、クロム、水銀等が例示できる。   Heavy metal pollutants are not limited, but examples include fly ash, soil, sludge, and examples of heavy metals to be treated include lead, cadmium, chromium, and mercury.

本発明の重金属処理剤を用いた重金属処理方法は、特に限定されるものではなく、本発明の重金属処理剤と重金属汚染物質を十分に混合すればよい。重金属処理剤の使用量は重金属汚染物質の状態、重金属の含有量や重金属の形態により異なるが、通常、例えば飛灰に対しては0.01〜30重量%の範囲で使用される。また、処理を容易にするため、処理物に対して5〜50重量%の加湿水を混練時に添加してもよい。   The heavy metal treatment method using the heavy metal treatment agent of the present invention is not particularly limited, and the heavy metal treatment agent of the present invention and the heavy metal contaminant may be sufficiently mixed. The amount of heavy metal treating agent used varies depending on the state of heavy metal contaminants, the content of heavy metals and the form of heavy metals. Moreover, in order to make a process easy, you may add 5-50 weight% humidified water with respect to a processed material at the time of kneading | mixing.

本発明のピペラジン−N,N’−ビスカルボジチオ酸ナトリウム水溶液は重金属固定化能が高い。   The piperazine-N, N'-biscarbodithioate aqueous solution of the present invention has a high heavy metal immobilization ability.

以下本発明を実施例で説明するが、本発明はこれら実施例に限定されるものではない。   EXAMPLES The present invention will be described below with reference to examples, but the present invention is not limited to these examples.

実施例1〜2
ピペラジン水溶液に対し、窒素気流中、攪拌下で二流化炭素、水酸化ナトリウムと水酸化カリウムの混合水溶液を滴下し、ピペラジン−N,N’−ビスカルボジチオ酸ナトリウム水溶液を得た。反応時間は4時間、水溶液は反応熱によって35℃に加温された。反応後、1時間熟成し、未反応の二硫化炭素を窒素ガスで留去し、黄色透明の水溶液を得た。
Examples 1-2
A piperazine-N, N′-biscarbodithioate aqueous solution was obtained by dropping a mixed aqueous solution of carbonized carbon and sodium hydroxide and potassium hydroxide under stirring in a nitrogen stream to the piperazine aqueous solution. The reaction time was 4 hours, and the aqueous solution was heated to 35 ° C. by the heat of reaction. After the reaction, it was aged for 1 hour, and unreacted carbon disulfide was distilled off with nitrogen gas to obtain a yellow transparent aqueous solution.

得られた水溶液を一晩放置し、室温(25℃)に冷却し、結晶析出の有無を確認した。   The obtained aqueous solution was allowed to stand overnight, cooled to room temperature (25 ° C.), and the presence or absence of crystal precipitation was confirmed.

表1に、得られた水溶液のピペラジン−N,N’−ビスカルボジチオ酸ナトリウム濃度(表1中の第二カラム上段)、混合カチオンがピペラジン−N,N’−ビスカルボジチオ酸塩を形成していると仮定した全ピペラジン−N,N’−ビスカルボジチオ酸塩濃度(表1中の第二カラム下段)、及び各カチオンの含有量(モル/kg)を示した。   Table 1 shows the concentration of piperazine-N, N′-biscarbodithioate in the aqueous solution (the upper column in the second column in Table 1) and the mixed cation forms piperazine-N, N′-biscarbodithioate. The total piperazine-N, N′-biscarbodithioate concentration assumed in the second column (lower column in Table 1) and the content of each cation (mol / kg) are shown.

比較例1〜2
水酸化カリウムを含まない水酸化ナトリウムを用い、実施例1と同様の手順でピペラジン−N,N’−ビスカルボジチオ酸ナトリウム水溶液を得た。結果を表1に示す。
Comparative Examples 1-2
Piperazine-N, N′-biscarbodithioate aqueous solution was obtained in the same procedure as in Example 1 using sodium hydroxide not containing potassium hydroxide. The results are shown in Table 1.

ピペラジン−N,N’−ビスカルボジチオ酸ナトリウム濃度が20重量%では結晶析出は観測されなかったが、25重量%では室温で結晶が析出した。   Crystal precipitation was not observed when the piperazine-N, N'-biscarbodithioate sodium concentration was 20% by weight, but at 25% by weight, crystals were precipitated at room temperature.

比較例3
異種カチオンの比率をK/(Na+K)のモル比で0.25(25モル%)に増大し、ピペラジン−N,N’−ビスカルボジチオ酸ナトリウムが30重量%の水溶液を製造した。
Comparative Example 3
The ratio of different cations was increased to 0.25 (25 mol%) in the molar ratio of K / (Na + K) to prepare an aqueous solution containing 30% by weight of sodium piperazine-N, N′-biscarbodithioate.

反応終了時から既に結晶の析出が観測された。   Crystal precipitation was already observed from the end of the reaction.

参考例
現在市販されているピペラジン−N,N’−ビスカルボジチオ酸カリウム水溶液のTS−275(東ソー株式会社製)は濃度が35重量%であり、モル濃度換算では約1.11モル/kgである。
Reference Example TS-275 (manufactured by Tosoh Corporation), an aqueous potassium piperazine-N, N′-biscarbodithioate solution currently on the market, has a concentration of 35% by weight and is approximately 1.11 mol / kg in terms of molar concentration. It is.

ピペラジン−N,N’−ビスカルボジチオ酸ナトリウムは分子量が小さいため、本発明の重金属処理剤の有効成分のモル濃度は従来製品と同程度であり、濃度が25重量%を超えるピペラジン−N,N’−ビスカルボジチオ酸ナトリウム水溶液では従来製品と同程度の重金属処理能を有することがわかる。   Since piperazine-N, N′-biscarbodithioate has a low molecular weight, the molar concentration of the active ingredient of the heavy metal treating agent of the present invention is comparable to that of the conventional product, and the concentration of piperazine-N, It can be seen that the sodium N'-biscarbodithioate aqueous solution has the same ability to treat heavy metals as conventional products.

Figure 2011126933
Figure 2011126933

(重金属処理試験)
飛灰(Pb含有量=2100ppm)100重量部に、水30重量部を加え、さらに実施例及び比較例の重金属処理剤をピペラジン−N,N’−ビスカルボジチオ酸塩の固形分換算で0.5重量部添加し、混練した後、環境庁告示13号試験を行った。
(Heavy metal treatment test)
30 parts by weight of water was added to 100 parts by weight of fly ash (Pb content = 2100 ppm), and the heavy metal treating agents of the examples and comparative examples were converted to 0 in terms of the solid content of piperazine-N, N′-biscarbodithioate. After adding 5 parts by weight and kneading, the Environmental Agency Notification No. 13 test was conducted.

溶出液中の鉛濃度はいずれも0.05ppm以下であった。   The lead concentration in the eluate was 0.05 ppm or less.

本発明の重金属処理剤は、飛灰、土壌、スラッジ等の重金属含有物中の鉛、カドミウム、クロム、水銀等の不溶化処理に用いられる。   The heavy metal treatment agent of the present invention is used for insolubilization treatment of lead, cadmium, chromium, mercury and the like in heavy metal-containing materials such as fly ash, soil, and sludge.

Claims (9)

室温(25℃)におけるピペラジン−N,N’−ビスカルボジチオ酸ナトリウムの濃度が25重量%を超える水溶液からなる重金属処理剤。   A heavy metal treating agent comprising an aqueous solution having a piperazine-N, N′-biscarbodithioic acid sodium concentration exceeding 25% by weight at room temperature (25 ° C.). ナトリウムカチオン以外の異種カチオンを含んでなる請求項1に記載の重金属処理剤。   The heavy metal treating agent according to claim 1, comprising a different cation other than a sodium cation. ナトリウムカチオンと異種カチオンのモル比が99:1〜80:20である請求項2に記載の重金属処理剤。   The heavy metal treating agent according to claim 2, wherein the molar ratio of the sodium cation to the different cation is 99: 1 to 80:20. 異種カチオンがカリウムカチオンである請求項2又は3に記載の重金属処理剤。   The heavy metal treating agent according to claim 2 or 3, wherein the different cation is a potassium cation. ピペラジン水溶液に二硫化炭素と水酸化ナトリウムを混合してピペラジン−N,N’−ビスカルボジチオ酸ナトリウムを製造する方法において、異種カチオンを含有する水酸化ナトリウムを用いることを特徴とする請求項1乃至4のいずれかに記載の重金属処理剤の製造方法。   2. A method for producing piperazine-N, N′-biscarbodithioate by mixing carbon disulfide and sodium hydroxide in an aqueous piperazine solution, wherein sodium hydroxide containing a different cation is used. The manufacturing method of the heavy metal processing agent in any one of thru | or 4. ナトリウムカチオンと異種カチオンのモル比が99:1〜80:20である請求項5に記載の製造方法。   The production method according to claim 5, wherein the molar ratio of the sodium cation to the different cation is 99: 1 to 80:20. 請求項1乃至4のいずれかに記載の重金属処理剤を重金属汚染物質と混合することを特徴とする重金属汚染物質の処理方法。   A method for treating a heavy metal pollutant, comprising mixing the heavy metal treating agent according to any one of claims 1 to 4 with a heavy metal pollutant. 重金属汚染物質が飛灰、土壌、スラッジである請求項7に記載の重金属汚染物質の処理方法。   The method for treating heavy metal contaminants according to claim 7, wherein the heavy metal contaminants are fly ash, soil, and sludge. 重金属汚染物質が鉛、カドミウム、クロム、水銀のいずれかを含有する物質である請求項7又は8に記載の重金属汚染物質の処理方法。   The method for treating a heavy metal contaminant according to claim 7 or 8, wherein the heavy metal contaminant is a substance containing any of lead, cadmium, chromium, and mercury.
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