JP2006316183A - Heavy metal treating agent and treating method of heavy metal using the same - Google Patents

Heavy metal treating agent and treating method of heavy metal using the same Download PDF

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JP2006316183A
JP2006316183A JP2005140959A JP2005140959A JP2006316183A JP 2006316183 A JP2006316183 A JP 2006316183A JP 2005140959 A JP2005140959 A JP 2005140959A JP 2005140959 A JP2005140959 A JP 2005140959A JP 2006316183 A JP2006316183 A JP 2006316183A
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heavy metal
treating agent
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dithiocarbamate
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JP4792810B2 (en
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Keisuke Tokunaga
敬助 徳永
Nobumasa Suzuki
紳正 鈴木
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Tosoh Corp
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a piperazinedithiocarbamate superior as a heavy metal treating agent without precipitation of solid contents at a low temperature even at a high concentration. <P>SOLUTION: This heavy metal treating agent comprises the piperazinedithiocarbamate having 0.7 wt.% or less of alkali hydroxide concentration. The agent does not precipitate the solid contents at a low temperature even when at a high concentration of 36-44 wt.% and does not generate gaseous substances such as hydrogen sulfide and carbon sulfide, so that it can be employed effectively and safely. <P>COPYRIGHT: (C)2007,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、特に高濃度でなおかつ低温において結晶の析出がない保存安定性に優れた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 is related to a heavy metal treatment agent that makes it possible to easily fix and elute harmful heavy metals such as zinc and copper, and has excellent storage stability especially at high concentrations and without crystal precipitation at low temperatures. The present invention relates to a heavy metal treating agent.

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。その様な重金属の処理方法として薬剤処理法があり、キレート系の重金属処理剤を添加して重金属を不溶化する方法が知られている。   Fly ash discharged from municipal waste incineration plants has a high heavy metal content and needs to be treated to prevent elution of heavy metals. As such a heavy metal treatment method, there is a chemical treatment method, and a method of insolubilizing heavy metal by adding a chelate heavy metal treatment agent is known.

重金属処理剤としてはアミン誘導体のジチオカルバミン酸塩が高性能であり、特にピペラジンジチオカルバミン酸塩では硫化水素及び二硫化炭素等の有害ガス発生が少ないために広く用いられている。(特許文献1参照)
しかしピペラジンジチオカルバミン酸塩の水溶液は、常温以上ではある程度高濃度にできるが、低温にすると高濃度における安定性が悪く、ジチオカルバミン酸塩の結晶が析出するという問題があった。重金属処理剤は水溶液で用いられるため、その輸送から重金属への使用に至るまで、経済性、取扱いの観点から高濃度であることが必要である。しかし、従来のピペラジンジチオカルバミン酸塩の水溶液からなる重金属処理剤では、合成直後は40重量%程度の水溶液が得られるものの、低温での安定性を維持するためには濃度を下げることが必要であり、高濃度のままでは低温での結晶析出の問題が避けられなかった。
As a heavy metal treating agent, an amine derivative dithiocarbamate has high performance, and piperazine dithiocarbamate is particularly widely used because it generates less harmful gases such as hydrogen sulfide and carbon disulfide. (See Patent Document 1)
However, the aqueous solution of piperazine dithiocarbamate can be increased to a certain degree at room temperature or higher, but there is a problem that the stability at a high concentration is poor at a low temperature, and crystals of dithiocarbamate precipitate. Since the heavy metal treating agent is used in an aqueous solution, it is necessary to have a high concentration from the viewpoint of economy and handling, from transportation to use for heavy metals. However, with a conventional heavy metal treating agent comprising an aqueous solution of piperazine dithiocarbamate, an aqueous solution of about 40% by weight can be obtained immediately after synthesis, but it is necessary to lower the concentration in order to maintain stability at low temperatures. However, the problem of crystal precipitation at low temperature is inevitable if the concentration remains high.

重金属処理剤の低温安定性を向上させる方法として、重金属処理剤成分にカルボン酸基、スルホン酸基、水酸基、リン酸基、ホスホン酸基およびこれらのアルカリ金属塩からなる群から選ばれる1種以上の官能基を有し、数平均分子量が1000〜30000のオリゴマーを添加する方法が提案されている。(例えば特許文献2)しかし、添加するオリゴマーの種類によっては重金属処理剤の性能、物性が変化する可能性があり、事前に詳細な検討を行う必要があった。また、ジエチルジチオカルバミン酸塩に対してピペラジン及びポリアミンからなる群から選ばれる1種を0.1から5重量%含有させる方法が提案されている。(例えば特許文献3)しかしこの方法はジエチルジチオカルバミン酸塩では効果があるが、ピペラジンジチオカルバミン酸塩に対するものではなかった。さらに、これらの方法では重金属処理剤にその原料以外の特定の添加物を添加することが必要であり、製造時における工程が増え、原単位が低下するという問題もあった。   One or more kinds selected from the group consisting of carboxylic acid groups, sulfonic acid groups, hydroxyl groups, phosphoric acid groups, phosphonic acid groups and their alkali metal salts as a method for improving the low temperature stability of the heavy metal treating agent There has been proposed a method of adding an oligomer having a functional group of and a number average molecular weight of 1,000 to 30,000. However, depending on the type of oligomer to be added, there is a possibility that the performance and physical properties of the heavy metal treating agent may change, and it is necessary to conduct a detailed examination in advance. Further, a method has been proposed in which 0.1 to 5% by weight of one kind selected from the group consisting of piperazine and polyamine is contained in diethyldithiocarbamate. However, this method is effective for diethyldithiocarbamate but not for piperazine dithiocarbamate. Furthermore, in these methods, it is necessary to add a specific additive other than the raw material to the heavy metal treating agent, and there is a problem that the number of steps during production increases and the basic unit decreases.

特許第3391173号(明細書第2項第0005欄1〜6行)Patent No. 3391173 (Specification, Item 2, Item 0005, Columns 1 to 6) 特許第3532798号(請求項1)Japanese Patent No. 3532798 (Claim 1) 特開2003−105318号(請求項1)JP 2003-105318 A (Claim 1)

ピペラジンジチオカルバミン酸塩を含んでなる水溶液は、重金属処理剤として優れているが、高濃度にすると低温で結晶が析出するという問題があった。本発明では、低温において結晶の析出がなく、保存時及び使用時の有害ガス発生量のない、安全で高濃度のピペラジンジチオカルバミン酸塩を含んでなる重金属処理剤を提供する。   An aqueous solution containing piperazine dithiocarbamate is excellent as a heavy metal treating agent, but there is a problem that crystals are precipitated at a low temperature when the concentration is high. In the present invention, there is provided a heavy metal treating agent comprising piperazine dithiocarbamate having a high concentration and which is safe and free from generation of crystals at low temperatures and does not generate harmful gases during storage and use.

本発明は上記の課題を解決すべく鋭意検討を重ねた結果、高濃度のピペラジンジチオカルバミン酸塩を主成分とする重金属処理剤では、ある特定の濃度範囲のアルカリ水酸化物含有量とすることにより、低温安定性を著しく向上させることができることを見出し、本発明を完成するに至った。   As a result of intensive investigations to solve the above-mentioned problems, the present invention provides a heavy metal treating agent mainly composed of a high concentration of piperazine dithiocarbamate, with an alkali hydroxide content in a specific concentration range. The inventors have found that the stability at low temperature can be remarkably improved, and have completed the present invention.

以下、本発明の重金属処理剤、及びその重金属処理剤を用いた重金属汚染物質の処理方法についてその詳細を説明する。   Hereinafter, the heavy metal treating agent of the present invention and the method for treating heavy metal contaminants using the heavy metal treating agent will be described in detail.

本発明の重金属処理剤はピペラジンジチオカルバミン酸塩を含んでなるものである。本発明のピペラジンジチオカルバミン酸塩としては、ピペラジンジチオカルバミン酸のアルカリ塩が使用でき、溶解度が高く、熱的に安定なナトリウム塩、カリウム塩であることが好ましい。ピペラジンジチオカルバミン酸塩にはビス体とモノ体とがあるが、本発明ではいずれの塩も用いることが出来るが、特にビス体が好ましい。   The heavy metal treating agent of the present invention comprises piperazine dithiocarbamate. As the piperazine dithiocarbamate of the present invention, an alkali salt of piperazine dithiocarbamate can be used, and it is preferably a sodium salt or potassium salt having high solubility and being thermally stable. Piperazine dithiocarbamate has a bis form and a mono form, and any salt can be used in the present invention, but a bis form is particularly preferred.

本発明で用いるアルカリ水酸化物は特に限定はないが、水酸化ナトリウム、水酸化カリウム等が例示でき、特に溶解度の高い水酸化カリウムを用いることが好ましい。   The alkali hydroxide used in the present invention is not particularly limited, and examples thereof include sodium hydroxide and potassium hydroxide, and it is particularly preferable to use potassium hydroxide having high solubility.

本発明の重金属処理剤中のアルカリ水酸化物は、0.7重量%以下であり、特に0.3〜0.7重量%の範囲、さらに0.4〜0.5重量%の範囲とすることが好ましい。0.3重量%未満とすると、重金属処理時において二硫化炭素等の有害ガスが発生する場合がある。一方、0.7重量%を超えると、常温以上では問題ないが、低温安定性が著しく低下し、冷寒地での使用において問題となる。   The alkali hydroxide in the heavy metal treating agent of the present invention is 0.7% by weight or less, particularly in the range of 0.3 to 0.7% by weight, more preferably in the range of 0.4 to 0.5% by weight. It is preferable. If it is less than 0.3% by weight, harmful gases such as carbon disulfide may be generated during heavy metal treatment. On the other hand, when it exceeds 0.7% by weight, there is no problem at room temperature or higher, but the low-temperature stability is remarkably lowered, which causes a problem in use in a cold region.

本発明の重金属処理剤中におけるアルカリ水酸化物の濃度は、酸塩基滴定等によって確認することができる。   The concentration of the alkali hydroxide in the heavy metal treating agent of the present invention can be confirmed by acid-base titration or the like.

従来、ピペラジンジチオカルバミン酸塩を主成分とする重金属処理剤においては、分解生成物である二硫化炭素等のガス発生抑制等の目的から、アルカリ水酸化物濃度が1.0重量%以上で合成されていた。本発明の重金属処理剤はアルカリ水酸化物を0.7重量%以下、特に0.3〜0.7重量%の範囲に制御することにより、36〜44重量%の高濃度においても低温安定性が高く、かつ有害ガスの発生量の低いものである。本発明において低温安定性を付与するアルカリ水酸化物は、ピペラジンジチオカルバミン酸塩の製造に用いる原料であり、新たな化合物を必要としないため、製造工程の負荷も小さい。   Conventionally, a heavy metal treating agent mainly composed of piperazine dithiocarbamate is synthesized with an alkali hydroxide concentration of 1.0% by weight or more for the purpose of suppressing gas generation such as carbon disulfide as a decomposition product. It was. The heavy metal treating agent of the present invention is stable at a low temperature even at a high concentration of 36 to 44% by weight by controlling the alkali hydroxide to 0.7% by weight or less, particularly 0.3 to 0.7% by weight. Is high and generates a low amount of harmful gases. In the present invention, the alkali hydroxide that imparts low-temperature stability is a raw material used for the production of piperazine dithiocarbamate and does not require a new compound, so the load on the production process is small.

本発明のピペラジンジチオカルバミン酸塩濃度は、36〜44重量%の高濃度の範囲、好ましくは38〜42重量%の範囲であることが好ましい。44重量%を超える範囲では低温において結晶の析出を完全に抑えることは困難であり、36重量%未満の濃度では、処理に必要な添加量が増大する。   The piperazine dithiocarbamate concentration of the present invention is preferably in the high concentration range of 36 to 44% by weight, and preferably in the range of 38 to 42% by weight. In the range exceeding 44% by weight, it is difficult to completely suppress the precipitation of crystals at a low temperature, and when the concentration is less than 36% by weight, the addition amount required for the treatment increases.

本発明の重金属処理剤は水溶液であるため、残りの成分は水である。本発明の重金属処理剤としての性能に悪影響を及ぼさない範囲において、他の成分(添加物、有機溶媒等)を含むことを妨げるものではない。   Since the heavy metal treating agent of the present invention is an aqueous solution, the remaining component is water. It does not preclude the inclusion of other components (additives, organic solvents, etc.) as long as the performance as a heavy metal treating agent of the present invention is not adversely affected.

次に本発明は、上述の重金属処理剤を使用した重金属汚染物質の処理方法について説明する。   Next, this invention demonstrates the processing method of the heavy metal contaminant which uses the above-mentioned heavy metal processing agent.

本発明の方法の重金属汚染物質の処理方法は、本発明の重金属処理剤を用いること以外は通常一般の手法が適用できる。   As a method for treating heavy metal contaminants according to the method of the present invention, a general method can be generally applied except that the heavy metal treating agent of the present invention is used.

例えば、重金属汚染物質が飛灰の場合、飛灰中の重金属含有量によっても異なるが、飛灰に対して重金属処理剤を0.01〜30重量%、多くは0.01〜5重量%の範囲で添加する。本発明の重金属処理剤は、有効成分であるピペラジンジチオカルバミン酸塩濃度が高いため、通常の方法より添加量は少なくできる。   For example, when the heavy metal pollutant is fly ash, it varies depending on the heavy metal content in the fly ash, but the heavy metal treatment agent is 0.01 to 30% by weight, most of which is 0.01 to 5% by weight. Add in range. Since the concentration of piperazine dithiocarbamate, which is an active ingredient, is high, the amount of the heavy metal treating agent of the present invention can be reduced as compared with the usual method.

また重金属処理剤と重金属汚染物質との混合時においては、処理した飛灰の廃棄を容易にするため、加湿水を混練時に添加してもよい。   Further, when mixing the heavy metal treating agent and the heavy metal contaminant, humidified water may be added during kneading in order to facilitate disposal of the treated fly ash.

本発明の重金属処理剤は低温安定性が高く、かつ重金属処理成分の濃度が高いため、冬季、寒冷地においても結晶の析出がなく、安定して使用することができ、少ない添加率で廃棄物を処理することができる。また、保存時及び使用時の有害ガス発生量も少なく、安全に使用することができる。   The heavy metal treatment agent of the present invention has high stability at low temperatures and high concentration of heavy metal treatment components, so that it can be used stably in winter and in cold regions, and can be used stably, and waste with a low addition rate. Can be processed. In addition, the amount of harmful gas generated during storage and use is small and can be used safely.

以下、実施例にて本発明を説明するが、本発明はこれらの実施例に限定されるものではない。   EXAMPLES Hereinafter, although an Example demonstrates this invention, this invention is not limited to these Examples.

実施例1
ピペラジンジチオカルバミン酸カリウムを40重量%、水酸化カリウムを0.3重量%となるように純水に溶解させ、ピペラジンジチオカルバミン酸カリウムと水酸化カリウムの混合水溶液を調製した。その水溶液150gとα―アルミナ0.5μm(和光純薬工業株式会社)10mg、テフロン(登録商標)回転子を150mlのガラス瓶に入れた。次に、それを恒温高湿槽LH41−13P(ナガノサイエンス株式会社)内に設置し、スターラーを用いて400〜500rpmで攪拌しながら、5℃から−5℃までの温度範囲を、−0.5℃/時間で冷却し、結晶が析出する温度を調査した。その結果を表1に示す。該溶液においては−5℃まで溶液中に結晶の析出は見られず、高い低温安定性があることを確認した。
Example 1
Piperazine dithiocarbamate potassium was dissolved in pure water so as to be 40 wt% potassium hydroxide and 0.3 wt% potassium to prepare a mixed aqueous solution of piperazine potassium dithiocarbamate and potassium hydroxide. 150 g of the aqueous solution, α-alumina 0.5 μm (Wako Pure Chemical Industries, Ltd.) 10 mg, and a Teflon (registered trademark) rotor were placed in a 150 ml glass bottle. Next, it is installed in a constant temperature and high humidity tank LH41-13P (Nagano Science Co., Ltd.) and stirred at 400 to 500 rpm using a stirrer, and the temperature range from 5 ° C. to −5 ° C. is set to −0. After cooling at 5 ° C./hour, the temperature at which crystals were precipitated was investigated. The results are shown in Table 1. In the solution, no precipitation of crystals was observed in the solution up to −5 ° C., and it was confirmed that the solution had high low temperature stability.

40mlのガラスバイアル瓶に該水溶液を3ml採り、25℃で1日静置後のバイアル瓶内の気体の二硫化炭素濃度をガスクロマトグラフィーにより測定を行った。その結果を表1に示す。その濃度は1ppm以下であり、ガス発生量が低いことが確認された。   3 ml of the aqueous solution was taken in a 40 ml glass vial, and the carbon disulfide concentration of the gas in the vial after standing at 25 ° C. for 1 day was measured by gas chromatography. The results are shown in Table 1. The concentration was 1 ppm or less, and it was confirmed that the amount of gas generated was low.

該ピペラジンジチオカルバミン酸カリウム水溶液を用いて、重金属含有飛灰Aの処理試験を行った。所定量(飛灰に対して1重量%、2重量%)の該水溶液と飛灰に対して30重量%の加湿水を添加し、5分間混練を行った。その混練後の灰において環境庁告示第13号試験を行った。試験に用いた飛灰Aの組成を表2、環境庁告示第13号試験結果を表3に示す。飛灰に対して2重量%の該水溶液の添加で、重金属類の溶出を基準値以下に処理でき、高い重金属処理性能であった。   Using the piperazine potassium dithiocarbamate aqueous solution, a treatment test for heavy metal-containing fly ash A was conducted. A predetermined amount (1% by weight, 2% by weight with respect to fly ash) of the aqueous solution and 30% by weight of humidified water with respect to fly ash were added and kneaded for 5 minutes. The ash after kneading was subjected to the Environmental Agency Notification No. 13 test. The composition of fly ash A used in the test is shown in Table 2, and the Environmental Agency Notification No. 13 test results are shown in Table 3. By adding 2% by weight of the aqueous solution with respect to fly ash, the elution of heavy metals could be treated to a standard value or less, and the heavy metal treatment performance was high.

実施例2
ピペラジンジチオカルバミン酸カリウムを40重量%、水酸化カリウムを0.7重量%となるように純水に溶解させ、ピペラジンジチオカルバミン酸カリウムと水酸化カリウムの混合水溶液を調製した。実施例1と同様にして結晶析出温度を調べた。その結果を表1に示す。−5℃においても結晶の析出が見られず、高い低温安定性があることを確認した。
Example 2
Piperazine dithiocarbamate potassium was dissolved in pure water so as to be 40 wt% potassium hydroxide and 0.7 wt% potassium to prepare a mixed aqueous solution of potassium piperazine dithiocarbamate and potassium hydroxide. The crystal precipitation temperature was examined in the same manner as in Example 1. The results are shown in Table 1. Crystal precipitation was not observed even at -5 ° C, and it was confirmed that there was high low-temperature stability.

また、実施例1と同様にして二硫化炭素濃度測定を行った。その結果を表1に示す。その測定濃度は1ppm以下であり、ガス発生量が低いことが確認された。   Further, the carbon disulfide concentration was measured in the same manner as in Example 1. The results are shown in Table 1. The measured concentration was 1 ppm or less, and it was confirmed that the amount of gas generated was low.

実施例1と同様にして重金属含有飛灰Aの処理試験を行った。環境庁告示第13号試験結果を表4に示す。飛灰に対して2重量%の該水溶液の添加で、重金属類の溶出を基準値以下に処理でき、高い重金属処理性能であった。   A treatment test of heavy metal-containing fly ash A was conducted in the same manner as in Example 1. Table 4 shows the results of the Environmental Agency Notification No. 13 test. By adding 2% by weight of the aqueous solution with respect to fly ash, the elution of heavy metals could be treated to a standard value or less, and the heavy metal treatment performance was high.

比較例1
ピペラジンジチオカルバミン酸カリウムを40重量%、水酸化カリウムを1.5重量%となるように純水に溶解させ、ピペラジンジチオカルバミン酸カリウムと水酸化カリウムの混合水溶液を調製した。実施例1と同様にして結晶析出温度を調べた。その結果を表1に示す。0℃において結晶の析出が確認された。実施例に比べて高い温度で結晶の析出が見られた。実施例1と同様にして重金属含有飛灰Aの処理試験を行った。環境庁告示第13号試験結果を表5に示す。
Comparative Example 1
Piperazine dithiocarbamate potassium was dissolved in pure water to a concentration of 40% by weight and potassium hydroxide to 1.5% by weight to prepare a mixed aqueous solution of piperazine dithiocarbamate potassium and potassium hydroxide. The crystal precipitation temperature was examined in the same manner as in Example 1. The results are shown in Table 1. Crystal precipitation was confirmed at 0 ° C. Crystal precipitation was observed at a higher temperature than in the Examples. A treatment test of heavy metal-containing fly ash A was conducted in the same manner as in Example 1. Table 5 shows the results of the Environmental Agency Notification No. 13 test.

比較例2
ピペラジンジチオカルバミン酸カリウムを40重量%、水酸化カリウムを0.8重量%となるように純水に溶解させ、ピペラジンジチオカルバミン酸カリウムと水酸化カリウムの混合水溶液を調製した。実施例1と同様にして結晶析出温度を調べた。その結果を表1に示す。−3℃において結晶の析出が確認された。実施例に比べて高い温度で結晶の析出が起こることが確認された。
Comparative Example 2
Piperazine dithiocarbamate potassium was dissolved in pure water so as to be 40% by weight and potassium hydroxide was 0.8% by weight to prepare a mixed aqueous solution of piperazine dithiocarbamate potassium and potassium hydroxide. The crystal precipitation temperature was examined in the same manner as in Example 1. The results are shown in Table 1. Crystal precipitation was confirmed at -3 ° C. It was confirmed that crystal precipitation occurred at a higher temperature than in the examples.

比較例3
ピペラジンジチオカルバミン酸カリウムを40重量%、水酸化カリウムを0.2重量%となるように純水に溶解させ、ピペラジンジチオカルバミン酸カリウムと水酸化カリウムの混合水溶液を調製した。実施例1と同様にして二硫化炭素濃度測定を行った。その結果を表1に示す。その測定濃度は2.4ppmであり、実施例に比べて高い値となり、実施例に比べて剤の安定性が低かった。
Comparative Example 3
Piperazine dithiocarbamate potassium was dissolved in pure water so as to be 40 wt% potassium hydroxide and 0.2 wt% to prepare a mixed aqueous solution of potassium piperazine dithiocarbamate and potassium hydroxide. The carbon disulfide concentration was measured in the same manner as in Example 1. The results are shown in Table 1. The measured concentration was 2.4 ppm, which was a higher value than that of the example, and the stability of the agent was lower than that of the example.

比較例4
ピペラジンジチオカルバミン酸カリウムを40重量%、水酸化カリウムを0.1重量%となるように純水に溶解させ、ピペラジンジチオカルバミン酸カリウムと水酸化カリウムの混合水溶液を調製した。実施例1と同様にして二硫化炭素濃度測定を行った。その結果を表1に示す。その測定濃度は7.5ppmであり、実施例に比べて高い値となり、実施例に比べて剤の安定性が低かった。
Comparative Example 4
Piperazine dithiocarbamate potassium was dissolved in pure water so as to be 40 wt% potassium hydroxide and 0.1 wt% potassium to prepare a mixed aqueous solution of potassium piperazine dithiocarbamate and potassium hydroxide. The carbon disulfide concentration was measured in the same manner as in Example 1. The results are shown in Table 1. The measured concentration was 7.5 ppm, which was a higher value than that of the example, and the stability of the agent was lower than that of the example.

Figure 2006316183
Figure 2006316183

Figure 2006316183
Figure 2006316183

Figure 2006316183
Figure 2006316183

Figure 2006316183
Figure 2006316183

Figure 2006316183
Figure 2006316183

本発明の重金属処理剤は、低温時に結晶析出が起こりにくく、かつ、ガス発生量も少ないために、特に寒冷地における重金属汚染物質処理に有効である。
The heavy metal treating agent of the present invention is effective for treating heavy metal pollutants particularly in cold regions because crystal precipitation hardly occurs at low temperatures and the amount of gas generation is small.

Claims (6)

0.7重量%以下のアルカリ水酸化物、36〜44重量%のピペラジンジチオカルバミン酸塩、及び水を含んでなる重金属処理剤。 A heavy metal treating agent comprising 0.7% by weight or less of alkali hydroxide, 36 to 44% by weight of piperazine dithiocarbamate, and water. アルカリ水酸化物濃度が0.3〜0.7重量%である請求項1に記載の重金属処理剤。 The heavy metal treating agent according to claim 1, wherein the alkali hydroxide concentration is 0.3 to 0.7% by weight. ピペラジンジチオカルバミン酸塩がピペラジンジチオカルバミン酸カリウムである請求項1に記載の重金属処理剤。 The heavy metal treating agent according to claim 1, wherein the piperazine dithiocarbamate is potassium piperazine dithiocarbamate. 請求項1乃至請求項3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 claim 1 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4に記載の重金属汚染物質の処理方法。 The heavy metal contaminant treatment method according to claim 4, wherein the heavy metal contaminant is fly ash, soil, or 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4及至請求項5に記載の重金属汚染物質の処理方法。
6. The method for treating heavy metal contaminants according to claim 4, wherein the heavy metal contaminant is a substance containing any one of lead, cadmium, chromium and mercury.
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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008184470A (en) * 2006-04-27 2008-08-14 Tosoh Corp Heavy metal-treating agent excellent in low temperature stability and method for treating heavy metal therewith
JP2008273996A (en) * 2007-01-11 2008-11-13 Tosoh Corp Heavy metal treatment agent and method for treating heavy metal contaminant
WO2012073976A1 (en) * 2010-11-30 2012-06-07 東ソー株式会社 Aqueous solution of piperazine-n, n'-bis-carbodithioate, and production method for same
JP2019026793A (en) * 2017-08-02 2019-02-21 オリエンタル技研工業株式会社 Heavy metal stabilization agent and manufacturing method therefor, and stabilization method of heavy metal using the same
CN111773607A (en) * 2020-08-05 2020-10-16 成都赢纳环保科技有限公司 Heavy metal chelating agent and solid product thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08224560A (en) * 1994-12-02 1996-09-03 Tosoh Corp Fixing of heavy metals in fly ash
JP2003221389A (en) * 2001-11-21 2003-08-05 Nippon Soda Co Ltd Method for producing aqueous solution containing piperazine biscarbodithioate
JP2004115639A (en) * 2002-09-26 2004-04-15 Nippon Soda Co Ltd Heavy metal fixing agent and low-temperature stabilization method of heavy metal fixing agent

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08224560A (en) * 1994-12-02 1996-09-03 Tosoh Corp Fixing of heavy metals in fly ash
JP2003221389A (en) * 2001-11-21 2003-08-05 Nippon Soda Co Ltd Method for producing aqueous solution containing piperazine biscarbodithioate
JP2004115639A (en) * 2002-09-26 2004-04-15 Nippon Soda Co Ltd Heavy metal fixing agent and low-temperature stabilization method of heavy metal fixing agent

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008184470A (en) * 2006-04-27 2008-08-14 Tosoh Corp Heavy metal-treating agent excellent in low temperature stability and method for treating heavy metal therewith
JP2008273996A (en) * 2007-01-11 2008-11-13 Tosoh Corp Heavy metal treatment agent and method for treating heavy metal contaminant
WO2012073976A1 (en) * 2010-11-30 2012-06-07 東ソー株式会社 Aqueous solution of piperazine-n, n'-bis-carbodithioate, and production method for same
CN103237796A (en) * 2010-11-30 2013-08-07 东曹株式会社 Aqueous solution of piperazine-N, N'-bis-carbodithioate, and production method for same
JP2019026793A (en) * 2017-08-02 2019-02-21 オリエンタル技研工業株式会社 Heavy metal stabilization agent and manufacturing method therefor, and stabilization method of heavy metal using the same
CN111773607A (en) * 2020-08-05 2020-10-16 成都赢纳环保科技有限公司 Heavy metal chelating agent and solid product thereof

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