JP2013087274A - Heavy metal-fixing agent - Google Patents

Heavy metal-fixing agent Download PDF

Info

Publication number
JP2013087274A
JP2013087274A JP2011232368A JP2011232368A JP2013087274A JP 2013087274 A JP2013087274 A JP 2013087274A JP 2011232368 A JP2011232368 A JP 2011232368A JP 2011232368 A JP2011232368 A JP 2011232368A JP 2013087274 A JP2013087274 A JP 2013087274A
Authority
JP
Japan
Prior art keywords
aqueous solution
sulfur
heavy metal
polysulfide
fixing agent
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2011232368A
Other languages
Japanese (ja)
Inventor
Junji Hoshi
純二 星
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP2011232368A priority Critical patent/JP2013087274A/en
Publication of JP2013087274A publication Critical patent/JP2013087274A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

PROBLEM TO BE SOLVED: To solve the problem that, in a polysulfide aqueous solution made from quicklime or slaked lime and sulfur and used as a heavy metal-fixing agent in the fields of wastewater treatment and soil treatment, the reactivity of the solution with heavy metal ions is low, the fixing of heavy metals is insufficient, and the odor of the hydrogen sulfide is generated.SOLUTION: A mixture having calcium hydroxide and sulfur as principal ingredients is obtained by blowing ozone gas into a polysulfide aqueous solution or adding an alkali agent thereto to change the structure of polysulfide. The use of this mixed aqueous solution as the fixing agent increases the reactivity with heavy metal ions and suppresses the generation of odor.

Description

本発明は、排水処理や土壌処理、焼却灰処理などの分野であって、排水や土壌、焼却灰の中に有害な重金属を含む場合、その重金属を固定化し無害化する重金属固定剤に関する。 The present invention relates to a heavy metal fixing agent that is used in wastewater treatment, soil treatment, incineration ash treatment, and the like, and in the case where harmful heavy metals are contained in wastewater, soil, or incineration ash, the heavy metal is fixed and detoxified.

排水や土壌、焼却灰中の重金属を固定化する処理剤として、多硫化物を主成分とする処理剤が複数存在している。こうした多硫化物を主成分とする処理材は、鉛、カドミウム、水銀、クロム、ヒ素などの有害な重金属を硫化し、安定で無害な硫化物に変えることが知られている。 There are a plurality of treatment agents mainly composed of polysulfides as treatment agents for immobilizing heavy metals in waste water, soil, and incineration ash. It is known that such a treatment material containing polysulfide as a main component sulfidizes harmful heavy metals such as lead, cadmium, mercury, chromium and arsenic, and converts it into a stable and harmless sulfide.

特開昭59−59281号広報JP-A-59-59281 特開2005−213375号広報Japanese Laid-Open Patent Publication No. 2005-213375

通常、多硫化物を生成する際には、生石灰や消石灰あるいは焼却灰などのアルカリ材と硫黄を水と混合し、加熱・加圧して製造される。この際、アルカリ材と硫黄が結合して多硫化物を形成するとされる。しかし、この製法では、アルカリ材と硫黄が飽和状態になるまで含有することで安定な水溶液となり、これを処理剤として使用した場合、重金属イオンとの反応において、十分な反応を起こさなかったり、また反応しても硫化水素を発生してしまい、きわめて劣悪な環境での作業となってしまう。 Usually, when polysulfide is produced, alkaline material such as quick lime, slaked lime or incinerated ash and sulfur are mixed with water, and heated and pressurized. At this time, the alkali material and sulfur are combined to form a polysulfide. However, in this production method, a stable aqueous solution is obtained by containing the alkali material and sulfur until they are saturated, and when this is used as a treating agent, the reaction with heavy metal ions does not cause sufficient reaction, or Even if it reacts, hydrogen sulfide is generated, and it becomes a work in a very poor environment.

たとえば、生石灰あるいは消石灰と硫黄から生成される化合物が、Bazhenoviteと名付けられた多硫化物で、結晶構造は、CaS5・CaS2O3・6Ca(OH)2・20(H2O)であるとされている。この化合物の形態を変え、水酸化カルシウムと硫黄を主成分とする混合体とすることが有効であることを見出した。
水酸化カルシウムと硫黄を主成分とする混合体とする方法としては、多硫化物水溶液にオゾンを吹き込む方法および多硫化物水溶液にアルカリ剤を添加する方法を考案した。
For example, a compound produced from quicklime or slaked lime and sulfur is a polysulfide named Bazhenovite, and its crystal structure is said to be CaS5 · CaS2O3 · 6Ca (OH) 2 · 20 (H2O). It has been found that it is effective to change the form of this compound to form a mixture mainly composed of calcium hydroxide and sulfur.
As a method of preparing a mixture mainly composed of calcium hydroxide and sulfur, a method of blowing ozone into a polysulfide aqueous solution and a method of adding an alkali agent to the polysulfide aqueous solution have been devised.

CaS5・CaS2O3・6Ca(OH)2・20(H2O)という結晶構造から水酸化カルシウムと硫黄を主成分とする混合体とすることで、重金属との反応性を改善し、硫化水素の発生を抑えることができるという知見を得た。 From the crystal structure of CaS5 ・ CaS2O3 ・ 6Ca (OH) 2 ・ 20 (H2O), by making a mixture mainly composed of calcium hydroxide and sulfur, the reactivity with heavy metals is improved and the generation of hydrogen sulfide is suppressed. I got the knowledge that I can do it.

多硫化物水溶液にオゾンガスを吹き込む例を示す。An example in which ozone gas is blown into the polysulfide aqueous solution is shown. 多硫化物水溶液および本発明の水酸化カルシウムと硫黄を主成分とする混合体のX線回折データ。 上段:水酸化ナトリウムの添加による本発明重金属固定剤 中断:オゾン処理による本発明重金属固定剤 下段:市販の多硫化物水溶液X-ray diffraction data of a polysulfide aqueous solution and a mixture of calcium hydroxide and sulfur as main components of the present invention. Upper: Heavy metal fixative of the present invention by addition of sodium hydroxide Discontinuation: Heavy metal fixative of the present invention by ozone treatment Lower: Commercial polysulfide aqueous solution 本発明と比較例の重金属固定化試験の結果Results of heavy metal immobilization tests of the present invention and comparative examples

水に生石灰あるいは消石灰と硫黄を混合し、加熱・加圧することで作られる多硫化物水溶液に関し、この水溶液にオゾンガスを吹き込み、結晶構造を変えることで、水酸化カルシウムと硫黄を主成分とする混合体を生成する。もう一法として、この水溶液に水酸化ナトリウムなどのアルカリ剤を添加しても、水酸化カルシウムと硫黄を主成分とする混合体を生成することができる。これらを重金属の固定化剤として使用すると、多硫化物水溶液に比べ、重金属の硫化物化を促進し、硫化水素の発生を抑えることができることを見出した。 About polysulfide aqueous solution made by mixing quick lime or slaked lime and sulfur in water, heating and pressurizing, mixing ozone hydroxide and sulfur as main components by blowing ozone gas into this aqueous solution and changing the crystal structure Generate a body. As another method, even when an alkaline agent such as sodium hydroxide is added to this aqueous solution, a mixture mainly composed of calcium hydroxide and sulfur can be produced. It has been found that when these are used as fixing agents for heavy metals, the formation of hydrogen sulfide can be promoted and the generation of hydrogen sulfide can be suppressed compared to polysulfide aqueous solutions.

以下に具体例を示し、本発明を更に詳しく説明する。
まずは、オゾンガスによる方法に関して説明する。
重金属固定剤を生成するために、市販の多硫化物水溶液(宮内硫黄合剤社製の石灰硫黄合剤)にオゾンガスを吹き込んだ。
図1にオゾンを吹き込む概要を示す。
1リッターの多硫化物水溶液を容器に入れ、これを撹拌し、この中にパイプを通してオゾンガスを毎分2リッターの量で吹き込み、8時間の保持をした。
オゾンを吹き込むことによって、市販の多硫化物水溶液の構造を崩し、水酸化カルシウムと硫黄を主成分とする混合体とした。
次いで、アルカリ剤の添加に関して説明する。
同様に市販の多硫化物水溶液(宮内硫黄合剤社製の石灰硫黄合剤)1リッターに、工業用のフレーク状水酸化ナトリウムを5重量%添加した。水酸化ナトリウムを添加しながら撹拌すると、固形物が沈殿するので、これをろ過分離し、水溶液を得た。この得られた水溶液は、水酸化カルシウムと硫黄を主成分とする混合体である。
この現象は、水酸化ナトリウムだけではなく、他のアルカリ剤、たとえば、水酸化カルシウムや水酸化カリウム、炭酸ナトリウムなどでも、同様の結果となることを確認している。
また、当然ながら、市販の多硫化物水溶液ではなく、圧力釜にて、生石灰あるいは消石灰と硫黄と水を混合・加熱して、多硫化物水溶液を得た場合でも、同様にオゾンガスを吹き込む、あるいは、アルカリ剤を添加することによって、水酸化カルシウムと硫黄を主成分とする混合体を得ることができる。
Hereinafter, the present invention will be described in more detail with reference to specific examples.
First, a method using ozone gas will be described.
In order to produce a heavy metal fixing agent, ozone gas was blown into a commercially available aqueous polysulfide solution (lime sulfur mixture manufactured by Miyauchi Sulfur Mixture Co., Ltd.).
FIG. 1 shows an outline of blowing ozone.
One liter of polysulfide aqueous solution was put into a container, stirred, and ozone gas was blown into the container at a rate of 2 liters per minute through the pipe and held for 8 hours.
By blowing in ozone, the structure of the commercially available polysulfide aqueous solution was broken to obtain a mixture mainly composed of calcium hydroxide and sulfur.
Next, the addition of an alkaline agent will be described.
Similarly, 5% by weight of industrial flaky sodium hydroxide was added to 1 liter of a commercially available aqueous solution of polysulfide (lime sulfur mixture manufactured by Miyauchi Sulfur Mixture Co., Ltd.). When the mixture was stirred while sodium hydroxide was added, a solid was precipitated, which was separated by filtration to obtain an aqueous solution. The obtained aqueous solution is a mixture mainly composed of calcium hydroxide and sulfur.
It has been confirmed that this phenomenon is not only caused by sodium hydroxide but also by other alkaline agents such as calcium hydroxide, potassium hydroxide, and sodium carbonate.
Of course, even when a polysulfide aqueous solution is obtained by mixing and heating quick lime or slaked lime with sulfur and water in a pressure cooker instead of a commercially available polysulfide aqueous solution, ozone gas is blown in the same manner, or By adding an alkali agent, a mixture mainly composed of calcium hydroxide and sulfur can be obtained.

市販の多硫化物水溶液と本発明の混合体を液体がなくなるまで常温で乾燥し、この乾燥にて得られた粉末を用いて、X線回折を行った。この結果を図2に示す。
図2によれば、市販の多硫化物水溶液の結晶構造は、CaS5・CaS2O3・6Ca(OH)2・20(H2O)であるが、これにオゾン処理した混合体も、水酸化ナトリウムを添加した混合体も、水酸化カルシウムと硫黄のピークに変化している。
これらのX線回折データに関して、今後データベースが蓄積され、ピークを示している物質の構造が変更される可能性があるが、多硫化物水溶液とは明らかに異なるピークであることは間違いない。本発明では、現状でのデータベースから、水酸化カルシウムと硫黄を主成分とする混合体としているが、結晶構造が変更されれば、物質名の変更が必然であることを追記する。
A commercially available polysulfide aqueous solution and the mixture of the present invention were dried at room temperature until the liquid disappeared, and X-ray diffraction was performed using the powder obtained by this drying. The result is shown in FIG.
According to FIG. 2, the crystal structure of the commercially available polysulfide aqueous solution is CaS5 · CaS2O3 · 6Ca (OH) 2 · 20 (H2O), but the mixture treated with ozone was also added with sodium hydroxide. The mixture also changes to calcium hydroxide and sulfur peaks.
Regarding these X-ray diffraction data, there is a possibility that the database will be accumulated in the future and the structure of the substance showing the peak may be changed. In the present invention, from the current database, a mixture containing calcium hydroxide and sulfur as main components is used. However, it is added that if the crystal structure is changed, the substance name must be changed.

図3は、本発明のオゾン処理による水酸化カルシウムと硫黄を主成分とする混合体と市販品である多硫化物水溶液に関して、重金属との反応性および硫化水素の発生状況を調査した結果である。
それぞれの濃度に設定したニッケルイオン溶液、ヒ素イオン溶液、鉄イオン溶液、亜鉛イオン溶液の4種を準備した。なお、このときの水溶液のpHは、5〜6とした。この溶液をビーカーに1リッター採取し、これにそれぞれの水溶液を1滴ずつ添加を行った。水溶液の添加の前後での各イオン濃度を測定した。また、添加の際に、温泉臭である硫化水素の臭気の有無を評価した。
図3に示す通り、4種類の重金属イオンに対し、いずれも本発明の重金属固定剤が有効であることがわかる。また、臭気に関しても、本発明の重金属固定剤が有利であることがわかる。
FIG. 3 is a result of investigating the reactivity with heavy metals and the generation state of hydrogen sulfide with respect to the mixture of calcium hydroxide and sulfur by the ozone treatment according to the present invention and the commercially available polysulfide aqueous solution. .
Four types of nickel ion solution, arsenic ion solution, iron ion solution, and zinc ion solution were prepared for each concentration. In addition, pH of the aqueous solution at this time was 5-6. One liter of this solution was collected in a beaker, and one drop of each aqueous solution was added thereto. Each ion concentration before and after the addition of the aqueous solution was measured. In addition, the presence or absence of hydrogen sulfide odor, which is a hot spring odor, was evaluated during the addition.
As shown in FIG. 3, it can be seen that the heavy metal fixing agent of the present invention is effective for four types of heavy metal ions. Moreover, it turns out that the heavy metal fixing agent of this invention is advantageous also regarding an odor.

1 オゾンガス吹き込み用パイプ
2 撹拌機
3 容器
4 多硫化物水溶液
1 Ozone gas blowing pipe 2 Stirrer 3 Container 4 Polysulfide aqueous solution

Claims (3)

X線回折における最大強度の回折ピークの回折角度(2θ)が34.5°±2°および23.5°±2°である水酸化カルシウムと硫黄を主成分とする重金属固定剤。 A heavy metal fixing agent mainly composed of calcium hydroxide and sulfur having diffraction angles (2θ) of diffraction peaks of maximum intensity in X-ray diffraction of 34.5 ° ± 2 ° and 23.5 ° ± 2 °. 多硫化物水溶液にオゾンガスを吹き込むことによって、請求項1に記載の水酸化カルシウムと硫黄を主成分とする重金属固定剤を製造する方法。 The method for producing a heavy metal fixing agent mainly comprising calcium hydroxide and sulfur according to claim 1 by blowing ozone gas into the polysulfide aqueous solution. 多硫化物水溶液にアルカリ剤を添加することによって、請求項1に記載の水酸化カルシウムと硫黄を主成分とする重金属固定剤を製造する方法。 The method of manufacturing the heavy metal fixing agent which has calcium hydroxide and sulfur as a main component of Claim 1 by adding an alkaline agent to polysulfide aqueous solution.
JP2011232368A 2011-10-24 2011-10-24 Heavy metal-fixing agent Pending JP2013087274A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2011232368A JP2013087274A (en) 2011-10-24 2011-10-24 Heavy metal-fixing agent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2011232368A JP2013087274A (en) 2011-10-24 2011-10-24 Heavy metal-fixing agent

Publications (1)

Publication Number Publication Date
JP2013087274A true JP2013087274A (en) 2013-05-13

Family

ID=48531512

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2011232368A Pending JP2013087274A (en) 2011-10-24 2011-10-24 Heavy metal-fixing agent

Country Status (1)

Country Link
JP (1) JP2013087274A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105016403A (en) * 2015-06-24 2015-11-04 陈伟 Domestic sewage ammonia nitrogen removal agent
CN105016402A (en) * 2015-06-24 2015-11-04 陈伟 Domestic sewage treatment agent
JP2020032386A (en) * 2018-08-31 2020-03-05 デンカ株式会社 Metal scavenger

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105016403A (en) * 2015-06-24 2015-11-04 陈伟 Domestic sewage ammonia nitrogen removal agent
CN105016402A (en) * 2015-06-24 2015-11-04 陈伟 Domestic sewage treatment agent
JP2020032386A (en) * 2018-08-31 2020-03-05 デンカ株式会社 Metal scavenger

Similar Documents

Publication Publication Date Title
KR101879598B1 (en) Apparatus and method for producing liquid ferrate
US7938766B2 (en) Calcium-sodium polysulfide chemical reagent and production methods
JP5975130B1 (en) Compound treatment agent for acid gas and heavy metal, and method for treating acid gas and heavy metal
JP2011056495A (en) Method for preventing elution of heavy metal
JP2013087274A (en) Heavy metal-fixing agent
JP5939328B1 (en) Compound treatment agent for acid gas and heavy metal, and method for treating acid gas and heavy metal
Sailo et al. Efficient use of ferrate (VI) for the remediation of wastewater contaminated with metal complexes
JP2007144405A (en) Method for treating boron-containing waste water and agent therefor
JP2008272590A (en) Heavy metal treating agent and stabilization treatment method of heavy metal contaminant using the same
JP4954131B2 (en) Treatment method of water containing borofluoride
JP5214756B2 (en) Boron-containing water treatment method and boron-containing water treatment apparatus
JP2008264627A (en) Waste treatment material and treatment method for detoxifying fly ash (soot and dust) and burned ash or the like
CN105130050A (en) Method for removing nitrogen and phosphorus in waste water
JP2013193939A (en) Method of producing ferric nitrate aqueous solution and sodium nitrite
JP2007260553A (en) Treatment method of exhaust gas and fly ash of incineration plant
JP2011131115A (en) Sludge treating agent and sludge treatment method
JP2014073441A (en) Insolubilizing method of heavy metal
KR20210015999A (en) Exhaust gas purifying agent and exhaust gas purifying method using the same
JP6034011B2 (en) Heavy metal insolubilizer and method for insolubilizing heavy metal
JP2013060517A (en) Heavy metal treating agent, manufacturing method of heavy metal treating agent, and method for treatment of heavy metal-containing material using the same
JP4696017B2 (en) Treatment method for boron-containing wastewater
JP2008272580A (en) Treatment method for heavy metals in waste ash
JP2011194248A (en) Heavy metal treatment agent and stable treatment method for heavy metal pollutant using the same
Song et al. Oxidation of inorganic contaminants by ferrates (VI)-A review
JP5182115B2 (en) Heavy metal immobilization treatment method, treatment agent used therefor, and production method thereof