JPH0975892A - Process of solidifying heavy metal in fly ash by low-molecular polyamine derivative - Google Patents

Process of solidifying heavy metal in fly ash by low-molecular polyamine derivative

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Publication number
JPH0975892A
JPH0975892A JP7234854A JP23485495A JPH0975892A JP H0975892 A JPH0975892 A JP H0975892A JP 7234854 A JP7234854 A JP 7234854A JP 23485495 A JP23485495 A JP 23485495A JP H0975892 A JPH0975892 A JP H0975892A
Authority
JP
Japan
Prior art keywords
fly ash
heavy metal
salt
nitrogen atoms
dithiocarbamate
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
JP7234854A
Other languages
Japanese (ja)
Inventor
Mitsuru Takahashi
満 高橋
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.)
Tosoh Corp
Original Assignee
Tosoh Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Tosoh Corp filed Critical Tosoh Corp
Priority to JP7234854A priority Critical patent/JPH0975892A/en
Publication of JPH0975892A publication Critical patent/JPH0975892A/en
Pending legal-status Critical Current

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  • Fire-Extinguishing Compositions (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a process of solidifying a heavy metal in fly ash generated by an incinerator for municipal waste, industrial waste and the like by using a heavy metal catching agent of high chelating capability so that the heavy metal is not eluted by rainwater or seawater. SOLUTION: Dithiocarbamic acid derived from a polyethylenepolyamine of 4-8 nitrogen atoms or at least one kind of its dithiocarbamate is mixed into fly ash together with water and kneaded.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は都市ゴミや産業廃棄
物などの焼却プラントからの飛灰を処理するに際し、飛
灰中に含有される鉛、水銀、クロム、カドミウム、亜鉛
及び銅等の有害な重金属をより効率良く固定化し不溶出
化することを可能にする方法に関するものである。
TECHNICAL FIELD The present invention relates to the treatment of fly ash from an incinerator plant such as municipal waste and industrial waste, which is harmful to lead, mercury, chromium, cadmium, zinc and copper contained in the fly ash. The present invention relates to a method for more efficiently immobilizing and immobilizing heavy metals.

【0002】[0002]

【従来の技術】都市ゴミや産業廃棄物などの焼却プラン
トから排出される飛灰は電気集塵機(EP)やバグフィ
ルター(BF)で捕集されたのち埋め立てや海洋投棄さ
れている。しかし、これら飛灰は有害な重金属を多く含
んでおり、埋め立て地からの雨水等による鉛、水銀等の
溶出は環境汚染の可能性がある。このため飛灰は特別管
理廃棄物に指定され、「セメント固化法」、「酸その他
の溶剤による抽出法」、「溶融固定化法」あるいは「薬
剤添加法」のいずれかの処理を施した後、廃棄すること
が義務づけられている。このうち薬剤添加法は他の方法
に比べ、一般に、装置ならびに取扱いが簡便なため種々
検討されている。例えば、ポリエチレンイミン等のポリ
アミンを原料とするジチオカルバミン酸塩に無機硫化物
を併用する方法が特開平5−50055号公報に開示さ
れ、ジエチレントリアミンを原料とするジチオカルバミ
ン酸塩を使用する方法が特開平6−79254号公報に
開示されている。
2. Description of the Related Art Fly ash discharged from an incineration plant such as municipal waste or industrial waste is collected by an electric dust collector (EP) or a bag filter (BF) and then landfilled or dumped in the ocean. However, these fly ash contains a lot of harmful heavy metals, and elution of lead, mercury, etc. from landfill by rainwater etc. may cause environmental pollution. For this reason, fly ash is designated as a specially controlled waste, and after undergoing any of the "cement solidification method", "acid or other solvent extraction method", "melt fixation method" or "chemical addition method" , Must be discarded. Among them, the drug addition method is generally studied in various ways because it is simpler in equipment and handling than other methods. For example, a method of using an inorganic sulfide in combination with a dithiocarbamate salt made from a polyamine such as polyethyleneimine is disclosed in JP-A-5-50055, and a method using a dithiocarbamate salt made from diethylenetriamine as a raw material is disclosed in JP-A-6-55005. It is disclosed in Japanese Patent Publication No. 79254.

【0003】[0003]

【発明が解決しようとする課題】飛灰処理に関しては、
EP或いはBF捕集などによるばいじん対策以外に、排
ガス及びダイオキシン対策が必要であり、これらの対策
を施すことによっては得られる飛灰の性状が大きく異な
り、特に消石灰噴霧処理された高アルカリ性飛灰におい
ては重金属溶出量が多くなることが知られている。この
ような飛灰の重金属固定化のためには、従来の薬剤では
その使用量を大幅に増加するか、或いは塩化第二鉄等の
pH調整剤、或いはセメント等の他の薬剤との併用法を
とらざるを得ず、処理薬剤費が増大し、或いは処理方法
が複雑化する等の問題があった。
[Problems to be Solved by the Invention] Regarding fly ash treatment,
In addition to measures against soot and dust by collecting EP or BF, measures against exhaust gas and dioxins are necessary. The properties of fly ash obtained by these measures are very different, especially in highly alkaline fly ash treated with slaked lime spray. It is known that the heavy metal elution amount increases. In order to fix such heavy metals in fly ash, the amount of conventional chemicals used should be greatly increased, or a combination method with a pH regulator such as ferric chloride or other chemicals such as cement. However, there has been a problem that the cost of the processing chemicals increases or the processing method becomes complicated.

【0004】本発明は上記の課題に鑑みてなされたもの
であり、その目的は、飛灰中に含まれる重金属を安定性
の高いキレート剤を用いることにより簡便に固定化でき
る方法を提供することである。
The present invention has been made in view of the above problems, and an object thereof is to provide a method for easily immobilizing heavy metals contained in fly ash by using a highly stable chelating agent. Is.

【0005】[0005]

【課題を解決するための手段】本発明者らは上記の課題
を解決すべく鋭意検討を重ねた結果、窒素原子数4〜8
個のポリエチレンポリアミンから誘導されるジチオカル
バミン酸又はその塩は重金属に対するキレート能力が高
く、アルカリ性飛灰においても少量の添加量で重金属を
固定化できることを見いだし、本発明を完成するに至っ
た。
The inventors of the present invention have conducted extensive studies to solve the above problems, and as a result, have 4 to 8 nitrogen atoms.
It was found that dithiocarbamic acid or a salt thereof derived from individual polyethylene polyamines has a high chelating ability for heavy metals, and that even in alkaline fly ash, heavy metals can be immobilized with a small addition amount, and the present invention has been completed.

【0006】すなわち、本発明は窒素原子数4〜8個の
ポリエチレンポリアミンから誘導されるジチオカルバミ
ン酸もしくはそれらの塩の少なくとも1種を水とともに
飛灰中に添加し、混練することを特徴とする飛灰中の重
金属の固定化方法に関するものである。
That is, the present invention is characterized in that at least one kind of dithiocarbamic acid or a salt thereof derived from polyethylene polyamine having 4 to 8 nitrogen atoms is added to fly ash together with water and kneaded. The present invention relates to a method for immobilizing heavy metals in ash.

【0007】本発明の方法において使用される飛灰は、
特に限定するものではないが、通常都市ゴミや産業廃棄
物等の焼却プラントから排出される。
The fly ash used in the method of the present invention is
Although not particularly limited, it is usually discharged from an incineration plant such as municipal waste and industrial waste.

【0008】本発明の方法において使用されるジチオカ
ルバミン酸の原料となる炭素数4個以上のポリエチレン
ポリアミンとしては、カルボジチオ酸基を導入可能な一
級或いは二級のアミノ基を4〜8個有するポリエチレン
ポリアミンであれば特に制限なく、例えば分子内に環状
或いは分岐構造による三級アミンを含んでいても使用可
能である。窒素原子数が3個以下のポリエチレンポリア
ミンを原料とした場合には、重金属の固定化効果能が低
く、また晶析点が低いため製品中のジチオカルバミン酸
塩の濃度を高くできない事などから飛灰の処理に際して
多量を要し好ましくない。また、窒素原子数が9個以上
のポリエチレンポリアミンの場合には高分子量のため処
理にあたって分散性が悪くなり、結果としてこの場合も
多量を要し好ましくない。好適な窒素原子数4〜8個の
ポリエチレンポリアミンとして、トリエチレンテトラミ
ン、テトラエチレンペンタミン、ペンタエチレンヘキサ
ミン、ヘキサエチレンヘプタミン、ヘプタエチレンオク
タミン及びこれらの混合物を例示できる。
The polyethylene polyamine having 4 or more carbon atoms, which is a raw material of dithiocarbamic acid used in the method of the present invention, is a polyethylene polyamine having 4 to 8 primary or secondary amino groups capable of introducing carbodithioic acid groups. There is no particular limitation so long as it can be used even if it contains, for example, a tertiary amine having a cyclic or branched structure in the molecule. When polyethylene polyamine with 3 or less nitrogen atoms is used as a raw material, the ability to immobilize heavy metals is low, and the crystallization point is low, so the concentration of dithiocarbamate in the product cannot be increased. It is not preferable because a large amount is required for the treatment of. Further, in the case of polyethylene polyamine having 9 or more nitrogen atoms, the dispersibility is poor during the treatment due to its high molecular weight, and as a result, a large amount is required, which is also not preferable. Examples of suitable polyethylene polyamines having 4 to 8 nitrogen atoms include triethylenetetramine, tetraethylenepentamine, pentaethylenehexamine, hexaethyleneheptamine, heptaethyleneoctamine, and mixtures thereof.

【0009】本発明の方法において使用されるジチオカ
ルバミン酸は、通常前記したポリエチレンポリアミンと
二硫化炭素とから容易に合成される。この際に苛性ソー
ダ等の塩基を共存させることによっては対応するジチオ
カルバミン酸塩とすることができる。
The dithiocarbamic acid used in the method of the present invention is usually easily synthesized from the above-mentioned polyethylene polyamine and carbon disulfide. At this time, a corresponding dithiocarbamate can be obtained by coexisting a base such as caustic soda.

【0010】本発明の窒素原子数4〜8個のポリエチレ
ンポリアミンから誘導されるジチオカルバミン酸の塩と
しては、アルカリ金属、アルカリ土類金属またはアンモ
ニウムの塩が使用できる。これらのうち水に対する溶解
度の高いリチウム、ナトリウム、カリウム、マグネシ
ム、カルシウム、アンモニウムの塩が好ましい。さら
に、熱的に安定でかつ安価なナトリウム塩及びカリウム
塩が特に好ましい。
As the salt of dithiocarbamic acid derived from the polyethylene polyamine having 4 to 8 nitrogen atoms in the present invention, an alkali metal salt, an alkaline earth metal salt or an ammonium salt can be used. Of these, salts of lithium, sodium, potassium, magnesium, calcium and ammonium, which have high solubility in water, are preferable. Furthermore, the thermally stable and inexpensive sodium salts and potassium salts are particularly preferable.

【0011】本発明の窒素原子数4〜8個のポリエチレ
ンポリアミンから誘導されるジチオカルバミン酸または
その塩の使用量は、処理する飛灰中の重金属の含有量や
重金属の形態により異なるが、通常飛灰に対して0.0
1〜10重量%の範囲で使用される。
The amount of dithiocarbamic acid or its salt derived from the polyethylene polyamine having 4 to 8 nitrogen atoms of the present invention varies depending on the content of heavy metal in the fly ash to be treated and the form of heavy metal. 0.0 for ash
It is used in the range of 1 to 10% by weight.

【0012】本発明の方法において使用する水の量は、
処理する飛灰に対して通常5〜60重量%の範囲で使用
される。5重量%以下では、薬剤との混練状態が充分で
ない場合があり、60重量%以上使用した場合には、処
理して得られる飛灰が液状となる等して廃棄が困難とな
る場合がある。
The amount of water used in the method of the present invention is
It is usually used in the range of 5 to 60% by weight with respect to the fly ash to be treated. If the amount is 5% by weight or less, the kneading state with the chemicals may not be sufficient, and if the amount is 60% by weight or more, the fly ash obtained by the treatment may become liquid and the disposal may be difficult. .

【0013】本発明の方法において、水と窒素原子数4
〜8個のポリエチレンポリアミンから誘導されるジチオ
カルバミン酸またはその塩を加える方法については特に
制限されない。例えば、前記した水使用量の範囲内にお
いて飛灰を混練したのち、予め上記カルボジチオ酸また
はその塩を溶解した水溶液を用いて処理する方法、或い
は、使用する水の全量に所定量の前記ジチオカルバミン
酸またはその塩を溶解して処理する方法等が採用でき
る。
In the method of the present invention, water and the number of nitrogen atoms are 4
There is no particular limitation on the method of adding dithiocarbamic acid or a salt thereof derived from ~ 8 polyethylene polyamines. For example, a method in which fly ash is kneaded within the range of the amount of water used and then treated with an aqueous solution in which the carbodithioic acid or a salt thereof is dissolved in advance, or a predetermined amount of the dithiocarbamic acid is added to the total amount of water used. Alternatively, a method of dissolving the salt and treating it can be adopted.

【0014】本発明の方法において、固定化される飛灰
中の重金属は、一般にジチオカルバミン酸基がキレート
することによって水溶液から不溶化できる金属であり、
鉛、水銀、クロム、カドミウム、亜鉛、銅、ニッケル、
砒素、セレン等が例示できる。
In the method of the present invention, the heavy metal in the fly ash to be immobilized is generally a metal that can be insolubilized from an aqueous solution by chelating a dithiocarbamic acid group,
Lead, mercury, chromium, cadmium, zinc, copper, nickel,
Examples include arsenic and selenium.

【0015】本発明の方法によれば、重金属固定化能が
高く、重金属溶出量の多い高アルカリ性飛灰において
も、少量の添加で効果を発揮し経済的であるとともに、
簡便な処理方法にて実施できる。
According to the method of the present invention, even in the case of highly alkaline fly ash, which has a high ability to fix heavy metals and a large amount of heavy metal is eluted, it is economical with the addition of a small amount thereof.
It can be carried out by a simple processing method.

【0016】[0016]

【実施例】次に、実施例によりさらに詳細に本発明を説
明する。但し、本発明は下記実施例によってなんら制限
を受けるものではない。
EXAMPLES Next, the present invention will be described in more detail by way of examples. However, the present invention is not limited to the following examples.

【0017】合成例1 トリエチレンテトラミン−N
1,N2,N3,N4−テトラカルボジチオ酸ナトリウ
ム(化合物No.1) ガラス製容器中に窒素雰囲気下、トリエチレンテトラミ
ン(東ソー社製、ジエチレントリアミン含有率0.5%
以下)46重量部、48%NaOH93重量部、水80
1重量部を入れ、この混合液中に撹拌しながら40℃以
下で二硫化炭素84重量部を4時間かけて滴下した。滴
下終了後、同温度にて1時間熟成を行った。反応液に窒
素を吹き込み未反応の二硫化炭素を留去し、黄褐色透明
液体を得た。ヨード滴定により測定した結果、この水溶
液中のジチオカルバミン酸塩濃度は15wt%であっ
た。
Synthesis Example 1 Triethylenetetramine-N
1, N2, N3, N4-Sodium tetracarbodithioate (Compound No. 1) Triethylenetetramine (manufactured by Tosoh Corporation, diethylenetriamine content 0.5%) in a glass container under a nitrogen atmosphere.
Below) 46 parts by weight, 48% NaOH 93 parts by weight, water 80
1 part by weight was added, and 84 parts by weight of carbon disulfide was added dropwise to this mixed solution at 40 ° C. or lower over 4 hours while stirring. After completion of dropping, aging was carried out for 1 hour at the same temperature. Nitrogen was blown into the reaction solution to distill off unreacted carbon disulfide to obtain a yellowish brown transparent liquid. As a result of measurement by iodine titration, the concentration of dithiocarbamate in this aqueous solution was 15 wt%.

【0018】合成例2 テトラエチレンペンタミン−N
1,N2,N3,N4,N5,−ペンタカルボジチオ酸
ナトリウム(化合物No.2) 合成例1と同様の装置を用いテトラエチレンペンタミン
(東ソー社製、トリエチレンテトラミン含有率1%以
下、ジエチレントリアミン含有率0.1%以下)53重
量部、48%NaOH91重量部、水821重量部を入
れ、この混合溶液中に撹拌しながら40℃以下で二硫化
炭素82重量部を4時間かけて滴下した。滴下終了後、
同温度にて約1時間熟成を行った。反応液に窒素を吹き
込み未反応の二硫化炭素を留去したところ、黄褐色透明
の液体を得た。ヨード滴定により測定した結果、この水
溶液中のジチオカルバミン酸塩濃度は15wt%であっ
た。 合成例3 エチレンジアミン−N1,N2−ビスカルボ
ジチオ酸ナトリウム(化合物No.3) 合成例1と同様の装置を用いエチレンジアミン(東ソー
社製、純度99.9%)39重量部、48%NaOH1
10重量部、水863重量部を入れ、この混合溶液中に
撹拌しながら40℃以下で二硫化炭素99重量部を4時
間かけて滴下した。滴下終了後、同温度にて約1時間熟
成を行った。反応液に窒素を吹き込み未反応の二硫化炭
素を留去したところ、黄褐色透明の液体を得た。ヨード
滴定により測定した結果、この水溶液中のジチオカルバ
ミン酸塩濃度は15wt%であった。
Synthesis Example 2 Tetraethylenepentamine-N
1, N2, N3, N4, N5, -Pentacarbodithioate sodium (Compound No. 2) Tetraethylene pentamine (manufactured by Tosoh Corporation, triethylenetetramine content 1% or less, diethylenetriamine) was prepared using the same device as in Synthesis Example 1. 53 parts by weight (content: 0.1% or less), 91 parts by weight of 48% NaOH, 821 parts by weight of water were added, and 82 parts by weight of carbon disulfide was added dropwise to this mixed solution at 40 ° C. or lower with stirring for 4 hours. . After dropping,
Aging was performed at the same temperature for about 1 hour. When nitrogen was blown into the reaction solution to distill off unreacted carbon disulfide, a yellowish brown transparent liquid was obtained. As a result of measurement by iodine titration, the concentration of dithiocarbamate in this aqueous solution was 15 wt%. Synthesis Example 3 Ethylenediamine-N1, N2-sodium biscarbodithioate (Compound No. 3) 39 parts by weight of ethylenediamine (manufactured by Tosoh Corporation, purity 99.9%), 48% NaOH 1 using the same apparatus as in Synthesis Example 1
10 parts by weight and 863 parts by weight of water were added, and 99 parts by weight of carbon disulfide was added dropwise to the mixed solution at 40 ° C. or lower over 4 hours while stirring. After completion of dropping, aging was carried out at the same temperature for about 1 hour. When nitrogen was blown into the reaction solution to distill off unreacted carbon disulfide, a yellowish brown transparent liquid was obtained. As a result of measurement by iodine titration, the concentration of dithiocarbamate in this aqueous solution was 15 wt%.

【0019】合成例4 ジエチレントリアミン−N1,
N2,N3−トリスカルボジチオ酸ナトリウム(化合物
No.4) 合成例1と同様の装置を用いジエチレントリアミン(東
ソー社製、純度99.9%)41重量部、48%NaO
H101重量部、水826重量部を入れ、この混合溶液
中に撹拌しながら40℃以下で二硫化炭素91重量部を
4時間かけて滴下した。滴下終了後、同温度にて約1時
間熟成を行った。反応液に窒素を吹き込み未反応の二硫
化炭素を留去したところ、黄褐色透明の液体を得た。ヨ
ード滴定により測定した結果、この水溶液中のジチオカ
ルバミン酸塩濃度は15wt%であった。
Synthesis Example 4 Diethylenetriamine-N1,
N2, N3-Sodium triscarbodithioate (Compound No. 4) 41 parts by weight of diethylenetriamine (manufactured by Tosoh Corporation, purity 99.9%), 48% NaO, using the same apparatus as in Synthesis Example 1
101 parts by weight of H and 826 parts by weight of water were added, and 91 parts by weight of carbon disulfide was added dropwise to this mixed solution at 40 ° C. or lower over 4 hours while stirring. After completion of dropping, aging was carried out at the same temperature for about 1 hour. When nitrogen was blown into the reaction solution to distill off unreacted carbon disulfide, a yellowish brown transparent liquid was obtained. As a result of measurement by iodine titration, the concentration of dithiocarbamate in this aqueous solution was 15 wt%.

【0020】実施例1 重金属固定化能試験 BF灰(Ca=30.7%、Na=1.4%、K=1.
6%、Pb=2000ppm、Cu=150ppmを含
む)100重量部に対し、水30重量部を加え、さらに
トリエチレンテトラミン−N1,N2,N3,N4−テ
トラカルボジチオ酸ナトリウム(化合物No.1)15
%水溶液を3部、4.5部及び6部となるように添加、
混練した後、環境庁告示第13号試験に従い溶出試験を
行った。鉛の溶出結果を表1に示す。鉛以外の重金属に
ついては、亜鉛は4ppm以下、クロムは0.05pp
m以下、カドミウム、水銀、銅、ニッケルについてはい
ずれも0.01ppm以下であった。
Example 1 Heavy metal immobilization ability test BF ash (Ca = 30.7%, Na = 1.4%, K = 1.
6%, including Pb = 2000 ppm and Cu = 150 ppm) 30 parts by weight of water was added to 100 parts by weight, and further triethylenetetramine-N1, N2, N3, N4-sodium tetracarbodithioate (Compound No. 1). 15
% Aqueous solution to be added to 3 parts, 4.5 parts and 6 parts,
After kneading, a dissolution test was conducted according to the Environmental Agency Notification No. 13 test. Table 1 shows the lead elution results. For heavy metals other than lead, zinc is 4ppm or less and chromium is 0.05pp
m or less, and all of cadmium, mercury, copper, and nickel were 0.01 ppm or less.

【0021】[0021]

【表1】 [Table 1]

【0022】実施例2 テトラエチレンペンタミン−N1,N2,N3,N4,
N5,−ペンタカルボジチオ酸ナトリウム(化合物N
o.2)15%水溶液を使用する以外は、実施例1と同
様にして、重金属固定化能試験を行った。結果を表1に
あわせて示す。鉛以外の重金属については、亜鉛は4p
pm以下、クロムは0.05ppm以下、カドミウム、
水銀、銅、ニッケルについてはいずれも0.01ppm
以下であった。
Example 2 Tetraethylenepentamine-N1, N2, N3, N4
Sodium N5, -pentacarbodithioate (Compound N
o. 2) A heavy metal immobilizing ability test was conducted in the same manner as in Example 1 except that a 15% aqueous solution was used. The results are also shown in Table 1. For heavy metals other than lead, zinc is 4p
pm or less, chromium is 0.05 ppm or less, cadmium,
0.01 ppm for mercury, copper and nickel
It was below.

【0023】比較例1 エチレンジアミン−N1,N2−ビスカルボジチオ酸ナ
トリウム(化合物No.3)15%水溶液を使用する以
外は、実施例1と同様にして、重金属固定化能試験を行
った。結果を表1にあわせて示す。
Comparative Example 1 A heavy metal immobilizing ability test was conducted in the same manner as in Example 1 except that a 15% aqueous solution of sodium ethylenediamine-N1, N2-biscarbodithioate (Compound No. 3) was used. The results are also shown in Table 1.

【0024】比較例2 ジエチレントリアミン−N1,N2,N3−トリスカル
ボジチオ酸ナトリウム(化合物No.4)15%水溶液
を使用する以外は、実施例1と同様にして、重金属固定
化能試験を行った。結果を表1にあわせて示す。
Comparative Example 2 A heavy metal immobilizing ability test was conducted in the same manner as in Example 1 except that a 15% aqueous solution of sodium diethylenetriamine-N1, N2, N3-triscarbodithioate (Compound No. 4) was used. . The results are also shown in Table 1.

【0025】[0025]

【発明の効果】本発明の方法によれば、窒素原子数4〜
8個のポリエチレンポリアミンから誘導されるポリジチ
オカルバミン酸又はその塩の少なくとも1種を使用する
ことにより、焼却炉飛灰中の有害重金属を確実に固定化
でき、しかも重金属固定剤の使用量を低減することがで
きる。
According to the method of the present invention, the number of nitrogen atoms is 4 to 4.
By using at least one of polydithiocarbamic acid or its salt derived from 8 polyethylene polyamines, harmful heavy metals in incinerator fly ash can be reliably fixed, and the amount of heavy metal fixative used is reduced. be able to.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 窒素原子数4〜8個のポリエチレンポリ
アミンから誘導されるポリジチオカルバミン酸又はその
塩の少なくとも1種を、飛灰に水とともに添加し、混練
することを特徴とする飛灰中の重金属の固定化方法。
1. A fly ash characterized in that at least one of polydithiocarbamic acid or a salt thereof derived from a polyethylene polyamine having 4 to 8 nitrogen atoms is added to fly ash together with water and kneaded. Heavy metal immobilization method.
【請求項2】 窒素原子数4〜8個のポリエチレンポリ
アミンが、トリエチレンテトラミン、テトラエチレンペ
ンタミン、ペンタエチレンヘキサミン、ヘキサエチレン
ヘプタミン、ヘプタエチレンオクタミンからなる群より
選ばれる1種又はそれ以上であることを特徴とする請求
項1に記載の方法。
2. The polyethylene polyamine having 4 to 8 nitrogen atoms is one or more selected from the group consisting of triethylene tetramine, tetraethylene pentamine, pentaethylene hexamine, hexaethylene heptamine, and heptaethylene octamine. The method of claim 1, wherein:
【請求項3】 窒素原子数4〜8個のポリエチレンポリ
アミンから誘導されるジチオカルバミン酸塩が、アルカ
リ金属、アルカリ土類金属塩又はアンモニウム塩である
ことを特徴とする請求項1又は請求項2に記載の方法。
3. The dithiocarbamate salt derived from a polyethylene polyamine having 4 to 8 nitrogen atoms is an alkali metal salt, an alkaline earth metal salt or an ammonium salt. The method described.
【請求項4】 窒素原子数4〜8個のポリエチレンポリ
アミンから誘導されるジチオカルバミン酸塩が、ジチオ
カルバミン酸ナトリウム塩またはカリウム塩である請求
項3に記載の方法
4. The method according to claim 3, wherein the dithiocarbamate derived from polyethylene polyamine having 4 to 8 nitrogen atoms is dithiocarbamate sodium salt or potassium salt.
【請求項5】 重金属が、鉛、水銀、クロム、カドミウ
ム、亜鉛及び銅である請求項1乃至請求項4に記載の方
法。
5. The method according to claim 1, wherein the heavy metal is lead, mercury, chromium, cadmium, zinc and copper.
JP7234854A 1995-09-13 1995-09-13 Process of solidifying heavy metal in fly ash by low-molecular polyamine derivative Pending JPH0975892A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7234854A JPH0975892A (en) 1995-09-13 1995-09-13 Process of solidifying heavy metal in fly ash by low-molecular polyamine derivative

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7234854A JPH0975892A (en) 1995-09-13 1995-09-13 Process of solidifying heavy metal in fly ash by low-molecular polyamine derivative

Publications (1)

Publication Number Publication Date
JPH0975892A true JPH0975892A (en) 1997-03-25

Family

ID=16977397

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7234854A Pending JPH0975892A (en) 1995-09-13 1995-09-13 Process of solidifying heavy metal in fly ash by low-molecular polyamine derivative

Country Status (1)

Country Link
JP (1) JPH0975892A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003094001A (en) * 2001-09-25 2003-04-02 Ebara Corp Treatment agent for incinerated flying ash and treating method using the same
JP2003117521A (en) * 2001-10-17 2003-04-22 Ebara Corp Method for treating incineration flying ash
JP2005118617A (en) * 2003-10-14 2005-05-12 Nippon Soda Co Ltd Method for fixing heavy metal in fly ash
JP2007183204A (en) * 2006-01-10 2007-07-19 Tosoh Corp Determining method of heavy metal immobilizing effect
WO2023277136A1 (en) * 2021-07-02 2023-01-05 ミヨシ油脂株式会社 Heavy metal treatment agent, and method for treating incinerated ash and wastewater using same

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003094001A (en) * 2001-09-25 2003-04-02 Ebara Corp Treatment agent for incinerated flying ash and treating method using the same
JP2003117521A (en) * 2001-10-17 2003-04-22 Ebara Corp Method for treating incineration flying ash
JP2005118617A (en) * 2003-10-14 2005-05-12 Nippon Soda Co Ltd Method for fixing heavy metal in fly ash
JP2007183204A (en) * 2006-01-10 2007-07-19 Tosoh Corp Determining method of heavy metal immobilizing effect
WO2023277136A1 (en) * 2021-07-02 2023-01-05 ミヨシ油脂株式会社 Heavy metal treatment agent, and method for treating incinerated ash and wastewater using same

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