JPH01231981A - Treatment of waste - Google Patents

Treatment of waste

Info

Publication number
JPH01231981A
JPH01231981A JP63059171A JP5917188A JPH01231981A JP H01231981 A JPH01231981 A JP H01231981A JP 63059171 A JP63059171 A JP 63059171A JP 5917188 A JP5917188 A JP 5917188A JP H01231981 A JPH01231981 A JP H01231981A
Authority
JP
Japan
Prior art keywords
waste
heavy metals
salt
water
cement
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
JP63059171A
Other languages
Japanese (ja)
Inventor
Atsushi Sato
淳 佐藤
Yutaka Niekawa
豊 贄川
Akio Toriyama
明夫 鳥山
Tadaaki Kawasugi
河杉 忠昭
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.)
Kubota Corp
Original Assignee
Kubota 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 Kubota Corp filed Critical Kubota Corp
Priority to JP63059171A priority Critical patent/JPH01231981A/en
Publication of JPH01231981A publication Critical patent/JPH01231981A/en
Pending legal-status Critical Current

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  • Processing Of Solid Wastes (AREA)

Abstract

PURPOSE:To maintain the density of a caked body of waste contg. salt and heavy metals by previously removing the salt by dissolution in water when the waste is caked with cement, etc. CONSTITUTION:Collected dust is mixed with an aq. soln. of calcium polysulfide in a mixing vessel 1 and this mixture is stirred in a reaction vessel 2. Salt in the dust dissolves in water in the aq. soln. and heavy metals react with S to form a precipitate of insoluble metal sulfides. The metal sulfides are separated from the resulting aq. soln. in a precipitate separating vessel 3, kneaded with cement in a kneading vessel 4, caked and discarded. Thus, the outflow of the heavy metals can be prevented.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、塩分および重金属を含有する廃棄物に、重金
属を不溶化するための添加剤を混入してセメントで固め
る廃棄物の処理方法に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a waste treatment method in which waste containing salt and heavy metals is mixed with an additive for insolubilizing the heavy metals and solidified with cement.

〔従来の技術〕[Conventional technology]

従来の処理方法では、廃棄物に添加剤とセメントを同時
に混入して固化していた。
Conventional treatment methods involve mixing additives and cement into waste at the same time and solidifying it.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

しかし、固化物が水に浸漬したり、長期にわたって雨水
等の水にさらされると、その固化物中の塩分が溶出して
来て固化物自体がポーラスでもろくなり、固化物内で不
溶化した重金属が外部に出やすく、再反応して有害化す
る危険性があった。
However, if the solidified material is immersed in water or exposed to water such as rainwater for a long period of time, the salt in the solidified material will leach out, making the solidified material porous and brittle, and the heavy metals that have become insolubilized within the solidified material may become porous and brittle. There was a risk that it would easily leak out and cause a re-reaction and become harmful.

本発明の目的は、固化物から不溶化した重金属を外部に
出にくくする点にある。
An object of the present invention is to make it difficult for heavy metals insolubilized from a solidified product to come out.

〔課題を解決するための手段〕[Means to solve the problem]

本発明の廃棄物の処理方法の特徴手段は、廃棄物をセメ
ントで固める前に、廃棄物中の塩分を水に溶かして除去
することにあり、その作用、効果は次の通りである。
The characteristic means of the waste treatment method of the present invention is that salts in the waste are removed by dissolving them in water before solidifying the waste with cement, and its functions and effects are as follows.

〔作 用〕[For production]

つまり、廃棄物中の塩分を水で溶かして除去することに
よって、セメントによる固化物を水にさらしても、その
中には水溶性の物質が存在しないために、固化物の密度
は維持されて、添加剤によって不溶化された重金属は、
固化物中に強固に保持されて外部には出て来ない。
In other words, even if a solidified cement product is exposed to water by dissolving and removing the salt in the waste, the density of the solidified product is maintained because there are no water-soluble substances in it. , heavy metals insolubilized by additives are
It is firmly held in the solidified material and does not come out.

〔発明の効果〕〔Effect of the invention〕

従って、不溶化した重金属が再び反応するということを
防止でき、廃棄物を長期にわたって無害の状態で、維持
できるようになり、安全な固化物として埋立て地又は山
間等への投棄が節単にできるようになった。
Therefore, it is possible to prevent the insolubilized heavy metals from reacting again, making it possible to maintain the waste in a harmless state for a long period of time, and making it possible to save waste by disposing of it in a landfill or mountain area as a safe solidified product. Became.

〔実施例〕〔Example〕

次に、本発明の実施例を、図面に基づいて説明する。 Next, embodiments of the present invention will be described based on the drawings.

下水汚泥や都市ゴミ等の焼却時の集塵ダストを無害化し
て投棄できるように、次の処理方法を行う。
The following treatment method will be used to render the dust collected during incineration of sewage sludge and municipal garbage harmless so that it can be disposed of.

つまり、前記集塵ダスト中には、塩化ナトリウム(Na
CR)等の水溶性塩及びカドミウム(Cd)、ヒ素(A
s)、亜鉛(Zn)、鉛(Pd)、クローム(Cr)等
の重金属が含まれるために、前記集塵ダストを多硫化カ
ルシウム(CaSx)の水溶液と共に混合槽(1)で混
合し、続いて反応槽(2)で攪拌されながら集塵ダスト
中の塩分は水溶液中の水に溶は込み、重金属(Cd、A
s、Zn、Pb、Cr)は多硫化カルシウム水溶液中の
イオウ(S)と反応して不溶性の硫化金M (CdS+
 AsS+ ZnS、 P bS+ Cry)の沈澱物
になる。
In other words, the collected dust contains sodium chloride (Na
water-soluble salts such as CR), cadmium (Cd), arsenic (A
s), zinc (Zn), lead (Pd), chromium (Cr), etc., the collected dust is mixed with an aqueous solution of calcium polysulfide (CaSx) in a mixing tank (1), and then While being stirred in the reaction tank (2), the salt in the collected dust is dissolved into the water in the aqueous solution, and heavy metals (Cd, A
s, Zn, Pb, Cr) react with sulfur (S) in the calcium polysulfide aqueous solution to form insoluble gold sulfide M (CdS+
This results in a precipitate of AsS+ ZnS, PbS+ Cry).

そして、反応処理水中から沈澱分離槽(3)によって、
塩分の溶けた水溶液と、硫化金属とを分離し、硫化金属
はセメントと共に混練槽(4)で混練して固化させ廃棄
する。
Then, from the reaction treated water, the sedimentation separation tank (3)
The aqueous solution containing dissolved salt and the metal sulfide are separated, and the metal sulfide is kneaded together with cement in a kneading tank (4), solidified, and disposed of.

面、前記反応槽(2)での反応状態は、塩の溶出と共に
イオン化して導電率が上がるために、導電率計(5)の
検出結果に基づいて反応槽(2)における撹拌装置(6
)の作動時間及び混合槽(1)に添加する多硫化カルシ
ウム水溶液の水量を変更制御する。
On the other hand, the reaction state in the reaction tank (2) is such that the salt is ionized as it elutes and the conductivity increases.
) and the amount of calcium polysulfide aqueous solution added to the mixing tank (1).

〔別実施例〕[Another example]

前記集塵ダストに代えて、他の廃棄物であっても良い。 Instead of the collected dust, other waste may be used.

前記多硫化カルシウム(CaSx)に代えて、硫化ナト
リウム(NazS)、又は多硫化ナトリウム(NazS
工)、多硫化アンモニウム(NH4SX)等の水溶性硫
化物又は重金属を不溶化する別の物質であっても良く、
それらを添加剤と総称する。
Instead of the calcium polysulfide (CaSx), sodium sulfide (NazS) or sodium polysulfide (NazS
may be a water-soluble sulfide such as ammonium polysulfide (NH4SX) or another substance that insolubilizes heavy metals;
These are collectively called additives.

前記廃棄物に含有する塩分としては、塩化カルシウム(
CaCβ2)、塩化カリウム(KCl ’)、硫酸ナト
リウム(NazSO,)等の塩であっても良い。
The salt contained in the waste includes calcium chloride (
Salts such as CaCβ2), potassium chloride (KCl'), and sodium sulfate (NazSO,) may also be used.

前記導電率計(5)に代えて、イオンメータであっても
良い。
An ion meter may be used instead of the conductivity meter (5).

また、集塵ダスト中の塩化ナトリウム(NaCit )
は、下水汚泥、都市ゴミ等の焼却時の排ガス中に含まれ
る塩化水素(HC1)を、水酸化ナトリウム(NaOl
l)水溶液の散布によって塩化ナトリウム(NaCI!
 )にされて集塵器で捕集されるものである。
In addition, sodium chloride (NaCit) in collected dust
The hydrogen chloride (HC1) contained in the exhaust gas from the incineration of sewage sludge, municipal waste, etc. is converted into sodium hydroxide (NaOl).
l) Sodium chloride (NaCI!) by sparging with an aqueous solution.
) and collected in a dust collector.

前記廃棄物に対して、水を混入した後に添加剤を添加し
ても良いが、水と同時に添加剤を混入した方が重金属の
不溶化が効率良い。
Although additives may be added to the waste after water is mixed therein, it is more efficient to insolubilize heavy metals if the additives are mixed in at the same time as water.

尚、特許請求の範囲の項に図面との対照を便利にする為
に符号を記すが、該記入により本発明は添付図面の構造
に限定されるものではない。
Incidentally, although reference numerals are written in the claims section for convenient comparison with the drawings, the present invention is not limited to the structure shown in the accompanying drawings.

【図面の簡単な説明】[Brief explanation of the drawing]

図面は本発明の廃棄物の処理方法を示す概略図である。 The drawing is a schematic diagram showing the waste treatment method of the present invention.

Claims (1)

【特許請求の範囲】 1、塩分および重金属を含有する廃棄物に、重金属を不
溶化するための添加剤を混入してセメントで固める廃棄
物の処理方法であって、前記廃棄物をセメントで固める
前に、廃棄物中の塩分を水に溶かして除去する廃棄物の
処理方法。 2、前記添加剤としての水溶性硫化物を、廃棄物に混入
するに際して前記水による塩分除去を実施すると同時に
添加する請求項1記載の廃棄物の処理方法。
[Claims] 1. A waste treatment method in which waste containing salt and heavy metals is mixed with an additive for insolubilizing the heavy metals and solidified with cement, the method comprising: before solidifying the waste with cement; Second, there is a waste treatment method that removes the salt in the waste by dissolving it in water. 2. The waste treatment method according to claim 1, wherein the water-soluble sulfide as the additive is added at the same time as the salt removal by the water is carried out when the waste is mixed.
JP63059171A 1988-03-11 1988-03-11 Treatment of waste Pending JPH01231981A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63059171A JPH01231981A (en) 1988-03-11 1988-03-11 Treatment of waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63059171A JPH01231981A (en) 1988-03-11 1988-03-11 Treatment of waste

Publications (1)

Publication Number Publication Date
JPH01231981A true JPH01231981A (en) 1989-09-18

Family

ID=13105671

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63059171A Pending JPH01231981A (en) 1988-03-11 1988-03-11 Treatment of waste

Country Status (1)

Country Link
JP (1) JPH01231981A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07155737A (en) * 1993-10-27 1995-06-20 Techno Frontier:Kk Recycling treatment method of incinerator ash of stalker type incinerator for waste
WO2000005004A1 (en) * 1998-07-21 2000-02-03 Murakashi Lime Industry Co., Ltd. Hazardous substance-fixing material
JP2001342461A (en) * 2000-05-31 2001-12-14 Ube Ind Ltd Ground improvement material
FR2826886A1 (en) * 2001-07-09 2003-01-10 Sagace STABILIZATION TREATMENT OF REFIOM, AND OTHER WASTE OR SIMILAR SPECIAL INDUSTRIAL BY-PRODUCTS
WO2003008119A1 (en) * 2001-07-09 2003-01-30 Sagace Services En Administration, Gestion Et Applications Au Conseil A L'environnement Stabilisation treatment, in particular for waste incineration residues
JP2008284522A (en) * 2007-05-21 2008-11-27 Nippon Steel Engineering Co Ltd Fly ash treatment method

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4826672A (en) * 1971-08-10 1973-04-07
JPS54137852A (en) * 1978-04-19 1979-10-25 Unitika Ltd Harmlessnesssmaking disposal method of industrial waste containing heavy metal
JPS5845783A (en) * 1981-09-16 1983-03-17 Ebara Infilco Co Ltd Treatment of heavy metal-contg. waste matter
JPS5853594A (en) * 1981-09-25 1983-03-30 Hitachi Zosen Corp Exhaust gas cleaning treatment ship

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4826672A (en) * 1971-08-10 1973-04-07
JPS54137852A (en) * 1978-04-19 1979-10-25 Unitika Ltd Harmlessnesssmaking disposal method of industrial waste containing heavy metal
JPS5845783A (en) * 1981-09-16 1983-03-17 Ebara Infilco Co Ltd Treatment of heavy metal-contg. waste matter
JPS5853594A (en) * 1981-09-25 1983-03-30 Hitachi Zosen Corp Exhaust gas cleaning treatment ship

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07155737A (en) * 1993-10-27 1995-06-20 Techno Frontier:Kk Recycling treatment method of incinerator ash of stalker type incinerator for waste
WO2000005004A1 (en) * 1998-07-21 2000-02-03 Murakashi Lime Industry Co., Ltd. Hazardous substance-fixing material
JP2001342461A (en) * 2000-05-31 2001-12-14 Ube Ind Ltd Ground improvement material
FR2826886A1 (en) * 2001-07-09 2003-01-10 Sagace STABILIZATION TREATMENT OF REFIOM, AND OTHER WASTE OR SIMILAR SPECIAL INDUSTRIAL BY-PRODUCTS
WO2003008119A1 (en) * 2001-07-09 2003-01-30 Sagace Services En Administration, Gestion Et Applications Au Conseil A L'environnement Stabilisation treatment, in particular for waste incineration residues
JP2008284522A (en) * 2007-05-21 2008-11-27 Nippon Steel Engineering Co Ltd Fly ash treatment method

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