JPH01231981A - Treatment of waste - Google Patents
Treatment of wasteInfo
- 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
Links
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
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.
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.
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.
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.
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.
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).
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)
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.
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)
| 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)
| 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 |
-
1988
- 1988-03-11 JP JP63059171A patent/JPH01231981A/en active Pending
Patent Citations (4)
| 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)
| 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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