JPS5929082A - Treatment of waste water of stack gas scrubbing in refuse incineration plant - Google Patents
Treatment of waste water of stack gas scrubbing in refuse incineration plantInfo
- Publication number
- JPS5929082A JPS5929082A JP13834882A JP13834882A JPS5929082A JP S5929082 A JPS5929082 A JP S5929082A JP 13834882 A JP13834882 A JP 13834882A JP 13834882 A JP13834882 A JP 13834882A JP S5929082 A JPS5929082 A JP S5929082A
- Authority
- JP
- Japan
- Prior art keywords
- compd
- added
- water
- waste water
- gas scrubbing
- 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
- Removal Of Specific Substances (AREA)
Abstract
Description
【発明の詳細な説明】
この発明は塵JF焼却場におりて発生する洗煙廃水の処
理方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating smoke washing wastewater generated at a dust JF incinerator.
塵芥焼却場では燃焼ガスをそのまま排出できないため洗
煙が行われているが、洗煙方法には乾式と湿式の2つの
方法がある。乾式法はフレーク状のCa(OHJffi
I@などにガスを1出して処理するが、水銀は捕捉され
ずに大気に放出される。Since combustion gas cannot be directly discharged at garbage incinerators, smoke cleaning is performed, and there are two methods for cleaning smoke: dry and wet. The dry method produces flaky Ca (OHJffi
Gas is released into I@ etc. for treatment, but the mercury is not captured and is emitted into the atmosphere.
これに対して湿式法は水銀を除去できるが、洗煙廃水の
処理が必要となる。In contrast, wet methods can remove mercury, but require treatment of smoke washing wastewater.
洗煙は、水酸化ナトラム溶液などのアルカリ吸収液によ
って行なわれ、燃焼ガス中の塩化水素が吸収されるので
洗煙廃水は’311類泊1g〔が高(。Smoke washing is performed using an alkaline absorption liquid such as a sodium hydroxide solution, and hydrogen chloride in the combustion gas is absorbed, so the amount of smoke washing wastewater is high (1 g).
また有機物や多種の亜金属を含んでいる。It also contains organic matter and various submetals.
この洗煙廃水の処理方法としr r;I 、キレート(
☆j脂や活性炭を充填した塔に通水して除去する方法と
イオウ化合物や水溶性キレ−1・剤等を添加し°C水銀
と何1・重性化合物に作り固液分離する沈殿法が知られ
ている。しかしながら、前渚の充填剤法ではその前処理
として濁Hrltの除去が必要であるのみならず、数p
pHlの水銀を数ppbまで除去するVLは充填剤の1
1替ガilK’に多くしなければならない等のために困
器である。The treatment method for this smoke washing wastewater is r r; I, chelate (
☆A method in which water is passed through a column filled with fat and activated carbon to remove it, and a precipitation method in which sulfur compounds, water-soluble cleating agents, etc. are added to form heavy compounds with mercury at °C and solid-liquid separation is carried out. It has been known. However, in the Maedagi filler method, not only is it necessary to remove the turbidity Hrlt as a pretreatment, but also several
The VL that removes mercury from pHl to several ppb is 1 of the filler.
It is difficult because you have to add a lot to the 1st replacement girl K'.
一方、後者のイオウ化合物による沈殿法はイメ臼ンイオ
ンを水銀に対して当M飴で数倍添加し2回時または前後
に過剰のイオウ−fオン除去のためにpH6〜8の条件
下で第2鉄イオン全添加し。On the other hand, in the latter precipitation method using a sulfur compound, rice ion is added several times as much as mercury, and two times or before and after, the precipitation is carried out under conditions of pH 6 to 8 to remove excess sulfur-f-ion. Fully added with 2 iron ions.
これらの不溶性生成物を沈殿分離する方法がとられてい
る。、第2鉄イオンf pll 6〜8の東件下で用い
るのは、このpH範囲が71’C銀の除去性によいため
と過剰の鉄イオンが水酸化物沈1般になって除去容易と
なるためである、
しかしながら、この@11Z物法は他の11■金属類(
Zn、pb、Cd等)とも反応するため、これらすべて
を除去する場合には薗度変動奮者應1.て爪金属知当;
杜の数倍、(1tの硫化物添加が必要である。A method has been adopted in which these insoluble products are separated by precipitation. , ferric ions f pll 6 to 8 are used under the conditions because this pH range is good for removing 71'C silver, and excess iron ions become hydroxide precipitates, making them easy to remove. However, this @11Z material method applies to other 11■ metals (
(Zn, PB, Cd, etc.), so if all of these are removed, it will be difficult to remove them.1. Te nail metal chito;
It is necessary to add 1 ton of sulfide, which is several times that of Mori.
従って、水銀に対して例えば硫化す) 11ウムが過剰
に添加さり、て処理水の白濁を招(上、鉄や水仙の除−
去性が悪化する欠点がある。他方、この方法でp、H9
〜11に”C処理すると水銀の除去を十分に行うことは
できない。この原因は明らか′r:はないかS/H,9
比が高い場合やpIlが高い場合は多硫化物全生成し几
り2 ]部第2鉄が還元されて第1鉄奢生成することに
よると考えられる。Therefore, an excessive amount of 11 um (for example, sulfide) is added to mercury, causing cloudiness in the treated water (in addition, iron and daffodil are removed).
It has the disadvantage of poor exfoliability. On the other hand, this method p, H9
~11 "C treatment cannot remove mercury sufficiently. The reason for this is obvious. S/H, 9
This is thought to be due to the fact that when the ratio is high or when pIl is high, all polysulfides are produced, and the ferric iron is reduced to produce a rich amount of ferrous iron.
本発明の目的は上記欠点會解決して水銀、その他の重金
属類が効果的に除去しイ4Iる塵芥焼却場の洗煙廃水の
処理方法ケ提供する事にある。SUMMARY OF THE INVENTION An object of the present invention is to overcome the above-mentioned disadvantages and provide a method for treating smoke washing wastewater from a garbage incinerator, in which mercury and other heavy metals can be effectively removed.
本発明者らの検討の結果、廃水にpH6〜Bの条件下で
イオlり化合物と鉄化合物を・力11えたνあ合。As a result of studies by the present inventors, it was found that iodine compounds and iron compounds were added to wastewater under conditions of pH 6 to B.
その後pH9〜11に上げても水銀や重金属類は溶解し
ないことを見い出した・
即し本発明は、一旦廃7.KにpII G〜8にて水側
1その他重合金絹除去の目的でイメウ化合物と未反応イ
オウイオン除去の目的で鉄fじ合物とを添加し反応させ
る。Afterwards, it was discovered that mercury and heavy metals did not dissolve even if the pH was raised to 9 to 11. Therefore, the present invention was temporarily abolished. At pII G~8, an iron compound is added to the water side for the purpose of removing other heavy alloy silk, and an iron compound is added for the purpose of removing unreacted sulfur ions, and the mixture is reacted.
次いで、アルカリ剤を添加してpH9〜11に調整して
他の重金属を不溶性水酸化物とじ固液分離するものであ
る。従って、 1)iJ記知見に邦3づいて2段階処l
!11r行9本発ツ、1は水銀、他のコ1(金属ともに
効果的に除去することかで@るのである。Next, an alkaline agent is added to adjust the pH to 9 to 11, and other heavy metals are separated from the insoluble hydroxide and solid-liquid. Therefore, 1) Two-stage treatment based on the findings of iJ.
! There are 9 lines in row 11r, 1 is mercury, and 1 is due to the effective removal of both metals.
本発明に使用されと)イオウ化合(吻どしては。Sulfur compounds (as used in the present invention)
硫化ソーダ(Na2S〕、水イ瀧化ソーダ(NallS
)等である。鉄化合物としては塩化NA2鉄、 jjf
fl酸第2鉄等が使用できる。Sodium sulfide (Na2S), sodium sulfide (NallS)
) etc. Iron compounds include NA2iron chloride, jjf
Ferric flate and the like can be used.
フッ素も除去したい、鴨合ば、前段(pH6〜8)にお
いてカルシウム化合物1例えkr CnCl、2. C
u(OH) v等を添加し、後段のアルカリ剤とじてC
A(O)lJt k用いると良い。フッ素除去にはアル
ミニウム化合物ノも考えらノ1;)が、吸着8tが低く
経済的に不利であるためカルシウム化合物の方がm1し
い。If you want to remove fluorine as well, add a calcium compound such as 1.kr CnCl, 2. C
Add u(OH)v, etc., and add C as an alkaline agent in the latter stage.
It is better to use A(O)lJtk. Aluminum compounds have also been considered for fluorine removal; however, calcium compounds are more expensive because their adsorption capacity is low and they are economically disadvantageous.
なお、固液分離は濾過、凝集沈殿等の公知の手段により
行なわれる。以下、実施例により本発明の効果ケ明らか
にする。Note that solid-liquid separation is performed by known means such as filtration and coagulation and precipitation. Hereinafter, the effects of the present invention will be clarified through examples.
実施例
L’>S芥焼却場の洗煙廃水(pH8,6、Hダニ11
.40g/)、フッ素:1106ffi/ノ+]l’鉛
: 8.81 t1g/ノ、鉛:380叩/ノ、カドミ
ウム1.0 m’j /ツノに(流化ソーダをイオウ換
1りで5 hg/ j!添加し、塩化第2鉄i30 t
lν/1添加し、消石灰を2000ハ9/Jl添加しp
H奮卸順で6〜8に調整して15分間15電押した。仄
いて消石灰を400−800MS//i添加してpH’
19−11に調整して15分間攪拌し、これを/1≦5
Aのp紙で濾過した。処理水の水質を下表に示す。比較
のため、硫化ソーダの添加量5m9/)、ノ盈化第2鉄
の添加量3QQmg/ノとし、γt’q石灰な: 28
00+IIg/ノ添加し、更に硫酸でpHを6〜8(比
較例)又はpll 9〜11(比較例2)の一段117
4整した後30分間攪拌した場合も表中に示す。Example L'>S Smoke washing wastewater from waste incineration plant (pH 8.6, H mites 11
.. 40g/), fluorine: 1106ffi/no+] l'lead: 8.81 t1g/no, lead: 380 t1g/no, cadmium 1.0 m'j/horn (soda fluid exchanged with sulfur in 1 part) hg/j!added, ferric chloride i30t
Add lν/1 and add 2000 ha9/Jl of slaked lime p
I adjusted it to 6 to 8 in the order of H excitation and pressed 15 volts for 15 minutes. Add 400-800MS//i of slaked lime to adjust pH'
Adjust the temperature to 19-11 and stir for 15 minutes.
It was filtered through A p paper. The quality of treated water is shown in the table below. For comparison, the amount of sodium sulfide added is 5 m9/), the amount of ferric oxide added is 3QQmg/, and γt'q lime: 28
Add 00+IIg/no and further adjust the pH with sulfuric acid to 6-8 (comparative example) or pll 9-11 (comparative example 2) to 117
The table also shows the case where the mixture was stirred for 30 minutes after being adjusted.
表に示しt結果から本発明の有λit性フ)(狸j宵さ
れよう。From the results shown in the table, it will be seen that the λit property of the present invention is effective.
Claims (1)
ウ化合物と鉄化合物とを添加し反応させ1次いでアルカ
リ剤を添加してpH9〜11に調整した後因前分!’i
1#することを特徴とす0塵芥焼却場の洗煙廃水の処J
IJj方法。 2、 アルカリ剤は消石灰である特許請求の範囲第1J
Ji記載の処理方法。[Scope of Claims] ], A sulfur compound and an iron compound are added to 7K of smoke washing waste from garbage incineration Jha at pH 6 to 8, the reaction is caused, and then an alkaline agent is added to adjust the pH to 9 to 11. The previous minute! 'i
Disposal of smoke washing wastewater of 0-waste incinerator characterized by #1
IJj method. 2. Claim 1J that the alkaline agent is slaked lime
The processing method described in Ji.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP13834882A JPS5929082A (en) | 1982-08-09 | 1982-08-09 | Treatment of waste water of stack gas scrubbing in refuse incineration plant |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP13834882A JPS5929082A (en) | 1982-08-09 | 1982-08-09 | Treatment of waste water of stack gas scrubbing in refuse incineration plant |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS5929082A true JPS5929082A (en) | 1984-02-16 |
Family
ID=15219817
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP13834882A Pending JPS5929082A (en) | 1982-08-09 | 1982-08-09 | Treatment of waste water of stack gas scrubbing in refuse incineration plant |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5929082A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS63502840A (en) * | 1986-09-03 | 1988-10-20 | アヴエスタ ニーベー パウダー アーベー | Method for powder metallurgical manufacturing of tubes, and capsules and devices used therefor |
-
1982
- 1982-08-09 JP JP13834882A patent/JPS5929082A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS63502840A (en) * | 1986-09-03 | 1988-10-20 | アヴエスタ ニーベー パウダー アーベー | Method for powder metallurgical manufacturing of tubes, and capsules and devices used therefor |
JPH031361B2 (en) * | 1986-09-03 | 1991-01-10 | Avesta Nyby Powder Ab |
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