JPS5821549B2 - Method for solidifying waste containing hazardous pollutants - Google Patents
Method for solidifying waste containing hazardous pollutantsInfo
- Publication number
- JPS5821549B2 JPS5821549B2 JP53037830A JP3783078A JPS5821549B2 JP S5821549 B2 JPS5821549 B2 JP S5821549B2 JP 53037830 A JP53037830 A JP 53037830A JP 3783078 A JP3783078 A JP 3783078A JP S5821549 B2 JPS5821549 B2 JP S5821549B2
- Authority
- JP
- Japan
- Prior art keywords
- water
- waste
- waste containing
- pollutants
- containing hazardous
- 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.)
- Expired
Links
Landscapes
- Processing Of Solid Wastes (AREA)
- Compositions Of Macromolecular Compounds (AREA)
Description
【発明の詳細な説明】
本発明は有害汚染物質を含む廃棄物の固型化方法に係り
、特に、都市ごみ焼却炉の電気集塵ダストのアスファル
トによる固型化方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for solidifying waste containing harmful pollutants, and particularly to a method for solidifying electrostatically precipitated dust from a municipal waste incinerator using asphalt.
都市ごみ焼却炉の電気集塵ダストにはCdやpbなとの
有害汚染物質である重金属類が含まれているため、これ
らのダストを埋立てたり、海洋投棄する場合にはアスフ
ァルトやセメント等によって固型化したのち行なうこと
が義務づけられている。Electrostatic precipitated dust from municipal waste incinerators contains heavy metals such as Cd and PB, which are harmful pollutants, so if this dust is to be landfilled or dumped into the ocean, it will be treated with asphalt, cement, etc. It is mandatory to do this after it has solidified.
ところが、上記のダスト中には水と反応する成分が含有
されており、埋立後などにおいて雨水や地下水と接触し
たりして、これらの成分が水と反応を生じ、固型化成形
品の強度低下を生じさせ、亀裂や破損個所から有害汚染
物質が溶出する原因となる。However, the above dust contains components that react with water, and when it comes into contact with rainwater or groundwater after landfilling, these components react with water, reducing the strength of solidified molded products. This can cause harmful contaminants to be leached from cracks and damaged areas.
例えば、都市ごみ焼却炉の電気集塵ダスト中にはNa2
O、CaOなどの酸化物およびAI、Znなどの金属が
含まれているが、これらの物質は水との間に下記のよう
な反応を生じる。For example, Na2 is contained in electrostatically collected dust from municipal waste incinerators.
It contains oxides such as O and CaO and metals such as AI and Zn, and these substances cause the following reaction with water.
CaO+H20→Ca(OH)2+ 15.1 Kca
l”・”・け)2Al+Na2O+3H20→2NaA
IO2+3H2・・・・・・・・・(2)
上記(1)式の場合はCa (OH)2という機械的に
極めて脆弱な物質と熱とを生じ、(2)式の場合にはH
2ガスおよび熱を生じることになる。CaO+H20→Ca(OH)2+ 15.1 Kca
l”・”・ke)2Al+Na2O+3H20→2NaA
IO2+3H2・・・・・・(2) In the case of the above equation (1), heat and a mechanically extremely fragile substance called Ca(OH)2 are generated, and in the case of the equation (2), H
2 gas and heat will be produced.
これらの物質およびガス、熱などは相乗作用を生じ、固
型化成形品の機械的強度を低め、前述したように亀裂や
破損を生じ、Cd、Pbなとの有害汚染物質を溶出させ
る結果となる。These substances, gas, heat, etc. have a synergistic effect, lowering the mechanical strength of the solidified molded product, causing cracks and breakage as mentioned above, and causing harmful contaminants such as Cd and Pb to be leached out. Become.
一方、廃棄物中に含まれるCd、PbさらにNaC1,
KCIなどは水溶性であり、埋立後において、雨水や地
下水と接触したりすると、これらの成分が水と反応を生
じ、固型化成形品の強度を低下させ、亀裂や破損個所か
ら有害汚染物質が溶出する原因となる。On the other hand, Cd, Pb, NaCl,
KCI and other substances are water-soluble, and when they come into contact with rainwater or groundwater after being landfilled, these components react with water, reducing the strength of solidified molded products and releasing harmful pollutants from cracks and damaged areas. This causes elution.
本発明の目的は廃棄物の固型化成形品の耐水強度の低下
を生じないようにし、かつ、有害汚染物質の溶出が生じ
ないようにした廃棄物の固型化方法を提供するにある。An object of the present invention is to provide a method for solidifying waste that does not cause a decrease in the water resistance of a solidified waste product and prevents the elution of harmful pollutants.
本発明によれば、上記の目的は固型化する前に水および
塩基性物質を加え廃棄物中の水との反応成分の反応を完
了させると共に、水溶性の有害汚染物質を不溶性にする
前処理を行なうことによって達成される。According to the present invention, the above objective is to complete the reaction of the reactive components with water in the waste by adding water and basic substances before solidification and to render water-soluble hazardous pollutants insoluble. This is achieved through processing.
以下、本発明の詳細な説明する。The present invention will be explained in detail below.
本発明者等は固型化したのち、埋立、海洋投棄などを行
なった場合、廃棄物中に含まれる水との反応成分および
有害な水溶性物質が水と反応を生じ、耐水強度の低下を
生じさせ、亀裂などから有害物質が溶出する原因となる
ことをつきとめたのち、この原因を除去する方法の1つ
として、前処理ということを考えた。The inventors of the present invention have found that when waste is solidified and then landfilled or dumped into the ocean, the water-reactive components and harmful water-soluble substances contained in the waste react with water, causing a decrease in water resistance. After discovering that this is the cause of harmful substances leaching out from cracks, etc., they considered pretreatment as one way to eliminate this cause.
即ち、固型化する以前において、水との反応成分を反応
させ、水溶性の有害物質を不溶性にすればより良い結果
が得られるであろうという点である。That is, better results will be obtained if the reactive components are made to react with water to make water-soluble harmful substances insoluble before solidification.
そこで、廃棄物を固型化する以前に水と消石灰などの塩
基性物質とを加えて混練する処理工程を加え、水の混合
比および溶出液OPH値を変化させ、固型化後における
有害汚染物質の溶出量と、強度とを調べて見た。Therefore, before solidifying the waste, we added a treatment process in which water and a basic substance such as slaked lime were added and kneaded, and the mixing ratio of water and the OPH value of the eluate were changed to prevent harmful pollution after solidification. The elution amount and intensity of the substance were investigated.
先ず、水との関係で説明すれば、水の混合比を変化させ
つつ前処理を行ない、水との反応が終了したのち、これ
を乾燥し、しかるのち、アスファルトと混練し、これを
円柱状に成形したものを7日間水中に浸漬したのち、圧
潰試験を行なったところ、第1図に示すような結果を得
た。First, to explain the relationship with water, pretreatment is performed while changing the mixing ratio of water, and after the reaction with water is completed, this is dried, then kneaded with asphalt, and this is made into a cylindrical shape. After immersing the molded product in water for 7 days, a crushing test was conducted, and the results shown in FIG. 1 were obtained.
第1図の線図からも明らかなように、水の混合比(重量
%・・・・・・廃棄物100に対する水の混合量)を太
き(して行くと、曲線Aで示すように、圧潰強度は著る
しく増大し、混合比50%の場合200kg/c77f
という大きな強度が得られた。As is clear from the diagram in Figure 1, as the mixing ratio of water (weight %...mixed amount of water per 100 parts of waste) increases (as shown by curve A), , the crushing strength increased significantly, reaching 200 kg/c77f at a mixing ratio of 50%.
Great strength was obtained.
これに比較し、水との間に前処理反応を行なわなかった
従来の方法による固型化成形品は、点Bで示すように圧
潰強度が著るしく低いことがわかり、満足すべき結果が
得られなかった。In comparison, it was found that the crushing strength of the solidified molded product made by the conventional method, which did not perform a pretreatment reaction with water, was significantly lower as shown at point B, and the result was satisfactory. I couldn't get it.
一方、圧潰強度試験と並行してCdおよびpbの溶出試
験を行なった結果、第2図に示すような成果を得た。On the other hand, as a result of conducting a Cd and PB elution test in parallel with the crushing strength test, the results shown in FIG. 2 were obtained.
図において縦軸は溶出量(ppm)を示す。In the figure, the vertical axis indicates the elution amount (ppm).
即ち、産廃基準である総理府令第5号(昭和48年)お
よび66号(昭和49年)によれば、Cdの溶出量は0
.3 ppm以下、pbのそれは3ppm 以下とされ
ており、この基準を満足させるPH値は図からも明らか
なようにCd、Pbの場合10〜12であることがわか
る。In other words, according to the industrial waste standards, Prime Minister's Office Ordinance No. 5 (1972) and No. 66 (1972), the amount of Cd eluted is 0.
.. 3 ppm or less, and that of Pb is 3 ppm or less, and as is clear from the figure, the pH value that satisfies this standard is 10 to 12 in the case of Cd and Pb.
勿論、この基準は地方公共団体によってはよりシビアな
ケースも考えられ、その時にはPH値の範囲はより狭く
なる。Of course, this standard may be more severe depending on the local government, and in that case the range of PH values will be narrower.
いずれにしても溶出液のpH値が11近傍のある範囲に
なるように調整して乾燥した後、アスファルトと混合す
れば、Cd、Pbの溶出量は溶出基準を下まわらせるこ
とができる。In any case, by adjusting the pH value of the eluate to a certain range around 11, drying it, and then mixing it with asphalt, the elution amount of Cd and Pb can be lowered below the elution standard.
このような溶出量の低下は下記のような事実に基づいて
いることが明らかである。It is clear that such a decrease in elution amount is based on the following facts.
即ち、一般に、Cd、Pbなとの重金属は、塩基性領域
では下記の反応により不溶性の塩となる。That is, in general, heavy metals such as Cd and Pb become insoluble salts in basic regions through the following reaction.
Cd 十Ca(OH)→Cd(OH) 2+Ca升・
・・・・・・・・・・・(3)廿
廿 廿0601.。Cd 10 Ca(OH) → Cd(OH) 2+Ca ・
・・・・・・・・・・・・(3) 廿廿 廿0601. .
Pb +Ca(OH)2→Pb(OH)2+Ca
・・・(4)上式(2)で得られるPb(OH)2は、
図からも明らかなように、高いPH値領領域は再び溶解
するため、Cd、Pb同時に不溶性とするためにはPH
値は10〜120間に調整する必要があるわけである。Pb + Ca (OH) 2 → Pb (OH) 2 + Ca
...(4) Pb(OH)2 obtained by the above formula (2) is
As is clear from the figure, the high pH value region dissolves again, so in order to make Cd and Pb insoluble at the same time, the pH
The value needs to be adjusted between 10 and 120.
以上の説明から明らかなように、本発明によれば水と反
応して脆弱な物質を成牛ずる物質や、水溶性の有害汚染
物質を含む廃棄物をアスファルト等によって所定の形状
に固型化する以前に、水および塩基性物質を加えて水と
の反応を終了させ、有害物質を不溶性に変える前処理工
程を加えているため、耐水強度も太き(、有害物質の溶
出しない廃棄物の固型化方法を実現できる。As is clear from the above explanation, according to the present invention, waste materials that react with water and are brittle, such as adult cow sludge, and waste containing water-soluble harmful pollutants, are solidified into a predetermined shape using asphalt, etc. Before the treatment, water and a basic substance are added to complete the reaction with water, and a pretreatment process is added to turn the hazardous substances into insoluble ones, so the water resistance is also high. A solidification method can be realized.
第1図は水の混合量と圧潰強度との関係を説明する線図
、第2図はPH値と有害物質の溶出量との関係を説明す
る線図である。FIG. 1 is a diagram illustrating the relationship between the amount of water mixed and the crushing strength, and FIG. 2 is a diagram illustrating the relationship between the pH value and the amount of harmful substances eluted.
Claims (1)
し、所定の形状に固型化する方法において、前記廃棄物
をアスファルトと混練する以前に水と塩基性物質とを加
え、水との反応を終了させると共に水溶性の有害物質を
不溶性の塩とする前処理を行なうことを特徴とする有害
汚染物質を含む廃棄物の固型化方法。1. In a method in which waste containing hazardous pollutants is kneaded with asphalt etc. and solidified into a predetermined shape, water and a basic substance are added to the waste before kneading it with asphalt to prevent the reaction with water. 1. A method for solidifying waste containing hazardous pollutants, which comprises the steps of: terminating water-soluble hazardous substances and performing pretreatment to convert water-soluble hazardous substances into insoluble salts.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53037830A JPS5821549B2 (en) | 1978-03-31 | 1978-03-31 | Method for solidifying waste containing hazardous pollutants |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53037830A JPS5821549B2 (en) | 1978-03-31 | 1978-03-31 | Method for solidifying waste containing hazardous pollutants |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS54128977A JPS54128977A (en) | 1979-10-05 |
| JPS5821549B2 true JPS5821549B2 (en) | 1983-04-30 |
Family
ID=12508436
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP53037830A Expired JPS5821549B2 (en) | 1978-03-31 | 1978-03-31 | Method for solidifying waste containing hazardous pollutants |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5821549B2 (en) |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS572654B2 (en) * | 1973-09-18 | 1982-01-18 | ||
| JPS5159771A (en) * | 1974-10-25 | 1976-05-25 | Kawasaki Heavy Ind Ltd | Gomishokyakubaino asufuarutoshoriho |
-
1978
- 1978-03-31 JP JP53037830A patent/JPS5821549B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS54128977A (en) | 1979-10-05 |
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