JPS586551B2 - How to detoxify harmful substances - Google Patents
How to detoxify harmful substancesInfo
- Publication number
- JPS586551B2 JPS586551B2 JP53057773A JP5777378A JPS586551B2 JP S586551 B2 JPS586551 B2 JP S586551B2 JP 53057773 A JP53057773 A JP 53057773A JP 5777378 A JP5777378 A JP 5777378A JP S586551 B2 JPS586551 B2 JP S586551B2
- Authority
- JP
- Japan
- Prior art keywords
- harmful substances
- value
- slaked lime
- relationship
- elution
- 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)
Description
【発明の詳細な説明】
本発明は有害物質の無害化処理方法に係り、特に、Cd
,Pb等の重金属を含んだ有害汚染物質の無害化処理方
法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for detoxifying harmful substances, and in particular, to a method for detoxifying harmful substances.
The present invention relates to a method for detoxifying harmful pollutants containing heavy metals such as , Pb, etc.
一般に、廃棄物焼却設備から発生する焼却灰集塵灰、製
鋼関係の還元キルンからの集塵灰、およびメッキスラツ
ジ等のCd , Pd等の重金属を含む有害汚染物質を
廃棄するためには、アスファルト、プラスチック等によ
り、有害汚染物質を含む粒子の表面を被覆、固定し、無
害化する必要がある。Generally, in order to dispose of hazardous pollutants containing heavy metals such as Cd and Pd from incineration ash generated from waste incineration equipment, collected ash from reduction kilns related to steel manufacturing, and plating sludge, asphalt, It is necessary to cover and fix the surface of particles containing harmful pollutants with plastic or the like to render them harmless.
これは、アスファルトやプラスチックの有する不透水性
、耐水性を利用したものであるが、被覆が完全に行なわ
れないと、埋立や海洋投棄後に有害物質が水と接触し、
溶解し、環境を汚染する恐れがある。This takes advantage of the water impermeability and water resistance properties of asphalt and plastics, but if the coating is not completely done, harmful substances may come into contact with water after being landfilled or dumped in the ocean.
It may dissolve and contaminate the environment.
このため、有害物質をあらかじめ不溶化してアスファル
ト等によって被覆する方法が採用されている。For this reason, a method has been adopted in which harmful substances are insolubilized in advance and then covered with asphalt or the like.
すなわち、Cd,Pb等を水酸化物の形に変えてからア
スファルト等によって被覆、固定するのである。That is, Cd, Pb, etc. are converted into hydroxides and then covered and fixed with asphalt or the like.
しかし、集塵灰、メッキスラツジの如く有害金属である
Cd,Pbを同時に含む場合には、単に、水酸化物にす
るだけでは無害化することはできない。However, when dust ash and plating sludge contain harmful metals Cd and Pb at the same time, it is not possible to render them harmless by simply converting them into hydroxide.
なぜならば、Pbは両性金属であるため、酸性側ではP
b2+,アルカリ側ではHPbO2−として溶解するの
で、Pbを難溶化できるpH値の範囲は非常に狭くなる
。This is because Pb is an amphoteric metal, so on the acidic side, Pb
Since Pb dissolves as HPbO2- on the alkali side, the range of pH values that can make Pb poorly soluble becomes very narrow.
すなわち、第1図に示すものはゴミ焼却炉からの集塵灰
中のCd,PbのpH値に対する溶解度を示すものであ
るが、PbおよびCdを基準値である3ppmおよび0
.3ppm以下に無害化するためには、pH値は10〜
12、安全を見れば10,5〜11.5の範囲に調整し
なければならないことがわかる。In other words, what is shown in Fig. 1 shows the solubility of Cd and Pb in the collected ash from the garbage incinerator with respect to the pH value, but Pb and Cd are set at the standard value of 3 ppm and 0.
.. In order to make it harmless to 3 ppm or less, the pH value must be 10~10.
12. If you look at safety, you will find that you have to adjust it to a range of 10.5 to 11.5.
このため、実際の設備の運転において、この範囲を保っ
て稼動させようとすると、安定性に問題が残り、設備費
も多額なものとなる。Therefore, in actual operation of the equipment, if it is attempted to maintain this range, problems with stability remain and equipment costs become large.
本発明の目的は、CdおよびPbの両重金属を含む廃棄
物を極めて制御の容易な状態で難溶化させることができ
る有害物質の無害化処理方法を提供するにある。An object of the present invention is to provide a method for detoxifying hazardous substances that can make waste containing both heavy metals, Cd and Pb, difficult to solubilize in an extremely easily controlled manner.
以下本発明方法の詳細につき説明する。The details of the method of the present invention will be explained below.
実験に使用した材料はゴミ焼却炉の集塵灰であり、その
物性は表1〜表4に示す如きである。The material used in the experiment was collected ash from a garbage incinerator, and its physical properties are shown in Tables 1 to 4.
以上のようなCd,Pb等の化合物を、まず、不溶化す
るために水酸化物に変えるべくアルカリ性物質である消
石灰を混合した。First, slaked lime, which is an alkaline substance, was mixed with the above compounds such as Cd and Pb in order to convert them into hydroxides in order to make them insolubilized.
すなわち、まず、前記組成の集塵灰100に対して重量
比で3〜10%の消石灰を添加、混合した後、溶出試験
を行なった。That is, first, 3 to 10% by weight of slaked lime was added to and mixed with 100 pieces of collected dust ash having the above composition, and then an elution test was conducted.
この結果、pH値との関係は第2図に示す如きであった
。As a result, the relationship with pH value was as shown in FIG.
第2図から明らかなように、溶出量を基準値以下に抑え
るためには、CdはpH≧8で、また、Pbは9.5<
pH<10.5において難溶化すればよい。As is clear from Figure 2, in order to suppress the elution amount below the standard value, the pH of Cd must be ≧8, and the pH of Pb must be 9.5<8.
It is sufficient to make it poorly soluble at pH<10.5.
従って、Cd,Pb共に溶出量を基準値以下とするため
には混合物のpH値を9.5〜10.5の範囲内に調節
しなければならない。Therefore, in order to keep the elution amount of both Cd and Pb below the standard value, the pH value of the mixture must be adjusted within the range of 9.5 to 10.5.
しかし、このままでは、調節範囲はpH値でわずかに1
であり、Pbの両性金属である性質が災いして調節範囲
が極めて狭い。However, as it is, the adjustment range is only 1 in terms of pH value.
The adjustment range is extremely narrow due to the nature of Pb as an amphoteric metal.
そこで、Pbを硫化物の形で沈澱させる実験を行なって
みた。Therefore, we conducted an experiment in which Pb was precipitated in the form of sulfide.
すなわち、集塵灰100に対して消石灰を3〜10%、
更に、硫酸マグネシウムを3〜15%、いずれも重量比
で添加し、混合後同様に溶出試験を行なってみた。That is, 3 to 10% of slaked lime to 100 parts of collected dust ash,
Further, magnesium sulfate was added in an amount of 3 to 15% by weight, and after mixing, an elution test was conducted in the same manner.
第3図は溶出量とpH値の関係を示し、第4図は消石灰
と硫酸マグネシウム(MgS04)の添加量を各種変え
た時に得られるpH値との関係を示す。FIG. 3 shows the relationship between the elution amount and the pH value, and FIG. 4 shows the relationship between the pH values obtained when the amounts of slaked lime and magnesium sulfate (MgSO4) added were varied.
以上の実験の結果、第3図に示す溶出曲線から明らかな
ように、CdおよびPbの溶出量を基準値以下に抑える
ためには、CdはpH≧8、PbはpH≦10.5にお
いて、難溶化すればよいことが明らかとなった。As a result of the above experiment, as is clear from the elution curve shown in Figure 3, in order to suppress the elution amount of Cd and Pb below the standard value, Cd should be kept at pH≧8 and Pb at pH≦10.5. It has become clear that it is sufficient to make it less soluble.
換言すれば、硫化物の形でPbを沈澱させることにより
、Cd,Pb共に溶出饋を基準以下にできるpH値の範
囲は8〜10.5となり、消石灰だけを使用した場合よ
りも適用範囲が広くなることが明らかとなった。In other words, by precipitating Pb in the form of sulfide, the pH range at which both Cd and Pb elution can be reduced to below the standard is 8 to 10.5, and the range of application is wider than when only slaked lime is used. It is clear that it will become wider.
以上の説明から明らかなように本発明によれば、Cd,
Pb等の有害汚染物質を含む廃棄物粒子をアスファルト
やプラスチック等によって被覆固定するに先立ち、前処
理工程としてCd,Pb等の有害重金属を水酸化物およ
び硫化物の形で難溶化できるアルカリ性物質を添加する
方法を採用しているため、有害重金属を溶出基準以下に
調整する場合のpH値の範囲を広くとれ、処理設備の運
転制御が容易となり、かつ、最終処分として埋立て、投
棄された場合の安定性が確保されるという優れた効果が
得られる。As is clear from the above description, according to the present invention, Cd,
Before covering and fixing waste particles containing harmful pollutants such as Pb with asphalt or plastic, alkaline substances that can make harmful heavy metals such as Cd and Pb hardly soluble in the form of hydroxides and sulfides are added as a pretreatment process. Because we use the addition method, we can widen the range of pH values when adjusting harmful heavy metals to below the elution standard, making it easier to control the operation of treatment equipment, and preventing waste from being landfilled or dumped as final disposal. This provides an excellent effect of ensuring stability.
第1図は水酸化物とした場合におけるCdおよびPbの
pH値と溶出量との関係を説明する線図、第2図は消石
灰を使用した場合におけるpH値と溶出量との関係を説
明する線図、第3図は消石灰と硫酸マグネシウムを使用
した場合におけるpH値と溶出量との関係を説明する線
図、第4図は硫酸マグネシウムと消石灰の混合量を変化
させた状態におけるpH値との関係を説明する線図であ
る。Figure 1 is a diagram explaining the relationship between pH value and elution amount of Cd and Pb when hydroxide is used, and Figure 2 is a diagram explaining the relationship between pH value and elution amount when slaked lime is used. Figure 3 is a diagram explaining the relationship between pH value and elution amount when slaked lime and magnesium sulfate are used, and Figure 4 is a diagram showing the relationship between pH value and elution amount when the mixed amount of magnesium sulfate and slaked lime is changed. It is a line diagram explaining the relationship.
Claims (1)
により、被覆、固定する有害物質の無害化処理法におい
て、アスファルトやプラスチック等を添加、混練する以
前に、有害物質を含む廃棄物100に対して消石灰、お
よび硫酸マグネシウムを重量比にて3〜15%添加し、
Cd,Pbを水酸化物および硫化物とする前処理工程を
施すことを特徴とする有害物質の無害化処理方法。In a hazardous substance detoxification treatment method that covers and fixes waste containing ICd and Pb with asphalt or plastic, slaked lime and Adding 3 to 15% magnesium sulfate by weight,
A method for detoxifying harmful substances, which comprises performing a pretreatment step of converting Cd and Pb into hydroxides and sulfides.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53057773A JPS586551B2 (en) | 1978-05-16 | 1978-05-16 | How to detoxify harmful substances |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53057773A JPS586551B2 (en) | 1978-05-16 | 1978-05-16 | How to detoxify harmful substances |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS54149373A JPS54149373A (en) | 1979-11-22 |
| JPS586551B2 true JPS586551B2 (en) | 1983-02-04 |
Family
ID=13065179
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP53057773A Expired JPS586551B2 (en) | 1978-05-16 | 1978-05-16 | How to detoxify harmful substances |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS586551B2 (en) |
-
1978
- 1978-05-16 JP JP53057773A patent/JPS586551B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS54149373A (en) | 1979-11-22 |
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