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JPS586550B2 - Asphalt solidification method for hazardous pollutants - Google Patents
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JPS586550B2 - Asphalt solidification method for hazardous pollutants - Google Patents

Asphalt solidification method for hazardous pollutants

Info

Publication number
JPS586550B2
JPS586550B2 JP53037834A JP3783478A JPS586550B2 JP S586550 B2 JPS586550 B2 JP S586550B2 JP 53037834 A JP53037834 A JP 53037834A JP 3783478 A JP3783478 A JP 3783478A JP S586550 B2 JPS586550 B2 JP S586550B2
Authority
JP
Japan
Prior art keywords
water
asphalt
waste
pollutants
solidified
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
Application number
JP53037834A
Other languages
Japanese (ja)
Other versions
JPS54130476A (en
Inventor
広沢賢一
西沢紀昭
渡辺隆
熱田稔雄
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.)
Kawasaki Heavy Industries Ltd
Original Assignee
Kawasaki Heavy Industries Ltd
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 Kawasaki Heavy Industries Ltd filed Critical Kawasaki Heavy Industries Ltd
Priority to JP53037834A priority Critical patent/JPS586550B2/en
Publication of JPS54130476A publication Critical patent/JPS54130476A/en
Publication of JPS586550B2 publication Critical patent/JPS586550B2/en
Expired legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)
  • 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のアスファルト固型化方法に関す
るものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for solidifying hazardous pollutants into asphalt.

例えば、都市ごみ焼却プラント等においては、Cb、P
b等の有害重金属を含む廃棄物も焼却されるため、焼却
灰、集塵灰中にはSiO2,Al2O3,CaO、Fe
2O3、MgO、Na2O、K2O等で代表される成分
の他に、Pb、Cd、Fe、Cr、Zn、Cu、Hg等
の金属または、その化合物が含まれている。
For example, in municipal waste incineration plants, Cb, P
Since waste containing hazardous heavy metals such as
In addition to components represented by 2O3, MgO, Na2O, K2O, etc., metals such as Pb, Cd, Fe, Cr, Zn, Cu, and Hg, or compounds thereof are included.

また、燃焼炉から排出される燃焼ガス中にはHCl、S
Ox等が含有されているため、通常NaOH、Ca(O
H)2等の中和剤を用いてガス洗滌したのちに、大気中
に放散させるため、HCl,SOxと中和剤が反応して
生成される塩類には有害重金属が含まれた状態で排出さ
れる。
In addition, HCl and S are contained in the combustion gas discharged from the combustion furnace.
Because it contains Ox, etc., it is usually used as NaOH, Ca(O
H) After gas cleaning using a neutralizing agent such as 2, the salts generated by the reaction between HCl, SOx and the neutralizing agent are discharged in a state containing harmful heavy metals, in order to be released into the atmosphere. be done.

そこで、これらの有害金属等の汚染物質を含む廃棄物を
廃棄するにはアスファルト等によって汚染物質が溶出し
ないように固型化したのち、独立、海洋投棄等を行なう
ことが義務づけられている。
Therefore, in order to dispose of waste containing pollutants such as these toxic metals, it is mandatory to solidify the waste with asphalt or the like to prevent the pollutants from leaching out, and then dump the waste separately into the ocean.

ところが、これらの有害汚染物質を含んだ廃棄物をその
ままアスファルトによって固型化し、埋立、投棄した場
合には、廃棄物中に含まれる成分や、外部からの水分に
よって固型化品の強度低下、膨脹、ひび割れ、更には崩
壊等の現象を生じ、有害汚染物質が溶出する危険がある
However, if waste containing these harmful pollutants is solidified with asphalt and then landfilled or dumped, the strength of the solidified product may decrease due to the components contained in the waste or moisture from the outside. Phenomena such as swelling, cracking, and even collapse may occur, and there is a risk that harmful pollutants may be leached out.

例えば、廃棄物中にNaCl、KCl、CaCl2等の
水溶性塩類が多量に含まれている場合には、投棄後に、
塩類の溶解がみられ、固型化品の強度を低下させる。
For example, if the waste contains large amounts of water-soluble salts such as NaCl, KCl, CaCl2, etc., after dumping,
Dissolution of salts is observed, reducing the strength of the solidified product.

また、廃棄物中にあるNa2O,K2O等アルカリ金属
の酸化物は、同じく灰中に混在しているAl、Fe等の
金属および水分と反応してH2ガスを発生し、固型化成
形品中の内圧を局部的に高め、亀裂等を生じ、ここから
有害汚染物質の溶出が生じることになる。
In addition, oxides of alkali metals such as Na2O and K2O in the waste react with metals such as Al and Fe, which are also mixed in the ash, and moisture, generating H2 gas, and forming solidified molded products. This increases the internal pressure locally, causing cracks, etc., from which harmful pollutants can be leached.

本発明の目的は、廃棄物の固型化成形品から有害汚染物
質の溶出が生じないようにした有害汚染物質のアスファ
ルト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 harmful pollutants into asphalt, which prevents the elution of harmful pollutants from waste solidified molded articles.

本発明によれば、上記の目的は、有害汚染物質を含む廃
棄物をアスファルトによって固型化する前に、水および
セメントを混合しながら造粒を行なう前処理を与えるこ
とによって達成される。
According to the invention, the above object is achieved by providing a pre-treatment of the waste containing hazardous pollutants by granulation with mixing of water and cement before solidification with asphalt.

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.

本発明者は、先ず、廃棄物をアスファルトによって固型
化したのち、これを埋立、海洋投棄すると、廃棄物中の
水との反応成分が水と反応し、固型化成形品を脆弱にし
、水溶性の有害汚染物質の溶出が生じるという事実をつ
きとめたのち、前処理ということを考えた。
The inventor first discovered that when waste is solidified with asphalt and then disposed of in a landfill or ocean, components that react with water in the waste react with water, making the solidified molded product brittle. After discovering the fact that water-soluble harmful pollutants were leached, we came up with the idea of pre-treatment.

即ち、固型化後に上記のような反応が生じるならば、固
型化前において水との反応を完了させてしまえば、固型
化後における上記のような水との反応は生ぜず、より良
い結果が得られるのではないかという点である。
In other words, if the above reaction occurs after solidification, if the reaction with water is completed before solidification, the above reaction with water will not occur after solidification, and it will be more The point is that good results may be obtained.

そこで、本発明者等は第1図に示すような成分の廃棄物
100に対して普通ボルトランドセメントを重量比にし
て3〜10混合し、さらに、水・セメント比が30%に
なるように水を添加し、混合機によって10分間以上混
合を続ける。
Therefore, the present inventors mixed ordinary Bortland cement in a weight ratio of 3 to 10 parts per 100 parts of waste having the components shown in Figure 1, and further adjusted the water/cement ratio to 30%. Add water and continue mixing with mixer for 10 minutes more.

このとき、混合機として、造粒機能を持つものを使用す
れば、混合中に水が結合材となって、廃棄物と普通ポル
トランドセメントとの混合物は、造粒作用を受け、第2
図に示すような粒度分布を得ることができた。
At this time, if a mixer with a granulation function is used, water will act as a binder during mixing, and the mixture of waste and ordinary Portland cement will be subjected to the granulation action, and the second
A particle size distribution as shown in the figure could be obtained.

そして、この混合作用を受けている間に廃棄物中に含ま
れている水と反応する成分は反応を完了する。
While undergoing this mixing action, components that react with water contained in the waste complete their reaction.

次に、この造粒物を大気中に10日間放置したところ、
セメントとの水和反応は更に進行し、硬化した造粒物が
得られた。
Next, when this granulated material was left in the atmosphere for 10 days,
The hydration reaction with cement further progressed, and hardened granules were obtained.

しかるのち、造粒物にアスファルトを重量比で8〜11
%添加して充分混練した後、直径100mm高さ75m
mの円柱状に成形した。
After that, the weight ratio of asphalt to the granules is 8 to 11.
% added and thoroughly kneaded, the diameter is 100mm and the height is 75m.
It was molded into a cylindrical shape of m.

この円柱状固型化成形品に対してマーシャル安定度試験
を行なった結果と、前処理を行なわなかった同一寸法の
固型化成形品についてのマーシャル安定度試験を行なっ
た結果を第3図に示す。
Figure 3 shows the results of the Marshall stability test conducted on this cylindrical solidified molded product and the results of the Marshall stability test conducted on a solidified molded product of the same size that was not pretreated. show.

第3図からも明らかなように、マーシャル安定度試験全
般にわたって満足すべき結果を得た。
As is clear from FIG. 3, satisfactory results were obtained throughout the Marshall stability test.

また、従来品との比較において、アスファルト配合比に
相違があるのは、本発明においては造粒した結果、比表
面積が減少し、混練すべきアスファルト添加量が大幅に
減少したためである。
Furthermore, the reason why there is a difference in the asphalt blending ratio in comparison with conventional products is that as a result of granulation in the present invention, the specific surface area is reduced and the amount of asphalt added to be kneaded is significantly reduced.

また、固型化成形品の圧縮強度および水中に浸漬した場
合の経時変化の調査結果を第4図および第5図に示す。
Furthermore, the results of the investigation of the compressive strength of the solidified molded product and its change over time when immersed in water are shown in FIGS. 4 and 5.

両図からも明らかなように、本発明方法によって得た固
型化成形品は圧縮強度および経時変化の両面においても
満足すべき結果を得た。
As is clear from both figures, the solidified molded product obtained by the method of the present invention had satisfactory results in terms of both compressive strength and change over time.

尚、第5図において、本発明方法を適用した固型化成形
品の体積膨脹率が減少したのは、前処理の段階において
水との反応が固型化前に行なわれた結果と考えられる。
In addition, in Figure 5, the decrease in the volumetric expansion rate of the solidified molded product to which the method of the present invention was applied is thought to be the result of the reaction with water taking place in the pretreatment stage before solidification. .

表1は固型化成形品の溶出試験の結果であるが、同表か
らも明らかなようにCd、Pbとも検出されなかった。
Table 1 shows the results of the elution test for the solidified molded product, and as is clear from the table, neither Cd nor Pb was detected.

これは、セメントの水和反応によって、廃棄物をアルカ
リ性に保つことができ、水溶性であったCd、Pbがア
ルカリ性領域において不溶な塩に変化したためであると
考えられる。
This is considered to be because the waste can be kept alkaline by the hydration reaction of cement, and water-soluble Cd and Pb are changed into insoluble salts in the alkaline region.

以上の説明から明らかなように、本発明によれば有害汚
染物質を含む廃棄物をアスファルトによって固型化する
前に、水とセメントとを混合し、廃棄物中に含まれる水
との反応成分を水と反応させ、セメントとの水和反応に
よって全体をアルカリ性に保つため、水溶性の有害汚染
物質を不溶性の塩とすることができるため、固型化成形
品の強度を向上させ、膨脹、亀裂等による汚染物質の溶
出がない。
As is clear from the above description, according to the present invention, before solidifying waste containing hazardous pollutants with asphalt, water and cement are mixed, and components that react with water contained in the waste are mixed. It reacts with water and maintains the overall alkalinity through a hydration reaction with cement, making it possible to turn water-soluble harmful pollutants into insoluble salts, improving the strength of solidified molded products, expanding, No elution of contaminants due to cracks, etc.

また、造粒を行なうため、比表面積が減少し、添加すべ
きアスファルトの量を大幅に減少でき経済的にも極めて
有利である等の優れた効果が得られる。
In addition, since granulation is performed, the specific surface area is reduced, and the amount of asphalt to be added can be significantly reduced, resulting in excellent effects such as being extremely economically advantageous.

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

第1図は廃棄物の成分、性状を説明する説明図、第2図
は造粒後の粒度分布を示す線図、第3図はマーシャル安
定度試験結果を示す線図、第4図は圧縮強度試験結果を
示す線図、第5図は経時変化を説明する線図である。
Figure 1 is an explanatory diagram explaining the components and properties of waste, Figure 2 is a diagram showing the particle size distribution after granulation, Figure 3 is a diagram showing the Marshall stability test results, and Figure 4 is a diagram showing the compression A diagram showing the strength test results, and FIG. 5 is a diagram explaining changes over time.

Claims (1)

【特許請求の範囲】[Claims] 1 有害汚染物質を含む廃棄物をアスファルトによって
固型化する前に、水とセメントとを加えて混練し、廃棄
物中に含まれる水との反応物質を水と反応させ、同時に
造粒を行なったのち、アスファルトを加えて固型化する
ことを特徴とする有害汚染物質のアスファルト固型化方
法。
1. Before solidifying waste containing hazardous pollutants with asphalt, water and cement are added and kneaded to cause the water-reactive substances contained in the waste to react with water, and at the same time granulation is performed. A method for solidifying hazardous pollutants into asphalt, which is characterized in that asphalt is then added and solidified.
JP53037834A 1978-03-31 1978-03-31 Asphalt solidification method for hazardous pollutants Expired JPS586550B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP53037834A JPS586550B2 (en) 1978-03-31 1978-03-31 Asphalt solidification method for hazardous pollutants

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP53037834A JPS586550B2 (en) 1978-03-31 1978-03-31 Asphalt solidification method for hazardous pollutants

Publications (2)

Publication Number Publication Date
JPS54130476A JPS54130476A (en) 1979-10-09
JPS586550B2 true JPS586550B2 (en) 1983-02-04

Family

ID=12508550

Family Applications (1)

Application Number Title Priority Date Filing Date
JP53037834A Expired JPS586550B2 (en) 1978-03-31 1978-03-31 Asphalt solidification method for hazardous pollutants

Country Status (1)

Country Link
JP (1) JPS586550B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
NL8006884A (en) * 1980-12-18 1982-07-16 Pelt & Hooykaas COMPOSITION CONTAINING AT LEAST ONE SOLUTION OF GAS AVOIDED IN THE PREPARATION OF STEEL.

Also Published As

Publication number Publication date
JPS54130476A (en) 1979-10-09

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