JPH11226549A - Production of sewage sludge incineration ash lightweight solidified material - Google Patents
Production of sewage sludge incineration ash lightweight solidified materialInfo
- Publication number
- JPH11226549A JPH11226549A JP10039113A JP3911398A JPH11226549A JP H11226549 A JPH11226549 A JP H11226549A JP 10039113 A JP10039113 A JP 10039113A JP 3911398 A JP3911398 A JP 3911398A JP H11226549 A JPH11226549 A JP H11226549A
- Authority
- JP
- Japan
- Prior art keywords
- sewage sludge
- incineration ash
- solidified
- sludge incineration
- kneaded material
- 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
【0001】[0001]
【発明の属する技術分野】本発明は、高分子凝集剤が加
えられた下水汚泥焼却灰から軽量固化物を製造するよう
にした、下水汚泥焼却灰軽量固化物の製造方法に関する
ものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for producing a light-weight solidified sewage sludge ash from a sewage sludge ash to which a polymer flocculant has been added.
【0002】[0002]
【従来の技術】下水処理によって発生する汚泥量は下水
道の普及に伴って増加し、その主たる処分先である埋立
地の減少などにより近年埋め立て処分は以前と比べて益
々困難となり、その処分量の低減のため下水汚泥の減
量、減容の必要性が要求されている。2. Description of the Related Art The amount of sludge generated by sewage treatment increases with the spread of sewerage, and landfill disposal has become increasingly difficult in recent years due to a decrease in landfills, which are the main disposal sites. There is a need to reduce the volume and volume of sewage sludge for reduction.
【0003】又、減量、減容に止まらず、下水汚泥の有
効利用のための資源化技術の確立が望まれている。[0003] Further, it is desired to establish resource recycling technology for effective use of sewage sludge, not limited to weight reduction and volume reduction.
【0004】下水汚泥の処理方法としては、下水汚泥
を脱水してコンポスト化し有機質土壌改良材として利用
する、埋め立て処分する、脱水ケーキを焼却後埋め
立て処分するなどが一般的である。[0004] As a method of treating sewage sludge, it is common to dewater sewage sludge, compost it and use it as an organic soil amendment, landfill disposal, incineration of a dewatered cake, and landfill disposal.
【0005】一方、近年、より高度な処理方法として、
下水汚泥焼却灰を煉瓦状に圧縮成形し、焼成して製品と
するか、下水汚泥或いは下水汚泥焼却灰を高温溶融し骨
材とするなどの方法が取られている。On the other hand, recently, as a more advanced processing method,
A method is employed in which sewage sludge incineration ash is compression-molded into a brick shape and fired to produce a product, or sewage sludge or sewage sludge incineration ash is melted at a high temperature to produce aggregate.
【0006】しかし、これら焼成煉瓦や溶融骨材などの
製造には、多大の熱量と特別の設備を必要とする。However, the production of these fired bricks and molten aggregates requires a large amount of heat and special equipment.
【0007】又、大量処理に適すと思われる土木、建築
の分野において用いられる下水汚泥や下水汚泥焼却灰と
セメントとの混合物は、強度的な面において十分ではな
く、一般的な用途に不向きである。Further, sewage sludge or a mixture of sewage sludge incineration ash and cement used in the fields of civil engineering and construction considered to be suitable for large-scale treatment is not sufficient in terms of strength, and is not suitable for general use. is there.
【0008】そこで、上述の問題点を解決すべく、本件
発明者等は種々の実験を行い、その結果次の事実が判明
した。In order to solve the above-mentioned problems, the present inventors conducted various experiments, and as a result, the following facts were found.
【0009】すなわち、高分子系凝集剤が加えられた下
水汚泥焼却灰は、酸と混練りすれば、反応してその形状
がゴム状に変化し、やがて粘土状の物質になり、この物
質はやがて硬化して強固な固化物が得られるが、下水汚
泥焼却灰はとりわけ、硫酸との反応が顕著である。な
お、下水汚泥焼却灰に高分子系凝集剤を加えるのは、通
常下水処理過程においては濃縮汚泥の含水率が高く、こ
のままでは脱水工程にかけることができないので、高分
子系凝集剤を加えフロック状にして脱水し、含水率の下
降した脱水汚泥を得るためである。That is, the sewage sludge incinerated ash to which the polymer-based flocculant has been added, when kneaded with an acid, reacts and changes its shape into a rubbery state, and eventually becomes a clay-like substance. A hardened product is eventually obtained by hardening, but the sewage sludge incineration ash has a remarkable reaction with sulfuric acid. In addition, adding a polymer flocculant to the sewage sludge incineration ash usually involves a high water content of the concentrated sludge in the sewage treatment process, and it is not possible to apply the polymer flocculant to the dehydration step as it is. This is for obtaining dewatered sludge having a reduced water content.
【0010】又、各々の処理場の下水汚泥焼却灰の組成
は異なるが、高分子系凝集剤が加えられた下水汚泥焼却
灰の場合、その組成に適した量、濃度の硫酸と十分混
合、混練りを行い乾燥すれば、その反応、作用は明らか
ではないが種々の硫酸塩を生成し、溶液中の水は結晶水
などとなり固化物内において遊離の水はごく少量であ
る。従ってこの固化物は水中に放置しても酸の溶出、吸
水がごく微量で長期に亘って安定である。In addition, although the composition of the sewage sludge incineration ash in each treatment plant is different, in the case of the sewage sludge incineration ash to which a polymer-based flocculant is added, the sewage sludge incineration ash is sufficiently mixed with sulfuric acid in an amount and concentration suitable for the composition. When kneading and drying, the reaction and action are not clear, but various sulfates are generated, and the water in the solution becomes crystallization water or the like, and the free water in the solidified product is very small. Therefore, even if this solidified product is left in water, the elution and absorption of acid are very small and stable for a long time.
【0011】なお、塩酸、燐酸を使用しても粘土状の物
質ができるものの、強度的には、硫酸使用のものに比べ
てかなり弱く、価格的にも硫酸は安価であるため、硫酸
が好適である。Although a clay-like substance can be formed by using hydrochloric acid or phosphoric acid, the strength is considerably weaker than that using sulfuric acid, and sulfuric acid is inexpensive in price. It is.
【0012】かかる事実を踏まえて、本件発明者等は特
願平7−316392号明細書に示すごとき下水汚泥焼
却灰固化物及びその製造方法について平成7年12月5
日付で特許出願を行った。[0012] Based on this fact, the present inventors have disclosed a solidified sewage sludge incinerated ash and a method for producing the same as disclosed in Japanese Patent Application No. 7-316392 on December 5, 1995.
Filed a patent application by date.
【0013】又、その後本件発明者等は特願平9−26
1714号明細書に示すごときより高品質、高能率な下
水汚泥焼却灰固化物の製造方法について平成9年9月2
6日付で特許出願を行った。After that, the present inventors have filed a Japanese Patent Application No. 9-26980.
No. 1714, a method for producing a solidified sewage sludge incineration ash having higher quality and higher efficiency than that described in the specification of September 17, 1997
A patent application was filed on the 6th.
【0014】而して、特願平7−316392号明細書
に開示された下水汚泥焼却灰固化物は、高分子系凝集剤
が加えられた下水汚泥焼却灰と酸との混練物からなるも
のであり、高分子系凝集剤が加えられた下水汚泥焼却灰
と硫酸溶液を混練り後、乾燥することにより製造され
る。The sewage sludge incineration ash solidified product disclosed in Japanese Patent Application No. 7-316392 is composed of a kneaded product of sewage sludge incineration ash to which a polymer-based flocculant is added and acid. It is manufactured by kneading sewage sludge incineration ash to which a polymer-based flocculant has been added and a sulfuric acid solution, followed by drying.
【0015】又特願平9−261714号明細書に開示
された下水汚泥焼却灰固化物の製造方法は、特願平7−
316392号明細書に開示された下水汚泥焼却灰固化
物を製造する場合に、下水汚泥焼却灰、酸、混練物が所
定の温度を上回らないように温度調整するものである。A method for producing a solidified sewage sludge incineration ash disclosed in Japanese Patent Application No. 9-261714 is disclosed in Japanese Patent Application No. 7-261714.
When manufacturing the solidified sewage sludge ash disclosed in the specification of 316392, the temperature is adjusted so that the sewage sludge incinerated ash, acid, and kneaded material do not exceed a predetermined temperature.
【0016】上述の各出願で使用された下水汚泥焼却灰
の組成は表1に示され、得られた下水汚泥焼却灰固化物
の物性は表2に示されている。The composition of the sewage sludge incineration ash used in each of the above applications is shown in Table 1, and the physical properties of the obtained sewage sludge incineration ash are shown in Table 2.
【0017】[0017]
【表1】 [Table 1]
【0018】[0018]
【表2】 [Table 2]
【0019】表2に示す供試体のうちA−1、A−2、
A−3は特願平7−316392号明細書に開示された
下水汚泥焼却灰固化物を示し、B−1、B−2、B−3
は特願平9−261714号明細書に開示された下水汚
泥焼却灰固化物を示している。Of the specimens shown in Table 2, A-1, A-2,
A-3 is a solidified sewage sludge incinerated ash disclosed in the specification of Japanese Patent Application No. 7-316392, and B-1, B-2 and B-3.
Indicates a solidified sewage sludge incineration ash disclosed in Japanese Patent Application No. 9-261714.
【0020】[0020]
【発明が解決しようとする課題】上述の各出願における
下水汚泥焼却灰固化物は、その曲げ強度において通常の
セメント系固化物に比較して優れているものの単位容積
重量において軽量コンクリート、木質系材料、プラスチ
ック系材料に比較して重い。The solidified sewage sludge incinerated ash in each of the above-mentioned applications is superior in bending strength to ordinary cement-based solidified matter, but is light weight concrete and woody material in unit volume weight. , Heavy compared to plastic materials.
【0021】一方、下水汚泥焼却灰固化物は、強度に対
する要求もさることながら、軽量であることを要求され
る用途も多く、このような場合には、下水汚泥焼却灰固
化物は、単位容積重量が小さいことが望ましい。On the other hand, the solidified sewage sludge incineration ash has many applications that require lightness in addition to the demand for strength. In such a case, the solidified sewage sludge incineration ash has a unit volume of It is desirable that the weight is small.
【0022】本発明は上述の実情に鑑み、単位容積重量
が小さく且つ軽量コンクリートなどと比較して強度が高
くしかも高品質の下水汚泥焼却灰軽量固化物を製造し得
るようにした、下水汚泥焼却灰軽量固化物の製造方法を
提供することを目的としてなしたものである。In view of the above-mentioned circumstances, the present invention provides a sewage sludge incineration system which has a small unit weight and a high strength as compared with lightweight concrete and is capable of producing a high-quality sewage sludge incineration ash lightweight solidified product. An object of the present invention is to provide a method for producing a light-weight solidified ash.
【0023】[0023]
【発明がなされるに至った過程】本件発明者等は特願平
9−261714号明細書に開示された方法を実際に適
用して下水汚泥焼却灰固化物を製造するに当たり、混練
物に発泡剤を混入して気泡を形成させると単位容積重量
の小さい下水汚泥焼却灰軽量固化物が得られることを見
いだした。Processes leading to the invention The inventors of the present invention actually applied the method disclosed in Japanese Patent Application No. 9-261714 to produce sewage sludge incinerated ash solidified material, and foamed the kneaded material. It has been found that by mixing the agent to form bubbles, a lightly solidified sewage sludge incineration ash having a small unit weight is obtained.
【0024】[0024]
【課題を解決するための手段】本発明の下水汚泥焼却灰
軽量固化物の製造方法は、高分子系凝集剤が加えられた
下水汚泥焼却灰及び酸並に発泡剤を混合すると共に混練
して多量の気泡を含んだ粘土状の混練物を作成し、該混
練物を成形して自然乾燥し、固化させるものである。SUMMARY OF THE INVENTION According to the present invention, a method for producing a lightweight solidified sewage sludge incineration ash is provided by mixing and kneading a sewage sludge incineration ash to which a polymer-based flocculant is added, an acid and a foaming agent. A clay-like kneaded material containing a large amount of air bubbles is prepared, and the kneaded material is molded, air-dried, and solidified.
【0025】又、本発明の下水汚泥焼却灰軽量固化物の
製造方法は、高分子系凝集剤が加えられた下水汚泥焼却
灰及び酸並に発泡剤を混合すると共に混練して多量の気
泡を含んだ粘土状の混練物を作成し、所定量の混練物を
型枠内に入れて加温し、膨張させると共に固化させるも
のである。Further, the method for producing a lightly solidified sewage sludge incineration ash according to the present invention comprises mixing a sewage sludge incineration ash to which a polymer-based flocculant has been added and a foaming agent together with an acid, and kneading to form a large amount of air bubbles. A kneaded material containing clay is prepared, and a predetermined amount of the kneaded material is placed in a mold, heated, expanded, and solidified.
【0026】従って、本発明においては、軽量コンクリ
ートなどよりも曲げ強度が大きく、且つ酸の量が少く、
しかも酸溶出量の少い、広範囲の形状に対応した単位容
積重量の小さい高品質の下水汚泥焼却灰軽量固化物を製
造することができる。Therefore, in the present invention, the flexural strength is higher and the amount of acid is smaller than that of lightweight concrete, etc.
In addition, it is possible to produce a high-quality light-weight solidified sewage sludge incineration ash with a small unit volume weight corresponding to a wide range of shapes with a small amount of acid elution.
【0027】[0027]
【発明の実施の形態】以下、本発明の実施の形態を説明
する。Embodiments of the present invention will be described below.
【0028】表1に示す化学組成の下水汚泥焼却灰30
grに対し、前もって用意して室内に保管しておいた硫
酸溶液を加え、温度が35℃を越えないように冷却しな
がら混合する。ここで硫酸溶液は硫酸97%含有濃硫酸
3.3ccと水10ccを混合したものである。Sewage sludge incineration ash 30 having the chemical composition shown in Table 1
The sulfuric acid solution previously prepared and stored in the room is added to gr, and mixed while cooling so that the temperature does not exceed 35 ° C. Here, the sulfuric acid solution is a mixture of 3.3 cc of concentrated sulfuric acid containing 97% sulfuric acid and 10 cc of water.
【0029】下水汚泥焼却灰と硫酸溶液が均一に混合し
たら発泡剤を加えて再度均一な状態となるよう混合し、
しかる後均一に混合した下水汚泥焼却灰及び硫酸溶液並
に発泡剤を混練りして気泡を含んだ粘土状の混練物を形
成した。When the sewage sludge incineration ash and the sulfuric acid solution are uniformly mixed, a foaming agent is added and mixed so as to be uniform again.
Thereafter, the foaming agent was mixed with the uniformly mixed sewage sludge incineration ash and sulfuric acid solution to form a clay-like kneaded material containing bubbles.
【0030】発泡剤としては、水或いは稀酸によって気
体を生ずる粉体、例えば炭酸水素ナトリウム、アルミニ
ューム粉、鉄粉などが用いられる。As the foaming agent, powders which generate gas by water or dilute acid, for example, sodium hydrogen carbonate, aluminum powder, iron powder and the like are used.
【0031】上述のごとく形成した混練物を型枠内にい
っぱいに充填して成形後、自然放置して硬化させると、
気泡を含んだ下水汚泥焼却灰軽量固化物が得られる。When the kneaded material formed as described above is fully filled in a mold, molded, and left to cure naturally,
A lightweight solidified sewage sludge incineration ash containing bubbles is obtained.
【0032】又、或いは型枠内に型枠内容積よりも少い
量の混練物を入れ、所定の温度に加温すると、混練物は
気泡の膨張に従い型枠内容積にいっぱいとなるよう膨張
し、型枠内の形状に忠実に倣った下水汚泥焼却灰軽量固
化物が得られる。この場合、型枠内に入れる粘土状の混
練物の量或いは加温の程度によって広範囲に亘って種々
の単位容積重量の下水汚泥焼却灰軽量固化物が得られ
る。Alternatively, when a kneaded material having a smaller volume than the volume in the mold is put in the mold and heated to a predetermined temperature, the kneaded material expands to fill the volume in the mold as the bubbles expand. In addition, a sewage sludge incineration ash lightweight solidified product that faithfully follows the shape in the formwork can be obtained. In this case, various weights of sewage sludge incinerated ash can be obtained over a wide range depending on the amount of clay-like kneaded material to be put in the mold or the degree of heating.
【0033】ところで、上述のようにして製造された下
水汚泥焼却灰軽量固化物の物性を知るため、幅30mm
×長さ80mm×厚さ10mmの供試体を作り比較試験
を行った。By the way, in order to know the physical properties of the sewage sludge incineration ash lightweight solidified material produced as described above, a width of 30 mm was used.
A test specimen having a length of 80 mm and a thickness of 10 mm was prepared and subjected to a comparative test.
【0034】表3は、各供試体A−1,A−2,A−
3,B−1,B−2,B−3の下水汚泥焼却灰と硫酸9
7%含有濃硫酸と水と発泡剤(NaHCO3)の配合量
を示し、表4は各供試体A−1,A−2,A−3,B−
1,B−2,B−3の物性を示す。Table 3 shows that each specimen A-1, A-2, A-
3, B-1, B-2, B-3 Sewage sludge incineration ash and sulfuric acid 9
The amounts of concentrated sulfuric acid containing 7%, water and a foaming agent (NaHCO 3 ) are shown. Table 4 shows the specimens A-1, A-2, A-3 and B-
1 shows the physical properties of B-2 and B-3.
【0035】而して、供試体A−1,A−2,A−3
は、型枠内にまだ硬化していない粘土状の気泡を含んだ
混練物をいっぱいに充填し、自然放置により硬化させた
後脱型したものである。Specimens A-1, A-2, A-3
Is a mold in which a kneaded material containing uncured clay-like air bubbles is fully filled in a mold frame, cured by standing naturally, and then demolded.
【0036】又、供試体B−1,B−2,B−3は、型
枠内に型枠の内容積よりも少量のまだ硬化していない粘
土状の気泡を含んだ混練物を入れ、蓋で覆ったうえ約9
0℃の温度で10分間加熱し、型枠いっぱいに混練物を
膨張させて硬化し、その後脱型したものである。For the test pieces B-1, B-2, and B-3, a kneaded material containing a small amount of uncured clay-like air bubbles smaller than the inner volume of the mold is placed in the mold. Covered with lid and about 9
The kneaded material was heated at a temperature of 0 ° C. for 10 minutes to expand and knead the kneaded material to fill the mold, and then removed from the mold.
【0037】供試体A−1,A−2,A−3の場合自然
放置により硬化させた後脱型するのは、ひび割れや歪の
ない型枠の形状に忠実に倣った形状の下水汚泥焼却灰軽
量固化物を得るためである。In the case of the specimens A-1, A-2 and A-3, after being cured by natural standing, demolding is performed by incineration of sewage sludge having a shape faithfully following the shape of a mold without cracks or distortion. This is to obtain a light-weight solidified ash.
【0038】又、供試体B−1,B−2,B−3の場
合、加温するのは、型枠内に入れる混練物の量の多少に
拘らず、型枠いっぱいに膨張して型枠の形状に忠実に倣
った形状の下水汚泥焼却灰軽量固化物を得るためであ
る。この場合型枠内に入れる混練物の量を調整すること
により、広範囲に亘って種々の値の単位容積重量の下水
汚泥焼却灰軽量固化物を得ることができる。In the case of the specimens B-1, B-2, and B-3, the heating was performed by expanding the mold to fill the mold regardless of the amount of the kneaded material put in the mold. This is to obtain a lightly solidified sewage sludge incineration ash shape that faithfully follows the shape of the frame. In this case, by adjusting the amount of the kneaded material to be put into the mold, it is possible to obtain a light weight solidified sewage sludge incinerated ash with various unit weights over a wide range.
【0039】[0039]
【表3】 [Table 3]
【0040】[0040]
【表4】 [Table 4]
【0041】本来、微細でポーラスな形状の表面積の大
きい高分子系凝集剤を含んだ下水汚泥焼却灰は、硫酸溶
液で改質されると共に発泡剤によって多量の気泡を含ん
だ混練物となる。Originally, sewage sludge incineration ash containing a high molecular surface flocculant having a fine, porous shape and a large surface area is modified by a sulfuric acid solution and becomes a kneaded material containing a large amount of bubbles by a foaming agent.
【0042】又、混練物は粘土状であるため成形自由度
が高く、種々の成形形状に対応できる。Further, since the kneaded material is clay-like, it has a high degree of freedom in molding and can cope with various molding shapes.
【0043】更に粘土状の混練物にグラスファイバなど
の繊維補強材を添加、混合する場合においても、同様に
種々の成形形状を得ることができる。Further, even when a fiber reinforcing material such as glass fiber is added to and mixed with the clay-like kneaded material, various molded shapes can be similarly obtained.
【0044】混練物は常温下に自然放置しても十分に自
己硬化するため、高品質の下水汚泥焼却灰軽量固化物を
製造することができる。The kneaded material is sufficiently self-cured even when left naturally at normal temperature, so that a high-quality light-weight solidified sewage sludge incinerated ash can be produced.
【0045】又、上述のごとく、密閉した型枠内に型枠
の容積よりも少量の混練物を入れ、加温して型枠内いっ
ぱいに膨張させた場合には、最初に型枠内に入れる混練
物の量を調整することにより異なった値の単位容積重量
の下水汚泥焼却灰軽量固化物を得ることができ、延いて
は種々の曲げ強度の下水汚泥焼却灰軽量固化物を製造す
ることができる。As described above, when a kneaded material smaller than the volume of the mold is placed in the closed mold and heated to expand the mold completely, the mold is first placed in the mold. By adjusting the amount of kneaded materials to be put, it is possible to obtain light weight solidified sewage sludge incinerated ash with different unit weights of unit weight, and to produce light weight solidified sewage sludge incinerated ash with various bending strengths. Can be.
【0046】得られた下水汚泥焼却灰軽量固化物は若干
酸性であり、又吸水性はセメントモルタルに比較して少
く、無機材であるため完全に不燃性を備えている。The obtained lightly solidified sewage sludge incineration ash is slightly acidic, has a lower water absorption than cement mortar, and is completely nonflammable because it is an inorganic material.
【0047】[実施例1]なお、以下の実施例において
は、室温20〜25℃の室内ですべての作業を行った。Example 1 In the following examples, all operations were performed in a room at a room temperature of 20 to 25 ° C.
【0048】表1に示す化学組成の下水汚泥焼却灰30
grと、硫酸97%含有濃硫酸3.3cc及び水10c
cを混合して室内に放置した硫酸溶液とを、冷却した厚
手の陶器製の鉢の中で温度が35℃を越えないように冷
却しつつ混合し、この混合物に発泡剤として炭酸水素ナ
トリウム0.3grを添加し、再び良く混合して得られ
た混合物をスクリュー式混練り機によって剪断的に混練
りし、気泡を多く含んだ褐色の粘土状の混練物を得た。The sewage sludge incineration ash 30 having the chemical composition shown in Table 1
gr, 3.3 cc of concentrated sulfuric acid containing 97% sulfuric acid and 10 c of water
c and mixed with the sulfuric acid solution left in the room while cooling in a cooled thick ceramic bowl so that the temperature does not exceed 35 ° C. 0.3 gr was added, and the mixture was mixed well again. The mixture was sheared and kneaded with a screw kneader to obtain a brown clay-like kneaded material containing many air bubbles.
【0049】次に、図1に示すごとく得られた混練物1
を型枠2内にいっぱいに充填し、室内に2時間の間放置
し、脱型した混練物をその後14日間自然養生し、硬化
させた。Next, the kneaded material 1 obtained as shown in FIG.
Was fully filled in the mold 2, left in the room for 2 hours, and the demolded kneaded material was naturally cured and cured for 14 days thereafter.
【0050】これにより、強固な褐色の下水汚泥焼却灰
軽量固化物を得た。これが表5の供試体A−1に相当す
る。As a result, a light brown solidified incinerated sewage sludge ash was obtained. This corresponds to the specimen A-1 in Table 5.
【0051】同様に炭酸水素ナトリウムの添加量を0.
15gr、0.45grとし、図1に示すようにして下
水汚泥焼却灰軽量固化物を製造した。炭酸水素ナトリウ
ムの添加量0.15grのものは表5の供試体A−2に
相当し、炭酸水素ナトリウムの添加量0.45grのも
のは表5の供試体A−3に相当する。Similarly, the amount of sodium bicarbonate added is set to 0.1.
The weight was set to 15 gr and 0.45 gr, and a light-weight solidified sewage sludge incinerated ash was produced as shown in FIG. The sample with the added amount of sodium hydrogencarbonate of 0.15 gr corresponds to the sample A-2 in Table 5, and the sample with the added amount of sodium hydrogencarbonate of 0.45 gr corresponds to the sample A-3 in Table 5.
【0052】表5に示す供試体A−1,A−2,A−3
を水道水に浸透させた際のpHの変化は図3の実線イに
示されている。Specimens A-1, A-2, A-3 shown in Table 5
The change in pH when water was permeated into tap water is shown by the solid line A in FIG.
【0053】図3に示すごとく、各供試体A−1,A−
2,A−3を10日間水道水に浸透させても、大きなp
H変化は生じず、これは、供試体A−1,A−2,A−
3からの酸の溶出が少いことを示している。As shown in FIG. 3, each specimen A-1, A-
Even if the A-3 is infiltrated into tap water for 10 days, a large p
No H change occurred, which was caused by specimens A-1, A-2, A-
3 indicates less elution of acid from 3.
【0054】[実施例2]表1に示す化学組成の下水汚
泥焼却灰30grと、硫酸97%含有濃硫酸3.3cc
及び水10ccを混合して室内に放置した硫酸溶液と
を、冷却した厚手の陶器製の鉢の中で温度が35℃を越
えないように冷却しつつ混合し、この混合物に発泡剤と
して炭酸水素ナトリウム0.3grを添加し、再び良く
混合して得られた混合物をスクリュー式混練り機によっ
て剪断的に混練りし、気泡を多く含んだ褐色の粘土状の
混練物を得た。Example 2 30 gr of sewage sludge incineration ash having the chemical composition shown in Table 1 and 3.3 cc of concentrated sulfuric acid containing 97% sulfuric acid
And a sulfuric acid solution mixed with 10 cc of water and allowed to stand in a room while being cooled in a cooled thick ceramic bowl so that the temperature does not exceed 35 ° C. 0.3 gr of sodium was added, and the mixture was mixed well again. The mixture was sheared and kneaded with a screw kneader to obtain a brown clay-like kneaded material containing many air bubbles.
【0055】次に、図2に示すごとくこの得られた混練
物1のうち25grを型枠2に入れ、蓋3をして90℃
の温度で10分間加温し、混練物1を型枠2いっぱいに
膨張させると共に硬化させ、成形体として型枠2から外
せる強度に達した後に脱型した。而して、その後14日
間自然養生をし、硬化させた。Next, as shown in FIG. 2, 25 gr of the kneaded material 1 thus obtained was put into the mold 2, and the lid 3 was closed, and 90 ° C.
The kneaded material 1 was expanded to fill the mold 2 and hardened at the same temperature for 10 minutes, and was released after reaching a strength at which it could be removed from the mold 2 as a molded product. After that, natural curing was performed for 14 days, followed by curing.
【0056】これにより、強固な褐色の下水汚泥焼却灰
軽量固化物を得た。これが表5の供試体B−1に相当す
る。As a result, a strong brown light-weight solidified sewage sludge incineration ash was obtained. This corresponds to the specimen B-1 in Table 5.
【0057】同様に上述のごとくして製造した混練物1
の量を20gr、30grとし、図2に示すようにして
下水汚泥焼却灰軽量固化物を製造した。混練物1の量が
20grのものは表5の供試体B−2に相当し、混練物
1の量が30grのものは表5の供試体B−3に相当す
る。The kneaded material 1 similarly produced as described above
The amount of sewage sludge incineration ash was lightly solidified as shown in FIG. When the amount of the kneaded material 1 is 20 gr, it corresponds to the specimen B-2 in Table 5, and when the amount of the kneaded material 1 is 30 gr, it corresponds to the specimen B-3 in Table 5.
【0058】表5に示す供試体B−1,B−2,B−3
を水道水に浸透させた際のpHの変化は図3の実線ロに
示されている。Specimens B-1, B-2 and B-3 shown in Table 5
The change in pH when water was permeated into tap water is shown by the solid line b in FIG.
【0059】図3に示すごとく、各供試体B−1,B−
2,B−3を10日間水道水に浸透させても、大きなp
H変化は生じず、これは供試体B−1,B−2,B−3
からの酸の溶出が少いことを示している。As shown in FIG. 3, each specimen B-1, B-
2, B-3 can be infiltrated into tap water for 10 days,
No H change occurred, which was caused by specimens B-1, B-2, and B-3.
This indicates that the elution of the acid from the gel was low.
【0060】[0060]
【表5】 [Table 5]
【0061】[0061]
【発明の効果】本発明の下水汚泥焼却灰軽量固化物の製
造方法によれば下記のごとき種々の優れた効果を奏し得
る。According to the method for producing a lightly solidified sewage sludge incinerated ash according to the present invention, various excellent effects can be obtained as follows.
【0062】I)得られた高分子系凝集剤を含む下水汚
泥焼却灰軽量固化物は、単位容積重量が軽量コンクリー
トなどと同様軽いうえ、軽量コンクリートなどに比し曲
げ強度が高く且つ吸水量が少く、しかも使用する酸の量
も少く、更には酸溶出量も少い。このため、高品質の下
水汚泥焼却灰軽量固化物を得ることができる。I) The obtained lightly solidified sewage sludge incinerated ash containing a polymer-based flocculant has a unit weight per unit weight similar to that of lightweight concrete and the like, and has a higher bending strength and a higher water absorption than lightweight concrete and the like. The amount of acid used is small, and the amount of acid eluted is also small. For this reason, a high-quality sewage sludge incineration ash lightweight solidified product can be obtained.
【0063】II)下水汚泥焼却灰軽量固化物は高分子
系凝集剤を含む下水汚泥焼却灰と、酸溶液と、発泡剤を
もとにして製造されるため、製造及び取扱に特別な配慮
を必要とする物質が不用で、又設備についても特別のも
のは必要ない。II) Sewage sludge incineration ash Light-weight solidified products are produced based on sewage sludge incineration ash containing a polymer-based flocculant, an acid solution, and a foaming agent. The required substances are unnecessary, and no special equipment is required.
【0064】III)発泡剤の量を調整することにより
或いは型枠内へ入れる混練物の重量を調整することによ
り、広範囲に亘って種々の値の単位容積重量の下水汚泥
焼却灰軽量固化物を製造することができる。III) By adjusting the amount of the foaming agent or the weight of the kneaded material to be put into the mold, the sewage sludge incineration ash lightweight solidified material having various unit weights over a wide range can be obtained. Can be manufactured.
【0065】IV)排水を初めなんらの副成物も生じ
ず、又溶融、焼結のように熱を必要とすることもない。
従って、装置や操作についても特別な配慮の必要がな
い。IV) No by-products are generated at the beginning of the drainage, and no heat is required unlike melting and sintering.
Therefore, no special consideration is required for the device and operation.
【0066】V)下水汚泥焼却灰軽量固形物は、混練直
後は粘土状をしていてプラスチックのような成形自由度
をもちしかも短時間で硬化するため、種々の形状に成形
することができ、グラスファイバなどの繊維補強材の混
入も可能である。V) The sewage sludge incineration ash lightweight solid is clay-like immediately after kneading, has a molding freedom like plastic, and is hardened in a short time, so that it can be molded into various shapes. It is also possible to mix fiber reinforcing materials such as glass fibers.
【0067】VI)成形の仕方や下水汚泥焼却灰軽量固
形物の形状に応じて温度管理を行うことにより混練物硬
化の速度を適切にすることが可能である。VI) By controlling the temperature in accordance with the method of molding and the shape of the sewage sludge incinerated ash lightweight solid, it is possible to make the kneaded material hardening speed appropriate.
【0068】VII)十分硬化した下水汚泥焼却灰軽量
固形物は、弱酸性で有害な物質の溶出もない。無機素材
なるがゆえ不燃で通常の温度においてはガスの発生もな
い。更に未処理の下水汚泥焼却灰に比し単位容積重量が
増加するため取扱が容易で著しい減容になる。VII) The fully cured sewage sludge incineration ash lightweight solids are weakly acidic and do not elute harmful substances. Since it is an inorganic material, it is nonflammable and does not generate gas at normal temperatures. Furthermore, since the unit volume weight is increased as compared with untreated sewage sludge incineration ash, handling is easy and the volume is significantly reduced.
【0069】VIII)下水汚泥焼却灰軽量固形物は、
セメントと異なり酸性であり、セメントの不得意とする
酸性雰囲気による素材としても有効である。複合材料と
してグラスファイバなどの繊維補強材と併用する場合に
も、セメントに対するような耐アルカリ性の繊維補強材
を必要としない。VIII) Sewage sludge incineration ash lightweight solids
Unlike cement, it is acidic, and is also effective as a material in an acidic atmosphere that cement is not good at. Even when used in combination with a fiber reinforcing material such as glass fiber as a composite material, an alkali-resistant fiber reinforcing material such as for cement is not required.
【0070】IX)下水汚泥焼却灰を廃棄物とせず、酸
で処理した成形自由度の高い耐酸、耐火、高強度、軽量
の新素材とすることができるので、下水汚泥焼却灰の減
量、減容と資源としての有効利用を可能とすることがで
きる。IX) The sewage sludge incineration ash can be made into a new acid-resistant, fire-resistant, high-strength, lightweight material that is treated with an acid and has a high degree of freedom of molding, without turning ash from sewage sludge into waste. It is possible to make effective use of resources and resources.
【図1】本発明の実施例1における型枠とその中に充墳
した混練物を示す断面図である。FIG. 1 is a cross-sectional view illustrating a mold and a kneaded material charged therein according to a first embodiment of the present invention.
【図2】本発明の実施例2における型枠とその中に入れ
た混練物の加温前の状態を示す断面図である。FIG. 2 is a cross-sectional view showing a state before heating of a mold and a kneaded material placed therein in Embodiment 2 of the present invention.
【図3】本発明の実施例において、下水汚泥焼却灰軽量
固形物から酸が溶出してpHが経時的に変化する状態を
示すグラフである。FIG. 3 is a graph showing a state in which acid is eluted from sewage sludge incineration ash lightweight solid matter and the pH changes with time in an example of the present invention.
1 混練物 2 型枠 3 蓋 1 kneaded material 2 formwork 3 lid
Claims (2)
却灰及び酸並に発泡剤を混合すると共に混練して多量の
気泡を含んだ粘土状の混練物を作成し、該混練物を成形
して自然乾燥し、固化させることを特徴とする下水汚泥
焼却灰軽量固化物の製造方法。1. A sewage sludge incineration ash to which a polymer-based flocculant has been added and a foaming agent as well as an acid are mixed and kneaded to prepare a clay-like kneaded material containing a large amount of air bubbles. A method for producing a lightly solidified sewage sludge incinerated ash, which is formed, air-dried, and solidified.
却灰及び酸並に発泡剤を混合すると共に混練して多量の
気泡を含んだ粘土状の混練物を作成し、所定量の混練物
を型枠内に入れて加温し、膨張させると共に固化させる
ことを特徴とする下水汚泥焼却灰軽量固化物の製造方
法。2. A sewage sludge incineration ash to which a polymer-based flocculant has been added and a foaming agent as well as an acid are mixed and kneaded to form a clay-like kneaded material containing a large amount of air bubbles, and a predetermined amount of kneading is performed. A method for producing a lightly solidified sewage sludge incinerated ash, which comprises placing an object in a mold, heating, expanding and solidifying the object.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP10039113A JPH11226549A (en) | 1998-02-20 | 1998-02-20 | Production of sewage sludge incineration ash lightweight solidified material |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP10039113A JPH11226549A (en) | 1998-02-20 | 1998-02-20 | Production of sewage sludge incineration ash lightweight solidified material |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH11226549A true JPH11226549A (en) | 1999-08-24 |
Family
ID=12544035
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP10039113A Pending JPH11226549A (en) | 1998-02-20 | 1998-02-20 | Production of sewage sludge incineration ash lightweight solidified material |
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Country | Link |
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JP (1) | JPH11226549A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2007532302A (en) * | 2004-04-14 | 2007-11-15 | ソルヴェイ(ソシエテ アノニム) | Sludge treatment method |
JP2011025245A (en) * | 2002-10-16 | 2011-02-10 | Solvay (Sa) | Method for treating sludge |
JP2011245404A (en) * | 2010-05-26 | 2011-12-08 | Central Res Inst Of Electric Power Ind | Method for producing solidified body |
JP2012187459A (en) * | 2011-03-09 | 2012-10-04 | Tokyo Metropolitan Sewerage Service Corp | Method for utilizing sewage sludge incineration ash |
-
1998
- 1998-02-20 JP JP10039113A patent/JPH11226549A/en active Pending
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2011025245A (en) * | 2002-10-16 | 2011-02-10 | Solvay (Sa) | Method for treating sludge |
JP2007532302A (en) * | 2004-04-14 | 2007-11-15 | ソルヴェイ(ソシエテ アノニム) | Sludge treatment method |
JP2011245404A (en) * | 2010-05-26 | 2011-12-08 | Central Res Inst Of Electric Power Ind | Method for producing solidified body |
JP2012187459A (en) * | 2011-03-09 | 2012-10-04 | Tokyo Metropolitan Sewerage Service Corp | Method for utilizing sewage sludge incineration ash |
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