JP3044611B2 - Construction method and material of upper subbase with mixed incineration ash - Google Patents

Construction method and material of upper subbase with mixed incineration ash

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Publication number
JP3044611B2
JP3044611B2 JP9212502A JP21250297A JP3044611B2 JP 3044611 B2 JP3044611 B2 JP 3044611B2 JP 9212502 A JP9212502 A JP 9212502A JP 21250297 A JP21250297 A JP 21250297A JP 3044611 B2 JP3044611 B2 JP 3044611B2
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JP
Japan
Prior art keywords
asphalt
crushed
cement
granular material
asphalt emulsion
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 - Fee Related
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JP9212502A
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Japanese (ja)
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JPH1136209A (en
Inventor
和平 西村
Original Assignee
株式会社市場西村建設
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Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は道路の施工方法およ
び道路の構成材料に関するものであり、特に一般焼却灰
を混用して一般焼却灰の処理を図ると共に有害成分の溶
出を防止し、かつアスファルト廃材等の有効活用を図り
得る上層路盤の施工方法および上層路盤材料に関するも
のである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a road construction method and a road material, and more particularly to a method of treating general incinerated ash by mixing general incinerated ash, preventing elution of harmful components, and asphalt. The present invention relates to an upper roadbed construction method and an upper roadbed material capable of effectively utilizing waste materials and the like.

【0002】[0002]

【従来の技術】従来より一般廃棄物を焼却してできた焼
却灰は埋め立てる等してその処理を図っているが、ある
種の産業廃棄物の焼却灰や分別が充分なされていない一
般家庭廃棄物の焼却灰の中には、ダイオキシン等の有害
成分が溶出し、公害を引き起こすおそれがあり、近年社
会的な問題となっている。そこで、埋立地の地中下方に
不透水性シートを配置して、有害成分の漏出を防止する
手段等が提案されている。
2. Description of the Related Art Conventionally, incineration ash produced by incineration of general waste has been treated by burying it in landfills. However, incineration ash of certain types of industrial waste and general household waste that has not been sufficiently separated have been used. Harmful components such as dioxin are eluted in the incineration ash of the products, and may cause pollution, which has become a social problem in recent years. Therefore, means for preventing leakage of harmful components and the like by disposing a water-impermeable sheet below ground in a landfill has been proposed.

【0003】[0003]

【発明が解決しようとする課題】ところが、前記不透水
性シートを地下に配置する手段によっても有害成分の漏
出防止が完全に行いうるかどうか疑問視する向きもあ
り、全国各地で埋立地の設置に地元住民の反対があるこ
とから国や各市町村では、埋め立てもままならず、また
他の有効な上記焼却灰の処分方法も見当らず、手詰りの
状態にあり、さりとて焼却灰をそのまま野積みにし放置
しておくわけにもいかず、社会的に大きな問題になって
いる。なお、焼却灰をセメントで固めたり、容器に詰め
たりすることも提案されているが、これらを野積みにす
るには、ぼう大な敷地が必要となり、また容器の腐食
や、破損により、あるいはセメントから有害成分が漏れ
だすおそれがあり、実現困難である。本発明はこのよう
な事情を背景としてなされたものであり、本発明の目的
は、焼却灰の処理(処分)を図ると共に有害成分の漏出
を防止し、かつ産業廃棄物たるアスファルト廃材の有効
活用を計り得る上層路盤の施工方法および上層路盤材料
を提供しようとするものである。なお、アスファルト廃
材を上層路盤に使用することについては、本願発明者ら
によって既に提案されている。特開平8ー226101
号の上層路盤の施工方法および上層路盤材料がこれであ
る。
However, some people question whether or not the means for arranging the water-impermeable sheet underground can completely prevent the leakage of harmful components. Due to the opposition of local residents, the government and municipalities have not been able to reclaim landfills and have found no other effective disposal method of the above incinerated ash, and are in a clogged state. It is a big social issue that we can't afford to keep. It has also been proposed to solidify the incinerated ash with cement or pack it in a container.However, in order to stack these materials, a large site is required, and because of the corrosion or damage of the container, or Harmful components may leak from the cement, which is difficult to achieve. The present invention has been made in view of such circumstances, and an object of the present invention is to treat (dispose) incinerated ash, prevent leakage of harmful components, and effectively utilize asphalt waste material, which is industrial waste. It is an object of the present invention to provide an upper subbase construction method and an upper subbase material capable of measuring the following. The use of asphalt waste for the upper roadbed has already been proposed by the present inventors. JP-A-8-226101
This is the method of construction of the upper roadbed and the material of the upper roadbed.

【0004】[0004]

【課題を解決するための手段】本発明は、前記目的を達
成するためになされたものであり、本発明は下記のよう
に構成される。 A 一般廃棄物の焼却灰とアスファルト乳剤と適当な水
とを少なくとも混合し、乾燥後破砕した粒径5mm程度
以下の粒状材料と、粒径が40mm以下のアスファルト
廃材の破砕物と、一般再生砕石と、セメントと、セメン
トが飛散しない程度の水とを、所定場所に固設した混合
用のプラントを使用する中央プラント方式で混合してか
ら、該混合物を施工個所に運搬し、施工するようにした
焼却灰を混用した上層路盤の施工方法。 B 前記A項記載の上層路盤の施工方法において、前記
粒状材料と、前記アスファルト廃材の破砕物と、前記一
般再生砕石との合計量に対する重量比は前記粒状材料が
5〜30%、前記アスファルト廃材の破砕物が30〜7
0%、前記一般再生砕石が20〜40%であり、かつ前
記アスファルト乳剤は焼却灰とアスファルト乳剤との合
計量に対する重量比が5〜50%である焼却灰を混用し
た上層路盤の施工方法。 C 一般廃棄物の焼却灰とアスファルト乳剤と適当な水
とを少なくとも混合し、乾燥後破砕した粒径5mm程度
以下の粒状材料と、粒径が40mm以下のアスファルト
廃材の破砕物と、一般再生砕石と、セメントと、セメン
トが飛散しない程度の水とを少なくとも含み、かつこれ
らを所定場所に固設した混合用のプラントを使用する中
央プラント方式で混合してなる上層路盤材料。 D 前記C項記載の上層路盤材料において、前記粒状材
料と、前記アスファルト廃材の破砕物と、前記一般再生
砕石との合計量に対する重量比は前記粒状材料が5〜3
0%、前記アスファルト廃材の破砕物が30〜70%、
前記一般再生砕石が20〜40%であり、かつ前記アス
ファルト乳剤は焼却灰とアスファルト乳剤との合計量に
対する重量比が5〜50%である上層路盤材料。 E 前記A項もしくはB項記載の上層路盤の施工方法に
おいて、前記粒状材料には、その製造時に焼却灰とアス
ファルト乳剤と水の他にさらに少量のセメント及び/又
は石灰を加え混合するようにした焼却灰を混用した上層
路盤の施工方法。 F 前記C項もしくはD項記載の上層路盤材料におい
て、前記粒状材料には、その製造時に焼却灰とアスファ
ルト乳剤と水の他にさらに少量のセメント及び/又は石
灰を加え混合するようにした上層路盤材料。 ここに、「アスファルト廃材の破砕物」とはアスファル
ト再生骨材といわれるものであり、「粒径が40mm以
下のアスファルト廃材の破砕物」とは、40mm角の篩
目から落ちる程度の大きさのアスファルト再生骨材を意
味する。また、「一般再生砕石」とは路盤の破砕物であ
り、路盤再生骨材といわれるものである。
Means for Solving the Problems The present invention has been made to achieve the above object, and the present invention has the following constitution. A Granulated material having a particle size of about 5 mm or less, which is obtained by mixing at least incineration ash of general waste, asphalt emulsion, and appropriate water, drying and crushing, crushed asphalt waste material having a particle size of 40 mm or less, and general recycled crushed stone And, cement, and water that does not scatter the cement, after mixing by a central plant method using a mixing plant fixed in place, transport the mixture to the construction site, and to construct Construction method of upper subgrade using mixed incineration ash. B In the method for constructing an upper roadbed according to the above A, the weight ratio of the granular material, the crushed asphalt waste material, and the general recycled crushed stone to the total amount of the granular material is 5 to 30%, and the asphalt waste material is 30 to 7 crushed pieces
A method of constructing an upper roadbed using a mixture of incinerated ash having a weight ratio of 0% to 20% to 40% for the general recycled crushed stone and 5 to 50% by weight of the asphalt emulsion to the total amount of the incinerated ash and the asphalt emulsion. C Granulated material having a particle size of about 5 mm or less, which is obtained by mixing at least incineration ash of general waste, asphalt emulsion and appropriate water, drying and crushing, crushed asphalt waste material having a particle size of 40 mm or less, and general recycled crushed stone And an upper roadbed material obtained by mixing at least a cement and water to such an extent that the cement is not scattered, and mixing them by a central plant method using a mixing plant fixed at a predetermined place. D In the upper roadbed material according to C, the weight ratio of the granular material, the crushed asphalt waste material, and the general recycled crushed stone to the total amount of 5 to 3 is as follows.
0%, the crushed material of the asphalt waste material is 30 to 70%,
An upper roadbed material in which the general recycled crushed stone is 20 to 40% and the asphalt emulsion has a weight ratio of 5 to 50% with respect to the total amount of incinerated ash and asphalt emulsion. E In the method for constructing an upper subgrade described in the above item A or B, in addition to incinerated ash, asphalt emulsion and water, a small amount of cement and / or lime is added to the granular material and mixed. Construction method of upper subgrade using incineration ash. F. The upper roadbed material according to the above item C or D, wherein the granular material is mixed with a small amount of cement and / or lime in addition to incineration ash, asphalt emulsion and water during the production thereof. material. Here, "crushed asphalt waste material" is referred to as asphalt recycled aggregate, and "crushed asphalt waste material having a particle size of 40 mm or less" is a size of about 40 mm square that falls from a sieve. It means asphalt recycled aggregate. The “general reclaimed crushed stone” is a crushed material of a roadbed, and is called a roadbed regenerated aggregate.

【0005】[0005]

【発明の実施の形態】先ず、一般廃棄物の焼却灰にアス
ファルト乳剤を加え、さらに適量の水を加えよく混合
し、これを潰すことができる程度に乾燥し、乾燥後摺り
潰しあるいはその他の方法により破砕してから、5mm
目程度のフルイで篩別して粒状材料を製造する。すなわ
ち、フルイを通過して下に落ちたものが粒状材料であ
る。焼却灰は大形の焼却残渣等が混じっている場合に
は、あらかじめ除いておくことが望ましい。また、焼却
灰としては家庭廃棄物の焼却灰、産業廃棄物の焼却灰あ
るいはこれらの混合物、さらには廃棄物から有害成分の
もれ出すおそれのある物質を除いた後焼却した焼却灰等
を使用できるが、有害成分は廃棄物処理関連の法律で許
容された範囲内であることが望ましい。アスファルト乳
剤は、有害成分の溶出防止のためには多いほどよいが、
焼却灰とアスファルト乳剤との合計量に対するアスファ
ルト乳剤の重量比が50%より大きくなると、団子状と
なり摺り潰しにくく粒状にしにくいので、50%を越え
ない範囲にとどめる。粒状材料製造時に焼却灰、アスフ
ァルト乳剤に加える水の量は、多くすると混ぜ易いが乾
燥時間が長くなるので、このことを勘案して決定する。
また、粒状材料の製造時には、必要に応じて、上記材料
に少量(1〜5%)の石灰、セメント等を加えることも
ある。混ぜ合わせた材料の乾燥に要する期間は、アスフ
ァルト乳剤の量や加えた水の量、混合物全体の量によっ
ても異なるが、自然乾燥で数日程度である。通風乾燥等
の手段も考えられる。このようにして製造した粒状材料
は、保存できるので有害成分の溶出試験の結果が判るま
で保管することができ、便利である。上記粒状材料と、
粒径が40mm以下のアスファルト廃材の破砕物(アス
ファルト再生骨材)と、一般再生砕石(路盤再生骨材)
と、セメントと、セメントが飛散しない程度の水とを、
中央プラント方式で混合すると、本発明の上層路盤材料
となり、該混合物を施工現場に運搬して施工すれば、本
発明の上層路盤の施工方法となる。各材料の混合比は、
粒状材料とアスファルト廃材の破砕物と一般再生砕石と
の合計量に対する重量比は、粒状材料が5〜30%、ア
スファルト廃材の破砕物が30〜70%、一般再生砕石
が20〜40%の範囲内であるが、日本道路協会のアス
ファルト舗装要綱の基準値を満足し、かつ経済的製造が
可能となるように決定することが望ましい。なお、中央
プラント方式とは所定場所に固設した混合用のプラント
を使用して行う方式であり、施工現場にて混合する路上
混合方式に対応する方式である。
DESCRIPTION OF THE PREFERRED EMBODIMENTS First, an asphalt emulsion is added to the incineration ash of general waste, an appropriate amount of water is further added and mixed well, and the mixture is dried to such an extent that it can be crushed. After crushing by 5mm
A granular material is produced by sieving with a coarse sieve. That is, the material that has passed through the sieve and dropped down is the granular material. It is desirable to remove incineration ash in advance when large incineration residues are mixed. Also, as incineration ash, incineration ash from household waste, incineration ash from industrial waste, or a mixture thereof, or incineration ash after removing substances that may leak harmful components from waste, etc. It is possible, but it is desirable that harmful components be within the range permitted by waste disposal laws. The more asphalt emulsion, the better to prevent the elution of harmful components, the better,
If the weight ratio of the asphalt emulsion to the total amount of the incineration ash and the asphalt emulsion is more than 50%, the asphalt emulsion becomes a dumpling and is hard to be crushed and granulated, so that it is not more than 50%. The amount of water to be added to the incineration ash and asphalt emulsion during the production of the granular material is determined by taking into account this fact, because if it is increased, it is easy to mix, but the drying time becomes longer.
In addition, when manufacturing the granular material, a small amount (1 to 5%) of lime, cement, or the like may be added to the above material as needed. The time required for drying the mixed material varies depending on the amount of asphalt emulsion, the amount of water added, and the total amount of the mixture, but is about several days for natural drying. Means such as ventilation drying are also conceivable. The granular material produced in this way can be stored, so that it can be conveniently stored until the result of the dissolution test of harmful components is known. Said granular material;
Crushed asphalt waste material with a particle size of 40 mm or less (recycled asphalt aggregate) and general recycled crushed stone (recycled roadbed aggregate)
And the cement and water that does not scatter the cement,
When mixed by the central plant method, it becomes the upper subbase material of the present invention, and when the mixture is transported to the construction site and executed, the upper subbase construction method of the present invention is achieved. The mixing ratio of each material is
The weight ratio to the total amount of the granular material, the crushed asphalt waste material and the general recycled crushed stone ranges from 5 to 30% for the granular material, 30 to 70% for the crushed asphalt waste material, and 20 to 40% for the general recycled crushed stone. However, it is desirable that the value be determined so as to satisfy the standard value of the Asphalt Pavement Outline of the Japan Road Association and to enable economical production. Note that the central plant method is a method that uses a mixing plant fixed at a predetermined place and is a method corresponding to an on-road mixing method of mixing at a construction site.

【0006】[0006]

【実施例】【Example】

[実施例1]一般廃棄物の焼却灰10、アスファルト乳
剤5、水5の重量比でよく混ぜ合わせてから3日間自然
乾燥させ、これを摺り潰してから篩別し、5mm目程度
のフルイを通過した粒状材料と、アスファルト再生骨材
と、路盤再生骨材とを中央プラント方式で混合し、日本
道路協会の路上再生路盤工法技術指針(案)により再生
セメント瀝青安定処理を行った。すなわち、粒状材料と
アスファルト再生骨材と路盤再生骨材との合計重量に対
する各材料の重量比は、粒状材料が5または10%、ア
スファルト再生骨材が70%、路盤再生骨材が20また
は25%とした場合の試験結果を表1に示す。なお、表
1には、最適含水比を決定するための突き固め試験の結
果と、最適添加材量を併記する。
[Example 1] The incineration ash 10 of general waste, the asphalt emulsion 5 and the water 5 were mixed well in a weight ratio, then dried naturally for 3 days, crushed, sieved, and sieved to a size of about 5 mm. The passed granular material, asphalt recycled aggregate, and roadbed recycled aggregate were mixed by a central plant system, and the recycled cement bitumen stabilization treatment was performed according to the Japan Road Association's Road Recycling Roadbed Construction Technical Guideline (draft). That is, the weight ratio of each material to the total weight of the granular material, the asphalt recycled aggregate, and the roadbed recycled aggregate is 5 or 10% for the granular material, 70% for the asphalt recycled aggregate, and 20 or 25 for the recycled roadbed aggregate. Table 1 shows the test results in the case of%. Table 1 also shows the results of a tamping test for determining the optimum water content and the optimum amount of additive.

【表1】 (注1)ここで、アスファルト乳剤量が0%であるとい
うことは、粒状材料、アスファルト再生骨材および一般
再生砕石に対し、さらに添加するアスファルト乳剤量が
0%であることを意味する。表1から判るように粒状材
料5%混入、10%混入のいずれの場合も一軸圧縮強
さ、残留強度率は、再生セメント瀝青安定処理の基準値
を満足し、たわみ性と剛性を有し、上層路盤として使用
可能である。セメント添加量も2%程度となり、経済的
な再生セメント瀝青安定処理混合物の製造が可能であ
る。焼却灰に含まれる有害成分等は事前にアスファルト
乳剤により被覆されるため、溶出しにくいので、再生セ
メント瀝青安定処理混合物が環境に及ぼす影響は少ない
と考えられる。なお、粒状材料は上層路盤に使用する前
に有害成分の溶出試験し、廃棄物処理関連の法律に規定
された許容値を満足するかどうか確認することが必要で
あるが、粒状材料は溶出試験までそのまま保管できるの
で、便利である。 表2、表3はそれぞれ焼却灰、アス
ファルト再生骨材のふるい分け試験(JISA110
2)の結果を示す。図1は上記粒状材料の粒度曲線図を
示す。
[Table 1] (Note 1) Here, the fact that the amount of asphalt emulsion is 0% means that the amount of asphalt emulsion further added to the granular material, asphalt regenerated aggregate and general reclaimed crushed stone is 0%. As can be seen from Table 1, the uniaxial compressive strength and the residual strength ratio satisfy the standard values of the stabilized cement bitumen stabilization treatment in both cases of 5% and 10% of the granular material, and have flexibility and rigidity. It can be used as an upper roadbed. The amount of cement added is also about 2%, and an economical production of a regenerated cement bitumen stabilizing mixture is possible. The harmful components and the like contained in the incineration ash are preliminarily covered with the asphalt emulsion and are therefore hardly eluted, so that it is considered that the stabilized cement bitumen mixture has little effect on the environment. Before using granular materials in the upper subgrade, it is necessary to perform a dissolution test for harmful components to confirm that the tolerance satisfies the allowable value prescribed by the law on waste disposal. It is convenient because it can be stored as it is. Tables 2 and 3 show the sieving test (JISA110) of incinerated ash and asphalt recycled aggregate, respectively.
The result of 2) is shown. FIG. 1 shows a particle size curve diagram of the granular material.

【表2】 [Table 2]

【表3】 [Table 3]

【0007】[実施例2]一般廃棄物の焼却灰10、ア
スファルト乳剤1、水9の重量比でよく混ぜ合わせてか
ら3日間自然乾燥させ、これを摺り潰してから篩別し、
5mm目程度のフルイを通過した粒状材料と、アスファ
ルト再生骨材と、路盤再生骨材とを中央プラント方式で
混合し、日本道路協会の路上再生路盤工法技術指針
(案)により再生セメント瀝青安定処理を行った。すな
わち、粒状材料とアスファルト再生骨材と路盤再生骨材
との合計重量に対する各材料の重量比は、粒状材料が5
または10%、アスファルト再生骨材が70%、路盤再
生骨材が20または25%とした場合の試験結果を表4
に示す。なお、表4には、最適含水比を決定するための
突き固め試験の結果と、最適添加材量を併記する。
Example 2 The incineration ash 10 of general waste, the asphalt emulsion 1 and the water 9 were mixed well in a weight ratio, then dried naturally for 3 days, crushed and sieved.
The granular material that has passed through a sieve of about 5 mm, asphalt recycled aggregate, and roadbed recycled aggregate are mixed by the central plant method, and the recycled cement bitumen stabilization treatment is performed according to the Japan Road Association's Road Recycling Roadbed Construction Technical Guideline (draft). Was done. That is, the weight ratio of each material to the total weight of the granular material, the asphalt recycled aggregate, and the roadbed recycled aggregate is 5% for the granular material.
Table 4 shows the test results when the asphalt recycled aggregate was 70% and the roadbed recycled aggregate was 20 or 25%.
Shown in Table 4 also shows the results of a tamping test for determining the optimum water content and the optimum amount of additive.

【表4】 (注2)ここで、アスファルト乳剤量が0%であるとい
うことは、粒状材料、アスファルト再生骨材および一般
再生砕石に対し、さらに添加するアスファルト乳剤量が
0%であることを意味する。実施例2は、実施例1に比
し、焼却灰に加えるアスファルト乳剤量を5分の1に減
らし、減った分だけ水の量を多くして、各材料の合計量
を変えないようにしたものであるが、表4から判るよう
に粒状材料5%混入、10%混入のいずれの場合も一軸
圧縮強さ、残留強度率は、再生セメント瀝青安定処理の
基準値を満足し、たわみ性と剛性を有し、上層路盤とし
て使用可能である。実施例1と同様にセメント添加量も
2%程度となり、経済的な再生セメント瀝青安定処理混
合物の製造が可能である。実施例1の場合と同様に、焼
却灰に含まれる有害成分等はアスファルト乳剤に被覆さ
れ、溶出しにくいので、再生セメント瀝青安定処理混合
物が環境に及ぼす影響は少ないと考えられる。粒状材料
は溶出試験までそのまま保管できるので、便利である。
なお、粒状材料の製造時に使用するアスファルト乳剤
は、実施例1の場合に比し少ないが、最適添加セメント
量は若干増加させることが必要である。表5は焼却灰の
ふるい分け試験(JISA1102)の結果を示す。図
2は上記粒状材料の粒度曲線図を示す。
[Table 4] (Note 2) Here, the fact that the amount of asphalt emulsion is 0% means that the amount of asphalt emulsion further added to the granular material, asphalt regenerated aggregate and general reclaimed crushed stone is 0%. In Example 2, as compared with Example 1, the amount of asphalt emulsion added to the incineration ash was reduced to one fifth, and the amount of water was increased by the reduced amount so that the total amount of each material was not changed. As can be seen from Table 4, the unconfined compressive strength and residual strength ratio satisfy the standard values of the stabilized cement bitumen stabilization treatment in both cases of 5% and 10% of the granular material. It has rigidity and can be used as an upper roadbed. As in the case of Example 1, the amount of cement added is also about 2%, and an economical production of a recycled cement bitumen stabilizing mixture is possible. As in the case of Example 1, the harmful components and the like contained in the incineration ash are coated on the asphalt emulsion and are hardly eluted. Therefore, it is considered that the stabilized cement bitumen mixture has little effect on the environment. The granular material is convenient because it can be stored as it is until the dissolution test.
The asphalt emulsion used in the production of the granular material is smaller than that in Example 1, but it is necessary to slightly increase the optimum amount of added cement. Table 5 shows the results of the incineration ash sieving test (JISA1102). FIG. 2 shows a particle size curve diagram of the granular material.

【表5】 [Table 5]

【0008】[実施例3]粒状材料として焼却灰とアス
ファルト乳剤との合計量に対するアスファルト乳剤の重
量比を5〜50%とし、かつ粒状材料とアスファルト再
生骨材と路盤再生骨材との合計量に対する重量比は、粒
状材料が30%、アスファルト再生骨材が30%、路盤
再生骨材が40%とし、さらにこれらの合計量に対し重
量比で1.5〜6%のセメントを加えた再生セメント瀝
青安定処理混合物についても、一軸圧縮強さ、残留強度
率いずれも基準値を満足し、上層路盤として使用可能で
ある。但し、粒状材料製造時に加えるアスファルト乳剤
の量は、多い程有害成分の溶出防止上好ましいが、50
%を越えるようになると焼却灰が団子状に固まり、摺り
潰し(破砕)困難になるので、50%以下とすることが
望ましい。
Example 3 The weight ratio of the asphalt emulsion to the total amount of the incinerated ash and the asphalt emulsion as the granular material is 5 to 50%, and the total amount of the granular material, the asphalt recycled aggregate and the roadbed recycled aggregate The weight ratio is as follows: 30% of granular material, 30% of asphalt recycled aggregate, and 40% of recycled roadbed aggregate, and furthermore, 1.5 to 6% by weight of recycled cement based on the total amount of these materials. The cement bitumen-stabilized mixture also satisfies the standard values for both the unconfined compressive strength and residual strength, and can be used as an upper subgrade. However, the larger the amount of asphalt emulsion added during the production of the granular material, the more preferable it is for preventing elution of harmful components.
%, The incinerated ash solidifies in a dumpling shape, making it difficult to crush (crush).

【0009】本発明に使用する焼却灰は、有害成分が廃
棄物処理関連の法律により許容された範囲内であること
が望ましい。前記各実施例において、粒状材料は製造時
に焼却灰、アスファルト乳剤の他にさらに1〜5%程度
の石灰もしくはセメントを混合する場合もある。以上本
発明のいくつかの実施例について説明したが、本発明は
このような実施例に何等限定されるものではなく、本発
明の要旨を逸脱しない範囲において種々なる態様で実施
し得ることはもちろんである。
The incinerated ash used in the present invention preferably has a harmful component within a range permitted by laws relating to waste disposal. In each of the above embodiments, about 1 to 5% of lime or cement may be mixed with the granular material in addition to incineration ash and asphalt emulsion during production. Although some embodiments of the present invention have been described above, the present invention is not limited to such embodiments at all, and it is needless to say that the present invention can be implemented in various modes without departing from the gist of the present invention. It is.

【0010】[0010]

【発明の効果】本発明は上述の通り構成されているの
で、次に記載する効果を奏する。請求項1〜請求項6記
載の上層路盤の施工方法および上層路盤材料によれば、
従来捨て場に困っていた焼却灰の大量処分を図り得ると
共に、焼却灰はアスファルト乳剤で被覆されているの
で、有害成分の溶出を防止することができ、さらに産業
廃棄物たるアスファルト廃材の有効活用を図ることがで
きる。また、焼却灰をアスファルト乳剤等で固めた前記
粒状材料は、その状態で保管できるので、有害成分の溶
出試験の結果がでるまで保管したり、中央プラントまで
運搬することができ好都合である。請求項5〜請求項6
記載の上層路盤の施工方法および上層路盤材料によれ
ば、粒状材料の製造時に石灰やセメントを混合するの
で、上層路盤に占める焼却灰の割合が大きい場合には、
一軸圧縮強さが低下する傾向になるのを改善することが
できる。
Since the present invention is configured as described above, the following effects can be obtained. According to the method of constructing the upper roadbed and the upper roadbed material according to claims 1 to 6,
A large amount of incineration ash, which had previously been difficult to dispose of, can be disposed of in large quantities, and since the incineration ash is covered with asphalt emulsion, elution of harmful components can be prevented, and asphalt waste material, which is industrial waste, can be effectively used. Can be achieved. Further, the granular material obtained by solidifying the incinerated ash with an asphalt emulsion or the like can be stored in that state, so that it can be conveniently stored until a result of a harmful component elution test is obtained or transported to a central plant. Claims 5 and 6
According to the upper roadbed construction method and upper roadbed material described, lime and cement are mixed at the time of the production of granular material, so when the proportion of incinerated ash in the upper roadbed is large,
The tendency of the uniaxial compressive strength to decrease can be improved.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の実施例に使用する焼却灰の粒度曲線図
である。
FIG. 1 is a particle size curve diagram of incinerated ash used in Examples of the present invention.

【図2】本発明の他の実施例に使用する焼却灰の粒度曲
線図である。
FIG. 2 is a particle size curve diagram of incineration ash used in another embodiment of the present invention.

Claims (6)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 一般廃棄物の焼却灰とアスファルト乳剤
と適当な水とを少なくとも混合し、乾燥後破砕した粒径
5mm程度以下の粒状材料と、粒径が40mm以下のア
スファルト廃材の破砕物と、一般再生砕石と、セメント
と、セメントが飛散しない程度の水とを、所定場所に固
設した混合用のプラントを使用する中央プラント方式で
混合してから、該混合物を施工個所に運搬し、施工する
ようにした焼却灰を混用した上層路盤の施工方法。
An incinerated ash of general waste, an asphalt emulsion, and at least an appropriate water are mixed, dried and crushed to obtain a granular material having a particle diameter of about 5 mm or less, and a crushed asphalt waste material having a particle diameter of 40 mm or less. , General recycled crushed stone, cement, and water to the extent that the cement does not scatter, after mixing in a central plant method using a mixing plant fixed in place, transport the mixture to the construction site, Construction method of upper subgrade using mixed incineration ash.
【請求項2】 請求項1記載の上層路盤の施工方法にお
いて、前記粒状材料と、前記アスファルト廃材の破砕物
と、前記一般再生砕石との合計量に対する重量比は前記
粒状材料が5〜30%、前記アスファルト廃材の破砕物
が30〜70%、前記一般再生砕石が20〜40%であ
り、かつ前記アスファルト乳剤は焼却灰とアスファルト
乳剤との合計量に対する重量比が5〜50%である焼却
灰を混用した上層路盤の施工方法。
2. The method according to claim 1, wherein the weight ratio of the granular material to the total amount of the crushed asphalt waste material and the general recycled crushed stone is 5 to 30%. The incineration wherein the asphalt waste material crushed material is 30 to 70%, the general recycled crushed stone is 20 to 40%, and the asphalt emulsion has a weight ratio of 5 to 50% to the total amount of incinerated ash and asphalt emulsion. Construction method of upper subgrade using ash.
【請求項3】 一般廃棄物の焼却灰とアスファルト乳剤
と適当な水とを少なくとも混合し、乾燥後破砕した粒径
5mm程度以下の粒状材料と、粒径が40mm以下のア
スファルト廃材の破砕物と、一般再生砕石と、セメント
と、セメントが飛散しない程度の水とを少なくとも含
み、かつこれらを所定場所に固設した混合用のプラント
を使用する中央プラント方式で混合してなる上層路盤材
料。
3. A granular material having a particle size of about 5 mm or less, which is obtained by mixing at least incineration ash of general waste, asphalt emulsion, and appropriate water, drying and crushing the same, and a crushed asphalt waste material having a particle size of 40 mm or less. An upper roadbed material comprising at least a general recycled crushed stone, cement, and water to such an extent that the cement is not scattered, and mixing them by a central plant method using a mixing plant fixed at a predetermined place.
【請求項4】 請求項3記載の上層路盤材料において、
前記粒状材料と、前記アスファルト廃材の破砕物と、前
記一般再生砕石との合計量に対する重量比は前記粒状材
料が5〜30%、前記アスファルト廃材の破砕物が30
〜70%、前記一般再生砕石が20〜40%であり、か
つ前記アスファルト乳剤は焼却灰とアスファルト乳剤と
の合計量に対する重量比が5〜50%である上層路盤材
料。
4. The upper subbase material according to claim 3, wherein
The weight ratio of the granular material, the crushed asphalt waste material, and the general recycled crushed stone to the total amount is 5 to 30% for the granular material, and 30 for the crushed asphalt waste material.
An upper roadbed material in which the weight ratio of the asphalt emulsion to the total amount of the incinerated ash and the asphalt emulsion is 5 to 50%, and the general recycled crushed stone is 20 to 40%.
【請求項5】 請求項1もしくは請求項2記載の上層路
盤の施工方法において、前記粒状材料には、その製造時
に焼却灰とアスファルト乳剤と水の他にさらに少量のセ
メント及び/又は石灰を加え混合するようにした焼却灰
を混用した上層路盤の施工方法。
5. The method according to claim 1, wherein a small amount of cement and / or lime is added to the granular material in addition to incinerated ash, asphalt emulsion and water during the production. Construction method of upper subgrade using mixed incineration ash.
【請求項6】 請求項3もしくは請求項4記載の上層路
盤材料において、前記粒状材料には、その製造時に焼却
灰とアスファルト乳剤と水の他にさらに少量のセメント
及び/又は石灰を加え混合するようにした上層路盤材
料。
6. The upper roadbed material according to claim 3, wherein said granular material is mixed with a small amount of cement and / or lime in addition to incineration ash, asphalt emulsion and water during its production. Upper subbase material.
JP9212502A 1997-07-22 1997-07-22 Construction method and material of upper subbase with mixed incineration ash Expired - Fee Related JP3044611B2 (en)

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JP3044611B2 true JP3044611B2 (en) 2000-05-22

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