JP2005154574A - Effectual utilization method of waste frp - Google Patents

Effectual utilization method of waste frp Download PDF

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JP2005154574A
JP2005154574A JP2003395160A JP2003395160A JP2005154574A JP 2005154574 A JP2005154574 A JP 2005154574A JP 2003395160 A JP2003395160 A JP 2003395160A JP 2003395160 A JP2003395160 A JP 2003395160A JP 2005154574 A JP2005154574 A JP 2005154574A
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asphalt mixture
asphalt
waste
frp
waste frp
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JP3981663B2 (en
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Hiroshi Yamagishi
宏 山岸
Tadanori Kozumi
忠教 小住
Yoshitomo Mizuno
喜友 水野
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Nippo Corp Inc
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Nippo Corp Inc
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

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Abstract

<P>PROBLEM TO BE SOLVED: To provide, in utilizing a waste FRP (fiber reinforced plastics) as a component of an asphalt mixture used for constructing a pavement like a driveway and the like, an asphalt mixture which is friendly to workers and the environment and also excellent economically. <P>SOLUTION: In the asphalt mixture consisting of aggregate, a filler and an asphalt-based binder, a crushed product of the waste FRP, obtained by crushing the waste FRP, is used as part of the aggregate, and a mixing temperature lowering agent, such as an inorganic compound containing crystallization water, is added. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は廃FRP(繊維強化プラスチック)の有効利用方法に関し、特に船体に用いられていたFRPの有効利用方法に関する。   The present invention relates to an effective utilization method of waste FRP (fiber reinforced plastic), and more particularly to an effective utilization method of FRP used in a hull.

FRPを構造材として用いたFRP漁船は、軽量かつ丈夫であることから昭和40年代以降木船に替わって急速に普及したが、近年船体の老朽化による廃船が増加しており、これに伴いFRP漁船の廃船処理が問題となっている。   FRP fishing boats using FRP as a structural material have been rapidly spread instead of wooden boats since the Showa 40s because they are light and strong, but in recent years the number of abandoned boats due to aging of the hulls has increased, and accordingly FRP Disposal of fishing boats is a problem.

従来、船体を構成する部材としてFRPを含む廃船(以下、「FRP廃船」という。)の処理は、以下の方法で行われてきた。
(1)FRP廃船を曳航してドックへ引き上げ、艤装解除および油抜き処理を行う。
(2)重機を用いて船体の大ばらしを行い、廃材を中間処理施設へ搬出する。
(3)廃材のうち木材は焼却により処理し、焼却灰を最終処理施設へ搬出する。
(4)廃材のうちFRPは破砕機を用いて15cm以下に破砕して廃FRP破砕物とし、該廃FRP破砕物を最終処理施設へ搬出する。
(5)焼却灰およびFRP破砕物は、最終処理施設において埋め立て処分する。また、焼却灰はセメントの原料として利用される場合がある。
Conventionally, disposal of a waste ship including FRP as a member constituting a hull (hereinafter referred to as “FRP waste ship”) has been performed by the following method.
(1) Tow the FRP scrap ship and pull it up to the dock to release the outfitting and drain the oil.
(2) The hull is expanded using heavy machinery, and the waste material is carried out to an intermediate treatment facility.
(3) Of the waste material, wood is treated by incineration, and the incineration ash is transported to the final treatment facility.
(4) Among the waste materials, the FRP is crushed to 15 cm or less using a crusher to obtain a waste FRP crushed material, and the waste FRP crushed material is transported to a final treatment facility.
(5) Incinerated ash and FRP crushed material are disposed of in landfills at the final treatment facility. Incineration ash may be used as a raw material for cement.

しかし、従来実施されていたFRP廃船の処理方法では最終的に廃FRP破砕物を埋め立て処分していたため、処理に多大な費用を要するという問題があった。また、近年FRP廃船から発生した廃FRPを破砕して得られる廃FRP破砕物をアスファルト混合物の一成分として利用する技術も提案されている(特許文献1)。   However, there has been a problem in that the processing method for the FRP waste ship that has been practiced in the past has caused waste FRP crushed material to be disposed of in landfills, requiring a large amount of processing costs. In recent years, a technique has also been proposed in which waste FRP crushed material obtained by crushing waste FRP generated from an FRP waste ship is used as one component of an asphalt mixture (Patent Document 1).

しかし、従来知られた一般的な方法でアスファルト混合物を製造した場合には、廃FRP破砕物中のポリエステル樹脂等の有機物質由来の悪臭発生等による作業者や周辺環境への悪影響を防ぎ得ないという問題点を有する。
特開2002−105322号公報
However, when an asphalt mixture is produced by a conventionally known general method, it is impossible to prevent adverse effects on workers and the surrounding environment due to generation of malodor derived from organic substances such as polyester resin in waste FRP crushed material. Has the problem.
JP 2002-105322 A

本発明の目的は、上記した従来技術の問題点を解決することにある。特に本発明の目的は、廃FRPを車道等の舗装体の構築に用いるアスファルト混合物の一成分として利用するに際し、作業者や環境にやさしく、経済性にも優れたアスファルト混合物を提供することにある。   An object of the present invention is to solve the problems of the prior art described above. In particular, an object of the present invention is to provide an asphalt mixture which is friendly to workers and the environment and is excellent in economic efficiency when using waste FRP as a component of an asphalt mixture used for construction of pavements such as roadways. .

本発明は、第1に、骨材と、フィラーと、アスファルト系バインダと、からなるアスファルト混合物において、骨材の一部として廃FRPを破砕して得られる廃FRP破砕物を用いると共に、アスファルト混合物が加熱アスファルト混合物であり且つ該混合物中に混合温度低下剤を含有させたことを特徴とするアスファルト混合物である。   The present invention firstly uses a waste FRP crushed material obtained by crushing waste FRP as a part of aggregate in an asphalt mixture comprising an aggregate, a filler, and an asphalt binder, and an asphalt mixture. Is an asphalt mixture characterized by being a heated asphalt mixture and containing a mixing temperature reducing agent in the mixture.

本発明は、第2に、廃FRP破砕物の粒径が6mm以下であることを特徴とする上記のアスファルト混合物である。   A second aspect of the present invention is the asphalt mixture described above, wherein the particle size of the waste FRP crushed material is 6 mm or less.

本発明は、第3に、廃FRP破砕物が、船体を構成する部材としてFRPを含む廃船から採取したFRPを破砕して得られることを特徴とする上記のアスファルト混合物である。   Thirdly, the present invention is the above asphalt mixture characterized in that the waste FRP crushed material is obtained by crushing FRP collected from a waste ship containing FRP as a member constituting the hull.

本発明は、第4に、廃FRP破砕物の含有量が、アスファルト混合物全体に占める体積比で1〜20%であることを特徴とする上記のアスファルト混合物である。   Fourthly, the present invention is the asphalt mixture described above, wherein the content of the waste FRP crushed material is 1 to 20% in a volume ratio to the entire asphalt mixture.

本発明は、第5に、混合温度低下剤が中温化材である上記のアスファルト混合物である。   5thly this invention is said asphalt mixture whose mixing temperature reducing agent is a medium temperature raising material.

本発明は、第6に、中温化剤が結晶水含有無機物質からなる上記のアスファルト混合物である。   Sixthly, the present invention is the above asphalt mixture in which the temperature-warming agent is made of a crystal water-containing inorganic substance.

本発明は、第7に、骨材と、フィラーと、アスファルト系バインダと、からなるアスファルト混合物において、骨材の一部として廃FRPを破砕して得られる廃FRP破砕物を用いると共に、アスファルト混合物が常温アスファルト混合物であることを特徴とするアスファルト混合物である。   Seventh, the present invention uses a waste FRP crushed material obtained by crushing waste FRP as a part of aggregate in an asphalt mixture comprising an aggregate, a filler, and an asphalt binder, and an asphalt mixture. Is an asphalt mixture characterized by being a normal temperature asphalt mixture.

本発明によれば、廃FRP、特にFRP廃船から発生する廃FRPの処理に要する費用を低減し、省資源に資することができると共に、作業者や環境にやさしく、優れた特性を有する舗装体を構築することが可能となる。   According to the present invention, it is possible to reduce the cost required for processing waste FRP, particularly waste FRP generated from an FRP waste ship, to contribute to resource saving, and to the workers and the environment, and a pavement having excellent characteristics. Can be built.

本発明の実施の形態を以下に説明する。
本発明のアスファルト混合物は、骨材と、フィラーと、アスファルト系バインダと、からなるアスファルト混合物において、骨材の一部として、第一に、廃FRPを破砕して得られる廃FRP破砕物を用いることを特徴とする。本発明で用いることができる骨材としては、砕石、玉砕、鉄鋼スラグ、砂、再生骨材などをあげることができる。本発明で用いることができるフィラーとしては、石粉、消石灰、セメント、回収ダスト、フライアッシュなどをあげることができる。これらのフィラーは、その目的に応じて適宜用いることができる。本発明で用いることができるアスファルト系バインダとしては、舗装用石油アスファルト、改質アスファルト、トリニダッドレイクアスファルト(天然アスファルト)、石油アスファルト乳剤などがある。これらの骨材、フィラーおよびアスファルト系バインダの添加量はアスファルト混合物の種類により異なり、マーシャル安定度試験における各性状値の共通範囲から求められるが、例えば「舗装施工便覧」((社)日本道路協会、平成13年12月発行)に記載される配合を用いることができる。
Embodiments of the present invention will be described below.
The asphalt mixture of the present invention uses a waste FRP crushed material obtained by crushing waste FRP as a part of the aggregate in an asphalt mixture comprising an aggregate, a filler, and an asphalt binder. It is characterized by that. Aggregates that can be used in the present invention include crushed stones, crushing stones, steel slag, sand, recycled aggregates and the like. Examples of the filler that can be used in the present invention include stone powder, slaked lime, cement, recovered dust, and fly ash. These fillers can be appropriately used depending on the purpose. Examples of the asphalt binder that can be used in the present invention include paving petroleum asphalt, modified asphalt, trinidad lake asphalt (natural asphalt), and petroleum asphalt emulsion. The amount of these aggregates, fillers and asphalt binders varies depending on the type of asphalt mixture, and is determined from the common range of property values in the Marshall stability test. For example, “Pavement Construction Handbook” , Published in December 2001).

本発明で用いられる廃FRP破砕物の粒径は6mm以下であることが好ましい。廃FRP破砕物の粒径が6mm以上であると、加熱により廃FRP破砕物が変形することによるアスファルト混合物層の耐久性への影響が大きくなってしまうという問題がある。   The particle size of the waste FRP crushed material used in the present invention is preferably 6 mm or less. When the particle size of the waste FRP crushed material is 6 mm or more, there is a problem that the influence on the durability of the asphalt mixture layer due to the deformation of the waste FRP crushed material by heating becomes large.

本発明で用いられる廃FRP破砕物は、FRP廃船から採取した廃FRPを破砕して得られるものが好ましい。ここで、FRP廃船とは構造材としてFRPを用いている船舶であれば、特に限定はされない。   The waste FRP crushed material used in the present invention is preferably obtained by crushing waste FRP collected from an FRP waste ship. Here, the FRP waste ship is not particularly limited as long as it is a ship using FRP as a structural material.

本発明で用いられる廃FRP破砕物の含有量は、アスファルト混合物全体に占める体積比で1〜20%であることが好ましい。廃FRP破砕物の含有量が1%以下では、廃FRP破砕物の使用量が少なすぎて、FRP廃船の処理費用を低減するという目的を達成することができない。廃FRP破砕物の含有量が20%以上では、廃FRPを利用したアスファルト混合物が所定の締固め度を得るために必要なアスファルト量が多くなり、アスファルト混合物の製造費用が高くなってしまう。   The content of the waste FRP crushed material used in the present invention is preferably 1 to 20% in volume ratio to the entire asphalt mixture. If the content of waste FRP crushed material is 1% or less, the amount of waste FRP crushed material used is too small to achieve the purpose of reducing the processing cost of FRP waste ships. When the content of the waste FRP crushed material is 20% or more, the amount of asphalt necessary for the asphalt mixture using the waste FRP to obtain a predetermined degree of compaction increases, and the production cost of the asphalt mixture increases.

本発明のアスファルト混合物は、上記成分に加えさらに混合温度低下剤を加えることを特徴とする。   The asphalt mixture of the present invention is characterized by further adding a mixing temperature lowering agent in addition to the above components.

アスファルト混合物は、通常予め加熱した骨材とフィラーとの混合物をミキサ内に投入し、これに加熱したアスファルト系バインダを加えて混合して製造される。本発明では、廃FRP破砕物を加熱混合時に直接ミキサへ投入してもよいし、予め他の骨材と混合しておいてもよい。その際、製造時の適切な混合性と舗設時の適切な締固め性を確保するためにアスファルト系バインダは必然的にかなりの高温となる。本発明者等の検討の結果、その際の加熱状態のアスファルト系バインダと廃FRP破砕物との相互作用により異様な臭気を発生し、作業者及び周辺環境に悪影響を与えることを知見した。そして、アスファルト混合物を製造するために必要なアスファルト系バインダの粘度を事実上維持しつつその加熱に必要な温度を低下させることにより、上記の相互作用に伴う悪臭発生が顕著に抑制され、作業者及び環境にやさしく、しかも品質にも優れた舗装体を舗設できることを見出した。   The asphalt mixture is usually produced by putting a preheated aggregate and filler mixture into a mixer and adding a heated asphalt binder to the mixer. In the present invention, the waste FRP crushed material may be directly charged into the mixer during heating and mixing, or may be mixed with other aggregates in advance. At that time, the asphalt-based binder is inevitably at a considerably high temperature in order to ensure proper mixing during production and proper compaction during paving. As a result of the study by the present inventors, it has been found that an abnormal odor is generated due to the interaction between the heated asphalt binder and the waste FRP crushed material, which adversely affects the worker and the surrounding environment. And by reducing the temperature required for the heating while effectively maintaining the viscosity of the asphalt binder necessary for producing the asphalt mixture, the generation of malodor associated with the above interaction is remarkably suppressed, and the operator It was also found that a paving body that is environmentally friendly and excellent in quality can be paved.

本発明に用いる混合温度低下剤は、アスファルト系バインダの粘度がアスファルト混合物の混合および/または締固めに適する粘度となる温度を、それが存在しない場合に比し相対的に低下させうる物質である。その典型例は、アスファルト混合物の加熱混合ないし締固め時に該混合物の熱によって微小気泡粒子を発生させる微小気泡粒子発生物質を典型例とする中温化剤である。このような微小気泡粒子発生物質の典型例としては結晶水を含有する無機物質や吸水性を有する物質の微粉末がある。   The mixing temperature reducing agent used in the present invention is a substance that can relatively lower the temperature at which the viscosity of the asphalt binder becomes a viscosity suitable for mixing and / or compacting the asphalt mixture as compared with the case where it does not exist. . A typical example is a warming agent, typically a microbubble particle generating material that generates microbubble particles by the heat of the mixture during heat mixing or compaction of an asphalt mixture. Typical examples of such a microbubble particle generating material include an inorganic material containing crystal water and a fine powder of a material having water absorption.

結晶水を含む無機物質や吸水性を有する物質には、例えば、二水石膏や半水石膏、硫酸アンモニウムアルミニウム水和物、塩化コバルト水和物、酢酸コバルト水和物、硫酸クロム水和物、硫酸銅水和物、塩化鉄水和物、硫酸鉄水和物、炭酸マグネシウム水和物、塩化マンガン水和物、酢酸マンガン水和物、亜硫酸ナトリウム水和物(亜硫酸ソーダ)、リン酸ソーダ、タングステン酸ナトリウム水和物、硫酸ニッケル水和物、ゼオライト、高吸水性樹脂などがあげられる。高吸水性樹脂とは、水を高度に吸収するが水に溶解しない樹脂であり、架橋ポリアクリル酸ソーダ、酢酸ビニル−アクリル酸メチル共重合体ケン化物、酢酸ビニル−マレイン酸モノメチル共重合体ケン化物、イソブチレン−無水マレイン酸共重合体ケン化物、デンプン−アクリル酸グラフト重合体、多糖類−アクリル酸グラフト重合体、デンプン−アクリルニトリルグラフト重合体、カルボキシメチルセルロース−ナトリウム塩、架橋ポリエチレンオキサイドなどが利用できる。これらの高吸水性樹脂は通常水を吸収した微粉末状で用いられる。   Examples of inorganic substances including crystal water and water-absorbing substances include dihydrate gypsum and hemihydrate gypsum, ammonium aluminum sulfate hydrate, cobalt chloride hydrate, cobalt acetate hydrate, chromium sulfate hydrate, sulfuric acid Copper hydrate, iron chloride hydrate, iron sulfate hydrate, magnesium carbonate hydrate, manganese chloride hydrate, manganese acetate hydrate, sodium sulfite hydrate (sodium sulfite), sodium phosphate, tungsten Examples thereof include sodium acid hydrate, nickel sulfate hydrate, zeolite, and a superabsorbent resin. Superabsorbent resin is a resin that absorbs water highly but does not dissolve in water. Cross-linked sodium polyacrylate, saponified vinyl acetate-methyl acrylate copolymer, vinyl acetate-monomethyl maleate copolymer ken Saponified products, saponified products of isobutylene-maleic anhydride copolymer, starch-acrylic acid graft polymer, polysaccharide-acrylic acid graft polymer, starch-acrylonitrile graft polymer, carboxymethylcellulose-sodium salt, crosslinked polyethylene oxide, etc. it can. These superabsorbent resins are usually used in the form of fine powder that has absorbed water.

これらの物質の中でも、アスファルト系バインダが軟化ないし溶融する加熱条件になるまでは微小気泡粒子が発生せず、上記条件下で微小気泡粒子を発生する物質を用いることが望ましく、例えば、二水石膏といった90℃〜160℃の温度で微小気泡粒子を安定的に発生かつ保持する物質を選択することがより望ましい。   Among these substances, it is desirable to use a substance that does not generate microbubble particles until a heating condition in which the asphalt binder is softened or melted, and generates microbubble particles under the above conditions. For example, dihydrate gypsum It is more desirable to select a substance that stably generates and retains microbubble particles at a temperature of 90 ° C. to 160 ° C.

これらの微小気泡粒子発生物質は界面活性剤の共有下により効果的に用いられる。界面活性剤としては、カチオン系界面活性剤である第1級、第2級、第3級アルキルアミン塩や第4級アンモニウム塩、アニオン系界面活性剤であるカルボン酸塩や硫酸エステル塩やスルホン酸塩、非イオン系のポリエチレングリコール型や多価アルコール型などがあげられる。界面活性剤においては、剥離防止剤としても使用されるカチオン系活性剤を用いれば、バインダと骨材との付着性は従来の舗装用混合物よりも向上し、舗装体としての耐久性が改善される。   These microbubble particle generating substances are more effectively used under the sharing of a surfactant. Surfactants include cationic surfactants such as primary, secondary, and tertiary alkylamine salts and quaternary ammonium salts, and anionic surfactants such as carboxylates, sulfates, and sulfones. Acid salts, nonionic polyethylene glycol type and polyhydric alcohol type. In surfactants, the use of cationic surfactants that are also used as anti-peeling agents improves the adhesion between binders and aggregates compared to conventional pavement mixtures, improving the durability of pavements. The

微小気泡粒子を発生する物質、例えば結晶水を持つ物質の使用量は通常バインダ量に対する重量比で1〜30%、界面活性剤の使用量は通常バインダ量に対する重量比で0.1〜3%である。これらを少量の遊離水と共にあらかじめ混練したペースト状物が特に好ましい。その際の遊離水の量はペースト状物を形成しうる量が望ましく、通常結晶水を持つ物質と界面活性剤の合計量に対する重量比で10〜100%、特に20〜70%が好ましい。   The amount of a substance that generates microbubble particles, for example, a substance having water of crystallization is usually 1 to 30% by weight with respect to the amount of binder, and the amount of surfactant to be used is usually 0.1 to 3% by weight with respect to the amount of binder. It is. A pasty product obtained by kneading these together with a small amount of free water is particularly preferable. The amount of free water at that time is preferably an amount capable of forming a paste-like substance, and is usually 10 to 100%, particularly preferably 20 to 70% in terms of a weight ratio to the total amount of the substance having crystal water and the surfactant.

本発明では、常温アスファルト混合物の一成分として廃FRP破砕物を用いることも可能である。本発明で用いられる常温アスファルト混合物としては、カットバックアスファルトで骨材を被覆した後さらに油脂で被覆した混合物、骨材にストレートアスファルトを噴霧した後さらに熱可塑性エラストマーを添加した混合物、カットバックアスファルトに熱可塑性樹脂を添加したバインダで骨材を被覆した混合物などを用いることができる。これらの常温アスファルト混合物の場合は、混合温度低下剤を併用する必要はない。   In the present invention, waste FRP crushed material can also be used as one component of the room temperature asphalt mixture. As the normal temperature asphalt mixture used in the present invention, the aggregate coated with cut back asphalt and further coated with oil and fat, the mixture further sprayed with straight asphalt on the aggregate and further added with the thermoplastic elastomer, the cut back asphalt A mixture in which an aggregate is coated with a binder to which a thermoplastic resin is added can be used. In the case of these room temperature asphalt mixtures, it is not necessary to use a mixing temperature reducing agent in combination.

本発明のアスファルト混合物は、骨材と、フィラーと、加熱型アスファルト系バインダと、船体を構成する部材としてFRPを含む廃船から採取した廃FRPを破砕して得られる廃FRP破砕物と、混合温度低下剤と、を混合して製造される。用いられる材料の最適配合量は、アスファルト混合物の種類によって異なり、その都度配合試験により求められる。材料の混合方法は特に限定されないが、通常はアスファルトプラントにおいてミキサを用いて混合される。その際、加熱型アスファルト系バインダはスプレーを用いてミキサ内に添加することが望ましい。廃FRP破砕物は、あらかじめ骨材の一部として混合して用いてもよいし、骨材、フィラーおよびアスファルト系バインダを混合した後、これらに添加して用いてもよい。混合温度低下剤も適宜の段階で添加しうる。   The asphalt mixture of the present invention is mixed with aggregate, filler, heated asphalt binder, waste FRP crushed material obtained by crushing waste FRP collected from a waste ship containing FRP as a member constituting the hull, It is manufactured by mixing with a temperature lowering agent. The optimum blending amount of the material used varies depending on the type of asphalt mixture, and is determined by a blending test each time. The mixing method of the material is not particularly limited, but is usually mixed using a mixer in an asphalt plant. At that time, it is desirable to add the heated asphalt binder into the mixer using a spray. The waste FRP crushed material may be used as a part of the aggregate in advance, or may be used after being added to the aggregate, filler and asphalt binder. A mixing temperature lowering agent may be added at an appropriate stage.

本発明による効果を確認するために、以下の試験を行った。
試験1:
廃船から採取した廃FRPを破砕機で破砕して製造した廃FRP破砕物について、その性状を確認するために次の試験を行った。
(a)ふるい分け試験
試験方法はJIS A 1102「骨材のふるい分け試験方法」による。試験結果を表1に示す。
In order to confirm the effect of the present invention, the following tests were conducted.
Test 1:
In order to confirm the properties of the waste FRP crushed material produced by crushing the waste FRP collected from the abandoned ship with a crusher, the following test was conducted.
(A) Screening test The test method is in accordance with JIS A 1102 "Aggregate screening test method". The test results are shown in Table 1.

Figure 2005154574
Figure 2005154574

(b)比重および吸水率試験
試験方法はJIS A 1109「細骨材の比重及び吸水率試験方法」による。試験結果を表2に示す。
(B) Specific gravity and water absorption rate test The test method is in accordance with JIS A 1109 “Test method for specific gravity and water absorption rate of fine aggregate”. The test results are shown in Table 2.

Figure 2005154574
Figure 2005154574

(c)単位体積質量試験および実績率試験
試験方法はJIS A 1104「骨材の単位容積質量及び実積率試験方法」による。試験結果を表3に示す。
(C) Unit Volume Mass Test and Actual Rate Test The test method is based on JIS A 1104 “Aggregate Unit Volume Mass and Actual Volume Ratio Test Method”. The test results are shown in Table 3.

Figure 2005154574
Figure 2005154574

(2)室内配合試験
試験2および試験3で用いるアスファルト混合物の配合試験を行った。試験は、密粒度アスファルト混合物(骨材最大粒径13mm、マーシャル安定度試験用供試体の突き固め回数50回)、砕石マスチック混合物(骨材最大粒径13mm、マーシャル安定度試験用供試体の突き固め回数50回)を母体として行い、廃FRP破砕物の混入率をアスファルト混合物全体に占める体積比でそれぞれ0%、5%、10%と変化させてマーシャル安定度試験用供試体を作成した。密粒度アスファルト混合物については「舗装設計施工指針」((社)日本道路協会、平成13年12月発行)に記載される粒度範囲の中央値を、砕石マスチック混合物については社内規格に示す粒度範囲の中央値をそれぞれ目標値として骨材配合比を求め、さらに比重補正を行って最終的な骨材配合比を決定した。引き続き各供試体についてマーシャル安定度試験を行い、基準値を満足する共通範囲の中央値を最適アスファルト量とした。試験結果を表4に示す。
(2) Indoor blending test The blending test of the asphalt mixture used in Test 2 and Test 3 was performed. The test consists of a dense asphalt mixture (aggregate maximum particle size 13 mm, Marshall stability test specimen tamped 50 times), crushed mastic mixture (aggregate maximum particle diameter 13 mm, Marshall stability test specimen thrust The number of times of solidification was 50), and the mixing ratio of waste FRP crushed material was changed to 0%, 5%, and 10%, respectively, in the volume ratio of the entire asphalt mixture, and specimens for Marshall stability test were prepared. For the fine-grained asphalt mixture, the median particle size range described in the “Pavement Design and Construction Guidelines” (issued by the Japan Road Association, December 2001) is used. Aggregate blending ratios were calculated using the median as target values, and the final aggregate blending ratio was determined by further correcting the specific gravity. Subsequently, a Marshall stability test was performed on each specimen, and the median value in a common range that satisfies the reference value was determined as the optimum amount of asphalt. The test results are shown in Table 4.

Figure 2005154574
Figure 2005154574

表4に示す試験結果より、廃FRP破砕物の混入率を体積比で5%、10%とした場合でも、いずれもアスファルト混合物としての規定値を全て満足しており、特に問題はないといえる。   From the test results shown in Table 4, even when the mixing ratio of the waste FRP crushed material is 5% and 10% by volume, all satisfy the specified values as the asphalt mixture, and it can be said that there is no particular problem. .

試験2:臭気確認試験
アスファルト混合物は、通常160±10℃程度に加熱された状態でミキサから排出される。廃FRP破砕物をミキサへ直接投入すると、ドライヤで加熱された骨材(180〜200℃程度)と接触することにより熱交換を受けて高温となり、これが原因となって臭気を発生するものと思われる。そこで、FRPから発生する臭気対策について以下に示す試験を行った。
Test 2: Odor confirmation test The asphalt mixture is usually discharged from the mixer while being heated to about 160 ± 10 ° C. When waste FRP crushed material is directly put into the mixer, it will heat up due to contact with the aggregate (about 180-200 ° C) heated by the dryer, and this will cause odors. It is. Then, the test shown below was done about the countermeasure against the odor generated from FRP.

(1)臭気確認試験
(a)混合物の臭気確認
最大粒径6mm以下に破砕した廃船から得られた廃FRP破砕物をアスファルト混合物全体に占める体積比で10%混入した密粒度アスファルト混合物(骨材最大粒径13mm)を2kg準備し、中華鍋に入れて混合しながらガスコンロで徐々に加熱し、臭気の程度を確認した。
(1) Odor confirmation test (a) Odor confirmation of mixture Dense particle size asphalt mixture (bone) mixed with 10% by volume ratio of waste FRP crushed material obtained from a crushed waste ship having a maximum particle size of 6 mm or less to the entire asphalt mixture 2 kg of a maximum particle size of 13 mm) was prepared and gradually heated in a gas stove while mixing in a wok, and the degree of odor was confirmed.

(b)加熱骨材に添加した場合の臭気確認
骨材を恒温乾燥炉に入れてそれぞれ160℃、180℃、200℃に加熱した後、この骨材に常温の廃FRP破砕物を体積比で10%投入し速やかに撹拌して温度および臭気の発生の有無を確認した。
(B) Odor confirmation when added to heated aggregate After putting the aggregate in a constant temperature drying furnace and heating to 160 ° C, 180 ° C and 200 ° C respectively, waste FRP crushed material at room temperature is added to this aggregate by volume ratio 10% was added and stirred rapidly to confirm the presence of temperature and odor.

(c)試験結果
(a)については、廃FRP破砕物を中華鍋に投入して混合を始めると同時に非常に強い臭気が確認された。(b)については、廃FRP破砕物を加熱骨材と混合するとすぐに非常に強い臭気が確認された。また、前記した加熱温度の範囲では、加熱温度の違いによる臭気の強さの差異は認められなかった。
以上の試験結果より、廃FRP破砕物を混入したアスファルト混合物は温度が100℃以上であれば温度に関係なく強い臭気を発生することが確認された。
(C) Test result Regarding (a), the waste FRP crushed material was put into a wok and mixing was started, and at the same time, a very strong odor was confirmed. As for (b), a very strong odor was confirmed as soon as the waste FRP crushed material was mixed with the heated aggregate. Moreover, in the above-mentioned heating temperature range, a difference in odor intensity due to a difference in heating temperature was not recognized.
From the above test results, it was confirmed that the asphalt mixture mixed with the waste FRP crushed material generates a strong odor regardless of the temperature when the temperature is 100 ° C. or higher.

(2)試験練り
廃FRP破砕物を混入したアスファルト混合物の臭気対策として、中温化剤を添加する方法、常温のアスファルト混合物とする方法について、その効果を確認するための試験練りを行った。ここで用いる中温化剤は結晶水を含む二水石膏を主成分とする添加剤で、微小気泡粒子を発生することにより通常のアスファルト混合物よりも約30℃低い温度で混合が可能となるものである。
(2) Test kneading As a countermeasure against odor of the asphalt mixture mixed with waste FRP crushed material, test kneading was performed to confirm the effect of a method of adding a warming agent and a method of using a normal temperature asphalt mixture. The warming agent used here is an additive mainly composed of dihydrate gypsum containing crystal water. By generating microbubble particles, mixing is possible at a temperature about 30 ° C. lower than that of a normal asphalt mixture. is there.

表4に示す配合のうち、廃FRP破砕物を体積比で5%混入した密粒度アスファルト混合物について試験練りを行った。ミキサ内へ投入した砕石、砂、石粉および廃FRP破砕物に混合温度低下剤として中温化剤(二水石膏粉末)を混合物全体に対する重量比で0.3%添加して混合し、その後アスファルトを噴霧してさらに混合した。このときの混合温度は通常の密粒度アスファルト混合物よりも約30℃低い温度とし、アスファルトを噴霧する前後の混合時間をともに通常の密粒度アスファルト混合物の場合よりも5秒ずつ長くした。通常(混合温度低下剤未添加)より臭気発生は顕著に少なく、品質にも優れたものであった。   Of the blends shown in Table 4, a test kneading was conducted on a dense particle size asphalt mixture in which 5% of the waste FRP crushed material was mixed by volume. Add to the crushed stone, sand, stone powder and waste FRP crushed material added to the mixer a mixing temperature lowering agent (dihydrate gypsum powder) as a mixing temperature reducing agent by 0.3% by weight with respect to the total mixture, and then mix asphalt. Further mixing by spraying. The mixing temperature at this time was about 30 ° C. lower than that of a normal dense-graded asphalt mixture, and the mixing time before and after spraying the asphalt was both increased by 5 seconds as compared with the case of a normal dense-graded asphalt mixture. Odor generation was remarkably less than usual (no mixing temperature reducing agent added), and the quality was excellent.

次に、表4に示す配合のうち、廃FRP破砕物を体積比で5%混入した密粒度アスファルト混合物と同じ骨材配合の常温混合物について試験練りを行った。ミキサへ砕石、砂、石粉および廃FRP破砕物を投入し、これらの骨材にカットバックアスファルトからなる常温型の改質アスファルトを噴霧して混合した。ここで、改質アスファルトの添加量は混合物全体に対する重量比で6.5%とした。臭気の発生はなかった。   Next, among the formulations shown in Table 4, a test kneading was conducted on a normal temperature mixture having the same aggregate composition as a dense particle size asphalt mixture in which waste FRP crushed material was mixed by 5% by volume. Crushed stone, sand, stone powder and waste FRP crushed material were put into a mixer, and room temperature type modified asphalt made of cutback asphalt was sprayed and mixed on these aggregates. Here, the addition amount of the modified asphalt was set to 6.5% by weight ratio with respect to the entire mixture. There was no odor generation.

試験3:試験施工
廃FRP破砕物を用いたアスファルト混合物から発生する臭気を低減する方法の効果を確認するために、本発明のアスファルト混合物および通常のアスファルト混合物を実際の車道に施工し、各々の路面性状と施工時の臭気について調査を行った。調査結果を以下の表に示す。ここで、混合物A〜Cについては、表4に示す配合のうち廃FRP破砕物を体積比で5%混入した密粒度アスファルト混合物を用いた。混合物Dについては、試験2に記載した方法で製造した常温アスファルト混合物を用いた。結果を表5に示す。
Test 3: Test construction In order to confirm the effect of the method of reducing the odor generated from the asphalt mixture using the waste FRP crushed material, the asphalt mixture of the present invention and the normal asphalt mixture were constructed on the actual roadway, We investigated road surface properties and odor during construction. The survey results are shown in the table below. Here, for the mixtures A to C, a dense particle size asphalt mixture in which the waste FRP crushed material was mixed by 5% in a volume ratio among the formulations shown in Table 4 was used. For the mixture D, a room temperature asphalt mixture produced by the method described in Test 2 was used. The results are shown in Table 5.

Figure 2005154574
Figure 2005154574

上表の測定結果より、以下のことがいえる。
(1)路面性状については、路面の轍掘れ量とすべり抵抗値について調査した。いずれの測定結果についても各工区の間に著しい差異は認められず、一般の車道用混合物として用いるうえで問題はないと思われる。
(2)施工時の臭気については、現場担当者、作業員、運転手からの聞き取り調査により評価した。混合物C、Dは通常の混合物Aと比較して特に強い臭気は感じられなかったが、混合物Bは通常の混合物Aと比較してかなり強い臭気を帯びており、周辺環境への影響が懸念された。
(3)したがって、臭気対策として中温化剤を添加した混合物Cおよび常温混合物としたDについては、施工時の臭気および施工後の路面性状とも通常の混合物と比較して遜色なく、一般の車道用混合物として用いるうえで特に問題がないということがいえる。
From the measurement results in the above table, the following can be said.
(1) Regarding road surface properties, the amount of digging and slip resistance on the road surface was investigated. There is no significant difference between each section in any measurement result, and there seems to be no problem in using it as a general roadway mixture.
(2) The odor at the time of construction was evaluated through interviews with field personnel, workers and drivers. Mixtures C and D did not feel a particularly strong odor compared to the normal mixture A, but the mixture B had a fairly strong odor compared to the normal mixture A, and there was concern about the effect on the surrounding environment. It was.
(3) Therefore, about the mixture C which added the warming agent as countermeasure against odor, and D made into the normal temperature mixture, the odor at the time of construction and the road surface property after construction are inferior to the ordinary mixture, and for general road It can be said that there is no particular problem in using the mixture.

Claims (7)

骨材と、フィラーと、アスファルト系バインダと、からなるアスファルト混合物において、骨材の一部として廃FRPを破砕して得られる廃FRP破砕物を用いると共に、アスファルト混合物が加熱アスファルト混合物であり且つ該混合物中に混合温度低下剤を含有させたことを特徴とするアスファルト混合物。     In an asphalt mixture comprising an aggregate, a filler, and an asphalt binder, a waste FRP crushed material obtained by crushing waste FRP as a part of the aggregate is used, and the asphalt mixture is a heated asphalt mixture and An asphalt mixture characterized by containing a mixing temperature lowering agent in the mixture. 廃FRP破砕物の粒径が6mm以下であることを特徴とする請求項1に記載のアスファルト混合物。   The asphalt mixture according to claim 1, wherein the particle size of the waste FRP crushed material is 6 mm or less. 廃FRP破砕物が、船体を構成する部材としてFRPを含む廃船から採取したFRPを破砕して得られることを特徴とする請求項1または2に記載のアスファルト混合物。   The asphalt mixture according to claim 1 or 2, wherein the waste FRP crushed material is obtained by crushing FRP collected from a waste vessel containing FRP as a member constituting the hull. 廃FRP破砕物の含有量が、アスファルト混合物全体に占める体積比で1〜20%であることを特徴とする請求項1〜3のいずれか1項に記載のアスファルト混合物。   The asphalt mixture according to any one of claims 1 to 3, wherein the content of the waste FRP crushed material is 1 to 20% in volume ratio to the entire asphalt mixture. 混合温度低下剤が中温化剤である請求項1〜4のいずれか1項に記載のアスファルト混合物。   The asphalt mixture according to any one of claims 1 to 4, wherein the mixing temperature lowering agent is a medium temperature increasing agent. 中温化剤が結晶水含有無機物質からなる請求項5に記載のアスファルト混合物。   The asphalt mixture according to claim 5, wherein the temperature-warming agent comprises a crystal water-containing inorganic substance. 骨材と、フィラーと、アスファルト系バインダと、からなるアスファルト混合物において、骨材の一部として廃FRPを破砕して得られる廃FRP破砕物を用いると共に、アスファルト混合物が常温アスファルト混合物であることを特徴とするアスファルト混合物。   In an asphalt mixture comprising aggregate, filler, and asphalt binder, waste FRP crushed material obtained by crushing waste FRP as part of the aggregate is used, and the asphalt mixture is a normal temperature asphalt mixture Characteristic asphalt mixture.
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CN114380539A (en) * 2022-02-13 2022-04-22 河北工业大学 Asphalt cold-patch material prepared from recycled glass fiber reinforced plastics
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