JP2008036532A - The effective use method for construction sludge - Google Patents

The effective use method for construction sludge Download PDF

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JP2008036532A
JP2008036532A JP2006213998A JP2006213998A JP2008036532A JP 2008036532 A JP2008036532 A JP 2008036532A JP 2006213998 A JP2006213998 A JP 2006213998A JP 2006213998 A JP2006213998 A JP 2006213998A JP 2008036532 A JP2008036532 A JP 2008036532A
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construction sludge
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Takaharu Otsubo
隆治 大坪
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OHTSUBO SAISEKI KK
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<P>PROBLEM TO BE SOLVED: To achieve an inexpensive solidifying treatment and a utilization technique by excluding dewatering treatment using a dewatering treatment apparatus, reducing the amount of cement for use in cement solidification and using low-cost cement when high-water content construction sludge is effectively used. <P>SOLUTION: To adjust the water content of the high-water content construction sludge, a roof tile-crushed rubble which is one of construction waste materials having a high water absorption performance and is not established with a treatment method is mixed. The grain size of the roof tile-crushed is adjusted at 40 mm or smaller. The mixture of the construction sludge and the roof tile-crushed is loaded with cement as a solidifying agent. Normally, Portland cement can also be used. However, an inexpensive treatment can be performed by applying Portland blast furnace cement. Further, a blend ratio of cement can be reduced down to not more than 20%. After loading and mixing treatment, it is aged in heaps. Thereafter, it is crushed into a size enough for utilization as a material for civil engineering/construction. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

本発明は、建設汚泥を有効に利用する方法に関する。   The present invention relates to a method for effectively using construction sludge.

従来の建設汚泥を有効に利用する方法は、建設汚泥にコンクリート殻とセメントのみを練混ぜし、その練混ぜ物を乾燥させ、乾燥した練混ぜ物を破砕して路盤材として利用する方法(例えば、特許文献1参照)、建設汚泥を脱水処理して得られた脱水ケーキにセメントからなる固化剤と水と添加剤を加えて混練することにより造粒し、養生、乾燥、分級して得られた所定粒度範囲の造粒物を、コンクリート殻の破砕処理物と混合することにより再生クラッシャランや再生粒度調整砕石として利用する方法(例えば、特許文献2参照)、ベントナイト系の汚泥又は汚水を含んでなる建設汚泥と、固化剤と、砕石とを混合して撹拌することにより、建設汚泥を固化し、所定期間養生した後、土木・建設用の資材ないし再生土として利用する方法(例えば、特許文献3参照)などがある。   The conventional method of effectively using construction sludge is a method of mixing only concrete shell and cement with construction sludge, drying the kneaded mixture, crushing the dried kneaded mixture and using it as roadbed material (for example, , Patent Document 1), obtained by dehydrating cake obtained by dehydrating construction sludge, granulating by adding a solidifying agent made of cement, water and additives and kneading, curing, drying and classification A method of using a granulated product in a predetermined particle size range as a recycled crusher or recycled particle size-adjusted crushed stone by mixing with a crushed concrete shell (for example, see Patent Document 2), including bentonite sludge or sewage The construction sludge, the solidifying agent, and the crushed stone are mixed and agitated to solidify the construction sludge, and after curing for a predetermined period, use it as civil engineering / construction materials or recycled soil ( In example, see Patent Document 3), and the like.

以下、従来の技術について説明する。特許文献1の方法は、建設汚泥にコンクリート殻とセメントのみを練混ぜし、その練混ぜ物を乾燥させ、乾燥した練混ぜ物を破砕して路盤材を得る。コンクリート殻はコンクリート廃材を破砕したものが、表面積が大きく吸水性が良いので好ましく、普通セメントを用いる場合、配合割合は、建設汚泥100:コンクリート殻90〜110:セメント40〜60である。破砕後の粒径を0〜30mmあるいは0〜40mmとすると、路盤材として必要な圧縮強度が得られ、施工性も良好となる。   Hereinafter, a conventional technique will be described. In the method of Patent Document 1, only concrete shell and cement are mixed with construction sludge, the mixed material is dried, and the dried mixed material is crushed to obtain a roadbed material. The concrete shell obtained by crushing concrete waste is preferable because it has a large surface area and good water absorption. When ordinary cement is used, the blending ratio is construction sludge 100: concrete shell 90-110: cement 40-60. When the particle size after crushing is 0 to 30 mm or 0 to 40 mm, the compressive strength necessary as a roadbed material is obtained, and the workability is also improved.

特許文献2の方法は、建設汚泥を脱水処理して得られた脱水ケーキにセメントからなる固化剤と水と添加剤を加えて混練することにより造粒し、得られた造粒物を水中にて一定期間養生した後に乾燥し、乾燥後の造粒物を分級して得られた所定粒度範囲の造粒物を、コンクリート殻を破砕処理した後に分級して得られた所定粒度範囲の破砕物と混合することにより再生クラッシャラン及び/又は再生粒度調整砕石として利用する方法である。   In the method of Patent Document 2, granulation is performed by adding a solidifying agent made of cement, water and additives to a dehydrated cake obtained by dehydrating construction sludge and kneading, and the resulting granulated product is submerged in water. After drying for a certain period of time, drying, and classifying the granulated product after drying, the granulated product of a predetermined particle size range obtained by classifying the granulated product after crushing the concrete shell It is the method of utilizing as a reproduction crusher run and / or reproduction particle size adjustment crushed stone by mixing with.

特許文献3の方法は、ベントナイト系の汚泥又は汚水を含んでなる建設汚泥(X)と、固化剤(Y)と、砕石(Z)とを、X:Y:Z=10:1〜2:1〜2の重量割合で混合して撹拌することにより、建設汚泥を固化し、所定期間養生した後、土木・建設用の資材ないし再生土として利用する際、65〜70重量%の酸化カルシウムと、13〜16重量%の二酸化ケイ素と、7〜9重量%の三酸化硫黄と、4〜6重量%の酸化アルミニウムとを主成分として含む固化剤を使用する。得られた汚泥固化物は、所定期間養生した後、土木・建設用の資材ないし再生土として用いうるように所要の大きさに破砕する方法である。 In the method of Patent Document 3, the construction sludge (X) containing bentonite sludge or sewage, the solidifying agent (Y), and the crushed stone (Z) are converted into X: Y: Z = 10: 1 to 2: By mixing and stirring at a weight ratio of 1 to 2, the construction sludge is solidified, cured for a predetermined period, and then used as a civil engineering / construction material or reclaimed soil. A solidifying agent containing 13 to 16% by weight of silicon dioxide, 7 to 9% by weight of sulfur trioxide and 4 to 6% by weight of aluminum oxide is used. The obtained sludge solidified product is a method of crushing to a required size so that it can be used as civil engineering / construction material or recycled soil after curing for a predetermined period.

特開2003−342902号公報JP 2003-342902 A 特開2003−33798号公報JP 2003-33798 A 特開平10−244297号公報Japanese Patent Laid-Open No. 10-244297

上記の特許文献1に記載された従来の方法では、高含水建設汚泥の場合、コンクリート殻の投入だけでは水分の調整が不可能であり、また、配合割合は建設汚泥100:コンクリート殻90〜110:セメント40〜60であり、セメント量が多く、高価格の路盤材となる。特許文献2に記載された方法では、脱水処理装置を用いた建設汚泥の脱水処理が不可欠である。特許文献3に記載された方法では、建設汚泥、特殊な固化剤、砕石を混合しており、また、高含水建設汚泥の場合、砕石の投入だけでは水分の調整が不可能である。   In the conventional method described in the above-mentioned Patent Document 1, in the case of high water content construction sludge, it is impossible to adjust the moisture only by charging the concrete shell, and the blending ratio is construction sludge 100: concrete shell 90-110. : Cement is 40 to 60, and the amount of cement is large, resulting in a high-priced roadbed material. In the method described in Patent Document 2, it is indispensable to dewater the construction sludge using a dewatering device. In the method described in Patent Document 3, construction sludge, a special solidifying agent, and crushed stone are mixed. In the case of high water content construction sludge, it is impossible to adjust the moisture only by adding crushed stone.

本発明は、このような従来の構成が有していた問題を解決しようとするものであり、脱水処理装置を用いた脱水処理を省き、セメント量を少なく、かつ安価なセメントを使用して、低コストの処理、利用技術を実現することを目的とするものである。   The present invention seeks to solve the problems of such a conventional configuration, omits the dehydration process using the dehydration apparatus, uses a small amount of cement, and an inexpensive cement. The purpose is to realize low-cost processing and utilization technology.

そして、本発明は上記目的を達成するために、種々検討した。高含水建設汚泥の水分調整に、高い吸水能を有する材料を混合することにした。特許文献1に記載されたコンクリート殻の場合、低含水建設汚泥では若干の効果が認められたが、高含水建設汚泥では何らかの脱水処理が不可欠であった。種々検討の結果、建設廃材の一種で、その処理方法が確定していない瓦破砕殻を混合することにより本発明の目的が達成できることを見いだした。   The present invention has been variously studied to achieve the above object. It was decided to mix materials with high water absorption capacity to adjust the water content of high water content construction sludge. In the case of the concrete shell described in Patent Document 1, some effects were recognized in the low water content construction sludge, but some dehydration treatment was indispensable in the high water content construction sludge. As a result of various investigations, it has been found that the object of the present invention can be achieved by mixing a kind of construction waste material, and a tile crushing shell whose processing method has not been determined.

第1の課題解決手段は、上記の瓦破砕殻の粒度を40mm以下に調整することで本発明の目的の一つが達成できることを見いだした。また、第2の課題解決手段は、セメントとして高炉セメントを適用することで本発明の目的の一つが達成できることを見いだした。さらに、第3の課題解決手段は、セメントの配合割合を20%以下にすることで本発明の目的の一つが達成できることを見いだした。   The first problem solving means has found that one of the objects of the present invention can be achieved by adjusting the particle size of the above-mentioned tile crushing shell to 40 mm or less. In addition, the second problem solving means has found that one of the objects of the present invention can be achieved by applying blast furnace cement as cement. Furthermore, the third problem solving means has found that one of the objects of the present invention can be achieved by setting the cement blending ratio to 20% or less.

上記第1の課題解決手段による作用は次の通りである。すなわち、高含水建設汚泥には水が50〜99%含まれている。粒度を40mm以下に調整した瓦破砕殻の吸水能は、特許文献1に記載されたコンクリート殻の吸水能の2〜3倍である。この値は水分調整材として、利用することができる値である。   The operation of the first problem solving means is as follows. That is, the high water content construction sludge contains 50 to 99% of water. The water absorption capacity of the tile crushing shell whose particle size is adjusted to 40 mm or less is 2 to 3 times the water absorption capacity of the concrete shell described in Patent Document 1. This value can be used as a moisture adjusting material.

また、上記第2の課題解決手段による作用は次の通りである。すなわち、本発明では普通ポルトランドセメント等の固化剤を使用することも可能であるが、より廉価な高炉セメントを使用することにより、低コストの処理を可能にすることができる。   The operation of the second problem solving means is as follows. That is, in the present invention, it is possible to use a solidifying agent such as ordinary Portland cement, but by using a cheaper blast furnace cement, it is possible to perform low-cost processing.

さらに、上記第3の課題解決手段による作用は次の通りである。すなわち、本発明では普通ポルトランドセメント等の固化剤よりも廉価な高炉セメントの使用とその配合割合を20%以下にすることにより、さらに、低コストの処理を可能にすることができる。   Further, the operation of the third problem solving means is as follows. That is, in the present invention, by using a blast furnace cement which is less expensive than a solidifying agent such as ordinary Portland cement and the blending ratio thereof is 20% or less, it is possible to further reduce the cost.

上記したように本発明の建設汚泥の有効利用方法は、脱水処理装置を用いた脱水処理を省き、安価なセメントを使用して、かつ、セメント量を少なく、低コストの処理、利用技術を提供できる。   As described above, the construction sludge effective utilization method of the present invention eliminates the dehydration process using the dehydration apparatus, uses an inexpensive cement, and provides a low-cost treatment and utilization technique with a small amount of cement. it can.

以下、実施例によって本発明をさらに詳細に説明するが、本発明はこれらの例によって何ら限定されるものではない。なお、各例中の配合成分の割合は質量%で表す。   EXAMPLES Hereinafter, although an Example demonstrates this invention further in detail, this invention is not limited at all by these examples. In addition, the ratio of the mixing | blending component in each case is represented by the mass%.

縦3m、横5m、深さ2mのコンクリート製貯留槽に貯留した高含水建設汚泥に40mm以下に調整した瓦破砕材を投入し、建設機械を用いて混合撹拌した。なお、上記の高含水建設汚泥には水が99%含まれ、その混合比は、高含水建設汚泥100重量部に対し、瓦破砕殻200重量部であった。つぎに、建設機械を用いてホッパーに投入し、その下部からベルトコンベアーによりミキサーに搬送し、普通ポルトランドセメントを添加しながら混練した。その後、ミキサー下部のベルトコンベアーを用いて排出した。なお、セメントの添加量は、建設汚泥と瓦破砕殻の合量の20%とした。   A highly crushed construction sludge stored in a concrete storage tank having a length of 3 m, a width of 5 m, and a depth of 2 m was charged with a tile crushing material adjusted to 40 mm or less, and mixed and stirred using a construction machine. In addition, 99% of water was contained in said high water content construction sludge, and the mixing ratio was 200 weight part of tile crushing shells with respect to 100 weight part of high water content construction sludge. Next, it was put into a hopper using a construction machine, conveyed from below to a mixer by a belt conveyor, and kneaded while adding ordinary Portland cement. Then, it discharged using the belt conveyor under a mixer. The amount of cement added was 20% of the total amount of construction sludge and tile crushing shell.

上記の排出物を山積みの状態で1週間養生した。養生後、40mm以下に破砕した。JIS A1102「骨材のふるい分け試験方法」による粒度試験結果を図1に示す。図1はJIS A5001「道路用砕石」に規定されているクラシャラン40mm(C40)の粒度範囲に適合していることを示している。また、JIS A1211によるCBR試験結果を図2に示す。図2の締固め度90%における修正CBR値の63.3%は、社団法人日本道路協会発行の「舗装施工便覧(平成18年版)」の78ページ表−5.2.1「下層路盤材料の品質規格」に記載されている基準値の20%以上の値であり、また、締固め度95%における修正CBR値の89.9%は、同84ページ表−5.3.1「上層路盤材料の品質規格」に記載されている基準値の80%以上の値であり、実施例1は、締固め度に依存するが、上層路盤材、下層路盤材共に使用できることを示している。   The above effluent was cured for 1 week in a pile. After curing, it was crushed to 40 mm or less. The particle size test result according to JIS A1102 “Aggregate screening test method” is shown in FIG. FIG. 1 shows that it conforms to the particle size range of Crusharan 40 mm (C40) defined in JIS A5001 “Crumble for road”. Moreover, the CBR test result by JIS A1211 is shown in FIG. The revised CBR value of 63.3% at 90% compaction in Fig. 2 is the "Pavement Construction Handbook (2006 edition)" published by Japan Road Association, Table 78, Table 5.2.1 "Lower layer roadbed material" The value is 20% or more of the standard value described in “Quality Standards”, and 89.9% of the corrected CBR value at a compaction degree of 95% is shown in Table-5.3.1 The value is 80% or more of the reference value described in “Quality standard of roadbed material”, and Example 1 shows that both upper layer roadbed material and lower layer roadbed material can be used, depending on the degree of compaction.

瓦破砕殻の粒度を25mm以下にし、普通ポルトランドセメントを高炉セメントに置き換え、セメントの添加量を建設汚泥と瓦破砕殻の合量の10%とした以外は、実施例1記載の方法と全く同じ処理を行った。粒度試験結果を図3に示す。図3はJIS A5001「道路用砕石」に規定されているクラシャラン40mm(C40)の粒度範囲に適合していることを示している。また、CBR試験結果を図4に示す。図4の締固め度90%における修正CBR値の43.0%は、前記の「下層路盤材料の品質規格」に記載されている基準値の20%以上の値であり、また、締固め度95%における修正CBR値の112.8%は、前記の「上層路盤材料の品質規格」に記載されている基準値の80%以上の値であり、実施例2も、締固め度に依存するが、上層路盤材、下層路盤材共に使用できることを示している。   Exactly the same as the method described in Example 1, except that the particle size of the tile crushing shell is 25 mm or less, ordinary portland cement is replaced with blast furnace cement, and the amount of cement added is 10% of the total amount of construction sludge and tile crushing shell. Processed. The particle size test results are shown in FIG. FIG. 3 shows that the particle size range of 40 mm (C40) specified by JIS A5001 “road crushed stone” is met. Further, the CBR test results are shown in FIG. 43.0% of the corrected CBR value at a compaction degree of 90% in FIG. 4 is a value that is 20% or more of the standard value described in the above-mentioned “Quality standard for lower layer roadbed material”, and the compaction degree. The corrected CBR value at 95% is 112.8%, which is 80% or more of the reference value described in the above-mentioned “Quality standard for upper-layer roadbed material”, and Example 2 also depends on the degree of compaction. However, it can be used for both upper layer roadbed material and lower layer roadbed material.

実施例2と同様に、瓦破砕殻の粒度を25mm以下にし、普通ポルトランドセメントを高炉セメントに置き換え、さらに、セメントの添加量を建設汚泥と瓦破砕殻の合量の5%とした。実施例1記載の方法と同様の処理を行った。養生後の破砕粒度を10mm以下とし、再生砂土とした。粒度試験結果を図3に示す。また、この再生砂土のコーン指数は2250kN/mであった。この値は、社団法人地盤工学会発行の「土質試験の方法と解説(第一回改訂版)」の269ページ表−5.3.1「建設発生土に関連する土質区分基準表」では第2種建設発生土に分類され、工作物の埋戻し、道路(路床)盛土、土木構造物の裏込め、道路路体用盛土等の適用用途標準(同上、270ページ表−5.3.2(a))によると、全ての用途にそのままで使用可能なものに分類される値である。 As in Example 2, the particle size of the tile crushing shell was 25 mm or less, ordinary portland cement was replaced with blast furnace cement, and the amount of cement added was 5% of the total amount of construction sludge and tile crushing shell. The same treatment as that described in Example 1 was performed. The crushed particle size after curing was set to 10 mm or less to obtain recycled sand. The particle size test results are shown in FIG. The cone index of this reclaimed sand was 2250 kN / m 2 . This value is shown in Table 5.3.1, “Soil Classification Criteria for Construction Soil”, in “Soil Test Methods and Explanations (First Revised Edition)” published by the Geotechnical Society of Japan. It is classified into two types of construction generated soil, and application standard such as backfilling of work, road (roadbed) embankment, backfilling of civil engineering structures, embankment for road road bodies, etc. (table on page 270-5.3. According to 2 (a)), the values are classified into those that can be used as they are for all purposes.

有効利用が望まれている建設汚泥と建設廃材の瓦を全量利用でき、かつ、高強度の路盤材として利用できる。また、埋め立て材としても利用でき、環境保全にも役立つ。   The construction sludge and construction waste tiles that are expected to be used effectively can be used in all quantities and can be used as high-strength roadbed materials. It can also be used as landfill material, which is useful for environmental conservation.

実施例1のJIS A1102による粒度試験結果である。3 is a particle size test result according to JIS A1102 of Example 1. 実施例1のJIS A1211によるCBR試験結果である。2 is a CBR test result according to JIS A1211 of Example 1. FIG. 実施例2のJIS A1102による粒度試験結果である。4 is a particle size test result according to JIS A1102 of Example 2. 実施例2のJIS A1211によるCBR試験結果である。It is a CBR test result by JIS A1211 of Example 2. 実施例3のJIS A1102による粒度試験結果である。4 is a particle size test result according to JIS A1102 of Example 3.

Claims (4)

高含水建設汚泥に瓦破砕殻を投入混合して水分を調整したのち、セメントを練り混ぜ、固化させたのち、破砕し、路盤材や埋め立て材として利用することを特徴とする建設汚泥の有効利用方法。   Efficient use of construction sludge, characterized by adding and crushing tile crushing shell into high water content construction sludge to adjust moisture, kneading and solidifying cement, crushing and using as roadbed material and landfill material Method. 請求項1記載の瓦破砕殻が、40mm以下であることを特徴とする建設汚泥の有効利用方法。   The method for effectively using construction sludge, wherein the tile crushing shell according to claim 1 is 40 mm or less. 請求項1記載のセメントが、高炉セメントであることを特徴とする建設汚泥の有効利用方法。   The method according to claim 1, wherein the cement according to claim 1 is a blast furnace cement. 請求項1記載のセメントの配合割合が20%以下であることを特徴とする建設汚泥の有効利用方法。

An effective utilization method of construction sludge, wherein the blending ratio of the cement according to claim 1 is 20% or less.

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JP2010024771A (en) * 2008-07-23 2010-02-04 Yamatakagumi:Kk Manufacturing method of lightweight base material for civil engineering work which comprises granulated object
JP2011235242A (en) * 2010-05-11 2011-11-24 Niigata Garbage Kk Method for manufacturing granulated improved soil
JP2016204578A (en) * 2015-04-27 2016-12-08 宇部興産株式会社 Solidification material for high water-containing soil and solidification treatment method of high water-containing soil
CN107129231A (en) * 2017-05-26 2017-09-05 张伟忠 A kind of high intensity backfilling material based on building waste and preparation method thereof
CN110282956A (en) * 2019-07-09 2019-09-27 上海环境保护有限公司 A kind of method that river bottom mud solidifies brickmaking resource utilization
WO2021201051A1 (en) * 2020-03-30 2021-10-07 ニチレキ株式会社 Method for constructing roadbase layer, and mixture for use in said method
CN114717884A (en) * 2022-04-27 2022-07-08 湖南建工交通建设有限公司 Completely weathered granite sedimentary soil subgrade and construction method

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JP2001336206A (en) * 2000-05-30 2001-12-07 Obayashi Road Corp Drainage ditch-shaped closed conduit and drainage block
JP2003342902A (en) * 2002-05-30 2003-12-03 Techno Network Shikoku Co Ltd Subbase course material and its manufacturing method
JP2005272546A (en) * 2004-03-24 2005-10-06 Kawai Sekkai Kogyo Kk Soil neutralizing and solidifying material, and improved method for neutralizing and solidifying soil

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008062219A (en) * 2006-09-11 2008-03-21 Tadao Santo Method for treating sludges and porous material
JP2010024771A (en) * 2008-07-23 2010-02-04 Yamatakagumi:Kk Manufacturing method of lightweight base material for civil engineering work which comprises granulated object
JP2011235242A (en) * 2010-05-11 2011-11-24 Niigata Garbage Kk Method for manufacturing granulated improved soil
JP2016204578A (en) * 2015-04-27 2016-12-08 宇部興産株式会社 Solidification material for high water-containing soil and solidification treatment method of high water-containing soil
CN107129231A (en) * 2017-05-26 2017-09-05 张伟忠 A kind of high intensity backfilling material based on building waste and preparation method thereof
CN110282956A (en) * 2019-07-09 2019-09-27 上海环境保护有限公司 A kind of method that river bottom mud solidifies brickmaking resource utilization
WO2021201051A1 (en) * 2020-03-30 2021-10-07 ニチレキ株式会社 Method for constructing roadbase layer, and mixture for use in said method
JP7382492B2 (en) 2020-03-30 2023-11-16 ニチレキ株式会社 Construction method of subbase layer and mixture used therein
CN114717884A (en) * 2022-04-27 2022-07-08 湖南建工交通建设有限公司 Completely weathered granite sedimentary soil subgrade and construction method
CN114717884B (en) * 2022-04-27 2023-11-24 湖南建工交通建设有限公司 Fully weathered granite sedimentary soil roadbed and construction method

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