Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP3547384B2 - Soil improvement material and pavement method - Google Patents
[go: Go Back, main page]

JP3547384B2 - Soil improvement material and pavement method - Google Patents

Soil improvement material and pavement method Download PDF

Info

Publication number
JP3547384B2
JP3547384B2 JP2000280067A JP2000280067A JP3547384B2 JP 3547384 B2 JP3547384 B2 JP 3547384B2 JP 2000280067 A JP2000280067 A JP 2000280067A JP 2000280067 A JP2000280067 A JP 2000280067A JP 3547384 B2 JP3547384 B2 JP 3547384B2
Authority
JP
Japan
Prior art keywords
soil
water
test
water content
content
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 - Lifetime
Application number
JP2000280067A
Other languages
Japanese (ja)
Other versions
JP2002088363A (en
Inventor
久雄 大沢
昌三 大川
国平 周
Original Assignee
株式会社ハイクレー
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by 株式会社ハイクレー filed Critical 株式会社ハイクレー
Priority to JP2000280067A priority Critical patent/JP3547384B2/en
Publication of JP2002088363A publication Critical patent/JP2002088363A/en
Application granted granted Critical
Publication of JP3547384B2 publication Critical patent/JP3547384B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Images

Landscapes

  • Road Paving Structures (AREA)
  • Treatment Of Sludge (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は、上水汚泥を用いた土質改良材および土舗装方法に関する。
【0002】
【従来の技術】
屋外のスポーツ施設、学校のグラウンドなどに多く採用されているクレイコートには、赤土、荒木田土、真砂土などの天然土が広く利用されている。このように天然土を利用することにより、低コストで、自然な感触のクレイコートを形成することができる。
【0003】
しかしながら、このような天然土は、シルト質あるいは粘土質を主成分とするものであるので、雨が降るとぬかるんだり、泥濘化しやすく、また晴天が続くと埃が立ちやすい欠点がある。
【0004】
そこで、天然土のメリットを保ちながら上述の欠点をカバーするために、本出願人は、特許1556916号(特公平1−041762号)において、上水汚泥(浄水場発生土)を用いた土舗装方法を提案している。この土舗装方法によれば、自然土の好ましい性質を有し、かつ耐久性、耐水性に優れた土舗装を行うことができ、土舗装面の保守に手間がかからなくなる。また、上水汚泥を、採取困難になりつつある一般舗装用土材料の増量材として、有効利用することができる。
【0005】
【発明が解決しようとする課題】
ところで、上水汚泥を用いた土舗装方法では、上水汚泥を細砂以下の粒状に粉砕加工する必要がある。この場合、
▲1▼上水汚泥を乾燥させたうえで、粉砕加工する方法
▲2▼上水汚泥を、含水したままの状態(30〜60%の水分を含む状態)でタイヤローラーなどによる加圧により、舗装用基礎上で微粒子状に破壊する方法等が考えられる。
【0006】
しかしながら、上水汚泥の含有する水分は通常高く、特に近年は、その含水率が70〜80%であるケースが多い。また、脱水装置により脱水ケーキを作成した場合も、その含水率にはかなりばらつきがある。このため、上記▲1▼の方法は、技術的に相当困難であり、実行するうえで高い費用がかかっていた。
【0007】
また、粉砕のために上水汚泥の乾燥度を高めてしまうと、上水汚泥中の凝集剤に基づく耐水性能が失われてしまい、土舗装面の耐水性、耐久性が弱くなってしまうことがある。そして、上水汚泥からいったん耐水性能が失われてしまうと、その後に加水したとしても、耐水性能を回復することができない。
【0008】
また、細砂以下の粒状に粉砕した上水汚泥は、土粒子と緊密に結合することにより堅固な舗装面を形成するものであるが、粒子が細かいため、十分な透水性が得られず、埃となり易いとという問題があった。
【0009】
一方、上記▲2▼の方法では、加圧作業を相当に繰り返す必要があるし、上水汚泥を混合する土材料の含水状態のばらつきや、混合用機械の性能の限界から、粉砕が困難となったり、土材料と上水汚泥の混合が不均一になるケースが多く、目的とする耐水性、耐久性を安定的に確保することが困難であった。また、高含水のままの上水汚泥を施工現場に用いると、上水汚泥の中に含まれている有機物によって、異臭が発生してしまうこともあった。
【0010】
本発明は、このような問題点に着目してなされたもので、製造が容易であり、かつ高い耐水性、透水性を備えた土質改良材およびこの土質改良材を用いた舗装方法を提供することを目的とする。
【0011】
【課題を解決するための手段】
第1の発明は、土質改良材は、浄水場から得られる上水汚泥を、その塑性限界付近の含水比に調整し、次いで、前記上水汚泥を粒径0.425mm4.75mmの粒度範囲のバインダー骨材粒子50重量%以上含有されるよう粒状化し、その後に、上水汚泥中の含水比が最低含水比限界を下回らない範囲で乾燥処理して形成され、主に粒径0.425mm〜4.75mmの粒度範囲のバインダー骨材粒子である粗粒部分およびそれ以下の細粒部分からなる。
【0012】
第2の発明は第1の発明において、前記塑性限界付近の含水比は、75〜95%であり、その状態に調整した後に粒状化される
【0014】
の発明は第1または第2の発明において、前記最低含水比限界は、50%である
【0015】
の発明は第1ないし第3の発明において、前記土質改良材は、前記乾燥処理後に加水して含水比を60%〜120%に調整して貯蔵される
【0016】
の発明は舗装方法であり、浄水場から得られる上水汚泥を、その塑性限 界付近の含水比に調整し、その状態で粒径0.425mm〜4.75mmの粒度範囲のバインダー骨材粒子が50重量%以上含有されるよう粒状化し、次いで上水汚泥中の含水比が最低含水比限界を下回らない範囲で乾燥処理した主に粒径0.425〜4.75mmの粒度範囲のバインダー骨材粒子である粗粒部分およびそれ以下の細粒部分からなる土質改良材、または前記乾燥処理後に加水して含水比を60%〜120%に調整して貯蔵した主にバインダー骨材粒子である粗粒部分および細粒部分からなる土質改良材を、混合物全体に対して容積比20〜50%の割合で土材料と混合し、この混合物を用いて舗装面を形成する。
【0017】
の発明は第5の発明において、前記土材料として粘性土を利用し、前記土質改良材を、混合物全体に対する容積比30〜50%の割合で粘性土と混合し、この混合物を用いて舗装面を形成する。
【0018】
の発明は、第の発明において、前記土質改良材は含水比60〜105%に調整されたものである。
の発明は第5の発明において、前記土材料として砂質土を利用し、前記土質改良材を、混合物全体に対する容積比20〜30%の割合で砂質土と混合し、この混合物を用いて舗装面を形成する。
【0019】
の発明は、第の発明において、前記土質改良材は含水比70〜110%に調整されたものである。
【0020】
10の発明は第5の発明において、前記土材料として岩石スクリーニングスを利用し、前記土質改良材を、混合物全体に対する容積比20〜40%の割合で岩石スクリーニングスと混合し、この混合物を用いて舗装面を形成する。
【0021】
11の発明は、第10の発明において、前記土質改良材は含水比60〜120%に調整されたものである。
【0022】
【発明の作用および効果】
第1の発明では、上水汚泥中にバインダー骨材粒子(汚泥粒子同士が団粒状態となった粒子)を形成して土質改良材とする。この場合、粒径0.425mm以上、4.75mm以下のバインダー骨材粒子が上水汚泥全体に対して50重量%以上含有されるようにすることにより、土材料との混合時に骨材として作用するのに適切な大きさのバインダー骨材粒子が、土質改良材中に十分に確保される。このため、土質改良材を土材料と混合して舗装面を形成する場合には、土材料の粒子は、土質改良材中の細粒部分(バインダー骨材粒子化されていない部分)からなる薄膜により覆われて、この薄膜を介して土粒子同士で強く結合される一方、土質改良材中の粗粒部分(バインダー骨材粒子部分)は、土粒子同士の間に介在して土粒子同士を結合させるとともに、土粒子間に適切な隙間を形成する(土粒子を支える骨材の役割をする)。これにより、舗装面は、水浸時に土粒子間の隙間から水を速やかに下層へ浸透させることができるので、泥濘を発生させることなく、優れた耐水性と透水性を持つものとなる。
また、粒状化後に、上水汚泥中の含水比が最低含水比限界を下回らない範囲で乾燥処理することによって、上水汚泥中に含まれる揮発性有機物を揮発させるので、土質改良材からは揮発性有機物に起因する異臭が取り除かれる。
【0023】
また、第2の発明では、第1の発明の効果に加えて、上水汚泥の含水比を75〜95%に調整してバインダー骨材粒子を形成するので、上水汚泥は塑性限界付近の含水比にあって、最適な可塑性をもつことになり、僅かな外力によって、効果的にバインダー骨材粒子構造を形成することができる。
【0025】
また、第の発明では、第1または第2の発明の効果に加えて、乾燥処理は、上水汚泥の含水比が50%(最低含水比限界)を下回らない範囲で行われるので、上水汚泥の乾燥度を高めすぎて、上水汚泥に含まれる凝集剤による耐水性能が失われてしまうことはない。したがって、完成した土質改良材は、優れた耐水性を持ち、水浸しても膨張崩壊することがない。
【0026】
また、第の発明では、第1ないし第3発明の効果に加えて、乾燥処理後に適切な加水がなされるので、土質改良材を用いて舗装を行った場合に、舗装面が硬くなり過ぎず、適切な締め固め度を持たせることができる。また、貯蔵時に含水比が50%を下回って耐水性能が失われてしまうことを未然に防止できる。
【0027】
、第、第、第10の発明では、適切な混合比で土質改良材と土材料との混合がなされるので、適切な締固め度合いの舗装面を形成できる。また、土材料に対する土質改良材の混合割合は容積比で50%以下であるので、現地土と土質改良材との置換により発生する廃棄土の量が多くなりすぎず、廃棄土処分の負担が小さくて済む。
【0028】
、第、第11の発明では、土質改良材の含水比が適切に調整されているので、適切な締固め度合いの舗装面を形成できる。
【0029】
【発明の実施の形態】
以下、添付図面に基づいて、本発明の実施の形態について説明する。
【0030】
本発明では、浄水場から採取した上水汚泥中にバインダー骨材粒子を形成して土質改良材とする。ここで、バインダー骨材粒子とは、上水汚泥の汚泥粒子が団粒状態となった粒子のことであり、舗装面形成時には、土粒子間に介在して、土粒子を結合させるとともに、結合された土粒子間に隙間が形成されるように土粒子を支持する骨材のような働きをするものである。
【0031】
上水汚泥中へのバインダー骨材粒子の形成は、以下のように行われる。
【0032】
まず、上水汚泥をバインダー骨材粒子が形成されやすい状態とするため、上水汚泥の含水比を、含水比75〜95%に調整する。これにより、上水汚泥は、含水比が塑性限界付近に調整されることになり、可塑性が最適な状態となって、わずかな外力によっても、バインダー骨材粒子構造を形成しやすい状態となる。また、形成されたバインダー骨材粒子も、壊れることなく、安定した形を保つことになる。
【0033】
例えば、上水汚泥の含水比が95%以上であれば、上水汚泥の加熱蒸発により、水分を蒸散させる。この場合、上水汚泥に含まれる揮発性有機物も揮発する。加熱蒸発は、天日乾燥、あるいは温室での通風乾燥等によりなされる。例えば、天日乾燥においては、工場敷地内で、上水汚泥を5〜30cmの厚さで敷き均し、時間毎にトラクターで攪拌し、水分を徐々に蒸発させる。このような加熱蒸発処理は、上水汚泥の含水比を時間毎に測定しつつ、含水比が75〜95%に調整されるまで続けられる。なお、含水比の測定は、例えば、事前に用意した含水比−かさ比重の関係曲線により行う。
【0034】
このように含水比を最適に調整した上水汚泥を、スニーダー(破砕機)に通して、19mm以下の粒状にする。さらに、このスニーダーに通した上水汚泥粒子を10mmの篩いにかけ、所定の粒度範囲(0.425〜4.75mm)のバインダー骨材粒子が、上水汚泥中に50重量%以上含有されるように調整する。この場合、バインダー骨材粒子の含有割合は、土質工学会(JSF T131)の粒度分析試験方法に準じた測定方法で測定される。
【0035】
このような方法で得られた上水汚泥を、さらに工場の敷地内で5〜10cmの厚さで敷き均し、時間毎に攪拌しながら天日により再び乾燥させ、最低含水比限界値(含水比50%)以上の所定値まで、水分を蒸発させる。この蒸発により、上水汚泥の中に含まれた揮発性有機物はほとんど揮発し、また、陽射に含まれる紫外線が殺菌効果を果たすため、上水汚泥中の揮発性有機物による異臭を解消することができる。なお、この乾燥処理(脱臭処理)は、温室内で通風乾燥および紫外線殺菌により行うことも可能である。
【0036】
このような乾燥処理を始め、以上のいずれの処理においても、上水汚泥の含水比は定期的に測定され、50%(最低含水比限界値)以上であり続けるようにコントロールされる。上水汚泥は、この最低含水比限界値以上の含水比に維持されることによって、耐水性能を維持することができる。
【0037】
以下、詳しく説明する。浄水場で浄水処理においては、懸濁物を速く沈殿させるため、凝集剤(例えば、PAC)の添加が実施される。これらの凝集剤は、水分子と化学反応すると同時に、大量の正電荷が発生させ、負電荷をもつ懸濁物と結びついて、大きなフロックを生成する。フロックは重力により底に沈殿する。これにより、懸濁物と凝集剤との結合物とも言える上水汚泥が生成される。水分子と反応した凝集剤は水に溶けない水酸化アルミニウム物質に変化し、この水酸化アルミニウム物質の効果で、上水汚泥は、強い耐水性を持つことになる。
【0038】
しかしながら、水酸化アルミニウム物質は、いったん水が無くなった状態におかれると、再び水分子と反応することができず、また他の負電荷を持つ物質と再び結びつくことができなくなり、水に溶けない性質も失ってしまう。このため、上水汚泥に耐水性能を維持するためには、常に有る程度以上の水分が存在することが必要となり、これが最低含水比限界となる。この最低含水比限界を下回らない範囲で各種処理を実行することにより、上水汚泥の耐水性を確保しながら、水分調整、脱臭処理を適切に行うことができ、高品質の土質改良材を形成できる。
【0039】
このように乾燥処理がなされた土質改良材は、含水比が低いため、そのままでは適当な締固め度合いが得られない。また、貯蔵している間に、乾燥で含水比が50%以下に下がる可能性もある。したがって、乾燥処理後、土質改良材に速やかに再び加水し、含水比を60%〜120%に調整してから、貯蔵する。
【0040】
舗装においては、このようにして得られた土質改良材を、一般の舗装用土材料と混合し、この混合物により舗装面を形成する。
【0041】
この場合、舗装用土材料の粒子は、土質改良材中の細粒部分(バインダー骨材粒子化されていない部分)からなる薄膜により覆われて、この薄膜を介して土粒子同士で強く結合される。一方、土質改良材中の粗粒部分(バインダー骨材粒子部分)は、土粒子同士の間に介在して土粒子同士を結合させるとともに、土粒子を支持する骨材のような働きをして、土粒子間に適切な隙間を形成する。これにより、舗装面は、水浸時に土粒子間の隙間から水を速やかに下層へ浸透させることができるので、泥濘を発生させることなく、優れた耐水性と透水性を持つものとなる。
【0042】
土質改良材と土材料の混合においては、土質改良材の混合割合を20%〜50%の範囲内のものとするとよい。混合物全体に対する土質改良材の混合割合を20%以上とすることにより、土材料の土粒子を完全に覆いきるのに十分な量の土質改良材を確保できる。また、この混合割合を50%以下とすることにより、舗装面が土質改良材を大量に混入し過ぎることで、舗装面が硬くなりすぎることを防止できる。土質改良材の混合割合が50%以下であれば、土質改良材と土材料(現地土)の置換による廃棄土の発生を比較的少なくすることができ、廃棄土処理の負担を軽減できる。
【0043】
土質改良材と各種舗装用土材料との具体的な混合においては、当該土材料の特性(含水状態、粒度分布、表面積、最適含水比など)に基づいて、混合すべき土質改良材の含水比、バインダー骨材粒子含有割合、土材料と土質改良材の混合割合を、最適混合効果が得られるように調整する。ここで最適混合効果とは、両者を混合した場合、混合の均一性が確保されると同時に、舗装面の耐水性、透水性を最大限に高めることができ、かつ適当な締固め度合いを得ることができることを言う。具体的には、土材料と土質改良材を混合したときに、混合物が最適な含水比を持つように調整することにより、舗装面には適切な締固め度合いが得られる。
【0044】
土質改良材と舗装用土材料との混合は、例えばプラント混合により、混合が全体に均一になるまで十分に行う。または、施工現場で中央混合により行ってもよい。
【0045】
図1は、各種舗装用土材料と土質改良材を、最適混合効果が得られるように混合した例を示すである。
【0046】
に示されるように、土材料が粘性土(例えば、荒木田土、赤土、黒土など)の場合、含水比は一般に高い(5〜25%)。また、粘土・シルト質分が50%以上を占め、表面積も大きいので、土質改良材とは混合しにくい。このような土材料に対しては、含水比60〜105%、バインダー骨材粒子含有割合65〜75重量%に調整した土質改良材を、30〜50%の混合割合で混合する(以下、実施形態2とする)
【0047】
土材料が砂質土(例えば、真砂土、山砂など)の場合、含水比は一般的に低い(5〜15%)。また、細砂以上の粒子が70%以上を占め、表面積は小さく、土質改良材と混合しやすい。このような土材料に対しては、含水比70〜110%、バインダー骨材粒子含有割合50〜65%に調整した土質改良材を、20〜30%の混合割合で混合する(以下、実施形態3とする)
【0048】
土材料が岩石スクリーニングス(例えば、緑色スクリーニングス、石灰岩ダストなど)の場合、含水比は低いものから中程度のものがある。また、粘土・シルト質の相当分が30%近くあり、細砂以上の構成分が多く、表面積のぱらつきが大きいので、土質改良材との混合は不確定な要素が多い。このような土材料に対しては、含水比60〜120%、バインダー骨材粒子含有割合60〜70%に調整した土質改良材を、20〜40%の混合割合で混合する(以下、実施形態4とする)
【0049】
以上のように、土材料の種類に応じて、土質改良材の含水比、バインダー骨材粒子含有量、土材料との混合割合を調整することにより、混合物は最適な含水比を持つものとなり、最適混合効果が得られる。なお、これについて裏付ける実験結果については、図以下のとともに説明する。
【0050】
つぎに、本発明により、舗装面の耐水性、透水性向上、異臭解消等の効果が得られることを裏づける実験結果について説明する。
【0051】
図2は、バインダー骨材粒子形成に最適な含水比を調べるために行った試験の結果を示すである。
【0052】
この試験では、種々の含水比の上水汚泥(試験番号1〜12号)を、破砕機にかけて19mm以下の粒子に破砕したうえで、10mmの篩いに通したものについて、0.425〜4.75mmのバインダー骨材粒子含有量を計測する。ここでは、含水比94%と75%の試験番号7、8の供試体が実施形態1の実施例1、2であり、試験番号6、9、10の供試体は参考例であり、その他の試験番号の供試体は比較例である。バインダー骨材粒子の含有量測定は、土質工学会(JSF T131)の粒度分析試験方法に準じた測定方法で行う。
【0053】
以下、試験結果について考察する。まず、含水比が多い試験番号1〜6号の供試体(いずれも含水比が95%以上)では、上水汚泥に含まれた水分が多すぎるため、大きな塊が形成されやすく、上記範囲のバインダー骨材粒子がなかなか形成されない。また、バインダー骨材粒子がいったん形成されたとしても、形状が安定せず、再び大きな塊になってしまう。このように、含水比が120%を超える供試体については、十分な量のバインダー骨材粒子が形成されず、また含水比が多いほど、バインダー骨材粒子の形成量が少ない傾向が見られる。
【0054】
一方、含水比が少ない試験番号10〜12号の供試体(いずれも含水比が65%以下)でも、十分な量のバインダー骨材粒子の形成がなされず(最大でも試験番号10の53重量%)、また、形成されたバインダー骨材粒子も外力で破壊されやすい。これは上水汚泥の水分が少ないため、上水汚泥の可塑性が小さくなっているからである。
【0055】
これに対して、含水比が塑性限界付近の75〜95%にある試験番号7〜9号の供試体では、バインダー骨材粒子が形成されやすく、バインダー骨材粒子の含有量は50〜70%となる。
【0056】
以上から、バインダー骨材粒子の形成は、含水比が75〜95%に調整された場合、最もなされやすいことが分かる。
【0057】
図3には、バインダー骨材粒子についての耐水性試験の結果を示す。
【0058】
この試験では、バインダー骨材粒子を形成した上水汚泥(産地の異なる7種類の上水汚泥)から、2〜4.75mmのバインダー骨材粒子を100gを取り出し、乾燥させた後、ビーカーを用いて水浸試験を行う。水浸試験では、水中に浸したバインダー骨材粒子をガラス棒で1分間攪拌し、24時間静置してバインダー骨材粒子の崩壊を観察する。24時間後、ビーカー中の試料を0.425mmの篩いに通し、残留物を乾燥させ、計量後バインダー骨材粒子の崩壊率を算出する。24時間後にバインダー骨材粒子がほとんど崩壊しない場合、耐水性があると評価できる。なお、比較のため、荒木田土の球状粒子(団粒)についても同じ試験を行った。ここでは、試験番号1〜7の試料が実施形態1の実施例3〜9であり、試験番号8の試料が比較例である。
【0059】
に示されるように、上水汚泥から採取したバインダー骨材粒子の7つの試料は、いずれも24時間後の崩壊率が3%以下である。一方、荒木田土の球状粒子は水浸、攪拌してから徐々に膨張、崩壊し始め、24時間後の崩壊率は95%となり、ほとんどの球状粒子が崩壊した。
【0060】
この結果から、上水汚泥のバインダー骨材粒子は、水に対して強い性質(耐水性)を有することが分かる。これは、上述したように、上水汚泥に含まれる凝集剤の作用によるものである。この耐水性により、バインダー骨材粒子は、土質改良材が一般の土材料と混合されたときに、土粒子間の隙間を支える骨材としての役割を発揮でき、舗装面の透水性を向上させる働きをする。
【0061】
図4は、土質改良材の透水試験の結果を示すである。
【0062】
この試験では、供試体を24時間に渡って水浸飽和させた後、供試体上部から透水し、所定時間経過後の透水量を計測する。これを基に透水係数を算出する。
【0063】
供試体としては、自然乾燥させた真砂土に上水汚泥を30%の容積割合で混合した混合物を、最適含水比近くに水分を調整し、直径8cm、高さ8cmの円柱体としたものを用いる。供試体の種類としては、バインダー骨材粒子含有量が異なる5種類の上水汚泥について作成したもの(試験番号1〜5)と、細砂以下に粉砕した上水汚泥について作成したもの(試験番号6)と、上水汚泥をそれぞれ荒木田土(球状粒子を形成したもの)、真砂土に置き換えて作成したもの(試験番号7、8)を用意する。ここでは、試験番号2〜5の供試体が実施形態1の実施例10〜13であり、その他の試験番号の供試体は比較例である。
【0064】
に示されるように、バインダー骨材粒子を形成した上水汚泥からなる供試体(試験番号1〜5号)は、荒木田土からなる供試体(試験番号7号)または真砂土のみからなる供試体(試験番号8号)と比較して、はるかに高い透水係数を持っている。例えば、試験番号7の供試体では、荒木田土の球状粒子は、水に非常に弱く、水浸するとすぐ崩壊してしまうので、バインダー骨材粒子のように真砂土粒子間を支持する骨材として作用することはなく、透水係数も非常に低いものとなる。
【0065】
また、バインダー骨材粒子を形成した上水汚泥からなる供試体同士を比較すると、上水汚泥中のバインダー骨材粒子量が多くなるほど、透水係数の向上が見られる。
【0066】
また、上水汚泥を用いた供試体でも、バインダー骨材粒子を形成せず、細砂以下に粉砕した上水汚泥からなる供試体(試験番号6号)では、透水係数は、真砂土からなる供試体(試験番号8号)よりもむしろ低下してしまう。これは、細砂以下の上水汚泥が、混合された真砂土の粒子間の隙間を塞いでしまうからと考えられる。
【0067】
以上から、上水汚泥にバインダー骨材粒子を形成することにより、これと土材料との混合物の透水性が著しく向上することが分かる。
【0068】
図5には、バインダー骨材粒子の耐水性効果と上水汚泥の含水比との関係を調べるために行った水浸試験結果をで示す。
【0069】
この試験では、バインダー骨材粒子を形成された上水汚泥に適当な加水をした後、型枠(4cm×3cm×0.7cm)に充填し、押し固めた後に取り出し、110℃で24時間乾燥させて、供試体とする。この供試体を水没させ、供試体の変化を観察する。24時間以内に供試体の崩壊時間、また24時間後の供試体の軟弱化などの状態を確認する。この試験は、含水比が異なる10種類の上水汚泥を供試体として行う。ここでは、試験番号1〜5の供試体が第1実施形態の実施例14〜18であり、試験番号6の供試体は参考例であり、その他の試験番号の供試体は比較例である。
【0070】
この水浸試験結果によれば、含水比が50%以上の供試体(試験番号1〜5)では、略十分な耐水性が示された。具体的に、試験番号1〜3号の供試体は、水浸24時間後においてもほとんど崩壊せず、軟弱化もしなかった。また、試験番号4号の供試体(含水比63%)はやや軟弱化し、試験番号5号の供試体(含水比52%)は軟弱化したが、いずれも崩壊することはなかった。
【0071】
一方、含水比が50%以下の供試体(試験番号6〜10)では、十分な耐水性が得られなかった。具体的に、試験番号7〜10号の供試体は、いずれも24時間以内に完全に崩壊した。また、含水比の一番多い試験番号6号の供試体(含水比43%)でも、24時間後には一部崩壊が見られた。
【0072】
以上の結果から、土質改良材が十分な耐水効果を持つためには、含水比を50%以上とする必要があると結論できる。
【0073】
図6には、上水汚泥の加熱乾燥による脱臭試験結果をで示す。
【0074】
この試験は、上水汚泥の異臭を簡単な加熱蒸発方法で取り消すことができるかどうかを確認するために行ったものである。
【0075】
試験は、含水比が150%前後の上水汚泥を500gづつ供試体として、恒温炉で加熱する。加熱前後の異臭を人の臭覚でチェックして、異臭の強さを区分する。なお、試験は加熱温度を20℃から110℃まで10段階に分け、加熱時間をそれぞれ4時間、6時間、8時間において行う。異臭の強さの分類は、試験を行った者の感覚で、相当気になる、気になる、あまり気にならない、ほとんど気にならない、の4段階で判定した。
【0076】
この試験により、次の傾向が見られる。まず、同じ加熱時間の場合、加熱温度が高いほど、異臭の解消量が多い。次に、同じ加熱温度の場合、加熱時間が長いほど、異臭の解消量が多い。具体的には、4時間加熱の場合、異臭があまり気にならない状態になるのに70℃の加熱温度が必要である。これに対して、6時間加熱の場合、この温度が50℃に下がり、また、8時間加熱の場合、さらに30℃にまで下がった。即ち、高温で短時間に得られる脱臭効果は、低温で長時間に同様な脱臭効果が得られることが分かった。後者は、設備投資の節約、またエネルギーの節約も果せる、より簡単かつ有効な脱臭方法でもある。
【0077】
また、試験結果に示されるように、異臭があまり気にならない状態までに下がったとき、上水汚泥の含水比は、ほぼ42〜63%の間にある。即ち、加熱蒸発により含水比を50%近くまで落とした時、上水汚泥の異臭を概ね解消することができる。
【0078】
この試験結果から、上水汚泥を脱臭する時、30℃〜50℃の温度を8時間以上保ったまま、含水比を50%近くに下げれば、かなりの脱臭効果が得られると結論できる。
【0079】
図7、図8には、土質改良材中のバインダー骨材粒子含有量と透水性との関係を調べた実験結果を示す。
【0080】
土は砂分、礫分等から構成されるが、土の透水性は粗砂〜細礫成分の含有割合に大きく影響されると考えられる。これについて、本発明者は、各種天然土についての粒度分析および透水試験により、高い透水性を示す土は、粗砂〜細礫成分の含有量が高いことを確認している。そこで、本発明では、粗砂〜細礫に相当する粒径のバインダー骨材粒子、すなわち粒径0.425〜4.75mmのバインダー骨材粒子の含有割合を調整することにより、土質改良材に十分な透水性を持たせるようにする。
【0081】
なお、土舗装においては、透水性と同時に、適当な締まりが求められるが、一般の土材料では、粗砂、細礫の含有割合が増加して粘土、シルト分の含有割合が減少すると、舗装時の締りが悪くなる傾向がある。しかし、上述したように、上水汚泥の場合、団粒構造(バインダー骨材粒子)を形成することにより、上水汚泥中に含まれる凝集材の作用で団粒同士が結合されるので、締まりの点でも十分な品質が得られる。
【0082】
図7には、上水汚泥におけるバインダー骨材粒子の含有割合と、透水係数との関係を調べた試験結果のである。また、図8は、図7の試験結果をグラフ化したものである。
【0083】
この透水試験では、供試体を24時間に渡って水浸飽和させた後、供試体上部から透水し、所定時間経過後の透水量を計測し、これに基づいて、15℃における透水係数を算出する。供試体としては、バインダー骨材粒子の含有率を異ならせた10種類の上水汚泥について、自然乾燥させた後に最適含水比近くに水分を調整し、直径8cm、高さ8cmの円柱体としたもの(試験番号1〜10)を用いる。ここでは、試験番号6〜10の供試体が実施形態1の実施例19〜23であり、その他の試験番号の供試体は比較例である。
【0084】
およびグラフから分かるように、無処理の上水汚泥(試験番号1)、細砂に粉砕しただけの上水汚泥(試験番号2)では、バインダー骨材粒子の含有率は低く(それぞれ、4.6重量%、5.3重量%)、透水係数も低い(それぞれ、1.04×10−5cm/s、6.87×10−6cm/s)。これに対して、上水汚泥にバインダー骨材粒子を形成すると(試験番号3〜8)、バインダー骨材粒子の含有率を高めるほど透水係数が向上し、特に、バインダー骨材粒子の含有割合が50〜60重量%となったところで、透水係数の急激な向上が見られる。具体的に、試験番号5(バインダー骨材粒子含有率=43.2重量%)では透水係数が7.76×10−4cm/sであったのが、試験番号6(バインダー骨材粒子含有率=55.1重量%)では透水係数が1.74×10−3cm/sとなり、十分な透水性を示すものとなっている。
【0085】
以上から、粒径0.425mm以上、4.75mm以下のバインダー骨材粒子が上水汚泥中に50重量%以上含有されるように、バインダー骨材粒子を形成することにより、土質改良材(バインダー骨材粒子形成後の上水汚泥)に十分な透水性を持たせることができると考えられる。
【0086】
図9〜図11には、土質改良材と土材料の混合割合による耐水性効果および舗装面の硬さを調べるために行った試験結果をで示す。
【0087】
この試験では、ランマーで突き固め処理を施した直径10cm、高さ6cmの供試体についてまず4日間の気乾養生後、硬度を測定する。その後、供試体を24時間水浸させ、供試体の耐水状況を観察する。24時間後、供試体の形が崩壊しない場合、耐水性効果があると評価する。なお、供試体は、土質改良材を3種類の土材料(真砂土、荒木田土、緑色スクリ一二ングス)にそれぞれ混合して作成し、各土材料に対して土質改良材の混合割合の異なる10種類をそれぞれ作成した。
【0088】
また、本試験における硬度測定は、山中式貫入器を用いて行った。したがって、においては、硬度が硬度指数で表現されている。ここで硬度指数(mm)と支持力強度(Pa)の関係は次の通りである。
支持力強度=100×硬度指数/{0.7952×(40−硬度指数)
このように支持力強度は硬度指数(内の数値)が大きいほど大きくなる。
【0089】
図9には、混合土材料が真砂土である供試体についての試験結果を示す。ここでは、試験番号5、6の供試体が図1に示す実施形態3の実施例1、2であり、試験番号7、8の供試体が参考例であり、その他の試験番号の供試体が比較例である。
【0090】
から分かるように、土質改良材の混合比が15%に満たない場合(試験番号1〜3号)、水浸後供試体は完全に崩壊してしまい、耐水性はほとんどないといえる。また、混合比が15%の場合(試験番号4)、水浸後供試体は大部分崩壊したが、24時間の間に一定の耐水性効果が認められ、土質改良材の混合割合が不足すると考えられる。これに対して、混合比が20%以上になると(試験番号5〜10)、混合比20%の5号で水浸24時間後に供試体の表面が少し軟弱化した以外は、供試体の崩壊は見られず、耐水性効果があることが確認された。
【0091】
つぎに、これらの供試体の硬度指数を検討すると、試験番号5〜8の供試体では、32mm前後の適当な硬さが得られた。これに対して、試験番号9〜10の供試体では、硬度指数が34〜35.5mmまで増大してしまい、一般的な目的で使用されるグランドとしては硬いという感じを与えてしまうといえる。この結果から、真砂土(砂質土)と土質改良材を混合する場合、土質改良材の混合比を20%以上50%以下にすれば、耐水性を保ちながら、舗装面に適当な硬さを持たせることができると考えられる。
【0092】
図10には、混合土材料が荒木田土である供試体についての試験結果を示す。ここでは、試験番号6〜8の供試体が図1に示す実施形態2の実施例1〜3であり、その他の試験番号の供試体が比較例である。図から分かるように、混合土材料が荒木田土の場合も、真砂土の場合と略同様な結果が得られたが、荒木田土の粒子が細かいことから、土質改良材の混合比が20%の供試体(試験番号5号)では、水浸24時間後一部崩壊が見られ、耐水性が十分とは言えない。したがって、荒木田土(粘性土)を混合土材料として土質改良材と混合する場合、土質改良材の混合比を30%以上50%以下にするのが適切と考えられる。
【0093】
図11には、混合土材料が緑色スクリーニングスである供試体についての試験結果を示す。ここでは、試験番号5〜7の供試体が図1に示す実施形態4の実施例1〜3であり、試験番号8の供試体が参考例であり、その他の試験番号の供試体が比較例である。図から分かるように、この場合も、真砂土の場合と略同様な結果が得られた。したがって、緑色スクリーニングス(岩石スクリーニングス)を混合土材料とする場合には、真砂土の場合と同様に、土質改良材の混合比を20%以上50%以下にすればよいと考えられる。
【0094】
図12〜図20には、土質改良材と各種土材料の混合土の透水性を十分に高いものとするために、土質改良材におけるバインダー骨材粒子の含有割合をどのように調整すればよいかを調べた試験結果を示す。
【0095】
これらの試験では、自然乾燥させた各種土材料(砂質土(真砂土)、粘性土、岩石スクリーニングス(緑色スクリーニングス))を土質改良材(試料毎にバインダー骨材粒子含有率を異ならせる)と混合し、最適含水比近くに水分を調整して、直径8cm、高さ8cmの円柱体を作成して供試体とする。この供試体を24時間に渡って水浸飽和させた後、供試体上部から透水し、所定時間経過後の透水量を計測し、これに基づいて透水係数を算出する。また、透水試験を行った供試体については粒度試験を行い、供試体中の粗砂細礫分(粒径0.425〜4.75mmの粒子)の割合を調べた。
【0096】
図12には、混合土材料を砂質土である真砂土とした場合の試験結果を示す。また、図13、図14には、この試験結果をグラフ化して示す。
【0097】
本試験において、土質改良材との混合前の真砂土としては、粗砂細礫分の割合が47.9重量%、粘土・シルト分が23.8重量%。透水係数が4.91×10−5cm/sのものを用いた。この真砂土に対して、土質改良材を20%および30%の混合比で混合して供試体とする。なお、この混合比は、図9の試験で砂質土に対する土質改良材の混合比は20〜30パーセントが適切であると結論されたことに基づき、この上限値と下限値を採ったものである。即ち、図9に示す実施形態3の実施例1、2の土質改良材におけるバインダー骨材粒子の含有割合を種々調整した試験結果である。
【0098】
まず、土質改良材の混合比が20%の供試体(試料1〜8)について検討すると、図12、図13から分かるように、供試体における土質改良材中のバインダー骨材粒子含有率が略50重量%を超えたあたりから(試料4〜5)、透水係数が目立って向上した。また、土質改良材の混合比が30%の供試体(試料9〜16)でも、図12、図14から分かるように、土質改良材のバインダー骨材粒子含有率が50重量%を超えると(試料12〜13)、供試体の透水係数が目立って向上した
【0099】
この結果から、土質改良材を真砂土(砂質土)と混合する場合、混合土に適当な透水性能を確保するため、土質改良材中のバインダー骨材粒子の含有量を50〜65重量%に調整することが適当であると結論できる。
【0100】
図15には、混合土材料を粘性土とした場合の試験結果を示す。また、図16、図17には、この試験結果をグラフ化して示す。
【0101】
本試験において、土質改良材との混合前の粘性土としては、粗砂細礫分の割合が35.7重量%、粘土・シルト分が38.4重量%。透水係数が5.13×10−6cm/sのものを用いた。この粘性土に対して、土質改良材を30%および50%の混合比で混合して供試体とする。なお、この混合比は、図10の試験で粘性土に対する土質改良材の混合比は30〜50パーセントが適切であると結論されたことに基づき、この上限値と下限値を採ったものである。即ち、図10に示す実施形態2の実施例1および3の土質改良材におけるバインダー骨材粒子の含有割合を種々調整した試験結果である。
【0102】
まず、土質改良材の混合比が30%の供試体(試料1〜9)について検討すると、図15、図16から分かるように、供試体における土質改良材のバインダー骨材粒子含有率が略65重量%を超えたあたりから(試料5〜6)、透水係数が目立って向上した。また、土質改良材の混合比が50%の供試体(試料10〜18)でも、図15、図17から分かるように、土質改良材中のバインダー骨材粒子含有率が65重量%を超えると(試料14〜15)、供試体の透水係数が目立って向上した
【0103】
この結果から、土質改良材を粘性土と混合する場合、混合土に適当な透水性能を確保するため、土質改良材中のバインダー骨材粒子の含有量を65〜75重量%に調整することが適当であると結論できる。
【0104】
図18には、混合土材料を岩石スクリーニングスである緑色スクリーニングスとした場合の試験結果を示す。また、図19、図20には、この試験結果をグラフ化して示す。
【0105】
本試験において、土質改良材との混合前の緑色スクリーニングスとしては、粗砂細礫分の割合が47.0重量%、粘土・シルト分が17.5重量%、透水係数が6.78×10−5cm/sのものを用いた。この緑色スクリーニングスに対して、土質改良材を20%および40%の混合比で混合して供試体とする。なお、この混合比は、図11の試験で緑色スクリーニングスに対する土質改良材の混合比は20〜40パーセントが適切であると結論されたことに基づき、この上限値と下限値を採ったものである。即ち、図11に示す実施形態4の実施例1および3の土質改良材におけるバインダー骨材粒子の含有割合を種々調整した試験結果である。
【0106】
まず、土質改良材の混合比が20%の供試体(試料1〜7)について検討すると、図18、図19から分かるように、供試体における土質改良材のバインダー骨材粒子含有率が60〜70重量%を超えたあたりから(試料5〜6)、透水係数の目立った向上が見られた。また、土質改良材の混合比が40%の供試体(試料10〜18)でも、図18、図20から分かるように、土質改良材中のバインダー骨材粒子含有率が略60重量%を超えると(試料12)、供試体の透水係数が目立って向上した。
【0107】
この結果から、土質改良材を緑色スクリーニングスと混合する場合、混合土に適当な透水性能を確保するため、土質改良材中のバインダー骨材粒子の含有量を60〜70重量%に調整することが適当であると結論できる。
【0108】
なお、土質改良材中のバインダー骨材粒子の含有量が多すぎると(例えば75重量%を超えると)、土材料との混合時に薄膜を形成すべき細粒分(0.425mm以下の粒子)の割合が不足してしまう。このため、上記土質改良材中のバインダー骨材粒子の含有量範囲は、いずれも75重量%以下に制限している。
【0109】
また、土質改良材と混合する土材料の粗砂細礫分が少なく、土質改良材に上限のバインダー骨材粒子含有率(例えば75重量%)を持たせても、混合土における粗砂細礫分の割合が十分に高まらない場合には、土材料を、他の粗砂細礫分の多い土材料と混合する等、適当な粒度調整をするとよい。
【0110】
図21〜図23には、土質改良材と各種土材料の混合物の締固め度合いと、土質改良材の含水比との関係を調べた試験の結果をで示す。
【0111】
なお、舗装面の締固め度合いは、この舗装面の硬さ、使用に対する耐久性、使用時の感触などに大きな影響を与えるもので、締固め度合いが適当かどうかは施工中に重要なポイントとなる。
【0112】
締固め度合いは、土材料の含水比により大きく影響を受け、含水比が少ないと、土材料の粒子同士の間の水による互いの結つきが弱いので、転圧しても十分に締固まらない。逆に、含水比が多いと、転圧時に粒子間の水が圧力により周辺に移動しやすく、結局、舗装面に窪み等の不具合が生じてしまう。また、乾燥後、舗装面にひび割れが発生しやすい。
【0113】
このように、舗装材の含水比調整は、適当な締固め度合いを得るために極めて重要である。特に、本発明のように複数材料の混合物により舗装面を形成する場合、各材料の含水状況が、混合物の含水比に対して複雑に影響するので、水分調整には特に気を使う必要がある。本試験は、このような観点から、代表的な舗装用土材料(真砂土、荒木田土、緑色スクリーニングス)の様々な含水状況に対して、土質改良材の最適な含水比を求めるために行ったものである。
【0114】
この試験では、まず、土材料と土質改良材の混合物について、突き固め法により最適含水比(締固め度合いが最適となる含水比)を求める。この最適含水比を目安にして、土材料の含水比に対する土質改良材の含水比を、混合物の含水比が最適含水比の前後10%程度に収まるように、調整する。この混合物により供試体を作成し、締固め度合いをチェックする。
【0115】
具体的には、混合物をランマーで25回/3層で突き固め、直径10cm、高さ12.7cmの円柱体を作成して供試体とする。作成直後の供試体にゴルフボールを1mの高さから供試体の上面に落下させ、供試体表面のゴルフボール落下による窪みの有無をチェックし、また、供試体乾燥後の収縮を観察する。なお、試験は、土材料の含水比、土質改良材の混合割合を異ならせた複数の供試体について行う。
【0116】
図21には、混合土材料を真砂土とした場合の試験結果を示す。
【0117】
真砂土70%と土質改良材30%の混合物の場合、最適含水比は25.8%である。真砂土は砂質土であり、細砂以上の粒子の割合が70%以上を占め、比表面積が比較的小さいため、含水比の変動範囲は狭い(5〜15%)。これに合わせて、含水比5%、10%、15%の真砂土について、供試体を作成する。また、土質改良材の混合割合は、20%〜40%とする(図9参照)。即ち、図9に示す実施形態3の実施例1、2の混合物の締固め度合いと土質改良材の含水比との関係を調べた結果である。そして、土質改良材を20%混合した試験番号1〜6内で試験番号3〜5が実施例1−1〜実施例1−3であり、その他の試験番号の供試体は比較例である。また、土質改良材を30%混合した試験番号7〜10内で試験番号8が実施例2−1であり、試験番号9が参考例であり、その他の試験番号の供試体は比較例である。土質改良材を40%混合した試験番号11、12の供試体も比較例である。
【0118】
土質改良材の混合比は20%の場合(試験番号1〜6)について検討すると、土質改良材の含水比を70%以上110%以下に調整した場合(試験番号3〜5)、供試体には適当な締固め度合いが得られた。即ち、ゴルフボールの落下試験による窪みが生じず、乾燥後の収縮も生じなかった。これら供試体の含水比は26%前後であって、最適含水比に近い値であった。
【0119】
一方、土質改良材の含水比を120%および150%に調整した供試体(試験番号1および2)には、窪みが生じ、適当な締固め度合いが得られなかった。これらの供試体の含水比は、いずれも最適含水比より高くなっていた。また、土質改良材の含水比を60%に調整した試験番号6の供試体の場合、含水比が24%と低いため、混合物の締まりが悪くなった。
【0120】
この結果から、土質改良材を20%の混合比で真砂土と混合する場合、土質改良材の含水比を70%以上110%以下に調整することにより、適当な締固め度合いを有する舗装面の形成ができると結論できる。
【0121】
次に、土質改良材の混合比を30%とする場合について検討すると、土質改良材の含水比を60%以上75%以下にした試験番号8、9の供試体では、適当な締固め度合いが得られ、供試体には窪みもひび割れも生じなかった。これらの供試体の含水比は25〜26%であり、最適含水比に近い値となっていた。
【0122】
一方、土質改良材の含水比を85%に調整した試験番号7の供試体は、真砂土の含水比が最低の5%の場合でも、窪みが生じた。この供試体の含水比は29%で、最適合水比より高くなっていた。また、土質改良材の含水比を60%に調整し、真砂土の含水比を15%に調整した試験番号10の供試体も、窪みが生じ、混合物の含水比は28.9%であった。
【0123】
したがって、土質改良材の混合比が30%の場合、土質改良材の含水比を60〜75%に調整することにより、適当な締固め度合いを有する舗装面の形成ができると結論できる。
【0124】
次に、土質改良材の混合比を40%とした場合について検討すると、真砂土の含水比が最低の5%であるのに対して、土質改良材の含水比を60%とした供試体(試験番号12)については、適当な締固め度合いが得られたが、土質改良材の含水比を70%とした供試体(試験番号11)については、窪みが生じ、適当な締固め度合いが得られなかった。この試験番号11の供試体の含水比は31%であり、最適含水比よりも高い値となっていた。
【0125】
したがって、土質改良材の混合比が40%の場合には、真砂土の含水比が最低の5%であっても、土質改良材の含水比を最低限度の60%にしなければならず、適当な締固め度合いを有する舗装面を形成するのは容易でないと言える。
【0126】
以上から、土質改良材を20%〜30%の混合比で砂質土(例えば真砂土)と混合する場合、適当な締固め度合いを得るためには、含水比を70〜110%に調整することが必要である。
【0127】
図22には、混合土材料を荒木田土とした場合の試験結果を示す。
【0128】
荒木田土70%と土質改良材30%の混合物の場合、最適含水比は35.2%である。荒木田土は粘性土であり、粘土とシルト質の割合が50%以上を占め、比表面積が大きいため、含水状況はかなり大きな範囲(5〜25%)で変化する。この変動範囲に合わせて、含水比5%、10%、15%、20%、25%の荒木田土について供試体を作成する。この場合、土質改良材の混合割合は、30%、40%、50%とする(図10参照)。即ち、図10に示す実施形態2の実施例1〜3の混合物の締固め度合いと土質改良材の含水比との関係を調べた結果である。そして、土質改良材を30%混合した試験番号1〜6内で試験番号2〜6が実施例1−1〜実施例1−5であり、その他の試験番号の供試体は比較例である。また、土質改良材を40%混合した試験番号7〜12内で試験番号8〜11が実施例2−1〜実施例2−4であり、その他の試験番号の供試体は比較例である。さらに、土質改良材を50%混合した試験番号13〜16内で試験番号14、15が実施例3−1〜実施例3−2であり、その他の試験番号の供試体は比較例である。
【0129】
まず、土質改良材の混合比が30%の場合(試験番号1〜6号)について検討すると、土質改良材の含水比を60%以上105%以下に調整した供試体(試験番号2〜6号)では、適当な締固め度合いが得られた。即ち、ゴルフボールの落下試験による窪みが生じず、乾燥後の収縮も生じなかった。これらの供試体は、いずれも最適含水比に近い値をとるものであった。
【0130】
一方、土質改良材の含水比を115%に調整した試験番号1の供試体には、窪みが生じ、適当な締固め度合いが得られなかった。この場合、荒木田土の含水比は5%で、想定される最も低い含水比のものであったが、供試体の含水比は38.3%で、最適含水比よりも高いものとなっていた。また、には示さないが、土質改良材の含水比を60%よりも低くすると、耐水性が失われ、混合物の締まりも悪くなる。
【0131】
この結果から、土質改良材を30%の混合比で荒木田土と混合する場合には、土質改良材の含水比を60%以上105%以下に調整することにより、適当な締固め度合いを有する舗装面が形成できると結論できる。
【0132】
次に、土質改良材の混合比を40%の場合(試験番号7〜12号)について検討すると、土質改良材の含水比を60%以上80%以下に調整した供試体(試験番号8〜11号)では、適当な締固め度合いが得られ、供試体には窪みもひび割れも生じなかった。これらの供試体の含水比は、35〜36%であり、最適含水比に近い値をなっていた。
【0133】
一方、含水比を90%に調整した試験番号7の供試体は、荒木田土の含水比が最低の5%の場合でも、かなりの窪みが生じた。また、乾燥後には、多少のひびが発生した。この供試体の含水比は39%で、最適含水比よりかなり高くなっていた。また、土質改良材の含水比を55%とした試験番号12の供試体では、耐水性が失われた。
【0134】
したがって、土質改良材の混合比が40%の場合、土質改良材の含水比を60〜80%に調整することにより、適当な締固め度合いを有する舗装面の形成ができると結論できる。
【0135】
次に、土質改良材の混合比を50%とした場合について検討すると、土質改良材の含水比を60%以上、65%以下にした試験番号14および15号の供試体では、適当な締固め度合いが得られ、供試体には窪みもひび割れも生じなかった。これらの供試体の含水比は35〜36%であり、最適含水比に近い値となっていた。
【0136】
一方、含水比を70%以上に調整した試験番号13の供試体には、窪みが生じた。この供試体の含水比は39%で、最適含水比より高いものとなっていた。また、荒木田土の含水比を15%とした場合(試験番号16)、土質改良材の含水比を最低限度の60%に調整しても、供試体には窪みが生じ、また乾燥するとひびが生じ、適当な締固め度合いが得られなかった。
【0137】
したがって、土質改良材の混合比が50%の場合、土質改良材の含水比を60〜65%に調整することにより、適当な締固め度合いを有する舗装面の形成ができると結論できる。
【0138】
以上から、土質改良材を30%〜50%の混合比で粘性土(例えば荒木田土)と混合する場合、適当な締固め度合いを得るために、含水比を60〜105%に調整することが必要である。
【0139】
図23には、混合土材料を緑色スクリーニングスとした場合の試験結果を示す。
【0140】
緑色スクリーニングス70%と土質改良材30%の混合物の場合、最適含水比は27.8%である。緑色スクリーニングスは粘土とシルト質の割合が30〜35%位、比表面積は中程度、含水比の変動範囲は5〜15%である。これに合わせて、含水比5%、10%、15%の真砂土について、供試体を作成する。また、土質改良材の混合割合は、20〜50%に設定する(図11参照)。即ち、図 11に示す実施形態4の実施例1〜3の混合物の締固め度合いと土質改良材の含水比との関係を調べた結果である。そして、土質改良材を20%混合した試験番号1〜6内で試験番号3〜5が実施例1−1〜実施例1−3であり、その他の試験番号の供試体は比較例である。また、土質改良材を30%混合した試験番号7〜10内で試験番号8〜10が実施例2−1〜実施例2−3であり、その他の試験番号の供試体は比較例である。土質改良材を40%混合した試験番号11〜13内で試験番号13が実施例3−1であり、その他の試験番号の供試体は比較例である。さらに、土質改良材を50%混合した試験番号14、15の供試体は比較例である。
【0141】
土質改良材の含水比を80%以上、120%以下に調整した試験番号3〜5の供試体では、適当な締固め度合いが得られ、ゴルフボールの落下試験による窪みが生じず、乾燥後の収縮も生じなかった。これらの供試体の含水比は28%位で、最適含水比に近い値であった。
【0142】
一方、土質改良材の含水比が130%の供試体(試験番号2)および含水比が150%の供試体(試験番号1)には、窪みが生じ、適当な締固め度合いが得られなかった。これらの含水比は30〜34%、最適含水比より高くなっていた。また、土質改良材の含水比を70%以下に調整した試験番号6の供試体は、締まりが悪く、含水比も低かった(26%)。
【0143】
この結果から、土質改良材を20%の混合比で緑色スクリーニングスと混合する場合、土質改良材の含水比を80%以上、120%以下に調整することにより、適当な締固め度合いを有する舗装面の形成ができると結論できる。
【0144】
次に、土質改良材の混合比を30%とした場合について検討すると、土質改良材の含水比を60%以上、80%以下にした試験番号8〜10の供試体では、適当な締固め度合いが得られ、供試体の窪みもひび割れも生じなかった。これらの供試体の含水比は27〜28%であり、最適含水比に近い値であった。
【0145】
一方、含水比を90%以上に調整した試験番号7の供試体は、緑色スクリーニングスの含水比が最低の5%の場合でも、窪みが生じ、含水比は31%で最適含水比より高くなっていた。
【0146】
したがって、土質改良材の混合比が30%の場合には、土質改良材の含水比を60〜80%に調整することにより、適当な締固め度合いを有する舗装面の形成ができる。
【0147】
次に、土質改良材の混合比を40%とした場合について検討すると、土質改良材の含水比を60%にした試験番号13の供試体では、適当な締固め度合いが得られた。一方、土質改良材の含水比を65%以上とした供試体(試験番号11、12)は、窪みが生じ、含水比も29〜31%で、最適含水比より高い値となった。したがって、土質改良材の混合比が40%の場合には、適切な締固め度合いを得るためには、土質改良材の含水比を60%に調整する必要がある。
【0148】
次に、土質改良材の混合比を50%とした場合について検討すると、土質改良材の含水比を最低限度の60%、緑色スクリーニングスの含水比を最低の5%に調整しても(試験番号14および15)、供試体は、窪みが生じたり、乾燥するとひびが生じ、適当な締固め度合いが得られなかった。これらの供試体の含水比は33〜38%で、最適含水比より高かった。したがって、土質改良材の混合比が50%では、適当な締固め度合いを得るのは難しいと考えられる。
【0149】
以上から、土質改良材を20〜40%の混合比で岩石スクリーニングス(例えば緑色スクリーニングス)と混合する場合、適当な締固め度合いを得るためには、含水比を60〜120%に調整することが必要である。
【図面の簡単な説明】
【図1】各種舗装用土材料と土質改良材を、最適混合効果が得られるように混合した例を示すである。
【図2】バインダー骨材粒子形成に最適な含水比を調べるために行った試験結果を示すである。
【図3】上水汚泥中のバインダー骨材粒子の耐水性試験結果を示すである。
【図4】バインダー骨材粒子を形成した上水汚泥の透水性向上効果を確認するための透水試験結果をで示す。
【図5】バインダー骨材粒子の耐水性効果と上水汚泥の含水比との関係を調べるために行った水浸試験結果を示すである。
【図6】上水汚泥の加熱乾燥による脱臭試験結果を示すである。
【図7】土質改良材中のバインダー骨材粒子含有量と透水性との関係についての試験結果を示すである。
【図8】土質改良材中のバインダー骨材粒子含有量と透水性との関係についての試験結果を示すグラフである。
【図9】土質改良材と土材料(真砂土)の混合割合による耐水性効果および舗装面の硬さを調べるために行った試験結果を示すである。
【図10】土質改良材と土材料(荒木田土)の混合割合による耐水性効果および舗装面の硬さを調べるために行った試験結果を示すである。
【図11】土質改良材と土材料(緑色スクリーニングス)の混合割合による耐水性効果および舗装面の硬さを調べるために行った試験結果を示すである。
【図12】土質改良材のバインダー骨材粒子含有率と、土質改良材と真砂土の混合土の透水係数との関係を調べた試験結果を示すである。
【図13】土質改良材のバインダー骨材粒子含有率と、土質改良材と真砂土の混合土(土質改良材の混合率20%)の透水係数との関係を調べた試験結果を示すグラフである。
【図14】土質改良材のバインダー骨材粒子含有率と、土質改良材と真砂土の混合土(土質改良材の混合率30%)の透水係数との関係を調べた試験結果を示すグラフである。
【図15】土質改良材のバインダー骨材粒子含有率と、土質改良材と粘性土の混合土の透水係数との関係を調べた試験結果を示すである。
【図16】土質改良材のバインダー骨材粒子含有率と、土質改良材と粘性土の混合土(土質改良材の混合率30%)の透水係数との関係を調べた試験結果を示すグラフである。
【図17】土質改良材のバインダー骨材粒子含有率と、土質改良材と粘性土の混合土(土質改良材の混合率50%)の透水係数との関係を調べた試験結果を示すグラフである。
【図18】土質改良材のバインダー骨材粒子含有率と、土質改良材と緑色スクリーニングスの混合土の透水係数との関係を調べた試験結果を示すである。
【図19】土質改良材のバインダー骨材粒子含有率と、土質改良材と緑色スクリーニングスの混合土(土質改良材の混合率20%)の透水係数との関係を調べた試験結果を示すグラフである。
【図20】土質改良材のバインダー骨材粒子含有率と、土質改良材と緑色スクリーニングスの混合土(土質改良材の混合率40%)の透水係数との関係を調べた試験結果を示すグラフである。
【図21】土質改良材および土材料(真砂土)の含水比と、これらの混合物の締固め度合いとの関係を調べた試験の結果を示すである。
【図22】土質改良材および土材料(荒木田土)の含水比と、これらの混合物の締固め度合いとの関係を調べた試験の結果を示すである。
【図23】土質改良材および土材料(緑色スクリーニングス)の含水比と、これらの混合物の締固め度合いとの関係を調べた試験の結果を示すである。
[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a soil improvement material using tap water sludge and a soil pavement method.
[0002]
[Prior art]
Natural clay such as red clay, Arakida clay, and Masago clay is widely used in clay courts, which are widely used for outdoor sports facilities and school grounds. By using natural soil in this manner, a clay coat having a natural feel can be formed at low cost.
[0003]
However, since such a natural soil is mainly composed of silt or clay, it has a drawback that it tends to be muddy or muddy when it rains, and that dust tends to rise when the weather continues.
[0004]
In order to cover the above-mentioned disadvantages while maintaining the merits of natural soil, the applicant of the present invention disclosed in Japanese Patent No. 1556916 (Japanese Patent Publication No. 1-041762) a soil pavement using clean water sludge (water purification plant generated soil). Suggest a way. According to this soil pavement method, soil pavement having preferable properties of natural soil and excellent in durability and water resistance can be performed, and the maintenance of the earth pavement surface does not require much labor. In addition, tap water sludge can be effectively used as a filler for general pavement soil materials that are becoming difficult to collect.
[0005]
[Problems to be solved by the invention]
By the way, in the soil pavement method using tap water sludge, it is necessary to pulverize tap water sludge into fine particles of fine sand or less. in this case,
(1) Drying of water sludge and crushing
{Circle over (2)} A method is considered in which tap water sludge is broken down into fine particles on a pavement foundation by pressurization with a tire roller or the like in a state of containing water (containing 30 to 60% of water).
[0006]
However, the water content of tap water sludge is usually high, and particularly in recent years, the water content is often 70 to 80%. Also, when a dewatered cake is prepared by a dewatering device, the moisture content thereof varies considerably. For this reason, the above method (1) is technically quite difficult and has a high cost for implementation.
[0007]
Also, if the degree of drying of water sludge is increased due to crushing, the water resistance performance based on the coagulant in the water sludge will be lost, and the water resistance and durability of the soil pavement surface will be weakened. There is. Then, once the water resistance is lost from the water sludge, the water resistance cannot be restored even if water is added thereafter.
[0008]
In addition, water sludge pulverized into fine particles of fine sand or less forms a solid pavement surface by tightly bonding with soil particles, but because the particles are fine, sufficient water permeability cannot be obtained, There was a problem that it easily became dust.
[0009]
On the other hand, in the above method (2), it is necessary to considerably repeat the pressurizing operation, and it is difficult to pulverize due to the variation of the water content of the soil material mixed with the water sludge and the limit of the performance of the mixing machine. In many cases, the mixing of the soil material and the water sludge is not uniform, and it has been difficult to stably secure the desired water resistance and durability. In addition, when tap water sludge having a high water content is used for a construction site, an unpleasant odor may be generated due to organic substances contained in the tap water sludge.
[0010]
The present invention has been made in view of such problems, and provides a soil improving material which is easy to manufacture and has high water resistance and high water permeability, and a pavement method using the soil improving material. The purpose is to:
[0011]
[Means for Solving the Problems]
First departureMing is, Soil improvement material,The water sludge obtained from the water purification plant is adjusted to a water content near its plastic limit, and then the water sludge isParticle size 0.425mm~4.75mmParticle size rangeBinder aggregate particlesBut50% by weight or moreGranulated, and then formed by drying treatment in a range where the water content in the water sludge does not fall below the minimum water content limit, and is mainly composed of binder aggregate particles having a particle size range of 0.425 mm to 4.75 mm. From a coarse-grained part and a fine-grained part below itBecome.
[0012]
Second departureMing is,In the first invention, the water content in the vicinity of the plastic limit is 75 to 95%, and after being adjusted to that state, it is granulated..
[0014]
No.3DepartureMing is,In the first or second invention, the minimum water content ratio limit is 50%..
[0015]
No.4DepartureMing is,In the first to third inventions, the soil improvement material is:After the drying treatment, water is added to adjust the water content to 60% to 120%.Stored.
[0016]
No.5DepartureMing is,This is a pavement method in which water sludge obtained from a water treatment plant is The binder is adjusted to a water content near the boundary, and in that state, granulation is performed so that binder aggregate particles having a particle size range of 0.425 mm to 4.75 mm are contained by 50% by weight or more. A soil improvement material comprising a coarse-grained portion and a fine-grained portion which are binder aggregate particles mainly having a particle size range of 0.425 to 4.75 mm and dried in a range not lower than the minimum moisture content limit, or It consists mainly of coarse and fine particles, which are mainly binder aggregate particles, which are stored by adjusting the water content to 60% to 120% by adding water after the drying treatment.The soil improving material is mixed with the soil material at a volume ratio of 20 to 50% with respect to the whole mixture, and a pavement surface is formed using the mixture.
[0017]
No.6DepartureMing is,In the fifth invention, a cohesive soil is used as the soil material,The soil conditioner is mixed with the cohesive soil at a ratio of 30 to 50% by volume to the entire mixture, and the mixture is used to form a pavement surface.
[0018]
No.7DepartureMing is,6In the invention, the soil improving material is,The water content was adjusted to 60 to 105%.
No.8DepartureMing is,In the fifth invention, a sandy soil is used as the soil material,The soil conditioner is mixed with the sandy soil at a ratio of 20 to 30% by volume to the whole mixture, and a pavement surface is formed using the mixture.
[0019]
No.9DepartureMing is,8In the invention, the soil improving material is,The water content was adjusted to 70 to 110%.
[0020]
No.10DepartureMing is,In the fifth invention, rock screenings are used as the soil material,The soil conditioner is mixed with rock screenings at a volume ratio of 20 to 40% based on the whole mixture, and the mixture is used to form a pavement surface.
[0021]
No.11DepartureMing is,10In the invention, the soil improving material is,The water content was adjusted to 60 to 120%.
[0022]
Function and Effect of the Invention
In the first invention, binder aggregate particles (particles in which sludge particles are aggregated) are formed in tap water sludge to obtain a soil improvement material. In this case, the binder aggregate particles having a particle size of not less than 0.425 mm and not more than 4.75 mm are contained in an amount of 50% by weight or more based on the whole water sludge, thereby acting as an aggregate when mixed with the soil material. The binder aggregate particles of the appropriate size to be used are sufficiently secured in the soil conditioner. For this reason, when the pavement surface is formed by mixing the soil improvement material with the soil material, the particles of the soil material are formed of a thin film composed of fine-grained portions (portions not converted into binder aggregate particles) in the soil improvement material. And the soil particles are strongly bonded to each other through this thin film, while the coarse-grained portion (binder aggregate particle portion) in the soil quality improving material is interposed between the soil particles to connect the soil particles to each other. At the same time as bonding, an appropriate gap is formed between the soil particles (acting as an aggregate supporting the soil particles). This allows the pavement surface to have excellent water resistance and water permeability without causing mud since water can quickly penetrate into the lower layer from the gap between the soil particles during water immersion.
Also, after granulation, the volatile organic matter contained in the water sludge is volatilized by performing a drying treatment so that the water content in the water sludge does not fall below the minimum water content limit. Offensive odors caused by organic substances are removed.
[0023]
In the second invention,In addition to the effects of the first invention,Since the water content of the water sludge is adjusted to 75 to 95% to form binder aggregate particles, the water sludge has an optimum plasticity at a water content near the plastic limit, and has a slight external force. Thereby, the binder aggregate particle structure can be effectively formed.
[0025]
Also,3In the invention ofIn addition to the effects of the first or second invention,Since the drying treatment is performed in a range where the water content of the water sludge does not fall below 50% (the minimum water content limit), the degree of drying of the water sludge is excessively increased, and the water resistance by the coagulant contained in the water sludge is increased. Will not be lost. Therefore, the completed soil improvement material has excellent water resistance, and does not expand and collapse even when immersed in water.
[0026]
Also,4In the invention ofIn addition to the effects of the first to third aspects,Since appropriate water is added after the drying treatment, when pavement is performed using the soil improving material, the pavement surface does not become too hard, and an appropriate degree of compaction can be provided. In addition, it is possible to prevent the water resistance ratio from dropping below 50% during storage and the water resistance is lost.
[0027]
No.5,6,8,10According to the invention, since the soil improving material and the soil material are mixed at an appropriate mixing ratio, a pavement surface having an appropriate compaction degree can be formed. In addition, since the mixing ratio of the soil improvement material to the soil material is 50% or less by volume, the amount of waste soil generated by replacing the soil with the soil improvement material does not become too large, and the burden of waste soil disposal is reduced. Small enough.
[0028]
No.7,9,11According to the invention, since the water content ratio of the soil conditioner is appropriately adjusted, a pavement surface having an appropriate compaction degree can be formed.
[0029]
BEST MODE FOR CARRYING OUT THE INVENTION
Hereinafter, embodiments of the present invention will be described with reference to the accompanying drawings.
[0030]
In the present invention, binder aggregate particles are formed in water sludge collected from a water purification plant to obtain a soil improvement material. Here, the binder aggregate particles are particles in which sludge particles of tap water sludge are in an aggregated state. It functions as an aggregate for supporting the soil particles so that a gap is formed between the soil particles.
[0031]
The formation of binder aggregate particles in tap water sludge is performed as follows.
[0032]
First, the water content of the water sludge is adjusted to a water content of 75 to 95% in order to make the water sludge into a state in which binder aggregate particles are easily formed. As a result, the water content of the clean water sludge is adjusted to a value close to the plastic limit, and the plasticity is in an optimal state, and the binder aggregate particle structure is easily formed by a small external force. Further, the formed binder aggregate particles also maintain a stable shape without breaking.
[0033]
For example, if the water content of the clean water sludge is 95% or more, the water is evaporated by heating and evaporating the clean water sludge. In this case, volatile organic substances contained in the water sludge are also volatilized. Heat evaporation is performed by solar drying, ventilation drying in a greenhouse, or the like. For example, in the case of sun drying, on the factory premises, tap water sludge is spread at a thickness of 5 to 30 cm, and the water is gradually evaporated by stirring with a tractor every hour. Such heating evaporation treatment is continued until the water content is adjusted to 75 to 95% while measuring the water content of the water sludge every hour. The measurement of the water content is performed, for example, by using a water content-bulk specific gravity relationship curve prepared in advance.
[0034]
The water sludge whose water content has been optimally adjusted in this way is passed through a sneader (crusher) to form granules of 19 mm or less. Further, the tap water sludge particles passed through the sneader are sieved through a 10 mm sieve so that binder water particles having a predetermined particle size range (0.425 to 4.75 mm) are contained in the tap water sludge in an amount of 50% by weight or more. Adjust to In this case, the content ratio of the binder aggregate particles is measured by a measuring method according to the particle size analysis test method of the Japan Society of Geotechnical Engineers (JSF T131).
[0035]
The water sludge obtained by the above method is further spread on the site of the factory with a thickness of 5 to 10 cm, and dried again by the sun while stirring every hour. The water is evaporated to a predetermined value of 50% or more. Due to this evaporation, the volatile organic substances contained in the water sludge are almost volatilized, and the ultraviolet rays contained in the sunlight perform a bactericidal effect, so that the odor due to the volatile organic substances in the water sludge is eliminated. Can be. This drying treatment (deodorization treatment) can be performed by ventilation drying and ultraviolet sterilization in a greenhouse.
[0036]
In any of the above treatments including the drying treatment, the water content of the clean water sludge is periodically measured and controlled so as to be kept at 50% or more (minimum water content limit value). By maintaining the water sludge at a water content ratio equal to or higher than the minimum water content ratio limit value, water resistance performance can be maintained.
[0037]
The details will be described below. In a water purification treatment at a water purification plant, an aggregating agent (for example, PAC) is added to precipitate a suspension quickly. These flocculants react with the water molecules while simultaneously generating a large amount of positive charge and combining with the negatively charged suspension to form large flocs. The flocs settle to the bottom due to gravity. As a result, water sludge, which can be said to be a combination of the suspension and the flocculant, is generated. The flocculant that has reacted with the water molecules is converted into an aluminum hydroxide substance that is insoluble in water, and the effect of the aluminum hydroxide substance causes the water sludge to have strong water resistance.
[0038]
However, once the aluminum hydroxide material is depleted of water, it cannot react with water molecules again, cannot re-associate with other negatively charged materials, and does not dissolve in water They lose their properties. For this reason, in order to maintain the water resistance of clean water sludge, it is necessary for the water to always have a certain amount of water or more, which is the minimum water content ratio limit. By performing various treatments within a range not to fall below the minimum water content limit, it is possible to appropriately perform moisture adjustment and deodorization treatment while securing the water resistance of water sludge, and to form a high quality soil improvement material it can.
[0039]
Since the soil improving material thus dried has a low water content, an appropriate degree of compaction cannot be obtained as it is. In addition, during storage, the water content may be reduced to 50% or less by drying. Therefore, after the drying treatment, water is immediately added again to the soil improvement material, the water content is adjusted to 60% to 120%, and then stored.
[0040]
In the pavement, the soil improvement material thus obtained is mixed with a general pavement soil material, and a pavement surface is formed with the mixture.
[0041]
In this case, the particles of the pavement soil material are covered with a thin film composed of fine-grained portions (portions not converted into binder aggregate particles) in the soil improvement material, and the soil particles are strongly bonded to each other via the thin film. . On the other hand, the coarse-grained portion (binder-aggregate particle portion) in the soil-improving material acts as an aggregate supporting the soil particles while interposing between the soil particles and binding the soil particles. , Forming appropriate gaps between the soil particles. This allows the pavement surface to have excellent water resistance and water permeability without causing mud since water can quickly penetrate into the lower layer from the gap between the soil particles during water immersion.
[0042]
In mixing the soil improving material and the soil material, the mixing ratio of the soil improving material may be in the range of 20% to 50%. By setting the mixing ratio of the soil improving material to the entire mixture to 20% or more, it is possible to secure a sufficient amount of the soil improving material to completely cover the soil particles of the soil material. Further, by setting the mixing ratio to 50% or less, it is possible to prevent the pavement surface from being excessively mixed with the soil improvement material in a large amount, thereby preventing the pavement surface from becoming too hard. When the mixing ratio of the soil improvement material is 50% or less, the generation of waste soil due to the replacement of the soil improvement material with the soil material (local soil) can be relatively reduced, and the burden of waste soil treatment can be reduced.
[0043]
In the concrete mixing of the soil improving material and various pavement soil materials, the water content of the soil improving material to be mixed is determined based on the properties of the soil material (such as water content, particle size distribution, surface area, and optimal water content). The content ratio of the binder aggregate particles and the mixing ratio of the soil material and the soil improving material are adjusted so as to obtain the optimum mixing effect. Here, the optimal mixing effect means that when both are mixed, uniformity of mixing is ensured, and at the same time, the water resistance and water permeability of the pavement surface can be maximized, and an appropriate degree of compaction is obtained. Say that you can. Specifically, when the soil material and the soil improvement material are mixed, by adjusting the mixture so as to have an optimum water content, an appropriate degree of compaction can be obtained on the pavement surface.
[0044]
The mixing of the soil improving material and the pavement soil material is sufficiently performed by, for example, plant mixing until the mixing becomes uniform throughout. Alternatively, it may be performed by central mixing at the construction site.
[0045]
FIG. 1 shows an example in which various pavement soil materials and soil improvement materials are mixed to obtain an optimum mixing effect.FigureIt is.
[0046]
FigureAs shown in (1), when the soil material is cohesive soil (for example, Arakida soil, red soil, black soil, etc.), the water content is generally high (5 to 25%). In addition, since the clay and silt content occupies 50% or more and the surface area is large, it is difficult to mix with the soil improving material. For such a soil material, a soil improvement material adjusted to a water content of 60 to 105% and a binder aggregate particle content of 65 to 75% by weight is mixed at a mixing ratio of 30 to 50%.(Hereinafter, it is referred to as a second embodiment).
[0047]
When the soil material is sandy soil (for example, masago, mountain sand, etc.), the water content is generally low (5 to 15%). In addition, particles equal to or greater than fine sand occupy 70% or more, have a small surface area, and are easily mixed with the soil improving material. For such a soil material, a soil improvement material adjusted to a water content of 70 to 110% and a binder aggregate particle content of 50 to 65% is mixed at a mixing ratio of 20 to 30%.(Hereinafter, a third embodiment).
[0048]
When the soil material is rock screenings (eg, green screenings, limestone dust, etc.), the water content may be low to medium. In addition, the equivalent of clay and silt is close to 30%, the composition is more than fine sand, and the surface area fluctuates greatly. Therefore, mixing with the soil improving material has many uncertain factors. For such a soil material, a soil improvement material adjusted to a water content of 60 to 120% and a binder aggregate particle content of 60 to 70% is mixed at a mixing ratio of 20 to 40%.(Hereinafter, it is referred to as Embodiment 4).
[0049]
As described above, depending on the type of soil material, by adjusting the water content of the soil improvement material, the binder aggregate particle content, and the mixing ratio with the soil material, the mixture has an optimal water content, An optimal mixing effect is obtained. The experimental results supporting this are shown in the figure.9belowFigureIt will be explained together.
[0050]
Next, a description will be given of experimental results which prove that the present invention achieves the effects of improving the water resistance and water permeability of a pavement surface and eliminating an unusual odor.
[0051]
FIG. 2 shows the results of a test performed to determine the optimum water content for forming binder aggregate particles.FigureIt is.
[0052]
In this test, 0.425 to 4.25 liters of tap water sludge (test Nos. 1 to 12) having various water contents were crushed into particles of 19 mm or less by a crusher and passed through a 10 mm sieve. The binder aggregate particle content of 75 mm is measured.Here, the test specimens of Test Nos. 7 and 8 having a water content of 94% and 75% are Examples 1 and 2 of Embodiment 1, the test specimens of Test Nos. 6, 9 and 10 are reference examples, and Specimens with test numbers are comparative examples.The content of the binder aggregate particles is measured by a measuring method according to the particle size analysis test method of the Japan Society of Geotechnical Engineers (JSF T131).
[0053]
Hereinafter, the test results will be considered. First, in the test specimens of Test Nos. 1 to 6 having a large water content (all of which have a water content of 95% or more), since the water contained in the water sludge is too large, a large lump is easily formed. Binder aggregate particles are not easily formed. Further, once the binder aggregate particles are formed, the shape is not stable, and the aggregates again become large. As described above, for the specimen having a water content of more than 120%, a sufficient amount of binder aggregate particles is not formed, and the larger the water content, the smaller the amount of binder aggregate particles formed.
[0054]
On the other hand, even in the specimens of Test Nos. 10 to 12 having a small water content (all having a water content of 65% or less), a sufficient amount of binder aggregate particles was not formed (at most 53% by weight of Test No. 10). ) Also, the formed binder aggregate particles are easily broken by external force. This is because the plasticity of the water sludge is low because the water of the water sludge is small.
[0055]
On the other hand, in the specimens of Test Nos. 7 to 9 having a water content of 75 to 95% near the plastic limit, binder aggregate particles are easily formed, and the content of the binder aggregate particles is 50 to 70%. It becomes.
[0056]
From the above, it is understood that the formation of the binder aggregate particles is most easily performed when the water content is adjusted to 75 to 95%.
[0057]
FIG. 3 shows the results of the water resistance test on the binder aggregate particles.
[0058]
In this test, 100 g of binder aggregate particles of 2 to 4.75 mm were taken out from the tap water sludge (7 types of tap water sludge having different production areas) on which the binder aggregate particles were formed, dried, and then used in a beaker. Water immersion test. In the water immersion test, the binder aggregate particles immersed in water are stirred with a glass rod for 1 minute, and left standing for 24 hours to observe the collapse of the binder aggregate particles. After 24 hours, the sample in the beaker is passed through a 0.425 mm sieve, the residue is dried, and after weighing, the disintegration rate of the binder aggregate particles is calculated. When the binder aggregate particles hardly disintegrate after 24 hours, it can be evaluated as having water resistance. For comparison, the same test was performed on spherical particles (aggregates) of Arakida soil.Here, the samples of test numbers 1 to 7 are Examples 3 to 9 of the first embodiment, and the sample of test number 8 is a comparative example.
[0059]
FigureAs shown in Table 2, the seven samples of binder aggregate particles collected from tap water sludge all had a disintegration rate of 3% or less after 24 hours. On the other hand, the spherical particles of Arakida soil gradually began to expand and collapse after being immersed in water and stirred, and the collapse ratio after 24 hours became 95%, and most of the spherical particles collapsed.
[0060]
From this result, it can be seen that the binder aggregate particles of the tap water sludge have a strong property (water resistance) to water. This is due to the action of the coagulant contained in the water sludge as described above. Due to this water resistance, the binder aggregate particles can serve as an aggregate supporting gaps between the soil particles when the soil improvement material is mixed with a general soil material, and improve the water permeability of the pavement surface. Work.
[0061]
FIG. 4 shows the results of the permeability test of the soil improvement material.FigureIt is.
[0062]
In this test, after the specimen is saturated with water for 24 hours, water is permeated from the upper part of the specimen, and the water permeation amount after a lapse of a predetermined time is measured. Based on this, the hydraulic conductivity is calculated.
[0063]
As the specimen, a mixture of naturally dried masago and a 30% by volume mixture of tap water sludge was adjusted to have a water content close to the optimum water content to form a cylinder having a diameter of 8 cm and a height of 8 cm. Used. The types of test specimens were prepared for five types of clean water sludge having different binder aggregate particle contents (test numbers 1 to 5), and prepared for clean water sludge pulverized to fine sand or less (test number). 6) and those prepared by replacing tap water sludge with Arakida soil (formed with spherical particles) and masago soil, respectively (test numbers 7 and 8).Here, the test pieces with test numbers 2 to 5 are Examples 10 to 13 of the first embodiment, and the test pieces with other test numbers are comparative examples.
[0064]
FigureAs shown in the above, the test piece composed of clean water sludge having formed binder aggregate particles (Test Nos. 1 to 5) was a test piece composed of Arakida soil (Test No. 7) or a specimen composed only of masago soil. (Test No. 8) has much higher hydraulic conductivity. For example, in the test specimen of Test No. 7, since the spherical particles of Arakida soil are very weak in water and collapse immediately after being immersed in water, they are used as aggregates that support between sand sand particles like binder aggregate particles. It has no effect and the permeability is very low.
[0065]
In addition, when comparing specimens made of tap water sludge with binder aggregate particles formed therein, the permeability increases as the amount of binder aggregate particles in the tap water sludge increases.
[0066]
Also, in the specimen using tap water sludge, the binder having no aggregate particles formed and the specimen consisting of tap water sludge pulverized to fine sand or less (Test No. 6) has a permeability coefficient of pure sand. The test specimen (Test No. 8) is lower than the test specimen. This is considered to be because water sludge below fine sand blocks the gaps between the particles of the mixed sand.
[0067]
From the above, it can be seen that the formation of binder aggregate particles in tap water sludge significantly improves the water permeability of a mixture of this and soil material.
[0068]
FIG. 5 shows the results of a water immersion test conducted to investigate the relationship between the water resistance effect of binder aggregate particles and the water content of water sludge.FigureIndicated by
[0069]
In this exam,Formed binder aggregate particlesAfter appropriate addition of water to the tap water sludge, it is filled into a mold (4 cm × 3 cm × 0.7 cm), compacted, taken out, and dried at 110 ° C. for 24 hours to obtain a specimen. This specimen is submerged and the change of the specimen is observed. Check the disintegration time of the specimen within 24 hours and the state of softening of the specimen after 24 hours. In this test, ten types of clean water sludge having different water contents are used as test specimens.Here, the test specimens of test numbers 1 to 5 are Examples 14 to 18 of the first embodiment, the test specimen of test number 6 is a reference example, and the test specimens of other test numbers are comparative examples.
[0070]
According to the results of the water immersion test, the test pieces (test numbers 1 to 5) having a water content of 50% or more exhibited substantially sufficient water resistance. Specifically, the test specimens of Test Nos. 1 to 3 hardly collapsed and did not soften even after 24 hours of water immersion. In addition, the test specimen of Test No. 4 (water content ratio 63%) softened slightly, and the test specimen of Test No. 5 (water content ratio 52%) softened, but none of them collapsed.
[0071]
On the other hand, in the test specimens having a water content of 50% or less (test numbers 6 to 10), sufficient water resistance was not obtained. Specifically, the test specimens of Test Nos. 7 to 10 completely disintegrated within 24 hours. Also, the test specimen of Test No. 6 having the highest water content (water content 43%) showed partial collapse after 24 hours.
[0072]
From the above results, it can be concluded that the moisture content needs to be 50% or more in order for the soil improving material to have a sufficient water resistance effect.
[0073]
Fig. 6 shows the results of the deodorization test by heating and drying the water sludge.FigureIndicated by
[0074]
This test was conducted to confirm whether the off-flavor of tap water sludge can be canceled by a simple heating and evaporation method.
[0075]
In the test, 500 g of tap water sludge having a water content of about 150% was used as a test piece and heated in a constant temperature furnace. The unpleasant odor before and after heating is checked by human odor, and the intensity of the unpleasant odor is classified. The test is performed by dividing the heating temperature into 10 stages from 20 ° C. to 110 ° C., and performing the heating for 4 hours, 6 hours and 8 hours, respectively. The classification of the intensity of the off-flavor was determined on the basis of the feeling of the person who performed the test in four stages: considerable, worried, not much worried, and hardly worried.
[0076]
The test shows the following trends: First, in the case of the same heating time, the higher the heating temperature, the greater the amount of odor removal. Next, at the same heating temperature, the longer the heating time, the greater the amount of odor removal. Specifically, in the case of heating for 4 hours, a heating temperature of 70 ° C. is required to make the off-odor less noticeable. On the other hand, in the case of heating for 6 hours, the temperature dropped to 50 ° C., and in the case of heating for 8 hours, the temperature further dropped to 30 ° C. That is, it was found that the same deodorizing effect can be obtained at a low temperature for a long time as the deodorizing effect obtained at a high temperature for a short time. The latter is also a simpler and more effective deodorizing method, which can save capital investment and energy.
[0077]
Further, as shown in the test results, when the off-flavor is reduced to a level that is not so noticeable, the water content of the clean water sludge is approximately between 42 to 63%. That is, when the water content is reduced to nearly 50% by heating evaporation, the off-flavor of clean water sludge can be substantially eliminated.
[0078]
From this test result, it can be concluded that when deodorizing clean water sludge, a considerable deodorizing effect can be obtained by reducing the water content to near 50% while maintaining the temperature of 30 ° C. to 50 ° C. for 8 hours or more.
[0079]
FIG. 7 and FIG. 8 show experimental results obtained by examining the relationship between the binder aggregate particle content in the soil improvement material and the water permeability.
[0080]
The soil is composed of sand, gravel, etc., but the permeability of the soil is considered to be greatly affected by the content ratio of coarse sand to fine gravel components. In this regard, the present inventor has confirmed that soil exhibiting high water permeability has a high content of coarse sand to fine gravel components by particle size analysis and water permeability test of various natural soils. Therefore, in the present invention, by adjusting the content ratio of binder aggregate particles having a particle size corresponding to coarse sand to fine gravel, that is, a binder aggregate particle having a particle size of 0.425 to 4.75 mm, a soil improvement material is obtained. Ensure that it has sufficient water permeability.
[0081]
In soil pavement, appropriate tightening is required at the same time as permeability, but in general soil materials, if the content of coarse sand and fine gravel increases and the content of clay and silt decreases, Tightening at the time tends to be worse. However, as described above, in the case of tap water sludge, the aggregates are bound by the action of the coagulant contained in the tap water sludge by forming the aggregate structure (binder aggregate particles), so that the sludge is tight. In this respect, sufficient quality can be obtained.
[0082]
FIG. 7 shows a test result of the relationship between the content ratio of binder aggregate particles in water sludge and the permeability coefficient.FigureIt is. FIG. 8 is a graph of the test result of FIG.
[0083]
In this water permeability test, the specimen was saturated with water for 24 hours, then permeated from the upper part of the specimen, and the amount of water permeation was measured after a lapse of a predetermined time. Based on this, the permeability coefficient at 15 ° C. was calculated. I do. As the test specimens, 10 kinds of water sludges having different contents of the binder aggregate particles were air-dried and then adjusted to a water content close to an optimum water content to obtain a cylindrical body having a diameter of 8 cm and a height of 8 cm. (Test Nos. 1 to 10) are used.Here, the test pieces with test numbers 6 to 10 are Examples 19 to 23 of the first embodiment, and the test pieces with other test numbers are comparative examples.
[0084]
FigureAs can be seen from the graph and in the graph, the untreated tap water sludge (test number 1) and the tap water sludge just crushed into fine sand (test number 2) have a low binder aggregate particle content (4. 6% by weight, 5.3% by weight) and low water permeability (1.04 × 10-5cm / s, 6.87 × 10-6cm / s). On the other hand, when binder aggregate particles are formed in tap water sludge (Test Nos. 3 to 8), the permeability increases as the content of binder aggregate particles increases, and in particular, the content ratio of binder aggregate particles increases. When the content reaches 50 to 60% by weight, a sharp improvement in the water permeability is observed. Specifically, in Test No. 5 (binder aggregate particle content = 43.2% by weight), the water permeability was 7.76 × 10-4cm / s, but in Test No. 6 (binder aggregate particle content = 55.1% by weight), the water permeability was 1.74 × 10-3cm / s, indicating sufficient water permeability.
[0085]
From the above, the binder aggregate particles were formed so that the binder aggregate particles having a particle size of 0.425 mm or more and 4.75 mm or less were contained in the water sludge by 50% by weight or more.MakeBy doing so, it is considered that the soil improving material (tap water sludge after forming the binder aggregate particles) can have sufficient water permeability.
[0086]
9 to 11 show the results of tests performed to examine the water resistance effect and the hardness of the pavement surface depending on the mixing ratio of the soil improvement material and the soil material.FigureIndicated by
[0087]
In this test, a test specimen having a diameter of 10 cm and a height of 6 cm, which has been subjected to tamping treatment with a rammer, is first air-cured for 4 days, and then the hardness is measured. Thereafter, the specimen is immersed in water for 24 hours, and the water resistance of the specimen is observed. If the shape of the specimen does not collapse after 24 hours, it is evaluated that there is a water resistance effect. Specimens were prepared by mixing soil improvement materials with three types of soil materials (masago, Arakida soil, green screenings), respectively, and the mixing ratio of the soil improvement materials was different for each soil material. Ten types were created respectively.
[0088]
The hardness measurement in this test was performed using a Yamanaka penetrator. Therefore,FigureIn, the hardness is represented by a hardness index. Here, the relationship between the hardness index (mm) and the bearing strength (Pa) is as follows.
Bearing strength = 100 × hardness index / {0.7952 × (40-hardness index)2
Thus, the bearing strength is determined by the hardness index (FigureThe larger the value in (), the larger the value.
[0089]
FIG. 9 shows the test results for a specimen in which the mixed soil material is a masago.Here, the test specimens of test numbers 5 and 6 are Examples 1 and 2 of Embodiment 3 shown in FIG. 1, the test specimens of test numbers 7 and 8 are reference examples, and the test specimens of other test numbers are It is a comparative example.
[0090]
FigureAs can be seen from the graph, when the mixing ratio of the soil improving material is less than 15% (Test Nos. 1 to 3), the test specimen completely collapses after water immersion, and it can be said that there is almost no water resistance. When the mixing ratio was 15% (Test No. 4), the test specimen collapsed after water immersion for the most part, but a certain water resistance effect was observed within 24 hours, and when the mixing ratio of the soil improvement material was insufficient. Conceivable. On the other hand, when the mixture ratio became 20% or more (test numbers 5 to 10), the specimen collapsed except that the surface of the specimen was slightly softened 24 hours after immersion in No. 5 with a mixture ratio of 20%. Was not observed, and it was confirmed that there was a water resistance effect.
[0091]
Next, when examining the hardness indices of these specimens, the specimens of Test Nos. 5 to 8 exhibited an appropriate hardness of about 32 mm. On the other hand, in the test specimens of Test Nos. 9 to 10, the hardness index increases to 34 to 35.5 mm, and it can be said that the ground used for general purposes is hard. From these results, it is found that when mixing the sand-improved soil and the soil-improving material, if the mixing ratio of the soil-improving material is set to 20% or more and 50% or less, the pavement surface can be appropriately hardened while maintaining water resistance. It is thought that it is possible to have.
[0092]
FIG. 10 shows the test results for a specimen in which the mixed soil material is Arakida soil.Here, the test pieces with test numbers 6 to 8 are Examples 1 to 3 of Embodiment 2 shown in FIG. 1, and the test pieces with other test numbers are comparative examples. FigureAs can be seen from the graph, when the mixed soil material was Arakita soil, the result was almost the same as that of the masago soil. However, since the particles of Arakida soil were fine, the mixing ratio of the soil improvement material was 20%. In the sample (Test No. 5), some disintegration was observed after 24 hours of water immersion, and the water resistance was not sufficient. Therefore, when mixing Arakita clay (cohesive soil) with a soil improvement material as a mixed soil material, it is considered appropriate to set the mixing ratio of the soil improvement material to 30% or more and 50% or less.
[0093]
FIG. 11 shows the test results for the test specimen in which the mixed soil material is green screenings.Here, the test pieces with test numbers 5 to 7 are Examples 1 to 3 of Embodiment 4 shown in FIG. 1, the test piece with test number 8 is a reference example, and the test pieces with other test numbers are comparative examples. It is. FigureAs can be understood from the above, in this case, the result was almost the same as that of the case of the masago. Therefore, when green screenings (rock screenings) are used as the mixed soil material, it is considered that the mixing ratio of the soil improvement material should be 20% or more and 50% or less as in the case of the masago.
[0094]
12 to 20 show how to adjust the content ratio of the binder aggregate particles in the soil improvement material in order to make the mixed soil of the soil improvement material and various soil materials sufficiently high in water permeability. This shows the test results of the examination.
[0095]
In these tests, naturally dried soil materials (sandy soil (mass sand), clayey soil, rock screenings (green screenings)) were used as soil improvement materials (binder aggregate particle content was varied for each sample). ), And adjust the water content to near the optimal water content to form a cylinder having a diameter of 8 cm and a height of 8 cm, which is used as a specimen. After the specimen is saturated with water for 24 hours, water is permeated from the upper part of the specimen, the amount of water permeated after a lapse of a predetermined time is measured, and the water permeability coefficient is calculated based on this. In addition, a particle size test was performed on the specimens that were subjected to the water permeability test, and the proportion of coarse sand fine gravel (particles having a particle diameter of 0.425 to 4.75 mm) in the specimens was examined.
[0096]
FIG. 12 shows the test results in the case where the mixed soil material was a sandy soil, a masago. 13 and 14 are graphs showing the test results.
[0097]
In this test, the ratio of coarse sand and fine gravel was 47.9% by weight and that of clay and silt was 23.8% by weight in the masago soil before being mixed with the soil improvement material. Permeability is 4.91 × 10-5cm / s. A sample is prepared by mixing a soil improvement material with the masago at a mixing ratio of 20% and 30%. The upper limit and the lower limit of the mixing ratio are determined based on the conclusion that the mixing ratio of the soil improving material to the sandy soil is preferably 20 to 30% in the test of FIG. is there.That is, it is a test result obtained by variously adjusting the content ratio of the binder aggregate particles in the soil improving materials of Examples 1 and 2 of Embodiment 3 shown in FIG.
[0098]
First, when the specimens (samples 1 to 8) in which the mixing ratio of the soil improving material is 20% are examined, as can be seen from FIGS. 12 and 13, the binder aggregate particle content in the soil improving material in the test material is approximately equal. From around 50% by weight (samples 4 and 5), the water permeability significantly improvesdid. Further, even in the specimens (samples 9 to 16) in which the mixing ratio of the soil improving material is 30%, as can be seen from FIGS. 12 and 14, when the binder aggregate particle content of the soil improving material exceeds 50% by weight ( Samples 12 and 13), the permeability of the test specimen was significantly improveddid.
[0099]
From this result, when the soil improving material is mixed with the masago (sandy soil), the content of the binder aggregate particles in the soil improving material is set to 50 to 65% by weight in order to secure appropriate water permeability to the mixed soil. It can be concluded that it is appropriate to adjust to.
[0100]
FIG. 15 shows a test result when the mixed soil material is a viscous soil. 16 and 17 show the test results in the form of graphs.
[0101]
In this test, the ratio of coarse sand and fine gravel was 35.7% by weight, and clay and silt was 38.4% by weight as the clay soil before being mixed with the soil improvement material. Permeability coefficient 5.13 × 10-6cm / s. This cohesive soil is mixed with a soil improvement material at a mixing ratio of 30% and 50% to obtain a specimen. The upper limit and the lower limit of the mixing ratio are determined based on the conclusion that the mixing ratio of the soil improving material to the clayey soil of 30 to 50% is appropriate in the test of FIG. .That is, it is a test result obtained by variously adjusting the content ratio of the binder aggregate particles in the soil improvement materials of Examples 1 and 3 of Embodiment 2 shown in FIG.
[0102]
First, when examining the specimens (samples 1 to 9) in which the mixing ratio of the soil improving material is 30%, as can be seen from FIGS. 15 and 16, the binder aggregate particle content of the soil improving material in the test material is approximately 65%. Permeability is remarkably improved from around the weight% (samples 5-6)did. Further, even in the specimens (samples 10 to 18) in which the mixing ratio of the soil improving material is 50%, as can be seen from FIGS. 15 and 17, when the binder aggregate particle content in the soil improving material exceeds 65% by weight. (Samples 14 and 15), the permeability of the test specimen was significantly improveddid.
[0103]
From this result, when mixing the soil improving material with the cohesive soil, it is possible to adjust the content of the binder aggregate particles in the soil improving material to 65 to 75% by weight in order to secure appropriate water permeability to the mixed soil. We can conclude that it is appropriate.
[0104]
FIG. 18 shows test results when the mixed soil material was green screenings, which are rock screenings. 19 and 20 are graphs showing the test results.
[0105]
In this test, as the green screenings before mixing with the soil improvement material, the proportion of coarse sand and fine gravel was 47.0% by weight, the content of clay and silt was 17.5% by weight, and the permeability was 6.78 ×. 10-5cm / s. This green screening is mixed with a soil improving material at a mixing ratio of 20% and 40% to obtain a test specimen. This mixing ratio is based on the upper limit and the lower limit based on the conclusion that the mixing ratio of the soil improving material to the green screenings of 20 to 40% is appropriate in the test of FIG. is there.That is, it is a test result obtained by variously adjusting the content ratio of the binder aggregate particles in the soil improvement materials of Examples 1 and 3 of Embodiment 4 shown in FIG.
[0106]
First, when examining specimens (samples 1 to 7) in which the mixing ratio of the soil improving material is 20%, as can be seen from FIGS. 18 and 19, the binder aggregate particle content of the soil improving material in the sample is 60 to 60%. From around 70% by weight (samples 5 and 6), a noticeable improvement in the water permeability was observed. Also, in the test specimens (samples 10 to 18) in which the mixing ratio of the soil improving material is 40%, as can be seen from FIGS. 18 and 20, the binder aggregate particle content in the soil improving material exceeds approximately 60% by weight. (Sample 12), the water permeability of the specimen was remarkably improved.
[0107]
From this result, soil improvement materialGreen screeningsIt can be concluded that it is appropriate to adjust the content of the binder aggregate particles in the soil conditioner to 60 to 70% by weight in order to secure appropriate water permeability to the mixed soil when mixing with the mixed soil.
[0108]
If the content of the binder aggregate particles in the soil quality improving material is too large (for example, more than 75% by weight), the fine particles (particles of 0.425 mm or less) to be formed into a thin film when mixed with the soil material. Ratio is insufficient. For this reason, the content range of the binder aggregate particles in the soil improvement material is limited to 75% by weight or less.
[0109]
In addition, even if the soil material mixed with the soil improving material has a small amount of coarse sand fine gravel, and the soil improving material has an upper limit of binder aggregate particle content (for example, 75% by weight), the coarse sand fine gravel in the mixed soil can be reduced. If the ratio of the minutes does not increase sufficiently, it is advisable to adjust the particle size appropriately, for example, by mixing the soil material with another soil material having a large amount of coarse sand and fine gravel.
[0110]
FIGS. 21 to 23 show the results of tests for examining the relationship between the compaction degree of the mixture of the soil improving material and various soil materials and the water content of the soil improving material.FigureIndicated by
[0111]
The degree of compaction of the pavement surface has a significant effect on the hardness of the pavement surface, durability against use, feel during use, etc.It is an important point during construction that the degree of compaction is appropriate. Become.
[0112]
The degree of compaction is greatly affected by the water content of the soil material, and if the water content is low, water particles between the soil material particles bind to each other.AndSince it is weak, it does not compact sufficiently even when it is rolled. Conversely, if the water content is high, the water between the particles tends to move to the periphery due to the pressure during compaction, and eventually causes a problem such as a depression on the pavement surface. Also, after drying,crackCracks easily occur.
[0113]
As described above, the adjustment of the water content of the pavement material is extremely important for obtaining an appropriate degree of compaction. In particular, when a pavement surface is formed with a mixture of a plurality of materials as in the present invention, the water content of each material has a complex effect on the water content of the mixture, so it is necessary to pay particular attention to moisture adjustment. . From this viewpoint, this test was performed to find the optimal water content ratio of the soil improvement material for various water content conditions of typical pavement soil materials (masago, Arakita soil, green screenings). Things.
[0114]
In this test, first, for a mixture of a soil material and a soil improvement material, an optimum water content ratio (a water content ratio at which the degree of compaction is optimal) is determined by a compaction method. Using this optimum water content as a guide, the water content of the soil improving material relative to the water content of the soil material is adjusted so that the water content of the mixture is about 10% before and after the optimum water content. A specimen is prepared from this mixture, and the degree of compaction is checked.
[0115]
More specifically, the mixture was tamped with a rammer 25 times / 3 layers to form a cylindrical body having a diameter of 10 cm and a height of 12.7 cm, which was used as a specimen. A golf ball is dropped from the height of 1 m onto the specimen just after the preparation, and the surface of the specimen is checked for dents due to the fall of the golf ball, and the shrinkage of the specimen after drying is observed. The test is performed on a plurality of specimens in which the water content ratio of the soil material and the mixing ratio of the soil improvement material are different.
[0116]
FIG. 21 shows a test result when the mixed soil material is masago.
[0117]
For a mixture of 70% masago and 30% soil conditioner, the optimum moisture content is 25.8%. The masago is a sandy soil, in which the ratio of particles equal to or greater than fine sand occupies 70% or more, and the specific surface area is relatively small, so that the fluctuation range of the water content is narrow (5 to 15%). In accordance with this, specimens are prepared for the masago soil having a water content of 5%, 10%, and 15%. Further, the mixing ratio of the soil improvement material is set to 20% to 40% (see FIG. 9).That is, it is the result of examining the relationship between the compaction degree of the mixture of Examples 1 and 2 of Embodiment 3 shown in FIG. 9 and the water content of the soil conditioner. Then, among Test Nos. 1 to 6 in which the soil improvement material was mixed at 20%, Test Nos. 3 to 5 are Examples 1-1 to 1-3, and test pieces with other test numbers are comparative examples. Also, among Test Nos. 7 to 10 in which 30% of the soil improvement material was mixed, Test No. 8 was Example 2-1; Test No. 9 was a reference example; and test pieces with other test numbers were comparative examples. . Specimens of Test Nos. 11 and 12 containing 40% of a soil improving material are also comparative examples.
[0118]
When the mixing ratio of the soil improvement material is 20% (test numbers 1 to 6), when the water content of the soil improvement material is adjusted to 70% or more and 110% or less (test numbers 3 to 5), Provided a suitable degree of compaction. That is, no dent was formed by the drop test of the golf ball, and no shrinkage after drying occurred. The water content of these test specimens was around 26%, which was close to the optimum water content.
[0119]
On the other hand, in the test specimens (test numbers 1 and 2) in which the water content of the soil conditioner was adjusted to 120% and 150%, depressions occurred, and an appropriate degree of compaction could not be obtained. The water content of each of these specimens was higher than the optimum water content. Further, in the case of the test sample of Test No. 6 in which the water content of the soil conditioner was adjusted to 60%, the compactness of the mixture was poor because the water content was as low as 24%.
[0120]
From this result, when the soil improvement material is mixed with masago at a mixing ratio of 20%, the water content of the soil improvement material is adjusted to 70% or more and 110% or less to obtain a pavement surface having an appropriate compaction degree. It can be concluded that formation is possible.
[0121]
Next, the case where the mixing ratio of the soil improvement material is set to 30% is examined. In the test specimens of Test Nos. 8 and 9 in which the water content of the soil improvement material is set to 60% or more and 75% or less, an appropriate compaction degree is determined. The sample is hollowcrackNo cracking occurred. The water content of these specimens was 25 to 26%, which was a value close to the optimum water content.
[0122]
On the other hand, in the specimen of Test No. 7 in which the water content of the soil improvement material was adjusted to 85%, depression occurred even when the water content of the sand was 5%, which is the minimum. The water content of this sample was 29%, which was higher than the optimum water content. In addition, the specimen of Test No. 10 in which the moisture content of the soil improvement material was adjusted to 60% and the moisture content of the masago was adjusted to 15%, a depression was formed, and the moisture content of the mixture was 28.9%. .
[0123]
Therefore, it can be concluded that when the mixing ratio of the soil improving material is 30%, the pavement surface having an appropriate compaction degree can be formed by adjusting the water content of the soil improving material to 60 to 75%.
[0124]
Next, the case where the mixing ratio of the soil improvement material is set to 40% is examined. The test piece in which the moisture content of the soil improvement material is 60% while the water content of the sand is 5% at the minimum. For Test No. 12), an appropriate degree of compaction was obtained, but for the specimen (Test No. 11) in which the water content of the soil improving material was 70%, a depression was formed, and an appropriate degree of compaction was obtained. I couldn't. The water content of the test sample of Test No. 11 was 31%, which was higher than the optimum water content.
[0125]
Therefore, when the mixing ratio of the soil improvement material is 40%, the water content of the soil improvement material must be set to the minimum limit of 60% even if the water content of the sand is the lowest of 5%. It can be said that it is not easy to form a pavement surface having a high degree of compaction.
[0126]
From the above, when the soil improvement material is mixed with the sandy soil (for example, masago) at a mixing ratio of 20% to 30%, the water content is adjusted to 70 to 110% in order to obtain an appropriate compaction degree. It is necessary.
[0127]
FIG. 22 shows the test results when the mixed soil material was Arakida soil.
[0128]
In the case of a mixture of 70% of Arakida soil and 30% of soil improvement material, the optimum water content is 35.2%. Arakida soil is a cohesive soil, in which the ratio of clay and silty occupies 50% or more, and the specific surface area is large, so that the water content varies within a fairly large range (5 to 25%). Specimens are prepared for Arakida soil having a water content of 5%, 10%, 15%, 20%, and 25% in accordance with this fluctuation range. In this case, the mixing ratio of the soil improvement material is 30%, 40%, and 50% (see FIG. 10).That is, it is the result of examining the relationship between the compaction degree of the mixture of Examples 1 to 3 of Embodiment 2 shown in FIG. 10 and the water content of the soil conditioner. Then, among Test Nos. 1 to 6 in which the soil improvement material was mixed at 30%, Test Nos. 2 to 6 are Examples 1-1 to 1-5, and test pieces with other test numbers are comparative examples. Test numbers 8 to 11 are Examples 2-1 to 2-4 in Test numbers 7 to 12 obtained by mixing 40% of the soil improving material, and test pieces having other test numbers are comparative examples. Furthermore, among Test Nos. 13 to 16 in which 50% of the soil improvement material was mixed, Test Nos. 14 and 15 are Examples 3-1 to 3-2, and specimens with other test numbers are comparative examples.
[0129]
First, when the case where the mixing ratio of the soil improving material is 30% (Test Nos. 1 to 6) is examined, a specimen (Test No. 2 to 6) in which the water content of the soil improving material is adjusted to 60% or more and 105% or less. In), an appropriate degree of compaction was obtained. That is, no dent was formed by the drop test of the golf ball, and no shrinkage after drying occurred. Each of these specimens had a value close to the optimum water content.
[0130]
On the other hand, the specimen of Test No. 1 in which the water content of the soil conditioner was adjusted to 115% had a depression, and an appropriate degree of compaction could not be obtained. In this case, the water content of the Arakida soil was 5%, which was the lowest expected water content, but the water content of the test specimen was 38.3%, which was higher than the optimum water content. . Also,FigureAlthough not shown, when the water content of the soil conditioner is lower than 60%, the water resistance is lost, and the compactness of the mixture is deteriorated.
[0131]
From this result, when the soil improvement material is mixed with Arakida soil at a mixing ratio of 30%, the pavement having an appropriate compaction degree is adjusted by adjusting the water content of the soil improvement material to 60% or more and 105% or less. It can be concluded that a surface can be formed.
[0132]
Next, when the mixing ratio of the soil improving material is 40% (Test Nos. 7 to 12), the specimens (Test Nos. 8 to 11) in which the water content of the soil improving material is adjusted to 60% or more and 80% or less. No.), a suitable degree of compaction is obtained, and the specimencrackNo cracking occurred. The water content of these specimens was 35 to 36%, which was a value close to the optimum water content.
[0133]
On the other hand, in the test specimen of Test No. 7 in which the water content was adjusted to 90%, even when the water content of Arakida soil was the lowest of 5%, considerable depression occurred. After drying, some cracks occurred. The water content of this sample was 39%, which was considerably higher than the optimum water content. Further, in the test specimen of Test No. 12 in which the moisture content of the soil improvement material was 55%, the water resistance was lost.
[0134]
Therefore, it can be concluded that when the mixing ratio of the soil improving material is 40%, the pavement surface having an appropriate compaction degree can be formed by adjusting the water content of the soil improving material to 60 to 80%.
[0135]
Next, the case where the mixing ratio of the soil improving material was set to 50% was examined. In the test specimens of Test Nos. 14 and 15 in which the water content of the soil improving material was set to 60% or more and 65% or less, appropriate compaction was performed. Degree is obtained, and the specimen also has a hollowcrackNo cracking occurred. The water content of these specimens was 35 to 36%, a value close to the optimum water content.
[0136]
On the other hand, the specimen of Test No. 13 in which the water content was adjusted to 70% or more had a depression. The water content of this sample was 39%, which was higher than the optimum water content. When the water content of Arakida soil was set to 15% (Test No. 16), even if the water content of the soil quality improvement material was adjusted to the minimum of 60%, the specimens were dented and dried.crackAnd an appropriate degree of compaction could not be obtained.
[0137]
Therefore, it can be concluded that when the mixing ratio of the soil improving material is 50%, the pavement surface having an appropriate compaction degree can be formed by adjusting the water content of the soil improving material to 60 to 65%.
[0138]
From the above, when the soil improving material is mixed with cohesive soil (for example, Arakida soil) at a mixing ratio of 30% to 50%, the water content may be adjusted to 60 to 105% in order to obtain an appropriate compaction degree. is necessary.
[0139]
FIG. 23 shows the test results when the mixed soil material was green screenings.
[0140]
For a mixture of 70% green screenings and 30% soil conditioner, the optimum moisture content is 27.8%. The green screenings have a clay to silt ratio of about 30 to 35%, a specific surface area of medium, and a variation range of the water content of 5 to 15%. In accordance with this, specimens are prepared for the masago soil having a water content of 5%, 10%, and 15%. The mixing ratio of the soil improvement material is set to 20 to 50% (see FIG. 11).That is, 11 is a result of examining the relationship between the compaction degree of the mixture of Examples 1 to 3 of Embodiment 4 shown in FIG. 11 and the water content of the soil improving material. Then, among Test Nos. 1 to 6 in which the soil improvement material was mixed at 20%, Test Nos. 3 to 5 are Examples 1-1 to 1-3, and test pieces with other test numbers are comparative examples. Further, among Test Nos. 7 to 10 in which 30% of the soil improvement material was mixed, Test Nos. 8 to 10 are Examples 2-1 to 2-3, and test pieces having other test numbers are comparative examples. In Test Nos. 11 to 13 obtained by mixing 40% of the soil improvement material, Test No. 13 is Example 3-1 and specimens with other test numbers are Comparative Examples. Further, the test specimens of Test Nos. 14 and 15 in which the soil improvement material was mixed at 50% are comparative examples.
[0141]
In the test specimens of Test Nos. 3 to 5 in which the water content of the soil conditioner was adjusted to 80% or more and 120% or less, an appropriate degree of compaction was obtained, no dent was formed by the drop test of the golf ball, and after drying, No shrinkage occurred. The water content of these specimens was about 28%, which was close to the optimum water content.
[0142]
On the other hand, the specimen having a moisture content of 130% (test number 2) and the specimen having a moisture content of 150% (test number 1) of the soil improvement material had depressions, and an appropriate degree of compaction could not be obtained. . Their water content was 30-34%, higher than the optimum water content. The specimen of Test No. 6 in which the water content of the soil conditioner was adjusted to 70% or less had poor tightening and a low water content (26%).
[0143]
From this result, when the soil improving material is mixed with the green screenings at a mixing ratio of 20%, the pavement having an appropriate compaction degree is adjusted by adjusting the water content of the soil improving material to 80% or more and 120% or less. It can be concluded that a surface can be formed.
[0144]
Next, the case where the mixing ratio of the soil improvement material was set to 30% was examined. In the test specimens of Test Nos. 8 to 10 in which the water content of the soil improvement material was set to 60% or more and 80% or less, an appropriate compaction degree was determined. And the hollow of the specimencrackNo cracking occurred. The water content of these specimens was 27 to 28%, a value close to the optimum water content.
[0145]
On the other hand, the specimen of Test No. 7 in which the water content was adjusted to 90% or more, even when the water content of the green screenings was the lowest of 5%, dents were formed, and the water content was 31%, which was higher than the optimum water content. I was
[0146]
Therefore, when the mixing ratio of the soil improving material is 30%, the pavement surface having an appropriate compaction degree can be formed by adjusting the water content of the soil improving material to 60 to 80%.
[0147]
Next, the case where the mixing ratio of the soil improving material was set to 40% was examined. In the specimen of Test No. 13 in which the water content of the soil improving material was set to 60%, an appropriate degree of compaction was obtained. On the other hand, the specimens (test numbers 11 and 12) in which the water content of the soil improvement material was 65% or more had dents and the water content was 29 to 31%, which was higher than the optimum water content. Therefore, when the mixing ratio of the soil improving material is 40%, it is necessary to adjust the water content of the soil improving material to 60% in order to obtain an appropriate degree of compaction.
[0148]
Next, the case where the mixing ratio of the soil improving material is set to 50% is examined. Even if the water content of the soil improving material is adjusted to the minimum of 60% and the water content of the green screenings is adjusted to the minimum of 5% (test Nos. 14 and 15), when the specimens are dented or driedcrackAnd an appropriate degree of compaction could not be obtained. The water content of these specimens was 33-38%, which was higher than the optimum water content. Therefore, it is considered that it is difficult to obtain an appropriate degree of compaction when the mixing ratio of the soil improving material is 50%.
[0149]
From the above, when the soil improvement material is mixed with rock screenings (for example, green screenings) at a mixing ratio of 20 to 40%, the water content is adjusted to 60 to 120% in order to obtain an appropriate compaction degree. It is necessary.
[Brief description of the drawings]
FIG. 1 shows an example in which various pavement soil materials and soil improvement materials are mixed to obtain an optimum mixing effect.FigureIt is.
FIG. 2 shows the results of a test performed to determine the optimum water content for forming binder aggregate particles.FigureIt is.
FIG. 3 shows the results of a water resistance test of binder aggregate particles in tap water sludge.FigureIt is.
FIG. 4 shows the results of a water permeability test for confirming the water permeability improvement effect of water sludge formed with binder aggregate particles.FigureIndicated by
FIG. 5 shows the results of a water immersion test performed to examine the relationship between the water resistance effect of binder aggregate particles and the water content of clean water sludge.FigureIt is.
FIG. 6 shows the results of a deodorization test of tap water sludge by heating and drying.FigureIt is.
FIG. 7 shows test results on the relationship between binder aggregate particle content and water permeability in soil improvement materials.FigureIt is.
FIG. 8 is a graph showing a test result on a relationship between a binder aggregate particle content in a soil improvement material and water permeability.
FIG. 9 shows the results of a test performed to examine the water resistance effect and the hardness of the pavement surface depending on the mixing ratio of the soil improvement material and the soil material (masago).FigureIt is.
FIG. 10 shows the results of a test performed to examine the water resistance effect and the hardness of the pavement surface according to the mixing ratio of the soil improvement material and the soil material (Arakita soil).FigureIt is.
FIG. 11 shows the results of a test performed to examine the water resistance effect and the hardness of the pavement surface depending on the mixing ratio of the soil improvement material and the soil material (green screenings).FigureIt is.
FIG. 12 shows test results obtained by examining the relationship between the binder aggregate particle content of the soil conditioner and the permeability of the soil mixture of the soil conditioner and the masago soil.FigureIt is.
FIG. 13 shows the binder aggregate particle content of the soil conditioner and the mixed soil of the soil conditioner and masago (Soil improvement materialIs a graph showing the test results of examining the relationship between (a mixing ratio of 20%) and water permeability.
FIG. 14 shows the binder aggregate particle content of the soil conditioner and the mixed soil of the soil conditioner and masago (Soil improvement materialIs a graph showing a test result obtained by examining the relationship between the water permeability and the mixing ratio of (30%).
FIG. 15 shows test results obtained by examining the relationship between the binder aggregate particle content of the soil conditioner and the permeability of the mixed soil of the soil conditioner and the cohesive soil.FigureIt is.
FIG. 16 shows the binder aggregate particle content of the soil conditioner and the mixed soil of the soil conditioner and the cohesive soil (Soil improvement materialIs a graph showing a test result obtained by examining the relationship between the water permeability and the mixing ratio of (30%).
FIG. 17 shows the binder aggregate particle content of the soil conditioner and the mixed soil of the soil conditioner and the cohesive soil (Soil improvement materialIs a graph showing the test results of examining the relationship between (a mixing ratio of 50%) and water permeability.
FIG. 18 shows the test results of examining the relationship between the binder aggregate particle content of the soil conditioner and the permeability of the soil mixture of the soil conditioner and the green screenings.FigureIt is.
FIG. 19 shows the binder aggregate particle content of the soil conditioner and the mixed soil of the soil conditioner and green screenings (Soil improvement materialIs a graph showing the test results of examining the relationship between (a mixing ratio of 20%) and water permeability.
FIG. 20 shows the binder aggregate particle content of the soil conditioner and the mixed soil of the soil conditioner and green screenings (Soil improvement materialIs a graph showing the test results obtained by examining the relationship between the water permeability and the mixing ratio (40%).
FIG. 21 shows the results of a test for examining the relationship between the water content of soil improvement materials and soil materials (masago) and the degree of compaction of these mixtures.FigureIt is.
FIG. 22 shows the results of a test examining the relationship between the water content of soil improvement materials and soil materials (Arakida soil) and the degree of compaction of these mixtures.FigureIt is.
FIG. 23 shows the results of a test examining the relationship between the water content of soil improvement materials and soil materials (green screenings) and the degree of compaction of these mixtures.FigureIt is.

Claims (11)

浄水場から得られる上水汚泥を、その塑性限界付近の含水比に調整し、
次いで、前記上水汚泥を粒径0.425mm4.75mmの粒度範囲のバインダー骨材粒子50重量%以上含有されるよう粒状化し、
その後に、上水汚泥中の含水比が最低含水比限界を下回らない範囲で乾燥処理して形成され、
主に粒径0.425mm〜4.75mmの粒度範囲のバインダー骨材粒子である粗粒部分およびそれ以下の細粒部分からなることを特徴とする土質改良材。
Adjust the clean water sludge obtained from the water purification plant to a water content near its plastic limit,
Next, the tap water sludge is granulated so that binder aggregate particles having a particle size range of 0.425 mm to 4.75 mm are contained in an amount of 50% by weight or more ,
After that, the water content in the water sludge is formed by drying treatment within a range that does not fall below the minimum water content limit,
A soil quality improving material comprising a coarse-grained portion, which is a binder aggregate particle having a particle size range of 0.425 mm to 4.75 mm, and a fine-grained portion smaller than the coarsened portion .
前記塑性限界付近の含水比は、75〜95%であり、その状態に調整した後に粒状化されることを特徴とする請求項1に記載の土質改良材。 2. The soil improvement material according to claim 1, wherein the moisture content near the plastic limit is 75 to 95%, and after being adjusted to that state, granulated . 前記最低含水比限界は、50%であることを特徴とする請求項1または請求項2に記載の土質改良材。The soil improvement material according to claim 1 or 2 , wherein the minimum water content ratio limit is 50% . 前記土質改良材は、前記乾燥処理後に加水して含水比を60%〜120%に調整して貯蔵されることを特徴とする請求項1ないし請求項3のいずれか一つに記載の土質改良材。 The soil improvement according to any one of claims 1 to 3, wherein the soil improvement material is stored after being adjusted to a water content of 60% to 120% by adding water after the drying treatment. Wood. 浄水場から得られる上水汚泥を、その塑性限界付近の含水比に調整し、その状態で粒径0.425mm〜4.75mmの粒度範囲のバインダー骨材粒子が50重量%以上含有されるよう粒状化し、次いで上水汚泥中の含水比が最低含水比限界を下回らない範囲で乾燥処理した主に粒径0.425〜4.75mmの粒度範囲のバインダー骨材粒子である粗粒部分およびそれ以下の細粒部分からなる土質改良材、または前記乾燥処理後に加水して含水比を60%〜120%に調整して貯蔵した主にバインダー骨材粒子である粗粒部分および細粒部分からなる土質改良材を、混合物全体に対して容積比20〜50%の割合で土材料と混合し、この混合物を用いて舗装面を形成することを特徴とする舗装方法。 The clean water sludge obtained from the water purification plant is adjusted to a water content near its plastic limit, and in that state, binder aggregate particles having a particle size range of 0.425 mm to 4.75 mm are contained in an amount of 50% by weight or more. Coarse-grained portion, mainly binder aggregate particles having a particle size range of 0.425 to 4.75 mm, which have been granulated and then dried so that the water content in the water sludge does not fall below the minimum water content limit, and A soil conditioner consisting of the following fine-grained portions, or a coarse-grained portion and a fine-grained portion, which are mainly binder aggregate particles, which are stored after being adjusted to a water content of 60% to 120% by adding water after the drying treatment. A pavement method comprising mixing a soil improvement material with a soil material at a volume ratio of 20 to 50% based on the whole mixture, and forming a pavement surface using the mixture. 前記土材料として粘性土を利用し、前記土質改良材を、混合物全体に対する容積比30〜50%の割合で粘性土と混合し、この混合物を用いて舗装面を形成することを特徴とする請求項5に記載の舗装方法。 Claims using cohesive soil as said soil material, the soil improvement agent, the entire mixture was mixed with cohesive soil at the rate of volume ratio 30-50% relative, and forming a pavement with a mixture Item 6. The pavement method according to Item 5 . 前記土質改良材は含水比60〜105%に調整されたものであることを特徴とする請求項に記載の舗装方法。The pavement method according to claim 6 , wherein the soil improvement material is adjusted to a water content of 60 to 105%. 前記土材料として砂質土を利用し、前記土質改良材を、混合物全体に対する容積比20〜30%の割合で砂質土と混合し、この混合物を用いて舗装面を形成することを特徴とする請求項5に記載の舗装方法。 Sandy soil is used as the soil material, and the soil improvement material is mixed with sandy soil at a volume ratio of 20 to 30% to the entire mixture, and a pavement surface is formed using the mixture. The pavement method according to claim 5, wherein 前記土質改良材は含水比70〜110%に調整されたものであることを特徴とする請求項に記載の舗装方法。The pavement method according to claim 8 , wherein the soil improvement material is adjusted to have a water content of 70 to 110%. 前記土材料として岩石スクリーニングスを利用し、前記土質改良材を、混合物全体に対する容積比20〜40%の割合で岩石スクリーニングスと混合し、この混合物を用いて舗装面を形成することを特徴とする請求項5に記載の舗装方法。 Using rock screenings as the soil material , mixing the soil improvement material with rock screenings at a volume ratio of 20 to 40% with respect to the entire mixture, and forming a pavement surface using the mixture. The pavement method according to claim 5, wherein 前記土質改良材は含水比60〜120%に調整されたものであることを特徴とする請求項10に記載の舗装方法。The pavement method according to claim 10 , wherein the soil improvement material is adjusted to have a water content of 60 to 120%.
JP2000280067A 2000-09-14 2000-09-14 Soil improvement material and pavement method Expired - Lifetime JP3547384B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000280067A JP3547384B2 (en) 2000-09-14 2000-09-14 Soil improvement material and pavement method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000280067A JP3547384B2 (en) 2000-09-14 2000-09-14 Soil improvement material and pavement method

Publications (2)

Publication Number Publication Date
JP2002088363A JP2002088363A (en) 2002-03-27
JP3547384B2 true JP3547384B2 (en) 2004-07-28

Family

ID=18764970

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000280067A Expired - Lifetime JP3547384B2 (en) 2000-09-14 2000-09-14 Soil improvement material and pavement method

Country Status (1)

Country Link
JP (1) JP3547384B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4824835B1 (en) * 2011-03-30 2011-11-30 岡山市 Method for crushing purified water-generated soil cake and crusher thereof
JP6182040B2 (en) * 2013-10-03 2017-08-16 前田建設工業株式会社 Management method of low water permeability of compacted soil

Also Published As

Publication number Publication date
JP2002088363A (en) 2002-03-27

Similar Documents

Publication Publication Date Title
Reddy et al. Physical, chemical and geotechnical characterization of fly ash, bottom ash and municipal solid waste from Telangana State in India
Modak et al. Stabilization of black cotton soil using admixtures
Tempest et al. Characterization and Demonstration of Reuse Applications ofSewage Sludge Ash
CN114933465B (en) Preparation method of foundation filler by using silt and lime combined improved expansive soil
Mandlik et al. Sludge use in concrete as a replacement of cement
JP3547384B2 (en) Soil improvement material and pavement method
Iqbal et al. Compaction characteristics and CBR of sludge blended with recycled clay bricks for road subgrade application
JP4848043B1 (en) Roadbed material
Yuan et al. The engineering performance of EICP-modified municipal solid waste incineration bottom ash for road construction
Yang et al. From agricultural waste to geotechnical application: Investigation of apple tree biochar for loess reinforcement
Chmeisse Soil stabilisation using some pozzolanic industrial and agricultural by products
JP3172910B2 (en) A method for manufacturing a foundation using a mass of concrete, which is construction waste material, such as gravel or foundation material for asphalt pavement
EP2468955B1 (en) Method for constructing a base course
JP2960400B1 (en) Soil conditioner, pavement method and pavement surface repair method
JP2684353B2 (en) Water-permeable material with concrete aggregate as aggregate and method for producing the same
Baker et al. Reuse of lime sludge from water softening and coal combustion byproducts
Abiero et al. Suitability of sewage sludge ash as a filler material in asphalt concrete
Paluszek Quality of structure and water-air properties of eroded Haplic Luvisol treated with gel-forming polymer
Kolay et al. Effect of alkali on tropical peat stabilized with different stabilizers
Yu et al. Sustainability through beneficial use of lime sludge for construction
JPH10266109A (en) Pavement method and pavement soil material or embankment modifier
White et al. Reuse of Lime Sludge From Water Softening and Coal Combustion Byproducts
Odi Utilization of olive husk as a replacement of fine aggregate in Portland cement concrete mixes for non-structural uses
JP5268263B2 (en) Fibrous greening base material and manufacturing method thereof
Le Characterisation of Expansive Soils Treated with Hydrated Lime, Bottom Ash and Bagasse Ash

Legal Events

Date Code Title Description
TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20040406

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20040413

R150 Certificate of patent or registration of utility model

Ref document number: 3547384

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100423

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130423

Year of fee payment: 9

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130423

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20140423

Year of fee payment: 10

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

EXPY Cancellation because of completion of term