JP2889464B2 - Stabilization method for backfill soil - Google Patents
Stabilization method for backfill soilInfo
- Publication number
- JP2889464B2 JP2889464B2 JP5168665A JP16866593A JP2889464B2 JP 2889464 B2 JP2889464 B2 JP 2889464B2 JP 5168665 A JP5168665 A JP 5168665A JP 16866593 A JP16866593 A JP 16866593A JP 2889464 B2 JP2889464 B2 JP 2889464B2
- Authority
- JP
- Japan
- Prior art keywords
- calcium hydroxide
- water
- chemical solution
- backfill soil
- present
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- 239000002689 soil Substances 0.000 title claims description 41
- 238000000034 method Methods 0.000 title claims description 19
- 230000006641 stabilisation Effects 0.000 title description 6
- 238000011105 stabilization Methods 0.000 title description 6
- 239000000126 substance Substances 0.000 claims description 35
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 31
- 239000000920 calcium hydroxide Substances 0.000 claims description 31
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 31
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 27
- 235000019353 potassium silicate Nutrition 0.000 claims description 17
- NTHWMYGWWRZVTN-UHFFFAOYSA-N sodium silicate Chemical compound [Na+].[Na+].[O-][Si]([O-])=O NTHWMYGWWRZVTN-UHFFFAOYSA-N 0.000 claims description 17
- 239000002245 particle Substances 0.000 claims description 15
- 230000000087 stabilizing effect Effects 0.000 claims description 4
- 239000000725 suspension Substances 0.000 claims description 3
- 230000003204 osmotic effect Effects 0.000 claims description 2
- 239000003814 drug Substances 0.000 claims 1
- 229940079593 drug Drugs 0.000 claims 1
- 239000000243 solution Substances 0.000 description 33
- 235000011116 calcium hydroxide Nutrition 0.000 description 29
- 230000035699 permeability Effects 0.000 description 15
- 239000004576 sand Substances 0.000 description 14
- 239000010419 fine particle Substances 0.000 description 11
- 238000002347 injection Methods 0.000 description 9
- 239000007924 injection Substances 0.000 description 9
- 239000007788 liquid Substances 0.000 description 8
- 238000002474 experimental method Methods 0.000 description 7
- 239000003795 chemical substances by application Substances 0.000 description 5
- 238000007596 consolidation process Methods 0.000 description 5
- 238000010276 construction Methods 0.000 description 5
- 239000000843 powder Substances 0.000 description 5
- 238000007711 solidification Methods 0.000 description 5
- 230000008023 solidification Effects 0.000 description 5
- 238000005507 spraying Methods 0.000 description 5
- 239000000203 mixture Substances 0.000 description 4
- 238000003756 stirring Methods 0.000 description 4
- 210000004556 brain Anatomy 0.000 description 3
- 238000005056 compaction Methods 0.000 description 3
- 238000004090 dissolution Methods 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 239000004568 cement Substances 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000007796 conventional method Methods 0.000 description 2
- 238000009826 distribution Methods 0.000 description 2
- 239000000155 melt Substances 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- BZHJMEDXRYGGRV-UHFFFAOYSA-N Vinyl chloride Chemical compound ClC=C BZHJMEDXRYGGRV-UHFFFAOYSA-N 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- LFYJSSARVMHQJB-QIXNEVBVSA-N bakuchiol Chemical compound CC(C)=CCC[C@@](C)(C=C)\C=C\C1=CC=C(O)C=C1 LFYJSSARVMHQJB-QIXNEVBVSA-N 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229940043430 calcium compound Drugs 0.000 description 1
- 150000001674 calcium compounds Chemical class 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- 235000012255 calcium oxide Nutrition 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000003111 delayed effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000002270 dispersing agent Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- -1 electricity Substances 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 238000001879 gelation Methods 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 230000008595 infiltration Effects 0.000 description 1
- 238000001764 infiltration Methods 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 230000035515 penetration Effects 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
- 238000000967 suction filtration Methods 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
Landscapes
- Consolidation Of Soil By Introduction Of Solidifying Substances Into Soil (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
Description
【発明の詳細な説明】
【0001】
【産業上の利用分野】この発明は、地盤を開削または掘
削して地下に上下水道、電気、ガス等の埋設管や地下構
造物(以下、地下構造物という)を築造または敷設した
後、その周辺に土砂を埋め戻すようにした工事におい
て、地下構造物周辺に埋戻した土を安定させるためこれ
に固結薬液を散布または注入して、埋戻し土の強化並び
に透水性を減少させるための埋戻し土の安定化処理方法
に関するものである。
【0002】
【従来の技術】従来の埋戻し土の安定化処理方法は、地
盤を開削または掘削して地下に地下構造物を築造(ある
いは敷設)した後、山砂等の砂質土でできるだけ密に突
き固めて埋戻す場合が多く、また埋戻し土にセメント、
石灰等の固化材を添加した上で埋戻す方法もとられてい
る。
【0003】
【発明が解決しようとする課題】上記従来の地下構造物
の周辺の埋戻し土の安定化処理には次のような問題点が
ある。
【0004】(イ)従来最も多い山砂等の浸透性のある
砂質土そのものを埋戻す方法では、埋戻しする地下構造
物の周辺空隙は非常に幅狭い局部的なものであり、一般
の盛土のように拡がりのある大きな埋立範囲が確保され
ている場合とは異なり、重機などで機械的に転圧するこ
とは困難であって、充分に締固めた埋戻しを期待するこ
とはできない。
【0005】このため、自動車等の走行車輛の振動や地
震等により地盤沈下が発生し、道路面下では空洞を生じ
たり、あるいは路面まで陥没するという問題がある。
【0006】特に、上水及び下水道等では、上記路面の
陥没などにより敷設管の接続部が損壊し、漏水あるいは
地下水の浸入が起こり、さらに大きな空洞が発生した場
合には周辺地盤(自然地盤も含めて)の沈下が発生する
という問題がある。
【0007】(ロ)一方、埋戻し土(砂質土)に小量の
固化材を加える方法では、ある程度の固結強度を高める
ことができるが、固化材が粉体であり、均一に攪拌混合
することは非常に困難であると共に、透水性を減少させ
ることはできないという問題点がある。
【0008】以上のように、従来の埋戻し土の安定化処
理方法は、多くの問題点を包含しており、このような問
題点を解決するには固結強度、並びに透水性の減少を改
善した安定化処理方法の開発が望まれる。
【0009】
【課題を解決するための手段】この発明は、埋戻し土を
固結させる薬液として、水に投入してなる難溶性の平均
粒径約8ミクロン以下の微粒子水酸化カルシウムを薬液
1m3当たり 2.5〜25kgを含有した懸濁液に、水ガラスを
加えることにより、水酸化カルシウムの大部分を溶解さ
せてなる浸透性薬液を、埋戻し土に散布または注入して
固結させるようにした埋戻し土の安定化処理方法を提案
するものである。
【0010】
【作用】水酸化カルシウムは水に対する溶解度は20℃で
0.165g/水100gで、水に極く僅かしか溶けない難溶性ア
ルカリであるが、水ガラス成分の存在のもとでは実用に
充分な量が溶解し、その添加量に応じたゲルタイムで水
ガラスをゲル化させる。
【0011】この水酸化カルシウムは、多少添加量がバ
ラツいてもゲルタイムの変化が少なく、ゲルタイムの調
整が(ゲルタイム3〜150分)が容易で施工性に非常に優
れ、またゲル能力が優れており、小量の硬化剤でも固結
させることができる等埋戻し土の固結剤として非常に優
れている。
【0012】
【実施例】本発明の埋戻し土の安定化処理方法は、従来
懸濁型(非浸透性)薬液として、セメント成分のみでは
瞬結タイプとすることができないという課題に対し、ゲ
ル化促進剤として補助的(単独で使用することはない)
に使われている水酸化カルシウムを成分とした微粒子粉
末が、水ガラスとの間で特異な反応を起こすことをつき
とめ、浸透性薬液としての性能を充分に満足する薬液を
用いることにより完成するに至ったものである。
【0013】即ち、水酸化カルシウムは水に対する溶解
度が20℃で 0.165g/水100gで、水に極く僅かしか溶けな
い難溶性アルカリであることは周知の通りであるが、水
ガラスの成分の存在のもとでは実用に充分な量が溶解す
ることが判った。
【0014】本発明の水酸化カルシウムの微粉末が、水
ガラスの存在のもとで溶ける量は、粉末度、水ガラスの
種類、水ガラスとの接触時間および混合方法等に影響さ
れるが、なかでも特に粉末度の影響が大である。
【0015】実施例からみれば水酸化カルシウムの大部
分(50%以上)が溶解される量は、薬液1m3当たり約25
kg程度がある。
【0016】また、本発明の水酸化カルシウムの粉末度
は、できるだけ微粒化したものが好ましいが、現状での
技術的制約を考慮して平均粒径約8ミクロンより細かい
微粒子を基準とした。
【0017】本発明はこのような微粒子を用いるため、
薬液中に極く小量の不溶性粒子が存在しても、砂質土に
浸透可能である。
【0018】即ち、砂の粒子が非常に細かい微細砂であ
って、例え水酸化カルシウムの微粉末粒子が浸透できな
くとも薬液中に含まれる量が非常に少ないため、溶液部
分の浸透を阻害することはほとんどなく、従来の溶液型
と同程度あるいはそれに近い浸透性を示す。
【0019】そのため、本発明で使用する水酸化カルシ
ウムの量は、薬液1m3当たり約 2.5〜25kgの範囲として
いる。
【0020】即ち、水酸化カルシウム量1m3当たり約
2.5kg以下であってもゲル化能力を有しているが、固結
強度があまりにも小さくなるため敢えて本発明より除外
した。
【0021】一方、逆に水酸化カルシウム量が1m3当た
り約25kg以上になると、溶解分に比べ不溶解分が多くな
る傾向にあり、一定の目安とした。
【0022】しかし、対象となる埋戻し土の種類によっ
ては、本発明の浸透性薬液としての技術的範囲を充分に
発揮することができる場合には、水酸化カルシウム量が
上記限値より多少越えても本発明の範囲とみなすことが
できる。
【0023】本発明の水に投入してなる難溶性の微粒子
水酸化カルシウムとは、水に投入した場合に Ca(OH)2と
いう物質で存在するもので、具体的には消石灰及び生石
灰である。なお、同じ微粒子のカルシウム化合物であっ
ても、水酸化カルシウム以外の化合物は水ガラスの存在
下でほとんど溶けないか、あるいはある程度溶けても実
用的なゲル化能力を示さないので、浸透性を考慮した場
合不適である。
【0024】また、本発明は微粒子の従来技術と同様
に、分散剤や必要あれば遅延剤、その他の添加剤を用い
ることができることは勿論である。
【0025】また、本発明の限定範囲以外の薬液であっ
ても、本発明の薬液と同様の性質を備え、施工的にも充
分満足できる結果が得られるものであれば、本発明の埋
戻し土の固結剤として使用できる。
【0026】本発明の埋戻し土を固結させるための施工
方法としては特に限定するものではないが、次の2つの
方法を採用することができる。
【0027】(A) 埋設管等の地下構造物が比較的浅い場
合、管周辺を山砂等の砂質土で密に埋戻した後、ゲルタ
イムが約30分以上と長い薬液(A液として水ガラス、B
液として微粒子の水酸化カルシウム懸濁液との混合液)
を散布して埋戻し土に浸透させて固結させる。
【0028】またこの発明の散布方法には、埋戻し土の
外に砂地盤等の透水性の良い地盤の地表面に薬液を散布
して、地盤の透水性の減少、あるいは固結化を図ること
ができる。
【0029】(B) 地下構造物が比較的深い場合、砂質土
を埋戻す時に同時に注入パイプを埋設するか、あるいは
埋戻し後に注入パイプを挿入して薬液を注入する。
【0030】この場合、特に限定されるのではないが、
薬液のゲルタイムが20〜30分以上の時は1ショット方式
(散布と同様、A、B液の混合液)を、またゲルタイム
が20〜30分以下の時は 1.5ショット方式(A、B液を別
々のポンプで圧送し注入パイプの頭部で両液を合流)で
注入して埋戻し土および周辺地山を含めて浸透固結させ
る。
【0031】また、上記の施工方法において注入パイプ
を用いる場合には、埋戻し土(乱した土)の他に自然地
盤(乱さない土)を対象として一般の地盤注入にも本発
明の薬液を浸透させることができるのは勿論である。
【0032】以上のような施工法により、地下構造物周
辺の埋戻し土を薬液を浸透させて固結することにより、
地盤の強度増加と共に透水性を減少させる。
【0033】このため、車輛等の振動並びに地震、それ
らによる地盤沈下、これに伴なう空洞や路面(道路)の
陥没等を防止でき、その結果埋設管等の地下構造物の破
損等を防止することができ、また仮に上下水道の埋設管
が破損しても漏水が少なく、また管周囲の埋戻し土が固
結しているため、砂の流出は少なく、空洞や陥没等を防
止することができる。
【0034】以下さらに本発明の薬液について実施例を
挙げて詳しく説明する。
【0035】実験に用いた水酸化カルシウムは、図1に
示す粒子径(粒径分布)の異なる試料1(平均粒径10.9
μ=ブレーン値10,315cm 2 /g)、試料2(平均粒径5.3μ
=ブレーン値 18,150cm 2 /g)、試料3(平均粒径2.8μ
=ブレーン値24,760cm 2 /g)の3種類、水ガラスはJI
S3号品を用いた。
【0036】また埋戻し土として下記表1の性質を示す
千葉県産出の山砂を用いた。
【0037】
【表1】
【0038】「実験−1」 水に懸濁した微粒子の水酸
化カルシウムが水ガラスの存在のもとに溶解する量を確
認するため、一定時間両者を攪拌混合した後、濾紙(東
洋濾紙製No.2)で吸引濾過により固液分離して溶解量を
測定した。
【0039】さらに、濾過した溶液(薬液)のゲルタイ
ムを測定し、併せて上記水酸化カルシウムの微粒子と水
ガラスをゲル化に到るまで常時攪拌混合した場合のゲル
タイムを測定した。その結果を表2に示す。
【0040】
【表2】
【0041】表2の水ガラスに溶解した量の欄におい
て、*印はA、B両液を3秒攪拌した結果を、**印は
同60秒攪拌した効果を、さらに註)以下の無印は同30秒
攪拌した結果を示す。
【0042】上記の表2より、水に難溶性( 0.165g/水
100g)の水酸化カルシウムが水ガラスの存在のもとでは
極めて多量に溶解することがわかり、しかもその溶解量
は水酸化カルシウムの粉末度および攪拌時間に影響さ
れ、なかでも前者の影響が大きいことが判明した。
【0043】また、ゲル化するまで水ガラスと水酸化カ
ルシウム微粒子を常時混合したゲルタイムに対して、粒
子部分を除いた溶液部分のゲルタイムは遅延されるが、
その度合いは粒子の粉末度に大きく影響され、特に粉末
度が平均粒径10ミクロン(試料1)では差が大きいこと
がわかる。
【0044】上記の溶解量およびゲルタイムからみて、
本発明で用いる水酸化カルシウムの粉末度は平均粒径約
8ミクロン以下の微粒子が好ましく、本発明の範囲とし
た。
【0045】「実験−2」 本発明の薬液を山砂に散布
した場合の固結強度並びに透水性の減少をみるため次の
実験を行った。
【0046】固結強度の試料作成は、底部を密閉した内
径約5cm、高さ15cmの塩化ビニール管(モールド)に山
砂を3層に分けて、一層あたり5回(径 4.8cmのつき棒
を木づちで)強く叩いて密に詰めた。
【0047】この試料の上部より表2の実施例−2の薬
液(A、B混合液)をジョウロから充分に散布した固結
させた。
【0048】1日後に脱枠、高さ10cmに整型して7日間
養生し、一軸圧縮強度を測定したところ1.8kgf/cm2であ
った。
【0049】また、透水係数は前記と同様な方法で内径
10cm高さ15cmの固結物を作り、JISA1218Tに準じて測
定したところ、2.5×10-6cm/secであり、未処理の山砂
に比べて透水係数は大幅に減少していた。
【0050】「実験−3」 本発明の薬液を山砂に注入
した場合の固結強度並びに透水性の実験を行った。
【0051】固結強度の試料の作成は、実験−2と同様
に内径5cm、高さ15cmのモールドに山砂を密に詰めた。
【0052】また注入は、表2の実施例−11の薬液
(A、B混合液)をモールドの下方から圧入した。その
時の注入圧力は約0.5kgf/cm2以下であった。
【0053】以下実験−2と同様一軸圧縮強度を測定し
たところ3.1kgf/cm2であった。
【0054】また透水係数も実験−2と同様行ったとこ
ろ 6.8×10-7cm/secと透水係数は大幅に減少していた。
【0055】以上の実験−2及び実験−3に示したよう
に、薬液を散布又は注入することにより、地下構造物周
辺の埋戻し土を地盤強化並びに透水性の減少をもたら
し、安定させることができる。
【0056】
【発明の効果】以上の通りこの発明によれば、地下構造
物周辺の埋戻し土の固結剤として用いる薬液の硬化剤と
して微粒子の水酸化カルシウムを、水ガラスの存在のも
とに大部分を薬液中に溶解させた浸透性薬液で地下構造
物周辺の埋戻し土を固結させることにより、地下構造物
の防護並びその周辺地盤を安定化することができる優れ
た埋戻し土の固結法である。
【0057】またこの発明の薬液の散布方法では、埋戻
し土の外に砂地盤等の透水性の良い地盤の地表面に薬液
を直接散布して、地盤の透水性の減少や固結化を図るこ
とができ、また注入パイプを用いる方法では、埋戻し土
(乱した土)の他に自然地盤(乱さない土)を対象とし
て一般の地盤注入により、地盤の透水性の減少や固結化
も図る地盤の安定処理方法としても用いることができ
る。Description: BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an underground structure in which a ground is excavated or excavated to bury underground pipes such as water and sewage, electricity, gas and the like and an underground structure (hereinafter referred to as an underground structure). After constructing or laying the soil, in the construction where the earth and sand are buried around it, in order to stabilize the buried soil around the underground structure, spray or inject a consolidation chemical solution into it, The present invention relates to a method for stabilizing backfill soil for strengthening and reducing water permeability. 2. Description of the Related Art Conventional stabilization methods for backfill soil include a method of digging or excavating the ground to build (or lay) an underground structure underground, and then using a sandy soil such as mountain sand as much as possible. In many cases, it is densely tamped and backfilled, and cement,
A method of backfilling after adding a solidifying material such as lime has been proposed. [0003] The above-mentioned conventional stabilization of backfill soil around an underground structure has the following problems. [0004] In the conventional method of backfilling permeable sandy soil itself such as mountain sand, which is the most common, the voids around the underground structure to be backfilled are very narrow and localized, and general Unlike the case where a large landfill area with expansion like an embankment is ensured, it is difficult to mechanically roll it with heavy equipment or the like, and it is not possible to expect sufficiently compacted backfill. [0005] For this reason, there is a problem that ground subsidence occurs due to vibration of a running vehicle such as an automobile, an earthquake, or the like, and a cavity is formed below a road surface or the road surface collapses. [0006] In particular, in the case of tap water and sewerage, the connecting portion of the laid pipe is damaged due to the depression of the road surface and the like, and water leakage or infiltration of groundwater occurs. The problem is that subsidence occurs. (B) On the other hand, the method of adding a small amount of solidification material to backfill soil (sandy soil) can increase the solidification strength to some extent, but the solidification material is powder and is uniformly stirred. It is very difficult to mix, and there is a problem that water permeability cannot be reduced. As described above, the conventional method for stabilizing backfill soil includes many problems. To solve such problems, reduction in compaction strength and water permeability are required. It is desired to develop an improved stabilization method. According to the present invention, as a chemical liquid for solidifying backfill soil, finely divided calcium hydroxide having an average particle size of about 8 μm or less, which is insoluble in water and poured into water, is applied to 1 m of the chemical liquid. By adding water glass to a suspension containing 2.5 to 25 kg per 3 , an osmotic chemical solution that dissolves most of the calcium hydroxide is sprayed or injected into the backfill soil and consolidated. It proposes a stabilization method for the backfilled soil. The solubility of calcium hydroxide in water is 20 ° C.
0.165 g / 100 g of water, which is a poorly soluble alkali that is only slightly soluble in water.However, in the presence of a water glass component, it dissolves in an amount sufficient for practical use, and water glass with a gel time according to the amount added. Is gelled. This calcium hydroxide has a small change in gel time even if the amount of calcium hydroxide is slightly varied, the gel time can be easily adjusted (gel time: 3 to 150 minutes), the workability is very excellent, and the gel ability is excellent. It is very excellent as a solidifying agent for backfill soil, such that even a small amount of hardening agent can be solidified. DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The method of stabilizing backfill soil according to the present invention is intended to solve the problem that conventional suspension-type (non-permeable) chemicals cannot be used as a flash-setting type using only cement components. Auxiliary as a chemical accelerator (not used alone)
Fine powder containing calcium hydroxide as a component
It has been found that the powder has a unique reaction with water glass, and has been completed by using a chemical solution that sufficiently satisfies the performance as a permeable chemical solution. That is, calcium hydroxide has a solubility in water of 0.165 g / 100 g of water at 20 ° C., and it is well known that calcium hydroxide is a sparingly soluble alkali which is very slightly soluble in water. It has been found that a practically sufficient amount dissolves in the presence. The amount by which the calcium hydroxide fine powder of the present invention dissolves in the presence of water glass is affected by the fineness, the type of water glass, the contact time with water glass, the mixing method, and the like. Among them, the influence of the fineness is particularly large. According to the embodiment, the amount of calcium hydroxide that is dissolved (50% or more) is about 25 per m 3 of the chemical solution.
There is about kg. The fineness of the calcium hydroxide of the present invention is preferably as fine as possible. However, in consideration of the technical limitations at present, fine particles having an average particle diameter smaller than about 8 μm are used as a standard. In the present invention, since such fine particles are used,
Even if a very small amount of insoluble particles are present in the chemical solution, they can penetrate sandy soil. That is, even if the fine sand particles are very fine and the fine powder particles of calcium hydroxide cannot penetrate, the amount contained in the chemical solution is very small, so that the penetration of the solution portion is inhibited. There is almost no permeability and it shows the same or similar permeability as the conventional solution type. Therefore, the amount of calcium hydroxide used in the present invention is in the range of about 2.5 to 25 kg per m 3 of the chemical solution. That is, about 1 m 3 of calcium hydroxide
Although it has a gelling ability even if it is 2.5 kg or less, it was excluded from the present invention because its consolidation strength was too small. On the other hand, when the amount of calcium hydroxide is about 25 kg or more per 1 m 3 , the insoluble content tends to be larger than the dissolved content. However, depending on the type of the backfill soil, if the technical range of the permeable chemical solution of the present invention can be sufficiently exhibited, the amount of calcium hydroxide slightly exceeds the above-mentioned limit. However, it can be considered as the scope of the present invention. The hardly soluble fine particle calcium hydroxide of the present invention which is introduced into water is present as a substance called Ca (OH) 2 when introduced into water, and is specifically slaked lime and quicklime. . The same fine particles of calcium compound
Even compounds other than calcium hydroxide have water glass
Hardly melts below, or melts to some extent
Since it does not show a practical gelling ability,
Not suitable . In the present invention, as in the prior art for fine particles, it is needless to say that a dispersant, a retarder if necessary, and other additives can be used. [0025] Even if the chemical solution is outside the limited range of the present invention, if it has the same properties as the chemical solution of the present invention and can obtain sufficiently satisfactory results in terms of construction, the backfill of the present invention can be used. Can be used as a soil compaction agent. The construction method for solidifying the backfill soil of the present invention is not particularly limited, but the following two methods can be adopted. (A) When the underground structure such as a buried pipe is relatively shallow, after the pipe periphery is densely backfilled with sandy soil such as mountain sand, a chemical solution having a long gel time of about 30 minutes or more (as the solution A) Water glass, B
Liquid mixture of fine particles and calcium hydroxide suspension)
And infiltrate the backfill soil to consolidate it. Further, in the spraying method of the present invention, a chemical solution is sprayed on the ground surface of a highly permeable ground such as a sand ground outside of the backfill soil to reduce or solidify the ground. be able to. (B) When the underground structure is relatively deep, an injection pipe is buried at the same time when the sandy soil is backfilled, or after the backfill, the injection pipe is inserted to inject the chemical. In this case, although not particularly limited,
When the gel time of the chemical solution is 20-30 minutes or more, use the one-shot method (a mixture of A and B liquids as in the case of spraying). When the gel time is 20-30 minutes or less, use the 1.5-shot method (the A and B liquids). The two liquids are pumped by separate pumps and the two liquids are merged at the head of the injection pipe) to infiltrate and solidify the backfill soil and the surrounding ground. When an injection pipe is used in the above-mentioned construction method, the chemical solution of the present invention is used not only for backfilled soil (disturbed soil) but also for natural ground (undisturbed soil) as well as general ground injection. Of course, it can be penetrated. By the above construction method, the backfill soil around the underground structure is infiltrated with the chemical solution and solidified.
Permeability decreases with increasing ground strength. Therefore, it is possible to prevent vibrations and earthquakes of vehicles and the like, land subsidence due to the vibrations and the resulting collapse of cavities and road surfaces (roads), thereby preventing damage to underground structures such as buried pipes. Even if the buried pipes of water and sewage are broken, there is little water leakage and the backfill soil around the pipes is solidified, so there is little outflow of sand, and cavities and depressions are prevented. Can be. Hereinafter, the chemical solution of the present invention will be described in detail with reference to examples. The calcium hydroxide used in the experiment was a sample 1 (average particle diameter of 10.9) having different particle diameters (particle diameter distribution) shown in FIG.
μ = Brain value 10,315 cm 2 / g ), sample 2 (average particle size 5.3 μm)
= Brain value 18,150cm 2 / g ), Sample 3 (average particle size 2.8μ)
= Brain value 24,760cm 2 / g ), water glass is JI
S3 product was used. As the backfill soil, mountain sand from Chiba Prefecture having the properties shown in Table 1 below was used. [Table 1] "Experiment-1" In order to confirm the amount of fine particles of calcium hydroxide suspended in water to dissolve in the presence of water glass, both were stirred and mixed for a certain period of time, and then filtered through a paper filter (No. In 2), solid-liquid separation was performed by suction filtration, and the amount of dissolution was measured. Further, the gel time of the filtered solution (chemical solution) was measured, and the gel time when the calcium hydroxide fine particles and water glass were constantly stirred and mixed until gelling was measured. Table 2 shows the results. [Table 2] In the column of the amount dissolved in water glass in Table 2, * indicates the result of stirring both solutions A and B for 3 seconds, and ** indicates the effect of stirring for 60 seconds. Indicates the result of stirring for 30 seconds. From the above Table 2, it is found that the compound is hardly soluble in water (0.165 g / water).
100 g) of calcium hydroxide was found to dissolve in a very large amount in the presence of water glass, and the amount of dissolution was affected by the fineness of the calcium hydroxide and the stirring time. There was found. Further, the gel time of the solution portion excluding the particle portion is delayed with respect to the gel time in which the water glass and the calcium hydroxide fine particles are always mixed until gelation,
It can be seen that the degree is greatly affected by the fineness of the particles, and the difference is particularly large when the fineness is 10 μm (sample 1). In view of the above dissolution amount and gel time,
The fineness of the calcium hydroxide used in the present invention is preferably fine particles having an average particle size of about 8 microns or less, which is within the scope of the present invention. "Experiment-2" The following experiment was carried out in order to see the reduction of the solidification strength and water permeability when the chemical solution of the present invention was sprayed on mountain sand. A sample of the consolidation strength was prepared by dividing mountain sand into three layers in a vinyl chloride tube (mold) having an inner diameter of about 5 cm and a height of 15 cm with a closed bottom, and performing five times per layer (with a stick having a diameter of 4.8 cm). (With a tree). From the upper part of the sample, the chemical solution (mixture of A and B) of Example 2 in Table 2 was solidified by sufficiently spraying it from a mug. One day later, it was unframed, shaped to a height of 10 cm, cured for 7 days, and measured for uniaxial compressive strength to be 1.8 kgf / cm 2 . The hydraulic conductivity is determined by the same method as described above.
When a consolidated product having a height of 10 cm and a height of 15 cm was prepared and measured according to JIS A1218T, it was 2.5 × 10 -6 cm / sec, and the permeability was significantly reduced as compared with untreated mountain sand. "Experiment-3" An experiment was conducted on the solidification strength and water permeability when the chemical solution of the present invention was poured into mountain sand. For the preparation of a sample having a compaction strength, as in Experiment 2, mountain sand was densely packed in a mold having an inner diameter of 5 cm and a height of 15 cm. For injection, the chemicals (mixtures A and B) of Example 11 in Table 2 were press-fitted from below the mold. The injection pressure at that time was about 0.5 kgf / cm 2 or less. The unconfined compressive strength was measured in the same manner as in Experiment-2 and found to be 3.1 kgf / cm 2 . When the coefficient of permeability was measured in the same manner as in Experiment-2, the coefficient of permeability was 6.8 × 10 −7 cm / sec, which was significantly reduced. As shown in Experiment 2 and Experiment 3 above, by spraying or injecting a chemical solution, it is possible to strengthen the backfill soil around the underground structure, reduce the water permeability, and stabilize it. it can. As described above, according to the present invention, fine particles of calcium hydroxide are used as a hardening agent for a chemical solution used as a solidifying agent for backfill soil around an underground structure, and the presence of water glass is used. An excellent backfill soil that can protect the underground structure and stabilize the surrounding ground by consolidating the backfill soil around the underground structure with a permeable chemical solution that is largely dissolved in the chemical solution It is a consolidation method. In the method for spraying a chemical solution according to the present invention, the chemical solution is directly sprayed on the ground surface of a ground having good water permeability such as sand ground outside the backfill soil to reduce the water permeability of the ground or to consolidate the ground. In addition, the method using an injection pipe reduces the water permeability and consolidation of the ground by general ground injection for natural ground (undisturbed soil) in addition to backfill soil (disturbed soil). It can also be used as a ground stabilization method.
【図面の簡単な説明】
【図1】この発明の実験に用いた水酸化カルシウムの各
試料の粒径分布図。BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a particle size distribution diagram of each sample of calcium hydroxide used in an experiment of the present invention.
───────────────────────────────────────────────────── フロントページの続き (72)発明者 富田 茂芳 東京都江東区南砂5−19−16 (56)参考文献 特開 平1−176262(JP,A) 特開 平1−190786(JP,A) 特開 平5−320644(JP,A) (58)調査した分野(Int.Cl.6,DB名) E02D 3/12 101 E02D 3/12 103 ────────────────────────────────────────────────── ─── Continued on the front page (72) Inventor Shigeyoshi Tomita 5-19-16 Minamisuna, Koto-ku, Tokyo (56) References JP-A-1-176262 (JP, A) JP-A-1-190786 (JP, A) JP-A-5-320644 (JP, A) (58) Fields investigated (Int. Cl. 6 , DB name) E02D 3/12 101 E02D 3/12 103
Claims (1)
微粒子水酸化カルシウムを薬液1m3当たり約 2.5〜25kg
含有した懸濁液に、水ガラスを加えることにより、前記
水酸化カルシウムの大部分を溶解させた浸透性薬液を、
埋戻し土に散布または注入して固結させることを特徴と
する埋戻し土の安定化処理方法。(57) [Claims] Insoluble calcium hydroxide having an average particle size of about 8 μm or less, which is poured into water, is added in an amount of about 2.5 to 25 kg per m 3 of a chemical solution.
By adding water glass to the suspension containing the osmotic drug solution in which most of the calcium hydroxide was dissolved,
A method for stabilizing a backfill soil, comprising scattering or pouring into the backfill soil and consolidating the same.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5168665A JP2889464B2 (en) | 1993-06-14 | 1993-06-14 | Stabilization method for backfill soil |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5168665A JP2889464B2 (en) | 1993-06-14 | 1993-06-14 | Stabilization method for backfill soil |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH073768A JPH073768A (en) | 1995-01-06 |
| JP2889464B2 true JP2889464B2 (en) | 1999-05-10 |
Family
ID=15872234
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP5168665A Expired - Fee Related JP2889464B2 (en) | 1993-06-14 | 1993-06-14 | Stabilization method for backfill soil |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2889464B2 (en) |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH01176262A (en) * | 1987-12-31 | 1989-07-12 | Kyokado Eng Co Ltd | Binder |
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1993
- 1993-06-14 JP JP5168665A patent/JP2889464B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH073768A (en) | 1995-01-06 |
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