JPH05331829A - Surplus soil improving method using shell incineration lime produced out of shell adhering to intake pipe for power station - Google Patents

Surplus soil improving method using shell incineration lime produced out of shell adhering to intake pipe for power station

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Publication number
JPH05331829A
JPH05331829A JP16168392A JP16168392A JPH05331829A JP H05331829 A JPH05331829 A JP H05331829A JP 16168392 A JP16168392 A JP 16168392A JP 16168392 A JP16168392 A JP 16168392A JP H05331829 A JPH05331829 A JP H05331829A
Authority
JP
Japan
Prior art keywords
shell
incineration
soil
lime
residual soil
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.)
Granted
Application number
JP16168392A
Other languages
Japanese (ja)
Other versions
JP2768147B2 (en
Inventor
Norio Kainuma
憲男 貝沼
Morio Takahashi
守男 高橋
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Tokyo Electric Power Company Holdings Inc
Original Assignee
Tokyo Electric Power Co Inc
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 Tokyo Electric Power Co Inc filed Critical Tokyo Electric Power Co Inc
Priority to JP16168392A priority Critical patent/JP2768147B2/en
Publication of JPH05331829A publication Critical patent/JPH05331829A/en
Application granted granted Critical
Publication of JP2768147B2 publication Critical patent/JP2768147B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Investigation Of Foundation Soil And Reinforcement Of Foundation Soil By Compacting Or Drainage (AREA)

Abstract

PURPOSE:To lower cost for surplus soil improvement by making use of shell incineration ashes as a lime constituent of improving agent, which are obtained through the incineration of raw shells collected from the wall of an intake pipe at a specified temperature. CONSTITUTION:A sort of shells on the wall of an intake pipe for a power station is peeled off and recovered so as to be dewatered. It is then incinerated at 700 to 900 deg.C in a rotary kiln and the like so as to be formed into shell incineration quick lime powder. It is formed into shell incineration slaked lime with the quantity of water added as specified so as to be formed into a condition suitable for handling and storing, and slaked lime is added to surplus soil and mixed to be used for reclamation and the like as improved soil. Furthermore, shell incineration ashes are combined with coal ashes and desulfurizing gypsum to accelerate borazon reaction. This constitution thereby enables cost for surplus soil improvement to be lowered because incineration ashes are utilized, enables a space for filling raw shells to be eliminated, enables energy cost to be lowered because of incineration at low temperatures, and also enables mixing properties to be enhanced because shell incineration slaked lime is coarse in grain size.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は残土の改良方法に関し、
特に火力発電所及び原子力発電所の取水路に付着する生
貝を回収し、焼却して得られる石灰を主成分とする焼却
灰を使用する残土の改良方法に関する。
BACKGROUND OF THE INVENTION The present invention relates to a method for improving residual soil,
In particular, the present invention relates to a method for improving the residual soil using incinerated ash containing lime as a main component, which is obtained by collecting and incinerating raw shellfish attached to intake channels of thermal power plants and nuclear power plants.

【0002】[0002]

【従来の技術及び発明が解決しようとする課題】近年、
残土処分場の確保が難しいこと、また埋戻し用の山砂の
採取が環境破壊につながる恐れがあること等から、山砂
の代替として残土のリサイクルを図ろうとする動きが活
発になっている。残土のリサイクルの流れは、図1に示
すようなもので、まず各土木作業現場から発生した残土
のうちそのままでは埋戻し材として適さない不良残土1
は、残土改良プラントにて、生石灰等の改良材2を添加
混合して堆積、養生することにより、一定の品質特性を
備えた埋戻し用改良土3として改良される。なお、本明
細書中でいう「残土」とは、掘削工事により排出する土
砂のうち該現場で資材として使用しない土砂をさす。現
在、残土改良材としては工業用生石灰が多く用いられて
おり、添加量は対乾燥土重量比で3〜5%程度である。
石灰による残土の改良は、土との反応を利用して土の物
理・化学的性質を改良するものであり、生石灰の場合は
(1)吸水発熱反応による脱水、(2)イオン交換反応
による粒度改善、(3)ポゾラン反応による固結、
(4)炭酸化反応等により残土が改良されるといわれて
いる。
2. Description of the Related Art In recent years,
Since it is difficult to secure a disposal site for surplus soil, and collecting sand for backfilling may lead to environmental damage, there are active moves to recycle surplus soil as an alternative to sand. The flow of recycling the residual soil is as shown in Fig. 1. First, of the residual soil generated from each civil engineering work site, it is not suitable as a backfill material 1
Is improved as the backfilling improved soil 3 having a certain quality characteristic by adding, mixing, depositing and curing the improving material 2 such as quick lime in the residual soil improving plant. In addition, the "remaining soil" in this specification refers to the earth and sand not used as a material in the said site among earth and sand discharged by excavation work. Currently, industrial quick lime is often used as a residual soil improving material, and the addition amount thereof is about 3 to 5% in terms of the dry soil weight ratio.
The improvement of the residual soil by lime is to improve the physical and chemical properties of the soil by utilizing the reaction with the soil. In the case of quick lime, (1) dehydration by water absorption exothermic reaction, (2) particle size by ion exchange reaction Improvement, (3) consolidation by pozzolanic reaction,
(4) It is said that the residual soil is improved by the carbonation reaction and the like.

【0003】ところで火力・原子力発電所においては、
発電設備の復水器の冷却水として海水が取水路を経て導
入・使用されるが、その水路底・側面にはムラサキイ貝
等の生貝が生育・付着し、水流抵抗を増大させ、あるい
は一部剥離して流れ出た生貝が発電所冷却管に付着して
閉塞するなどの問題を発生させるため、定期的に該生貝
を剥奪除去する必要がある。この取水路に付着する生貝
の年間除去回収量は、1火力発電所当たりで1,000
t/年程度にも及ぶもので、膨大量の生貝が除去され、
生貝のまま多くが埋立て処分されている状況である。埋
立て処分については、埋立て地の確保やその堆積個所に
おける腐敗異臭対策が課題である。
By the way, in thermal power and nuclear power plants,
Seawater is introduced and used as cooling water for the condenser of the power generation facility via the intake channel, but raw shellfish such as mussels grow and adhere to the bottom and side surfaces of the channel, increasing water flow resistance, or part of it. Since the raw shellfish that separates and flows out adheres to the cooling pipe of the power plant and causes a problem, it is necessary to regularly strip and remove the raw shellfish. Annual removal and recovery of raw shellfish adhering to this intake channel is 1,000 per thermal power plant.
It is about t / year, and a huge amount of raw shellfish is removed.
A lot of raw shellfish is being landfilled. With regard to landfill disposal, securing landfill sites and measures against spoilage and offensive odors at their deposits are issues.

【0004】[0004]

【課題を解決するための手段】本発明者らは上記事情に
鑑み、火力・原子力発電所取水路付着生貝の有効利用を
促進し、生貝埋立て処分量の低減を図るべく鋭意研究
し、本発明をなすに至った。すなわち、本発明は、
(1)火力・原子力発電所取水路壁から剥奪回収された
生貝を、焼却して得られる貝焼却灰粉末を残土改良材の
石灰成分として、残土に添加・混合して改良土とするこ
とを特徴とする発電所取水路付着貝焼却石灰を用いる残
土改良方法及び、(2)発電所取水路壁から剥奪回収さ
れた生貝を焼却して得られる貝焼却灰粉末と、石炭灰
と、脱硫石膏とからなる混合物を残土改良材として、残
土に添加・混合して改良土とすることを特徴とする発電
所取水路付着貝焼却石灰を用いる残土改良方法である。
ここで、貝焼却石灰とは、生石灰又は消石灰を主体とす
る貝焼却灰をいう。
[Means for Solving the Problems] In view of the above circumstances, the present inventors have earnestly studied to promote effective use of raw shellfish attached to thermal power / nuclear power plant intake channels and reduce the amount of raw shellfish landfill disposal. Invented the invention. That is, the present invention is
(1) Addition and mixing of raw shellfish, which has been stripped and collected from the intake channel wall of thermal power and nuclear power plants, as a lime component of the residual soil improving material, to form improved soil. Characteristic method for improving residual soil using incinerated lime adhering to power plant intake channel, and (2) Shell incinerated ash powder obtained by incinerating raw shellfish stripped and recovered from power station intake channel wall, coal ash, and desulfurization gypsum It is a method for improving the residual soil using the incineration lime from the power plant intake channel, which comprises adding and mixing the mixture consisting of and as the residual soil improving material to the residual soil to mix with the residual soil.
Here, the shell cremation lime means shell ash mainly composed of quick lime or slaked lime.

【0005】本発明を好適条件等を挙げて詳細に説明す
ると、火力・原子力発電所取水路壁から剥奪回収される
生貝は、例えば(1)取水路清掃工事において、発電所
の取水口、取水路の底、側壁部に付着しているムラサキ
イ貝類を掻き出す剥奪回収を行って得られ、次いで
(2)水切りを行ない、(3)生貝のままロータリーキ
ルン等で700〜900℃、1〜2時間、焼却する。以
上の工程によって、貝焼却生石灰粉末を取得することが
できる。ここで貝焼却生石灰粉末とは、生石灰が主成分
となっている貝焼却灰をいう。なお、貝焼却生石灰は、
工業用生石灰と同様、反応性が高く残土改良材としては
良好となるが、水と接触して急激に高温となる危険性を
もつものであるため、保存上制約がある場合は、これに
所要量の水(貝焼却生石灰の約30%)をミキサーで加
水混合して貝焼却消石灰となし、取り扱い性及び保存性
を良好なものとすることが好ましい。貝焼却消石灰は、
焼却灰中の生石灰成分が消石灰になったものをいう。
The present invention will be described in detail with reference to preferable conditions and the like. Raw shellfish stripped and collected from the intake channel wall of a thermal power / nuclear power station is, for example, (1) in the intake channel cleaning work, the intake port of the power station, the intake channel. Obtained by scraping and collecting the mussels attached to the bottom and side walls of the road, then (2) draining, (3) 700-900 ° C for 1-2 hours in a rotary kiln, etc. Incinerate. Through the above steps, shellfish incineration quicklime powder can be obtained. Here, the incineration quicklime powder of shellfish refers to the incineration ash of shellfish whose main component is quicklime. In addition, shellfish incineration quicklime is
Like industrial quicklime, it has high reactivity and is good as a residual soil improvement material, but it has the risk of suddenly becoming hot when it comes into contact with water. It is preferable that a certain amount of water (about 30% of shell-burned quick lime) is mixed with a mixer to form shell-burned slaked lime, which has good handleability and storage stability. Shellfish incineration slaked lime
The quick lime component in the incinerated ash is slaked lime.

【0006】前記生貝の焼却温度は、通常700℃〜9
00℃で充分であり、これにより貝肉及び採取時に含ま
れていた海生物、有機質雑物は消散し、殆どが生石灰で
ある貝焼却生石灰が得られる。得られる貝焼却生石灰
は、貝殻の形を残す粗粒分の多い灰である。これに加水
混合すると貝焼却消石灰が白色の微細な粉体として取得
できる特徴がある。以上によって得られた貝焼却灰の化
学組成及び物理性状は表1に示す通りである。なお、石
炭灰、及び脱硫石膏の各組成・性状についても記載し
た。
[0006] The incineration temperature of the raw shellfish is usually 700 ° C to 9 ° C.
A temperature of 00 ° C. is sufficient. As a result, shellfish, sea life and organic substances contained at the time of collection are dissipated, and shell-burned quicklime, which is mostly quicklime, is obtained. The obtained shellfish incineration quicklime is a coarse-grained ash that retains the shape of the shell. When mixed with water, shellfish incineration slaked lime can be obtained as a fine white powder. The chemical composition and physical properties of the shell incineration ash obtained as described above are as shown in Table 1. The composition and properties of coal ash and desulfurized gypsum are also described.

【0007】[0007]

【表1】 [Table 1]

【0008】本発明に係る残土改良材は上記により得ら
れる貝焼却灰単独で残土に添加混合して改良土となすこ
とができるが、さらに石炭灰、脱硫石膏を加配した混合
物型残土改良材とすることもできる。混合物型残土改良
材の製造に使用する石炭灰としては、火力発電所より多
量に副産するものを用いることができ、また脱硫石膏も
火力発電所排ガス処理において多量に副産するものを用
いることができる。したがって、本発明における残土改
良材混合物は、全て火力・原子力発電所等の副産物を原
料として製造することができるものである。残土の水分
が多い場合は、それに比例して本発明に係る残土改良材
添加量も増量する必要があるが、改良材重量(M)と残
土中の水分含量(W)の比M/Wと改良土の強度には線
形関係がみられ、M/Wの増加とともに強度は増加す
る。 M/W=a/ω (ただし、a:改良材添加率(%)、
ω:残土含水比(%)) であるため、改良土の一軸圧縮強さは含水比が変動して
もM/Wを一定にすれば、強度を一定にすることができ
るので、残土の含水比に応じて改良材の添加量を調整す
ればよい。通常、本発明に係る貝焼却生石灰の添加量は
対乾燥土重量比で3〜5%程度であり、工業用生石灰と
同程度である。貝焼却消石灰の場合はいく分添加量が多
くなる。
The residual soil improving material according to the present invention can be added to and mixed with the residual soil by adding the shell incineration ash obtained as described above to the improved soil, and further, it is a mixture type residual soil improving material containing coal ash and desulfurized gypsum. You can also do it. As the coal ash used for the production of the mixture type residual soil improving material, it is possible to use a large amount of by-product from the thermal power plant, and use desulfurized gypsum that is a large amount of by-product in the exhaust gas treatment of the thermal power plant. You can Therefore, the residual soil improving material mixture according to the present invention can be produced by using the by-products of thermal power plants, nuclear power plants, etc. as raw materials. When the residual soil has a large amount of water, it is necessary to increase the amount of the residual soil improving material according to the present invention in proportion to the amount of the residual soil. However, the ratio M / W between the weight of the improving material (M) and the water content in the residual soil (W) is There is a linear relationship between the strength of the improved soil and the strength increases as M / W increases. M / W = a / ω (where a: improvement material addition rate (%),
ω: Remaining soil water content ratio (%)), the uniaxial compressive strength of the improved soil can be kept constant if M / W is kept constant even if the water content ratio changes. The addition amount of the improving material may be adjusted according to the ratio. Usually, the amount of the incineration quicklime to be added according to the present invention is about 3 to 5% by weight ratio to dry soil, which is about the same as industrial quicklime. In the case of incinerated slaked lime, the amount added increases to some extent.

【0010】本発明に係る混合物型残土改良材おいて
は、発電所貝焼却生石灰あるいは、貝焼却消石灰に、石
炭灰(フライアッシュ)を組み合わせると、Ca2+
増加することになり、石炭灰のポゾラン反応が促進さ
れ、石炭灰の水和硬化による改良効果が期待される。さ
らに、脱硫石膏を組み合わせると、SO4 2−が増加す
ることから、ポゾラン反応が一層促進されることが期待
される。なお、脱硫石膏は、結晶水以外に3%程度の水
分を含んでいることから、組み合わせて用いる場合、乾
燥してからブレンドする必要があり、乾燥工程を必要と
する。
In the mixture type residual soil improving material according to the present invention, when coal ash (fly ash) is combined with power plant shell burned quick lime or shell burned slaked lime, Ca 2+ is increased, and the coal ash content increases. The pozzolanic reaction is promoted, and the improvement effect by the hydration hardening of coal ash is expected. Further, when combined with desulfurized gypsum, SO 4 2− increases, so that it is expected that the pozzolanic reaction is further promoted. Since desulfurized gypsum contains about 3% of water in addition to water of crystallization, when used in combination, it is necessary to dry and then blend, which requires a drying step.

【0011】[0011]

【実施例】次に、本発明を実施例によって具体的に説明
する。表2に示す残土に、本発明実施例に係る貝焼却灰
単独あるいは石炭灰や脱硫石膏と組合せて、添加混合し
て改良土を製造した。本実施例で使用した試料残土の性
状は表2に示すとおりで、含水比83.5%、粘土分
40%、砂分24%、シルト分36%の粒度からなるも
のである。
EXAMPLES Next, the present invention will be specifically described by way of examples. Improved soil was manufactured by adding to and mixing with the residual soil shown in Table 2 alone or in combination with the coal ash or desulfurized gypsum according to the example of the present invention. The properties of the sample residual soil used in this example are as shown in Table 2, with a water content ratio of 83.5% and a clay content.
It has a particle size of 40%, sand content 24% and silt content 36%.

【0012】[0012]

【表2】 [Table 2]

【0013】上記貝焼却灰粉末の製造は、下記の工程に
したがって行った。 .取水路からの貝の回収→.水切り→.生貝をロ
ータリーキルンで焼却(700〜900℃、1〜2時
間)→.貝焼却生石灰の生成貯蔵→.加水混合→
.貝焼却消石灰の生成貯蔵
The above-mentioned shellfish incineration ash powder was manufactured according to the following steps. . Recovery of shellfish from the intake channel →. Draining →. Incinerating raw shellfish in a rotary kiln (700-900 ° C, 1-2 hours) →. Generation and storage of shellfish incineration quicklime →. Water mix →
. Generation and storage of incinerated slaked lime

【0014】上記においては、発電所の取水口、取水
路の底、側壁部に付着しているムラサキイ貝を掻き出し
による剥奪回収を行い、続いて〜において、生貝を
水切りしロータリーキルンに供給し、700〜900℃
で、 1〜2時間加熱し、貝焼却生石灰粉末を回収す
る。さらに、これに散水して貝焼却消石灰となす。
In the above, the mussels adhering to the intake of the power plant, the bottom of the intake channel, and the side wall are stripped and collected by scraping, and subsequently, in (1) to (7), the raw shells are drained and supplied to the rotary kiln. ~ 900 ° C
Then, the mixture is heated for 1 to 2 hours to collect shellfish incineration quicklime powder. Furthermore, water is sprinkled on this to make slaked lime by incineration.

【0015】得られた貝焼却生石灰および貝焼却消石灰
の物理性状及び化学組成は表1に示す通りである。
The physical properties and chemical compositions of the obtained shellfish incineration quicklime and shellfish incineration slaked lime are shown in Table 1.

【0016】また図2には、上記貝焼却生石灰(L)
に、石炭灰(F)及び脱硫石膏(G)を各種配合割合で
加配して得られた混合物型残土改良材を用いて、残土改
良テストを行った結果(材令10日)を示す。該改良材
の添加率は対乾燥土重量比で12%である。なお、図中
の数字は改良土の一軸圧縮強さを示し、いくつかの等高
線は、2,5,10,15,18kgf/cmの各一
軸圧縮強さの等高線を示している。該図から判るよう
に、一軸圧縮強さが材令10日で10kgf/cm
上を示す概略組成は貝焼却生石灰50〜100%、石炭
灰0〜45%、脱硫石膏0〜20%からなるものであ
り、また15kg/cm以上を示す概略組成は貝焼却
生石灰70〜100%、石炭灰0〜30%、脱硫石膏0
〜20%からなるものである。
Further, in FIG. 2, the above shellfish incineration quicklime (L) is used.
The result (10 days of age) of the residual soil improvement test using the mixture type residual soil improving material obtained by adding coal ash (F) and desulfurized gypsum (G) in various mixing ratios is shown in FIG. The addition ratio of the improving material is 12% based on the weight ratio of dry soil. The numbers in the figure show the uniaxial compressive strength of the improved soil, and some contour lines show the uniaxial compressive strength contour lines of 2 , 5, 10, 15, 18 kgf / cm 2 . As can be seen from the figure, the general composition showing a uniaxial compressive strength of 10 kgf / cm 2 or more after 10 days of age consists of shell-burned quicklime 50-100%, coal ash 0-45%, desulfurized gypsum 0-20%. Further, the general composition showing 15 kg / cm 2 or more is 70 to 100% of shell-burning quicklime, 0 to 30% of coal ash, 0 of desulfurization gypsum.
.About.20%.

【0017】得られた貝焼却生石灰、貝焼却消石灰、石
炭灰(F)と脱硫石膏(G)および貝焼却生石灰(L)
の組み合わせ材料(F:G:L=2:1:7)を上記試
料残土に添加混合して改良土となしたテスト結果を図3
に示す。なお、改良土の品質基準(東京都)は表3に示
す通りであるが、本発明方法によれば同基準を満たす改
良土を容易に造ることができた。
Obtained shell-and-burnt quicklime, shell-and-burnt lime, coal ash (F) and desulfurization gypsum (G) and shell-and-burnt quicklime (L)
The combined material (F: G: L = 2: 1: 7) of No. 1 was added to and mixed with the above-mentioned residual soil of the sample to obtain the improved soil.
Shown in. The quality standards for the improved soil (Tokyo) are as shown in Table 3, but according to the method of the present invention, the improved soil satisfying the same standard could be easily produced.

【0018】[0018]

【表3】 [Table 3]

【0019】[0019]

【発明の効果】以上に述べた説明から明らかなごとく、
本発明によれば .従来火力・原子力発電所において、取水路の底・側
面に生育付着する膨大量の生貝を埋立て処分することな
く、焼却灰を残土改良材として有効利用できる結果、残
土改良コストが低減され、生貝の埋立て用地確保の問題
も解決される。 .発電所取水路付着生貝から製造される製造される石
灰は、比較的低温焼却にもかかわらず高活性の石灰が得
られ、エネルギーコストも低いものとなる。またその貝
焼却生石灰粉末は粒径が粗いため残土改良材として残土
との混合性が良好で容易に均質な混合ができ、よって使
用量も必要最少量で足りる。また、混合時に粉塵も立ち
にくい。 .混合物型残土改良材は全て火力・原子力発電所から
得られる副産物で製造することができ、かつ得られた残
土改良材を用いて埋戻し材として要求される条件を満た
す改良土を容易に製造することができる。
As is apparent from the above description,
According to the invention: In conventional thermal and nuclear power plants, the incineration ash can be effectively used as a residual soil improvement material without landfill disposal of a huge amount of raw shellfish that grows and adheres to the bottom and sides of the intake channel, resulting in a reduction in residual soil improvement cost and a reduction in raw shellfish. The problem of land reclamation site is also solved. . The lime produced from the raw shellfish attached to the intake of the power plant produces highly active lime despite incineration at a relatively low temperature, resulting in a low energy cost. Further, the shellfish incineration quicklime powder has a coarse particle size, so that it has good compatibility with the residual soil as a residual soil improving material and can be easily mixed homogeneously. Therefore, the required minimum amount is sufficient. In addition, dust is unlikely to rise during mixing. . All of the mixture type residual soil improving materials can be produced by-products obtained from thermal power plants and nuclear power plants, and the obtained residual soil improving materials can be used to easily produce improved soil satisfying the conditions required as backfill materials. be able to.

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

【図1】残土のリサイクルの流れを示す説明図FIG. 1 is an explanatory diagram showing the flow of recycling the residual soil.

【図2】混合物型残土改良材を用いて、残土改良テスト
を行った結果の三角座標グラフ図
FIG. 2 is a triangular coordinate graph showing the results of the residual soil improvement test using a mixture type residual soil improving material.

【図3】残土改良材を試料残土に添加混合して改良土と
なしたテスト結果のグラフ図
[Fig. 3] Graph of the test results obtained by adding and mixing the residual soil improving material to the sample residual soil to obtain improved soil.

【符号の説明】[Explanation of symbols]

1:不良残土 2:改良材 3:改良土 F:石炭灰 G:脱硫石膏 L:貝焼却生石灰 1: Bad residual soil 2: Improved material 3: Improved soil F: Coal ash G: Desulfurized gypsum L: Shell incineration quicklime

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 火力・原子力発電所取水路壁から剥奪回
収された生貝を焼却して得られる貝焼却灰粉末を残土改
良材の石灰成分として、残土に添加・混合して改良土と
することを特徴とする発電所取水路付着貝焼却石灰を用
いる残土改良方法。
1. A shell soil incineration ash powder obtained by incinerating raw shellfish stripped and collected from the intake wall of a thermal power / nuclear power plant is added to and mixed with the residual soil as a lime component of the residual soil improving material to form improved soil. A method for improving residual soil using incinerated lime attached to a power plant intake canal.
【請求項2】 火力・原子力発電所取水路壁から剥奪回
収された生貝を焼却して得られる貝焼却灰粉末と、石炭
灰と、脱硫石膏とからなる混合物を、残土に添加・混合
して改良土とすることを特徴とする発電所取水路付着貝
焼却石灰を用いる残土改良方法。
2. A mixture of shell incineration ash powder obtained by incinerating raw shellfish stripped and collected from the intake wall of a thermal power / nuclear power plant, coal ash, and desulfurized gypsum is added and mixed to the residual soil. A method for improving residual soil using incinerated lime attached to a water intake of a power plant, which is characterized as improved soil.
【請求項3】 火力・原子力発電所取水路壁から剥奪回
収された生貝を700℃〜900℃で焼却して得られる
貝焼却灰粉末を用いることを特徴とする請求項1又は2
記載の発電所取水路付着貝焼却石灰を用いる残土改良方
法。
3. A shell incineration ash powder obtained by incinerating raw shellfish stripped and collected from the intake channel wall of a thermal power / nuclear power plant at 700 ° C. to 900 ° C. is used.
A method for improving the residual soil using the incinerated lime that adheres to the water intake of the power plant described above.
JP16168392A 1992-05-29 1992-05-29 Remaining soil improvement method using incinerated lime from shellfish attached to power plant intake channel Expired - Fee Related JP2768147B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16168392A JP2768147B2 (en) 1992-05-29 1992-05-29 Remaining soil improvement method using incinerated lime from shellfish attached to power plant intake channel

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16168392A JP2768147B2 (en) 1992-05-29 1992-05-29 Remaining soil improvement method using incinerated lime from shellfish attached to power plant intake channel

Publications (2)

Publication Number Publication Date
JPH05331829A true JPH05331829A (en) 1993-12-14
JP2768147B2 JP2768147B2 (en) 1998-06-25

Family

ID=15739867

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16168392A Expired - Fee Related JP2768147B2 (en) 1992-05-29 1992-05-29 Remaining soil improvement method using incinerated lime from shellfish attached to power plant intake channel

Country Status (1)

Country Link
JP (1) JP2768147B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006152150A (en) * 2004-11-30 2006-06-15 Shimizu Corp Method for producing ground stabilizer

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006152150A (en) * 2004-11-30 2006-06-15 Shimizu Corp Method for producing ground stabilizer
JP4609701B2 (en) * 2004-11-30 2011-01-12 清水建設株式会社 Method for manufacturing ground improvement material

Also Published As

Publication number Publication date
JP2768147B2 (en) 1998-06-25

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