JPH04326975A - Production of slag due to melting of waste - Google Patents
Production of slag due to melting of wasteInfo
- Publication number
- JPH04326975A JPH04326975A JP3125093A JP12509391A JPH04326975A JP H04326975 A JPH04326975 A JP H04326975A JP 3125093 A JP3125093 A JP 3125093A JP 12509391 A JP12509391 A JP 12509391A JP H04326975 A JPH04326975 A JP H04326975A
- Authority
- JP
- Japan
- Prior art keywords
- slag
- hot water
- waste
- melting
- water
- 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
Links
- 239000002893 slag Substances 0.000 title claims abstract description 75
- 238000002844 melting Methods 0.000 title claims abstract description 39
- 230000008018 melting Effects 0.000 title claims abstract description 39
- 239000002699 waste material Substances 0.000 title claims abstract description 24
- 238000004519 manufacturing process Methods 0.000 title claims description 13
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 61
- 238000001816 cooling Methods 0.000 claims abstract description 22
- 238000009835 boiling Methods 0.000 claims abstract description 8
- 239000000203 mixture Substances 0.000 claims abstract description 6
- 239000000654 additive Substances 0.000 claims abstract description 3
- 239000000463 material Substances 0.000 claims description 28
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 21
- 239000000155 melt Substances 0.000 claims description 12
- 239000000377 silicon dioxide Substances 0.000 claims description 5
- 229910017344 Fe2 O3 Inorganic materials 0.000 claims description 3
- 229910052681 coesite Inorganic materials 0.000 claims description 3
- 229910052906 cristobalite Inorganic materials 0.000 claims description 3
- 235000012239 silicon dioxide Nutrition 0.000 claims description 3
- 229910052682 stishovite Inorganic materials 0.000 claims description 3
- 229910052905 tridymite Inorganic materials 0.000 claims description 3
- 230000000996 additive effect Effects 0.000 claims 1
- 238000000034 method Methods 0.000 abstract description 21
- 239000007788 liquid Substances 0.000 abstract description 15
- 239000002245 particle Substances 0.000 abstract description 13
- 239000004576 sand Substances 0.000 abstract description 12
- 239000010802 sludge Substances 0.000 abstract description 9
- 239000004566 building material Substances 0.000 abstract description 2
- 238000002156 mixing Methods 0.000 abstract description 2
- 238000010335 hydrothermal treatment Methods 0.000 description 9
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 6
- 238000010276 construction Methods 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 239000004570 mortar (masonry) Substances 0.000 description 5
- 239000003245 coal Substances 0.000 description 4
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 3
- 235000011941 Tilia x europaea Nutrition 0.000 description 3
- 239000004567 concrete Substances 0.000 description 3
- 229910052742 iron Inorganic materials 0.000 description 3
- 239000004571 lime Substances 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- 239000010801 sewage sludge Substances 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- 230000002378 acidificating effect Effects 0.000 description 2
- 239000002956 ash Substances 0.000 description 2
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 2
- 239000000920 calcium hydroxide Substances 0.000 description 2
- 235000011116 calcium hydroxide Nutrition 0.000 description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 2
- 239000000571 coke Substances 0.000 description 2
- 230000006835 compression Effects 0.000 description 2
- 238000007906 compression Methods 0.000 description 2
- 239000004035 construction material Substances 0.000 description 2
- 239000000498 cooling water Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000010979 pH adjustment Methods 0.000 description 2
- 239000004575 stone Substances 0.000 description 2
- 229910004298 SiO 2 Inorganic materials 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 239000002585 base Substances 0.000 description 1
- 238000009412 basement excavation Methods 0.000 description 1
- 239000000378 calcium silicate Substances 0.000 description 1
- 229910052918 calcium silicate Inorganic materials 0.000 description 1
- OYACROKNLOSFPA-UHFFFAOYSA-N calcium;dioxido(oxo)silane Chemical compound [Ca+2].[O-][Si]([O-])=O OYACROKNLOSFPA-UHFFFAOYSA-N 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 239000011083 cement mortar Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 239000010883 coal ash Substances 0.000 description 1
- 238000005056 compaction Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- -1 etc. Substances 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 238000009415 formwork Methods 0.000 description 1
- 238000010413 gardening Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 238000002309 gasification Methods 0.000 description 1
- 235000014413 iron hydroxide Nutrition 0.000 description 1
- NCNCGGDMXMBVIA-UHFFFAOYSA-L iron(ii) hydroxide Chemical compound [OH-].[OH-].[Fe+2] NCNCGGDMXMBVIA-UHFFFAOYSA-L 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 235000011121 sodium hydroxide Nutrition 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000012798 spherical particle Substances 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 235000011149 sulphuric acid Nutrition 0.000 description 1
- 238000010998 test method Methods 0.000 description 1
- 238000004056 waste incineration Methods 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Landscapes
- Processing Of Solid Wastes (AREA)
- Curing Cements, Concrete, And Artificial Stone (AREA)
Abstract
Description
【0001】0001
【産業上の利用分野】本発明は、建設汚泥(シールド掘
削工法、杭打ち工法等による工事で排出される泥土)、
上下水道汚泥、都市ゴミ焼却灰、シュレッダーダスト焼
却灰、食品・紙パルプ工場からの汚泥、石炭灰等の廃棄
物を溶融処理して、高強度で表面に凹凸のあるスラグを
製造する方法に関するものである。本発明の方法により
製造されたスラグは、土工事材(サンドドレーン材、サ
ンドコンパクション材、埋戻材等)、舗装材(路盤材、
歩道材等)、コンクリート骨材、壁材、園芸材、ろ過材
、建材等に利用することができる。[Industrial Application Field] The present invention is applicable to construction sludge (sludge discharged from construction work using shield excavation method, pile driving method, etc.),
A method for manufacturing slag with high strength and an uneven surface by melting and processing wastes such as water and sewage sludge, municipal waste incineration ash, shredder dust incineration ash, sludge from food and pulp and paper factories, and coal ash. It is. The slag produced by the method of the present invention can be used as earthwork materials (sand drain materials, sand compaction materials, backfill materials, etc.), paving materials (road base materials,
It can be used for materials such as sidewalk materials, concrete aggregates, wall materials, gardening materials, filter materials, and building materials.
【0002】0002
【従来の技術】近年、廃棄物処分地確保が困難となって
おり、廃棄物の安定化、減容化のみならず、再資源化が
求められている。従来、水冷によるスラグ製造方法とし
て廃棄物に必要に応じて、融点降下の目的でCaO源材
等を加えて、1300〜1600℃の温度で溶融し、溶
融炉雰囲気圧力の沸騰温度よりも0〜80℃低い範囲で
、成行きの温度(昼夜、スラグ量等で温度が変化)で水
中へ流下させてスラグを製造する方法が知られている。
また、液pH調整を実施しておらず、液pHは、通常6
.0〜9.0で、殆どの場合、pH7.0〜8.0であ
った。したがって高強度で、表面に凹凸があり、品質の
安定したスラグの製造が困難であった。BACKGROUND OF THE INVENTION In recent years, it has become difficult to secure waste disposal sites, and there is a demand for not only stabilization and volume reduction of waste, but also recycling. Conventionally, in the water-cooled slag manufacturing method, CaO source material etc. are added to the waste as necessary for the purpose of lowering the melting point, and the waste is melted at a temperature of 1300 to 1600°C, and the temperature is lower than the boiling temperature of the melting furnace atmosphere pressure. A method is known in which slag is produced by flowing it into water at a normal temperature (temperature changes depending on day and night, amount of slag, etc.) within a range of 80°C lower. In addition, the liquid pH is not adjusted, and the liquid pH is usually 6.
.. 0 to 9.0, and in most cases the pH was 7.0 to 8.0. Therefore, it has been difficult to produce slag with high strength, unevenness on the surface, and stable quality.
【0003】また、特開昭63−20099号公報には
、溶融炉から落下する溶融スラグを冷却手段及び加振手
段を備えた受容器に受け、間接的に冷却して粒状の固化
体とし、連続的に取り出す下水汚泥溶融スラグの処理方
法が記載されている。Furthermore, Japanese Patent Application Laid-Open No. 63-20099 discloses that the molten slag falling from the melting furnace is received in a receiver equipped with cooling means and vibration means, and is indirectly cooled to form a granular solidified body. A method for treating continuously extracted sewage sludge molten slag is described.
【0004】0004
【発明が解決しようとする課題】上記の特開昭63−2
0099号公報記載の方法においては、80〜350℃
の高い温度でスラグを冷却しており、本発明と温度範囲
の一部が共通するが、間接水冷又は間接空冷を行うもの
であるので、冷却部面積が小さく、廃棄物溶融による大
量の融液を、同一温度で安定的に冷却し、かつ、搬送す
るのは困難である。また、間接冷却であるから、液pH
の制御によりスラグを水熱処理することができない。[Problem to be solved by the invention] The above-mentioned Japanese Patent Application Laid-Open No. 63-2
In the method described in No. 0099, the temperature is 80 to 350°C.
The slag is cooled at a high temperature, which shares a part of the temperature range with the present invention, but since indirect water cooling or indirect air cooling is performed, the area of the cooling section is small and a large amount of melted liquid is generated by melting the waste. It is difficult to stably cool and transport materials at the same temperature. In addition, since indirect cooling is used, the liquid pH
It is not possible to hydrothermally treat slag due to the control of
【0005】また、上記の従来技術では、次の4つを満
足する水冷スラグが得られない。
(1) 天然砂並みの高強度スラグ、(2) 表面
に凹凸を有したスラグ、(3) 土木建築資材等とし
ての適正粒度分布を有したスラグ、(4) 品質の安
定したスラグ、本発明者らは、上記の(1)〜(4)を
満足するスラグを得るために、種々研究した結果、溶融
炉雰囲気圧力の沸騰温度よりも2〜50℃低い範囲で±
10℃に維持され、又は/及び液pHが8.0〜13.
0の熱水中に流下させて冷却することで、(1)〜(4
)を満足するスラグを得ることができることを知見した
。さらに、破砕後のスラグを融液冷却用の熱水と同性状
の熱水中で処理することにより、スラグ表面の凹凸を大
きくすることができることを知見した。本発明は、上記
の知見に基づいてなされたもので、高強度で表面に凹凸
を有するスラグを得ることができるスラグの製造方法を
提供することを目的とするものである。[0005] Furthermore, with the above-mentioned conventional techniques, water-cooled slag that satisfies the following four conditions cannot be obtained. (1) High-strength slag comparable to natural sand, (2) Slag with uneven surface, (3) Slag with appropriate particle size distribution for civil engineering and construction materials, (4) Slag with stable quality, the present invention In order to obtain a slag that satisfies the above (1) to (4), they have conducted various studies and found that the temperature range is ±2 to 50 degrees Celsius lower than the boiling temperature of the melting furnace atmosphere pressure.
The temperature is maintained at 10°C, and/or the liquid pH is maintained at 8.0-13.
(1) to (4) are cooled by flowing down into hot water of 0.
) It was discovered that it is possible to obtain a slag that satisfies the following. Furthermore, it was discovered that by treating the crushed slag in hot water having the same properties as the hot water used to cool the melt, it was possible to increase the roughness of the slag surface. The present invention has been made based on the above findings, and an object of the present invention is to provide a method for manufacturing slag that can produce a slag with high strength and an uneven surface.
【0006】[0006]
【課題を解決するための手段及び作用】上記の目的を達
成するために、請求項1の廃棄物溶融によるスラグの製
造方法は、図1に示すように、廃棄物を溶融した後、溶
融炉雰囲気圧力の沸騰温度よりも2〜50℃低い範囲で
±10℃に維持された熱水中に、融液を流下・冷却して
スラグを得ることを特徴としている。10は溶融炉、1
2は水冷装置、14は熱水容器、16は破砕機、18は
ポンプである。図1において、溶融炉雰囲気圧力の沸騰
温度よりも2〜50℃、望ましくは5〜20℃低い範囲
で±10℃、望ましくは±5℃に維持された循環熱水中
に融液を流下させて冷却することにより、スラグが製造
される。そして、破砕機16により破砕することにより
製品となる。循環熱水の温度は、例えば、熱水容器14
内の熱水温度を検出し冷水供給量を調節することにより
制御される。[Means and operations for solving the problems] In order to achieve the above object, the method of manufacturing slag by melting waste according to claim 1, as shown in FIG. The method is characterized in that slag is obtained by flowing the melt into hot water maintained at ±10°C within a range of 2 to 50°C lower than the boiling temperature of the atmospheric pressure. 10 is a melting furnace, 1
2 is a water cooling device, 14 is a hot water container, 16 is a crusher, and 18 is a pump. In Figure 1, the melt is allowed to flow down into circulating hot water maintained at ±10°C, preferably ±5°C, within a range of 2 to 50°C, preferably 5 to 20°C, lower than the boiling temperature of the melting furnace atmospheric pressure. By cooling the slag, slag is produced. A product is then crushed by a crusher 16. The temperature of the circulating hot water is, for example, the temperature of the hot water container 14.
It is controlled by detecting the temperature of hot water inside and adjusting the amount of cold water supplied.
【0007】また、請求項2の方法は、廃棄物を溶融し
た後、pH8.0〜13.0に調整された熱水中に、融
液を流下・冷却してスラグを得ることを特徴としている
。
熱水のpH調整は、循環系、例えば熱水容器14にpH
調整材を添加することによりなされ、pH8.0〜13
.0、望ましくはpH9.0〜12.0に調整される。
また、請求項3の方法は、請求項1又は2の方法におい
て、廃棄物にCaO源材、Fe2 O3 源材、SiO
2 源材からなる群より選ばれた添加材を加えて組成調
整した後、溶融することを特徴としている。さらに、請
求項4の方法は、請求項1、2又は3の方法において、
図2に示すように、スラグを破砕した後、破砕物を融液
冷却用の熱水と同じ性状の熱水中で0.5〜20時間処
理することを特徴としている。図2は、破砕機16で破
砕したスラグを、水熱処理容器20内の融液冷却用の熱
水中、又は融液冷却用の熱水と同性状の熱水中で処理す
ることにより、品質の向上したスラグを製造する方法を
示している。22は固液分離機、24はポンプである。[0007] Furthermore, the method according to claim 2 is characterized in that after melting the waste, the melt is poured into hot water whose pH is adjusted to 8.0 to 13.0 and cooled to obtain slag. There is. The pH adjustment of the hot water is carried out by adjusting the pH of the circulating system, for example, the hot water container 14.
This is done by adding an adjusting agent, and the pH is adjusted to 8.0 to 13.
.. 0, preferably adjusted to pH 9.0 to 12.0. Further, the method according to claim 3 is the method according to claim 1 or 2, in which the waste contains CaO source material, Fe2 O3 source material, SiO
2. It is characterized by adding additives selected from the group consisting of source materials to adjust the composition and then melting. Furthermore, the method of claim 4 is the method of claim 1, 2 or 3, comprising:
As shown in FIG. 2, the method is characterized in that after the slag is crushed, the crushed material is treated in hot water having the same properties as the hot water for cooling the melt for 0.5 to 20 hours. FIG. 2 shows that the slag crushed by the crusher 16 is treated in hot water for cooling the melt in the hydrothermal treatment container 20, or in hot water having the same properties as the hot water for cooling the melt. A method for producing improved slag is shown. 22 is a solid-liquid separator, and 24 is a pump.
【0008】溶融炉雰囲気圧力は、通常は常圧の場合が
多いが、石炭ガス化炉等では雰囲気圧力は加圧状態とな
る。常圧状態の場合は、熱水温度は50〜98℃、望ま
しくは80〜95℃で±10℃、望ましくは±5℃に維
持されるが、加圧状態の場合は、熱水温度は水の沸騰温
度よりも2〜50℃、望ましくは5〜20℃低い範囲で
±10℃、望ましくは±5℃に維持される。石炭ガス化
炉のような高圧下では、水冷装置12からのスラグの取
出しは、水冷装置底部からの取出しとなる。[0008] The atmospheric pressure in a melting furnace is usually normal pressure in many cases, but in a coal gasification furnace, etc., the atmospheric pressure is in a pressurized state. In the case of a normal pressure state, the hot water temperature is maintained at 50 to 98 °C, preferably 80 to 95 °C, ±10 °C, preferably ±5 °C, but in the case of a pressurized state, the hot water temperature is The temperature is maintained within a range of 2 to 50°C, preferably 5 to 20°C lower than the boiling temperature of ±10°C, preferably ±5°C. Under high pressure conditions such as in a coal gasifier, slag is removed from the water cooling device 12 from the bottom of the water cooling device.
【0009】溶融炉10としては、電気、ガス、油、石
炭、コークス、可燃性ゴミ、廃材等を熱源とした電気炉
、表面溶融炉、旋回溶融炉、コークスベッド溶融炉等が
用いられる。水冷装置12としては、容器内に熱水を充
満させてポンプ18で循環しながら温度、及び/又は液
pHをコントロールするもの等が用いられる。破砕機1
6としては、回転数を調整することで粒度調整が容易な
ハンマーミル等の衝撃式破砕機が用いられる。水熱処理
容器20としては、外部ジャケットを熱水循環により保
温し、スラグを底部より抜き出す型式、又はコンベアで
上部より抜き出す型式のもの等が用いられる。As the melting furnace 10, an electric furnace, a surface melting furnace, a rotating melting furnace, a coke bed melting furnace, etc. using electricity, gas, oil, coal, coke, combustible garbage, waste materials, etc. as a heat source can be used. As the water cooling device 12, a device is used that fills a container with hot water and circulates it with a pump 18 while controlling the temperature and/or the pH of the liquid. Crusher 1
As No. 6, an impact crusher such as a hammer mill is used, which allows particle size to be easily adjusted by adjusting the rotation speed. As the hydrothermal treatment vessel 20, a type in which the external jacket is kept warm by circulating hot water and the slag is extracted from the bottom, or a type in which the slag is extracted from the top using a conveyor, etc. is used.
【0010】熱水pH調整材としては、アルカリ性の廃
棄物、石灰、水酸化鉄、カセイソーダ等が用いられる。
また、酸性側に調整する場合は、硫酸、塩酸等が用いら
れる。組成調整用のCaO源材としては、石灰、貝殻、
高炉スラグ、コンクリート片、石灰系下水汚泥等が用い
られ、Fe2 O3 源材としては、鉄鉱石、鉄鋼汚泥
、酸化鉄等が用いられ、SiO2 源材としては、ケイ
砂、ケイ石、砕石、使用済み鋳物砂、残土等が用いられ
る。冷却水(熱水)の温度が、溶融炉雰囲気圧力の沸騰
温度よりも50℃を越えて低い場合、例えば常圧下にお
いて、冷却水温が、50℃未満であると粒径が大きく、
表面に凹凸のある高強度スラグが得られず、98℃を越
えると、発生スチームが溶融炉に悪影響を及ぼす。さら
に、液pHが8.0〜13.0あれば、スラグが水熱処
理され、表面にケイ酸カルシウム水和物等が生成するな
どにより、スラグの強度が大となり、表面の凹凸が大き
くなる。液pHが8.0未満であると水熱処理効果が不
十分となり、液pHが13.0を越えるとアルカリ残存
量が多くなるなどの問題がある。また、水熱処理時間が
0.5時間未満であると水熱処理効果が不十分であり、
20時間を越えると水熱処理容器が大きくなって経済性
に問題がある。
さらに、破砕後に水熱処理すれば、すべての表面が水熱
処理されるのでスラグ品質がより向上する。また、水温
が±10℃よりも変動が大きくなれば、スラグ品質が変
動する。すなわち、低い側になれば、粒径が小さくなり
、強度が低下し、高い側となれば、粒径が大きくなり、
かつ、強度が大きくなる。[0010] As the hydrothermal pH adjusting material, alkaline waste, lime, iron hydroxide, caustic soda, etc. are used. Moreover, when adjusting to the acidic side, sulfuric acid, hydrochloric acid, etc. are used. CaO source materials for composition adjustment include lime, shells,
Blast furnace slag, concrete pieces, lime-based sewage sludge, etc. are used, Fe2 O3 source materials include iron ore, steel sludge, iron oxide, etc., and SiO2 source materials include silica sand, silica stone, crushed stone, etc. Finished foundry sand, leftover soil, etc. are used. If the temperature of the cooling water (hot water) is more than 50°C lower than the boiling temperature of the melting furnace atmospheric pressure, for example under normal pressure, if the cooling water temperature is less than 50°C, the particle size will be large;
If a high-strength slag with an uneven surface cannot be obtained and the temperature exceeds 98°C, the generated steam will have an adverse effect on the melting furnace. Further, if the liquid pH is 8.0 to 13.0, the slag is hydrothermally treated and calcium silicate hydrate is generated on the surface, thereby increasing the strength of the slag and increasing the surface irregularities. If the liquid pH is less than 8.0, the hydrothermal treatment effect will be insufficient, and if the liquid pH exceeds 13.0, there will be problems such as an increased amount of alkali remaining. Furthermore, if the hydrothermal treatment time is less than 0.5 hours, the hydrothermal treatment effect will be insufficient;
If the treatment time exceeds 20 hours, the hydrothermal treatment container becomes large and there is a problem in economical efficiency. Furthermore, if hydrothermal treatment is performed after crushing, the quality of the slag will be further improved since all surfaces will be hydrothermally treated. Furthermore, if the water temperature fluctuates more than ±10°C, the slag quality will fluctuate. In other words, when it is on the low side, the particle size becomes small and the strength decreases, and when it is on the high side, the particle size becomes large.
Moreover, the strength increases.
【0011】廃棄物にCaO源材を加えて、溶流点を1
350℃以下とし、1400℃〜1600℃で溶融する
とスラグ量の変化、昼と夜との外気温変化等による炉の
放熱量などの変化によって、融液の流動性変化が小さく
なり、融液状態で安定して熱水中に流下し、高品質で、
かつ、品質の安定したスラグが得られる。破砕機16の
回転数を調整すると、スラグの粒度が異なるので、各用
途による適正粒度とするために、回転数を変えて破砕す
るか、異なる回転数によるスラグを混合するなどの方法
が用いられる。なお、溶流点とは、JIS M 8
801(石炭類の試験方法)に準拠し、3角錐(2.7
×2.7×3.0×8H mm)を製作した後、電気炉
に入れ、5℃/分で昇温し、三角錐の高さが幅のほぼ1
/6になった時の温度を言う。[0011] By adding CaO source material to the waste, the melting point is increased to 1.
If the temperature is 350°C or lower and melting is performed at 1400°C to 1600°C, changes in the fluidity of the melt will be small due to changes in the amount of slag, changes in the amount of heat released from the furnace due to changes in outside temperature between day and night, etc., and the state of the melt will change. It flows stably into hot water and is of high quality.
Moreover, slag with stable quality can be obtained. If the rotation speed of the crusher 16 is adjusted, the particle size of the slag will differ, so in order to obtain the appropriate particle size for each application, methods such as changing the rotation speed or mixing slags produced at different rotation speeds are used. . Note that the melting point is defined as JIS M 8.
801 (test method for coal), triangular pyramid (2.7
x 2.7 x 3.0 x 8H mm), it was placed in an electric furnace and heated at a rate of 5°C/min until the height of the triangular pyramid was approximately 1 inch of the width.
Say the temperature when it reaches /6.
【0012】0012
【実施例】以下、本発明の実施例について説明する。圧
壊強度は、木屋式硬度計を用い、3mmの球形粒子が破
壊する強度である。
実施例1
建設汚泥100部に鉄鉱石20部を加えて原料調整をし
た。この混合物の溶流点は1300℃で、旋回溶融炉を
用いて1450℃で溶融し、冷却用の熱水の水温、液p
H(Ca(OH)2 で調整)を1時間サイクルで変化
させ、種々の水冷条件下で黒色のスラグを製造した。回
転数2500rpmで破砕したスラグ製造時の水温pH
と圧壊強度との関係は図3に示すとおり、水温が高いほ
ど大きくなり、かつ、pHが8.0よりも10.0の方
が大きくなっていた。なお、比較のため天然砕砂(硬質
砂岩)の圧壊強度を測定したところ、19kg/3mm
φであり、水温が約600℃以上で天然砕砂以上の強度
を有するスラグとなった。また、製造時の水温と250
0rpmの回転数で破砕した後の5mm以上スラグの割
合の関係を図4に示す。図4に示すとおり、水温が高い
ほど多くなり、かつ、液pHが8.0よりも10.0の
方が多くなっており、5mm以上の粒子が有効なテラゾ
タイルのような美観材骨材への適用が図れる。[Examples] Examples of the present invention will be described below. The crushing strength is the strength at which a 3 mm spherical particle breaks using a Kiya type hardness tester. Example 1 Raw materials were prepared by adding 20 parts of iron ore to 100 parts of construction sludge. The melting point of this mixture is 1300°C, and it is melted at 1450°C using a rotating melting furnace.
H (adjusted with Ca(OH)2) was varied in 1 hour cycles to produce black slag under various water cooling conditions. Water temperature and pH when producing slag crushed at a rotation speed of 2500 rpm
As shown in FIG. 3, the relationship between water temperature and crushing strength increased as the water temperature increased, and was greater at pH 10.0 than at pH 8.0. For comparison, we measured the crushing strength of natural crushed sand (hard sandstone) and found that it was 19 kg/3 mm.
φ, and when the water temperature was about 600° C. or higher, the slag had a strength higher than that of natural crushed sand. Also, the water temperature at the time of manufacture and 250
FIG. 4 shows the relationship between the percentage of slag with a diameter of 5 mm or more after crushing at a rotation speed of 0 rpm. As shown in Figure 4, the higher the water temperature, the higher the amount, and the amount is higher when the liquid pH is 10.0 than 8.0, and particles of 5 mm or more are effective for aesthetic aggregates such as terrazzo tiles. can be applied.
【0013】実施例2
乾燥した建設汚泥のみを原料とし、旋回溶融炉を用いて
1550℃で溶融し、種々の水冷条件下でスラグを製造
し、破砕機の回転数を3500rpmとして破砕した。
得られたスラグを用い、水セメント比50%、フロー値
190±5mmでボルトランドセメントによるモルタル
を作成し、5φ×10cmの型枠に流し込み20℃で1
日養生後に脱形し、さらに、6日養生して圧縮強度を測
定した。製造時の熱水のpH、温度とモルタルの7日養
生圧縮強度との関係を図5に示す。図5から、水温が高
いほどモルタル強度は高く、かつ、液pHが8.0〜1
3.0で最大となっていることがわかる。なお、pH調
整において、アルカリ性側はCa(OH)2 を用いて
行い、酸性側はH2 SO4 を用いて行った。Example 2 Using only dried construction sludge as a raw material, slag was melted at 1550° C. using a rotating melting furnace to produce slag under various water-cooling conditions, and crushed at a crusher rotation speed of 3500 rpm. Using the obtained slag, a boltland cement mortar was prepared with a water-cement ratio of 50% and a flow value of 190±5mm, and poured into a 5φ x 10cm formwork and heated at 20°C.
After curing for one day, it was removed from the shape, further cured for 6 days, and the compressive strength was measured. FIG. 5 shows the relationship between the pH and temperature of hot water during production and the compressive strength of mortar after 7 days of curing. From Figure 5, the higher the water temperature, the higher the mortar strength, and the higher the liquid pH is 8.0 to 1.
It can be seen that it is maximum at 3.0. In addition, in pH adjustment, the alkaline side was performed using Ca(OH)2, and the acidic side was performed using H2SO4.
【0014】実施例3
建設汚泥100部に鉄鉱石20部を加えて原料調整した
。この混合物を旋回溶融炉を用いて1450℃で溶融し
、温度90℃、pH10.0の熱水中に投下してスラグ
とした。このスラグを破砕機の回転数を3500rpm
として破砕した。得られたスラグは黒色で、JIS
A 5004(コンクリート砕砂)を満足する粒度分
布を有していた。このスラグを冷却用熱水(温度90℃
、pH10.0)下で2時間処理した。圧壊強度は23
kg/3mmφであり、モルタルの7日強度(圧縮)は
470kg/cm2 であり、天然砕砂によるモルタル
の7日強度(圧縮)420kg/cm2よりも約10%
高い値を示し、破砕後に水熱処理することで、スラグ単
体ならびにモルタルはより高強度となった。Example 3 A raw material was prepared by adding 20 parts of iron ore to 100 parts of construction sludge. This mixture was melted at 1450° C. using a rotating melting furnace and poured into hot water at a temperature of 90° C. and a pH of 10.0 to form slag. The rotation speed of this slag crusher was set to 3500 rpm.
It was crushed as The obtained slag is black and JIS
It had a particle size distribution that satisfied A5004 (crushed concrete sand). This slag is heated with hot water (temperature 90℃) for cooling.
, pH 10.0) for 2 hours. The crushing strength is 23
kg/3mmφ, and the 7-day strength (compression) of the mortar is 470 kg/cm2, which is approximately 10% higher than the 7-day strength (compression) of 420 kg/cm2 of mortar made from natural crushed sand.
It showed a high value, and by hydrothermal treatment after crushing, the slag itself and the mortar became even stronger.
【0015】[0015]
【発明の効果】本発明は上記のように構成されているの
で、つぎのような効果を奏する。
(1) 高強度で表面に凹凸のあるスラグが得られ、
天然砕砂、砂代替として土木建築資材等として再資源化
を図ることができる。
(2) 得られたスラグを破砕する場合は、破砕機の
回転数を小さくすることにより、粒径5mm以上の高強
度スラグが多く得られ、かつ、色が黒色であるので、テ
ラゾタイルのような付加価値の高い美観材の骨材へ適用
することができる。[Effects of the Invention] Since the present invention is constructed as described above, it has the following effects. (1) A slag with high strength and uneven surface can be obtained.
It can be recycled as a civil engineering and construction material as a substitute for natural crushed sand or sand. (2) When crushing the obtained slag, by reducing the rotation speed of the crusher, a large amount of high-strength slag with a particle size of 5 mm or more can be obtained, and since it is black in color, it can be used for slag such as terrazzo tiles. It can be applied to aggregates for aesthetic materials with high added value.
【図1】本発明の廃棄物溶融によるスラグの製造方法の
一実施例を示す工程図である。FIG. 1 is a process diagram showing an embodiment of the method for producing slag by melting waste of the present invention.
【図2】本発明の方法の他の実施例を示す工程図である
。FIG. 2 is a process diagram showing another embodiment of the method of the present invention.
【図3】熱水の水温とスラグ圧壊強度との関係を示すグ
ラフである。FIG. 3 is a graph showing the relationship between hot water temperature and slag crushing strength.
【図4】熱水の水温とスラグ破砕後の粒径5mm以上ス
ラグ割合との関係を示すグラフである。FIG. 4 is a graph showing the relationship between the temperature of hot water and the proportion of slag with a particle size of 5 mm or more after slag crushing.
【図5】熱水のpHと7日養生後のスラグ圧縮強度との
関係を示すグラフである。FIG. 5 is a graph showing the relationship between the pH of hot water and the compressive strength of slag after 7 days of curing.
10 溶融炉 12 水冷装置 14 熱水容器 16 破砕機 18 ポンプ 20 水熱処理容器 22 固液分離機 24 ポンプ 10 Melting furnace 12 Water cooling device 14 Hot water container 16 Crushing machine 18 Pump 20 Hydrothermal treatment container 22 Solid-liquid separator 24 Pump
Claims (4)
力の沸騰温度よりも2〜50℃低い範囲で±10℃に維
持された熱水中に、融液を流下・冷却してスラグを得る
ことを特徴とする廃棄物溶融によるスラグの製造方法。Claim 1: After melting the waste, the melt is cooled by flowing down into hot water maintained at ±10°C within a range of 2 to 50°C lower than the boiling temperature of the melting furnace atmospheric pressure to form slag. A method for producing slag by melting waste, characterized in that:
3.0に調整された熱水中に、融液を流下・冷却してス
ラグを得ることを特徴とする廃棄物溶融によるスラグの
製造方法。[Claim 2] After melting the waste, the pH is 8.0 to 1.
A method for producing slag by melting waste, characterized in that slag is obtained by flowing and cooling the melt in hot water adjusted to a temperature of 3.0.
源材、SiO2 源材からなる群より選ばれた添加材を
加えて組成調整した後、溶融することを特徴とする請求
項1又は2記載の廃棄物溶融によるスラグの製造方法。[Claim 3] CaO source material, Fe2 O3 in waste
3. The method for producing slag by melting waste according to claim 1, wherein the slag is melted after adjusting the composition by adding an additive material selected from the group consisting of SiO2 source material and SiO2 source material.
却用の熱水と同じ性状の熱水中で0.5〜20時間処理
することを特徴とする請求項1、2又は3記載の廃棄物
溶融によるスラグの製造方法。4. After crushing the slag, the crushed material is treated in hot water having the same properties as the hot water for cooling the melt for 0.5 to 20 hours. A method for producing slag by melting waste.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP12509391A JPH0829312B2 (en) | 1991-04-26 | 1991-04-26 | Method for producing slag by melting waste |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP12509391A JPH0829312B2 (en) | 1991-04-26 | 1991-04-26 | Method for producing slag by melting waste |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH04326975A true JPH04326975A (en) | 1992-11-16 |
JPH0829312B2 JPH0829312B2 (en) | 1996-03-27 |
Family
ID=14901676
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP12509391A Expired - Fee Related JPH0829312B2 (en) | 1991-04-26 | 1991-04-26 | Method for producing slag by melting waste |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH0829312B2 (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20010017293A (en) * | 1999-08-10 | 2001-03-05 | 이구택 | A Method for Preparing Water-Granulated Slag Having Low Density |
JP2002346502A (en) * | 2001-05-25 | 2002-12-03 | Fuji Electric Systems Co Ltd | Molten and solidified incinerator ash melting and solidifying method and apparatus and method for using molten and solidified ash |
JP2009207992A (en) * | 2008-03-04 | 2009-09-17 | Central Res Inst Of Electric Power Ind | Manufacturing system and manufacturing method of foamed material |
JP2016077261A (en) * | 2014-10-22 | 2016-05-16 | 株式会社大林組 | Weed-proof material and construction method for the same |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS63205189A (en) * | 1987-02-19 | 1988-08-24 | Daido Steel Co Ltd | Method for solidifying molten slag |
-
1991
- 1991-04-26 JP JP12509391A patent/JPH0829312B2/en not_active Expired - Fee Related
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS63205189A (en) * | 1987-02-19 | 1988-08-24 | Daido Steel Co Ltd | Method for solidifying molten slag |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20010017293A (en) * | 1999-08-10 | 2001-03-05 | 이구택 | A Method for Preparing Water-Granulated Slag Having Low Density |
JP2002346502A (en) * | 2001-05-25 | 2002-12-03 | Fuji Electric Systems Co Ltd | Molten and solidified incinerator ash melting and solidifying method and apparatus and method for using molten and solidified ash |
JP4514363B2 (en) * | 2001-05-25 | 2010-07-28 | メタウォーター株式会社 | Molten solidified product of incinerated ash, method and apparatus for melting and solidifying, and method of using molten solidified product |
JP2009207992A (en) * | 2008-03-04 | 2009-09-17 | Central Res Inst Of Electric Power Ind | Manufacturing system and manufacturing method of foamed material |
JP2016077261A (en) * | 2014-10-22 | 2016-05-16 | 株式会社大林組 | Weed-proof material and construction method for the same |
Also Published As
Publication number | Publication date |
---|---|
JPH0829312B2 (en) | 1996-03-27 |
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