TWI287582B - Improved basic oxygen furnace slag material with ability to inhibit swell again and leaching of heavy metals-Pozzolans addition - Google Patents

Improved basic oxygen furnace slag material with ability to inhibit swell again and leaching of heavy metals-Pozzolans addition Download PDF

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TWI287582B
TWI287582B TW94120132A TW94120132A TWI287582B TW I287582 B TWI287582 B TW I287582B TW 94120132 A TW94120132 A TW 94120132A TW 94120132 A TW94120132 A TW 94120132A TW I287582 B TWI287582 B TW I287582B
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heavy metals
rate
stone
leaching
wet
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TW94120132A
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TW200700560A (en
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Chin-Chung Wang
Der-Her Lee
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Chin-Chung Wang
Der-Her Lee
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    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
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    • Y02W30/50Reuse, recycling or recovery technologies

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Abstract

The present invention is to provide a processing method for CSC byproduct, basic oxygen furnace slag, to reduce the leaching of heavy metals and swell again. The present invention uses Pozzolans method utilizing wet-binder method and substitution-wet-binder method to dilute, solidify, and chelate the basic oxygen furnace slag so as to stabilize the basic oxygen furnace slag. The wet-binder method and substitution-wet-binder method used in the present invention belong to Pozzolans addition. The rate of swell again and heavy metals are decreasing with the increasing addition amount of Pozzolans after calculating a series of data. Further, the control mode of the rate of swell again is calculated as Y=5.35X-0.507 and the control mode of the leaching of heavy metals is calculated as Y=729.81X-0.494, wherein Y represents the rate of swell again and the leaching amount of heavy metals respectively, X represents the addition amount of. Considering about the rate of swell again and the leaching amount of heavy metals at the same time, the result showed that the quality requirements of engineering and environment can be met by adding only 8%-50% of Pozzolans. As the leaching of heavy metals, the toxicity characteristic leaching, the leaching of soil contaminants, and the aqua regia digestion test are conducted showing that heavy metals such as chromium, cadmium, plumbum, arsenic, mercury, copper, zinc, nickel, etc., are lower than the control standard of leaching of heavy metals. As the rate of swell again is proceeded under the regulation of CNS 14602 (JIS A5015), the result shows that the rate of swell again is lower than 1.36% which is much lower than 1.5% of the requirement final rate of swell again defined in CNS 14602. The CBR value is more than 133.63% which exceeds in the quality requirement of CBR value for highway base. These results prove that basic oxygen furnace slag may obtain the effects of inhibiting the leaching of heavy metals, reducing the rate of swell again, increasing the shear strength, and improving the bearing-ratio after treatment and becomes excellent filling and construction material used for civil and architect engineering.

Description

1287582 五、發明說明(1) 太^發明所屬之技術領域】 承發明乃以沃 濕裹並用法等工:加波索蘭材料方式,採用濕裹法、取代 趨於穩定。經由1,目的在稀釋、固化、螯合轉爐石使之 波索蘭材料添加;導出回脹率及重金屬隨 5. 35Χ'°·5〇7 ; ^ 曰 降低 其回脹率控制模式為γ = Υ分別為回脹率、界f屬溶出控制模式為γ = 729· 81Χ-。·494式中 再由回脹率及重//屬絡溶出量’Χ為波索蘭材料添加量 •短轉爐石:;;;規:境品質要求。本技術可縮 處理或處置「減量化」、「資源化」、m棄物 定化」的目標,因此本發明所屬技術領域; 範疇。 &馬土木再生材料 (二)、【先前技術】 轉爐石是由多種礦物組成的固熔體,其 灰(f-CaO)、氧化鎂(Mg0)、矽酸三鈣(CaS)、矽酸二鈣 (QS)等,這些組成在驗度高的熔渣内都具有不穩^性,其 中以未反應石灰(f-CaO)水化產生氫氧化鈣體積膨脹最八 大,其次為MgO水化成為氫氧化鎂體積會膨脹;通常含有 修未反應石灰(f-CaO)、氧化鎂(Mg〇)的轉爐石是處於^穩 定狀態,只有當f-CaO、MgO水化消解完成時,才合穩定"。 因此轉爐渣出場後,只作堆積場堆置,待f〜Ca〇、Mg〇完全 水化消解後,再作其他用途,如此相當不經濟,也造=^ 爐石無處堆置的窘境及國家資源的浪費。1287582 V. INSTRUCTIONS INSTRUCTIONS (1) The technical field to which the invention belongs is: The invention is based on the wet wrap and the usage of the work: the gaussaulan material method, which adopts the wet wrap method and replaces it to stabilize. Through 1, the purpose is to dilute, solidify, and chelate the converter stone to add the corsol material; derive the rebound rate and heavy metal with 5. 35 Χ ' ° · 5 〇 7 ; ^ 曰 reduce its rebound rate control mode is γ = Υ 为 回 729 729 回 、 、 、 界 属 属 属 属 属 属 属 属 属 属 属 属 属 属 属· Type 494, by the rate of re-expansion and the amount of heavy / / genus dissolution Χ Χ is the amount of Posolan material added • Short tortstone:;;; Regulation: environmental quality requirements. The present technology can reduce or deal with the goals of "reduction", "resources", and m-distribution, and therefore the technical field to which the present invention pertains. & Ma Tumu Recycled Materials (II), [Prior Art] Converter stone is a solid solution composed of various minerals, such as ash (f-CaO), magnesium oxide (Mg0), tricalcium citrate (CaS), tannic acid Dicalcium (QS), etc., these compositions have instability in the high-calculation slag, in which unreacted lime (f-CaO) hydration produces the largest volume expansion of calcium hydroxide, followed by MgO hydration. The volume of magnesium hydroxide will expand; usually the converter stone containing unreacted lime (f-CaO) and magnesium oxide (Mg〇) is in a stable state, and only when f-CaO and MgO are hydrated and dissolved, Stable ". Therefore, after the converter slag is on the scene, it is only used as a stacking yard. After the f~Ca〇 and Mg〇 are completely hydrated and dissolved, it can be used for other purposes. This is quite uneconomical, and it also creates the dilemma of no-stacking of the hearth and Waste of national resources.

第6頁 1287582 五、發明說明(2) 因為轉爐石具有回脹性,致使其用途受到限制。由於 轉爐石回脹問題尚未能有效解決,故一般僅將之作初步的 填平低窪地的整平處理。 (三)、【發明内容】 本發明為減少轉爐石中重金屬、溶解性鹽類溶出量以稀 釋、固化、螯合使轉爐石趨於穩定,採用濕裹法、取代濕 裹並用法等穩定工法,來稀釋轉爐石中重金屬及鹼的含 量,降低pH值,減少重金屬溶出,相對減少鹼的供應量, 降低轉爐石回脹率。 _本發明採用的穩定方法【一】濕袠法【二】取代濕裹並用 法其方法說明如下: 【一】濕裹法 本發明均選用水泥作為膠結材兼具固化功能〃 多孔質轉爐石顆粒表面,使轉爐石顆粒表面濕裹成一較緻 密的膠結膜’由於水泥和水產生水化作用,促使轉爐石達 到固化效果;其次選用水淬爐石粉、飛灰及電廠底灰等波 索蘭材料,此等材料均屬於波索蘭及膠結材料,除稀 能外並兼具膠結功能,此等材料將與水泥水化產物氫氧化 轉等進行緩慢波索蘭反應,消耗驗離子,同時轉爐石中卜 • aO亦會消解為氫氧化鈣與填縫材進行波索蘭反應,相 地降低f-CaO的含量,使轉爐石更趨穩定。依選用材子 分為(1)水泥底灰濕裹法(2)水泥飛 )/ = 爐石濕裹法等三種。 .、、、衷忐C3)水泥水淬 (1)水泥底灰濕裹法 以2 %水泥加水攪拌成 黏祠狀使之完Page 6 1287582 V. INSTRUCTIONS (2) Because the converter stone has a resilience, its use is limited. Since the problem of converter stone back-expansion has not been effectively solved, it is generally only used as a preliminary leveling treatment for low-lying land. (III), [Summary of the Invention] The present invention is to reduce the amount of heavy metals and dissolved salts in the converter stone to dilute, solidify, and chelate to stabilize the converter stone, and adopts a wet-pack method, a wet-wrap method, and the like. To dilute the content of heavy metals and alkalis in the converter stone, reduce the pH value, reduce the dissolution of heavy metals, relatively reduce the supply of alkali, and reduce the rebound rate of the converter stone. _ The stabilization method adopted by the invention [1] Wet 袠 method [2] replaces the wet wrap and the method is described as follows: [1] Wet Wrap Method The invention uses cement as a cement material and has a solidifying function 多孔 Porous converter stone particles The surface causes the surface of the converter stone to be wet-wrapped into a denser cemented film. The hydration effect of the cement and water promotes the curing effect of the converter stone. Secondly, the water quenching furnace powder, fly ash and power plant bottom ash are used. These materials are all Poislan and cemented materials. In addition to the rare energy, they also have a cementation function. These materials will react with the hydration product of the hydration product of the cement, such as slow-wave solanan reaction, consumption of ions, and converter stone. Zhongbu•aO will also be digested into a corsosol reaction between calcium hydroxide and the joint filler, which will reduce the content of f-CaO and make the converter stone more stable. According to the selection of materials, it is divided into three types: (1) cement bottom ash wet wrap method (2) cement fly) / = hearth wet wrap method. ., ,, Congratulations C3) Cement water quenching (1) Cement bottom ash wet wrap method 2% cement and water are stirred into a sticky shape to complete

1287582 五、發明說明(3) 兼具之表面’再以電廠底灰作為稀釋 化作田 i實後轉爐石的孔隙。本法具有稀釋、固 _以故盖=Ϊ廠底灰作為稀釋劑,以水泥作為固化劑 特性,減少轉爐石中重金屬、ί 孤’員的洛出量,使其更趨於穩定。 (2)=灰濕裹法:以2%水泥加水授拌成黏稠狀使之完 兼i膠:石粒料之表面,再以電廠飛灰作為稀釋 膠結並;Γ充據添加8%電廠飛灰’用以稀釋、 實後轉爐石的孔隙。本法也具有稀釋、 乍用’以電廠飛灰作為稀釋劑, 劑错以改善轉爐石回脹特性。 勹u化 —裹法:以2%水泥加水攪拌成黏稠狀使 為稀ϋ呈赚ϊ爐石粒料之表面,再以水淬爐石粉作 =功能的材料,添加8%水淬爐石粉,用 右= 填充务實後轉爐石的孔隙。本法也具 =盖::作用,以水淬爐石作為稀釋及固化劑, 石回脹特性。依選用材料區分為⑴濕裹 鲁3¾ ^Λ .王取代(2 )濕裹及電廠底灰全取代(3 )濕裹 及局爐石細料全取代等三種。 ” 【二】取代濕裹並用法 取/Λ裹Λ用法除分別以河床細料、電廠底灰及高爐 石細料元王取代轉爐石細料,藉以減少 -轉爐石回脹量,減少轉爐石中重金屬、溶解性鹽類的、=出1287582 V. INSTRUCTIONS (3) The surface of the invention is further reduced by the use of the bottom ash of the power plant as the pore of the converter. The method has the characteristics of diluting and solidifying, so that the bottom of the plant is used as a diluent, and the cement is used as a curing agent to reduce the amount of heavy metals in the converter stone and to make it more stable. (2)=Gray wet wrap method: Mix 2% cement and water to make it viscous and make it the same: the surface of the stone material, and then use the fly ash of the power plant as the diluted cement; The ash is used to dilute and stabilize the pores of the converter stone. This method also has the function of diluting and using the power plant fly ash as a diluent to improve the converter's re-expansion characteristics.勹uhua-wrapping method: 2% cement and water are stirred into a viscous shape to make the surface of the granulated stone granules thin, and then water quenched ston furnace powder as the functional material, adding 8% water quenching furnace powder, Fill right with the right = fill the pores of the converter. This method also has a cover:: role, with water quenching furnace as a dilution and curing agent, stone back expansion characteristics. According to the selected materials, it is divided into three types: (1) wet wrap, 33⁄4 ^ Λ , king replacement ( 2 ) wet wrap and complete replacement of power plant bottom ash (3 ) wet wrap and full replacement of calcareous stone. [2] Instead of wet wrap and use / Λ Λ Λ Λ 除 除 Λ Λ Λ Λ Λ Λ Λ Λ Λ Λ Λ Λ 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河 河Medium heavy metals, soluble salts, = out

1287582 五、發明說明(4) 量。再以水泥作為固化劑濕裹在轉爐石表面,藉以改善轉 爐石工程特性。 (1 )濕裹及河床細料全取代:以2%水泥加水攪拌成黏稠狀 使之完全包裹於轉爐石粒料之表面,然後以河床細料 完全取代轉爐石細料,目的以河床細料作為稀釋劑, 以水泥作為固化劑,藉以減少轉爐石用量,降低轉爐 石回脹量,減少轉爐石中重金屬、溶解性鹽類的溶出 量。 (2)濕裹及電廠底灰全取代:以2%水泥加水攪拌成黏稠狀 使之完全包袠於轉爐石粒料之表面,然後以電廠底灰 完全取代轉爐石細料,目的以電廄底灰作為稀釋劑, 以水泥作為固化劑,藉以改善轉爐石特性。 -(3 )濕衷及焉爐石細料全取代··以2 %水泥加水擾掉成黏 狀使之完全包裹於轉爐石粒料之表面,然後以^爐 細料完全取代轉爐石細料,目的以高爐石細料^ = 釋劑,以水泥作為固化劑,藉以改善轉爐石特性γ稀 兩者工法所添加材料都是波索蘭材料,主要彳。1287582 V. Description of invention (4) Quantity. The cement is used as a curing agent to wet the surface of the converter stone to improve the engineering properties of the converter stone. (1) Wet wrap and riverbed fine material are completely replaced: 2% cement is mixed with water to form a viscous shape so that it is completely wrapped on the surface of the converter stone pellets, and then the converter stone fine material is completely replaced by the river bed fine material, aiming at the river bed fine material. As a diluent, cement is used as a curing agent to reduce the amount of converter stone, reduce the amount of converter stone swell, and reduce the amount of heavy metals and dissolved salts in the converter stone. (2) Wet wrap and complete replacement of bottom ash in power plant: stir it with 2% cement and water to make it completely covered on the surface of converter stone, and then completely replace the converter stone with the bottom ash of the power plant. The bottom ash is used as a diluent, and cement is used as a curing agent to improve the characteristics of the converter stone. - (3) Wet and kiln stone fines are completely replaced. · 2% cement and water are disturbed to form a sticky shape so that it is completely wrapped on the surface of the converter stone pellets, and then the converter stone fine material is completely replaced by the furnace fine material. The purpose is to use blast furnace stone fine material ^ = release agent, cement as curing agent, to improve the characteristics of converter stone γ thinning. The materials added are all Poislan materials, mainly 彳.

CaO、Si02、FeO、MgO、Na20、Al2〇3、Ti2〇 等組成物^由 ::濕袠法、取代及濕裹並用法都是波索蘭材料、: 因此如何延伸此添加波索蘭材料的觀念,曰日—,、、加法, J ΐ波ί ?材料添加量與回脹率、波索蘭:料添:]:驗推 金屬溶出量的關係。 竹添加量與重Compositions such as CaO, SiO2, FeO, MgO, Na20, Al2〇3, Ti2〇, etc.:: Wet 袠 method, substitution and wet wrap are all uses of Possolan materials, so how to extend this added Possolan material The concept, the next day -,,, addition, J ΐ ί ? material addition and back expansion rate, Possolan: material added:]: the relationship between the amount of metal elution. Bamboo addition and weight

!287S82 五、發明說明(5) 2則為游離石灰(f-Ca0)分別為〗02%、4 6%及6 8%的各種 =法中利用CNS 14602(JIS A5015)方法所測得結果,當轉 關:==;;〇2%時,推導出波索蘭材料添加量與回脹率 5 I*4''1·273 ; 中yl , * f_Ca〇:6· 8%時,其關係式為Υ = 65· 88Γΐ·⑽式 争蘭材:3Γ:Χ為波索蘭材料添加量,式中回脹率隨波 增加而降低,這三組方程式中以f_Ca0 = 5·35Χ切為控制模式如圖= 發明以Υ = 〜50¾:夕β . 田/次豕闌材料添加:g:達12% 之間其回脹率即符合規範1.5%要求。 本發明為瞭解波索蘭材料 性溶出、土壌中污染物、容盥、、 一重金屬鉻在毒性特 係,在重金屬溶出^重金屬^王水消化中溶出濃度的關 作為溶出量ί屬中;;:量最大因此將重金屬鉻 方法中(氧化故;5 4波索蘭材料添加量為各種穩定 ,與M 方法中利用土 丨:土壌污染物溶出試驗中推導里;鉻溶出量關係模式, 出量關係式為γ = 729 8 1 ρ 494出波索蘭材料添加量與鉻溶 索蘭材料添加量與鉻溶出=水消化試驗中推導出波 Λ鉻:出量,χ為波索蘭材:ΐ: ,313.58Χ-°·282 ’式中 波索蘭材料添加量增加而降:^置,兩式中鉻溶出量隨 -。這兩組方程式中以土壤污 _ 第ίο頁 1287582 五、發明說明(6) 染物溶出試驗中推導出波索蘭材料添 式為Υ = 729· 81Γ〇·494鉻溶出量最大,二ϋ 1與鉻溶出量關係 729.81以494為控制模式,如圖14所示^^發明以卜 氧化矽極少量氧化鋁的波索蘭材料,卷=加含有大量 達8%〜50%之間即滿足規範環境品質要田求。’、材料添加量 (四)、【實施方式】 / 本實作項目包括【1】轉爐石基本物理性質、力 ^學性質試驗’【2】轉爐石混合料基本物理/質 二性質及化學性質試驗,【3】轉爐石及轉爐石混合料= 兄品質特性試驗,【4】微觀結構觀察。 【1】轉爐石基本物理性質、力學性質及化學性質試驗 轉爐石為煉鋼過程中所產生的爐渣類副產品,每年產 出量約為120萬噸,依AASHTO分類法區分,則屬於A-ba (蝶石及砂,優至良路基材料),其粒徑分佈如圖1所示。 液性與塑性限度均為NP ;其比重高達3· 58,可能是含金屬 成份偏高所造成;洛杉磯磨損率約為10. 2%,健性為 0 · 5 3%,充分證實轉爐石具有相當好的抗風化能力及抗磨 損特性,其物理性質如表1所示。 > 純轉爐石依據AASHTO T180(D)法、AASHTO T99(D)法, 進行改良夯實試驗及標準夯實試驗,得到的最大乾密度分 別為2.84g/cm3與2.58g/cm3,最佳含水量分別為7.1%與 7· 2%,其CBR值分別為145%及80% ;再由三軸透水試驗測得 滲透係數K為8. 4 X 10_4cm3/sec ;由直接剪力試驗測得剪力強 度參數 Cp 為 〇.〇6kgf/cm2,Φρ 為 46.7。 、Φγ 為 33.6° ,其! 287S82 V. INSTRUCTIONS (5) 2 The results of the method using CNS 14602 (JIS A5015) for the various methods of free lime (f-Ca0) are 〖02%, 4 6% and 6 8% respectively. When the transfer: ==;; 〇 2%, the amount of corsolin material added and the rate of rebound are 5 I*4''1·273; when yl, * f_Ca〇: 6·8%, the relationship The formula is Υ = 65· 88 Γΐ · (10) type of ramming material: 3 Γ: Χ is the amount of bolsolan material added, in which the rate of rebound increases as the wave increases, the three sets of equations are controlled by f_Ca0 = 5·35 Mode as shown in the figure = invention to Υ = ~ 503⁄4: 夕β. Field / sub-material addition: g: up to 12% of its rebound rate is in line with the specification of 1.5%. The invention relates to understanding the dissolution of the material of the corsolan, the pollutants in the soil, the volume of the metal, the chrome of the heavy metal, and the dissolution concentration of the heavy metal in the digestion of the heavy metal and the aqua regia; : The largest amount will therefore be in the heavy metal chromium method (oxidation; 5 4 wave solanan material addition amount is stable, and the M method uses soil sputum: soil sputum pollutant dissolution test derivation; chromium dissolution amount relationship mode, output The relationship is γ = 729 8 1 ρ 494. The amount of corsolsol and the amount of chrome-soled Solanium material added and chromium dissolution = water digestion test. Derived from the enthalpy of chromium: yield, χ is Possolan: ΐ : , 313.58 Χ - ° · 282 'In the middle of the increase of the amount of corsolin material decreased: ^ set, the amount of chromium dissolved in the two formulas with -. The two sets of equations in the soil soil _ ̄ ̄ ̄ ̄ ̄ ̄ ̄ ̄ ̄ ̄ ̄ ̄ ̄ ̄ ̄ (6) In the dye dissolution test, it is deduced that the addition of the Possolan material is Υ = 729· 81Γ〇·494 The maximum amount of chromium elution is 2, and the relationship between the concentration of bismuth 1 and chromium is 729.81 with 494 as the control mode, as shown in Fig. 14 ^Invented a corsosol material with a small amount of alumina Volume = plus a large amount of up to 8% to 50% to meet the requirements of the standard environmental quality of the field. ', material addition amount (four), [implementation] / This implementation project includes [1] basic physical properties of converter stone, Force ^ nature test '[2] basic physical / qualitative properties and chemical properties of converter stone mixture, [3] converter stone and converter stone mixture = brother quality characteristics test, [4] microstructure observation. [1] The basic physical properties, mechanical properties and chemical properties of the converter stone are the slag by-products produced during the steel making process. The annual output is about 1.2 million tons. According to the AASHTO classification, it belongs to A-ba (Butterstone). And sand, excellent to good road base material), its particle size distribution is shown in Figure 1. The liquid and plastic limits are NP; its specific gravity is as high as 3 · 58, may be caused by high metal content; Los Angeles wear rate is about It is 10.2% and the fitness is 0 · 5 3%. It is fully confirmed that the converter stone has quite good weathering resistance and wear resistance. The physical properties are shown in Table 1. > Pure converter stone according to AASHTO T180 (D ), AASHTO T99 (D) method, improved Test and standard tamping test, the maximum dry density is 2.84g/cm3 and 2.58g/cm3 respectively, the optimum water content is 7.1% and 7.2%, respectively, and the CBR value is 145% and 80% respectively; The permeability coefficient K measured by the triaxial permeable test is 8. 4 X 10_4 cm 3 /sec; the shear strength parameter Cp measured by the direct shear test is 〇.〇6kgf/cm2, Φρ is 46.7, and Φγ is 33.6°,

1287582 五、發明說明(7) 抗剪性質介於中等至緊密砂之間,無膠結性,且具良好抗 剪強度及承載力;由壓密試驗求得土壤壓縮性指數Cc為 0.288,再壓指數Cr為0.064屬於低壓縮性材料,如表2所 示0 表1 新鮮轉爐石之物理性質 種類 比重 吸水率 (%) 健性試驗 (疏鍵鎂溶液) ㈣ 含砂當董 m 液限 塑限 土壤分類 (AASHTO 分頬) pH値 轉爐石 3.58 2.2 0.53 53.36 NP NP A-1-a 12〜 12.5 表2新鮮轉爐石之基本力學性質 種類 改良夯實試驗 標準夯實試驗 直接剪力試驗 滲遘 係數 Κ (cm/sec) 壓縮 指數 Cc 再摩 指數 Cr 磨損孪 (%) Υάααχ (g/cm3) *W〇〇J1|C (%) CBR (%) Υύχχαχ (g/cm3) (T〇) CBR (°/〇) 尖峰強度 殘餘強度 Cp φρ Cr Φγ 轉爐石 10.2 2.84 7.1 145 2.58 7.2 80 0.06 46.7 0 33.6 8.4x1 Ο*4 0.288 0.064 本發明為探討轉爐石回脹原因首先以X光繞射分析 (XRD)瞭解不同f-CaO含量下的新鮮轉爐石各個相位的組成 φ生成物,如圖2所示。其中以氫氧化妈與納锰氧化物含量 最高,其次為氧化石夕、碳酸弼、氧化紹、氧化鐵等化合 物。 以轉爐石熟化前而言,仍以片狀的結構組成,如圖3 所示;轉爐石熟化後,外觀則以鹼-骨材反應的薔薇狀膠1287582 V. INSTRUCTIONS (7) The shear resistance is between medium to tight sand, no cementation, and has good shear strength and bearing capacity; the soil compressibility index Cc is 0.288, which is obtained by compaction test. The index Cr is 0.064, which is a low compressibility material, as shown in Table 2. Table 1 Physical properties of fresh converter stone Specific gravity water absorption (%) Fitness test (salt magnesium solution) (4) Sand containing Dong m liquid limit plastic limit Soil classification (AASHTO bifurcation) pH値 converter stone 3.58 2.2 0.53 53.36 NP NP A-1-a 12~ 12.5 Table 2 Basic mechanical properties of fresh converter stone Improvement type Compaction test standard Compaction test Direct shear test Percolation coefficient Κ ( Cm/sec) Compression index Cc Re-friction index Cr Wear 孪 (%) Υάααχ (g/cm3) *W〇〇J1|C (%) CBR (%) Υύχχαχ (g/cm3) (T〇) CBR (°/ 〇) Peak strength residual strength Cp φρ Cr Φγ Converter stone 10.2 2.84 7.1 145 2.58 7.2 80 0.06 46.7 0 33.6 8.4x1 Ο*4 0.288 0.064 The invention is based on X-ray diffraction analysis (XRD) Composition of individual phases of fresh converter stone under different f-CaO contents φ product, as shown in Figure 2. Among them, the content of hydroxide and nano-manganese oxide is the highest, followed by oxides such as oxidized stone, strontium carbonate, oxidized, and iron oxide. Before the converter stone is matured, it still has a sheet-like structure, as shown in Figure 3; after the converter stone is matured, the appearance is the alkali-aggregate reaction of the rose-like glue.

第12頁 1287582 ^^ - 五、發明說明(8) 示。再由eds得知轉爐石熟化前後其組成 ^ 鐵厌鋁、鈦、猛、鎂、鈉箄含量 較高,如圖5及圖6所示。 納寺3里 整體而S ’新鮮韓愤石中所人_ 钟 h 褥歷石T所3兀素仍以鈣、氧、矽、 鐵、碳、紹、鈦、链、鎮、納等兔 顏备π你^ ^ ^ 納寺為主’其回脹量多寡完全 現氧化鈣、活性氧化矽、氣化鈉、备 故砂 ^ A y乳化納氧化鉀、氧化鋁、氧化 鎖荨不安定化合物含量而定。 再由X光螢光分析(XRF)探討在不同f_Ca0含量下孰化 前後轉爐石試樣中各元素含量,其中以弼、彳、鐵等元素 #含量最高,如表3所示。依XRD分析所得的各種化合物再 以重量分析計算其化學計量,其化學成分如表4所示,其 轉爐石熟化刖後氧化#5 (C a 0 )、氧化鈉(n七〇)、氧化钟 (KgO)、氧化鎮(MgO)等驗性化合物含量明顯變化,且μ值 也尚達12〜12.5 ’充分證實轉爐石具有強鹼反應。 表3轉爐石熟化前後之組成元素Page 12 1287582 ^^ - V. Description of invention (8). Then, eds knows that the composition of the iron before the ripening of the converter is high, such as aluminum, titanium, magnesium, sodium and sodium, as shown in Fig. 5 and Fig. 6. Na Temple 3 in the whole and S 'Fresh Han Anshizhong people _ Zhong H 褥 石 T T 所 所 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍 仍Prepare π you ^ ^ ^ Na Temple-based 'the amount of re-expansion of calcium oxide, active cerium oxide, sodium sulphate, prepared sand ^ A y emulsified sodium sulphate, alumina, oxidized lock stagnation compound content And set. X-ray fluorescence analysis (XRF) was used to investigate the content of each element in the converter stone samples before and after deuteration at different f_Ca0 contents. The content of elements such as lanthanum, cerium and iron was the highest, as shown in Table 3. The stoichiometry was calculated by gravimetric analysis of various compounds obtained by XRD analysis. The chemical composition of the various compounds was as shown in Table 4. After the converter was aged, the oxidized #5 (C a 0 ), sodium oxide (n 〇 〇), and oxidized clock were oxidized. The content of the test compound such as (KgO) and oxidized town (MgO) changed significantly, and the μ value also reached 12~12.5'. It was confirmed that the converter stone had a strong base reaction. Table 3 The constituent elements before and after the transformation of the converter stone

測定A ,素 Ca W Si (7〇) Fe 0¼) Mg <%) K (?/〇) Na (%) A1 (%) Ti (%) f-CaO1.02% 熟化前 41.0 4.31 6.49 1.32 <0.1 0.69 0.097 0.143 熟化後 48.7 3.88 5.84 1.95 0.95 2.28 1.15 - f-CaO=4.6% 熟化前 41.7 4.31 6.08 1.08 <0.1 0.79 0.101 0.137 熟化後 47.9 4.02 3.39 3.17 1.07 3.69 1.24 0.53 f-CaO=6.8°/o 熟化前 42.9 4.79 6.46 1.24 <0.1 0.75 0.084 0.115 熟化後 49.8 4.31 6.20 1.93 0.85 1.50 1.16 0.25Determination A, Prime Ca W Si (7〇) Fe 01⁄4) Mg <%) K (?/〇) Na (%) A1 (%) Ti (%) f-CaO1.02% Before maturing 41.0 4.31 6.49 1.32 <;0.1 0.69 0.097 0.143 After curing 48.7 3.88 5.84 1.95 0.95 2.28 1.15 - f-CaO=4.6% 41.7 before maturing 4.31 6.08 1.08 <0.1 0.79 0.101 0.137 After aging 47.9 4.02 3.39 3.17 1.07 3.69 1.24 0.53 f-CaO=6.8°/ o Before aging 42.9 4.79 6.46 1.24 <0.1 0.75 0.084 0.115 After aging 49.8 4.31 6.20 1.93 0.85 1.50 1.16 0.25

1287582 五、發明說明(9) 表4轉爐石熟化前後之化學成份 1 種類 CaO (%) Si03 (%) FeO (%) Mgp c%) K20 Na30 A1A 〇) Ti03 0½) 驗茂 CaO 雉基* CaO pH值 JS〇i+Jih〇i f-CaO=1.02°/〇 熟化前 57.36 9.22 8.35 2.19 <0.12 0.93 0.175 0.239 6.11 6.22 12.3 熟化後 68.17 8.30 7.51 3.23 1.14 3.07 2.17 0 6.51 8.21 - f-CaO=4.6% 熟化前 58.34 9.22 T82 1.79 <0.12 1.06 0.182 0.229 6.21 6.32 12.5 熟化後 67.05 7.66 4.85 5.26 1.29 4.97 2.34 0.62 6.71 8.75 - fCaO-6.8% 熟化前 60.02 10.24 8.31 2.06 <0.12 1.01 0.151 0.192 5.78 5.86 12.0 熟化後 69.67 9.22 7.97 3.20 1.02 2.02 2.19 0.29 6.11 7.56 - 再從轉爐石的鹽基度、驗度作探討,當轉爐石的驗度 〔Ca0/(Si02 + Al203 )〕大於 1·8 時,便含有 60 - 80% 的 C3S 和 QS,並且隨著鹼度增加,CsS和含量也隨之增加,活性 也相對提高。艾萊土QSUlite)、貝萊土C2S(Belite)兩種 為水泥單礦物在水泥熟料中約佔70%〜80%,但是在轉爐渣 中均以非純礦物A1 ite和Bel ite之型態出現。當轉爐石中 f — Ca〇含量分別為1· 02%、4· 6%及6· 8%在熟化前後鹼度落在 5·78〜6·71之間遠大於1.8,充分證實轉爐石中含有报古 >的艾萊土C3S(Alite)、貝萊土C2S(Belite),因此 之活性。 M此具有較尚 、 在鍊鋼過程中為了去除鋼液中的雜質,轉爐中常加 ::的石灰,因此轉爐石常含有相當高的未反應二'入 口為石灰含有豐富的碳酸鹽類、氧化鈣及氧化鎂等化人又1287582 V. INSTRUCTIONS (9) Table 4 Chemical composition before and after converter aging 1. Type CaO (%) Si03 (%) FeO (%) Mgp c%) K20 Na30 A1A 〇) Ti03 01⁄2) Cao CaO 雉* CaO pH JS〇i+Jih〇i f-CaO=1.02°/〇57.36 9.22 8.35 2.19 <0.12 0.93 0.175 0.239 6.11 6.22 12.3 After curing 68.17 8.30 7.51 3.23 1.14 3.07 2.17 0 6.51 8.21 - f-CaO=4.6 % before ripening 58.34 9.22 T82 1.79 <0.12 1.06 0.182 0.229 6.21 6.32 12.5 After curing 67.05 7.66 4.85 5.26 1.29 4.97 2.34 0.62 6.71 8.75 - fCaO-6.8% Before curing 60.02 10.24 8.31 2.06 <0.12 1.01 0.151 0.192 5.78 5.86 12.0 After curing 69.67 9.22 7.97 3.20 1.02 2.02 2.19 0.29 6.11 7.56 - From the salt base degree and the degree of verification of the converter stone, when the degree of curvature of the converter stone [Ca0/(Si02 + Al203)] is greater than 1·8, it contains 60 - 80% of C3S and QS, and as the alkalinity increases, the CsS and content also increase, and the activity is relatively increased. Two kinds of cement single minerals are about 70%~80% in cement clinker, but in the converter slag, the types of non-pure minerals A1 ite and Belite are in the form of non-pure minerals. appear. When the content of f-Ca〇 in the converter stone is 0.02%, 4.6% and 6.8%, the alkalinity falls between 5.78~6·71 and is much greater than 1.8 before and after ripening, which is fully confirmed in the converter stone. It contains Agile C3S (Alite) and Belle C2S (Belite), which are active. M has a relatively good, in order to remove impurities in the molten steel in the process of the chain steel, the converter often adds:: lime, so the converter stone often contains a relatively high unreacted two 'inlet for the lime is rich in carbonates, oxidation Calcium and magnesium oxide

第14頁 1287582 五、發明說明(10) 物,在強驗環境下可能發生鹼-碳酸鹽反應。根據Swenson 提出具鹼-碳酸鹽反應的骨材種類為白雲石、石灰石等, 此類骨材共同點為具有豐富碳酸鹽類、氧化鈣及氧化鎂。 再根據Hadley指出碳酸鱗#5(CaMg(C03)2)遇驗會起 Dedolomitization(脫白雲石)反應,其反應式為: (1) CaMg(C03)2 + 2M0H — Mg(〇H)2 + M2C03 + CaC03 (2) M2C03 + Ca(0H)2 — 2M0H + CaC03 其中M代表Na或K ’Μ/Ο3的M遇Ca(OH)2會再度發生反應,由 上兩式(1)反應式生成的遇到Ca(0H)2產生驗Μ〇ίΙ,此 Μ0Η可再與CaMg(C〇3 &反應生成MgCOs,以此方式循環。在 -白雲石及石灰石中CaO與碳酸鹽類含量豐富,因此若存在 驗與水,將發生驗-骨材反應,此反應將產生有害之回服 作用,使骨材分解,然而此反應則持續不斷,直到CaQ水 化完畢或碳酸鹽類耗盡為止。 【2】轉爐石混合料基本物理性質、力學性質及化學性質 本發明為減少轉爐石中重金屬、溶解性鹽類溶出量 '以 稀釋、固化螯合使轉爐石趨於穩定,添加波索蘭材料=1 釋轉爐石中重金屬及驗的含量,降低pH值,減少重金屬= 出量,相對減少鹼的供應量,降低轉爐石回脹率。 & 採用濕裹法、取代濕裹並用法都是波索蘭材料添加、去, .討轉爐石經穩定工法處理後混合料的各種物理、+ / 木 刀學赫Page 14 1287582 V. INSTRUCTIONS (10) The alkali-carbonate reaction may occur in a strong environment. According to Swenson, the types of aggregates with alkali-carbonate reaction are dolomite, limestone, etc., and these aggregates are rich in carbonates, calcium oxide and magnesium oxide. According to Hadley, the carbonate scale #5 (CaMg(C03)2) will be subjected to the Dedolomitization reaction. The reaction formula is: (1) CaMg(C03)2 + 2M0H — Mg(〇H)2 + M2C03 + CaC03 (2) M2C03 + Ca(0H)2 - 2M0H + CaC03 where M represents Na or K 'Μ/Ο3, and M reacts again with Ca(OH)2, which is generated by the above two formula (1) When Ca(0H)2 is produced, the Μ0Η can be further reacted with CaMg (C〇3 & to form MgCOs, which circulate in this way. In the dolomite and limestone, CaO and carbonate are abundant. Therefore, if water and water are detected, a test-bone reaction will occur, which will produce a harmful retraction effect and decompose the aggregate. However, the reaction continues until the CaQ hydration or the carbonate is exhausted. [2] Basic physical properties, mechanical properties and chemical properties of the converter stone mixture The present invention is to reduce the amount of heavy metals and dissolved salts in the converter stone. The dilution and solidification of the chelate make the converter stone tend to be stable, and the corsosol material is added. =1 release the heavy metal and test content in the hearth, reduce the pH value, reduce the heavy metal = output, reduce the alkali Supply, reduce the rate of returning to the converter. & Use wet wrap, replace wet wrap and use is the addition of corsolan material, go, discuss the various physics of the mixture after the sinter treatment by the stable method, + / wooden knife Xuehe

1287582 五、發明說明(11) 性、回脹等工程品質。 本研究回脹試驗乃依據CNS 1 4602 CJIS A 5015)所規 定之方法進行,由回脹試驗結果得知卜Ca0=1· 〇2%未處理 轉爐石其回脹率高達7· 62%,採用濕裹法後其回脹率明顯 下降,如圖7所示。其中以2%水泥濕裹+ 8%水淬爐石粉抑 制回脹效果最佳回脹率僅達〇· 52%,CBR值最大可高達 294.58%,如表5所示。 當f-CaO = 4.6%未處理轉爐石其回脹率高達9〇5%,採用 濕裹法後其回脹率也明顯下降,其中以2%水泥濕裹+ 水 #淬爐石粉抑制回脹效果最佳,回脹率僅達113%如圖8所 示.’CBR值最大,高達276.58%。至於當f_Ca〇 = 6 8%未處理 轉爐石其回脹率高達4. 30%,採用濕裹法後其回脹率也明 顯下降,其中仍以2%水泥濕裹+ 8%水淬爐石粉抑制回脹效 果最佳回脹率僅達〇.74%,如圖9所示;CBR值最大可高 314 43^,由此可見濕裹法對於轉爐石回脹抑制效果 顯者,對於降低轉爐石的滲透性、阻隔外來水份入涞、 增加抗壓性、剪力強度、承載力具有相當好的效果〔1287582 V. Description of invention (11) Engineering quality such as sex and rebound. The re-expansion test of this study was carried out according to the method specified in CNS 1 4602 CJIS A 5015). It is known from the results of the re-expansion test that the Ca0=1·〇2% untreated converter stone has a rebound rate as high as 7.62%. After the wet wrap method, the rebound rate is significantly reduced, as shown in Figure 7. Among them, 2% cement wet wrap + 8% water quenching furnace powder suppresses the rebounding effect. The best rebound rate is only 52%, and the CBR value can be as high as 294.58%, as shown in Table 5. When f-CaO = 4.6% untreated converter stone, its rebound rate is as high as 9〇5%, and its rebound rate is also significantly reduced after wet-wetting. Among them, 2% cement wet wrap + water # quenching furnace powder inhibits rebound The best effect, the rebound rate is only 113% as shown in Figure 8. 'CBR value is the largest, up to 276.58%. As for the f_Ca〇 = 6 8% untreated converter stone, the rebound rate is as high as 4. 30%, and the rebound rate is also significantly reduced after the wet wrap method, which is still wet with 2% cement + 8% water quenching furnace powder The best rebound rate for suppressing the rebound effect is only 74.74%, as shown in Figure 9; the maximum CBR value can be 314 43^, which shows that the wet wrap method has a significant effect on the inhibition of the converter stone, and the converter is reduced. The permeability of stone, the resistance to foreign water, the increase of pressure resistance, shear strength and bearing capacity have quite good effects.

1287582 五、發明說明(12) 表5 濕裹法處理後轉爐石混合料回脹試驗結果 轉垴$ 通哀法 改民夯寶 (9扳牵(%) JISA5015 CBR值 莜大乾密度 嵚诠含水专 Womc(%) j f-CaO=1.02% 2%水延泜哀+8%底灰 2.50 7.7 1.12 210.68 2%水此逋衷+8%飛灰 2.20 8.0 0.83 234.35 2%水泥逋衷+ 8%水淖垴石粉 2.61 7.5 0.52 294.58 来輿理 2.84 7.1 7.62 103.49 f-Ca04.6% 2%水泥逋衷+8%底灰 - - 1.36 196.91 2%水泥通泉+8%¾灰 - - 1.25 218.78 2%水泥滬裹+ 8%术淬垴石粉 - - 1.13 276.58 未處理 - - 9.06 104.27 f-CaO=6.8% 2%水泥逋衷+8%底灰 - - 1.20 242.99 2%水泥逋衷+S%飛灰 - - 1.07 269.98 2%水泥通哀+ 8%水淬垴名粉 - - 0.74 314.43 未輿理 - - 4.30 124.221287582 V. INSTRUCTIONS (12) Table 5 After the wet wrap treatment, the results of the re-expansion test of the converter stone mixture turn to $ 通 法 法 法 法 夯 ( 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 Dedicated Womc(%) j f-CaO=1.02% 2% water delay 泜 + +8% bottom ash 2.50 7.7 1.12 210.68 2% water this + +8% fly ash 2.20 8.0 0.83 234.35 2% cement + + 8% Water gangue powder 2.61 7.5 0.52 294.58 to handle 2.84 7.1 7.62 103.49 f-Ca04.6% 2% cement + +8% bottom ash - - 1.36 196.91 2% cement pass spring +8% 3⁄4 ash - - 1.25 218.78 2 % cement wrap + 8% quenched vermiculite powder - - 1.13 276.58 untreated - - 9.06 104.27 f-CaO = 6.8% 2% cement + +8% bottom ash - - 1.20 242.99 2% cement + + S% fly Ash - - 1.07 269.98 2% cement pass + 8% water quenching powder - - 0.74 314.43 untreated - - 4.30 124.22

經取代濕裹並用法處理後轉爐石混合料回脹試驗結果 中得知f-CaO = l. 02%未處理轉爐石其回脹率高達7. 62%,採 用取代濕裹並用法後其回脹率明顯下降,其中以2%水泥濕 裹+ 高爐石全取代細料抑制回脹效果最佳回脹率僅達 0.33%,如圖10所示,其CBR值也高達184. 11%,如表6所 示。當f-CaO = 4. 6%未處理轉爐石其回脹率高達9. 06%,仍 採用2%水泥先濕裹,再以河床料、電廠底灰、南爐石等全 部取代細料,結果其回脹率明顯下降落在0. 90%〜0. 99°/〇 f間,效果相當接近,如圖11所示;其CBR值也高達 1 82.32%之間,如表6 所示。當f-CaO = 6.8%未處理轉爐石 其回脹率高達4. 30%,其中仍以2%水泥濕裹+高爐石全取代 .細料抑制回脹效果最佳回脹率僅達0. 45%,如圖12所示; CBR值最大可高達1 96. 52%,如表6所示。由此可見取代濕After replacing the wet wrap and the treatment, the results of the re-expansion test of the converter stone mixture were found to be f-CaO = l. 02% untreated converter stone, the rebound rate was as high as 7.62%, replaced by wet wrap and used after returning The expansion rate is obviously reduced, and the best rebound rate of the 2% cement wet wrap + blast furnace stone completely replaces the fine material to suppress the rebound effect is only 0.33%, as shown in Figure 10, the CBR value is also as high as 184.1%, such as Table 6 shows. When f-CaO = 4.6% untreated converter stone, its rebound rate is as high as 9. 06%, still use 2% cement first wet wrap, and then replace the fine material with riverbed material, power plant bottom ash, Nanfang stone, etc. As a result, the rebound rate decreased significantly between 0.90% and 0. 99°/〇f, and the effect was quite close, as shown in Fig. 11; the CBR value was also as high as 1 82.32%, as shown in Table 6. When f-CaO = 6.8% untreated converter stone, its rebound rate is as high as 4. 30%, which is still completely replaced by 2% cement wet wrap + blast furnace stone. The best rebound rate of fine material inhibits the rebound effect is only 0. 45%, as shown in Figure 12; CBR value can be as high as 1 96.52%, as shown in Table 6. This shows that replacing the wet

第17頁 1287582 五、發明說明(13) 裹並用法對於轉爐石回脹抑制效果相顯著,對於降低轉爐 石的滲透性、阻隔外來水份入滲、並增加抗壓性、剪力強 度、承載力具有相當好的效果。 表6取代濕裹並用法處理後轉爐石混合料回脹試驗結果 轉«U 取代傾袠並用法 改&夯貲 闰脹毕供) JISA5015 CBR值 W 最大乾密茂 最仕含水量 Womc(%) f-CaO=1.02% 2%水烬渴H+芮床利全取代蜱葙;C細利 2.59 7.5 1.20 195.29 2%永泥《哀+底灰会取代_搞;C細利 2.10 8.2 0.47 175.57 2%水泥《哀+姦葙石会取代轉搞ΧΛθ利 2.25 7.8 0.33 184.11 未夷霣 2.84 7.1 7.62 103.49 f-CaO=4.6% 2%水泥《裹+河床料全取代縳搞石Αθ利 - - 0.99 182.32 2%永烬底灰会取代蜱葙茗鉍利 - - 0.92 133.63 2%水泥《 H+ S葙茗全取代蜱楣名Αβ利 - 0.90 172.86 未槔運 - 9.06 104.27 f-CaO:6.8% 2%永泥涔哀+対床料会取代轉戏石Λθ利 - 0.59 224.98 2%水泥渑裹+ί*底灰会取代蜱嫌;6知利 - 1.34 164.33 2%水烬《裘+S葙名全取代_搞名知利 - 0.45 196.52 未鴣鼉 - 4.30 124.22Page 17 1278582 V. INSTRUCTIONS (13) The effect of wrapping and suppressing on the converter's rebound is significant, reducing the permeability of the converter stone, blocking the infiltration of foreign water, and increasing the compressive strength, shear strength and load. The force has quite good results. Table 6 replaces the wet wrap and after the treatment, the converter stone mixture re-expansion test results turn «U replaces the dumping and the usage change & swell expansion supply" JISA5015 CBR value W the largest dry dense Moxa water content Womc (% ) f-CaO=1.02% 2% water thirst H+ trampoline replaces 蜱葙; C fine 2.59 7.5 1.20 195.29 2% Yong mud "sorrow + bottom ash will replace _ engage; C fine 2.10 8.2 0.47 175.57 2 % cement "Amour + 葙石石 will replace the turn ΧΛθ利2.25 7.8 0.33 184.11 Not smashed 2.84 7.1 7.62 103.49 f-CaO=4.6% 2% cement "wrap + riverbed material full replacement binding stone Αθ 利 - - 0.99 182.32 2% 烬 烬 bottom ash will replace 蜱葙茗铋利 - - 0.92 133.63 2% cement "H + S 葙茗 full replacement 蜱楣 Α β 利 - 0.90 172.86 未槔运 - 9.06 104.27 f-CaO: 6.8% 2% forever Muddy mourning + trampoline material will replace the turn of the stone Λθ利 - 0.59 224.98 2% cement 渑 wrapped + ί 底 灰 will replace the suspicion; 6 Zhili - 1.34 164.33 2% water 烬 "裘 + S nickname full replacement _ 知名知利 - 0.45 196.52 未鸪鼍- 4.30 124.22

轉爐石經濕裹法、取代及濕裹並用法處理後之混合料 依據AASHTO T180(D)法,進行改良夯實試驗,得到的最大 乾密度介於2.84g/cm3〜2.1g/cm3之間,最佳含水量介於 ♦ . 1 %〜8. 2% ;再由三軸透水試驗測得滲透係數K介於2. 32 X 1 〇-4〜7. 61 X 1 0_4cm/sec之間,相當於中等至緊密砂,由壓 密試驗求得土壤壓縮指數Cc介於0.1 07〜0.399,再壓指數 • Cr介於0. 027〜0. 0 60屬於低壓縮性材料,由直接剪力試驗 •測得剪力強度參數Cp介於0〜0.84.kgf/cm2,Φρ介於49.8°The converter stone is wet-wrapped, replaced and wet-wrapped and the mixture after the treatment is subjected to a modified tamping test according to the AASHTO T180 (D) method, and the maximum dry density is between 2.84 g/cm3 and 2.1 g/cm3. The optimum water content is between ♦ 1% and 8.2%; and the permeability coefficient K measured by the triaxial permeable test is between 2.32 X 1 〇-4~7. 61 X 1 0_4cm/sec, equivalent For medium to compact sand, the soil compression index Cc is determined by the compaction test to be between 0.107 and 0.399, and the pressure index is 1. 0. 027~0. 0 60 is a low compressibility material, tested by direct shear force. The measured shear strength parameter Cp is between 0 and 0.84.kgf/cm2, and the Φρ is between 49.8°.

第18頁 1287582 五、發明說明(14) 〜33· 3 ° ; Cr 貝1J 介於0 〜0· 07· kgf/cm2 , Φγ 貝1J 介於 31.7° 〜 4 4. 8 ° ,其抗剪性質也介於中等至緊密砂之間,整體而 言,轉爐石混合料均屬於膠結性低、抗剪強度佳、透水性 大、承載力高的工程填方材料,表7所示。 表7轉爐石混合料之基本力學性質 « 痛 浴杉-磨租丰 (%) 改il务貨5¾¾ ΐ接贫力戈映 係眈 Κ (cin/sec) 拍fe Q 拍軚 Cr YtUit 叙 (Stem) w_: (%) 尖峰狃產 (r) Ψ* η 未典S鳟葙石 10.2 2B4 7.1 0D6 46.7 0 33.6 8.41x1 IT1 0288 OD60 2*/冰烬《哀+sy成灰 - 2*50 7.7 0 49.2 OD1 36.6 3.44x10^ 0352 0D32 2%^«»哀+8%戏灰 - 22 8D 0.7 31.7 0D5 33.3 4&M04 0.1¾ OJ027 2%永泥《褒+ 8*/冰淬搞名扮 - 261 7JS 0S4 40.5 0D7 38.3 232Δ0α 0306 0D33 2%水泥《蒗+河床料会取代轉楣名*9利 攀 259 Ί5 033 49.8 0 44.8 7j61x10^ 0361 0D48 2%水泥《哀+«*底灰会取代轉搞;SAe利 - 2.1 82 Q62 46.9 021 36.3 624^104 0.107 OJ030 2*/冰泥《裟+S鴂名全取代蜱楣名Αβ利 - 261 Ί5 05Ί 47.3 0 39.9 2£3χ104 0399 OD20 就濕裹法而言,轉爐石混合料其主要結晶型化合物為 氫氧化鈣與碳酸鈣,次要結晶型化合物為氧化矽、鈣鋁氧 化物及氧化鐵等化合物;就取代濕裹並用法而言,轉爐石 混合料其主要結晶型化合物為氧化矽、氫氧化鈣等,次要 結晶型化合物為鎂矽氧化物、鈣鋁矽氧化物等化合物。 丨再由X光螢光分析(XRF)探討(1 )濕裹法處理後轉爐石 混合料試樣中各元素含量,其中以鈣、矽、鐵、鋁、鎂等 元素含量最高,其中鈣含量大約為矽和鐵含量的3〜4倍, 如表8所示;依XRD分析所得的各種化合物再以重量分析計 算其化學成份計量,得知濕裹法處理後各種轉爐石混合料Page 18 1278582 V. Description of invention (14) ~33· 3 ° ; Cr shell 1J between 0 〜0· 07· kgf/cm2 , Φγ shell 1J between 31.7° 〜 4 4. 8 ° , its shear properties It is also between medium and tight sand. As a whole, converter stone mixes are engineering fill materials with low cementation, good shear strength, high water permeability and high bearing capacity, as shown in Table 7. Table 7 Basic mechanical properties of converter stone mixture « Pain cedar - mill rent (%) Change il goods 53⁄43⁄4 贫 贫 戈 戈 cin cin (cin / sec) 拍 fe Q 軚 軚 Cr YtUit 叙 (Stem ) w_: (%) spikes (r) Ψ* η 典 鳟葙 鳟葙 0.2 10.2 2B4 7.1 0D6 46.7 0 33.6 8.41x1 IT1 0288 OD60 2*/Ice 烬 哀 + sy into gray - 2*50 7.7 0 49.2 OD1 36.6 3.44x10^ 0352 0D32 2%^«» sorrow +8% play ash - 22 8D 0.7 31.7 0D5 33.3 4&M04 0.13⁄4 OJ027 2% Yong Mu "褒+ 8*/冰淬造作装- 261 7JS 0S4 40.5 0D7 38.3 232Δ0α 0306 0D33 2% cement "蒗 + river bed material will replace the transfer name *9 Li Pan 259 Ί 5 033 49.8 0 44.8 7j61x10^ 0361 0D48 2% cement "sorrow + « * bottom ash will replace the transfer; SAe利 - 2.1 82 Q62 46.9 021 36.3 624^104 0.107 OJ030 2*/Ice mud "裟+S鴂名全换蜱楣名Αβ利- 261 Ί5 05Ί 47.3 0 39.9 2£3χ104 0399 OD20 In terms of wet wrap, The main crystalline compound of the converter stone mixture is calcium hydroxide and calcium carbonate, and the secondary crystalline compounds are compounds such as cerium oxide, calcium aluminum oxide and iron oxide; instead of wet wrapping, the converter stone The main crystalline compound of the mixture is cerium oxide, calcium hydroxide or the like, and the secondary crystalline compound is a compound such as magnesium cerium oxide or calcium aluminum cerium oxide. X-ray fluorescence analysis (XRF) is used to investigate (1) the content of each element in the converter stone mixture sample after wet-coating treatment, in which the content of calcium, barium, iron, aluminum, magnesium and other elements is the highest, of which calcium content It is about 3~4 times of the content of bismuth and iron, as shown in Table 8; the chemical composition of each compound obtained by XRD analysis is calculated by gravimetric analysis, and the various converter stone mixes after wet wrapping treatment are known.

第19頁 1287582 五、發明說明(15) 中組成化合物為CaO、S i 02、FeO、MgO、Na20、A 12 03、Page 19 1287582 V. Inventive Note (15) The constituent compounds are CaO, S i 02, FeO, MgO, Na20, A 12 03,

Ti20,其含量如表9 所示。 由X光螢光分析(XRF )探討(2)取代濕裹並用法處理後 轉爐石混合料試樣中各元素含量,仍以鈣、矽、鐵、鋁、 鎂等元素含量最高,其中鈣和矽含量相近,如表8所示。 依XRD分析所得的各種化合物再以重量分析計算其化學成 份計量,得知濕裹法處理後各種轉爐石混合料中組成化合 物為CaO、Si02、FeO、MgO、Na20、Al2〇3、Ti20,其含量如 表9 所示。 表8 轉爐石混合料元素組成Ti20, the content of which is shown in Table 9. X-ray fluorescence analysis (XRF) to explore (2) replace the wet wrap and the content of each element in the converter stone mixture sample after treatment, still the highest content of calcium, barium, iron, aluminum, magnesium and other elements, of which calcium and The cerium content is similar, as shown in Table 8. The chemical composition of each compound obtained by XRD analysis was calculated by gravimetric analysis. It was found that the composition compounds of various converter stone mixtures after wet coating were CaO, SiO 2 , FeO, MgO, Na20, Al2〇3, Ti20. The contents are shown in Table 9. Table 8 Composition of converter stone mixture

Cn ㈨ Si Ft (♦八) A1 m Mg (和 K Ti ㈨ P S (汾 Cr ㈨ Sr r八) m Ski Cl r八) 耒«« 45.40 4J5 62S 〇J〇9 120 0.74 - 065 - * - 0i0014 * - - • - +8你灰 42P4 1156 ΙΑ 96 332 231 - 0JD6 0.46 191 0S6 0⑽ 0D007 OJ04O OJ0003 OJOOOl OJ9004 OJ0013 +β%λμ. 42^1 13.1D 15JOO 599 195 • 0.15 059 197 058 OJOQ26 OJ0008 OJ04O OJ0003 OJOOOl OJ0004 0細5 +8y冰 Sajis» 42J88 13·52 1165 596 3i4 - 〇J〇2 036 1.73 0.41 OJD033 OJOOO? a 036 0細2 0脚1 0Λ003 0J0004 复 +Λ來》金取代ΙίΑΛί»;» 27J87 2291 955 521 2.11 - 0.15 0.43 1J08 037 OJ0019 0娜 OJ022 OJ0002 OJOOOl 0細4 0J0O03 取代 洪λ +¾¾底灰仝取代 23.74 21.79 13 S3 560 220 • 0.19 022 033 0.71 OJOOB6 0㈣1 OiOli - • OJOOOl OJOOB8 洪 1 +毐違龙仝取代嵙 3637 1239 1053 2B7 297 - OJOS9 037 1.49 036 OJOQ34 0J0006 0015 OJ0002 OJOOOl 00005 0i0003Cn (nine) Si Ft (♦ eight) A1 m Mg (and K Ti (nine) PS (汾Cr (nine) Sr r eight) m Ski Cl r eight) 耒«« 45.40 4J5 62S 〇J〇9 120 0.74 - 065 - * - 0i0014 * - - • - +8 you gray 42P4 1156 ΙΑ 96 332 231 - 0JD6 0.46 191 0S6 0(10) 0D007 OJ04O OJ0003 OJOOOl OJ9004 OJ0013 +β%λμ. 42^1 13.1D 15JOO 599 195 • 0.15 059 197 058 OJOQ26 OJ0008 OJ04O OJ0003 OJOOOl OJ0004 0细5 +8y冰Sajis» 42J88 13·52 1165 596 3i4 - 〇J〇2 036 1.73 0.41 OJD033 OJOOO? a 036 0fine 2 0 foot 1 0Λ003 0J0004 complex + Λ来”金换Ι ΑΛίΑΛί»;» 27J87 2291 955 521 2.11 - 0.15 0.43 1J08 037 OJ0019 0Na OJ022 OJ0002 OJOOOl 0fine 4 0J0O03 Replaced hong λ +3⁄43⁄4 bottom ash with the same 23.74 21.79 13 S3 560 220 • 0.19 022 033 0.71 OJOOB6 0 (four) 1 OiOli - • OJOOOl OJOOB8 Hong 1 + 毐 龙Same as 嵙3637 1239 1053 2B7 297 - OJOS9 037 1.49 036 OJOQ34 0J0006 0015 OJ0002 OJOOOl 00005 0i0003

第20頁 1287582 五、發明說明(16) 表9轉爐石混合料組成成份 C%0 (%) SiOs ㈨ FeO (%) Κ,Ο (%) Ν&:Ό ㈨ ai;〇5 (%) TbO (%) ΜκιΟ ㈨ S0s CrO ㈨ PA. (%) PH 爾 蝓« c<»». 未《JC ηΑΛ 57¾ 922 835 2.19 • 0Ρ3 0.17 024 0.13 * 00018 * 1230 622 6.11 48J09 19.?9 15.-W 3J06 〇J〇6 • 5Q2 0.43 1卯 OJ004 OJOOO? 1J03 1140 2.43 194 2*/^·«ί»*.+8%Λ4£ 46J06 22.49 15.44 2i9 0.14 - 506 0·55 2J03 OJOQ5 00008 1J06 1160 2J05 167 4839 24JOO 1102 3jS9 〇J〇2 - 7.48 034 1.79 OJ006 0ΰ007 0.75 1160 2J02 li4 2V·水笔«ILM系科金軌代ΛΑΛ >«斜 32:31 21切 981 2J80 0.14 - 4J02 0.40 1.12 om OJ0005 0j68 1110 1.49 126 馭代 洪1 2¾水笔澡底灰全軌代缚Α名N A 2629 3730 1433 292 0.18 * 8.17 021 034 OJ007 οοοοι 130 IOjOO 0.71 0^8 2V冰1+高應£含取代 38.45 36.40 1025 3P4 009 • 634 035 li4 OJ0O7 0D006 0jS6 1120 106 0Ρ0 _【3】轉爐石及轉爐石混合料環境品質特性試驗 此外本發明再以環境品質觀點深入研究轉爐石作為工 程土方材料時對環境可能的影響程度,首先將所有純轉爐 石及濕裹法、取代濕裹並用法處理後轉爐石混合料的樣品 依「有害事業廢棄物認定標準」中之「溶出毒性事業廢棄 物」分析方法對其重金屬作有害特性判定。 (一)毒性特性溶出分析(T C L P ) 根據溶出毒性的有害特性判定標準,以轉爐石及濕裹 法、取代濕裹並用法處理後轉爐石混合料之溶出液中除 、鉛、砷等重金屬溶出較高外,整體而言,六價鉻、總 鉻、鎘、鉛、砷、汞、銅、鋅、鎳等重金屬也遠低於溶出 標準,其分析結果如表1 〇所示;換言之,以毒性特性溶 .出試驗(TCLP)而言,轉爐石及濕袠法、取代濕裹並用法處 理後轉爐石混合料不需作任何處理其重金屬溶出值均遠低Page 20 1287582 V. INSTRUCTIONS (16) Table 9 Composition of Converter Stone Mixture C%0 (%) SiOs (9) FeO (%) Κ, Ο (%) Ν &: Ό (9) ai; 〇 5 (%) TbO (%) ΜκιΟ (9) S0s CrO (9) PA. (%) PH 蝓« c<»». Not JC ηΑΛ 573⁄4 922 835 2.19 • 0Ρ3 0.17 024 0.13 * 00018 * 1230 622 6.11 48J09 19.?9 15.-W 3J06 〇J〇6 • 5Q2 0.43 1卯OJ004 OJOOO? 1J03 1140 2.43 194 2*/^·«ί»*.+8%Λ4£46J06 22.49 15.44 2i9 0.14 - 506 0·55 2J03 OJOQ5 00008 1J06 1160 2J05 167 4839 24JOO 1102 3jS9 〇J〇2 - 7.48 034 1.79 OJ006 0ΰ007 0.75 1160 2J02 li4 2V·水笔«ILM系科金轨代ΛΑΛ >« oblique 32:31 21 cut 981 2J80 0.14 - 4J02 0.40 1.12 om OJ0005 0j68 1110 1.49 126驭代洪1 23⁄4 pens bath bottom gray full rails Α NA NA 2629 3730 1433 292 0.18 * 8.17 021 034 OJ007 οοοοι 130 IOjOO 0.71 0^8 2V ice 1 + high should contain £ 38.45 36.40 1025 3P4 009 • 634 035 Li4 OJ0O7 0D006 0jS6 1120 106 0Ρ0 _ [3] Environmental quality characteristics test of converter stone and converter stone mixture In addition, the invention is further environmental quality In-depth study of the degree of possible environmental impact of converter stone as engineering earth material, first of all the samples of pure converter and wet wrap, instead of wet wrap and after-treatment of converter stone mix, according to the "Hazardous Waste Determination Standard" The "dissolution toxicity business waste" analysis method is used to determine the harmful properties of heavy metals. (1) Toxicity characteristic dissolution analysis (TCLP) According to the determination criteria of the harmful characteristics of dissolution toxicity, the dissolution of heavy metals such as lead and arsenic in the eluate of the converter stone mixture by the converter stone and the wet wrap method instead of the wet wrap and the usage treatment Higher, overall, heavy metals such as hexavalent chromium, total chromium, cadmium, lead, arsenic, mercury, copper, zinc, nickel are also far below the dissolution standard, and the analysis results are shown in Table 1 ;; in other words, For the toxic characteristic dissolution test (TCLP), the converter stone and wet sputum method, instead of wet wrap and after the treatment, the converter stone mixture does not need any treatment, and the heavy metal dissolution value is far lower.

第21頁 1287582 五、發明說明(17) 於毒性特性溶出標準。 表1 0轉爐石及轉爐石混合料毒性特性溶出試驗結果 2臺«耷1(1边《 z m ««(Cr) (邮) 麯 CCdJ ㈣ *(Pb) ㈣句 豕㈣ ㈣ 餉(叫 鋅(at) 鵪(NLJ (邮) 耒 0J9146 OJ0183 m> 〇J〇08ti OJ0019 ND OJOQ99 〇J〇〇ei OJOQ82 0JDQ35 OJ0030 m> OJ0305 OJOOS4 0_2 HD OJ02S1 0細 OJ0199 OJ0397 ND OJ0136 OJOQ22 ND OJ0O44 OJ0474 OJ0082 2V冰其洪IL+8y冰« ΑΛ » OJ0169 OJ0337 m> 0J0152 OJOQ22 OJOOOl ND OJ01D5 〇J〇»7 馭代 洪λ 2*/4水奖» i+fr床Λ含取代ΛΑΛ OJ0380 OJ031S4 HD OJ0122 00026 HD OJOCQ2 OJ0596 ND 2*/冰这《 金取代ΛΑΛ和科 OJ0108 0J0136 ND OJ0088 OJOQ37 m> ND 00067 0 JO 177 2V冰%鼉含取代轉Λ名拉科 OJOQ99 ΟΧ) 124 HD OJ01O3 OJ0026 OJOOOl OJOQ29 oom OJOW6 f 金物4故》«在#(TCLP珐由赛》 1S 5J0 1J0 5J〇 5J〇 02 - * H1EA R30912C NIEA S30611C HIEA K30611C H1EA R30611C H1EA E30U1C HIEA K31411C NIEA S30611C H1EA R30611C HIEA S30(511C 确 J* 老飧MUliSv抒祗4故表长值必•《并穿逍供Μ桷痄务·以小并衹4呔电祗典碟售我矛* 【提示 1 mg/1 = 1 mg/kg = lppm】 (二)土壤中污染物溶出分析 其次將純轉爐石及濕裹法、取代濕裹並用法處理後轉 爐石混合料的樣品視為土壤,以土壤中污染物溶出試驗分 析其在酸性條件下重金屬的溶出結果,轉爐石之溶出液中 以鉻、銅、鉛、鎳等重金屬溶出濃度較大,其中純轉爐石 中鉻溶出量偏高,遠高出管制標準3倍之多值得注意,其 φ餘鎘、銅、鉛、鋅、砷、汞、鎳等重金屬溶出量則遠低於 管制值,因此純轉爐石若作為工程土方使用將對環境造成 影響。 濕裹法、取代濕裹並用法處理後轉爐石混合料之溶出 液中仍以鉻、銅、鉛、鋅等重金屬溶出濃度較大,其中值Page 21 1287582 V. INSTRUCTIONS (17) Dissolution criteria for toxic characteristics. Table 1 0 converter stone and converter stone mixture toxicity characteristics dissolution test results 2 sets «耷1 (1 side "zm «« (Cr) (mail) Qu CCdJ (four) * (Pb) (four) sentence (four) (four) 饷 (called zinc ( At) 鹌 (NLJ (mail) 耒0J9146 OJ0183 m> 〇J〇08ti OJ0019 ND OJOQ99 〇J〇〇ei OJOQ82 0JDQ35 OJ0030 m> OJ0305 OJOOS4 0_2 HD OJ02S1 0fine OJ0199 OJ0397 ND OJ0136 OJOQ22 ND OJ0O44 OJ0474 OJ0082 2V ice hong IL+8y冰« ΑΛ » OJ0169 OJ0337 m> 0J0152 OJOQ22 OJOOOl ND OJ01D5 〇J〇»7 驭代洪λ 2*/4水奖» i+fr bed Λ with replacement ΛΑΛ OJ0380 OJ031S4 HD OJ0122 00026 HD OJOCQ2 OJ0596 ND 2 */冰的"""""""""""""""""""""""" In #(TCLP珐由赛》 1S 5J0 1J0 5J〇5J〇02 - * H1EA R30912C NIEA S30611C HIEA K30611C H1EA R30611C H1EA E30U1C HIEA K31411C NIEA S30611C H1EA R30611C HIEA S30 (511C J* 飧 MUliSv抒祗4 Value must be痄 · · · · · · · · · · · · · · · · · · · · · The sample of the converter stone mixture after the wet wrap and the treatment is regarded as the soil, and the dissolution result of the heavy metal under the acidic condition is analyzed by the pollutant dissolution test in the soil, and the molten iron of the converter stone is made of chromium, copper, lead, nickel, etc. The concentration of heavy metals is relatively high, and the amount of chromium dissolved in pure converter stone is too high, which is much higher than the control standard by 3 times. The amount of heavy metals such as cadmium, copper, lead, zinc, arsenic, mercury and nickel is more than φ. It is far below the control value, so pure converter stone will have an impact on the environment if it is used as engineering earth. The wet-packing method, the wet-wrap method and the treatment of the converter stone mixture are still dissolved in heavy metals such as chromium, copper, lead and zinc.

第22頁 1287582 五、發明說明(18) 得注意重金屬鉻溶出濃度偏高,需注意;就整體而言,除 鉻溶出濃度偏高外,其餘鎘、銅、鎳、鉛、鋅、砷、汞等 重金屬溶出均遠低於監測值,其分析結果如表1 1所示。 因此在土污考量下,以濕裹法、取代濕裹法處理後轉爐石 混合料在自然環境下若作為道路基底層級配及工程土方資 源化再利用時,對於土壤、地下水等自然環境應不致造成 污染與影響。 表11轉爐石及轉爐石混合料土壤污染物溶出物溶出結果 方法 名 稱 史金屬洛出壤茂 (mg/lcg) 鉻(Ci) (mg/k 自 铜(Cu) (mg/kg) 鉛(Pb) (mg/kg) 锌㈣ (mg/k卣 砷(As) (mg/kg) 采㈣ (rngflcg) 錁(Ni) (mg/kg) 来處眾 0.4195 1008.00 7.802 7.336 ND 0.305 0.095 4.021 濞A法 2%水泥濞衷+8%底灰 0·船0 189.80 12.86 7.266 11.67 0.433 0.084 9.360 2%水泥淇裏+8%飛灰 0.5111 185.00 12.88 9.073 6.593 0.854 0.096 7.740 2%水龙濞衷+ 8%水淬谑石扮 0.4393 152.70 8.屯 7.545 2.517 0.191 0.056 3.819 取代 濞衷 並用法 2%水泥濞衷+河床科全取代輯*石細科 0.4413 127.33 11.60 11.80 24.93 0.661 0.035 9.733 2%水龙濞裹+«麻«灰全取代轉«石細钭 0.4S61 129.28 18.32 14.58 48.28 0.573 0.082 26.28 2%水泥濞裹+高«石全取代輯城石細科 0.5196 138.58 15.23 14.43 28.45 ND 0.083 4.956 土«污染監測值 10 175 220 1000 1000 - - 130 土碟污染fW揉箄值 20 250 400 2000 2000 60 20 200 技驗规瘅 HIEA S321.61C N1EA S321.62C H1EA S321.63C NIEA S321.64C HIEA S121.65C HIEA M317.01C 腿A M317.01C HIEA S321.68C 備任 當撿潑换鼉線ft低值々备於方法俊珣杨蚨時· JX小於撿金婊*低tt度值表承· _ 參(三)王水消化分析 將純轉爐石及處理後轉爐石混合料的樣品視為土壤, 以王水消化試驗分析在酸性條件下重金屬的溶出結果,轉 -爐石之溶出液中以鉻、鉛、鋅等重金屬溶出較大,其中值 .得注意純轉爐石中鉻溶出濃度偏高’遠高出管制標準3倍Page 22 1278582 V. INSTRUCTIONS (18) Attention should be paid to the high concentration of heavy metal chromium, which should be noted; as a whole, in addition to the high chromium dissolution concentration, the remaining cadmium, copper, nickel, lead, zinc, arsenic and mercury The dissolution of heavy metals was much lower than the monitored value, and the analysis results are shown in Table 11. Therefore, under the consideration of soil pollution, if the converter stone mixture is treated as a basal gradation of the road and recycled by the earthwork in the natural environment by the wet wrap method instead of the wet wrap method, it should not be used for the natural environment such as soil and groundwater. Cause pollution and impact. Table 11 Converter stone and converter stone mixture soil pollutants dissolution solution method name history metal Luo Lemu (mg / lcg) chromium (Ci) (mg / k from copper (Cu) (mg / kg) lead (Pb (mg/kg) Zinc (4) (mg/k arsenic (As) (mg/kg) Mining (4) (rngflcg) 锞 (Ni) (mg/kg) to the public 0.4195 1008.00 7.802 7.336 ND 0.305 0.095 4.021 濞A method 2% cement + 8% 8% bottom ash 0 · ship 0 189.80 12.86 7.266 11.67 0.433 0.084 9.360 2% cement ash +8% fly ash 0.5111 185.00 12.88 9.073 6.593 0.854 0.096 7.740 2% water dragon 濞 + 8% water quenching 谑Stone Dressing 0.4393 152.70 8.屯7.545 2.517 0.191 0.056 3.819 Substitute and use 2% cement 濞心+河床科全换辑 *石细科0.4413 127.33 11.60 11.80 24.93 0.661 0.035 9.733 2% water dragon 濞 wrapped + «麻〗 Fully substituted to turn «石细钭0.4S61 129.28 18.32 14.58 48.28 0.573 0.082 26.28 2% cement 濞 wrapped + high « stone replacement stone stone fine branch 0.5196 138.58 15.23 14.43 28.45 ND 0.083 4.956 soil « pollution monitoring value 10 175 220 1000 1000 - - 130 Soil dish contamination fW depreciation 20 250 400 2000 2000 60 20 200 Technical specification 瘅 HIEA S321.61C N1EA S32 1.62C H1EA S321.63C NIEA S321.64C HIEA S121.65C HIEA M317.01C Leg A M317.01C HIEA S321.68C When the 捡 鼍 鼍 ft ft low value is prepared in the method Jun Jun Yang · · JX is less than捡金婊*low tt degree value bearing _ ginseng (3) Wangshui digestion analysis The samples of pure converter stone and treated converter stone mixture are regarded as soil, and the dissolution of heavy metals under acidic conditions is analyzed by aqua regia digestion test. As a result, the heavy metal such as chromium, lead, and zinc is dissolved in the eluate of the converter-hearthstone. The value of the solution is high. It is noted that the concentration of chromium dissolved in the pure converter stone is too high, which is 3 times higher than the control standard.

第23頁 1287582 五、發明說明(19) 之多,其餘鎘、銅、鉛、鋅、鎳等重金屬溶出量則遠低於 監測值,因此純轉爐石若作為工程土方使用將會對環境造 成影響。 濕裹法、取代濕裹並用法處理後轉爐石混合料之溶出 液中仍以鉻、鉛、鋅等重金屬溶出濃度較大,其中值得注 意重金屬鉻溶出濃度偏高,接近監測值,但仍低於管制 值,就整體而言,除鉻溶出濃度偏高外,其餘鎘、銅、 鎳、鉛、鋅等重金屬溶出均遠低於監測值,如表1 2所示。 因此將轉爐石混合料視成土壤考量下在自然環境下若作為 •道路基底層級配及工程土方資源化再利用時,對於土壤、 地下水等自然環境均不致造成污染與影響。 表1 2轉爐石及轉爐石混合料王水消化試驗結果 金全屑落出泫度 方法 名 稱 痛(Cd) (ing/k^) 路(Cr) (mg/kgj 拥(Cu) 嫌(Ni) (mg/kgj 鉛(Fb) (ingikg) ff(Zn) (mg)kg) 本處理 ⑽石 0.515 908.02 ND ND 12.7 舶 3.464 2%水泥通裏+8%底灰 0.626 144.774 2.227 3 284 13.608~ 17.704 通衷法 2%水泥邁衷+8%飛灰 0.602 140.529 2.678 ND 14.976 9.703 2%水泥通衷+ 8%水淬垴石粉 0.528 135.232 ND ND 11.142 4.640 吹代 通衷 2%水泥通裏+蚵床料仝吹代特垴石如料 0.643 111.258 3.669 5.655 11.848 25.244 2%水泥逋衷+¾¾底灰全取代轉垴:輪枓 0.740 114.496 12.144 26.539 14.771 72.660 並法 2%水迟通哀+高垴石仝吹代特垴名知料 0.601 120.870 7.559 ND 14.748 35.435 上绰讨换B激基牵值 10 175 220 130 1000 1000 上绰艿染管糾播準值 20 250 400 200 20⑽ 2000 H1EA S321.636 H1EA S321.63B HIEA S321.63B WEA S321.63B HIEA S321.63B H1EA S321.63B 儀 « «值iMMlfeSsftft低值~备於方法後闲&浓時_以'丨,於检曼線度值*承·Page 23 1,278,582 V. Inventive Note (19), the amount of heavy metals such as cadmium, copper, lead, zinc and nickel is much lower than the monitored value, so pure converter stone will have an impact on the environment if it is used as engineering earthwork. . The wet metal coating, the wet wrap and the treatment of the converter stone mixture still use a large concentration of heavy metals such as chromium, lead and zinc. The concentration of heavy metal chromium is high, close to the monitoring value, but still low. As a whole, the concentration of heavy metals such as cadmium, copper, nickel, lead and zinc is much lower than the monitored value, as shown in Table 12. Therefore, when the converter stone mixture is considered as a soil, it will not cause pollution and impact on the natural environment such as soil and groundwater if it is used as a basal layer gradation and engineering earthwork recycling in the natural environment. Table 1 2 Converter stone and converter stone mixture Wangshui digestion test results Gold full chip falling out method Method name pain (Cd) (ing/k^) Road (Cr) (mg/kgj 抱 (Cu) suspicion (Ni) (mg/kgj lead (Fb) (ingikg) ff (Zn) (mg) kg) The treatment (10) stone 0.515 908.02 ND ND 12.7 ship 3.464 2% cement pass +8% bottom ash 0.626 144.774 2.227 3 284 13.608~ 17.704 pass Concentrate 2% cement is eager to +8% fly ash 0.602 140.529 2.678 ND 14.976 9.703 2% cement through + 8% water quenched vermiculite powder 0.528 135.232 ND ND 11.142 4.640 Blow generation Tongxin 2% cement Tongli + trampoline material吹特特垴石如料0.643 111.258 3.669 5.655 11.848 25.244 2% cement + +3⁄43⁄4 bottom ash full replacement switch: rim 0.740 114.496 12.144 26.539 14.771 72.660 and 2% water late mourning + high 垴 stone with blowing Specially known as 0.601 120.870 7.559 ND 14.748 35.435 Upper 绰 换 B 激 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 S321.63B WEA S321.63B HIEA S321.63B H1EA S321.63B Instrument « «Value iMMlfeSsftft low value ~ ready for method after idle & thick time _ to '丨, inspected manda line value * Cheng·

(四)波索蘭材料添加量與回脹率關係模式(4) Mode of relationship between the amount of material added to the wave and the rebound rate

第24頁 1287582 五、發明說明(20) 本發明中濕裹法、取代及 加材料都是波索蘭材料,i i f並用法等兩種工法所添 FeO、Mg〇、Na2〇、A1 〇 化合物由ca〇、Si02、 取代及濕裹並用法i〇i波τ;2= 此添加波索蘭材料的觀念:、不管因此如何延伸 取代濕裹並用法,尸I天Λ I任何組合,不限濕裹法、 合規範工程及環境品質^ ^ 了疋比率的波索蘭材料即可符 波索蘭材料係指所含惫务 成之氫氧化辑,或外加驗Κ =氧化銘能與水泥水化生 卜而有類似水泥水化產物之膠 波索蘭水化反應’ Γ其波索蘭反應之反應式可簡之任何材料均屬之。 ΚΗ ΝΗ CH水泥或外加fit· K-S/A-H n-s/a-h C-S/A-H 黪ft S/A 波索β材料 :)上可看/波索蘭材料主要因含有大量氧化矽及少量 銘,才能和水泥中之「氫氧化鹼…水」產生反 應作\因為波索蘭材料能消耗驗f反應,包括氫氧化 =虱_化鉀等,可清除水泥及骨材中有害物質,有助於 产硫性質及抗鹼骨材反應作用;另外波索蘭材料更由於固 化易溶性之氫氧化躬,冑骨材水泥衆界面更穩定,明顯會 減低水的渗透性,故叉被稱為「減滲劑」。 本發明藉由波索蘭材料的各種功能與優點藉以改善轉 爐石的各種性質,本發明中所採用的穩定處理方法就是以 + + Η水 (1)Page 24 1278582 V. INSTRUCTIONS (20) In the present invention, the wet wrap method, the substitution and the addition materials are both Possolan materials, and the two methods of iif and usage are added by FeO, Mg〇, Na2〇, and A1 〇 compounds. Ca〇, SiO2, substitution and wet wrap and usage i〇i wave τ; 2= The concept of adding Possolan material: no matter how it is extended to replace the wet wrap and usage, corpse I Λ I any combination, not limited to wet Wrap method, standard engineering and environmental quality ^ ^ The ratio of the Poislan material to the 疋 索 材料 符 符 索 索 索 索 索 索 氢氧化 氢氧化 氢氧化 氢氧化 氢氧化 氢氧化 氢氧化 氢氧化 氢氧化 氢氧化 Κ Κ Κ Κ Κ Κ Κ Κ Κ Κ Κ Κ Κ Κ Κ Κ Κ Κ There is a plastic hydration product similar to the cement hydration product, which can be used in any reaction. ΚΗ ΝΗ CH cement or plus fit· KS/AH ns/ah CS/AH 黪ft S/A corrugated beta material:) can be seen / Possolan material mainly contains a large amount of cerium oxide and a small amount of "Hydroxide alkali...water" produces a reaction. Because the corsolone material can consume the f reaction, including hydroxide = 虱 potassium, etc., it can remove harmful substances in cement and aggregates, and contribute to the sulfur-producing properties. Alkali-resistant aggregate reaction; in addition, the Possolan material is more stable due to the curing of the soluble yttrium hydroxide, and the joint interface of the strontium cement is more stable, which obviously reduces the permeability of the water. Therefore, the fork is called a "reduction agent". The present invention utilizes various functions and advantages of the Poislan material to improve various properties of the converter stone. The stable treatment method used in the present invention is to + + Η水 (1)

1287582 五、發明說明(21) 稀f、,結、固化、降低鹽基度的方式,來降低重金屬、容 出量,減少驗的供應量,降低ρΗ值。 *低重金屬令 回脹試驗方面乃依據JIS Α 5〇15所規定之方法 ί = 所示,本發明為瞭解波索蘭材料添加量 與3 Ϊίΐ 特將表5、表6及表9彙整成表13,表中 所ίί”材料添加量為各種穩定方法中(氧化矽及氧化 鋁)〜〇扣除純轉爐石中(氧化矽及鋁 率則為游離石Hf_Ca〇)分別為1〇2%、4 6%^8% = 種方法中利用CNS 14602( JIS A 5015)方法所測得結果; t建立波索蘭材料添加量與回脹率關係模式,再利用 表13-貝料,將波索蘭材料添加量作為橫座標, 縱座標,緣製成圖13所示,當卜Ca〇=1.〇2%時,推脹導革作為 索蘭材料添加量與回脹率關係式為γ = 33. 4Γ1 m ;\ 4女6%時,關係式為γ = 5. 35χ_0·507 ;卜^㈣ :二 ,中回脹率随波索蘭材料添加量增加而降低,這三組 以卜Cao=4.6%時方程κγ=5.35χ_。·5。7回脹率最大,因t -(含有大量氧化二,=加t波索蘭材料 •合規範工程品質i求氧幻'在12%〜5n之間即符1287582 V. INSTRUCTIONS (21) Lean f, knot, solidification, and reduction of the basicity of the salt to reduce the amount of heavy metals and the amount of charge, reduce the supply of the test, and reduce the value of ρΗ. * Low-heavy metal causes the re-expansion test to be based on the method ί = specified in JIS Α 5〇15. The present invention summarizes Table 5, Table 6 and Table 9 for understanding the amount of Possolan material added and 3 Ϊίΐ. 13, the amount of material added in the table is a variety of stable methods (yttria and alumina) ~ 〇 deducted from the pure converter stone (the yttrium oxide and aluminum rate is free stone Hf_Ca 〇) respectively 1 〇 2%, 4 6%^8% = the results measured by the method of CNS 14602 (JIS A 5015) in the method; t establish the relationship between the amount of the addition of the material and the rebound rate, and then use the table 13 - shell material to The amount of material added as the abscissa, the ordinate, and the edge are shown in Fig. 13. When the Ca 〇 = 1. 〇 2%, the relationship between the amount of the swelled leather as the addition of the Solan material and the rebound rate is γ = 33. 4Γ1 m ; \ 4 female 6%, the relationship is γ = 5. 35χ_0·507; Bu ^ (4): Second, the medium back expansion rate decreases with the increase of the amount of Posoline material added, these three groups with Bu Cao = 4.6% equation κγ=5.35χ_··5. 7 rebound rate is the largest, because t - (containing a large amount of oxidation, = plus t wave solan material • standard engineering quality i seeking oxygen illusion) in 12% ~ 5n Instant

第26頁 1287582 五、發明說明(22) 表1 3波索蘭材料添加量與回脹率關係 方法 名箱 加f 铒Λ曼(%) sm m) S+A m S/A (%) f-C4〇 :1.02% f-C4〇 *4.6% f-C4〇 *6.8% 料霣石 9.22 0.17 9.39 0 7.62 9.06 4.30 2»水ΛΛλ+8%底灰 19.79 5.02 24.81 15.42 1.13 1.36 1.20 2%永ΛΛ 4+8%戒灰 23.49 5.06 27.55 18.1(5 0.83 1.25 1.07 2%水ΛΛ Λ+ 8%水洚Jtt石粉 24 7.48 31.48 22.09 0.52 1.13 0.74 法 2%水ΛΛ 科全氦代拽Jtt石㈣*4 21.60 4.02 25.62 16.23 1.20 0.99 0.59 2%水ΛΛ 4+耋廒底灰全Λ代料逋石知科 37.30 8.17 45.47 36.08 0.47 0.92 134 2%水Λ扁&+备逋;仑敫代轶逋石知科 36.40 6.34 42.74 33.35 0.33 0.90 0A5 供it 表中S代* Si02A代表AlaCb;波犮<8杖科峥加曼•(各挽方法+ 合争S*Aft合) (五)波索蘭材料添加量與重金屬鉻溶出量關係模式 本發明為瞭解波索蘭材料添加量與重金屬鉻在毒性特 性溶出、土壤中污染物溶出與王水消化中溶出濃度的關 係,在重金屬溶出中以重金屬鉻溶出量最大,因此將重金 屬鉻作為溶出量控制的元素。特將表9、表11及表12彙整 成表1 4,表中所述波索蘭材料添加量為各種穩定方法中 (氧化矽及氧化鋁)總合扣除純轉爐石中(氧化矽及氧化 鋁)總合,鉻重金屬溶出濃度則為各種方法中利用土壤中 •污染物溶出與王水消化溶出所測得結果;另外為建立波索 蘭材料添加量與絡溶出量關係模式,再利用表1 4資料,將 波索蘭材料添加量作為橫座標,將土壤中污染物溶出與王 水消化溶出中重金屬鉻溶出濃度分別作為縱座標,繪製成 圖1 4所示。Page 26 1278582 V. Description of invention (22) Table 1 Relationship between the amount of addition of corsolin material and the rate of rebound. Name box plus f 铒Λman (%) sm m) S+A m S/A (%) f -C4〇:1.02% f-C4〇*4.6% f-C4〇*6.8% 霣石9.22 0.17 9.39 0 7.62 9.06 4.30 2»Water ΛΛλ+8% bottom ash 19.79 5.02 24.81 15.42 1.13 1.36 1.20 2% forever 4+8% ash ash 23.49 5.06 27.55 18.1 (5 0.83 1.25 1.07 2% leeches Λ + 8% leeches Jtt stone powder 24 7.48 31.48 22.09 0.52 1.13 0.74 method 2% hydrazine 氦 氦 拽 tt tt tt tt tt tt tt tt tt tt 60 60 4.02 25.62 16.23 1.20 0.99 0.59 2% leeches 4+ 耋廒 灰 Λ Λ 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 36.40 6.34 42.74 33.35 0.33 0.90 0A5 For the S generation in the table * Si02A stands for AlaCb; Waves <8 rods 峥 峥 曼 • • ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( ( Mode of relationship with heavy metal chromium elution amount The present invention relates to understanding the relationship between the amount of corsosol material added and the dissolution of heavy metal chromium in the toxic characteristic, the dissolution of pollutants in the soil and the dissolution concentration in the aqua regia. In the metal elution, the amount of heavy metal chromium eluted is the largest, so the heavy metal chromium is used as the element for controlling the amount of dissolution. Table 9, Table 11 and Table 12 are summarized into Table 14. The amount of the Possolan material added in the table is stable. In the method (the combination of cerium oxide and aluminum oxide), the total combination of pure converter stone (yttria and alumina) is subtracted, and the concentration of chromium heavy metal is determined by using various methods in the soil. • Contaminant dissolution and aqua regia digestion. Results; In addition, in order to establish the relationship between the amount of corsosol material added and the amount of complex dissolution, and then use the data of Table 14 to use the amount of corsosol material as the abscissa, dissolve the pollutants in the soil and digest the dissolved heavy metal chromium in the aqua regia. The dissolution concentrations were plotted as ordinates, respectively, as shown in Figure 14.

第27頁 1287582 五、發明說明(23) 在土壤污染物溶出試驗中推導出波索蘭材料添加量與 鉻溶出量關係式為Y = 729. 8 irG·494 ;在王水消化試驗中推導 出波索蘭材料添加量與鉻溶出量關係式為Υ = 313. 58Γ0·282, 式中Υ為重金屬鉻溶出量,X為波索蘭材料添加量,兩式中 鉻溶出量均隨波索蘭材料添加量增加而降低,如圖1 4所 示。這兩組方程式中以土壌污染物溶出試驗中推導出波索 蘭材料添加量與鉻溶出量關係式為Υ = 729. 81 X_G·49鉻溶出量 最大,因此本發明以Y = 729. 8 1 X_D·49為控制模式,只要波索 蘭材料添加量落在8%〜50%之間,即符合環境品質要求。 • 表1 4波索蘭材料添加量與土污王水消化鉻溶出量關係 方法 名蒱 浃女蚪含曼 法宏<1杈 料峥加t L壤泞诠 水屯化 sm 雄) S+A m S/A m 极态圯Λ度 扣妙幻 铱渚1&龙度 轶逋石 9.22 0.17 939 0 1008.00 908.02 2%水Λ肩裊+3%底灰 19.79 5.02 24.81 15.42 189.80 144.74 2%水ΛΛλ+8%戒灰 22.49 5.06 27.55 18.16 185.00 140.529 2%水ΛΛ 4+8%禾淬嫌石粉 24 7.*8 31.48 22.09 152.70 135.232 2%永ΛΛ 仝株逋石知科 21.60 4.02 25.62 16.23 127.33 111.2 筇 2%水裊+嘗廉底灰仑Λ·代轶嫿石私料 37.30 8.17 45.47 36.08 129.28 114.496 2%禾Λ為%+备逋石会丸R料逋石私科 36.40 6.34 42.74 33.35 138.58 120.870 倩ϋ *和SfUt SiO:i?A代袅AHh,法ί:β杖料砟加曼(各Λ方法令S*Aft合)一(»»石令S*Aft合) _【4】微觀結構觀察 再以掃描式電子顯微鏡(SEM)觀察水泥及波索蘭材料-飛灰、電廠底灰、高爐石、水淬爐石粉及河床粒料等材料 養治7天後晶相變化,(1)水泥:外觀以針刺狀的C-S-Η膠 •體與六角片狀的氫氧化弼結合,如圖15所示;(2)電薇底Page 27 1278582 V. INSTRUCTIONS (23) In the soil pollutant dissolution test, the relationship between the amount of corsosol material added and the amount of chromium dissolved is Y = 729. 8 irG·494; deduced in the aqua regia test The relationship between the amount of corsosol added and the amount of chromium dissolved is Υ = 313. 58Γ0·282, where Υ is the amount of heavy metal chrome dissolved, X is the amount of corsol blue material added, and the amount of chrome dissolved in both formulas is related to the wave solan The amount of material added increases and decreases, as shown in Figure 14. In the two sets of equations, the relationship between the amount of corsosol material added and the amount of chromium dissolved is derived from the soil contaminant dissolution test. Υ = 729. 81 X_G·49 The maximum amount of chromium elution, so the present invention takes Y = 729. 8 1 X_D·49 is the control mode, as long as the amount of the Possolan material is between 8% and 50%, that is, it meets the environmental quality requirements. • Table 1 4 The relationship between the amount of corsosol material added and the amount of digested chrome dissolved by the soil aqua regia. The name of the 蒱浃 蚪 蚪 曼 曼 曼 杈 杈 杈 杈 杈 杈 杈 杈 t t t t t t t + + + + + + + A m S/A m Extreme state deduction 妙 铱渚 1 & Long 轶逋 9.2 9.22 0.17 939 0 1008.00 908.02 2% Λ shoulder 袅 +3% bottom ash 19.79 5.02 24.81 15.42 189.80 144.74 2% ΛΛ λ +8% ash ash 22.49 5.06 27.55 18.16 185.00 140.529 2% leeches 4+8% boring stone powder 24 7.*8 31.48 22.09 152.70 135.232 2% yongshao 逋石知科 21.60 4.02 25.62 16.23 127.33 111.2 筇2 %水袅+尝廉底灰仑Λ·代轶婳石私料37.30 8.17 45.47 36.08 129.28 114.496 2% 禾Λ is %+备逋石会丸R material 逋石私科36.40 6.34 42.74 33.35 138.58 120.870 Qian ϋ * And SfUt SiO:i?A on behalf of AHh, method ί:β rod material 砟Manman (each method makes S*Aft) one (»»石令S*Aft combination) _[4] microstructure observation Scanning electron microscopy (SEM) was used to observe the changes of crystal phase in cement and corsosol materials - fly ash, power plant bottom ash, blast furnace stone, water quenching furnace powder and river bed pellets after 7 days. (1) Cement: The appearance of a needle-shaped C-S-silicone rubber body combined with a hexagonal sheet of barium hydroxide, as shown in Figure 15; (2)

第28頁 1287582 五、發明說明(24) 灰··外觀則以2 /zm〜5 大小不等球狀結構及桿狀結構組 合,其球狀顆粒粒徑較小,中間分佈著大小不等的^隙a 如圖1 6所示;(3 )電廠飛灰··外觀均以大小不等球狀結構 交錯組合’其球狀顆粒粒徑較大,中間分佈著大小 隙,如圖1 7所示;(4)水淬爐石粉:外觀則以多邊行角粒 狀結構及片狀結構組合,組成牟 大小不等孔隙,如圖18所干成^參差不齊,巾間分佈著 ’結構熔融成-體成土團狀? 土(5):爐石:外觀則以片狀、 佈著密集的微細孔隙,土困 σ 土團結合,土團中分 •圖19所示;(6)河床細粒料團/冰土團間分佈著較大的孔隙如 •土團,土困與土圏緊密乂.外觀則以片狀結構疊彻而成 冢在、、、σ合,如圖20所示。Page 28 1278582 V. INSTRUCTIONS (24) The appearance of ash··················································· ^Gap a as shown in Figure 16.; (3) Power plant fly ash · · Appearances are arbitrarily combined with spheroidal structures of different sizes. 'The spherical particles have larger particle sizes, and there are large and small gaps in the middle, as shown in Figure 17. (4) Water quenching furnace powder: The appearance is a combination of polygonal granular structure and sheet structure, which constitutes unequal pores. As shown in Fig. 18, the mixture is uneven and the structure is melted. Is it a body-like mass? Soil (5): Hearthstone: Appearance is in the form of flakes, densely packed with fine pores, soil trapped in σ soil group, and divided into soil masses; Figure 19; (6) Riverbed fine grain mass / ice soil mass There are large pores such as • soil mass, the soil is tight and the soil is tight. The appearance is formed by laminating the sheet structure, and the σ is combined, as shown in Fig. 20.

第29頁 1287582 圖式簡單說明 【圖式簡單說明】 第一圖轉爐石粒徑分佈曲線 第二圖新鮮轉爐石X光繞射分析圖 第三圖轉爐石熟化前晶相圖 (1)片狀結構 第四圖轉爐石熟化前晶相圖 (1)薔薇狀膠體 第五圖轉爐石熟化前EDS分析圖 '第六圖轉爐石熟化後EDS分析圖 •第七圖濕裹法養治時間與回脹率關係圖 第八圖濕裹法養治時間與回脹率關係圖 第九圖濕裹法養治時間與回脹率關係圖 .第十圖取代濕裹並用法養治時間與回脹率關係圖 第十一圖取代濕裹並用法養治時間與回脹率關係圖 第十二圖取代濕裹並用法養治時間與回脹率關係圖 第十三圖波索蘭材料添加量與回脹率關係圖 第十四圖波索蘭材料添加量與重金屬鉻溶出量關係圖 第十五圖水泥養治7天後晶相圖 (1 )六角片狀晶氧化鈣 • (2)針刺狀C-S-Η膠體 第十六圖電廠底灰養治7天後晶相圖 (1)球狀結構 (2 )桿狀結構 •第十七圖電廠飛灰養治7天後晶相圖Page 29 1278582 Brief description of the diagram [Simple description of the diagram] The first map of the converter stone particle size distribution curve The second diagram of the fresh converter stone X-ray diffraction analysis diagram The third diagram of the converter stone before the crystal phase diagram (1) sheet Structure 4: Pre-crystallizing pre-crystal phase diagram (1) Rose-like colloids Figure 5 EDS analysis before toughening of the converter stone Figure 6 EDS analysis after the transformation of the converter stone • Figure 7: Wet wrap method for curing time and rebound Figure 8 shows the relationship between the curing time and the rebound rate of the wet wrap. The ninth figure shows the relationship between the curing time and the rebound rate of the wet wrap. The tenth figure replaces the wet wrap and the relationship between the curing time and the rebound rate is the tenth. Figure 1 replaces the wet wrap and the relationship between the curing time and the rebound rate. Figure 12 replaces the wet wrap and the relationship between the curing time and the rebound rate. The thirteenth figure shows the relationship between the amount of the material and the rebound rate. Diagram of the relationship between the addition amount of four figure Possolan and the amount of chromium dissolved by heavy metal. Figure 15: Crystal phase diagram after 7 days of cement curing (1) Hexagonal plate crystal calcium oxide • (2) Needle-like CS-Η colloid 16th Figure 7: Crystal phase diagram after 7 days of power plant bottom ash treatment (1) Spherical structure (2) Rod structure • The seventeenth figure of the power plant fly ash after 7 days of crystal phase diagram

第30頁 1287582 圖式簡單說明 (1)中空圓球 第十八圖水淬爐石粉養治7天後晶相圖 (1 )片狀及角粒狀結構 第十九圖高爐石養治7天後晶相圖 (1 )片狀結構熔融成土團 第二十圖河床粒料晶相圖 (1 )片狀結構 _ 1^1 第31頁Page 30 1278582 Brief description of the diagram (1) Hollow sphere 18th water quenching furnace stone powder after 7 days of crystal phase diagram (1) sheet and angular structure 19th blast furnace stone treatment 7 days after crystal Phase diagram (1) sheet structure melting into earth masses twentieth map riverbed pellet phase diagram (1) sheet structure _ 1^1 Page 31

Claims (1)

1287582 六、申請專利範圍 1· 一種製作可抑制问勝孩& s 方法,包括: 及重金屬浴出之改良轉爐石材料的 a)轉::經濕裹法、取代濕裹並用波 ::處理後混合料,統稱為轉爐石混合料; ΐ Ϊ : Ϊ定工法中所採用(1)濕裹法⑴取代濕裹並用 '^於波索蘭材料添加法,其添加之波索蘭材料 電廠底灰、碎灰、電廠飛灰、高爐石、水 、砂石粒料等及其他具相同功效之材料; ""算膠」鉍\蘭材料系指所含氧化矽及氧化鋁能與水泥 化生成之氫氧化鈣,或外加鹼質物產生緩 慢波索蘭水化反靡,;女*s ,, 應而有類似水泥水化產物之膠結性 反應之任何材料均屬之; HZ” ’僅考慮回脹率時,應添加 料。卽-° 1招2篁氧化矽及少量氧化鋁的波索蘭材 料’即付合規範工程品質要求; 。經處理後轉爐石混合料,僅考慮 添加8%〜50%含有大詈惫外访丨、窃e合®董于應 u & μ入ω…氧化矽及少$氧化鋁的波索蘭 材枓即符合規乾環境品質要求· 混合料’同時考慮回脹率及重金屬溶 出篁,應添加8%〜50%之波索蘭材料, 及環境品質要求。 付0 依據申請專利範圍第!項之方法,經處理後 合料,可增加剪力強度、 轉爐 率與承載力符合公路規範的要纟g : ^率’其θ ^ 祝乾的要求,顯不所得之改良轉爐 第32頁 1287582 六、申請專利範圍 石材料是合於規範的良好填築材; 3·依據申請專利範圍第】項之方法,經處 ;^ f金f溶出、土壤污染物溶出及王/走轉爐石混合 4 Μ Γ f I管制標準,符合環境品質要灰'肖化均遠低於 •二料確ϊ ί利範圍第1項之方法,經處理後二 良好填築材,可應用於道政爐石混 π址4其他相關之土木、建 、路、平台填方 圍第1項之方法,以添加含有大 6.依據料,即… 料添加法,經本法處理,本專利屬於波索蘭材 木、建築再生材料、2 ^爐石混合料可成為良好土 本專利之重點。、、表色建材及其他相關工程材料亦為 第33頁1287582 VI. Scope of Application for Patention 1. A method for producing a method for suppressing a child's shovel, including: and a modified converter stone material from a heavy metal bath: a) Transfer: Wet wrap, replace wet wrap and use wave:: The post-mixing material, collectively referred to as the converter stone mixture; ΐ Ϊ : used in the Ϊ 工 method (1) wet wrap method (1) instead of wet wrap and using '^ in the wave solan material addition method, the added Possolan material power plant bottom Ash, crushed ash, power plant fly ash, blast furnace stone, water, sand stone pellets, etc. and other materials with the same effect; ""According rubber"铋\兰材料 means cerium oxide and alumina containing cement and cement Calcium hydroxide produced by the formation of calcium hydroxide, or added alkalinity, produces a slow wave of osmolality; female *s, any material that has a cementitious reaction similar to cement hydration products; HZ" 'only When considering the rate of re-expansion, the material should be added. 卽-° 1 stroke 2 篁 篁 矽 矽 矽 矽 矽 矽 矽 矽 矽 ' ' ' ' ' ' ' ' ' ' ' ' ' ' ' ' 规范 规范 规范 规范 规范 规范 规范 规范 规范 。 。 。 %~50% contains Daxie’s visit, and e-mailing® Dong Yuying u & μ into ω... yttrium oxide and less than $ alumina of corsolan 枓 meet the requirements of the standard environmental quality · Mixture 'considering the rebound rate and heavy metal dissolution 篁, should add 8% ~ 50% of the wave Blue material, and environmental quality requirements. Pay 0 According to the method of the application of the scope of the patent item, after the treatment, the shear strength, converter rate and bearing capacity can be increased to meet the requirements of the highway code: ^ rate 'the θ ^ The request for the dry, the improved converter, the 32nd page, 1287582 6. The patented stone material is a good filling material in accordance with the specifications; 3. According to the method of applying for the patent scope, the method; Gold f dissolution, soil contaminant dissolution and king / go to hearthstone mix 4 Μ I f I control standards, in line with environmental quality to be gray 'Shaw is far lower than • two materials are indeed ί 范围 range of the first method, by After the treatment, the second good filling material can be applied to the method of the first item of the civil engineering, construction, road and platform filling of the XX site of the Daozhen furnace stone mixing, to add the large amount of the material according to the material. Adding method, processed by this method, this patent belongs to wave Blue timber wood, construction recycled materials, 2 ^ furnace slag mix may be the focus of this patent is good soil. ,, table color building materials and other related engineering materials also page 33
TW94120132A 2005-06-16 2005-06-16 Improved basic oxygen furnace slag material with ability to inhibit swell again and leaching of heavy metals-Pozzolans addition TWI287582B (en)

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