TWI631091B - A method of modifying alkaline solid wastes as green construction materials - Google Patents
A method of modifying alkaline solid wastes as green construction materials Download PDFInfo
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- 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
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- 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
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Abstract
本發明係一種利用含二氧化碳源之排氣,於液相溶液中與鹼性固體廢棄物混和反應,以降低固體廢棄物之活性及鹼性,達到廢棄物改質安定化目的,此發明有助於反應後之固體廢棄物可直接作為綠色建材。本發明依序包含有一液相注入步驟,一鹼性固體廢棄物投入步驟,一混和步驟,一二氧化碳源注入步驟,一反應步驟,一分離步驟,及一作為綠色建材步驟。本發明有別於傳統安定化方法使用高溫高壓蒸氣或長時間風化程序,係直接使用一含二氧化碳源之排氣進行鹼性固體廢棄物改質及安定化,以確保安定化後固體廢棄物適宜作為綠色建材,改善避免日後建築材料出現體積膨脹之現象。 The invention relates to an exhaust gas containing a carbon dioxide source, which is mixed with an alkaline solid waste in a liquid phase solution to reduce the activity and alkalinity of the solid waste, thereby achieving the purpose of reforming and restoring waste, and the invention is helpful The solid waste after the reaction can be directly used as a green building material. The invention comprises a liquid phase injection step, an alkaline solid waste input step, a mixing step, a carbon dioxide source injection step, a reaction step, a separation step, and a green building material step. The invention is different from the traditional stabilization method using high temperature and high pressure steam or long-time weathering procedure, and directly uses an exhaust gas containing a carbon dioxide source to reform and stabilize the alkaline solid waste to ensure the solid waste after stabilization. As a green building material, it will improve the phenomenon of avoiding the volume expansion of building materials in the future.
Description
本發明係關於一種鹼性固體廢棄物改質作為綠色建材之方法;特別關於一種利用含二氧化碳源之氣體,於液相溶液中與鹼性固體廢棄物混和反應,以降低固體廢棄物之鹼性,反應後之固體廢棄物可直接作為綠色建材。 The invention relates to a method for upgrading alkaline solid waste as a green building material; in particular to a method for mixing and reacting with a basic solid waste in a liquid phase solution by using a gas containing a carbon dioxide source to reduce the alkalinity of the solid waste. The solid waste after the reaction can be directly used as green building materials.
鹼性固體廢棄物(例如:煉鋼爐碴、飛灰等)常是工廠或發電廠需處理之副產品。由於鹼性固體廢棄物成分類似天然砂石,具耐磨、耐高溫及耐腐蝕等優異特性,適合取代土木工程中使用之天然砂石,深具資源再利用效益,可應用作為例如:建築材料、路基鋪面、磚瓦摻配料等。 Alkaline solid waste (eg, steelmaking furnaces, fly ash, etc.) is often a by-product of the plant or power plant. Because the alkaline solid waste is similar to natural sandstone, it has the characteristics of wear resistance, high temperature resistance and corrosion resistance. It is suitable to replace the natural sand used in civil engineering. It has deep resource reuse benefits and can be applied as, for example, building materials. , roadbed paving, bricks and other ingredients.
查,2015年05月01日公告之中華民國專利第201507990號中披露之「以固體廢棄物製備混凝土的方法、所製成之混凝土以及固體廢棄物的回收處理方法」,該發明係一種以固體廢棄物製備混凝土之方法,於試體中摻混一去鹼試劑,並進行養護程序步驟,以形成混凝土應用於土木工程建設。 The method of preparing concrete from solid waste, the concrete produced and the method for recovering solid waste disclosed in the Republic of China Patent No. 201507990, which is disclosed in the Japanese Patent No. 201507990, the invention is a solid For the method of preparing concrete by waste, a de-alkali reagent is mixed in the test body, and a maintenance procedure is carried out to form concrete for civil engineering construction.
然,鹼性固體廢棄物多半含有約1-10%之游離氧化鈣(Free-CaO)與氫氧化鈣(Ca(OH)2)等活性物質,資源化應用時易造成「高 鹼度」及「體積不穩定」等困境,故需經過「安定化」改質處理,將其所含活性物質成份去除,以避免造成路基膨脹破裂或地基鬆動等嚴重工安問題。 However, most of the alkaline solid waste contains about 1-10% of free calcium oxide (Free-CaO) and calcium hydroxide (Ca(OH) 2 ) and other active substances, which may cause "high alkalinity" when used in resource utilization. In the case of "unstable volume" and other difficulties, it is necessary to undergo "enhanced" upgrading treatment to remove the active substances contained in it to avoid serious work safety problems such as roadbed expansion and rupture or loose foundation.
查,2010年11月01日公告之中華民國專利第201038741 A1號中披露之「利用濕磨法進行安定化之轉爐石資源化處理方法」,該發明係針對一未安定化之爐碴,進行濕磨成漿體狀,以進行安定化步驟,處理後漿體可直接拌合應用於混凝土工程。 Investigating, in November 1, 2010, the "Recycling Stone Resource Recycling Method by the Wet Grinding Method" disclosed in the Republic of China Patent No. 201038741 A1, the invention is directed to an unsteady furnace It is wet-ground into a slurry to carry out the stabilization step. After the treatment, the slurry can be directly mixed and applied to concrete engineering.
現已有商業化之鹼性固體廢棄物安定化技術運轉,例如:室外自然養生法、高壓蒸氣養生法、常壓蒸氣養生法、HK水淬粒化法、悶罐法、滾筒法、及改質法等,可去除鹼性固體廢棄物內活性物質,例如:游離氧化鈣、氫氧化鈣等。然,以室外自然養生法為例,係將爐碴直接堆置於室外,利用大氣中中二氧化碳及水氣(或雨水)對鹼性固體廢棄物產生水化反應,耗時長且需大面積處理場地,並易造成廠區揚塵,難以進行大規模處理。以常壓蒸氣養生法為例,係將鹼性固體廢棄物放置在儲坑內後上蓋帆布,用加壓蒸氣(壓力約為1kg/cm2,溫度保持100℃以上)使鹼性固體廢棄物與蒸氣反應。上述該類方法仍將游離氧化鈣轉化成氫氧化物,而氫氧化物仍處於不穩定狀態,且常需額外投入大量能量或化學藥劑。此類技術雖然對於習知技術有所貢獻,惟其技術手段及功效仍具有改善的空間。 Commercialized alkaline solid waste stabilization technology has been put into operation, such as: outdoor natural health method, high pressure steam regimen, atmospheric pressure steam regimen, HK water quenching granulation method, stuffing tank method, roller method, and modification The mass method and the like can remove active substances in alkaline solid waste, such as free calcium oxide and calcium hydroxide. However, taking the outdoor natural health method as an example, the furnace is directly stacked outdoors, and the carbon dioxide and water vapor (or rainwater) in the atmosphere are used to hydrate the alkaline solid waste, which takes a long time and requires a large area. Dealing with the site, and easily causing dust in the plant area, it is difficult to carry out large-scale processing. Taking the atmospheric pressure steam curing method as an example, the alkaline solid waste is placed in the storage pit and then covered with canvas, and the alkaline solid waste is made by pressurized steam (pressure is about 1 kg/cm 2 and temperature is maintained above 100 ° C). Reacts with steam. The above methods still convert free calcium oxide to hydroxide, while the hydroxide is still in an unstable state and often requires additional energy or chemicals. Although such technologies contribute to the prior art, their technical means and functions still have room for improvement.
綜合以上,發現過去鹼性固體廢棄物安定化技術,若係傾倒於廠內或室外,所需時間長或占地面積大,且易造成揚塵與空污問題,活性物質無法完全安定化;有些技術則尚需消耗大量能資源,例如:化學藥 劑、水資源、加壓蒸氣等,因此,此類鹼性固體廢棄物處理之成本高,並不符合「綠色科技」原則。 Based on the above, it has been found that the alkaline solid waste stabilization technology in the past, if it is dumped in the factory or outdoors, takes a long time or a large area, and is easy to cause dust and air pollution problems, the active material can not be completely stabilized; Technology still consumes a lot of energy resources, such as: chemical drugs Agents, water resources, pressurized steam, etc. Therefore, the cost of such alkaline solid waste treatment is high and does not meet the "green technology" principle.
本發明目的係在提供一新穎綠色科技,將鹼性固體廢棄物改質作為「綠色建材」,其特徵為使用一含有二氧化碳源之排氣,與鹼性固體廢棄物於液相媒介中反應,以安定化鹼性固體廢棄物中之活性物質,確保安定化後固體廢棄物適宜作為綠色建材,改善避免日後建築材料出現體積膨脹之現象。本發明處理後之固體產物成分類似天然礦石,且為安定化物料,可應用於建築工程,作為綠色建築材料,提供環境與經濟效益,達成循環經濟概念。 The object of the present invention is to provide a novel green technology for upgrading alkaline solid waste as "green building materials", characterized in that a waste gas containing a carbon dioxide source is used to react with alkaline solid waste in a liquid medium. In order to stabilize the active substances in the alkaline solid waste, it is ensured that the solid waste after stabilization is suitable as a green building material, and the phenomenon of avoiding the volume expansion of the building materials in the future is improved. The solid product component treated by the invention is similar to natural ore, and is a stable material, which can be applied to construction engineering, as a green building material, providing environmental and economic benefits, and achieving the concept of circular economy.
本發明提供一鹼性固體廢棄物改質作為綠色建材之方法,參閱圖1,其依序包含有液相注入步驟(11),鹼性固體廢棄物投入步驟(12),混和步驟(13),二氧化碳源注入步驟(14),反應步驟(15),分離步驟(16)及作為綠色建材步驟(17)。本發明提供一鹼性固體廢棄物改質作為綠色建材之方法,可針對各種不同性質之鹼性固體廢棄物進行改質及安定化,應用範圍廣,避免傳統安定化程序使用高溫高壓蒸氣,有效減少能資源使用;同時,反應後固體產物成分類似天然礦石,可作為綠色建材應用於建築工程,提供額外環境與經濟效益。其中,藉由該液相注入步驟(11)與該鹼性固體廢棄物投入步驟(12),並進行混和步驟(13),形成液固重量比為1:1到50:1之混和物,該混和物具高鹼性。而後再進行二氧化碳源注入步驟(14),此類含二氧化碳源可為煙囪、熱風爐、燃燒爐等煙囪排氣,以進行反應步驟(15),改質安定化鹼性固體 廢棄物。最後,藉由該分離步驟(16)進行液固分離,所得之該安定化固體廢棄物可做資源化用途,例如:水泥摻配料等,作為綠色建材步驟(17)。 The invention provides a method for upgrading an alkaline solid waste as a green building material, and referring to FIG. 1 , which comprises a liquid phase injection step (11), an alkaline solid waste input step (12), and a mixing step (13). The carbon dioxide source is injected into step (14), reaction step (15), separation step (16) and as green building step (17). The invention provides a method for upgrading alkaline solid waste as a green building material, which can be modified and stabilized for various alkaline solid wastes with wide application range, avoiding the use of high temperature and high pressure steam in the traditional stabilization program, and is effective Reduce the use of energy resources; at the same time, the solid product composition after the reaction is similar to natural ore, which can be used as a green building material in construction projects, providing additional environmental and economic benefits. Wherein, the liquid phase injection step (11) and the alkaline solid waste are introduced into the step (12), and the mixing step (13) is carried out to form a mixture having a liquid-solid weight ratio of 1:1 to 50:1. The mixture is highly alkaline. Then, a carbon dioxide source injection step (14) is performed, and the carbon dioxide source can be exhausted from a chimney, a hot blast stove, a combustion furnace, and the like to carry out a reaction step (15) to reform the stabilized alkaline solid. Waste. Finally, the liquid-solid separation is carried out by the separation step (16), and the stabilized solid waste obtained can be used for resource utilization, for example, cement blending, etc., as a green building material step (17).
本發明係可於常溫、常壓下進行鹼性固體廢棄物安定化,有別於傳統加壓蒸氣養生法等,且不需額外投入化學藥劑(例如:去鹼試劑),係直接使用煙道氣中二氧化碳,作為鹼性固體廢棄物安定化之反應劑,符合綠色化學原則。鹼性固體廢棄物中高活性成分,例如:游離氧化鈣、游離氧化鎂、氫氧化鈣、氫氧化鎂等,可於液體媒介中溶出解離,轉換成鈣離子或鎂離子,再與排氣中之二氧化碳成分反應,生成安定之碳酸鹽沉澱,達到鹼性固體廢棄物改質及安定化之目的。 The invention can carry out the stabilization of the alkaline solid waste under normal temperature and normal pressure, and is different from the traditional pressurized steam health method, and does not require additional chemical injection (for example, alkali removal reagent), and directly uses the flue. Carbon dioxide in the gas, as a reactant for the stabilization of alkaline solid waste, conforms to the principle of green chemistry. Highly active ingredients in alkaline solid waste, such as free calcium oxide, free magnesium oxide, calcium hydroxide, magnesium hydroxide, etc., can be dissolved and dissociated in liquid medium, converted into calcium or magnesium ions, and then in the exhaust The carbon dioxide component reacts to form a stable carbonate precipitate to achieve the purpose of upgrading and stabilizing the alkaline solid waste.
故,本發明方法避免使用傳統安定化程序之高溫/高壓蒸氣手段,轉而直接使用相對低溫/低壓之含二氧化碳源排氣,有效改質鹼性固體廢棄物,安定化其內活性物質,反應產物並可作為綠色建材,提供環境效益,減少能資源使用成本。 Therefore, the method of the invention avoids the high temperature/high pressure steam means using the traditional stabilization program, and directly uses the relatively low temperature/low pressure carbon dioxide source exhaust gas, effectively reforms the alkaline solid waste, stabilizes the active substance therein, and reacts The product can be used as a green building material to provide environmental benefits and reduce the cost of energy resources.
11‧‧‧液相注入步驟 11‧‧‧ Liquid injection step
12‧‧‧鹼性固體廢棄物投入步驟 12‧‧‧Alkaline solid waste input steps
13‧‧‧混和步驟 13‧‧‧mixing steps
14‧‧‧二氧化碳源注入步驟 14‧‧‧ Carbon dioxide source injection step
15‧‧‧反應步驟 15‧‧‧Reaction steps
16‧‧‧分離步驟 16‧‧‧Separation steps
17‧‧‧作為綠色建材步驟 17‧‧‧ as a green building step
第1圖係本發明之流程示意圖。 Figure 1 is a schematic flow diagram of the present invention.
第2圖係本發明一實施例,就「未處理A」及「本發明處理後B」之固體廢棄物,其內所含游離氧化鈣與氫氧化鈣含量之示意圖。 Fig. 2 is a schematic view showing the contents of free calcium oxide and calcium hydroxide contained in solid wastes of "untreated A" and "process B after treatment" according to an embodiment of the present invention.
在本發明被詳細描述之前,應當注意在以下的說明內容中, 類似的元件是以相同的編號來表示。 Before the present invention is described in detail, it should be noted that in the following description, Similar elements are denoted by the same reference numerals.
本發明將就以下實施例來作進一步說明,使本發明所屬技術領域中具有通常知識者,得以實現本發明應用,以達到預期環境經濟效益。然,應瞭解的是,以下實施例僅為例示說明之用,不應被解釋為本發明實施之限制。 The invention will be further illustrated by the following examples insofar as they are of ordinary skill in the art to which the invention pertains. It is understood that the following examples are for illustrative purposes only and are not to be construed as limiting.
請參看第1圖所示,本發明關於一種使用含有二氧化碳源氣體改質鹼性固體廢棄物作為綠色建材之方法,係包括有下述步驟:液相注入步驟(11),固體廢棄物投入步驟(12),混和步驟(13),二氧化碳源注入步驟(14),反應步驟(15),分離步驟(16)及作為綠色建材步驟(17)。 Referring to FIG. 1 , the present invention relates to a method for using a carbon dioxide source-containing gas modified alkaline solid waste as a green building material, comprising the steps of: a liquid phase injection step (11), and a solid waste input step. (12), a mixing step (13), a carbon dioxide source injection step (14), a reaction step (15), a separation step (16), and a green building material step (17).
1.於該液相注入步驟(11):係通過幫浦設備,將液相媒介注入暫存槽。此類液相媒介例如但不侷限為自來水、工業製程無機廢水、濃鹽水等。此暫存槽可為但不侷限圓筒形儲槽、可曝氣式反應槽、泥漿反應槽等。 1. In the liquid phase injection step (11): the liquid medium is injected into the temporary storage tank through the pumping device. Such liquid mediums are, for example but not limited to, tap water, industrial process inorganic wastewater, concentrated brine, and the like. The temporary storage tank can be, but not limited to, a cylindrical storage tank, an aerated reaction tank, a mud reaction tank, and the like.
2.於該鹼性固體廢棄物投入步驟(12):係指透過固體輸送設備,將鹼性固體廢棄物投入暫存槽,此液相媒介與鹼性固體廢棄物調配重量比例為液固比1:1到50:1間。此類鹼性固體廢棄物例如但不侷限為鋼鐵爐碴(例如:高爐碴、轉爐碴、精煉碴、脫硫碴、電弧爐氧化碴、還原碴等)、爐灰(例如:飛灰、底灰、集塵灰等)等。 2. In the alkaline solid waste input step (12), the solid solid waste is put into a temporary storage tank through a solid conveying device, and the ratio of the liquid medium to the alkaline solid waste is liquid-solid ratio. 1:1 to 50:1. Such alkaline solid wastes are, for example but not limited to, steel furnaces (eg, blast furnace crucibles, converter crucibles, refining crucibles, desulfurization crucibles, electric arc furnaces, antimony oxides, reduction crucibles, etc.), furnace ash (eg, fly ash, bottom) Ash, dust, etc.).
3.於該混和步驟(13):係將鹼性固體廢棄物投入步驟(12)所得之液固混和物,透過攪拌設備,使固體廢棄物能與液相媒介 於暫存槽中均勻混和。 3. In the mixing step (13): the alkaline solid waste is charged into the liquid-solid mixture obtained in the step (12), and the solid waste can be mixed with the liquid medium through the stirring device. Evenly mixed in the temporary storage tank.
於該二氧化碳源注入步驟(14):係將含二氧化碳源之排氣透過鼓風機引入泥漿暫存槽中。此類含二氧化碳源之排氣為煙囪排氣,例如但不侷限熱風爐排氣、燃燒爐排氣、焚化爐排氣等。此類二氧化碳源之排氣氣體溫度可介於50℃至500℃,氣體壓力可介於1.0atm至2.0atm,且排氣中二氧化碳濃度可藉於3vol.%至50vol.%。此氣體注入設備可為但不侷限氣體分散器、曝氣設備、攪拌設備等。 In the carbon dioxide source injection step (14), the exhaust gas containing the carbon dioxide source is introduced into the slurry temporary storage tank through the air blower. Such a carbon dioxide-containing exhaust gas is a chimney exhaust, such as, but not limited to, hot air furnace exhaust, combustion furnace exhaust, incinerator exhaust, and the like. The exhaust gas temperature of such a carbon dioxide source may be between 50 ° C and 500 ° C, the gas pressure may be between 1.0 atm and 2.0 atm, and the carbon dioxide concentration in the exhaust gas may be from 3 vol. % to 50 vol. %. The gas injection device can be, but is not limited to, a gas disperser, an aeration device, a stirring device, and the like.
於該反應步驟(15):係指將二氧化碳源注入步驟(14)之含二氧化碳源排氣,與混和步驟(13)所得之該均勻液固混和物,於暫存槽中分散地接觸,進行鹼性固體廢棄物改質。 In the reaction step (15), the carbon dioxide source is injected into the carbon dioxide source exhaust gas of the step (14), and the uniform liquid solid mixture obtained in the mixing step (13) is dispersedly contacted in the temporary storage tank. Alkaline solid waste is upgraded.
於該分離步驟(16):係指將該反應步驟(15)所得之該反應後固體廢棄物泥漿進行液固分離,其中,反應後固體廢棄物應已妥善安定化,活性物質例如但不局限於游離氧化鈣、游離氧化鎂、氫氧化鈣、氫氧化鎂等已被有效去除。 In the separating step (16), the solid waste slurry obtained by the reaction step (15) is subjected to liquid-solid separation, wherein the solid waste should be properly stabilized after the reaction, and the active substance is, for example, not It is limited to free calcium oxide, free magnesium oxide, calcium hydroxide, magnesium hydroxide and the like which have been effectively removed.
作為綠色建材步驟(17):所得安定化後固體廢棄物可作為綠色建材使用,例如但不侷限為骨材、輔助性水泥膠結材料等。由於鹼性固體廢棄物中活性物質與二氧化碳反應生成碳酸物沉澱,此改質後固體廢棄物使用添加於建築材料中,不會造成日後材料體積不穩定。此類綠色建材中含有安定化後固體廢棄物之重量百分比可介於0%至50%。 As a green building material step (17): the obtained solid waste can be used as a green building material, for example, but not limited to aggregates, auxiliary cement bonding materials, and the like. Since the active substance in the alkaline solid waste reacts with carbon dioxide to form a carbonate precipitate, the modified solid waste is added to the building material without causing the material volume to be unstable in the future. The weight percentage of the solid waste contained in the green building materials may range from 0% to 50%.
請參閱第2圖,本實施例中說明未處理A與本發明「鹼 性固體廢棄物改質作為綠色建材之方法」處理B之固體廢棄物中活性物質成分比較。可發現未處理A之固體廢棄物,其內含有部分游離氧化鈣及氫氧化鈣,含量分別為11.4%與3.4%;然,經過本發明處理B後,固體廢棄物中游離氧化鈣及氫氧化鈣含量有效降低,分別降至0.1%與0.1%。由此可知,結合本發明鹼性固體廢棄物改質作為綠色建材之方法,進行固體廢棄物改質與安定化,可有效地將固體廢棄物活性物質降低,達到物化性質改良效益,有利於其後作為綠色建築材料應用。 Please refer to FIG. 2, in which the untreated A and the "alkali" of the present invention are described in the present embodiment. Comparison of the active substance composition in the solid waste treated with B as a method of green building materials. It can be found that the solid waste of untreated A contains some free calcium oxide and calcium hydroxide, and the contents are 11.4% and 3.4%, respectively; however, after treatment B of the invention, free calcium oxide and hydroxide in the solid waste The calcium content was effectively reduced to 0.1% and 0.1%, respectively. It can be seen that, in combination with the method of modifying the alkaline solid waste of the present invention as a green building material, the solid waste is reformed and stabilized, and the solid waste active material can be effectively reduced to achieve the physicochemical property improvement benefit, which is beneficial to the same. Later applied as a green building material.
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TW201016599A (en) * | 2008-06-17 | 2010-05-01 | Calera Corp | Methods and systems for utilizing waste sources of metal oxides |
CN104003637A (en) * | 2014-05-29 | 2014-08-27 | 大连理工大学 | Method of preparing building material products by carbonating municipal waste incineration ash |
TW201623630A (en) * | 2014-12-27 | 2016-07-01 | Pen-Chi Chiang | Method and system for stabilizing furnace slag having different particle sizes |
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TW201016599A (en) * | 2008-06-17 | 2010-05-01 | Calera Corp | Methods and systems for utilizing waste sources of metal oxides |
CN104003637A (en) * | 2014-05-29 | 2014-08-27 | 大连理工大学 | Method of preparing building material products by carbonating municipal waste incineration ash |
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