TW202104085A - Method for dry recovery of lime from by-products of ironmaking or steelmaking process including a preparation step, a feeding step, and a sieving step - Google Patents
Method for dry recovery of lime from by-products of ironmaking or steelmaking process including a preparation step, a feeding step, and a sieving step Download PDFInfo
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Abstract
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本發明是有關於一種乾式回收的方法,特別是指一種由還原渣、脫硫渣或其混合物中乾式回收石灰的方法。The present invention relates to a method for dry recovery, in particular to a method for dry recovery of lime from reduction slag, desulfurization slag or a mixture thereof.
一般廢鐵回收煉鋼廠主要是以電弧爐煉鋼,而煉鋼過程可依其化學反應分成熔解期、氧化期及還原期等三個階段。在還原期中,待造渣完成並將浮渣倒除後,為了與氧化物充分反應以避免鋼液內殘留過多的氧氣,因此會加入大量的石灰石及碳粉等副原料,但在反應過後往往還有不少的石灰殘留於還原渣及脫硫渣中,具有強鹼性的石灰若未經回收而與還原渣或脫硫渣一同廢棄處理,將會對環境造成衝擊及傷害,在環保意識日趨高漲的情況下,由還原渣及脫硫渣中有效回收石灰(CaO)應是勢在必行的,但可惜的是,我國目前尚未見到任何的相關處理方式,對於綠色永續發展無疑是一大重擊。此外,在回收石灰後一般還需進行安定性處理以避免膨脹率過高之問題,處理上較為不便且工序較多。Generally, steelmaking plants for scrap iron recycling mainly use electric arc furnaces to make steel, and the steelmaking process can be divided into three stages: melting, oxidation, and reduction according to its chemical reactions. In the reduction period, after the slagging is completed and the scum is poured out, in order to fully react with the oxides to avoid excessive oxygen remaining in the molten steel, a large amount of auxiliary materials such as limestone and carbon powder are added. However, after the reaction, it is often There is still a lot of lime left in the reduction slag and desulfurization slag. If the lime with strong alkalinity is discarded together with the reduction slag or desulfurization slag without being recycled, it will cause impact and damage to the environment. Under the situation of increasing growth, it is imperative to effectively recover lime (CaO) from reduction slag and desulfurization slag, but unfortunately, China has not yet seen any relevant treatment methods, which is undoubtedly for green and sustainable development. It's a big blow. In addition, after the lime is recovered, stability treatment is generally required to avoid the problem of excessive expansion rate, which is inconvenient to handle and requires more procedures.
根據篩分析,還原渣中的篩分粒徑比例大致為:較大物料佔顆粒通過重量百分比30~40%、通過48號篩(約300微米)約佔顆粒通過重量百分比40%、通過200號篩(約75微米)約佔顆粒通過重量百分比28%,其中75微米以下的成分中氧化鈣的成分高達重量百分比54%,300微米至75微米的成分中氧化鈣的成分也高達重量百分比52%,因此若能將300微米以下的顆粒與還原渣分離,將可得到總重量百分比50%以上的石灰,同樣地,脫硫渣中的篩分粒徑比例大致為:較大物料佔顆粒通過重量百分比30~40%、通過48號篩(約300微米)約佔顆粒通過重量百分比50%、通過200號篩(約75微米)約佔顆粒通過重量百分比35%,若能將300微米以下的顆粒與還原渣分離,將可得到總重量百分比55%以上的石灰。According to the sieve analysis, the proportion of the sieved particle size in the reduction slag is roughly as follows: the larger material accounts for 30-40% of the particle passing weight, the 48th sieve (about 300 microns) accounts for about 40% of the particle passing weight, and the 200th The sieve (approximately 75 microns) accounts for about 28% by weight of the particles. Among them, the content of calcium oxide in components below 75 microns is as high as 54% by weight, and the content of calcium oxide in components from 300 to 75 microns is also as high as 52% by weight. Therefore, if the particles below 300 microns can be separated from the reduction slag, more than 50% of the total weight percentage of lime can be obtained. Similarly, the proportion of the sieved particle size in the desulfurization slag is roughly: the larger material accounts for the weight of the particles. Percentage of 30-40%, passing through the No. 48 sieve (about 300 microns) accounts for about 50% by weight of the particles, passing through the No. 200 sieve (about 75 microns), accounting for about 35% by weight of the particles, if the particles below 300 microns can be removed Separating from the reduction slag, more than 55% lime by weight can be obtained.
若使用篩網進行篩濾的回收方式,則300微米以下的顆粒過小而容易在篩濾時飄散於外在環境中,導致回收效率低落並對環境造成汙染,有違當初回收石灰以防環境衝擊之初衷,而本發明不僅能克服前述篩網回收之問題,且回收效率高,能有效減少鋼鐵廠的廢棄物而大幅降低環境污染。If the screen is used for the recycling method of screening, the particles below 300 microns are too small and easily dispersed in the external environment during screening, resulting in low recovery efficiency and pollution of the environment, which is contrary to the original recycling of lime to prevent environmental impact The original intention, and the present invention can not only overcome the aforementioned screen recycling problem, but also has high recycling efficiency, which can effectively reduce the waste of steel plants and greatly reduce environmental pollution.
此外,目前常見的鋼廠(包括一貫化鋼廠或電爐煉鋼廠)在作業過程中排出爐渣時,均會利用水冷方式進行降溫,所以這些爐渣出廠時均會帶有總重量百分比10至20%的水分,也因此前述的回收方式大多採濕式處理(水蒸氣、水坑撈渣),故目前市場上尚未有乾式處理之技術。In addition, the current common steel plants (including Yiguanhua Steel Plant or Electric Furnace Steelmaking Plant) will use water cooling to cool down the slag during operation, so these slags will be shipped with a total weight percentage of 10 to 20. % Moisture, so most of the aforementioned recovery methods use wet treatment (steam, puddle slag removal), so there is no dry treatment technology currently on the market.
因此,本發明之目的,即在提供一種可有效率地乾式回收還原渣、脫硫渣或其混合物中之石灰的方法。Therefore, the object of the present invention is to provide a method for efficiently and dry recovery of lime in reduction slag, desulfurization slag or their mixture.
於是,本發明自煉鐵或煉鋼製程副產物中乾式回收石灰的方法,包含一預備步驟、一入料步驟,及一篩濾步驟。在該預備步驟中,準備一石灰回收裝置,該石灰回收裝置包含一分料單元、一連通該分料單元的篩濾單元、一用於將氣體由該分料單元及該篩濾單元內抽出的負壓單元,及一加熱單元。在該入料步驟中,開啟該負壓單元及該加熱單元,使氣流依序通過該分料單元及該篩濾單元後再向外排出,接著將選自還原渣、脫硫渣、或其混合物的待篩濾料置入該分料單元中,並透過該加熱單元加熱氣流以烘乾待篩濾料,且待篩濾料會在該分料單元中初步篩分為粒徑較大的粗料及粒徑較小的細料。在該篩濾步驟中,氣流帶動待篩濾料中的細料,並使細料通過該篩濾單元而被進一步篩濾,通過該篩濾單元的細料被收集而完成回收,所回收的細料中含有重量百分比50%以上的石灰。Therefore, the method for dry recovery of lime from the by-products of the ironmaking or steelmaking process of the present invention includes a preliminary step, a feeding step, and a sieving step. In this preliminary step, a lime recovery device is prepared. The lime recovery device includes a distributing unit, a sieving unit connected to the distributing unit, and a unit for extracting gas from the distributing unit and the sieving unit The negative pressure unit, and a heating unit. In the feeding step, the negative pressure unit and the heating unit are turned on, and the airflow is sequentially passed through the distributing unit and the screening unit and then discharged outward, and then selected from the reduction slag, desulfurization slag, or the like The material to be sieved of the mixture is placed in the material separation unit, and the airflow is heated by the heating unit to dry the material to be sieved, and the material to be sieved will be preliminarily sieved into the material with a larger particle size in the material separation unit. Coarse materials and fine materials with smaller particle size. In the sieving step, the airflow drives the fine material in the material to be sieved, and the fine material passes through the sieving unit to be further sieved. The fine material passing through the sieving unit is collected to complete the recovery, and the recovered The fine material contains more than 50% lime by weight.
本發明之功效在於:透過該負壓單元所產生的氣流可帶動待篩濾料中粒徑較小的細料進一步通過篩濾後被收集,透過該分料單元及該篩濾單元承接待篩濾料可避免其飄散至外界,並以氣流帶動300微米以下的顆粒通過該篩濾單元並被引導至外部收集,由於能將300微米以下含有大量氧化鈣的顆粒由待篩濾料中分離,因此可大幅提升回收石灰之效率,並能避免細小顆粒飄散於外在環境而造成汙染之情事。此外,該加熱單元可在待篩濾料入料過程中對其烘烤,以除去待篩濾料內含的水分,屬於市面上未見的乾式回收石灰之方法,且該加熱單元所產生的二氧化碳可與待篩濾料中的石灰反應形成碳酸鈣,可提升所回收的細料之安定度及降低膨脹率,達到穩定回收之功效。The effect of the present invention is that the airflow generated by the negative pressure unit can drive the fine material with a smaller particle size in the material to be sieved to be collected after further passing through the sieving unit, and receiving the sieve through the separating unit and the sieving unit. The filter material can prevent it from drifting to the outside, and the particles below 300 microns are driven by the airflow to pass through the filter unit and be guided to the outside for collection. Because the particles below 300 microns containing a large amount of calcium oxide can be separated from the filter material to be screened, Therefore, the efficiency of lime recovery can be greatly improved, and pollution caused by fine particles floating in the external environment can be avoided. In addition, the heating unit can bake the material to be sieved during the feeding process to remove the moisture contained in the material to be sieved, which is a method of dry recovery of lime that has not been seen in the market, and the heating unit produces Carbon dioxide can react with the lime in the material to be screened to form calcium carbonate, which can improve the stability of the recovered fine material and reduce the expansion rate to achieve the effect of stable recovery.
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 numbers.
參閱圖1與圖2,本發明自煉鐵或煉鋼製程副產物中乾式回收石灰的方法之一第一實施例,包含一預備步驟、一入料步驟,及一篩濾步驟。在該準備步驟中,準備一石灰回收裝置1。該石灰回收裝置1包含一分料單元2、一連接該分料單元2的篩濾單元3、一連通該篩濾單元3的負壓單元4,及一加熱單元5。該分料單元2包括一界定出一內部空間210的外壁21、一設置於該內部空間210內的篩分機構22,及一破碎機23。該外壁21形成一連通該內部空間210頂部且朝向上方的入料口211、一位於該入料口211下方且側向(即水平方向)開設並連通該內部空間210的連通口212、一位於該連通口212下方且連通該內部空間210底部的收集口213,及一位於該入料口211下方及該收集口213上方且側向開設的入風口214。在本第一實施例中,該入風口214是由上而下傾斜延伸以連接該內部空間210。該篩分機構22沿上下方向位於該入料口211及該收集口213之間,並具有複數沿上下方向彼此相間隔地固定於該外壁21內表面的承板221。每一承板221是傾斜延伸,其中較高的一端朝該入料口211延伸,較低的一端朝該連通口212延伸。該破碎機23可為顎碎機、離心破碎機,或輥壓破碎機。1 and 2, a first embodiment of the method for dry recovery of lime from the by-products of the ironmaking or steelmaking process of the present invention includes a preliminary step, a feeding step, and a filtering step. In this preparation step, a
該篩濾單元3包括一界定出一過濾空間310的外殼體31,及一設置於該外殼體31之過濾空間310內的濾材32。該外殼體31形成一側向開設而連通該過濾空間310及該分料單元2之連通口212的接口311,及一位於該接口311下方而連通該過濾空間310底部的出料口312。該濾材32具有複數固定於該外殼體31內表面且位於該出料口312上方的濾袋321,需要特別說明的是,除了該等濾袋321外,該濾材32也可以是多層濾網或其他過濾元件,不以此為限。該負壓單元4包括一連通該出料口312而可將空氣由該出料口312抽出,且可調控風力的抽風機41。該加熱單元5包括一設置於該入風口214內而位於該等承板221相對上方的燃燒加熱器51,該燃燒加熱器51也可視實際需求而使配置數量為多個,不以此為限。The
在該入料步驟中,開啟該抽風機41及該燃燒加熱器51,使空氣由該內部空間210及該過濾空間310中抽出,形成從該入風口214進入,並通過該連通口212及該接口311,最後通過該等濾袋321並由該出料口312排出的氣流,而該燃燒加熱器51則對由該入風口214進入的氣流加熱。由還原渣、脫硫渣或兩者混合物5形成的待篩濾料6會從該入料口211送入該內部空間210,向下掉落的待篩濾料6會先撞擊最上層的承板221,含有不同粒徑及重量之成分的待篩濾料6,此時會如圖2所示地先初步篩分成因粒徑較大(重量較重)而沿該承板221向下滑落的粗料61,及因粒徑較小(重量較輕)而揚起且飄散的細料62,向下滑落的粗料61會向下掉落至該收集口213中而被收集,有的則會再次撞擊位於下方的承板221,從而再次進行篩分,而多個承板221的設置可確保待篩濾料6掉下時能擊中該等承板221。此外,一般還原渣中含有總重量百分比0~5%的水分,脫硫渣中則含有總重量百分比10%~12%的水分,在上述過程中可透過該燃燒加熱器51加熱氣流以對待篩濾料6進行加熱烘乾,進而脫去待篩濾料6中的水分,該燃燒加熱器51可視待篩濾料6的含水情形開關, 當偵測到待篩濾料6的含水量足夠低時,也可關閉該燃燒加熱器51以節省能源。需要另外說明的是,該收集口213所收集的粗料61除了因粒徑較大而落下外,有時是因含水量高而使得重量較重所致,因此可以將該收集口213中的粗料61先通過該破碎機23進行破碎後,再次送入該入料口211,如此可重新對粗料61進行烘乾脫水,使因含水量較高而導致重量較重的粗料61,在循環脫水烘乾後成為細料62,提升回收率。In the feeding step, the
在該篩濾步驟中,由於前述被篩分出的細料62重量較輕,故會被該抽風機41所引導的氣流帶動而通過該連通口212及該接口311,並進入該過濾空間310中。進入該過濾空間310中的細料62續行被氣流帶動,接著會通過該等濾袋321而被進一步篩濾,細料62中粒徑較大的顆粒會被留在該等濾袋321內,而粒徑較小的顆粒會通過篩濾並被氣流引導至底部的出料口312而被回收,所被回收的顆粒之粒徑多在300微米以下,為煉鐵或煉鋼製程副產物中回收之高石灰質材料,含有極高成分的氧化鈣,從而可達成回收重量百分比55%以上的石灰(CaO)之功效,回收效率高,且可避免因粉塵逸散至外界環境而造成汙染之情事。此外,該燃燒加熱器51不僅可脫去待篩濾料6中的水分,從而獲得含有乾式石灰的高石灰質材料,且在該燃燒加熱器51的燃燒加熱過程中,所排出的二氧化碳可與待篩濾料6中的石灰反應而形成碳酸鈣,提升高石灰質材料的安定性並降低膨脹率,減少後續加工的工序及時間。In the sieving step, since the weight of the
需要特別說明的是,透過本第一實施例而回收的顆粒,由於其氧化鈣和氧化鎂含量加總超過重量百分比60%,因此相當適合作為燒結配料及造渣劑,同時由於氧化鈣的含量超過重量百分比50%而可符合水泥生料之要求,因此可取代開山開礦的石灰石粉,如此還能省去生料粉磨造成的電力耗損,屬於十分環保的綠色材料。此外,由於所回收之顆粒的高鹼性特質,因此也可用於中和廢水中的酸性而取代消石灰,或提供鹼度供波蜀蘭材料反應而作為固化劑之配料,應用層面十分廣泛且有助於降低對生態之衝擊。It should be particularly noted that the particles recovered through the first embodiment, because the total content of calcium oxide and magnesium oxide exceeds 60% by weight, they are quite suitable as sintering ingredients and slagging agents. At the same time, due to the content of calcium oxide It is more than 50% by weight and can meet the requirements of cement raw material. Therefore, it can replace the limestone powder from Kaishan mining. This can also save the power consumption caused by raw meal grinding. It is a very environmentally friendly green material. In addition, due to the high alkalinity of the recovered particles, it can also be used to neutralize the acidity in wastewater instead of slaked lime, or to provide alkalinity for the reaction of boszulan materials as a solidifying agent ingredient. The application level is very wide and has a wide range of applications. Help reduce the impact on the ecology.
參閱圖3及圖4,為本發明自煉鐵或煉鋼製程副產物中乾式回收石灰的方法之一第二實施例,本第二實施例大致上是與該第一實施例相同,不同之處在於:在該預備步驟中,該分料單元2之篩分機構22具有一沿上下方向位於該入料口211及該收集口213之間,且對應該連通口212設置於該內部空間210中的離心機222。該離心機222具有複數呈環狀排列且轉軸平行上下方向的扇葉223。而該入風口214是由下而上地傾斜延伸以連接該內部空間210。Referring to Figures 3 and 4, there is a second embodiment of the method for dry recovery of lime from the by-products of the self-ironmaking or steelmaking process of the present invention. The second embodiment is substantially the same as the first embodiment, with the difference The point is: in the preliminary step, the
在該入料步驟中,當待篩濾料6落下時,會如圖4所示地受到該等扇葉223的撞擊或被周遭的風力吹散,如此便可將待篩濾料6篩分成因重量而向下落至該收集口213的粗料61,及飄散揚起的細料62,而該收集口213中的粗料61同樣會經該破碎機23破碎後再次送入該入料口211中,故本第二實施例透過離心式分離進行初步篩分,不同於該第一實施例的重力式分離,提供了另一種供使用者選擇的篩分方式,提高泛用性及選擇性。該篩分機構22也可具有多個沿上下方向間隔設置的離心機222,以對落下的粗料61進一步地進行篩分,提高回收率。此外,該燃燒加熱器51所加熱的氣流也會被該等風扇223捲起,而對待篩濾料6進行烘乾加熱。In the feeding step, when the
綜上所述,本發明透過該篩分機構22可初步將還原渣、脫硫渣或其混合物篩分為細料62及粗料61,透過該抽風機41所引導的氣流,可帶動細料62通過該等濾袋321以續行過濾,透過該燃燒加熱器51的烘乾脫水,可進一步除去待篩濾料6及粗料61中的水分,從而濾得粒徑在300微米以下的高石灰質材料,有效提高所回收石灰的含量,並能避免粒徑較小的顆粒飄散於外境環境中,降低對環境的汙染及衝擊,以有效減少鋼鐵廠的廢棄物,本發明屬於市面上未見的乾式石灰回收方法,且透過不斷的循環對物料重複進行烘乾及落下篩分,可達到最高的回收率,故確實能達成本發明之目的。To sum up, the present invention can preliminarily screen the reduced slag, desulfurization slag or their mixture into
惟以上所述者,僅為本發明之實施例而已,當不能以此限定本發明實施之範圍,凡是依本發明申請專利範圍及專利說明書內容所作之簡單的等效變化與修飾,皆仍屬本發明專利涵蓋之範圍內。However, the above are only examples of the present invention. When the scope of implementation of the present invention cannot be limited by this, all simple equivalent changes and modifications made in accordance with the scope of the patent application of the present invention and the content of the patent specification still belong to This invention patent covers the scope.
1:石灰回收裝置 2:分料單元 21:外壁 210:內部空間 211:入料口 212:連通口 213:收集口 214:入風口 22:篩分機構 221:承板 222:離心機 223:扇葉 23:破碎機 3:篩濾單元 31:外殼體 310:過濾空間 311:接口 312:出料口 32:濾材 321:濾袋 4:負壓單元 41:抽風機 5:加熱單元 51:燃燒加熱器 6:還原渣 61:粗料 62:細料1: Lime recovery device 2: Distribution unit 21: Outer Wall 210: internal space 211: Inlet 212: Connecting port 213: Collection Port 214: air inlet 22: Screening mechanism 221: Shelf 222: Centrifuge 223: Fan Blade 23: Crusher 3: Screening unit 31: Outer shell 310: filter space 311: Interface 312: Outlet 32: filter material 321: filter bag 4: Negative pressure unit 41: Exhaust fan 5: Heating unit 51: Combustion heater 6: Reduction slag 61: Coarse material 62: fine material
本發明之其它的特徵及功效,將於參照圖式的實施方式中清楚地呈現,其中: 圖1是一示意圖,說明本發明自煉鐵或煉鋼製程副產物中乾式回收石灰的方法之一第一實施例; 圖2是一不完整的示意圖,說明該第一實施例中,一篩分機構進行分料之情形; 圖3是一示意圖,說明本發明自煉鐵或煉鋼製程副產物中乾式回收石灰的方法之一第二實施例;及 圖4是一不完整的示意圖,說明該第二實施例中,該篩分機構進行分料之情形。Other features and effects of the present invention will be clearly presented in the embodiments with reference to the drawings, in which: Figure 1 is a schematic diagram illustrating a first embodiment of the method for dry recovery of lime from the by-products of the self-ironmaking or steelmaking process of the present invention; Figure 2 is an incomplete schematic diagram illustrating the situation in which a screening mechanism performs material distribution in the first embodiment; 3 is a schematic diagram illustrating a second embodiment of the method for dry recovery of lime from the by-products of the self-ironmaking or steelmaking process of the present invention; and Figure 4 is an incomplete schematic diagram illustrating how the screening mechanism performs material separation in the second embodiment.
1:石灰回收裝置 1: Lime recovery device
2:分料單元 2: Distribution unit
21:外壁 21: Outer Wall
210:內部空間 210: internal space
211:入料口 211: Inlet
212:連通口 212: Connecting port
213:收集口 213: Collection Port
214:入風口 214: air inlet
22:篩分機構 22: Screening mechanism
221:承板 221: Shelf
23:破碎機 23: Crusher
3:篩濾單元 3: Screening unit
31:外殼體 31: Outer shell
310:過濾空間 310: filter space
311:接口 311: Interface
312:出料口 312: Outlet
32:濾材 32: filter material
321:濾袋 321: filter bag
4:負壓單元 4: Negative pressure unit
41:抽風機 41: Exhaust fan
5:加熱單元 5: Heating unit
51:燃燒加熱器 51: Combustion heater
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