TWI638895B - Method for suppressing slag foaming - Google Patents
Method for suppressing slag foaming Download PDFInfo
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- TWI638895B TWI638895B TW106104165A TW106104165A TWI638895B TW I638895 B TWI638895 B TW I638895B TW 106104165 A TW106104165 A TW 106104165A TW 106104165 A TW106104165 A TW 106104165A TW I638895 B TWI638895 B TW I638895B
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- slag
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- pulverized
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- 239000002893 slag Substances 0.000 title claims abstract description 318
- 238000005187 foaming Methods 0.000 title claims abstract description 41
- 238000000034 method Methods 0.000 title claims abstract description 23
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims abstract description 49
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 46
- 229910052742 iron Inorganic materials 0.000 claims abstract description 24
- 239000002245 particle Substances 0.000 claims abstract description 13
- 230000002401 inhibitory effect Effects 0.000 claims 1
- 101100298225 Caenorhabditis elegans pot-2 gene Proteins 0.000 description 25
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 14
- 230000000694 effects Effects 0.000 description 11
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 7
- 238000001816 cooling Methods 0.000 description 6
- 238000007599 discharging Methods 0.000 description 6
- 239000007790 solid phase Substances 0.000 description 5
- 238000005261 decarburization Methods 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 238000009834 vaporization Methods 0.000 description 4
- 230000008016 vaporization Effects 0.000 description 4
- 229910004298 SiO 2 Inorganic materials 0.000 description 3
- 238000007664 blowing Methods 0.000 description 3
- 239000006260 foam Substances 0.000 description 3
- 239000002344 surface layer Substances 0.000 description 3
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 2
- 229910000831 Steel Inorganic materials 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 238000007667 floating Methods 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 238000010298 pulverizing process Methods 0.000 description 2
- 238000007670 refining Methods 0.000 description 2
- 229920006395 saturated elastomer Polymers 0.000 description 2
- 239000010959 steel Substances 0.000 description 2
- 238000005303 weighing Methods 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000009749 continuous casting Methods 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000000155 melt Substances 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000012071 phase Substances 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 230000002035 prolonged effect Effects 0.000 description 1
- 238000002791 soaking Methods 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 238000009628 steelmaking Methods 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000008400 supply water Substances 0.000 description 1
- 230000001629 suppression Effects 0.000 description 1
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- Carbon Steel Or Casting Steel Manufacturing (AREA)
- Curing Cements, Concrete, And Artificial Stone (AREA)
Abstract
本發明之抑制爐渣起泡的方法係於利用轉爐進行熔鐵處理後,自前述轉爐將熔融爐渣以每1分鐘3噸以上之速度往排渣鍋排出,並於前述排出開始後至排渣結束時間點之後為止,從前述排渣鍋之上方朝自前述轉爐排出之熔融爐渣到達前述排渣鍋內之位置附近,持續投入每1分鐘50.0kg~200kg之水及每1分鐘50.0kg~200kg之粒徑5.0mm~30mm之粉碎爐渣。The method for suppressing slag foaming according to the present invention is that after the molten iron treatment is performed by a converter, the molten slag is discharged from the converter at a speed of 3 tons or more per minute to the slag discharge pot, and after the discharge starts, the slag discharge ends. After the time point, the molten slag discharged from the above-mentioned converter from the top of the slag pot reaches the position in the slag pot, and continuously inputs 50.0 kg to 200 kg of water per minute and 50.0 kg to 200 kg per minute. A pulverized slag having a particle diameter of 5.0 mm to 30 mm.
Description
發明領域 本發明尤其有關於一種抑制在熔鐵處理後排出至排渣鍋之爐渣於排渣鍋內起泡(發泡)的方法。FIELD OF THE INVENTION The present invention relates in particular to a method of suppressing foaming (foaming) of a slag discharged to a slag pot after the molten iron treatment in a slag pot.
發明背景 近年來,於精煉熔鐵來製造熔鋼時,執行如下方法(多功能轉爐法),即,利用轉爐進行熔鐵脫磷處理後,將轉爐內所生成之一部分爐渣排出至設置於轉爐之下方之排渣鍋,繼而進行脫碳處理(參照專利文獻1)。於該方法中,於轉爐內將爐渣成分之CaO/SiO 2質量比(以下,稱為鹼度)調整為0.8~1.5,提高爐渣之黏性而使得容易產生爐渣劇烈發泡之現象(以下起泡),藉此,使爐渣之排出性良好。 BACKGROUND OF THE INVENTION In recent years, when refining molten iron to produce molten steel, the following method (multi-functional converter method) is performed, that is, after the molten iron dephosphorization treatment is performed by a converter, a part of the slag generated in the converter is discharged to the converter. The slag pot below it is subjected to decarburization treatment (see Patent Document 1). In this method, the mass ratio of CaO/SiO 2 of the slag component (hereinafter referred to as alkalinity) is adjusted to 0.8 to 1.5 in the converter, thereby improving the viscosity of the slag and causing the slag to be foamed violently (from below) Soaking), whereby the slag discharge property is good.
如此,於制鋼步驟中,有如下情形,即,爐渣中之FeO(氧化鐵)與鐵水中之C於界面發生反應或者爐渣中之FeO與爐渣內部包含之粒鐵中之C發生反應而大量地產生微細之CO氣泡、並發生起泡。Thus, in the steel making step, there is a case where FeO (iron oxide) in the slag reacts with C in the molten iron at the interface or FeO in the slag reacts with C in the granulated iron contained in the slag. Fine CO bubbles are generated and foaming occurs.
例如,於自轉爐將爐渣排出至排渣鍋時,藉由爐渣降落之能量而使爐渣與爐渣中之粒鐵劇烈地產生攪拌及混合,爐渣中之FeO與粒鐵中之C急遽反應而大量地產生微細之CO氣泡。其結果,剛排出至排渣鍋後爐渣容易迅速地起泡。又,即便暫時使起泡沉靜,亦容易因相繼排出之爐渣而繼續起泡。For example, when the slag is discharged from the converter to the slag pot, the slag and the granulated iron in the slag are vigorously stirred and mixed by the energy of the slag falling, and the FeO in the slag reacts with the C in the granulated iron rapidly. Produces fine CO bubbles. As a result, the slag is easily foamed immediately after being discharged to the slag pot. Further, even if the foaming is temporarily silenced, it is easy to continue foaming due to the slag discharged successively.
因此,為了防止爐渣自排渣鍋橫溢並且將此種爐渣於短時間內自轉爐大量地排出至排渣鍋內,而必須抑制排渣鍋中之起泡或者使排渣鍋中之起泡迅速沉靜。為此,抑制起泡或者使起泡迅速沉靜且使該沉靜狀態持續的技術不可或缺。Therefore, in order to prevent the slag from overflowing from the slag pot and discharging the slag into the slag pot in a short time, it is necessary to suppress foaming in the slag pot or to cause blistering in the slag pot quickly. Quiet. For this reason, a technique for suppressing foaming or allowing the foam to be quickly calmed and the static state to continue is indispensable.
再者,於排渣鍋內之起泡抑制效果不足之情形時,為了避免爐渣自排渣鍋橫溢,而必須降低排渣速度或者削減排渣量。於該情形時,會引起如下問題:轉爐之週期時間延長而導致生產性降低,或者排渣後之脫碳處理中之複磷增大,或者產生浮溢。Further, in the case where the foaming suppressing effect in the slag pot is insufficient, in order to prevent the slag from overflowing from the slag pot, it is necessary to reduce the slag discharge speed or reduce the slag discharge amount. In this case, there is a problem that the cycle time of the converter is prolonged to cause a decrease in productivity, or the rephosphorization in the decarburization treatment after slag removal is increased, or a floating overflow occurs.
再者,可藉由在排渣後之脫碳吹煉中增加CaO使用量而抑制上述複磷及浮溢。然而,於該情形時,CaO濃度較高之爐渣之生成量增加,不僅就精煉成本之觀點而言不佳,而且就爐渣處理之觀點而言亦不佳。Further, the above-mentioned multiple phosphorus and floating can be suppressed by increasing the amount of CaO used in the decarburization blowing after slag discharge. However, in this case, the amount of slag generated with a high CaO concentration is increased, which is not only poor from the viewpoint of refining cost, but also poor from the viewpoint of slag treatment.
另一方面,已知碳粉作為起泡沉靜材而有效。例如於專利文獻2中,揭示有以5~100kg/分之速度對起泡之爐渣吹送碳粉之沉靜方法。碳由於不易與爐渣潤濕,故而若將碳粉吹入至起泡之爐渣中,則經由碳粉促進微細之CO氣泡彼此之合體及上浮分離,因此,使起泡沉靜。On the other hand, carbon powder is known to be effective as a foaming and sinking material. For example, Patent Document 2 discloses a method of cooling a foamed slag at a speed of 5 to 100 kg/min. Since carbon is hard to be wetted by the slag, if the carbon powder is blown into the foamed slag, the fine CO bubbles are promoted to each other and floated and separated by the carbon powder, so that the foaming is calmed.
又,於專利文獻3中,作為抑制排渣鍋(爐渣鍋)內之爐渣起泡之方法,揭示有一對排渣鍋內之爐渣表面噴灑噴霧狀之水之方法。藉由將排渣鍋內之爐渣表層部冷卻並固化,而可抑制起泡。Further, in Patent Document 3, as a method of suppressing slag foaming in a slag pot (slag pot), a method of spraying a spray-like water on the surface of a slag in a slag pot is disclosed. Foaming can be suppressed by cooling and solidifying the surface layer portion of the slag in the slag pot.
為了於排渣鍋內使起泡沉靜,而如專利文獻2所記載之方法般朝爐渣表面吹送碳粉之情形時,由於碳粉比重較小,且體積亦較小,故而碳粉難以侵入至爐渣內部。其結果,碳粉之效果僅體現於爐渣表面側,於劇烈起泡之狀況下幾乎無效果。又,有如下問題,即,為了將碳粉吹入至爐渣中,而必須於排渣鍋附近設置吹入用噴槍之升降裝置等複雜且高價之設備。In order to calm the foaming in the slag pot, and to blow the toner toward the surface of the slag as in the method described in Patent Document 2, since the carbon powder has a small specific gravity and a small volume, it is difficult for the carbon powder to intrude. Inside the slag. As a result, the effect of the toner is only reflected on the surface side of the slag, and there is almost no effect in the case of severe foaming. Further, in order to blow the carbon powder into the slag, it is necessary to provide a complicated and expensive equipment such as a lifting device for blowing the lance in the vicinity of the slag pot.
又,亦考慮欲如專利文獻3所記載之方法般對排渣鍋內之爐渣表面噴灑噴霧狀之水而將排渣鍋內之爐渣表面冷卻及固化而抑制起泡。然而,於自轉爐相繼排出爐渣之狀況下,藉由爐渣降落流而劇烈地產生攪拌混合,而使爐渣表面持續更新,因此,難以抑制起泡。 [先前技術文獻 ] [專利文獻 ] Further, in order to spray the water on the surface of the slag in the slag pot, the surface of the slag in the slag pot is cooled and solidified to suppress foaming, as in the method described in Patent Document 3. However, in the case where the slag is successively discharged from the converter, stirring and mixing are vigorously generated by the slag falling flow, and the surface of the slag is continuously renewed, so that it is difficult to suppress foaming. [ Prior Technical Literature ] [ Patent Literature ]
[專利文獻1 ]日本專利第2582692號公報 [專利文獻2 ]日本專利特開平4-180507號公報 [專利文獻3]日本專利特開平8-325619號公報 [Patent Document 1] Japanese Patent Publication No. 2582692 [Patent Document 2] Japanese Laid-Open Patent Publication No. 4-180507 [Patent Document 3] Japanese Laid-Open Patent Publication No. 8-325619
發明概要 發明欲解決之課題 鑒於前述問題點,本發明之目的在於提供一種抑制爐渣起泡的方法,該方法可於自轉爐往排渣鍋排出爐渣時在不延長爐渣排出時間之下效率良好地抑制起泡。 用以解決課題之手段SUMMARY OF THE INVENTION Problems to be Solved by the Invention In view of the foregoing problems, an object of the present invention is to provide a method for suppressing slag foaming, which can efficiently and efficiently discharge slag from a converter to a slag pot without extending the slag discharge time. Suppresses foaming. Means to solve the problem
本發明人反覆進行鑽研,結果有如下見解,藉由利用簡單之設備將低價且容易獲得之水與粉碎爐渣作為起泡抑制材投入至排渣鍋即能解決上述課題,從而完成了本發明。本發明如以下所列示。 (1)一種抑制爐渣起泡的方法,其特徵在於:利用轉爐進行熔鐵處理後,自前述轉爐將熔融爐渣以每1分鐘3噸以上之速度排出至排渣鍋,並於前述排出開始後至排渣結束時間點之後為止,從前述排渣鍋之上方朝自前述轉爐排出之熔融爐渣到達前述排渣鍋內之位置附近,持續投入每1分鐘50.0kg~200kg之水及每1分鐘50.0kg~200kg之粒徑5.0mm~30mm之粉碎爐渣。 (2)如(1)之抑制爐渣起泡的方法,其中前述粉碎爐渣為選自於由脫矽爐渣、熔鐵脫磷爐渣、轉爐爐渣及澆桶爐渣所構成群組中之1種以上。 [發明之效果]As a result of the inventors' research, the inventors have found out that the above problem can be solved by using a simple apparatus to put low-cost and easily available water and pulverized slag as a foaming suppressing material into a slag discharging pot, thereby completing the present invention. . The invention is as set forth below. (1) A method for suppressing slag foaming, characterized in that after the molten iron treatment by a converter, the molten slag is discharged from the converter to a slag pot at a rate of more than 3 tons per minute, and after the start of the discharge Until the end of the slag discharge time, the molten slag discharged from the above-mentioned slag pot reaches the vicinity of the slag pot in the vicinity of the slag pot, and continuously inputs 50.0 kg to 200 kg of water per minute and 50.0 per minute. A crushing slag having a particle diameter of 5.0 mm to 30 mm of kg to 200 kg. (2) The method of suppressing slag foaming according to (1), wherein the pulverized slag is one or more selected from the group consisting of a slag slag, a molten iron dephosphorization slag, a converter slag, and a slag. [Effects of the Invention]
根據本發明,可於自轉爐往排渣鍋排出爐渣時在不延長爐渣排出時間之下效率良好地抑制起泡。According to the present invention, it is possible to efficiently suppress foaming without discharging the slag discharge time when the slag is discharged from the rotary kiln to the slag discharge pot.
以下,參照附圖對本發明具體化後之實施形態進行說明。 圖1係用於說明抑制排渣鍋2內之爐渣起泡之方法的圖。 圖1所示之例表示於多功能轉爐法中自轉爐1將熔融爐渣排出至排渣鍋2之例。首先,於進行脫磷處理後,於使熔鐵保留於轉爐1內之狀態下使轉爐1傾轉,並從轉爐1之爐口3朝設置於轉爐1下方之排渣鍋2排出例如12t~14t之熔融爐渣。此時,自剛開始排渣後至排渣結束時間點之後為止,從設置於排渣鍋2上方之配管4投入水,並且從設置於排渣鍋2上方之未圖示之滑槽投入已粉碎之粉碎爐渣。此時,朝自轉爐1排出之熔融爐渣流到達排渣鍋2內之位置附近投入水及粉碎爐渣。再者,熔融爐渣流到達排渣鍋2內之位置係指熔融爐渣流到達排渣鍋2內之熔融爐渣之表面之位置,水及粉碎爐渣必須投入至該到達位置附近之熔融爐渣表面劇烈流動之範圍內。上述範圍內係指由與熔融爐渣流到達之位置上之爐渣流外周相距1m之一圈所包圍的區域。藉此,抑制排渣鍋2內之熔融爐渣之起泡。於後述之實驗中,該熔融爐渣之排出時間設為約3分鐘。再者,排渣中之熔融爐渣之質量可利用安裝於設置排渣鍋2之移動台車之稱量機進行測定,但亦可根據操作條件與實績而推斷熔融爐渣之質量。其中,減去自上述滑槽投入之粉碎爐渣之質量而計算。Hereinafter, embodiments of the present invention will be described with reference to the accompanying drawings. Fig. 1 is a view for explaining a method of suppressing slag foaming in the slag pot 2. The example shown in Fig. 1 shows an example in which the molten slag is discharged from the converter 1 to the slag pot 2 in the multi-function converter method. First, after performing the dephosphorization treatment, the converter 1 is tilted while leaving the molten iron in the converter 1, and discharged from the furnace opening 3 of the converter 1 to the slag pot 2 disposed below the converter 1, for example, 12t~ 14t molten slag. At this time, from the beginning of the slag discharge to the time after the slag discharge end time, the water is supplied from the pipe 4 provided above the slag discharge pot 2, and is discharged from the chute (not shown) provided above the slag discharge pot 2. Crushed slag. At this time, the molten slag flow discharged from the converter 1 reaches the position in the slag pot 2, and water and pulverized slag are introduced. Further, the position where the molten slag flow reaches the slag discharge pot 2 means that the molten slag flow reaches the surface of the molten slag in the slag discharge pot 2, and the water and the pulverized slag must be thrown to the surface of the molten slag near the arrival position to flow vigorously. Within the scope. The above range refers to a region surrounded by one of the circumferences of the slag flow at the position where the molten slag flow reaches. Thereby, the foaming of the molten slag in the slag pot 2 is suppressed. In the experiment described later, the discharge time of the molten slag was set to about 3 minutes. Further, the quality of the molten slag in the slag discharge can be measured by a weighing machine attached to a moving trolley provided with the slag pot 2, but the quality of the molten slag can be estimated based on the operating conditions and actual performance. Among them, the mass of the pulverized slag from the above-mentioned chute is subtracted and calculated.
再者,宜預先將粉碎爐渣沾上水,進而較佳為預先使粉碎爐渣含水。其原因在於,上述做法更確實地使水與粉碎爐渣混入至起泡爐渣中。又,於配管4之直徑相對較大之情形時,亦可自配管4一起投入水與粉碎爐渣。於圖1所示之例中,表示自配管4一起投入水與粉碎爐渣之例。於該情形時,配管4之直徑只要為粉碎爐渣於配管內不堵塞之程度之大小即可。Further, it is preferred that the pulverized slag is contaminated with water in advance, and it is preferred that the pulverized slag is contained in water beforehand. The reason for this is that the above method more reliably mixes water and pulverized slag into the foaming slag. Further, when the diameter of the pipe 4 is relatively large, water and pulverized slag may be supplied together from the pipe 4. In the example shown in Fig. 1, an example in which water and pulverized slag are introduced from the pipe 4 is shown. In this case, the diameter of the pipe 4 may be such a degree that the pulverized slag does not clog in the pipe.
其次,對如下機制進行詳細敍述:從開始自轉爐1往排渣鍋2排出熔融爐渣後至排渣結束時間點之後為止,朝熔融爐渣到達排渣鍋2內之位置附近投入水及粉碎爐渣,藉此可抑制排渣鍋2內之熔融爐渣之起泡。Next, the following mechanism will be described in detail: from the start of the converter 1 to the slag pot 2, after discharging the molten slag to the point after the end of the slag discharge, the water is poured into the slag pot 2 and the slag is poured into the slag pot 2, Thereby, foaming of the molten slag in the slag pot 2 can be suppressed.
自轉爐1排出至排渣鍋2之熔融爐渣係例如CaO/SiO 2質量比(鹼度)為0.8~2.0,FeO濃度為10質量%~40質量%。於排渣初期,熔融爐渣撞擊於排渣鍋2之底部,因此,熔融爐渣強烈地得以攪拌而熔融爐渣內部之微細之CO氣泡合體並上浮分離。又,所排出之熔融爐渣藉由與排渣鍋2之底部接觸而急遽冷卻,因此,熔融爐渣之固相率上升。由於在如此般熔融爐渣之固相率上升之狀態下自排渣鍋2之上方投入水及粉碎爐渣,故而自轉爐1排出之熔融爐渣藉由水分之氣化而進一步急遽冷卻,熔融爐渣之固相率進一步增加,而更顯著地抑制起泡。 The molten slag discharged from the converter 1 to the slag pot 2 has a mass ratio (basicity) of, for example, CaO/SiO 2 of 0.8 to 2.0, and a FeO concentration of 10% by mass to 40% by mass. At the initial stage of slag discharge, the molten slag impinges on the bottom of the slag pot 2, so that the molten slag is strongly stirred to melt the fine CO bubbles inside the slag and float up and separate. Further, the discharged molten slag is rapidly cooled by being brought into contact with the bottom of the slag pot 2, so that the solid phase ratio of the molten slag is increased. When the solid phase ratio of the molten slag is increased, water is poured from the slag pot 2 and the slag is pulverized. Therefore, the molten slag discharged from the converter 1 is further cooled by the vaporization of moisture, and the molten slag is solidified. The phase rate is further increased, and foaming is more significantly suppressed.
再者,排渣鍋2之底側及熔融爐渣之表層之固相率上升而令起泡暫時得到抑制,但若排渣鍋2內之熔融爐渣與自轉爐1相繼排出之熔融爐渣接觸而再次熔融,則開始起泡。對此,與水一起投入之粉碎爐渣將排渣鍋2中之熔融爐渣之已固化之表層部破壞,因此,水進入至排渣鍋2中之熔融爐渣之內部並冷卻,從而可進一步抑制起泡。Further, the solid phase ratio of the bottom side of the slag pot 2 and the surface layer of the molten slag is increased to temporarily suppress the foaming, but if the molten slag in the slag pot 2 is in contact with the molten slag successively discharged from the converter 1, When it melts, it starts to foam. On the other hand, the pulverized slag which is put together with the water destroys the solidified surface layer portion of the molten slag in the slag pot 2, so that the water enters the inside of the molten slag in the slag pot 2 and is cooled, thereby further suppressing bubble.
其後,於排渣鍋2內產生爐渣堆,而熔融爐渣則自轉爐1相繼排向該爐渣堆。然後,朝自轉爐1排出之熔融爐渣到達排渣鍋2內之位置附近繼續投入水及粉碎爐渣,水及粉碎爐渣混入至熔融爐渣中,而發揮與排渣初期相同之效果。藉由如此般自排渣初期繼續地持續投入水及粉碎爐渣,而使水及粉碎爐渣混入至熔融爐渣中,將自轉爐1排出之熔融爐渣依次冷卻而使熔融爐渣之固相率上升,藉此,可抑制排渣鍋2內之爐渣堆之起泡。為了確實地享有該效果,必須持續投入水及粉碎爐渣至少直至排渣結束時間點為止,為了更確實地享受該效果,宜於排渣結束時間點之後亦繼續投入水及粉碎爐渣。該排渣結束時間點之後之投入繼續時間若過長,則於時間方面且成本方面不佳,而且,亦無須將熔融爐渣完全凝固,因此,20秒鐘以內較為適宜。Thereafter, a slag heap is produced in the slag pot 2, and the molten slag is successively discharged from the converter 1 to the slag pile. Then, the molten slag discharged from the converter 1 reaches the vicinity of the position in the slag pot 2, and the water and the pulverized slag are continuously supplied, and the water and the pulverized slag are mixed into the molten slag to exhibit the same effect as the initial stage of slag discharge. By continuously pouring water and pulverizing the slag in the initial stage of self-slagging, the water and the pulverized slag are mixed into the molten slag, and the molten slag discharged from the converter 1 is sequentially cooled to increase the solid phase ratio of the molten slag. Thereby, the foaming of the slag pile in the slag pot 2 can be suppressed. In order to surely enjoy this effect, it is necessary to continuously supply water and pulverize the slag at least until the end of the slag discharge. In order to more reliably enjoy the effect, it is preferable to continue to input water and pulverize the slag after the slag discharge end time. If the input continuation time after the slag discharge time point is too long, the cost is not good in terms of time and cost, and the molten slag does not need to be completely solidified. Therefore, it is preferably within 20 seconds.
此處,若僅投入水,則能夠侵入至熔融爐渣中之範圍有限,起泡抑制效果亦有限。於不投入粉碎爐渣之情形時,於水氣化時使周圍之熔融爐渣急遽冷卻而形成凝固殼,藉由氣化而生成之大部分水蒸氣朝上方吹出。由此,熔融爐渣之冷卻範圍變窄。對此,若將粉碎爐渣與水一起投入,則粉碎爐渣物理性地將藉由水之氣化而產生之爐渣之凝固殼破壞,因此,粉碎爐渣與水可自凝固殼被破壞之部分侵入至熔融爐渣中,可於更大之範圍將熔融爐渣冷卻而使固相率上升而效率良好地抑制起泡。Here, when only water is supplied, the range in which it can infiltrate into the molten slag is limited, and the foaming suppression effect is also limited. When the slag is not put into the slag, the surrounding molten slag is rapidly cooled to form a solidified shell when the water is vaporized, and most of the water vapor generated by the vaporization is blown upward. Thereby, the cooling range of the molten slag is narrowed. On the other hand, when the pulverized slag is charged together with the water, the pulverized slag physically destroys the solidified shell of the slag generated by the vaporization of water, so that the pulverized slag and the water can be invaded from the portion where the solidified shell is broken. In the molten slag, the molten slag can be cooled in a larger range to increase the solid phase ratio, and foaming can be efficiently suppressed.
其次,對更佳之條件進行敍述。以下,按下述條件範圍進行研究並就獲得之理想條件範圍進行說明,該條件範圍係利用轉爐進行熔鐵處理後,朝排渣鍋排出1分鐘3噸以上之熔融爐渣,並投入每1分鐘30.0kg~250kg之水及每1分鐘30.0kg~250kg之粒徑1.0mm~50mm之粉碎爐渣。Second, describe the better conditions. In the following, the following conditions are studied and the desired condition range is described. The condition range is that after the molten iron treatment in the converter, the molten slag of 3 tons or more is discharged to the slag pot for 1 minute, and is put into the 1 minute. 30.0kg to 250kg of water and 30.0kg to 250kg of pulverized slag having a particle diameter of 1.0mm to 50mm per minute.
首先,就不延長轉爐之操作時間之觀點而言,朝內容積30m 3~70m 3之排渣鍋排出熔融爐渣之速度設為每1分鐘3噸以上。宜為4噸以上。又,關於上限,並無特別限定,但速度越快則降落之熔融爐渣之勢頭越強從而越容易自排渣鍋飛出,因此,宜設為每1分鐘6噸以下。更佳為5噸以下。 First, from the viewpoint of not extending the operation time of the converter, the speed at which the molten slag is discharged to the slag pot having an internal volume of 30 m 3 to 70 m 3 is set to be 3 tons or more per minute. It should be 4 tons or more. Further, the upper limit is not particularly limited, but the faster the speed, the stronger the momentum of the molten slag that falls, and the easier it is to fly out of the slag pot. Therefore, it is preferably set to 6 tons or less per minute. More preferably 5 tons or less.
其次,在投入水量為每1分鐘50.0kg~200kg及投入粉碎爐渣量為每1分鐘50.0kg~200kg的條件下,變更粉碎爐渣之粒徑範圍,結果可知,獲得效果之粉碎爐渣之粒徑為5.0mm~30mm。粒徑小於5.0mm之粉碎爐渣無法破壞熔融爐渣藉由水之氣化而急遽冷卻所生成的凝固殼。Next, when the amount of the input water is 50.0 kg to 200 kg per minute and the amount of the pulverized slag is 50.0 kg to 200 kg per minute, the particle size range of the pulverized slag is changed, and as a result, it is understood that the particle size of the pulverized slag obtained is 5.0mm ~ 30mm. The pulverized slag having a particle diameter of less than 5.0 mm cannot break the solidified shell formed by the rapid cooling of the molten slag by vaporization of water.
另一方面,粒徑超過30mm之之粉碎爐渣過重,因此,即便朝自轉爐排出之熔融爐渣流到達排渣鍋內之位置附近投入,以降落之熔融爐渣之動能亦不大能讓粉碎爐渣於排渣鍋內分散。再者,投入之粉碎爐渣中亦可包含粒徑小於5.0mm及超過30mm之粉碎爐渣,只要至少每1分鐘投入50.0kg~200kg之粒徑5.0mm~30mm之粉碎爐渣即可。粉碎爐渣之粒徑為8.0mm~20mm較佳,粒徑10mm~15mm則更佳。關於粉碎爐渣之投入量,將於下文進行敍述。On the other hand, the pulverized slag having a particle diameter of more than 30 mm is excessively heavy. Therefore, even if the molten slag flow discharged from the converter reaches the position near the slag pot, the kinetic energy of the molten slag which falls can not cause the slag to be crushed. Dispersed in the slag pot. Further, the pulverized slag to be charged may include pulverized slag having a particle diameter of less than 5.0 mm and more than 30 mm, and it is sufficient to supply at least 50.0 kg to 200 kg of pulverized slag having a particle diameter of 5.0 mm to 30 mm per minute. The particle size of the pulverized slag is preferably 8.0 mm to 20 mm, and more preferably 10 mm to 15 mm. The input amount of the pulverized slag will be described below.
其次,在以每1分鐘50.0kg~200kg之量投入粒徑5.0mm~30mm之粉碎爐渣的條件下,變更水之投入速度,結果可知,藉由將水量設為每1分鐘50.0kg~200kg可獲得效果。又,可知該傾向在每1分鐘投入50.0kg粉碎爐渣時及投入200kg粉碎爐渣時均相同。若每1分鐘之水量少於50.0kg,則無法將自轉爐排出之熔融爐渣依次完全冷卻,從排渣中途就會起泡加劇而自排渣鍋上端橫溢。另一方面,即便使每1分鐘之水量為200kg以上,由於排渣鍋內之熔融爐渣之起泡已得到充分抑制,故效果飽和而浪費水。水量宜為每1分鐘70kg~150kg,更佳為100kg~120kg。Then, when the pulverized slag having a particle diameter of 5.0 mm to 30 mm is charged in an amount of 50.0 kg to 200 kg per minute, the water input speed is changed. As a result, it is understood that the amount of water is 50.0 kg to 200 kg per minute. Get results. In addition, it is understood that this tendency is the same when 50.0 kg of pulverized slag is charged per minute and when 200 kg of pulverized slag is charged. If the amount of water per minute is less than 50.0 kg, the molten slag discharged from the converter cannot be completely cooled in order, and the foaming is intensified from the middle of the slag discharge, and the upper end of the slag pot overflows. On the other hand, even if the amount of water per minute is 200 kg or more, since the foaming of the molten slag in the slag pot is sufficiently suppressed, the effect is saturated and water is wasted. The amount of water is preferably from 70 kg to 150 kg per 1 minute, more preferably from 100 kg to 120 kg.
其次,於設定每1分鐘投入水50.0kg~200kg且令粉碎爐渣之粒徑為5.0mm~30mm的條件下,變更粉碎爐渣之投入速度,結果可知,藉由每1分鐘投入50.0kg~200kg之粉碎爐渣可獲得效果。又,可知該傾向在每1分鐘投入50.0kg水時及投入200kg水時均相同。若每1分鐘之粉碎爐渣量小於50.0kg,則能夠利用粉碎爐渣破壞爐渣之藉由水之氣化而急遽冷卻所生成之凝固殼的範圍有限,以致熔融爐渣之冷卻範圍變窄。其結果,從排渣中途就會起泡加劇而自排渣鍋上端橫溢。另一方面,即便每1分鐘之粉碎爐渣量超過200kg,由於排渣鍋內之熔融爐渣之起泡得到充分抑制,故效果飽和而浪費粉碎爐渣。粉碎爐渣宜為每1分鐘70kg~150kg,更佳為100kg~120kg。Then, when the input water is 50.0 kg to 200 kg per minute and the particle size of the pulverized slag is 5.0 mm to 30 mm, the input speed of the pulverized slag is changed. As a result, it is found that 50.0 kg to 200 kg is charged per minute. The slag is pulverized to obtain an effect. Further, it is understood that this tendency is the same when 50.0 kg of water is charged per minute and when 200 kg of water is charged. When the amount of the pulverized slag per minute is less than 50.0 kg, the range of the solidified shell formed by the rapid cooling of the slag by the pulverization of the slag can be limited, so that the cooling range of the molten slag is narrowed. As a result, foaming is intensified from the middle of the slag discharge and overflows from the upper end of the slag pot. On the other hand, even if the amount of the pulverized slag per one minute exceeds 200 kg, the foaming of the molten slag in the slag pot is sufficiently suppressed, so that the effect is saturated and the pulverized slag is wasted. The pulverized slag is preferably from 70 kg to 150 kg per 1 minute, more preferably from 100 kg to 120 kg.
又,作為粉碎爐渣之種類,可為轉爐爐渣、脫矽爐渣、熔鐵脫磷爐渣、澆桶爐渣(造塊爐渣)之任一種。其原因在於,需要能夠將上述水之氣化時生成之爐渣凝固殼破壞的程度之強度與比重。再者,將上述爐渣之代表組成記於表1。Further, the type of the pulverized slag may be any one of a converter slag, a slag slag, a molten iron dephosphorization slag, and a slag slag (agglomerated slag). The reason for this is that the strength and specific gravity of the degree of destruction of the solidified shell of the slag generated when the water is vaporized is required. Further, the representative composition of the above slag is shown in Table 1.
【表1】 <TABLE border="1" borderColor="#000000" width="85%"><TBODY><tr><td> 表1 粉碎爐渣之代表性之組成(質量%) </td></tr><tr><td> 品種 </td><td> CaO </td><td> SiO<sub>2</sub></td><td> t.Fe </td><td> Al<sub>2</sub>O<sub>3</sub></td></tr><tr><td> 轉爐爐渣 </td><td> 45 </td><td> 12 </td><td> 15 </td><td> 1 </td></tr><tr><td> 脫矽爐渣 </td><td> 20 </td><td> 45 </td><td> 8 </td><td> 4 </td></tr><tr><td> 熔鐵脫磷爐渣 </td><td> 30 </td><td> 30 </td><td> 15 </td><td> 2 </td></tr><tr><td> 澆桶爐渣 </td><td> 45 </td><td> 10 </td><td> 8 </td><td> 15 </td></tr></TBODY></TABLE>【Table 1】 <TABLE border="1" borderColor="#000000" width="85%"><TBODY><tr><td> Table 1 Representative composition of crushed slag (% by mass) </td></tr> <tr><td> variety</td><td> CaO </td><td> SiO<sub>2</sub></td><td> t.Fe </td><td> Al< Sub>2</sub>O<sub>3</sub></td></tr><tr><td> converter slag</td><td> 45 </td><td> 12 </ Td><td> 15 </td><td> 1 </td></tr><tr><td> 脱炉炉</td><td> 20 </td><td> 45 </td ><td> 8 </td><td> 4 </td></tr><tr><td> molten iron dephosphorization slag</td><td> 30 </td><td> 30 </ Td><td> 15 </td><td> 2 </td></tr><tr><td> pouring slag </td><td> 45 </td><td> 10 </td ><td> 8 </td><td> 15 </td></tr></TBODY></TABLE>
轉爐爐渣係利用轉爐進行脫碳吹煉後自爐內排出之爐渣,鹼度一般為3~5左右。脫矽爐渣係於熔鐵中添加氧化鐵或氧氣而使熔鐵中[Si]氧化時生成之SiO 2濃度較高的爐渣。熔鐵脫磷爐渣係添加CaO或氧化鐵、氧氣使熔鐵中[P]氧化成(P 2O 5)而摻入有P 2O 5的爐渣。澆桶爐渣係將熔鋼排出至連續鑄造機後殘留於澆桶內之Al 2O 3濃度較高的爐渣。 [實施例] The converter slag is a slag discharged from the furnace after decarburization and blowing by a converter, and the alkalinity is generally about 3 to 5. The slag is a slag having a high concentration of SiO 2 formed when iron oxide or oxygen is added to the molten iron to oxidize [Si] in the molten iron. The molten iron dephosphorization furnace slag is added with CaO or iron oxide, oxygen to oxidize [P] in the molten iron to (P 2 O 5 ) and is doped with P 2 O 5 slag. The ladle slag is a slag having a high concentration of Al 2 O 3 remaining in the ladle after the molten steel is discharged to the continuous casting machine. [Examples]
其次,基於實施例對本發明進一步進行說明,實施例中之條件係為了確認本發明之可實施性及效果而採用的一條件例,本發明並不限定於該一條件例。本發明只要不脫離本發明之主旨而達成本發明之目的,則可採用各種條件。Next, the present invention will be further described based on examples, and the conditions in the examples are a conditional example employed to confirm the workability and effects of the present invention, and the present invention is not limited to the one condition example. The present invention can adopt various conditions as long as the object of the present invention is achieved without departing from the gist of the present invention.
[實施例1] 利用多功能轉爐法進行熔鐵脫磷處理後,於使熔鐵保留於轉爐內之狀態下使轉爐傾轉,自轉爐爐口朝設置於爐體下方之容積為50m 3之排渣鍋花費約3分鐘排出鹼度約1之熔融爐渣約14t。又,於排出熔融爐渣時,自剛開始排渣後至排渣結束為止,從配管每1分鐘投入100kg水,同時從滑槽每1分鐘投入200kg之表1所示組成之轉爐爐渣(粒徑5.0mm~30mm)。此時,朝自轉爐排出之熔融爐渣流到達排渣鍋內之位置附近持續投入水及轉爐爐渣。再者,排渣中之熔融爐渣之質量不利用安裝於設置排渣鍋之移動台車之稱量機測定,而是根據操作條件與實績進行推斷。其中,減去自上述滑槽投入之粉碎爐渣之質量。 其結果,自轉爐排出至排渣鍋內之熔融爐渣不怎麼起泡,而未自排渣鍋橫溢。 [Example 1] After the molten iron dephosphorization treatment was carried out by the multi-function converter method, the converter was tilted while the molten iron was kept in the converter, and the volume of the converter furnace mouth was set to be 50 m 3 below the furnace body. The slag pot takes about 3 minutes to discharge about 14 tons of molten slag having a basicity of about 1. In addition, when the molten slag is discharged, 100 kg of water is supplied from the piping every 1 minute from the start of slag discharge, and 200 kg of the converter slag having the composition shown in Table 1 is injected from the chute every minute. 5.0mm ~ 30mm). At this time, the molten slag flow discharged from the converter into the slag pot is continuously supplied with water and converter slag. Further, the quality of the molten slag in the slag discharge is not measured by a weighing machine attached to a moving trolley provided with a slag pot, but is estimated based on the operating conditions and actual performance. Among them, the mass of the pulverized slag input from the above chute is subtracted. As a result, the molten slag discharged from the converter to the slag pot does not foam much, but does not overflow from the slag pot.
[比較例1] 利用多功能轉爐法進行熔鐵脫磷處理後,於使熔鐵保留於轉爐內之狀態下使轉爐傾轉,自轉爐爐口朝設置於爐體下方之容積為50m 3之排渣鍋花費約3分鐘排出鹼度約1之熔融爐渣約14t。又,於排出熔融爐渣時,自剛開始排渣後至排渣結束為止,從配管每1分鐘投入40.0kg水,同時從滑槽每1分鐘投入300kg之表1所示組成之轉爐爐渣(粒徑5.0mm~30mm)。此時,朝自轉爐排出之熔融爐渣流到達排渣鍋內之位置附近持續投入水及轉爐爐渣。再者,排渣中之熔融爐渣之質量根據操作條件與實績進行推斷。其中,減去自上述滑槽投入之轉爐爐渣之質量。 其結果,從開始自轉爐往排渣鍋內排渣後經過1.5分鐘時起,排渣鍋內之熔融爐渣就會劇烈起泡而自排渣鍋橫溢。 [產業上之可利用性] [Comparative Example 1] After the molten iron dephosphorization treatment was carried out by the multi-function converter method, the converter was tilted while the molten iron was kept in the converter, and the volume of the converter furnace mouth was set to be 50 m 3 below the furnace body. The slag pot takes about 3 minutes to discharge about 14 tons of molten slag having a basicity of about 1. In addition, when the molten slag is discharged, 40.0 kg of water is supplied from the piping immediately after the slag discharge to the end of the slag discharge, and 300 kg of the converter slag having the composition shown in Table 1 is injected from the chute every minute. The diameter is 5.0mm to 30mm). At this time, the molten slag flow discharged from the converter into the slag pot is continuously supplied with water and converter slag. Furthermore, the quality of the molten slag in the slag is estimated based on the operating conditions and actual performance. Among them, the mass of the converter slag input from the above chute is subtracted. As a result, from 1.5 minutes after the start of the slag discharging from the converter to the slag pot, the molten slag in the slag pot is vigorously foamed and overflows from the slag pot. [Industrial availability]
根據本發明,可於自轉爐往排渣鍋排出爐渣時在不延長爐渣排出時間之下效率良好地抑制起泡。According to the present invention, it is possible to efficiently suppress foaming without discharging the slag discharge time when the slag is discharged from the rotary kiln to the slag discharge pot.
1…轉爐 2…排渣鍋 3…爐口 4…配管1... converter 2... slag pot 3... furnace mouth 4... piping
圖1係用於說明抑制排渣鍋內之爐渣起泡之方法的圖。Fig. 1 is a view for explaining a method of suppressing slag foaming in a slag pot.
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