TWI570244B - Preliminary treatment method for molten iron - Google Patents
Preliminary treatment method for molten iron Download PDFInfo
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- TWI570244B TWI570244B TW103101625A TW103101625A TWI570244B TW I570244 B TWI570244 B TW I570244B TW 103101625 A TW103101625 A TW 103101625A TW 103101625 A TW103101625 A TW 103101625A TW I570244 B TWI570244 B TW I570244B
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- C—CHEMISTRY; METALLURGY
- C21—METALLURGY OF IRON
- C21C—PROCESSING OF PIG-IRON, e.g. REFINING, MANUFACTURE OF WROUGHT-IRON OR STEEL; TREATMENT IN MOLTEN STATE OF FERROUS ALLOYS
- C21C1/00—Refining of pig-iron; Cast iron
- C21C1/02—Dephosphorising or desulfurising
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- C—CHEMISTRY; METALLURGY
- C21—METALLURGY OF IRON
- C21C—PROCESSING OF PIG-IRON, e.g. REFINING, MANUFACTURE OF WROUGHT-IRON OR STEEL; TREATMENT IN MOLTEN STATE OF FERROUS ALLOYS
- C21C1/00—Refining of pig-iron; Cast iron
- C21C1/04—Removing impurities other than carbon, phosphorus or sulfur
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- Refinement Of Pig-Iron, Manufacture Of Cast Iron, And Steel Manufacture Other Than In Revolving Furnaces (AREA)
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Description
本發明是關於一種使用一個轉爐型精煉爐,隔著中途的排渣步驟連續地進行熔鐵的脫矽處理與脫磷處理的熔鐵的預備處理方法。 The present invention relates to a method for preparing a molten iron which is continuously subjected to a desulfurization treatment and a dephosphorization treatment of a molten iron by using a converter type refining furnace through a slag discharging step in the middle.
近年來,強烈要求削減溫室效應氣體的排出量,於鋼鐵業中,利用轉爐或熔鐵鍋等處理容器進行脫磷處理或脫碳精煉等時,於爐內的熔鐵中調配鐵屑(iron scrap)等冷鐵源而削減製造鋼鐵所需的能源。其原因在於,冷鐵源與裝入至高爐的鐵礦石之類的氧化鐵不同,無需進行還原,因此與將自高爐出鐵的生鐵精煉而製造熔鋼的方法相比,可以少量的能源消耗量、少量的溫室效應氣體排出量製造熔鋼。 In recent years, there has been a strong demand to reduce the amount of greenhouse gas emissions. In the steel industry, when decontamination treatment or decarburization refining is carried out using a processing vessel such as a converter or a molten iron pan, iron filings (iron) are placed in the molten iron in the furnace. Scrap) and other cold iron sources reduce the energy needed to make steel. The reason is that the cold iron source is different from the iron oxide such as iron ore charged in the blast furnace, and it is not necessary to carry out the reduction. Therefore, compared with the method of refining the pig iron from the blast furnace to produce molten steel, a small amount of energy can be used. The consumption and the amount of greenhouse gas emissions are small to produce molten steel.
另外,近年來,由於在成本方面及品質方面有利,故而實施有於利用轉爐進行脫碳精煉前對熔鐵實施預備處理而預先去除熔鐵中的磷的精煉方法(亦稱為「預備脫磷處理」)。通常,脫磷處理藉由如下方式進行:將氧化劑(氧氣等氧源)及脫磷精煉劑(CaO系助熔劑)添加至熔鐵中,利用氧化劑將熔鐵中的磷氧化而製成磷氧化物,並使其吸收於經渣化的脫磷精煉劑,就熱力 學而言,該脫磷反應是精煉溫度越低越有利。即,溫度低於熔鋼階段的熔鐵階段容易進行脫磷反應,可利用少量的氧化劑及脫磷精煉劑進行脫磷處理。因此,藉由進行上述預備脫磷處理,雖然使處理步驟增加,但是可削減全部製鋼精煉步驟中的爐渣(slag)產生量。 In addition, in recent years, it is advantageous in terms of cost and quality, and therefore, a refining method for preliminarily removing phosphorus from molten iron before performing decarburization refining by a converter to perform pre-dephosphorization (also referred to as "pre-dephosphorization" deal with"). Usually, the dephosphorization treatment is carried out by adding an oxidizing agent (oxygen source such as oxygen) and a dephosphorization refining agent (CaO-based flux) to the molten iron, and oxidizing the phosphorus in the molten iron to form phosphorus oxidation. And absorb it into the slag-removing dephosphorization refining agent In theory, the dephosphorization reaction is advantageous as the refining temperature is lower. That is, the dephosphorization reaction is easily carried out at a temperature lower than the molten iron phase of the molten steel stage, and a dephosphorization treatment can be carried out using a small amount of an oxidizing agent and a dephosphorization refining agent. Therefore, by performing the above-described preliminary dephosphorization treatment, although the number of processing steps is increased, the amount of slag generated in all the steel refining steps can be reduced.
且說,於自高爐出鐵的熔鐵中含有0.3質量%(mass%) ~0.6質量%左右的矽,若對含有矽的熔鐵進行脫磷處理,則最初將矽氧化去除而使熔鐵中的矽濃度降低至某程度後,將熔鐵中的磷氧化去除。藉由上述矽的氧化而產生以SiO2為主成分的爐渣,該爐渣會妨礙脫磷反應。其原因在於,為了進行脫磷反應,必需鹼度([CaO(質量%)]/[SiO2(質量%)])為1.2以上的爐渣,但相對於此,藉由矽的氧化而產生的SiO2具有降低爐渣的鹼度的作用。 In addition, the molten iron from the blast furnace is contained in a range of 0.3% by mass to 0.6% by mass. If the molten iron containing cerium is dephosphorized, the ruthenium is first removed by oxidation and the molten iron is removed. After the cerium concentration is lowered to a certain extent, the phosphorus in the molten iron is oxidized and removed. The slag containing SiO 2 as a main component is generated by the oxidation of the above ruthenium, and the slag hinders the dephosphorization reaction. This is because slag having a basicity ([CaO (% by mass)) / [SiO 2 (% by mass))) of 1.2 or more is necessary for the dephosphorization reaction, but it is produced by oxidation of ruthenium. SiO 2 has a function of lowering the alkalinity of the slag.
包括高爐-轉爐的組合的鋼鐵精煉步驟中,鐵屑等冷鐵 源的熔解用熱源是以熔鐵所具有的顯熱(sensible heat)、以及熔鐵中的碳及矽的燃燒熱為主體,基本上無法熔解大量冷鐵源。而且,如上所述,於實施脫矽處理及脫磷處理作為對熔鐵的預備處理的情形時,除了隨著處理步驟的追加熔鐵溫度降低以外,成為燃燒熱源的熔鐵中的碳及矽亦因上述脫矽處理及脫磷處理氧化而減少,因此對轉爐中的冷鐵源的熔解更不利。 In the steel refining step including the combination of blast furnace and converter, cold iron such as iron filings The heat source for melting of the source is mainly composed of the sensible heat of the molten iron and the heat of combustion of carbon and helium in the molten iron, and it is basically impossible to melt a large amount of cold iron source. Further, as described above, in the case where the untwisting treatment and the dephosphorization treatment are performed as the preliminary treatment for the molten iron, carbon and bismuth in the molten iron which becomes the combustion heat source are removed in addition to the decrease in the temperature of the additional molten iron in the processing step. It is also reduced by the above-described deodorization treatment and dephosphorization treatment, so that the melting of the cold iron source in the converter is more disadvantageous.
因此,於進行熔鐵預備處理的情形時,為了熔解更多的 冷鐵源,例如於專利文獻1中提出如下熔鐵的預備處理方法:使用一個轉爐型精煉爐進行熔鐵的脫矽、脫磷處理時,首先以使脫矽處理結束時的爐渣的鹼度成為0.3~1.3的範圍的方式調節CaO 系助熔劑的供給量而進行脫矽處理,其後,傾動精煉爐將爐內所產生的爐渣自爐口排出,繼而,重新添加CaO系助熔劑進行脫磷處理。另外,專利文獻2中提出如下熔鐵的預備處理方法:使用一個轉爐型精煉爐進行熔鐵的脫矽、脫磷處理時,於脫磷處理結束使熔鐵流出後,在不排出爐渣而使其殘留於爐內的狀態下,將下一爐次(charge)的熔鐵裝入至精煉爐內,供給氧而進行脫矽處理,於脫矽處理後,暫且中斷吹煉(blowing)而設置排出爐渣的中間排渣步驟,其後,繼續進行脫磷處理。 Therefore, in the case of performing the molten iron preparation process, in order to melt more In the cold iron source, for example, Patent Document 1 proposes a method for preparing a molten iron in which the alkalinity of the slag at the end of the deodorization treatment is first performed when the molten iron is removed and dephosphorized using a converter type refining furnace. Adjusting CaO in a way that is in the range of 0.3~1.3 The desulfurization treatment is performed by supplying the flux, and thereafter, the slag generated in the furnace is discharged from the furnace mouth by the tilting refining furnace, and then the CaO-based flux is newly added to perform dephosphorization treatment. Further, Patent Document 2 proposes a method for preparing a molten iron in which a desulfurization treatment is performed using a converter type refining furnace, and after the dephosphorization treatment is completed, the molten iron is discharged, and the slag is not discharged. In the state where it remains in the furnace, the molten iron of the next charge is charged into the refining furnace, and oxygen is supplied to perform the deodorization treatment, and after the deodorization treatment, the blowing is temporarily interrupted and set. The intermediate slag discharging step of the slag is discharged, and thereafter, the dephosphorization treatment is continued.
上述專利文獻1的技術可藉由利用一個轉爐型精煉爐進 行脫矽處理及脫磷處理,而防止由熔鐵的轉移引起的溫度降低,另外,專利文獻2的技術除了該效果以外,由於將脫磷處理中產生的爐渣(以下亦稱為「脫磷爐渣」)再次使用於脫矽處理中,故而亦可減少由於在脫矽處理步驟中添加造渣劑而引起的溫度降低。 The technique of the above Patent Document 1 can be carried out by using a converter type refining furnace In addition to the effect, the technique of the patent document 2 removes the slag generated by the dephosphorization treatment (hereinafter also referred to as "dephosphorization", in addition to the effect, in addition to the effect of the de-phosphorization treatment and the dephosphorization treatment. The slag ") is reused in the deodorization treatment, so that the temperature drop due to the addition of the slagging agent in the deodorization treatment step can be reduced.
即,藉由採用專利文獻1或專利文獻2的技術,可降低熔鐵的預備處理步驟中的熱損耗,因此與先前相比可增大冷鐵源的調配比率,並且可實現溫室效應氣體的排出量的削減或製造成本的降低。 That is, by employing the technique of Patent Document 1 or Patent Document 2, the heat loss in the preliminary processing step of the molten iron can be reduced, so that the blending ratio of the cold iron source can be increased as compared with the prior, and the greenhouse effect gas can be realized. Reduction in discharge amount or reduction in manufacturing cost.
[現有技術文獻] [Prior Art Literature]
[專利文獻] [Patent Literature]
[專利文獻1]:日本專利特開平10-152714號公報 [Patent Document 1]: Japanese Patent Laid-Open No. Hei 10-152714
[專利文獻2]:日本專利特開平11-323420號公報 [Patent Document 2]: Japanese Patent Laid-Open No. Hei 11-323420
然而,上述現有技術中存在以下問題。 However, the above problems exist in the above prior art.
如專利文獻1或專利文獻2中揭示的技術般,於利用一個轉 爐型精煉爐連續地進行脫矽處理、中間排渣、脫磷處理的情形時,為了將爐渣的鹼度設為脫磷所需的規定值以上,且減少脫磷處理中使用的CaO系助熔劑,必須將脫矽處理中產生的含有大量SiO2的爐渣(以下亦稱為「脫矽爐渣」)自轉爐型精煉爐排出規定量以上。 In the case where the desulfurization treatment, the intermediate slag removal, and the dephosphorization treatment are continuously performed by a converter type refining furnace as in the technique disclosed in Patent Document 1 or Patent Document 2, in order to set the alkalinity of the slag to dephosphorization When the CaO-based flux used in the dephosphorization treatment is reduced, the slag containing a large amount of SiO 2 (hereinafter also referred to as "de-slurry slag") generated in the decarburization treatment must be discharged from the converter-type refining furnace. More than the specified amount.
就該觀點而言,縱觀上述現有技術,關於專利文獻1的 技術,一般認為若將脫矽處理結束時的爐渣的鹼度控制為0.3~1.3,則爐渣充分地顯示出流動性,而充分地進行脫矽爐渣的排渣。 然而,若僅將脫矽爐渣的鹼度控制為0.3~1.3,則爐渣的成型(forming)不充分,流動性亦差,難以於短時間內排出爐渣而不使熔鐵流出,反之,則有過度成型,於脫矽處理中爐渣自爐口溢出而妨礙操作等的情況,因此難以充分地控制排渣。 From this point of view, with regard to the above prior art, regarding Patent Document 1 In the technique, it is considered that when the alkalinity of the slag at the end of the deodorization treatment is controlled to 0.3 to 1.3, the slag sufficiently exhibits fluidity, and the slag discharge of the slag is sufficiently performed. However, if only the alkalinity of the slag is controlled to 0.3 to 1.3, the slag is insufficiently formed and the fluidity is poor, and it is difficult to discharge the slag in a short time without flowing the molten iron, and vice versa. Excessive molding, in which the slag overflows from the furnace mouth during the untwisting process, and the operation or the like is hindered, so that it is difficult to sufficiently control the slag discharge.
另外,專利文獻2的技術提出較佳為於將脫矽爐渣的鹼度設為1.0~3.0,使熔鐵中的矽濃度成為0.20質量%以下之後進行中間排渣。然而,其原因在於,在脫矽處理結束時的熔鐵中的矽濃度高於0.20質量%的情形時,為了將下一步驟的脫磷處理時的爐渣的鹼度調整為2.0所必需的含CaO的物質變得過多,於成本上變得不利,但對於脫矽爐渣的排渣性並無任何考慮。 Further, the technique of Patent Document 2 proposes to perform intermediate slag discharge by setting the alkalinity of the slag slag to 1.0 to 3.0 and the cerium concentration in the molten iron to 0.20% by mass or less. However, the reason is that when the concentration of cerium in the molten iron at the end of the decanting treatment is higher than 0.20% by mass, the content necessary for adjusting the alkalinity of the slag at the time of dephosphorization treatment in the next step to 2.0 is included. The substance of CaO becomes excessive and becomes disadvantageous in terms of cost, but there is no consideration for the slagging property of the slag.
即,上述專利文獻1及專利文獻2中揭示的技術存在如下問題:無法充分地排出脫矽爐渣,而必須於下一步驟的脫磷處理中增加CaO系助熔劑的使用量,或者有脫磷處理後的熔鐵中的磷濃度變高之虞。 In other words, the techniques disclosed in Patent Document 1 and Patent Document 2 have a problem in that the slag can not be sufficiently discharged, and the amount of the CaO-based flux must be increased in the dephosphorization treatment in the next step, or dephosphorization is required. The concentration of phosphorus in the molten iron after the treatment becomes high.
本發明是鑒於上述現有技術中的問題而完成,其目的在 於提出如下熔鐵的預備處理方法,其是使用一個轉爐型精煉爐,隔著中途的排渣步驟連續地進行熔鐵的脫矽處理與脫磷處理的熔鐵的預備處理方法,且藉由改善脫矽處理中產生的脫矽爐渣的排渣性,可抑制熔鐵的溫度降低且以低成本進行下一步驟的脫磷處理。 The present invention has been made in view of the above problems in the prior art, and its object is The present invention proposes a method for preparing a molten iron, which is a method for preparing a molten iron which is continuously subjected to a desulfurization treatment and a dephosphorization treatment of a molten iron by using a converter type refining furnace through a slag discharging step in the middle. The slag discharge property of the slag slag generated in the mashing treatment is improved, and the temperature reduction of the molten iron can be suppressed and the dephosphorization treatment in the next step can be performed at low cost.
為了解決上述課題而開發的本發明的第1實施方式是如 下熔鐵的預備處理方法:向轉爐型精煉爐內的熔鐵供給氧源進行脫矽處理後,在爐內殘留有熔鐵的狀態下將存在於爐內的爐渣的一部分自轉爐型精煉爐排出,其後,向轉爐型精煉爐內供給CaO系助熔劑及氧源進行脫磷處理,使經上述脫磷處理的熔鐵自轉爐型精煉爐流出,藉此使用一個轉爐型精煉爐對熔鐵進行脫矽處理及脫磷處理,上述熔鐵的預備處理方法的特徵在於:於上述脫矽處理中,對利用轉爐型精煉爐的排出氣體(exhaust gas)處理設備吸入的吸入氣體(suction gas)中的至少一種以上含有碳原子的氣態物質(gaseous species)的濃度進行分析,基於其分析值決定脫矽處理的結束時間點。 The first embodiment of the present invention developed to solve the above problems is as A method for preparing a molten iron after the molten iron is supplied to the converter-type refining furnace to be subjected to a desulfurization treatment, and a part of the slag present in the furnace is self-rotating furnace-type refining furnace in a state in which molten iron remains in the furnace. After the discharge, the CaO-based flux and the oxygen source are supplied to the converter type refining furnace for dephosphorization treatment, and the molten iron subjected to the dephosphorization treatment is discharged from the converter type refining furnace, thereby melting the furnace using a converter type refining furnace. The iron is subjected to a degassing treatment and a dephosphorization treatment, and the method for preparing the molten iron is characterized in that the suction gas sucked by the exhaust gas processing equipment of the converter type refining furnace is used in the above-described deodorization treatment (suction gas) The concentration of at least one or more gaseous species containing carbon atoms is analyzed, and the end time of the dislocation treatment is determined based on the analysis value.
本發明的第2實施方式是如本發明的第1實施方式的熔 鐵的預備處理方法,其特徵在於:基於上述吸入氣體中的含有碳原子的氣態物質的濃度的分析值及上述吸入氣體的流量,算出上述脫矽處理中的自轉爐型精煉爐排出的排出氣體中的碳的排出速度,基於上述算出的排出氣體中的碳的排出速度成為極大值,成為極小值後再次增大的變動圖案(pattern),決定上述脫矽處理的結束時間點。 A second embodiment of the present invention is a melting method according to the first embodiment of the present invention. The iron preparation processing method is characterized in that the exhaust gas discharged from the converter type refining furnace in the deodorization treatment is calculated based on an analysis value of a concentration of a gaseous substance containing carbon atoms in the intake gas and a flow rate of the suction gas. The discharge rate of the carbon in the above-described calculated exhaust gas is a maximum value after the discharge rate of the carbon in the exhaust gas is a maximum value, and the pattern of the end of the dislocation process is determined.
本發明的第3實施方式是如本發明的第1實施方式的熔 鐵的預備處理方法,其特徵在於:基於上述吸入氣體中的CO氣體濃度、CO2氣體濃度、及CO氣體與CO2氣體的合計濃度中的任一濃度的分析值成為極大值,成為極小值後再次增大的變動圖案,決定上述脫矽處理的結束時間點。 According to a third aspect of the present invention, in a method for preparing a molten iron according to the first embodiment of the present invention, the CO gas concentration, the CO 2 gas concentration, and the CO gas and the CO 2 gas are based on the inhaled gas. The analysis value of any of the total concentrations is a maximum value, and the fluctuation pattern which is increased again after the minimum value is determined, and the end time of the above-described dislocation processing is determined.
本發明的第4實施方式是如本發明的第1實施方式的熔 鐵的預備處理方法,其特徵在於:基於根據上述吸入氣體中的CO氣體濃度、CO2氣體濃度、及CO氣體與CO2氣體的合計濃度中的任一濃度的分析值與上述吸入氣體的流量的乘積算出的變動圖案,決定上述脫矽處理的結束時間點,上述變動圖案為上述吸入氣體中的CO氣體流量、CO2氣體流量及CO氣體與CO2氣體的合計流量中的任一流量成為極大值,成為極小值後再次增大的變動圖案。 According to a fourth aspect of the present invention, in a method of preparing a molten iron according to the first embodiment of the present invention, the CO gas concentration, the CO 2 gas concentration, and the CO gas and the CO 2 are based on the inhaled gas. The fluctuation pattern calculated by the product of the analysis value of any of the total concentration of the gas and the flow rate of the suction gas determines the end time of the deodorization process, and the fluctuation pattern is the CO gas flow rate and CO 2 in the intake gas. Any one of the gas flow rate and the total flow rate of the CO gas and the CO 2 gas is a maximum value, and the fluctuation pattern is increased again after the minimum value.
本發明的第5實施方式是如本發明的第2實施方式至第 4實施方式中任一實施方式的熔鐵的預備處理方法,其特徵在於:於上述成為極大值,成為極小值後再次增大的變動圖案中,以再次增大的值相對於極大值成為90%以上且150%以下的規定比率的值以上的時間點為基準,將上述脫矽處理的結束時間點設為規定的經過時間範圍內。 According to a fifth embodiment of the present invention, the second embodiment to the present invention According to a fourth aspect of the present invention, in the method of preparing a molten iron according to any of the above-described embodiments, in the variation pattern which becomes a maximum value and then increases again, the value which is increased again becomes 90 with respect to the maximum value. The time point above the value of the predetermined ratio of % or more and 150% or less is used as a reference, and the end time of the above-described dislocation processing is set to a predetermined elapsed time range.
本發明的第6實施方式是如本發明的第2實施方式至第 5實施方式中任一實施方式的熔鐵的預備處理方法,其特徵在於:上述成為極大值,成為極小值後再次增大的變動圖案中的極大值與極小值的差為極大值的10%以上。 According to a sixth embodiment of the present invention, the second embodiment to the present invention According to a fifth aspect of the present invention, in the method of preparing a molten iron according to any one of the embodiments, the maximum value is a maximum value, and a difference between a maximum value and a minimum value in a variation pattern that increases again after a minimum value is 10% of a maximum value. the above.
本發明的第7實施方式是如本發明的第1實施方式的熔 鐵的預備處理方法,其特徵在於:以上述吸入氣體中的CO氣體濃度、CO2氣體濃度、及CO氣體與CO2氣體的合計濃度中的任一濃度的分析值成為規定閾值以上的時間點為基準,將上述脫矽處理的結束時間點設為規定的經過時間範圍內。 According to a seventh aspect of the present invention, in a method of preparing a molten iron according to the first embodiment of the present invention, the CO gas concentration, the CO 2 gas concentration, and the CO gas and the CO 2 gas in the suction gas are used. The end time of the above-described dislocation processing is set to a predetermined elapsed time range based on the time point when the analysis value of any of the total concentrations is equal to or greater than the predetermined threshold value.
本發明的第8實施方式是如本發明的第7實施方式的熔 鐵的預備處理方法,其特徵在於:上述排出氣體處理設備具有回收所吸入的上述轉爐型精煉爐的排出氣體作為燃料氣體的功能,利用上述排出氣體處理設備一併吸入轉爐型精煉爐的排出氣體與大氣,使上述排出氣體中的CO氣體的至少一部分燃燒,並且以上述燃燒後的吸入氣體中的CO氣體濃度成為2.0vol%以上且18.0vol%以下的規定閾值以上的時間點為基準,將上述脫矽處理的結束時間點設為規定的經過時間範圍內。 An eighth embodiment of the present invention is a melting method according to a seventh embodiment of the present invention. In the method for preparing an iron, the exhaust gas treatment device has a function of recovering the exhaust gas of the converter-type refining furnace that is sucked in as a fuel gas, and sucks the exhaust gas of the converter-type refining furnace together with the exhaust gas treatment device. In the atmosphere, at least a part of the CO gas in the exhaust gas is burned, and the time when the CO gas concentration in the inhaled gas after the combustion is equal to or greater than a predetermined threshold of 2.0 vol% or more and 18.0 vol% or less is used as a reference. The end time point of the above-described dislocation processing is set within a predetermined elapsed time range.
本發明的第9實施方式是如本發明的第1實施方式的熔 鐵的預備處理方法,其特徵在於:以根據上述吸入氣體中的CO氣體濃度、CO2氣體濃度、及CO氣體與CO2氣體的合計濃度中的任一濃度的分析值與上述吸入氣體的流量的乘積算出的上述吸入氣體中的CO氣體流量、CO2氣體流量及CO氣體與CO2氣體的合計流量中的任一流量成為規定閾值以上的時間點為基準,將上述脫矽處理的結束時間點設為規定的經過時間範圍內。 According to a ninth aspect of the present invention, in a method for preparing a molten iron according to the first embodiment of the present invention, the CO gas concentration, the CO 2 gas concentration, and the CO gas and the CO 2 in the suction gas are used. Any one of the CO gas flow rate, the CO 2 gas flow rate, and the total flow rate of the CO gas and the CO 2 gas in the intake gas calculated by multiplying the analysis value of any of the total concentration of the gas and the flow rate of the intake gas. The time point of the above-described dislocation processing is set to be within a predetermined elapsed time range based on the time point of the predetermined threshold or more.
本發明的第10實施方式是如本發明的第1實施方式的 熔鐵的預備處理方法,其特徵在於:基於上述吸入氣體中的含有碳原子的氣態物質的濃度的分析值及上述吸入氣體的流量,算出上述脫矽處理中的自轉爐型精煉爐排出的排出氣體中的碳的排出速度,以該排出速度成為規定閾值以上的時間點為基準,將上述 脫矽處理的結束時間點設為規定的經過時間範圍內。 A tenth embodiment of the present invention is the first embodiment of the present invention. A method for preparing a molten iron, which is characterized in that the discharge of the spin-type refining furnace in the above-described deodorization treatment is calculated based on an analysis value of a concentration of a gaseous substance containing carbon atoms in the inhaled gas and a flow rate of the inhaled gas. The discharge speed of the carbon in the gas is based on the time point at which the discharge speed is equal to or greater than a predetermined threshold value. The end time of the dislocation process is set within a predetermined elapsed time range.
本發明的第11實施方式是如本發明的第1實施方式至 第10實施方式中任一實施方式的熔鐵的預備處理方法,其特徵在於:在使前一爐次的脫磷處理中產生的爐渣於爐內殘留30質量%的狀態下,將下一爐次的熔鐵裝入至轉爐型精煉爐內,並進行脫矽處理。 An eleventh embodiment of the present invention is the first embodiment of the present invention to A method for preparing a molten iron according to any one of the tenth embodiments, wherein the slag generated in the dephosphorization treatment of the previous heat is 30% by mass in the furnace, and the next furnace is used. The secondary molten iron is charged into a converter type refining furnace and subjected to deodorization treatment.
本發明的第12實施方式是如本發明的第1實施方式至 第11實施方式中任一實施方式的熔鐵的預備處理方法,其特徵在於:在上述脫矽處理結束時,將上述轉爐型精煉爐內存在的爐渣的鹼度([CaO(質量%)]/[SiO2(質量%)])控制為0.80~1.50的範圍。 According to a twelfth aspect of the present invention, in the method of preparing a molten iron according to any one of the first to eleventh embodiments of the present invention, the converter type is The alkalinity ([CaO (mass%)) / [SiO 2 (% by mass))) of the slag present in the refining furnace is controlled to be in the range of 0.80 to 1.50.
根據本發明,於使用一個轉爐型精煉爐,隔著中間排渣連續地進行熔鐵的脫矽處理及脫磷處理時,基於轉爐型精煉爐的排出氣體處理設備所吸入的吸入氣體中的含有碳原子的氣態物質的分析值,決定脫矽處理的結束時間點,因此脫矽處理結束判定的偏差大幅度降低,可始終於脫矽爐渣充分地成型,流動性高的狀態下進行中間排渣,而可於短時間內且充分地排出脫矽爐渣而不會使熔鐵流出,進而,可降低脫矽處理後的脫磷處理的成本及處理後的熔鐵中的磷濃度的偏差。 According to the present invention, in the case of using a converter type refining furnace, the desulfurization treatment and the dephosphorization treatment of the molten iron are continuously performed through the intermediate slag, and the contents of the suction gas sucked by the exhaust gas treatment equipment of the converter type refining furnace are contained. When the analysis value of the gaseous substance of the carbon atom determines the end time of the dislocation treatment, the deviation of the determination of the completion of the dislocation treatment is greatly reduced, and the slag can be continuously formed in the state where the slag is sufficiently formed and the fluidity is high. On the other hand, the degreasing furnace slag can be sufficiently discharged in a short time without flowing out the molten iron, and further, the cost of the dephosphorization treatment after the deodorization treatment and the variation in the phosphorus concentration in the molten iron after the treatment can be reduced.
1‧‧‧轉爐型精煉爐 1‧‧‧ Converter type refining furnace
2‧‧‧頂吹噴槍 2‧‧‧ top blow gun
3‧‧‧底吹風口 3‧‧‧ bottom air outlet
4‧‧‧出鐵口 4‧‧‧iron outlet
5‧‧‧熔鐵 5‧‧‧ molten iron
5a‧‧‧脫矽處理後的熔鐵 5a‧‧‧Fused iron after dislocation treatment
5b‧‧‧脫磷處理後的熔鐵 5b‧‧‧Fused iron after dephosphorization
6‧‧‧脫矽爐渣 6‧‧‧Desulfurization slag
7‧‧‧脫磷爐渣 7‧‧‧Dephosphorization furnace slag
8‧‧‧冷鐵源 8‧‧‧cold iron source
9‧‧‧氧氣 9‧‧‧Oxygen
10‧‧‧底吹氣體 10‧‧‧ bottom blowing gas
11‧‧‧裙罩 11‧‧‧ skirt
12‧‧‧煙道 12‧‧‧ flue
13‧‧‧氣體採取探針 13‧‧‧ gas probe
14‧‧‧氣體分析裝置 14‧‧‧Gas analysis device
15‧‧‧裝入鍋 15‧‧‧Loading the pot
圖1是表示脫矽處理中的排出氣體中的碳的排出速度的變化 的例的圖表。 Figure 1 is a graph showing changes in the discharge rate of carbon in the exhaust gas during the deodorization treatment. The chart of the example.
圖2(a)~圖2(c)是對排出氣體中的碳的排出速度的變化進行說明的圖。 2(a) to 2(c) are diagrams for explaining changes in the discharge speed of carbon in the exhaust gas.
圖3是本發明的熔鐵的預備處理方法中使用的轉爐型精煉爐的大致剖面圖。 Fig. 3 is a schematic cross-sectional view showing a converter type refining furnace used in a method for preparing a molten iron according to the present invention.
圖4是表示脫矽處理結束時的吸入氣體中的CO氣體濃度與脫矽爐渣的排渣性的關係的圖。 4 is a view showing the relationship between the concentration of CO gas in the intake gas and the slagging property of the slag of the slag at the end of the devolatilization treatment.
圖5(a)~圖5(f)是按照步驟對本發明的預備處理方法進行說明的示意圖。 5(a) to 5(f) are schematic views for explaining a preliminary processing method of the present invention in accordance with the steps.
圖6是與現有方法比較表示本發明的方法中的中間排渣時間與熔鐵中Si濃度的關係的圖表。 Fig. 6 is a graph showing the relationship between the intermediate slag discharge time and the Si concentration in the molten iron in the method of the present invention as compared with the conventional method.
首先,對本發明的基本的技術思想進行說明。 First, the basic technical idea of the present invention will be described.
發明者等人於使用一個轉爐型精煉爐,隔著脫矽處理後的脫矽爐渣的排出(以下亦稱為「中間排渣」)對熔鐵連續地進行脫矽處理及脫磷處理的情形時,為了改善上述脫矽爐渣的排渣性,而對影響到脫矽爐渣的排渣性的各種因素反覆進行努力研究。 The inventor of the present invention uses a converter-type refining furnace to continuously perform deodorization treatment and dephosphorization treatment on the molten iron through the discharge of the degreasing furnace slag after deodorization treatment (hereinafter also referred to as "intermediate slag discharge"). In order to improve the slagging property of the above-mentioned slag slag, various factors affecting the slagging property of the slag slag are repeatedly studied.
其結果為以下事項成為明確,關於中間排渣中的脫矽爐渣的排渣性,除了脫矽爐渣本身的流動性以外,脫矽爐渣的成型狀況亦產生大的影響,為了使脫矽爐渣的排渣性變得良好,重要的是於排渣時脫矽爐渣處於充分地渣化而顯示良好的流動性的狀態,並且爐渣充分地成型而使體積(volume)比重變小。 As a result, it is clear that the slag discharge property of the slag slag in the intermediate slag is in addition to the fluidity of the slag slag itself, and the molding condition of the slag slag is greatly affected, in order to remove the slag. The slag discharge property is good, and it is important that the slag is sufficiently slag at the time of slag discharge to exhibit good fluidity, and the slag is sufficiently molded to reduce the volume specific gravity.
脫矽處理中所產生的脫矽爐渣是藉由將由熔鐵中的矽 的燃燒而產生的SiO2、及添加或殘留於爐內的造渣材料渣化而形成。於熔鐵溫度低、熔鐵中的矽濃度高的脫矽處理的初期,優先進行脫矽反應,爐內的SiO2量逐漸增大,為了確保排渣時的流動性,重要的是添加或預先裝入生石灰或製鋼爐渣等含有CaO的造渣材料,將爐渣的組成調整為適當範圍。 The slag slag generated in the mashing treatment is formed by slag-forming SiO 2 produced by combustion of ruthenium in the molten iron and slag-forming material added or left in the furnace. In the initial stage of the deodorization treatment in which the molten iron temperature is low and the rhodium concentration in the molten iron is high, the decoupling reaction is preferentially performed, and the amount of SiO 2 in the furnace is gradually increased. In order to ensure fluidity during slag discharge, it is important to add or A slag-forming material containing CaO such as quicklime or steel slag is preliminarily charged, and the composition of the slag is adjusted to an appropriate range.
另一方面,CO氣體的產生速度於脫矽處理的初期處於 低位,但隨著進行脫矽反應,熔鐵中的矽濃度降低至不足0.20質量%,熔鐵溫度上升,脫碳反應變得活躍,而使CO氣體的產生速度逐漸增大。另外,爐渣中的氧化鐵的濃度於熔鐵中的矽濃度高的脫矽處理的初期亦相對較低為不足10質量%,但隨著脫矽反應的進行,熔鐵中的矽濃度降低,爐渣量增大,而使爐渣中的氧化鐵的濃度逐漸增大。 On the other hand, the rate of CO gas generation is at the initial stage of the dislocation treatment. In the low position, as the desorption reaction proceeds, the concentration of ruthenium in the molten iron is reduced to less than 0.20% by mass, the temperature of the molten iron rises, the decarburization reaction becomes active, and the rate of generation of CO gas gradually increases. Further, the concentration of iron oxide in the slag is relatively low at the initial stage of the deodorization treatment in which the concentration of antimony in the molten iron is low, but the concentration of antimony in the molten iron is lowered as the deodorization reaction proceeds. The amount of slag is increased, and the concentration of iron oxide in the slag is gradually increased.
並且,若爐渣中的氧化鐵的濃度增大而超過10質量%, 則爐渣的低熔點化或液相比率的增大變得顯著,再加上爐內溫度的上升,爐渣的流動性提高。進而,由爐渣中的氧化鐵與熔鐵浴或捲入爐渣中的熔鐵滴的反應引起的CO氣體的產生亦變得活躍,而使爐渣中內包大量的CO氣體氣泡,成為所謂「造渣(slag forming)」的狀態。一旦爐渣開始成型,則由自頂吹噴槍(top-blowing lance)進行送氧獲得的對爐渣層的供氧量亦增加,而促進鐵等的氧化,因此根據噴槍高度等送氧條件,亦存在成型高度加速地增大,而達成所謂「噴濺(slopping)」的情況。 Further, if the concentration of iron oxide in the slag increases by more than 10% by mass, Then, the low melting point of the slag or the increase in the liquid phase ratio becomes remarkable, and the increase in the temperature in the furnace increases the fluidity of the slag. Further, the generation of CO gas by the reaction between the iron oxide in the slag and the molten iron bath or the molten iron droplets involved in the slag is also active, and the slag contains a large amount of CO gas bubbles, which becomes a so-called "made" The state of slag forming. When the slag is started to be formed, the amount of oxygen supplied to the slag layer by the oxygen supplied from the top-blowing lance is also increased, and the oxidation of iron or the like is promoted. Therefore, depending on the oxygen supply conditions such as the height of the lance, there is also The molding height is accelerated to increase, and the so-called "slopping" is achieved.
若可於脫矽爐渣的排渣時控制、維持在該造渣狀態,則 會使爐渣的體積比重非常小,即便為相同的爐渣質量亦可成為約10倍左右的大體積,因此於使爐渣自爐口流出時,可迅速地排出 爐渣而不會使熔鐵流出。然而,若脫矽處理中的造渣過度進行,則有爐渣自爐口溢出而妨礙操作之虞,因此需要注意。 If it can be controlled and maintained in the slagging state when the slag is removed from the slag, then The slag has a very small specific gravity, and even if the same slag quality is about 10 times as large, it can be quickly discharged when the slag flows out from the furnace mouth. The slag does not cause the molten iron to flow out. However, if the slag formation in the untwisting treatment is excessively performed, there is a possibility that the slag overflows from the furnace mouth and hinders the operation, so care is required.
然而,於現有技術中,並未確立控制、維持上述造渣的 方法,或者適當評價成型狀態,適當地判斷自脫矽處理移行至中間排渣的時機的技術。因此,難以穩定地提高中間排渣中的脫矽爐渣的排渣率。 However, in the prior art, it is not established to control and maintain the above-mentioned slagging. The method, or the molding state is appropriately evaluated, and the technique of shifting from the dislocation treatment to the timing of the intermediate slag discharge is appropriately determined. Therefore, it is difficult to stably increase the slag discharge rate of the slag in the intermediate slag.
發明者等人對適當地評價脫矽處理中的爐渣的成型狀 態,而決定結束脫矽處理並開始中間排渣的時機的方法反覆進行努力研究。結果發現,於使用轉爐型精煉爐的脫矽處理中,排出氣體中的碳的排出速度顯示特定的變動圖案,且於該變動圖案的特定範圍內成型狀態變得最適合排渣,並且,結束脫矽處理而開始中間排渣的時機可基於轉爐型精煉爐所附帶的排出氣體處理設備所吸入的吸入氣體(以下亦簡稱為「吸入氣體」)中所含的含有碳原子的氣態物質的濃度分析值而決定,從而達成本發明的開發。 The inventors and the like have appropriately evaluated the molding state of the slag in the dislocation treatment. In the state, the method of determining the timing of ending the dislocation treatment and starting the intermediate slagging is repeatedly studied. As a result, it has been found that in the degassing treatment using the converter type refining furnace, the discharge speed of the carbon in the exhaust gas shows a specific fluctuation pattern, and the molding state becomes the most suitable for slag discharge within a specific range of the variation pattern, and ends. The timing of the slag discharge in the middle of the slag removal process can be based on the concentration of the gaseous substance containing carbon atoms contained in the suction gas (hereinafter also referred to as "inhalation gas") sucked by the exhaust gas treatment equipment attached to the converter type refining furnace. The analysis is performed to determine the development of the present invention.
圖1是將排出氣體中所含的碳的排出速度(每單位時間 排出的排出氣體中所含的碳量)的推移(經時變化)與吸入氣體流量、送氧速度及吸入氣體中的CO氣體濃度與CO2氣體濃度的和的推移一併表示的圖,上述排出氣體中所含的碳的排出速度是基於在脫矽爐渣容易成型的條件下對熔鐵中的矽濃度為0.35質量%的熔鐵進行將矽濃度降低至0.10質量%以下的脫矽處理時的轉爐型精煉爐所附帶的排出氣體處理設備所吸入的吸入氣體中的CO氣體濃度、CO2氣體濃度及吸入氣體流量(標準狀態)而算出。 1 is a transition (change over time) of a discharge rate of carbon contained in an exhaust gas (amount of carbon contained in an exhaust gas discharged per unit time), a flow rate of a suction gas, an oxygen supply rate, and CO in an intake gas. The graph showing the sum of the gas concentration and the CO 2 gas concentration together shows that the discharge speed of the carbon contained in the exhaust gas is based on the concentration of ruthenium in the molten iron under the condition that the slag is easily molded. The molten iron is subjected to a CO gas concentration, a CO 2 gas concentration, and a suction gas flow rate in the suction gas sucked into the exhaust gas treatment equipment attached to the converter type refining furnace at the time of the deuterium concentration reduction of 0.10% by mass or less. Calculated in the standard state).
根據該圖可知,於脫矽爐渣成型的情形時,排出氣體中 所含的碳的排出速度顯示如下特異的變動圖案:於脫矽處理開始 後,隨著脫矽反應的進行,排出氣體中所含的碳的排出速度逐漸上升(階段I),於暫且顯示極大值後減少,而顯示極小值(階段II),其後,再次增大(階段III)。此外,關於上述排出氣體中的碳的排出速度,嚴格而言亦包含排出氣體處理設備所吸入的空氣中所含的CO2,但空氣中的CO2為微量,因此可忽視由此造成的影響。 As can be seen from the figure, in the case of the formation of the slag, the discharge rate of the carbon contained in the exhaust gas shows a specific fluctuation pattern as follows: after the start of the deodorization treatment, the discharge gas is discharged as the degassing reaction proceeds. The discharge rate of the contained carbon gradually rises (stage I), and decreases after temporarily displaying the maximum value, and shows the minimum value (stage II), and then increases again (stage III). Further, regarding the discharge rate of the carbon in the exhaust gas, strictly speaking, the exhaust gas processing device also includes a sucked air contained in the CO 2, CO 2 in the air, but a trace amount, it can ignore the influence of the resulting .
關於排出氣體中的碳的排出速度顯示如上所述的特異 的變動圖案的原因,發明者等人考慮如下。 The discharge speed of carbon in the exhaust gas shows the specificity as described above The reason for the change pattern, the inventors and the like are considered as follows.
首先,階段I是隨著由進行脫矽處理引起的熔鐵溫度的上升及熔鐵中的矽濃度的降低,CO氣體的產生量逐漸上升的階段,脫碳反應開始初期的脫矽爐渣的產生量仍較少,而且溫度低且未成型,因此如圖2(a)所示,CO氣體可容易地通過脫矽爐渣層排出至爐外。然而,若進行脫矽反應而成為階段II,則CO氣體的產生量變多,並且脫矽爐渣的溫度上升,黏性變小,因此如圖2(b)所示,所產生的CO氣體被取入至脫矽爐渣中,引起爐渣的成型,排出氣體中的碳的排出速度於表觀上一次性地減少。若進而進行脫矽反應而成為階段III,則變得無法於脫矽爐渣中取入其以上的CO氣體,成型達到飽和狀態,因此如圖2(c)所示,CO氣體被排出至爐外,排出氣體中的碳的排出速度再次開始上升。 First, the stage I is a stage in which the amount of CO gas is gradually increased as the temperature of the molten iron rises due to the deodorization treatment and the concentration of rhodium in the molten iron is lowered, and the generation of the decarburization slag at the initial stage of the decarburization reaction is generated. The amount is still small, and the temperature is low and unformed, so as shown in Fig. 2(a), the CO gas can be easily discharged to the outside of the furnace through the slag layer. However, when the deuteration reaction is carried out and the phase II is obtained, the amount of CO gas generated is increased, and the temperature of the desulfurization slag is increased, and the viscosity is reduced. Therefore, as shown in Fig. 2(b), the generated CO gas is taken. The slag is formed in the slag, and the discharge rate of carbon in the exhaust gas is reduced by an apparent one-time. When the phase III is further removed by the deoximation reaction, the CO gas above the slag can not be taken in, and the molding is saturated. Therefore, as shown in Fig. 2(c), the CO gas is discharged to the outside of the furnace. The discharge rate of carbon in the exhaust gas starts to rise again.
另外,可認為排出氣體中的碳的排出速度的變動圖案亦 與如下的現象有關。 In addition, it can be considered that the variation pattern of the discharge speed of carbon in the exhaust gas is also It is related to the following phenomenon.
於脫矽處理的階段I中,自頂吹噴槍供給的氧主要消耗於脫矽反應及脫碳反應,但若成為階段II,則產生的爐渣量增大,爐渣層的厚度增大,並且爐渣中的氧化鐵濃度上升,所供給的氧亦 消耗於鐵的氧化反應,因此脫碳中使用的氧相應地減少,排出氣體中的碳的排出速度降低。尤其是,若爐渣開始成型,爐渣層的厚度變大,則由自頂吹噴槍進行送氧獲得的對爐渣層的供氧量加速地增加,氧化鐵濃度上升。其次,若成為階段III,則藉由爐渣中的氧化鐵與熔鐵的反應而產生CO氣體,並且爐渣中的氧化鐵相應地減少,爐渣中的氧化鐵成為收支平衡的狀態,因此CO氣體的產生速度再次增大,排出氣體中的碳的排出速度開始上升。 In the stage I of the deodorization treatment, the oxygen supplied from the top blowing lance is mainly consumed in the deodorization reaction and the decarburization reaction, but if it is in the stage II, the amount of generated slag increases, the thickness of the slag layer increases, and the slag The concentration of iron oxide in the rise increases, and the oxygen supplied Since the oxidation reaction of iron is consumed, the oxygen used for decarburization is correspondingly reduced, and the discharge rate of carbon in the exhaust gas is lowered. In particular, when the slag is started to be formed and the thickness of the slag layer is increased, the amount of oxygen supplied to the slag layer obtained by oxygen supply from the top blowing lance is accelerated, and the concentration of iron oxide is increased. Next, in the case of the stage III, CO gas is generated by the reaction of iron oxide and molten iron in the slag, and the iron oxide in the slag is correspondingly reduced, and the iron oxide in the slag is in a state of balance, so CO gas The rate of generation increases again, and the rate of carbon discharge in the exhaust gas begins to rise.
根據以上探討可知,排出氣體中的碳的排出速度自極大 值變為極小值,並自極小值再次增大,若於脫矽爐渣處於成型狀態的上述階段III的階段結束脫矽處理而開始中間排渣,則可確實地提高脫矽爐渣的排渣率。另外確認,該階段的熔鐵中的矽濃度穩定地降低至可於接下來進行的脫磷處理中減少脫磷精煉劑的使用量而有效率地進行脫磷的0.10質量%以下。 According to the above discussion, the discharge rate of carbon in the exhaust gas is extremely large. The value becomes a minimum value and increases again from the minimum value. If the deodorization treatment is completed at the stage of the above-mentioned stage III in which the slag is in the molding state, and the intermediate slag is started, the slag discharge rate of the slag can be surely increased. . In addition, it is confirmed that the cerium concentration in the molten iron in this stage is steadily lowered to 0.10 mass% or less which can be efficiently dephosphorized by reducing the amount of the dephosphorization refining agent used in the subsequent dephosphorization treatment.
進而,發明者等人發現,於在上述階段III的特定區域、 具體為相對於排出氣體中的碳的排出速度的極大值為90%以上且150%以下的範圍內結束脫矽處理的情形時,可進一步提高脫矽爐渣的排渣率。 Further, the inventors found that in the specific region of the above stage III, Specifically, when the maximum value of the discharge speed of carbon in the exhaust gas is 90% or more and 150% or less, the slag removal rate of the slag can be further increased.
其原因可認為如下,如上述所說明般,藉由進行脫碳反應,脫矽爐渣的溫度上升,黏性降低,而使流動性提高,而且藉由成型,脫矽爐渣的比重於表觀上變小,因此熔鐵浴上的爐渣層的高度(厚度)增大而變得容易自爐口流出。於排出氣體中的碳的排出速度相對於上述極大值不足90%而結束脫矽處理的情形時,有爐渣的成型不充分,脫矽爐渣的排渣率亦變得不充分的情況。另一方面,於相對於上述極大值超過150%而結束脫矽處理的情形 時,有於結束脫矽處理前爐渣自爐口溢出而妨礙操作之虞。 The reason for this is considered to be as follows. As described above, by performing the decarburization reaction, the temperature of the slag is increased, the viscosity is lowered, and the fluidity is improved, and the specific gravity of the slag is apparently formed by molding. As the size becomes smaller, the height (thickness) of the slag layer on the molten iron bath increases and it becomes easy to flow out from the furnace mouth. When the discharge rate of the carbon in the exhaust gas is less than 90% with respect to the maximum value, the slag is insufficiently formed, and the slag discharge rate of the slag is also insufficient. On the other hand, the case where the dislocation treatment is ended with respect to the above maximum value exceeding 150% At the time, there is a problem that the slag overflows from the furnace mouth before the end of the dislocation treatment and hinders the operation.
本發明是基於如上所述的新穎見解進行開發而成,其特 徵在於:其是向轉爐型精煉爐內的熔鐵供給氧源進行脫矽處理後,將存在於爐內的爐渣的至少一部分自轉爐型精煉爐排出(中間排渣),其後,向轉爐型精煉爐內的熔鐵供給CaO系助熔劑及氧源進行脫磷處理而流出的熔鐵的預備處理方法,且對上述脫矽處理中的轉爐型精煉爐的排出氣體處理設備所吸入的吸入氣體中的含有碳原子的氣態物質的濃度進行分析,基於其分析值決定脫矽處理的結束時間點。 The present invention has been developed based on the novel findings described above, The method is: after the desulfurization treatment is performed on the molten iron supply source in the converter type refining furnace, at least a part of the slag present in the furnace is discharged from the converter type refining furnace (intermediate slag discharge), and thereafter, to the converter The molten iron in the refining furnace is supplied with a CaO-based flux and an oxygen source to perform dephosphorization treatment, and the molten iron is discharged, and the inhalation is taken in the exhaust gas treatment equipment of the converter type refining furnace in the above-described deodorization treatment. The concentration of the gaseous substance containing carbon atoms in the gas is analyzed, and the end time of the dislocation treatment is determined based on the analysis value.
上述本發明的熔鐵的預備處理方法使用如圖3所示的可 進行頂吹及底吹的轉爐型精煉爐1。頂吹是經由可於轉爐型精煉爐1的內部升降的頂吹噴槍2,自該頂吹噴槍2的前端向熔鐵5供給作為氧源的含氧氣體9而進行。上述含氧氣體9可使用氧氣(工業用純氧)、富氧空氣、空氣、氧氣與惰性氣體的混合氣體等。 The method for preparing the molten iron of the present invention described above is as shown in FIG. A converter type refining furnace 1 for top blowing and bottom blowing. The top blowing is performed by supplying the oxygen-containing gas 9 as an oxygen source from the tip end of the top blowing lance 2 to the molten iron 5 via the top blowing lance 2 that can be raised and lowered inside the converter type refining furnace 1. As the oxygen-containing gas 9, oxygen (industrial pure oxygen), oxygen-enriched air, air, a mixed gas of oxygen and an inert gas, or the like can be used.
另一方面,底吹是藉由經由設置於轉爐型精煉爐1的底 部的底吹風口(bottom-blowing tuyere)3,向熔鐵中吹入底吹氣體10而進行。上述底吹氣體10可為含有氧氣的氣體,亦可僅為氬氣或氮氣等惰性氣體。底吹氣體10具有藉由吹入至熔鐵中而促進熔鐵5的攪拌從而促進冷鐵源的熔解的功能,亦可具有自底吹風口3將造渣劑吹入至熔鐵中的作為搬送用氣體的功能。 On the other hand, the bottom blowing is performed by passing through the bottom of the converter type refining furnace 1 The bottom-blowing tuyere 3 is blown into the molten iron by the bottom blowing gas 10. The bottom blowing gas 10 may be a gas containing oxygen or an inert gas such as argon or nitrogen. The bottom blowing gas 10 has a function of promoting the stirring of the molten iron 5 by blowing into the molten iron to promote melting of the cold iron source, and may also have a function of blowing the slag forming agent into the molten iron from the bottom blowing port 3. The function of the gas for transportation.
另外,於轉爐型精煉爐1的上方設置有進行升降而覆蓋轉爐型精煉爐1的爐口的裙罩(skirt)11及與其連接的煙道12。自轉爐型精煉爐1排出的排出氣體是經由煙道12,藉由未圖示的排出氣體處理設備吸入,灑水並除塵後,測定吸入速度。於排出 氣體處理設備具有回收所吸入的吸入氣體作為燃料氣體的功能的情形時,吸入氣體根據組成或流量可回收為燃料氣體或進行放散,但於脫矽處理中,由於CO氣體的產生速度低,故而通常不回收為燃料氣體。此處,於利用未圖示的排出氣體處理設備吸入的吸入氣體中,除了自轉爐型精煉爐1排出的排出氣體以外,亦包含根據裙罩11內的與大氣壓的差壓、及轉爐型精煉爐1與裙罩11的間隔的大小(以下亦稱為「裙罩高度」)而吸入的空氣(大氣)。 Further, a skirt 11 for lifting and covering the mouth of the converter type refining furnace 1 and a flue 12 connected thereto are provided above the converter type refining furnace 1. The exhaust gas discharged from the converter type refining furnace 1 is sucked through the flue 12 by an exhaust gas treatment device (not shown), and is sprinkled with water to remove the dust, and then the suction speed is measured. Exhaust When the gas processing apparatus has a function of recovering the sucked inhaled gas as a fuel gas, the inhaled gas can be recovered as a fuel gas or discharged according to the composition or the flow rate, but in the dislocation treatment, since the CO gas is generated at a low speed, Usually not recycled as fuel gas. Here, in addition to the exhaust gas discharged from the converter type refining furnace 1, the intake gas sucked by the exhaust gas treatment equipment (not shown) includes a differential pressure from the atmospheric pressure in the skirt 11 and a converter type refining. Air (atmosphere) that is inhaled by the size of the gap between the furnace 1 and the skirt 11 (hereinafter also referred to as "skirt height").
與高溫的排出氣體一併被吸入至裙罩內的空氣中的氧與排出氣體中的CO進行反應而產生CO2直至氧與CO中任一者實質上耗盡為止。煙道12設置有採取分析用吸入氣體的氣體採取探針13,且與該氣體採取探針13連接而設置有對利用氣體採取探針13採取的吸入氣體中的CO、CO2、O2等氣體組成進行分析的氣體分析裝置14。即,以如下方式構成:藉由氣體分析裝置14連續或間斷地對利用氣體採取探針13採取的吸入氣體的氣體組成進行測定。此外,亦有於煙道12等高溫氣體通過的部分設置蒸氣鍋爐的情況。 The oxygen in the air sucked into the skirt together with the high-temperature exhaust gas reacts with the CO in the exhaust gas to generate CO 2 until substantially any of oxygen and CO is exhausted. The flue 12 is provided with a gas take-up probe 13 for taking in the analysis inhalation gas, and is connected to the gas-taking probe 13 to provide CO, CO 2 , O 2 , etc. in the intake gas taken by the probe 13 by the gas. The gas composition is analyzed by a gas analysis device 14. That is, it is configured such that the gas composition of the suction gas taken by the gas taking probe 13 is continuously or intermittently measured by the gas analyzer 14 . Further, there is a case where a steam boiler is provided in a portion through which a high temperature gas such as the flue 12 passes.
於利用排出氣體處理設備回收高溫的排出氣體作為燃料氣體的情形時,排出氣體處理設備的運轉通常是儘量降低裙罩高度而儘可能減少所吸入的空氣。然而,由於脫矽處理時的CO氣體的產生速度小(產生量少),故而通常不進行作為燃料氣體的回收,因此裙罩高度可任意地設定。因此,例如於煙道12具有蒸氣鍋爐的功能的情形時,理想的是使裙罩11上升而積極地吸入空氣,藉此使排出氣體中的CO氣體燃燒,回收其燃燒熱(熱能)作為高壓的蒸氣。另一方面,於煙道12不具有蒸氣鍋爐的功能的情 形時,為了抑制空氣的吸入,亦可降低裙罩11的位置而使排出氣體處理設備運轉,藉此可減輕煙道12等的熱負荷。 In the case where the exhaust gas treatment apparatus recovers the high-temperature exhaust gas as the fuel gas, the operation of the exhaust gas treatment apparatus is generally to minimize the height of the skirt and to minimize the air taken in. However, since the rate of generation of CO gas during the deodorization treatment is small (the amount of generation is small), recovery of the fuel gas is not normally performed, and thus the height of the skirt can be arbitrarily set. Therefore, for example, when the flue 12 has the function of a steam boiler, it is desirable to raise the skirt 11 to actively suck in air, thereby burning the CO gas in the exhaust gas, and recovering the heat of combustion (thermal energy) as a high pressure. Vapor. On the other hand, the flue 12 does not have the function of a steam boiler. In order to suppress the suction of air, the position of the skirt 11 can be lowered to operate the exhaust gas processing apparatus, whereby the heat load of the flue 12 or the like can be reduced.
排出氣體處理設備所吸入的吸入氣體的成分組成根據排出氣體處理設備的特徵或其運轉條件而完全不同。即,於降低裙罩11的位置而抑制空氣的吸入量的情形時,CO及CO2的濃度相對較高,於使裙罩11上升而積極地吸入空氣的情形時,若來自轉爐型精煉爐1的CO氣體的產生速度相對於排出氣體處理設備的氣體吸入速度並非為某程度的比率以上(具體約為30vol%以上),則吸入氣體的分析中僅檢測到CO2,未檢測到CO。其原因在於,排出氣體中的CO因所吸入的空氣中的O2而燃燒。另外,吸入氣體中的CO及CO2的濃度由於經N2稀釋,故而相對較低。另外,圖1表示使用具有氣體回收功能但煙道不包含蒸氣鍋爐的排出氣體處理設備,於脫矽處理開始後確認排出氣體的著火後,進行降低裙罩11而抑制空氣的吸入的操作的例子。 The composition of the intake gas taken in by the exhaust gas treatment device is completely different depending on the characteristics of the exhaust gas treatment device or its operating conditions. In other words, when the position of the skirt 11 is lowered and the amount of intake of air is suppressed, the concentration of CO and CO 2 is relatively high, and when the skirt 11 is raised and the air is actively taken in, it is from a converter type refining furnace. The rate of generation of the CO gas of 1 is not more than a certain ratio (specifically, about 30 vol% or more) with respect to the gas suction rate of the exhaust gas treatment equipment, and only CO 2 is detected in the analysis of the intake gas, and CO is not detected. The reason for this is that CO in the exhaust gas is burned by O 2 in the air taken in. Further, the concentration of CO and CO 2 in the inhaled gas is relatively low due to dilution with N 2 . In addition, FIG. 1 shows an example of an operation of reducing the skirt 11 and suppressing the inhalation of air after confirming the ignition of the exhaust gas after the start of the dislocation process using the exhaust gas treatment device having the gas recovery function but not including the steam boiler. .
另外,上述圖1所示的排出氣體中的碳的排出速度是基於利用圖3所示的配設於通至轉爐排出氣體處理設備的煙道的氣體採取探針13測得的吸入氣體中的CO氣體濃度、CO2氣體濃度及排出氣體處理設備的氣體吸入速度(標準狀態下的吸入氣體流量)而算出。CO、CO2的氣體組成的測定通常使用紅外線吸收式的分析計,但該測定法與氣體流量的測定相比,應答速度緩慢,產生十秒~數十秒左右的延遲時間,因此對各測定時間施加修正。另外,為了防止排出氣體的洩漏,故而排出氣體處理設備中的氣體吸入量大於脫矽處理或脫碳處理中自轉爐型精煉爐產生的氣體量,因此自爐口與裙罩之間吸入空氣,使所產生的CO的至少 一部分進行氧化而變成CO2。 Further, the discharge speed of carbon in the exhaust gas shown in FIG. 1 described above is based on the intake gas measured by the gas take-up probe 13 disposed in the flue of the exhaust gas treatment device shown in FIG. The CO gas concentration, the CO 2 gas concentration, and the gas suction speed of the exhaust gas treatment equipment (the intake gas flow rate in the standard state) were calculated. In the measurement of the gas composition of CO and CO 2 , an infrared absorption type analyzer is usually used. However, compared with the measurement of the gas flow rate, the measurement method is slow in response speed, and a delay time of about 10 seconds to several tens of seconds is generated. Time is applied to the correction. Further, in order to prevent leakage of the exhaust gas, the amount of gas suction in the exhaust gas treatment device is larger than the amount of gas generated in the spinner type refining furnace in the decarburization treatment or the decarburization treatment, so that air is taken in from the furnace mouth and the skirt. At least a portion of the produced CO is oxidized to become CO 2 .
因此,為了決定脫矽處理的結束時間點,以下方法有 效:藉由測定吸入氣體中的CO濃度及CO2濃度、與排出氣體處理設備的吸入速度(標準狀態的流量)而求出排出氣體中的碳的排出速度。然而,根據發明者等人的實驗結果,只要轉爐排出氣體處理設備的操作條件(裙罩高度、爐口壓力等)固定,則亦可代替排出氣體中的碳的排出速度,而根據吸入氣體中的CO氣體濃度、CO2氣體濃度、及CO氣體與CO2氣體的合計濃度中的任一濃度成為極大值,成為極小值後再次增大的變動圖案,決定脫矽處理結束的時間點。此時,若為所吸入的空氣量相對較少,CO殘留於吸入氣體中的操作條件,則可基於CO氣體與CO2氣體的合計濃度的變動圖案而決定脫矽處理結束的時間點,於所吸入的空氣量幾乎未有變動而CO2氣體濃度穩定的情形時,亦可基於僅CO氣體濃度的變動圖案而決定脫矽處理結束的時間點。另外,若為所吸入的空氣量足夠大,排出氣體中的CO完全燃燒的操作條件,則亦可基於僅CO2氣體濃度的變動圖案而決定脫矽處理結束的時間點。 Therefore, in order to determine the end time of the dislocation treatment, the following method is effective: the exhaust gas is obtained by measuring the CO concentration and the CO 2 concentration in the inhaled gas, and the suction speed of the exhaust gas treatment equipment (flow rate in the standard state). The rate of carbon discharge. However, according to the experimental results of the inventors and the like, as long as the operating conditions (skirt height, mouth pressure, etc.) of the converter exhaust gas treatment apparatus are fixed, the discharge speed of carbon in the exhaust gas can be replaced instead of the inhaled gas. Any one of the CO gas concentration, the CO 2 gas concentration, and the total concentration of the CO gas and the CO 2 gas becomes a maximum value, and the fluctuation pattern which is increased again after the minimum value is determined, and the time point at which the dislocation process is completed is determined. In this case, if the amount of air to be inhaled is relatively small and the operating conditions of the CO remaining in the inhaled gas are determined, the time point at which the dislocation process is completed can be determined based on the variation pattern of the total concentration of the CO gas and the CO 2 gas. When the amount of air to be sucked hardly changes and the CO 2 gas concentration is stable, the time point at which the dislocation process is completed may be determined based on the fluctuation pattern of only the CO gas concentration. Further, if the amount of air to be sucked is sufficiently large, and the operating conditions in which the CO in the exhaust gas is completely combusted, the time point at which the dislocation process is completed may be determined based on the fluctuation pattern of only the CO 2 gas concentration.
進而,亦可代替排出氣體中的碳的排出速度,而根據由 吸入氣體中的CO氣體濃度及/或CO2氣體濃度的分析值與吸入氣體的流量的乘積算出的變動圖案,而決定脫矽處理結束的時間點。上述變動圖案為吸入氣體中的CO氣體流量、CO2氣體流量、及CO氣體與CO2氣體的合計流量中的任一流量成為極大值,成為極小值後再次增大的變動圖案。此時,若為所吸入的空氣量相對較少,CO殘留於吸入氣體中的操作條件,則可基於CO氣體與 CO2氣體的合計流量的變動圖案而決定脫矽處理結束的時間點,於所吸入的空氣量幾乎未有變動而CO2氣體流量穩定的情形時,亦可基於僅CO氣體流量的變動圖案而決定脫矽處理結束的時間點。另外,若為所吸入的空氣量足夠大,排出氣體中的CO完全燃燒的操作條件,則亦可基於僅CO2氣體流量的變動圖案而決定脫矽處理結束的時間點。 Further, instead of the discharge speed of carbon in the exhaust gas, the flicker is determined based on the fluctuation pattern calculated from the product of the CO gas concentration and/or the CO 2 gas concentration in the inhaled gas and the flow rate of the inhaled gas. The point in time at which the processing ends. The fluctuation pattern is a fluctuation pattern in which the flow rate of the CO gas in the intake gas, the flow rate of the CO 2 gas, and the total flow rate of the CO gas and the CO 2 gas become maximum values, and becomes a minimum value and then increases again. In this case, if the amount of air to be sucked is relatively small and the operating conditions of the CO remaining in the intake gas are determined, the time point at which the dislocation process is completed can be determined based on the fluctuation pattern of the total flow rate of the CO gas and the CO 2 gas. When the amount of air to be sucked hardly changes and the flow rate of the CO 2 gas is stable, the time point at which the dislocation process is completed may be determined based on the fluctuation pattern of the flow rate of only the CO gas. Further, if the amount of air to be sucked is sufficiently large, and the operating conditions in which the CO in the exhaust gas is completely combusted, the time point at which the dislocation process is completed may be determined based on the fluctuation pattern of the flow rate of only the CO 2 gas.
另外,吸入氣體流量隨著脫矽處理前後進行的裙罩高度 的調節而大幅度變化(參照圖1),如上所述,於吸入氣體流量的測定及氣體組成的分析時,由於應答速度不同,因此若吸入氣體流量有大的變動,則於測定排出氣體中的碳的排出速度的變化時成為產生誤差的原因。因此,於判定上述極大值及極小值時,理想的是以不會對極大值及極小值產生前後的吸入氣體流量帶來大幅度變動的方式進行操作。裙罩高度通常以將氣體的吸入壓力保持一定的方式進行控制,或以將裙罩高度保持一定的方式進行控制,於該些情形時,吸入氣體流量的變動成為對判定極大值及極小值而言不成問題的等級(level)。 In addition, the suction gas flow rate is the height of the skirt before and after the dislocation treatment As a result of the adjustment and the large change (see Fig. 1), as described above, in the measurement of the flow rate of the suction gas and the analysis of the gas composition, since the response speed is different, if the flow rate of the suction gas greatly changes, the exhaust gas is measured. The change in the carbon discharge rate becomes a cause of error. Therefore, when determining the maximum value and the minimum value, it is preferable to operate so as not to greatly vary the flow rate of the intake gas before and after the maximum value and the minimum value. The height of the skirt is usually controlled in such a manner that the suction pressure of the gas is kept constant, or is controlled in such a manner that the height of the skirt is kept constant. In these cases, the fluctuation of the flow rate of the suction gas becomes a maximum value and a minimum value. The level is not a problem.
如上所述,可基於排出氣體中的碳的排出速度或吸入氣 體中的CO氣體濃度、CO2氣體濃度、CO氣體與CO2氣體的合計濃度、CO氣體流量、CO2氣體流量、及CO氣體與CO2氣體的合計流量中的任一測定值成為極大值,成為極小值後再次增大的變動圖案,而決定脫矽處理的結束時間點,於極大值與極小值的差為極大值的10%以上的情形時,理想的是判定為上述變動圖案中的極大值及極小值。其原因在於,若上述差不足10%,則有將由吸入氣體流量的變動等引起的微小變動誤認為與上述爐渣的成型 現象相關的變動圖案之虞,因此忽視微小的變動而確實地防止誤檢測。此外,於上述測定值的極大值與極小值的差不足極大值的10%的情形時,理想的是不識別為上述變動圖案中的極大值及極小值而進行忽視,繼續監視測定值的變動直至極大值與極小值的差成為極大值的10%的變動圖案出現為止。 As described above, it may be based on the discharge speed of carbon in the exhaust gas or the CO gas concentration in the suction gas, the CO 2 gas concentration, the total concentration of the CO gas and the CO 2 gas, the CO gas flow rate, the CO 2 gas flow rate, and the CO gas. When any of the measured values of the total flow rate of the CO 2 gas is a maximum value and becomes a minimum value and then increases again, the end time of the dislocation process is determined, and the difference between the maximum value and the minimum value is a maximum value. In the case of 10% or more, it is preferable to determine the maximum value and the minimum value in the above-described variation pattern. The reason is that if the difference is less than 10%, a slight variation caused by fluctuations in the flow rate of the intake gas or the like is mistaken for the variation pattern related to the molding phenomenon of the slag, and therefore, slight fluctuations are ignored to reliably prevent erroneous detection. . Further, when the difference between the maximum value and the minimum value of the measured value is less than 10% of the maximum value, it is preferable to ignore the maximum value and the minimum value in the fluctuation pattern, and to continue monitoring the fluctuation of the measured value. The variation pattern until the maximum value and the minimum value become 10% of the maximum value appears.
另外,脫矽處理的結束時間點理想的是以上述成為極小 值後再次增大的變動值相對於上述極大值成為90%以上且150%以下的規定比率的值以上的時間點為基準,設為規定的經過時間範圍內。將相對於極大值為上述範圍的規定比率的值設為閾值的原因在於,上述變動圖案中成為極小值後再次增大的區域是進行脫矽爐渣的成型而使爐內的爐渣高度急劇增大的區域,相對於極大值不足90%的區域由於造渣不充分,故而有脫矽爐渣的排渣率變得不充分之虞,另一方面,超過150%的區域有於結束脫矽處理前爐渣自爐口溢出而妨礙操作之虞。另外,脫矽處理的結束時間點只要可設為上述變動值成為閾值以上的時間點本身即可,即便設為自該時間點經過必要的操作等作業或裝置的作動所需的數十秒左右後,實際上亦不會產生障礙。上述經過時間理想的是設為0秒~50秒的範圍內,更理想的是設為0秒~30秒的範圍內。若為上述時間的範圍內,則可結束脫矽處理而充分地進行中間排渣,而不會過度進行成型而妨礙操作。 In addition, the end time of the dislocation treatment is desirably such that it becomes extremely small as described above. The fluctuation value that is increased again after the value is within a predetermined elapsed time range based on the time point at which the maximum value is equal to or greater than the value of the predetermined ratio of 90% or more and 150% or less. The reason why the value of the predetermined ratio with respect to the maximum value is the threshold value is that the region which is increased again after the minimum value of the fluctuation pattern is formed by the formation of the slag, and the slag height in the furnace is sharply increased. In the region where the maximum value is less than 90%, the slag discharge rate is insufficient due to insufficient slag formation, and on the other hand, more than 150% of the area is before the end of the dislocation treatment. The slag overflows from the furnace mouth and hinders the operation. In addition, the time point of the completion of the dislocation process may be a time point itself in which the fluctuation value is equal to or greater than the threshold value, and it may be several tens of seconds required for the operation or the operation of the device to be performed from the time point. After that, there will actually be no obstacles. The above elapsed time is preferably set in the range of 0 second to 50 seconds, and more preferably in the range of 0 second to 30 seconds. If it is in the range of the above-mentioned time, the deodorization treatment can be completed, and the intermediate slag discharge can be sufficiently performed without excessively molding and hindering the operation.
此外,以上述方式決定的脫矽處理的結束時間點可設為 上述任一測定值相對於極大值成為規定比率的值以上的時間點,亦可設為自該時間點經過規定的處理時間的時間點。然而,於後者的情形時,理想的是設定為於上述任一測定值相對於極大值不 超過150%的時間點內結束脫矽處理。 In addition, the end time point of the dislocation process determined in the above manner can be set to The time point at which any of the above-described measured values is equal to or greater than the value at which the maximum value is a predetermined ratio may be a time point at which a predetermined processing time elapses from the time point. However, in the latter case, it is desirable to set it to any of the above measured values relative to the maximum value. The dislocation treatment was terminated at a time point of more than 150%.
進而,決定脫矽處理的結束時間點的方法除了如上所述 的基於變動圖案而決定的方法以外,如下方法亦有效:以排出氣體中的碳的排出速度或吸入氣體中的CO氣體濃度、CO2氣體濃度、CO氣體與CO2氣體的合計濃度、CO氣體流量、CO2氣體流量、及CO氣體與CO2氣體的合計流量中的任一測定值成為規定閾值以上的時間點為基準,設為規定的經過時間範圍內。此處,上述測定值成為閾值以上的時間點至脫矽處理的結束時間點為止的經過時間與上述同樣,理想的是設為0秒~50秒的範圍內,更理想的是設為0秒~30秒的範圍內。 Further, in addition to the method determined based on the fluctuation pattern as described above, the method of determining the end time of the dislocation treatment is also effective as follows: the discharge rate of carbon in the exhaust gas or the concentration of CO gas in the inhaled gas, CO 2, based on the time point at which the gas concentration, the total concentration of the CO gas and the CO 2 gas, the CO gas flow rate, the CO 2 gas flow rate, and the total flow rate of the CO gas and the CO 2 gas are equal to or greater than a predetermined threshold value, For the specified elapsed time range. Here, the elapsed time from the time when the measured value is equal to or greater than the threshold value to the end time of the dislocation processing is preferably in the range of 0 second to 50 seconds, and more preferably set to 0 second. Within the range of ~30 seconds.
其中,於該些方法的情形時,必須於脫矽處理的中間階 段、例如圖1所示的碳排出速度的變動圖案上觀察到的極大值的部分,不識別為上述測定值成為閾值以上。為此,理想的是於結束供給根據脫矽處理前的熔鐵中的Si濃度與作為目標的脫矽處理後的熔鐵中的Si濃度計算而得的化學計量上必需的氧量的1.2倍、理想的是1.5倍的氧的時間點之後,設為上述測定值成為規定閾值以上的時間點。另外,上述閾值可為根據經驗求出的數值,亦可為例如使用熔鐵溫度或熔鐵中的Si濃度等變數進行計算而得的值,較佳為考慮中間排渣時的排渣狀況或其後的脫磷處理的實際成績而決定。 Among them, in the case of these methods, it must be in the middle of the dislocation process. The portion of the segment, for example, the maximum value observed on the fluctuation pattern of the carbon discharge rate shown in Fig. 1, is not recognized as the above-described measured value being equal to or greater than the threshold value. For this reason, it is desirable to end the supply of 1.2 times the amount of stoichiometrically necessary oxygen calculated from the Si concentration in the molten iron before the deodorization treatment and the Si concentration in the molten iron after the target deodorization treatment. Preferably, after the time point of 1.5 times of oxygen, the time when the measured value is equal to or greater than a predetermined threshold value is set. Further, the threshold value may be a value obtained empirically, and may be a value calculated by using a variable such as a molten iron temperature or a Si concentration in the molten iron, and is preferably a slagging condition in consideration of intermediate slag discharge or It is determined by the actual results of the subsequent dephosphorization treatment.
此處,於排出氣體處理設備具有回收轉爐型精煉爐的排 出氣體作為燃料氣體的功能、及包含蒸氣鍋爐的煙道,且以於脫矽處理中積極地吸入大氣而使排出氣體中的CO氣體的至少一部分燃燒的方式使排出氣體處理設備運轉的情形時,對於調查基於 上述所說明的閾值決定脫矽處理的結束時間點時、具體為基於吸入氣體中的CO氣體濃度決定脫矽處理的結束時間點時的脫矽爐渣的排渣性的例子進行以下說明。 Here, the exhaust gas treatment equipment has a row of a recovery converter type refining furnace When the gas is used as the fuel gas and the flue gas is included in the exhaust gas, and the exhaust gas processing equipment is operated such that at least a part of the CO gas in the exhaust gas is actively burned in the degassing process. For survey based When the threshold value described above determines the end time of the dislocation process, specifically, the slag discharge property of the slag is determined based on the CO gas concentration in the intake gas at the end time of the dislocation process.
於該例子中,脫矽爐渣的排渣性是在使脫矽處理前的熔 鐵中的矽濃度及所產生的脫矽爐渣的質量大致固定,且使排渣時的轉爐型精煉爐的傾動角度固定的條件下,基於自轉爐型精煉爐排出的脫矽爐渣的量進行評價。具體而言,將排出至在轉爐型精煉爐的正下方受渣的受渣容器中的脫矽爐渣的質量為存在於爐內的脫矽爐渣的質量的50%以上的情況評價為「排渣優良」,將上述值為30%以上且不足50%的情況評價為「排渣良好」,將上述值不足30%的情況評價為「排渣不良」。 In this example, the slagging property of the slag slag is melted before the dislocation treatment The concentration of bismuth in the iron and the mass of the slag slag generated are substantially fixed, and the amount of the slag slag discharged from the converter type refining furnace is evaluated under the condition that the tilting angle of the converter type refining furnace at the time of slag removal is fixed. . Specifically, the mass of the slag slag which is discharged to the slag receiving container which is directly under the converter-type refining furnace is 50% or more of the mass of the slag slag which is present in the furnace, and is evaluated as "slag discharge". In the case where the above value is 30% or more and less than 50%, the case where the above value is less than 30% is evaluated as "poor slag discharge".
圖4表示上述調查結果。根據該圖可知,脫矽處理結束 時的吸入氣體中的CO氣體濃度越高,脫矽爐渣的排渣性越提高,另外,脫矽處理結束時的吸入氣體中的CO氣體濃度為6.0vol%以上時,不會產生「排渣不良」。即,可知較佳為可基於脫矽處理中的吸入氣體中的CO氣體濃度決定脫矽處理的結束;以及於該情形時,將吸入氣體中的CO氣體濃度為6.0vol%以上的值設為決定脫矽處理的結束時間點的閾值。 Figure 4 shows the results of the above investigation. According to the figure, the dislocation process ends. The higher the concentration of the CO gas in the inhaled gas, the higher the slag discharge property of the slag, and the slag discharge does not occur when the CO gas concentration in the suction gas at the end of the devolatilization treatment is 6.0 vol% or more. bad". In other words, it is preferable that the end of the dislocation treatment can be determined based on the CO gas concentration in the inhalation gas in the deodorization treatment, and in this case, the value of the CO gas concentration in the inhaled gas is set to 6.0 vol% or more. Determine the threshold for the end time of the dislocation process.
此外,轉爐型精煉爐等精煉爐是以批次式對爐內的熔鐵 或熔鋼實施精煉,將該一個單位的精煉稱為「爐次」,圖4中的爐次數表示其次數。另外,於脫矽處理中,由於排出氣體的產生量少,故而藉由自轉爐型精煉爐的爐口與裙罩之間所吸入的空氣使吸入氣體中的CO氣體濃度發生變化,上述吸入氣體中的「CO氣體濃度為6.0vol%以上」的閾值是於使操作條件(送氧量、裙罩 高度、爐口壓力等)固定的操作條件下獲得。因此,只要為該條件下,則可作為閾值充分地使用。 In addition, the refining furnace such as the converter type refining furnace is a batch type of molten iron in the furnace. Or the refining of the molten steel, the refining of one unit is referred to as "heating", and the number of furnaces in Fig. 4 indicates the number of times. Further, in the untwisting treatment, since the amount of generated exhaust gas is small, the concentration of CO gas in the suction gas is changed by the air taken in between the furnace mouth of the converter type refining furnace and the skirt, and the suction gas is changed. The threshold value of "CO gas concentration is 6.0 vol% or more" is to make the operating conditions (oxygen supply amount, skirt) Height, mouth pressure, etc.) Obtained under fixed operating conditions. Therefore, as long as it is under this condition, it can be fully used as a threshold.
進而,作為上述閾值而適合的值亦根據排出氣體處理設 備的吸入能力等設備條件或氧供給速度等操作條件而不同。於排出氣體處理設備具有回收轉爐型精煉爐的排出氣體作為燃料氣體的功能,且於脫矽處理中積極地吸入空氣而使排出氣體中的CO燃燒的情形時,決定脫矽處理的結束時間點的閾值較佳為於吸入氣體中的CO氣體濃度為2.0vol%以上且18.0vol%以下的範圍內,根據中間排渣時的排渣率或排渣時間的實際成績有經驗地選定適當的值而使用。若CO氣體濃度的閾值為2.0vol%以上,則即便僅使用CO氣體濃度的測定值代替上述排出氣體中的碳的排出速度的變動圖案,亦可減少判定爐渣的成型得到充分促進時的誤識別,另一方面,若CO氣體濃度的閾值為18.0vol%以下,則可防止因爐渣的過度成型而妨礙操作,且精度良好地判定用於有效率地進行排渣的成型狀態。 Further, a value suitable as the threshold value is also set according to the exhaust gas treatment The operating conditions such as the inhalation capacity and the operating conditions such as the oxygen supply rate differ. The exhaust gas treatment device has a function of recovering the exhaust gas of the converter type refining furnace as a fuel gas, and when the air is actively sucked in the deodorization treatment to burn the CO in the exhaust gas, the end time of the dislocation process is determined. The threshold value is preferably such that the concentration of the CO gas in the inhaled gas is in the range of 2.0 vol% or more and 18.0 vol% or less, and the appropriate value is empirically selected based on the actual results of the slagging rate or the slag discharge time during the intermediate slag discharge. And use. When the threshold value of the CO gas concentration is 2.0 vol% or more, even if only the measured value of the CO gas concentration is used instead of the fluctuation pattern of the carbon discharge rate in the exhaust gas, it is possible to reduce misidentification when the molding of the slag is sufficiently promoted. On the other hand, when the threshold value of the CO gas concentration is 18.0 vol% or less, it is possible to prevent the slag from being excessively molded and to prevent the operation, and to accurately determine the molding state for efficiently performing the slag discharge.
如上所述,脫矽處理中的爐渣的成型狀況及結束脫矽處 理而開始中間排渣的適合時機可僅根據由吸入氣體獲得的資訊而判定,亦可藉由將由事先獲得的操作條件計算而得的脫矽吹煉中的必要氧量、排出氣體溫度、爐渣自爐口的噴出狀況、爐渣自出鋼口的流出狀況、噴槍或副噴槍(sublance)的振動的變化、氧吹煉中的聲音的變化等資訊、或利用既知方法獲得的爐渣等級的推定技術等進行組合,而使上述判定條件精度更高。 As described above, the molding condition of the slag in the deodorization treatment and the end of the dislocation The appropriate timing for starting the intermediate slag discharge can be determined only based on the information obtained by the inhalation gas, and the necessary oxygen amount, the exhaust gas temperature, and the slag in the deodorization blowing obtained by calculating the operating conditions obtained in advance can also be determined. Information such as the discharge state from the furnace mouth, the outflow condition of the slag from the tapping port, the change in the vibration of the spray gun or the sublance, the change in the sound during the oxygen blowing, or the estimation technique of the slag grade obtained by the known method. The combination is performed such that the above determination conditions are more accurate.
繼而,以使用圖3所示的轉爐型精煉爐的情形為例,對本發明的熔鐵的預備處理方法進行具體說明。 Next, the method of preparing the molten iron of the present invention will be specifically described by taking the case of using the converter type refining furnace shown in Fig. 3 as an example.
首先,如圖5(a)所示,本發明的熔鐵的預備處理方法是向裝入有鐵屑等冷鐵源8的轉爐型精煉爐1中經由裝入鍋15裝入未實施脫矽處理及脫磷處理、即預備處理前的熔鐵5(熔鐵裝入步驟)。 First, as shown in Fig. 5 (a), the molten iron preparation method of the present invention is carried out in a converter type refining furnace 1 in which a cold iron source 8 such as iron filings is loaded, via a loading pot 15, and is not subjected to untwisting. The treatment and dephosphorization treatment, that is, the molten iron 5 before the preliminary treatment (the molten iron charging step).
其次,如圖5(b)所示,對該轉爐型精煉爐1內的熔鐵5供給作為氧源的含氧氣體或含氧氣體及氧化鐵而實施脫矽處理(脫矽處理步驟)。此時,熔鐵5中所含的矽與所供給的氧發生反應而進行脫矽反應(Si+O2→SiO2)。因由該脫矽反應獲得的矽的燃燒熱而使熔鐵溫度上升,而促進熔鐵中的冷鐵源8的熔解。 Next, as shown in FIG. 5(b), the molten iron 5 in the converter type refining furnace 1 is supplied with an oxygen-containing gas or an oxygen-containing gas and iron oxide as an oxygen source, and is subjected to a deodorization treatment (deintercalation treatment step). At this time, the ruthenium contained in the molten iron 5 reacts with the supplied oxygen to carry out a depurination reaction (Si + O 2 → SiO 2 ). The molten iron temperature rises due to the heat of combustion of the crucible obtained by the decoupling reaction, and the melting of the cold iron source 8 in the molten iron is promoted.
其後,隨著上述脫矽處理的進行,熔鐵中的矽濃度緩慢地降低,而產生CO氣體,若進而進行脫矽處理,使脫矽爐渣的產生量增加,熔鐵溫度上升,則爐渣的組成及物性亦發生變化,藉由所產生的CO氣體引起爐渣的成型。 Then, as the above-described decarburization treatment progresses, the concentration of ruthenium in the molten iron is gradually lowered to generate CO gas, and if the deodorization treatment is further performed, the amount of generation of the slag slag is increased, and the temperature of the molten iron is increased, and the slag is slag. The composition and physical properties also change, and the slag is formed by the generated CO gas.
此處,關於藉由上述脫矽處理產生的脫矽爐渣6,為了於脫矽處理中防止源自下述脫磷爐渣7所含的磷氧化物(P2O5)分解而產生的磷移行至熔鐵5(將該現象稱為「復磷(rephosphorization)」),較佳為將脫矽處理結束後的鹼度([CaO(質量%)]/[SiO2(質量%)])設為0.80以上。此外,關於脫矽爐渣6的鹼度的上限值,就脫矽反應方面而言無需規定。然而,鹼度高意味著CaO相對於所產生的SiO2的比例高,由於脫矽爐渣6的量增大,因此上限較佳為設為1.50左右。更佳為不足1.30,進而較佳為不足1.20。 Here, the degreasing slag 6 produced by the above-described decarburization treatment prevents the phosphorus transition from the decomposition of the phosphorus oxide (P 2 O 5 ) contained in the dephosphorization slag 7 described below during the deodorization treatment. To the molten iron 5 (this phenomenon is referred to as "rephosphorization"), it is preferable to set the alkalinity ([CaO (% by mass)) / [SiO 2 (% by mass))) after the completion of the deuteration treatment. It is 0.80 or more. Further, the upper limit of the alkalinity of the slag slag 6 is not required to be specified in terms of the detachment reaction. However, a high alkalinity means that the ratio of CaO to SiO 2 produced is high, and since the amount of the slag slag 6 is increased, the upper limit is preferably set to about 1.50. More preferably, it is less than 1.30, and further preferably less than 1.20.
此外,將脫矽爐渣6的鹼度調整為上述範圍內可藉由在脫矽處理前及脫矽處理中向爐內添加CaO系助熔劑等助熔劑而進 行。其中,於在脫矽處理的初期添加CaO系助熔劑的情形時,脫矽爐渣6的鹼度最低時為所產生的SiO2量最多的脫矽處理結束的時間點,因此若將脫矽處理結束時的鹼度設為0.80以上,則其以前的脫矽處理中的鹼度必然成為0.80以上。另外,於僅藉由殘留於爐內的前一爐次的脫磷爐渣7中所含的CaO可使脫矽處理結束時的鹼度成為0.80以上的情形時,基本上不需要添加CaO系助熔劑等助熔劑。 Further, adjusting the alkalinity of the slag slag 6 to the above range can be carried out by adding a flux such as a CaO-based flux to the furnace before the mashing treatment and the mashing treatment. In the case where the CaO-based flux is added in the initial stage of the deuterium treatment, when the alkalinity of the de-slagging slag 6 is the lowest, the time at which the amount of SiO 2 generated is the highest, the deodorization treatment is completed. When the alkalinity at the end is 0.80 or more, the alkalinity in the previous deodorization treatment must be 0.80 or more. In addition, when the alkalinity at the end of the deodorization treatment is 0.80 or more by CaO contained in the dephosphorization slag 7 of the previous heat remaining in the furnace, it is basically unnecessary to add CaO-based assistance. Flux such as flux.
此外,上述CaO系助熔劑的添加方法可為將粒狀及塊狀助熔劑自爐上的料斗(hopper)投入或將粉狀助熔劑經由頂吹噴槍2投入的方法,並無特別限制。 Further, the method of adding the CaO-based flux may be a method of introducing a granular or bulk flux from a hopper on a furnace or a method of feeding a powdery flux through the top-blowing lance 2, and is not particularly limited.
此外,脫矽爐渣6的鹼度可基於下述(1)式計算:鹼度=[(爐內殘留CaO量(kg/熔鐵-t))+(脫矽處理中的添加CaO量(kg/熔鐵-t))]/[(爐內殘留SiO2量(kg/熔鐵-t))+(脫矽處理中產生的SiO2量(kg/熔鐵-t))]…(1)。 Further, the alkalinity of the slag slag 6 can be calculated based on the following formula (1): alkalinity = [(the amount of residual CaO in the furnace (kg / molten iron - t)) + (the amount of added CaO in the deodorization treatment (kg /Fused iron-t))]/[(Amount of residual SiO 2 in the furnace (kg/melt-t)) + (Amount of SiO 2 produced during the deodorization treatment (kg/melt-t))]... ).
此外,上述式中的脫矽處理中產生的SiO2量是根據脫矽處理前後的熔鐵中的矽濃度的變化而算出。 Further, the amount of SiO 2 generated in the deodorization treatment in the above formula is calculated from the change in the concentration of rhodium in the molten iron before and after the deodorization treatment.
另外,用於脫矽處理的氧源可僅為自頂吹噴槍2供給的氧氣9,另外,除了上述氧氣9以外,亦可併用氧化鐵(未圖示)。但,就本發明的目的之一即大量熔解冷鐵源8的觀點而言,使用升溫及分解時吸熱的氧化鐵欠佳。因此,較佳為儘量避免使用氧化鐵作為氧源。 Further, the oxygen source used for the delining treatment may be only the oxygen gas 9 supplied from the top blowing lance 2, and in addition to the above oxygen gas 9, iron oxide (not shown) may be used in combination. However, in view of the fact that one of the objects of the present invention is to melt the cold iron source 8 in a large amount, the iron oxide which absorbs heat during temperature rise and decomposition is not preferable. Therefore, it is preferred to avoid the use of iron oxide as an oxygen source.
另外,本發明的一實施方式是基於測定脫矽處理中的自轉爐型精煉爐排出的排出氣體中所含的碳的排出速度時獲得的成為極大值,成為極小值後再次增大的變動圖案,決定脫矽處理的 結束時間點,因此理想的是於上述碳的排出速度成為極大值及極小值的期間,進行將氧源的供給速度儘量保持固定的操作。此外,通常的操作是於短時間內完成脫矽處理,因此增大送氧速度或投入氧化鐵的操作是於脫矽處理的初期進行,故而其後藉由使氧供給速度保持固定可穩定地測定碳的排出速度的極大值及極小值。 In addition, one embodiment of the present invention is a variable pattern which is obtained by measuring the discharge rate of carbon contained in the exhaust gas discharged from the converter-type refining furnace in the degassing process, and becomes a maximum value and becomes a minimum value and then increases again. , decided to dislocate Since the time point is ended, it is preferable to perform an operation of keeping the supply rate of the oxygen source as constant as possible while the discharge speed of the carbon is a maximum value and a minimum value. Further, the usual operation is to complete the dislocation treatment in a short time, so that the operation of increasing the oxygen supply rate or the introduction of the iron oxide is performed at the initial stage of the deodorization treatment, and thereafter, the oxygen supply rate is kept constant and stably stabilized. The maximum value and the minimum value of the carbon discharge rate were measured.
以上述方式對熔鐵實施脫矽處理並決定結束其之後,立刻使頂吹噴槍2上升而結束脫矽處理,但實際上脫矽處理的結束時間點通常為自上述決定時間點起經過必要的操作等作業或裝置的作動所需的數十秒左右之後。其後,立刻如圖5(c)所示,將轉爐型精煉爐1朝設置有出鐵口4的側的相反側傾動,使脫矽處理中產生的含有大量SiO2的低鹼度的脫矽爐渣6自轉爐型精煉爐1的爐口排出(中間排渣步驟)。此外,於圖5(c)中,為了與脫矽處理前的熔鐵5加以區別而將脫矽處理後的熔鐵表示為5a。 After the molten iron is subjected to the dislocation treatment in the above-described manner and the determination is completed, the top-blowing lance 2 is immediately raised to complete the dislocation treatment, but the end time of the dislocation treatment is usually necessary after the above-mentioned determined time point. After several tens of seconds required for the operation or operation of the device or the like. Immediately thereafter, as shown in Fig. 5(c), the converter type refining furnace 1 is tilted to the side opposite to the side on which the tap hole 4 is provided, so that the low alkalinity containing a large amount of SiO 2 generated during the decanting treatment is removed. The crucible slag 6 is discharged from the mouth of the converter type refining furnace 1 (intermediate slagging step). Further, in Fig. 5(c), the molten iron after the disintegration treatment is indicated as 5a in order to distinguish it from the molten iron 5 before the deodorization treatment.
關於上述中間排渣步驟中的脫矽爐渣6的排渣率,為了於下述脫磷處理步驟中,以少量的CaO系助熔劑的使用量有效率地進行脫磷反應,較佳為設為30質量%以上。進而,為了使自熔鐵預備處理至下一步驟的脫碳精煉步驟之間所使用的CaO系助熔劑的總量比不實施中間排渣步驟的現有方法少,更佳為穩定地確保50質量%以上的排渣率。 The slag discharge rate of the slag slag 6 in the intermediate slag removal step is preferably set to be efficiently dephosphorization in a dephosphorization treatment step using a small amount of the CaO-based flux. 30% by mass or more. Further, in order to make the total amount of the CaO-based flux used between the self-melting iron preparation treatment and the decarburization refining step in the next step smaller than the conventional method in which the intermediate slag removal step is not performed, it is more preferable to stably ensure the quality of 50%. Slag discharge rate above %.
然而,若將脫矽爐渣6排出超過80質量%,則有下一步驟的脫磷處理步驟中新添加的CaO系助熔劑的渣化受損,而妨礙脫磷反應之虞。因此,於本發明中,較佳為將脫矽爐渣6的排渣率控制為50質量%~80質量%的範圍。 However, when the untwisting slag 6 is discharged by more than 80% by mass, the slag of the newly added CaO-based flux in the dephosphorization treatment step in the next step is impaired, and the dephosphorization reaction is hindered. Therefore, in the present invention, it is preferable to control the slag discharge rate of the slag slag 6 to be in the range of 50% by mass to 80% by mass.
此外,上述排渣率是以下述(2)式進行定義。 Further, the above slag discharge rate is defined by the following formula (2).
排渣率(質量%)=(排出爐渣質量)×100/[(脫矽處理步驟中產生的爐渣質量)+(前一爐次的殘留爐渣質量)]…(2) Slag discharge rate (% by mass) = (discharge slag quality) × 100 / [(quality of slag produced in the de-slipping treatment step) + (residual slag quality of the previous heat)] (2)
上述中間排渣後,如圖5(d)所示向殘留於轉爐型精煉爐內的脫矽處理後的熔鐵5a供給CaO系助熔劑或氧源而進行脫磷處理(脫磷處理步驟)。此處,於上述脫磷處理步驟中,爐內所產生的脫磷爐渣7的鹼度較佳為調整為1.2~3.0的範圍。其原因在於,若鹼度為1.2以上,則爐渣的脫磷能力成為適當的範圍,可以少量的爐渣量降低熔鐵中的磷濃度。另一方面,若為3.0以下,則可無損CaO系助熔劑的渣化而使爐渣的流動性成為適當的範圍進行脫磷反應。 After the middle slag is discharged, as shown in FIG. 5(d), a CaO-based flux or an oxygen source is supplied to the molten iron 5a after the deodorization treatment remaining in the converter type refining furnace to perform dephosphorization treatment (dephosphorization treatment step). . Here, in the dephosphorization treatment step, the alkalinity of the dephosphorization slag 7 generated in the furnace is preferably adjusted to a range of 1.2 to 3.0. The reason for this is that if the alkalinity is 1.2 or more, the dephosphorization ability of the slag is in an appropriate range, and the phosphorus concentration in the molten iron can be lowered by a small amount of slag. On the other hand, when it is 3.0 or less, the dephosphorization reaction can be carried out without impairing the slag of the CaO-based flux and making the fluidity of the slag an appropriate range.
此處,上述脫磷處理步驟中使用的氧源亦可與脫矽處理同樣,以來自頂吹噴槍2的氧氣9為主體,一部分使用氧化鐵。但,本發明的目的之一是擴大冷鐵源8的使用,因此較佳為儘量將升溫或分解時吸熱的氧化鐵的使用設為少量。為此,較佳為適當地控制送氧條件或噴槍高度等而調整脫磷爐渣7的T.Fe濃度,不藉由氧化鐵的使用而促進CaO系助熔劑的渣化。 Here, the oxygen source used in the dephosphorization treatment step may be the same as the deodorization treatment, and the oxygen gas 9 from the top-blowing lance 2 is mainly used, and part of the iron oxide is used. However, one of the objects of the present invention is to expand the use of the cold iron source 8. Therefore, it is preferable to use a small amount of iron oxide which absorbs heat when heating or decomposing as much as possible. For this reason, it is preferable to adjust the T.Fe concentration of the dephosphorization furnace slag 7 by appropriately controlling the oxygen supply conditions, the height of the lance, and the like, and to promote the slag formation of the CaO-based flux without using the iron oxide.
另外,脫磷處理中使用的CaO系助熔劑可使用生石灰(CaO)、石灰石(CaCO3)、消石灰(Ca(OH)2)等。但並不限定於該些,例如亦可使用含有40質量%以上的CaO且視需要含有氟或氧化鋁等其他成分的物質作為CaO系助熔劑。此外,上述CaO系助熔劑的添加方法與在脫矽處理中添加CaO系助熔劑時相同,可為將粒狀及塊狀助熔劑自爐上的料斗投入或將粉狀助熔劑經由頂吹噴槍2等投入的方法,並無特別限制。 Further, as the CaO-based flux used in the dephosphorization treatment, quicklime (CaO), limestone (CaCO 3 ), hydrated lime (Ca(OH) 2 ), or the like can be used. However, it is not limited to these. For example, a CaO-based flux containing 40% by mass or more of CaO and optionally containing other components such as fluorine or alumina may be used. Further, the method of adding the above-mentioned CaO-based flux is the same as the case of adding a CaO-based flux in the deodorization treatment, and it is possible to introduce the granular and bulk flux from the hopper on the furnace or to pass the powdery flux through the top-blowing lance. There is no particular limitation on the method of 2 inputs.
該脫磷處理步驟中,熔鐵中的磷藉由所供給的氧源中的 氧進行氧化而成為磷氧化物(P2O5),並被取入至藉由CaO系助熔劑的渣化而形成的作為脫磷精煉劑發揮功能的脫磷爐渣7中,而成為穩定形態的化合物(3CaO.P2O5),藉此進行熔鐵5a的脫磷。此外,脫磷處理的結束只要設為脫磷處理時間經過規定的時間時,或者進行脫磷反應使熔鐵5a的磷濃度降至規定值以下時即可。 In the dephosphorization treatment step, phosphorus in the molten iron is oxidized by oxygen in the supplied oxygen source to become phosphorus oxide (P 2 O 5 ), and is taken into slag by the CaO-based flux. and as a dephosphorizing agent functioning dephosphorization slag formation 7 become stable form of the compound (3CaO.P 2 O 5), whereby the dephosphorization of molten iron 5a. In addition, the end of the dephosphorization treatment may be performed when the dephosphorization treatment time has elapsed for a predetermined period of time or when the dephosphorization reaction is performed to lower the phosphorus concentration of the molten iron 5a to a predetermined value or less.
於脫磷處理結束後,如圖5(e)所示,將轉爐型精煉爐1朝與中間排渣的方向相反的方向傾動,使轉爐型精煉爐1內的熔鐵5b經由出鐵口4流出至未圖示的熔鐵保持容器(出鐵步驟)。此外,於圖5(e)中,為了與脫矽處理後的熔鐵5a加以區別而將脫磷處理後的熔鐵表示為5b。熔鐵5b的出鐵結束後,如圖5(f)所示,以使爐口朝向上方的方式使轉爐型精煉爐1反轉而結束出鐵。 After the dephosphorization treatment is completed, as shown in FIG. 5(e), the converter type refining furnace 1 is tilted in a direction opposite to the direction in which the slag is discharged in the middle, and the molten iron 5b in the converter type refining furnace 1 is passed through the tap hole 4 It flows out to a molten iron holding container (not shown) (ironing step). Further, in Fig. 5(e), the molten iron after the dephosphorization treatment is shown as 5b in order to distinguish it from the molten iron 5a after the deodorization treatment. After the iron discharge of the molten iron 5b is completed, as shown in Fig. 5 (f), the converter type refining furnace 1 is reversed so that the furnace opening faces upward, and the iron discharge is completed.
此外,於上述出鐵步驟中,有脫磷爐渣7混雜於自出鐵口4流出的熔鐵5b中而流出的情況,該脫磷爐渣7的流出雖不可避免,但為少量,可與意圖排出的下述脫磷爐渣的排出明確地區別開。因此,出鐵結束後的轉爐型精煉爐1內殘留有未流出的少量熔鐵5b(未圖示)及幾乎全部的脫磷爐渣7。 Further, in the above-described tapping step, the dephosphorization slag 7 is mixed in the molten iron 5b flowing out of the tap hole 4 and flows out, and the outflow of the dephosphorization furnace slag 7 is unavoidable, but is small, and is intended The discharge of the following dephosphorization slag discharged is clearly distinguished. Therefore, a small amount of molten iron 5b (not shown) and almost all of the dephosphorization slag 7 which have not flowed out remain in the converter type refining furnace 1 after the completion of the tapping.
此外,該脫磷爐渣7由於磷酸濃度高,故而若直接用作下一爐次的脫矽爐渣,則有引起復磷,熔鐵中的磷濃度上升之虞。因此,先前是於上述出鐵步驟完成後,將脫磷爐渣全部排出。然而,若將脫磷爐渣全部排出,則下一爐次的脫矽處理所需的用以產生脫矽爐渣的造渣材料的使用量增大,導致副原料成本的上升。因此,於本發明中,較佳為調整脫矽處理中的精煉條件,防止源自脫磷爐渣的復磷,並且於中間排渣後進行脫磷處理後使熔 鐵流出,其後,使殘留於轉爐型精煉爐內的脫磷爐渣中的30質量%以上殘留於爐內,而用作下一爐次的脫矽爐渣的原料的一部分。所殘留的脫磷爐渣更佳為50質量%以上。 Further, since the dephosphorization furnace slag 7 has a high concentration of phosphoric acid, if it is directly used as the slag of the next heat, the phosphorus concentration in the molten iron is increased. Therefore, all of the dephosphorization furnace slag was previously discharged after the above-described tapping step was completed. However, when all of the dephosphorization furnace slag is discharged, the amount of the slag-forming material used to generate the slag slag required for the deodorization treatment of the next heat is increased, resulting in an increase in the cost of the auxiliary material. Therefore, in the present invention, it is preferred to adjust the refining conditions in the deodorization treatment to prevent the re-phosphorization derived from the dephosphorization furnace slag, and to perform the dephosphorization treatment after the intermediate slag discharge. After the iron flows out, 30% by mass or more of the dephosphorization slag remaining in the converter type refining furnace remains in the furnace, and is used as a part of the raw material of the slag slag of the next heat. The residual dephosphorization slag is more preferably 50% by mass or more.
此外,如上述般使脫磷爐渣殘留的排渣方法亦可與通常進行的爐渣的排渣方法同樣,將出鐵後的爐體朝出鐵口的相反側傾動而自爐口排出爐渣時,調節傾動角度以使爐渣的一部分殘留於爐內的方式進行排出的方法。此外,為了使脫磷爐渣的流動性適合於排渣,較佳為將脫磷處理後的爐渣的鹼度調整為1.2~1.8的範圍,且將氧化鐵的濃度調整為10質量%以上。 Further, the slag discharging method in which the dephosphorization slag remains as described above may be the same as the slag slag discharging method which is generally performed, and when the furnace body after the iron tapping is tilted toward the opposite side of the tap hole and the slag is discharged from the furnace port, A method of adjusting the tilting angle so that a part of the slag remains in the furnace. Further, in order to make the fluidity of the dephosphorization slag suitable for slag discharge, it is preferable to adjust the alkalinity of the slag after the dephosphorization treatment to a range of 1.2 to 1.8, and to adjust the concentration of the iron oxide to 10% by mass or more.
繼而,於使脫磷爐渣7全部殘留於轉爐型精煉爐1的爐內的情形時,以及於上述出鐵步驟後將一部分脫磷爐渣7自轉爐型精煉爐1排出的情形時,亦可如圖5(f)所示,使轉爐型精煉爐1成為直立的狀態後,自爐上的料斗將小尺寸的冷鐵源8裝入至轉爐型精煉爐1內,或者向前後數次傾動轉爐型精煉爐1,使殘留於爐內的脫磷爐渣7固化(脫磷爐渣固化步驟),藉此使殘留於爐內的熔鐵5b凝固。該脫磷爐渣固化步驟是用以防止由於殘留於爐內的脫磷爐渣7及熔鐵5b流入至底吹風口3的內部而使底吹風口3堵塞的步驟,較佳為至少於脫磷爐渣7及熔鐵5b固化、凝固之前自底吹風口3噴出底吹氣體10。其中,於持續供給底吹氣體的情形時,該步驟亦可省略。 Then, when all of the dephosphorization slag 7 remains in the furnace of the converter type refining furnace 1, and when a part of the dephosphorization slag 7 is discharged from the converter type refining furnace 1 after the above-described tapping step, As shown in Fig. 5 (f), after the converter type refining furnace 1 is in an upright state, a small-sized cold iron source 8 is charged into the converter type refining furnace 1 from the hopper on the furnace, or the converter is tilted several times forward and backward. In the refining furnace 1, the dephosphorization slag 7 remaining in the furnace is solidified (the dephosphorization slag solidification step), whereby the molten iron 5b remaining in the furnace is solidified. The dephosphorization slag solidification step is for preventing the clogging of the bottom air outlet 3 due to the dephosphorization slag 7 and the molten iron 5b remaining in the furnace flowing into the bottom of the bottom air outlet 3, preferably at least the dephosphorization slag 7 and the molten iron 5b is solidified and solidified before being solidified, and the bottom blowing gas 10 is ejected from the bottom blowing port 3. Here, in the case where the bottom blowing gas is continuously supplied, this step can also be omitted.
該脫磷爐渣固化步驟後,再次回到圖5(a)所示的熔鐵裝入步驟,按照上述步驟實施下一爐次的脫矽處理及脫磷處理。 After the dephosphorization slag solidification step, the molten iron charging step shown in Fig. 5 (a) is returned again, and the next heat treatment and dephosphorization treatment are carried out in accordance with the above steps.
根據上述說明的本發明,可使用一個轉爐型精煉爐,隔著中間排渣連續地進行脫矽處理與脫磷處理,因此可將由更替精 煉容器引起的熱損失有效地用作用於熔解冷鐵源的熱源。另外,根據本發明,基於轉爐型精煉爐的排出氣體處理設備所吸入的吸入氣體(排出氣體)中的含有碳原子的氣態物質的濃度而決定脫矽處理的結束時間點,因此可始終於脫矽爐渣的體積比重小、流動性高的狀態下進行中間排渣,故而可穩定地提高脫矽爐渣的排渣率。 According to the invention described above, a converter-type refining furnace can be used, and the de-slipping treatment and the dephosphorization treatment are continuously performed through the intermediate slag, so that the ginseng can be replaced by The heat loss caused by the refining vessel is effectively used as a heat source for melting the cold iron source. Further, according to the present invention, the concentration of the gaseous substance containing carbon atoms in the intake gas (exhaust gas) sucked into the exhaust gas treatment equipment of the converter type refining furnace determines the end time of the dislocation treatment, so that it is always possible to take off When the slag has a small specific gravity and a high fluidity, the slag is discharged in the middle, so that the slag discharge rate of the slag can be stably increased.
此外,於本發明的上述說明中,對如下情況進行了說明:使用一個轉爐型精煉爐,隔著脫矽處理後的脫矽爐渣的排出(以下亦稱為「中間排渣」)對熔鐵連續地進行脫矽處理及脫磷處理,於該情形時,較佳為對於熔鐵5的精煉,使用2台以上的轉爐型精煉爐,將其中至少1台轉爐型精煉爐1使用於本發明的熔鐵預備處理,並藉由剩餘的至少1台轉爐型精煉爐進行實施了本發明的上述熔鐵預備處理的熔鐵的脫碳精煉。 Further, in the above description of the present invention, the following description has been made on the use of a converter type refining furnace in which the discharge of the degreasing furnace slag after the deodorization treatment (hereinafter also referred to as "intermediate slag discharge") is applied to the molten iron. In this case, it is preferable to use two or more converter type refining furnaces for the refining of the molten iron 5, and at least one converter type refining furnace 1 is used in the present invention. The molten iron is pretreated, and the molten iron of the molten iron preparation process of the present invention is subjected to decarburization refining by at least one of the remaining converter type refining furnaces.
[實施例1] [Example 1]
實施如下熔鐵預備處理:使用圖3所示的容量300噸規模的轉爐型精煉爐,自頂吹噴槍對收容於上述爐內的300噸的熔鐵吹送精煉用氧氣,並且自設置於爐底的底吹風口向熔鐵中吹入攪拌用氮氣,而對熔鐵實施脫矽處理與脫磷處理。上述熔鐵預備處理具體包括如下一連串步驟:於圖3所示的轉爐型精煉爐中裝入鐵屑後,裝入熔鐵,進而視需要添加作為CaO系助熔劑的生石灰,自頂吹噴槍供給氧氣進行脫矽處理,將脫矽爐渣的一部分排出後,自頂吹噴槍供給氧氣,並添加作為CaO系助熔劑的生石灰進行脫磷處理後,使熔鐵流出,其後,將脫磷爐渣全部排出。 The following molten iron preparation process is carried out: using a converter-type refining furnace having a capacity of 300 tons as shown in FIG. 3, the refining oxygen is blown to the 300-ton molten iron accommodated in the furnace from the top-blowing lance, and is set at the bottom of the furnace. The bottom air outlet blows nitrogen for stirring into the molten iron, and the molten iron is subjected to a de-corrosion treatment and a dephosphorization treatment. The molten iron preparation process specifically includes the following steps: after the iron filings are placed in the converter type refining furnace shown in FIG. 3, the molten iron is charged, and the quicklime as a CaO-based flux is added as needed, and is supplied from the top blowing lance. After the oxygen is removed, a part of the slag is discharged, oxygen is supplied from the top blowing lance, and quicklime is added as a CaO-based flux to perform dephosphorization treatment, and then the molten iron is discharged, and thereafter, the dephosphorization slag is completely discharge.
此外,實施上述熔鐵預備處理的熔鐵是使用溫度為1250℃~ 1320℃、矽濃度為0.20質量%~0.55質量%、磷濃度約為0.12質量%的熔鐵。另外,上述脫矽處理後的熔鐵中的目標矽濃度設為0.03質量%,脫矽處理結束後的脫矽爐渣的目標鹼度設定為0.6~0.9的範圍。另外,上述脫矽處理結束時的目標熔鐵溫度設為1300℃~1340℃,其控制是藉由如下方式進行:使鐵屑裝入量固定為80kg/t,根據裝入的熔鐵溫度,於脫矽處理的初期添加成為冷卻材料的冷鐵源及/或鐵礦石或成為熱源的碳材及/或矽鐵,調整該些材料的添加量及送氧量。 In addition, the molten iron for performing the above molten iron preparation treatment is used at a temperature of 1250 ° C~ The molten iron at 1320 ° C, the cerium concentration is 0.20% by mass to 0.55% by mass, and the phosphorus concentration is about 0.12% by mass. In addition, the target cerium concentration in the molten iron after the above-described deodorization treatment is set to 0.03 mass%, and the target alkalinity of the slag slag after the completion of the devolatilization treatment is set to a range of 0.6 to 0.9. Further, the target molten iron temperature at the end of the above-described deodorization treatment is set to 1300 ° C to 1340 ° C, and the control is performed by fixing the iron filing amount to 80 kg/t, depending on the temperature of the molten iron to be charged. At the initial stage of the deodorization treatment, a cold iron source and/or iron ore which is a cooling material or a carbon material and/or ferroniobium which are heat sources are added, and the amount of addition and the amount of oxygen supplied are adjusted.
另外,於接下來進行的脫磷處理中,基於殘留於爐內的脫矽爐渣量與其組成的推定值,以使脫磷爐渣的鹼度成為1.6~2.0的範圍的方式調整生石灰的使用量。 In addition, in the dephosphorization treatment to be carried out, the amount of quicklime used is adjusted so that the alkalinity of the dephosphorization slag is in the range of 1.6 to 2.0 based on the amount of the slag remaining in the furnace and the estimated value of the composition.
上述熔鐵預備處理是利用以下兩種方法決定脫矽處理的結束時間點。 The above molten iron preparation process determines the end time point of the dislocation treatment by the following two methods.
.方法1:設為結束供給根據預備處理前的熔鐵中的矽濃度、與對應該濃度的脫矽氧效率(經驗值)算出的使熔鐵中的矽濃度成為0.03質量%時所必需的氧量的時間點的現有方法(比較例)。 . In the first method, the oxygen required for the enthalpy concentration in the molten iron to be 0.03 mass% calculated from the enthalpy concentration in the molten iron before the preliminary treatment and the deuterium oxygen efficiency (empirical value) corresponding to the concentration is calculated. The current method of time points (comparative example).
.方法2:如圖1所示,以排出氣體中的碳的排出速度的變動圖案中,顯示極大值、極小值後再次上升的碳的排出速度成為上述極大值以上的時間點為基準,決定脫矽處理的結束,於自上述時間點經過約20秒後,碳的排出速度相對於上述極大值成為100%以上且150%以下的範圍時結束脫矽處理的方法(發明例)。 . In the variation pattern of the discharge rate of the carbon in the exhaust gas, as shown in FIG. 1, the time at which the discharge rate of the carbon which rises again after the maximum value and the minimum value is equal to or greater than the maximum value is determined as a reference. When the carbon discharge rate is in the range of 100% or more and 150% or less with respect to the maximum value after the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the lapse of the above-mentioned time,
此外,任一方法均將自頂吹噴槍的送氧速度固定為30000Nm3/hr,並以吹入速度1200Nm3/hr自底部吹入氮氣。 Further, in either method, the oxygen supply rate from the top blowing lance was fixed to 30,000 Nm 3 /hr, and nitrogen gas was blown from the bottom at a blowing speed of 1200 Nm 3 /hr.
另外,將以上述方法1及方法2兩種方法決定脫矽處理 的結束時間點的熔鐵預備處理以各自的方法各實施數十爐次,比較各方法的中間排渣中的脫矽爐渣的排渣率。 In addition, the dislocation treatment will be determined by the above methods 1 and 2 The molten iron preparation process at the end time point was carried out for several tens of times in each method, and the slag discharge rate of the slag slag in the intermediate slag of each method was compared.
此時,上述脫矽處理結束後的脫矽爐渣的排渣(中間排渣)是於脫矽處理結束後,立刻使頂吹噴槍上升後傾動爐體而開始,且於不會阻礙設置於爐下的移動台車上的爐渣用鍋受渣,且不使熔鐵流出的範圍內,儘可能增大轉爐型精煉爐的傾動角度而進行,中間排渣的結束是設為可利用稱量值確認充分的排渣量時、難以僅使爐渣流出而不使熔鐵流出時、及排渣時間成為操作上可容許的最長時間時中的任一時間點。另外,上述中間排渣中的脫矽爐渣的排渣率是利用設置於爐下的移動台車上的稱量裝置測定上述爐渣用鍋所受渣的脫矽爐渣的質量,根據下述(2)式而求出。 At this time, the slag discharge (intermediate slag discharge) of the slag slag after the completion of the devolatilization treatment is started immediately after the completion of the devolatilization treatment, and the top blasting gun is raised and then the furnace body is tilted, and the furnace is not hindered from being placed in the furnace. The slag on the moving trolley is subjected to the slag, and the tilting angle of the converter-type refining furnace is increased as much as possible within the range in which the molten iron flows out. The end of the intermediate slag is set to be usable by the weighing value. When the amount of slag is sufficient, it is difficult to cause only the slag to flow out without flowing the molten iron, and the slag discharge time becomes any one of the longest time allowed for the operation. In addition, the slag discharge rate of the slag slag in the middle slag is a mass measuring device that measures the slag of the slag pot by a weighing device provided on a moving trolley provided under the furnace, according to the following (2) Determined by the formula.
排渣率(質量%)=(排出爐渣質量)×100/[(脫矽處理步驟中產生的爐渣質量)+(前一爐次的殘留爐渣質量)]…(2) Slag discharge rate (% by mass) = (discharge slag quality) × 100 / [(quality of slag produced in the de-slipping treatment step) + (residual slag quality of the previous heat)] (2)
將上述結果示於表1。由此可知,利用熔鐵中的Si濃度決定脫矽處理的結束的現有方法(比較例)中,脫矽處理後的脫矽爐渣的排渣率於20質量%~70質量%的範圍內存在偏差,平均排渣率為37質量%,相對於此,根據排出氣體中的碳的排出速度決定脫矽處理的結束的本發明例中,脫矽處理後的脫矽爐渣的排渣率為50質量%~80質量%的範圍,平均排渣率為67質量%,可穩定地達成50質量%以上的排渣率。另外,可知藉由如此提高中間排渣的排渣率,亦可大幅度地削減脫磷處理中添加的造渣材料的使用量。 The above results are shown in Table 1. In the conventional method (comparative example) in which the concentration of Si in the molten iron is determined to be the end of the dislocation treatment, the slag discharge rate of the slag after the deodorization treatment is in the range of 20% by mass to 70% by mass. The deviation and the average slagging rate are 37% by mass. On the other hand, in the example of the present invention in which the release of the carbon in the exhaust gas is determined, the slag removal rate of the slag after the mashing treatment is 50. In the range of %% to 80% by mass, the average slagging rate is 67% by mass, and the slagging rate of 50% by mass or more can be stably achieved. Further, it is understood that the amount of the slag-forming material added during the dephosphorization treatment can be drastically reduced by increasing the slagging rate of the intermediate slag.
另外,圖6表示中間排渣所需要的時間與預備處理前的熔鐵中的Si濃度的關係,可知於本發明例中,中間排渣需要的作業時 間可大幅度地縮短為10分鐘以下。藉由該排渣時間的縮短,可將熔鐵預備處理的處理間距縮短至與下一步驟的脫碳處理的處理間距大致同等的水平,因此可對幾乎全部熔鐵實施熔鐵預備處理。 In addition, FIG. 6 shows the relationship between the time required for the intermediate slag discharge and the Si concentration in the molten iron before the preliminary treatment, and it is understood that in the example of the present invention, the operation required for the intermediate slag discharge is required. The room can be greatly shortened to less than 10 minutes. By shortening the slag discharge time, the processing pitch of the molten iron preparation process can be shortened to a level substantially equal to the processing pitch of the decarburization treatment in the next step, so that the molten iron preparation process can be performed on almost all of the molten iron.
[實施例2] [Embodiment 2]
於不排出脫磷處理後的脫磷爐渣而使其全部殘留於爐內的狀態下裝入下一爐次的熔鐵,且將脫矽處理中的爐渣的鹼度控制為0.9~1.2的範圍以防止源自脫磷爐渣的復磷,除此以外,於與藉由實施例1的方法2決定脫矽處理的結束時間點的發明例相同的條件下,連續實施10爐次實施熔鐵預備處理的實驗。 The molten iron after the dephosphorization treatment is discharged, and the molten iron in the next heat is placed in the furnace, and the alkalinity of the slag in the deodorization treatment is controlled to be in the range of 0.9 to 1.2. In the same manner as the invention example in which the desorption treatment was determined by the method 2 of the first embodiment, the molten iron preparation was carried out continuously for 10 times in order to prevent the re-phosphorization derived from the dephosphorization slag. Processed experiments.
其結果,可將脫矽處理中的CaO系助熔劑(生石灰)的使用量自實施例1的本發明例的情形時的6.0kg/熔鐵t(參照表1)大幅度降至2.0kg/熔鐵t。另外,使爐內殘留有前一爐次的脫磷爐渣幾乎不會對脫磷處理中的生石灰使用量或處理後的熔鐵中的磷濃度造成不良影響,因此可於該狀態下享受削減上述脫矽處理中的生石灰使用量的優點。 As a result, the amount of the CaO-based flux (lime) used in the deodorization treatment can be greatly reduced from 6.0 kg/molten iron t (refer to Table 1) in the case of the inventive example of Example 1 to 2.0 kg/ Fused iron t. In addition, the dephosphorization slag in which the previous heat is left in the furnace hardly adversely affects the amount of quicklime used in the dephosphorization treatment or the phosphorus concentration in the molten iron after the treatment, so that the above-mentioned state can be reduced. The advantage of the amount of quicklime used in the deodorization process.
[實施例3] [Example 3]
對利用與實施例1的方法1相同的方法決定脫矽處理的結束時間點,且將脫磷處理中的生石灰使用量設為7.0kg/t,除此以外,於與實施例2相同的條件下實施熔鐵預備處理的比較例,與將該比較例中的脫矽處理的結束時間點的決定方法變更為下述方法3的發明例進行比較實驗。 The same conditions as in Example 2 were carried out except that the end time of the deodorization treatment was determined by the same method as in the method 1 of the first embodiment, and the amount of quicklime used in the dephosphorization treatment was 7.0 kg/t. In the comparative example in which the molten iron preparation process was performed, a comparative experiment was carried out by changing the method of determining the end time of the dislocation process in the comparative example to the invention example of the following method 3.
具體而言,反覆進行如下熔鐵預備處理:如圖5(a)~圖5(f)所示,於前一爐次的熔鐵預備處理中產生的脫磷爐渣7未排出而全部殘留於其中的轉爐型精煉爐1中裝入鐵屑8,繼而,於上述轉爐型精煉爐1中裝入熔鐵5,進而視需要添加生石灰,自頂吹噴槍2供給氧氣9進行脫矽處理後,將脫矽爐渣6的一部分排出,其後,添加生石灰,繼續自頂吹噴槍2供給氧氣9進行脫磷處理。 此外,該轉爐型精煉爐1的排出氣體處理設備具有回收吸入氣體作為燃料氣體的功能,且於吹煉時使裙罩11上升的狀態下具有90000Nm3/hr~100000Nm3/hr左右的吸入能力。另外,煙道12包含蒸氣鍋爐(排熱鍋爐),由於脫矽處理中不進行吸入氣體的回收,因此使裙罩11上升而吸入大氣,使排出氣體中的CO氣體積極地燃燒,作為高壓的蒸氣進行能源的回收。 Specifically, the molten iron preparation process is repeated as follows: as shown in FIGS. 5( a ) to 5 ( f ), the dephosphorization slag 7 generated in the molten iron preparation process of the previous heat is not discharged and remains in the entire The converter type refining furnace 1 is filled with iron scraps 8, and then the molten iron 5 is placed in the above-described converter type refining furnace 1, and then quicklime is added as needed, and oxygen gas 9 is supplied from the top blowing lance 2 to perform deodorization treatment. A part of the slag slag 6 is discharged, and thereafter, quicklime is added, and oxygen gas 9 is continuously supplied from the top-blowing lance 2 to perform dephosphorization treatment. In addition, the exhaust gas treatment device of the converter-type refining furnace 1 has a function of recovering the intake gas as a fuel gas, and has an intake capacity of about 90000 Nm 3 /hr to 100,000 Nm 3 /hr in a state where the skirt 11 is raised during the blowing. . Further, the flue 12 includes a steam boiler (exhaust heat boiler), and since the suction gas is not recovered during the dislocating process, the skirt 11 is raised and sucked into the atmosphere, and the CO gas in the exhaust gas is actively burned as a high pressure. Vapor for energy recovery.
此時,上述脫矽處理的結束時間點的決定方法是使用與實施例1的方法1相同的方法(比較例)與下述方法3(發明例)兩種方法並加以比較。 At this time, the method of determining the end time of the above-described dislocation treatment is to use the same method as the method 1 of the first embodiment (comparative example) and the following method 3 (invention example) and compare them.
.方法3:於結束供給根據脫矽處理前的熔鐵中的Si濃度與作為目標的脫矽處理後的熔鐵中的Si濃度計算而得的化學計量上必需的氧量的1.2倍的氧的時間點之後,以吸入氣體中的CO氣體濃度成為6.0vol%以上的時間點為基準,決定脫矽處理的結束,於自上述時間點經過約20秒後,CO氣體濃度成為6.0vol%以上且18.0vol%以下的範圍內時結束脫矽處理的方法(發明例) . Method 3: At the end of the supply of oxygen which is 1.2 times the stoichiometrically necessary amount of oxygen calculated from the Si concentration in the molten iron before the deodorization treatment and the Si concentration in the molten iron after the target deodorization treatment After the time point, the end of the deodorization treatment is determined based on the time point when the CO gas concentration in the inhaled gas is 6.0 vol% or more, and the CO gas concentration is 6.0 vol% or more after about 20 seconds from the above time point. Method for ending the dislocation treatment in the range of 18.0 vol% or less (Example of the invention)
利用上述方法1及方法3兩種方法分別各實施100爐次熔鐵預備處理,調查脫矽處理結束後的中間排渣中的脫矽爐渣的平均排渣率及熔鐵預備處理後的熔鐵中的磷濃度,將其結果示於表2。 According to the above method 1 and method 3, 100 furnaces of molten iron preparation were respectively carried out, and the average slagging rate of the slag slag in the intermediate slag after the completion of the mashing treatment and the molten iron after the molten iron preparation treatment were investigated. The phosphorus concentration in the medium is shown in Table 2.
根據該結果可知,利用與先前相同的方法決定脫矽處理結束時間點的方法1中的脫矽爐渣的平均排渣率為47質量%,相對於此,利用適合於本發明的方法決定脫矽處理結束時間點的方法3中的脫矽爐渣的平均排渣率大幅度提高至62質量%,另外,隨之熔鐵預備處理後的熔鐵中的磷濃度大幅度降低,並且其偏差(標 準偏差)亦可大幅度縮小。 According to the results, it is understood that the average slagging rate of the slag slag in the method 1 of determining the end time of the mashing treatment is 47% by mass by the same method as the above, and the detachment is determined by the method suitable for the present invention. The average slagging rate of the slag slag in the method 3 at the end of the treatment is greatly increased to 62% by mass, and the phosphorus concentration in the molten iron after the molten iron preparation is greatly reduced, and the deviation thereof The quasi-bias can also be greatly reduced.
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Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH06240378A (en) * | 1993-02-16 | 1994-08-30 | Nisshin Steel Co Ltd | Production of low-si, low-p, high-mn molten iron accompanying smelting reduction of mn ore |
JPH10152714A (en) * | 1996-11-25 | 1998-06-09 | Nippon Steel Corp | Method for refining molten iron |
JP2008184648A (en) * | 2007-01-30 | 2008-08-14 | Jfe Steel Kk | Method for desiliconizing and dephosphorizing molten pig iron |
Family Cites Families (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH02209411A (en) * | 1989-02-07 | 1990-08-20 | Nippon Steel Corp | Method for pre-treating molten iron |
WO1995001458A1 (en) * | 1993-06-30 | 1995-01-12 | Nippon Steel Corporation | Steel manufacturing method using converter |
JPH10102133A (en) * | 1996-09-27 | 1998-04-21 | Sumitomo Metal Ind Ltd | Method for controlling decarburization to extra-low carbon steel |
JPH11264008A (en) * | 1998-03-16 | 1999-09-28 | Kawasaki Steel Corp | Method for preventing erosion of lined refractory in converter |
JPH11323420A (en) | 1998-05-15 | 1999-11-26 | Nippon Steel Corp | Pretreating method for molten iron |
JP2002047509A (en) * | 2000-07-31 | 2002-02-15 | Sumitomo Metal Ind Ltd | Method for refining molten iron |
JP4984946B2 (en) * | 2007-02-14 | 2012-07-25 | Jfeスチール株式会社 | Hot metal pretreatment method |
-
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Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH06240378A (en) * | 1993-02-16 | 1994-08-30 | Nisshin Steel Co Ltd | Production of low-si, low-p, high-mn molten iron accompanying smelting reduction of mn ore |
JPH10152714A (en) * | 1996-11-25 | 1998-06-09 | Nippon Steel Corp | Method for refining molten iron |
JP2008184648A (en) * | 2007-01-30 | 2008-08-14 | Jfe Steel Kk | Method for desiliconizing and dephosphorizing molten pig iron |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
TWI830137B (en) * | 2021-02-01 | 2024-01-21 | 日商杰富意鋼鐵股份有限公司 | Top blowing lance of converter, method of adding auxiliary raw materials and refining method of molten iron |
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JPWO2014112521A1 (en) | 2017-01-19 |
BR112015016931A2 (en) | 2017-07-11 |
BR112015016931B1 (en) | 2020-04-07 |
JP5790964B2 (en) | 2015-10-07 |
JP2015092026A (en) | 2015-05-14 |
KR101701658B1 (en) | 2017-02-01 |
WO2014112521A1 (en) | 2014-07-24 |
JP5950133B2 (en) | 2016-07-13 |
TW201441378A (en) | 2014-11-01 |
KR20150092298A (en) | 2015-08-12 |
CN104884641B (en) | 2017-09-22 |
CN104884641A (en) | 2015-09-02 |
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