JPS6115127B2 - - Google Patents
Info
- Publication number
- JPS6115127B2 JPS6115127B2 JP9522877A JP9522877A JPS6115127B2 JP S6115127 B2 JPS6115127 B2 JP S6115127B2 JP 9522877 A JP9522877 A JP 9522877A JP 9522877 A JP9522877 A JP 9522877A JP S6115127 B2 JPS6115127 B2 JP S6115127B2
- Authority
- JP
- Japan
- Prior art keywords
- decarburization
- blowing
- decarburization rate
- exhaust gas
- blow
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
- 238000005261 decarburization Methods 0.000 claims description 56
- 238000007664 blowing Methods 0.000 claims description 37
- 238000012937 correction Methods 0.000 claims description 18
- 239000007789 gas Substances 0.000 claims description 17
- 238000000034 method Methods 0.000 claims description 16
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 14
- 229910052760 oxygen Inorganic materials 0.000 claims description 14
- 239000001301 oxygen Substances 0.000 claims description 14
- 238000005259 measurement Methods 0.000 claims description 9
- 238000006243 chemical reaction Methods 0.000 claims description 5
- 238000004868 gas analysis Methods 0.000 claims description 5
- 230000001186 cumulative effect Effects 0.000 claims description 4
- 230000000694 effects Effects 0.000 claims description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 12
- 229910052799 carbon Inorganic materials 0.000 description 12
- 229910000831 Steel Inorganic materials 0.000 description 10
- 239000010959 steel Substances 0.000 description 10
- 239000002184 metal Substances 0.000 description 7
- 229910052751 metal Inorganic materials 0.000 description 7
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 4
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 235000012255 calcium oxide Nutrition 0.000 description 2
- 239000000292 calcium oxide Substances 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000003068 static effect Effects 0.000 description 2
- 229910000805 Pig iron Inorganic materials 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000007704 transition Effects 0.000 description 1
Description
この発明は、転炉酸素吹錬において吹止時の鋼
浴炭素濃度と脱炭速度との間に強い相関があるこ
とに着目し、その吹止脱炭速度を吹錬末期の脱炭
速度曲線パターンで区分された操業条件による重
回帰式と排ガス実績補正値およびその操業条件に
よる変動補正値とから求め、吹錬末期に転炉の排
ガス分析から時々刻々求めた排ガス脱炭速度に前
述の補正を加えた計算脱炭速度を逐次比較監視し
て、前述の吹止脱炭速度による吹止条件を満足し
た時点で吹錬を終了させて吹止時の鋼浴炭素濃度
を制御することを特徴とする転炉吹錬制御方法に
関するものである。
転炉の脱炭反応の制御に当り、吹錬中の排ガス
(脱炭速度)の情報から吹錬過程を推定して吹止
炭素濃度を制御する方法の多くは、排ガス分析値
(CO、CO2)および排ガス流量値の連続測定によ
り脱炭量(脱炭速度)を逐次計算で求めて、残存
する鋼浴中炭素濃度を推定し吹錬酸素量を決める
方法である。
この方法では、プロセス測定値の測定上あるい
は経時変化上の測定誤差およびその集積誤差が無
視しえない量となるため、良好な制御精度が得ら
れていない。
この発明は、かような問題点を有利に克服して
転炉の実操業に適合して的確な吹上炭素濃度の制
御を実現することを目的とするものである。
この発明の方法は次にのべるようにして実際の
転炉操業に適用し、その吹上操業濃度(C%)の
適切な制御を実現するものである。以下この発明
を具体的に説明する。
この発明では、転炉吹錬初期に炉内反応モデル
による吹錬制御計算式から吹錬予定酸素量(O
E)を求める。
次にこの酸素量による吹錬末期から公知の排ガ
ス分析による排ガス脱炭速度(dc/do又はdc/d
t)を、
単位時間(例えば秒単位)にわたる脱炭速度A
と、これより粗い期間(例えば分単位)にわたる
脱炭速度Bについて連続的に測定算出する。
この排ガス脱炭速度は一般的にプロセス測定値
の測定誤差および操業条件による変動性などの影
響を強く受けるため、これらの補正を行い、補正
後の計算脱炭速度をそれぞれA*、B*とし、表
示装置(例えばCRT表示装置)に逐次表示す
る。
上記補正は次のようにして行う。
A*=k1・k2・A ………(1)
B*=k1・k2・B ………(2)
こゝにk2=k2 2/k1 1、ただしk1は排ガス実績補
正値(前チヤージ実績脱炭量/排ガス脱炭量)、
k2は操業条件による重回帰式から求めたk1の変動
補正値で、k2 1は前チヤージの推定補正値、k2 2は
本チヤージの推定補正値である。
排ガス実績補正値k1に関して前チヤージ実績脱
炭量、排ガス脱炭量は次の(3)、(4)式で求め、また
本チヤージ推定補正値は(5)式で与えられる。
実積脱炭量=10{10HM・WHM+4.2WCI
−CS・WS}+9.6WCaO ………(3)
ただしCHM;溶銑C濃度(%)、WHM;溶銑重
量(ton)、WCI;冷銑重量(ton)、CS;溶鋼吹
止C濃度(%)、WS;製出鋼重量(wton)、WCa
O;焼石灰重量(ton)
ただしQ(t+τ1);時刻(t+τ1)の排
ガス流量(Nm3/h)、CO(t+τ2)、CO2(t
+τ2);時刻(t+τ2)の排ガス分析CO、
CO2成分(%vol)、K:定数、tO;吹錬開始時
刻、tE;吹錬終了時刻、
This invention focuses on the fact that there is a strong correlation between the steel bath carbon concentration at the end of blowing and the decarburization rate in converter oxygen blowing, and calculates the end of the blowing decarburization rate to the decarburization rate curve at the end of blowing. The above-mentioned correction is made to the exhaust gas decarburization rate obtained moment by moment from the exhaust gas analysis of the converter at the end of blowing, which is calculated from the multiple regression equation based on the operating conditions divided by patterns, the actual exhaust gas correction value, and the fluctuation correction value depending on the operating conditions. It is characterized by successively monitoring the calculated decarburization rate in addition to the above, and when the above-mentioned blowout conditions based on the blowout decarburization rate are satisfied, the blowing is terminated to control the steel bath carbon concentration at the time of blowout. The present invention relates to a converter blowing control method. When controlling the decarburization reaction in a converter, most methods estimate the blowing process from information on the exhaust gas during blowing (decarburization rate) and control the end-of-blown carbon concentration. 2 ) and the amount of decarburization (decarburization rate) is calculated sequentially by continuous measurement of the exhaust gas flow rate, and the remaining carbon concentration in the steel bath is estimated to determine the amount of oxygen for blowing. In this method, good control accuracy cannot be obtained because the measurement errors in the measurement or changes over time of the process measurement values and the accumulated errors thereof are not negligible. It is an object of the present invention to advantageously overcome these problems and realize accurate control of the blow-up carbon concentration in a manner suitable for actual operation of a converter. The method of this invention is applied to actual converter operation as described below, and achieves appropriate control of the blow-up operation concentration (C%). This invention will be specifically explained below. In this invention, in the early stage of converter blowing, the expected blowing oxygen amount (O
Find E ). Next, from the final stage of blowing using this amount of oxygen, the exhaust gas decarburization rate (dc/do or dc/d
t) is the decarburization rate A over unit time (e.g. seconds)
Then, the decarburization rate B is continuously measured and calculated over a coarser period (for example, in minutes). Since this exhaust gas decarburization rate is generally strongly influenced by measurement errors in process measurements and variability due to operating conditions, these are corrected and the calculated decarburization rates after correction are designated as A * and B * , respectively. , sequentially displayed on a display device (for example, a CRT display device). The above correction is performed as follows. A * =k 1・k 2・A ………(1) B * =k 1・k 2・B ………(2) Here k 2 =k 2 2 /k 1 1 , however, k 1 is Exhaust gas performance correction value (previous charge performance decarburization amount/exhaust gas decarburization amount),
k 2 is the variation correction value of k 1 obtained from the multiple regression equation depending on the operating conditions, k 2 1 is the estimated correction value of the previous charge, and k 2 2 is the estimated correction value of the main charge. Regarding the actual exhaust gas correction value k1 , the previous charge actual decarburization amount and the exhaust gas decarburization amount are determined by the following equations (3) and (4), and the main charge estimated correction value is given by the equation (5). Actual decarburization amount = 10 {10 HM・W HM +4.2W CI −C S・W S }+9.6W CaO ……(3) where C HM : Hot metal C concentration (%), W HM : Hot metal weight (ton), W CI ; Cold pig iron weight (ton), C S ; Molten steel blowout C concentration (%), W S ; Weight of produced steel (wton), W Ca
O ; Burnt lime weight (ton) However, Q(t+τ 1 ); exhaust gas flow rate (Nm 3 /h) at time (t+τ 1 ), CO (t+τ 2 ), CO 2 (t
+τ 2 ); Exhaust gas analysis CO at time (t + τ 2 );
CO 2 component (%vol), K: constant, t O ; blowing start time, t E ; blowing end time,
【表】
ただしTHM;溶銑温度(℃)、SiHM;溶銑Si濃
度(%)、SHM;溶銑S濃度(%)、WORE;鉄鉱
石重量(ton)、Wacale;スケール重量(ton)、
CF;溶鋼吹止C濃度(%)、TF;溶鋼吹上温
度、OS;吹錬積算酸素量(Nm3)、
また、本チヤージの推定吹止脱炭速度A* Fは次
の(7)式で与えられる。
ただしMnHM;溶銑Mn濃度(%)、HR;溶銑配
合比、NLD;炉回数、Ot;送酸量(Nm2/t)
そして脱炭速度測定算出開始後一定期間の間の
計算脱炭速度B*の曲線軌跡を、あらかじめ決め
られた第1図のごとき数種類の曲線パターン判定
条件によつて判定し、本チヤージの脱炭曲線パタ
ーンを決定する。
一方あらかじめ脱炭速度曲線パターンによつて
区分された吹止脱炭速度の操業条件による重回帰
式から本チヤージの推定吹止脱炭速度A* Fを求
め、それ次式ように目標吹止脱炭速度A* Eとす
る。
A*(E)=A* F ………(6)
この目標吹止脱炭速度A*(E)も同様に表示装置に
表示する。
計算脱炭速度A*と目標吹止脱炭速度A*(E)を逐
次比較監視して、次の吹止条件置を満たしたとき
吹錬を終了する。
条 件
(1) A*(E)A*<(1+α)A*(E) 0<α<1
(2) β・OE<OS(1+β)OE 0<β<1
但し、OS;吹錬積算酸素量、OE;吹錬予定酸
素量(炉内反応モデルによる)
実施例
この発明の方法を100ton転炉の操業に適用した
場合について述べる。
本チヤージの吹錬前に目標炭素濃度を0.070%
として炉内反応モデルにより、吹錬予定酸素量O
Eを計算し、OE=5120Nm3を得た。
排ガス脱炭速度の補正係数である排ガス積分補
正値k1は前チヤージの実績値から(3)、(4)式により
k1=0.99を求め、さらに操業条件によるk1の変動
補正値k2は前チヤージと本チヤージの操業条件デ
ータから(5)式によりk2=k2 2/k2 1=1.11を得た。
吹錬開始後、排ガス分析により排ガス脱炭速度
A、Bを時々刻々に測定算出し、前述のk1、k2の
補正後のの計算脱炭速度A*=1.099A、B*=
1.099BをCRT画面に表示する。これらの計算脱
炭速度推移を第2図に示した。
吹錬予定酸素量OE(=5120Nm3)の75%〜88
%(3840〜4506Nm3)間、約3分間に計算脱炭速
度B*の曲線パターンは第1図aに示したであ
つた。パターンの認識後、このパターンの推
定吹止脱炭速度A* Fを(7)式の重回帰式により本チ
ヤージの吹止目標条件下で求めてA* F=55.5Kg・
C/minを得た。この値を本チヤージの目標吹止脱
炭速度A*(E)としてCRT画面に表示した。
(2)式A*=1.099Aにしたがつて、時々刻々計
算表示される計算脱炭速度A*がまず、
(1) 経験的にα=0.2とすると
A*(E)=5.55Kg・C/minA*66.6Kg・C/minの
条件を満たし、次に吹錬積算酸素量OSが
(2) β=0.95として 4870Nm3<OS
の条件を満たした時点で吹止めた。
吹止炭素濃度(CF)ACTは0.066%以下と目標炭
素濃度0.070%に極めて近い値を示した。
この発明の方法を100ton転炉の吹錬制御に適用
した場合の効果を第3図に示す。
これは20日間にわたり763ヒート(1日平均38
ヒート)の吹錬に対して得られた吹止時の鋼浴内
目標炭素濃度(CF)AIMと実績炭素濃度(CF)ACT
のずれを次式で定義するσで日間表示したもので
ある。
但し、nは1日のヒート数
比較上の参考のために、この発明の方法を適用
する以前にスタテイツク・チヤージ計算のみで制
御した吹錬のデータを同様に第3図にあわせ掲げ
た。
両者のσ値を較べると、スタテイツク・チヤー
ジ計算によるものが0.025%〜0.034%であるのに
対し、この発明によれば0.002%〜0.005%のよう
に前者の約1/10となり、吹止炭素濃度の的中率が
従来法よる頗る高いものといえる。
この発明の効果を要約すると次のとおりであ
る。
1 炉内反応数式モデル等の吹錬制御計算式だけ
で吹止め的中成績を大巾に向上させることがで
き、とくにサブランス設備のない転炉吹錬制御
に有効である。もちろんサブランス設備のある
転炉で、これを併用すれば更に有効である。
2 従来の排ガス分析法は脱炭速度を測定算出し
て鋼中カーボン濃度の推定、吹止カーボン濃度
までの吹錬酸素量の推定を積分計算するため非
常に精度が悪かつたが、この方法は脱炭速度の
測定計算だけでよく非常に簡単な方法である。
また脱炭速度の測定計算精度も種々の補正によ
つて極めても良いものとなる。[Table] However, T HM : Hot metal temperature (℃), Si HM : Hot metal Si concentration (%), S HM : Hot metal S concentration (%), W ORE : Iron ore weight (ton), Wacale : Scale weight (ton) ,
C F : Molten steel blow-off C concentration (%), T F : Molten steel blow-up temperature, O S : Blowing cumulative oxygen amount (Nm 3 ), and the estimated blow-off decarburization rate A * F of this charge is as follows ( 7) given by Eq. However, Mn HM : Hot metal Mn concentration (%), HR: Hot metal blending ratio, N LD : Number of furnaces, O t : Oxidation amount (Nm 2 /t). The curve locus of the coal speed B * is determined according to several kinds of predetermined curve pattern determination conditions as shown in FIG. 1, and the decarburization curve pattern of the main charge is determined. On the other hand, the estimated blowout decarburization rate A * F of the main charge is determined from the multiple regression equation based on the operating conditions of the blowout decarburization rate, which is divided in advance by the decarburization rate curve pattern, and the target blowout decarburization rate is calculated as follows. Let the coal speed be A * E . A * (E) = A * F (6) This target blow-off decarburization rate A * (E) is also displayed on the display device. The calculated decarburization rate A * and the target blow-off decarburization rate A * (E) are monitored successively, and the blowing is terminated when the next blow-off condition is satisfied. Condition (1) A * (E)A * <(1+α)A * (E) 0<α<1 (2) β・O E <O S (1+β)O E 0<β<1 However, O S ; Cumulative oxygen amount for blowing, O E ; Planned oxygen amount for blowing (according to furnace reaction model) Example A case will be described in which the method of the present invention is applied to the operation of a 100 ton converter. Target carbon concentration is 0.070% before main charge blowing.
According to the furnace reaction model, the expected amount of oxygen for blowing O
E was calculated and O E =5120 Nm 3 was obtained. The exhaust gas integral correction value k1 , which is the correction coefficient for the exhaust gas decarburization rate, is calculated from the actual value of the previous charge using equations (3) and (4).
k 1 = 0.99 was calculated, and the correction value k 2 for the fluctuation of k 1 due to operating conditions was obtained from equation (5) using the operating condition data of the previous charge and main charge as k 2 = k 2 2 /k 2 1 = 1.11. . After the start of blowing, the exhaust gas decarburization rates A and B were measured and calculated from time to time by exhaust gas analysis, and the calculated decarburization rates A * = 1.099A, B * = after correction of k 1 and k 2 mentioned above.
Display 1.099B on the CRT screen. Figure 2 shows these calculated decarburization rate trends. 75% to 88 of the planned oxygen amount for blowing O E (=5120Nm 3 )
The curve pattern of the calculated decarburization rate B * for about 3 minutes between 3840 and 4506 Nm 3 was shown in FIG. 1a. After recognizing the pattern, the estimated blow-off decarburization rate A * F of this pattern is determined using the multiple regression equation (7) under the blow-off target conditions of the main charge, and A * F = 55.5Kg・
C/min was obtained. This value was displayed on the CRT screen as the target blow-off decarburization rate A * (E) for the main charge. (2) According to formula A * = 1.099A, the calculated decarburization rate A * that is calculated and displayed every moment is (1) If α = 0.2 empirically, then A * (E) = 5.55Kg・C /minA * 66.6Kg・C/min, and then the blowing was stopped when the cumulative oxygen amount O S of blowing met the condition of 4870Nm 3 <O S (2) β = 0.95. The end carbon concentration (C F ) ACT was 0.066% or less, which is extremely close to the target carbon concentration of 0.070%. Figure 3 shows the effect when the method of this invention is applied to blowing control of a 100 ton converter. This is 763 heats over 20 days (38 average per day)
Target carbon concentration in the steel bath at the end of blowing (C F ) AIM and actual carbon concentration (C F ) ACT obtained for blowing with heat)
The deviation is expressed in days as σ defined by the following formula. However, n is the number of heats per day.For comparative reference, the data of blowing controlled only by static charge calculation before applying the method of this invention are also shown in FIG. Comparing the σ values of the two, it is 0.025% to 0.034% based on static charge calculation, whereas it is 0.002% to 0.005% according to this invention, about 1/10 of the former, and the It can be said that the concentration accuracy rate is significantly higher than that of the conventional method. The effects of this invention are summarized as follows. 1. The blowing control calculation formula such as the in-furnace reaction formula model alone can greatly improve the blow-stop performance, and is particularly effective for converter blowing control without sublance equipment. Of course, it will be even more effective if used in combination with a converter equipped with sublance equipment. 2. Conventional exhaust gas analysis methods measure and calculate the decarburization rate, estimate the carbon concentration in steel, and perform integral calculations to estimate the blowing oxygen amount up to the blow-off carbon concentration, which is extremely inaccurate, but this method This is a very simple method that only requires calculation of the decarburization rate.
Furthermore, the accuracy of measurement and calculation of the decarburization rate can be improved by various corrections.
第1図a〜eは脱炭速度曲線のパターンを例示
した説明図、第2図はこの発明の実施例について
示した脱炭速度推移線図、第3図は吹止め鋼浴脱
炭速度制御の効果の比較グラフである。
Fig. 1 a to e are explanatory diagrams illustrating patterns of decarburization rate curves, Fig. 2 is a decarburization rate transition diagram showing an example of the present invention, and Fig. 3 is a decarburization rate control in a stopper steel bath. This is a comparison graph of the effects of
Claims (1)
より排ガス脱炭速度を算出し、そのプロセス測定
値の測定誤差と操業条件の変動性の影響を除去す
るため、各々前チヤージの排ガス脱炭量に対する
実績脱炭量の排ガス積分補正値およびその操業条
件による重回帰式から求めた変動補正値によつて
補正された計算脱炭速度A*、B*を逐次求める
こと、吹錬末期の或る期間の前記脱炭速度B*曲
線パターンを、数種類の曲線パターンの判定条件
から自動的に認識し決定すること、あらかじめ脱
炭速度曲線パターンによつて区分された吹止脱炭
速度の操業条件による重回帰式から、本チヤージ
の推定吹止脱炭速度A* Fを算出し、これを本チヤ
ージの目標吹止脱炭速度A*(E)とすること、計算脱
炭速度A*と目標吹止脱炭速度A*(E)を表示装置に
逐次表示しながら比較監視すること、前記計算脱
炭速度A*が目標吹止脱炭速度A*(E)の吹止条件を
満足すること、および吹錬積算酸素量が炉内反応
モデルによる吹錬酸素量の吹止条件を満足するこ
とをもとにして吹錬終了時点を制御することの結
合を特徴とする転炉の吹止炭素濃度の制御方法。1. In the converter oxygen blowing process, the exhaust gas decarburization rate is calculated using a known exhaust gas analysis method, and in order to eliminate the effects of measurement errors in the process measurement values and variability of operating conditions, the exhaust gas decarburization rate of each pre-charge Calculated decarburization rates A * and B * corrected by the exhaust gas integral correction value of the actual decarburization amount with respect to the actual decarburization amount and the fluctuation correction value obtained from the multiple regression equation depending on the operating conditions are successively determined. automatically recognizing and determining the decarburization rate B * curve pattern for the period during which the decarburization rate B* curve pattern is determined from several types of curve pattern determination conditions; Calculate the estimated blow-off decarburization rate A * F for this charge from the multiple regression equation, and use this as the target blow-off decarburization rate A * (E) for this charge, and calculate the calculated decarburization speed A * and the target. Compare and monitor the blow-off decarburization rate A * (E) while sequentially displaying it on the display device, and make sure that the calculated decarburization rate A * satisfies the blow-off condition of the target blow-off decarburization rate A * (E). , and controlling the end point of blowing based on the blowing cumulative oxygen amount satisfying the blowing oxygen amount blowing condition according to the in-furnace reaction model. How to control concentration.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9522877A JPS5428718A (en) | 1977-08-09 | 1977-08-09 | Method of controlling carbon concentration in converter operation |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9522877A JPS5428718A (en) | 1977-08-09 | 1977-08-09 | Method of controlling carbon concentration in converter operation |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5428718A JPS5428718A (en) | 1979-03-03 |
| JPS6115127B2 true JPS6115127B2 (en) | 1986-04-22 |
Family
ID=14131890
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9522877A Granted JPS5428718A (en) | 1977-08-09 | 1977-08-09 | Method of controlling carbon concentration in converter operation |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5428718A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2019183227A (en) * | 2018-04-11 | 2019-10-24 | 日本製鉄株式会社 | Converter parameter deriving device, converter parameter deriving method and program |
-
1977
- 1977-08-09 JP JP9522877A patent/JPS5428718A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2019183227A (en) * | 2018-04-11 | 2019-10-24 | 日本製鉄株式会社 | Converter parameter deriving device, converter parameter deriving method and program |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5428718A (en) | 1979-03-03 |
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