JPS635449B2 - - Google Patents

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Publication number
JPS635449B2
JPS635449B2 JP15178580A JP15178580A JPS635449B2 JP S635449 B2 JPS635449 B2 JP S635449B2 JP 15178580 A JP15178580 A JP 15178580A JP 15178580 A JP15178580 A JP 15178580A JP S635449 B2 JPS635449 B2 JP S635449B2
Authority
JP
Japan
Prior art keywords
amount
exhaust gas
gas
generated
flow rate
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
Application number
JP15178580A
Other languages
Japanese (ja)
Other versions
JPS5776119A (en
Inventor
Hideji Takeuchi
Nagayasu Betsusho
Kyoji Nakanishi
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
JFE Steel Corp
Original Assignee
Kawasaki Steel Corp
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Kawasaki Steel Corp filed Critical Kawasaki Steel Corp
Priority to JP15178580A priority Critical patent/JPS5776119A/en
Publication of JPS5776119A publication Critical patent/JPS5776119A/en
Publication of JPS635449B2 publication Critical patent/JPS635449B2/ja
Granted legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21CPROCESSING OF PIG-IRON, e.g. REFINING, MANUFACTURE OF WROUGHT-IRON OR STEEL; TREATMENT IN MOLTEN STATE OF FERROUS ALLOYS
    • C21C5/00Manufacture of carbon-steel, e.g. plain mild steel, medium carbon steel or cast steel or stainless steel
    • C21C5/28Manufacture of steel in the converter
    • C21C5/38Removal of waste gases or dust

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Manufacturing & Machinery (AREA)
  • Materials Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)

Description

【発明の詳細な説明】 この発明は吹錬に伴つて転炉から発生する可燃
性の排ガスの回収方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for recovering flammable exhaust gas generated from a converter during blowing.

周知のように、酸素転炉において吹錬中に発生
する排ガスは、溶銑が脱炭されることによるCO
を主成分とし、純酸素底吹転炉の場合には炉底羽
口を冷却するために供給する炭化水素が分解する
ことによるCOやH2をも含むため熱量が極めて高
いものであり、そのため従来から転炉排ガスをエ
ネルギー源として利用している。
As is well known, the exhaust gas generated during blowing in an oxygen converter is CO2 caused by the decarburization of hot metal.
In the case of a pure oxygen bottom-blown converter, the heat content is extremely high as it also contains CO and H 2 due to the decomposition of the hydrocarbons supplied to cool the bottom tuyere. Conventionally, converter exhaust gas has been used as an energy source.

従来、転炉排ガスをエネルギー源として利用す
る方式として、転炉排ガスを炉上煙道部に設けた
ボイラにて燃焼させ、蒸気として熱回収する燃焼
方式と、転炉排ガスをガスホルダーに導いて回収
する非燃焼方式とが知られているが、近年、エネ
ルギー価格の上昇に伴い後者の非燃焼方式が主流
となりつつある。この非燃焼方式により排ガス回
収を行なう場合、排ガスが可燃性であり、空気と
の混合比がある一定値に達すると爆発する危険が
あるため、回収に先立つて煙道内の空気を排除
し、また回収終了後においては煙道内の排ガスを
排除しておく必要がある。そのため従来から吹錬
開始後排ガス回収に移行する前に、炉口部から煙
道内に空気を吸引導入して排ガスを燃焼させ、そ
の結果生成するCO2,H2O,N2を主成分とした
不活性ガス層で煙道内の空気を置換し、また排ガ
ス回収終了後においても同様な操作を行なつて煙
道内の排ガスを燃焼させ、不活性ガス層を煙道内
に生成するようにしている。
Conventionally, two methods have been used to utilize converter exhaust gas as an energy source: one is to combust converter exhaust gas in a boiler installed in the flue above the furnace and recover heat as steam, and the other is to direct converter exhaust gas to a gas holder. A non-combustion method that recovers energy is known, but in recent years, the latter non-combustion method has become mainstream as energy prices have increased. When collecting exhaust gas using this non-combustion method, the exhaust gas is flammable and there is a risk of explosion if the mixture ratio with air reaches a certain value, so the air in the flue must be removed before collection. After completion of recovery, it is necessary to eliminate the exhaust gas in the flue. Therefore, conventionally, after the start of blowing and before transitioning to exhaust gas recovery, air is sucked into the flue from the furnace mouth and the exhaust gas is combusted, and the resulting CO 2 , H 2 O, and N 2 are the main components. The air in the flue is replaced with an inert gas layer, and the same operation is performed after exhaust gas collection is completed to combust the flue gas and create an inert gas layer inside the flue. .

第1図は吹錬開始から吹錬終了までの間におけ
る従来の回収方法による排ガス流量の経時変化を
可燃性ガス発生量の経時変化と共に示すグラフで
あつて、まず、炉内から発生する可燃性ガス量は
吹錬開始時から増加し、脱炭最盛期にほぼ一定と
なり、そして吹錬末期には鋼浴中の炭素の減少と
ともに脱炭に使用される酸素が減少して鉄が酸化
されるため可燃性ガス量が漸次減少する。また、
吹錬中に固体酸素を含む副原料を鋼浴中に投入す
ると脱炭反応が促進されるので可燃性ガス量が増
加する(第1図中のA期)。これに対し、排ガス
量は、吹錬開始と同時に集塵器に設けたダンパを
開いて炉口部の圧力を減ずることにより外部から
多量の空気を吸入して予め定めた流量に設定し
(期)、この状態を所定時間保つ。しかる後、ダ
ンパを絞つて排ガス流量を漸次減少させ、所定の
流量に設定する(期)。従来の排ガス回収方法
では上記の操作によりこの〜期に不活性ガス
層を形成しているが、この期間における排ガス流
量制御すなわち吸入空気量の制御を溶銑の成分や
温度等の性状あるいは操業条件に拘わらず予め定
められた一定時間継続して行ない、従来一般には
最低限必要な不活性ガス量よりも2〜3倍の量の
不活性ガスが生じるように行ない、煙道内の空気
を不活性ガスで置換したとみなしている。そし
て、排ガス流量を所定の流量まで減少させた後、
炉口部からの噴出や空気の過剰吸入を防止するよ
うダンパを調整し(〜期)、COガス濃度が設
定値に達し、回収ガスの熱量が要求値まで上昇し
かつO2ガス濃度が爆発を誘引しない濃度まで減
少した時点(期終了時)から排ガス回収を開始
する。以後、吹錬終了時の炭素濃度を制御するた
めのデータを得る目的でサブランスを鋼溶中に挿
入するまでの間(期)排ガス回収を継続し、そ
れ以降は可燃性ガスの発生如何に拘わらず排ガス
流量を多くして外部から空気を吸入し、もつて可
燃性ガスを燃焼させることにより不活性ガス層を
生成させる(期)。
Fig. 1 is a graph showing the change over time in the exhaust gas flow rate due to the conventional recovery method from the start of blowing to the end of blowing, together with the change over time in the amount of combustible gas generated. The amount of gas increases from the beginning of blowing, becomes almost constant at the peak of decarburization, and then, at the end of blowing, as the carbon in the steel bath decreases, the oxygen used for decarburization decreases and the iron is oxidized. Therefore, the amount of combustible gas gradually decreases. Also,
When an auxiliary material containing solid oxygen is introduced into the steel bath during blowing, the decarburization reaction is promoted and the amount of combustible gas increases (period A in FIG. 1). On the other hand, the amount of exhaust gas is set at a predetermined flow rate by opening a damper installed in the precipitator at the same time as blowing starts and reducing the pressure at the furnace mouth, sucking in a large amount of air from outside. ) and maintain this state for a predetermined period of time. Thereafter, the damper is throttled to gradually reduce the exhaust gas flow rate and set to a predetermined flow rate (phase). In the conventional exhaust gas recovery method, an inert gas layer is formed during this period by the above-mentioned operation, but the exhaust gas flow rate control during this period, that is, the control of the amount of intake air, can be controlled depending on the properties such as hot metal components and temperature, or operating conditions. Regardless of the situation, the process is continued for a predetermined period of time, and the process is performed to generate an amount of inert gas that is 2 to 3 times the minimum amount of inert gas that is conventionally required. It is assumed that it has been replaced with . After reducing the exhaust gas flow rate to a predetermined flow rate,
The damper is adjusted to prevent blow-off from the furnace mouth and excessive intake of air (period ~), and the CO gas concentration reaches the set value, the calorific value of the recovered gas rises to the required value, and the O 2 gas concentration explodes. Exhaust gas collection will begin when the concentration has decreased to a level that does not induce oxidation (at the end of the period). After that, exhaust gas collection was continued until the sublance was inserted into the steel melt in order to obtain data for controlling the carbon concentration at the end of blowing, and from then on, regardless of whether flammable gas was generated. First, the exhaust gas flow rate is increased to suck in air from outside, and the combustible gas is burned to generate an inert gas layer (phase).

しかるに、上述の従来の排ガス回収方法は、吹
錬開始時における不活性ガス層の生成を、想定さ
れた平均的操業条件下における最低限必要な不活
性ガス層の2〜3倍の量の不活性ガス層が生じる
よう一律に一定量の空気を吸入して可燃性ガスを
燃焼させることにより行なうものであるため、換
言すれば溶銑の成分や温度等の性状あるいは吹込
み酸素量等の操業条件によつて決まる実際の可燃
性ガス発生量に合わせて吸入空気量の制御を行な
うものではないため、多くの場合回収可能な可燃
性ガスまでも燃焼させており、また吹錬開始時に
固体酸素を含有する副原料(例えば鉄鉱石)を多
量に添加する場合のように多量のCOガスが発生
する場合には、逆に吸入酸素量が不足し、不活性
ガス層が生成しないまま排ガス回収を開始してし
まう危険があつた。さらに、従来の排ガス回収方
法にあつては、サブランスを鋼中に挿入した後は
可燃性ガスが未だ多量に発生していても排ガス回
収を中止し、空気を外部から吸入して不活性ガス
層を生成させるものであるから、回収可能な可燃
性ガスが多量に燃焼してしまつている。このよう
に従来の排ガス回収方法は、排ガス回収前後にお
ける不活性ガス層の生成時に、排ガス流量を制御
することによる空気の吸入を一律に一定時間継続
して行なつており、しかも不活性ガス層の量を本
質的に必要な量の2〜3倍に設定しているため、
回収可能な可燃性ガスが多量に燃焼し、排ガスの
回収量が理論的に回収可能な量よりも相当少なく
なり、また溶銑中の炭素濃度によつては逆に吸入
空気量が不足し、不活性ガス層が十分に生成され
ないまま排ガス回収を行なう危険があつた。
However, the above-mentioned conventional flue gas recovery method reduces the generation of an inert gas layer at the start of blowing to an amount of inert gas that is two to three times the minimum required inert gas layer under assumed average operating conditions. This is done by uniformly inhaling a certain amount of air and burning flammable gas so as to generate an active gas layer.In other words, it depends on the properties of the hot metal, such as its composition and temperature, and the operating conditions, such as the amount of oxygen blown into it. Since the amount of intake air is not controlled according to the actual amount of combustible gas generated, which is determined by When a large amount of CO gas is generated, such as when a large amount of auxiliary raw materials (e.g. iron ore) is added, the amount of intake oxygen becomes insufficient, and exhaust gas recovery begins before an inert gas layer is formed. There was a danger of doing so. Furthermore, in the conventional exhaust gas recovery method, after inserting the sublance into the steel, exhaust gas recovery is stopped even if a large amount of flammable gas is still generated, and air is sucked in from the outside to form an inert gas layer. As a result, a large amount of recoverable combustible gas is burned. In this way, conventional exhaust gas recovery methods uniformly and continuously draw air for a certain period of time by controlling the exhaust gas flow rate when an inert gas layer is generated before and after exhaust gas recovery. Since the amount of is set to 2 to 3 times the amount that is essentially required,
A large amount of recoverable combustible gas is combusted, and the amount of exhaust gas recovered is considerably less than the amount that can be theoretically recovered.Also, depending on the carbon concentration in the hot metal, the amount of intake air may be insufficient, resulting in There was a risk that the exhaust gas would be recovered before a sufficient active gas layer was generated.

この発明は上記の事情に鑑みてなされたもの
で、不活性ガス層を過不足なく生成し、もつて排
ガス回収率を向上するとともに回収ガス中に空気
が混入することによる爆発の危険を解消すること
のできる排ガス回収方法を提供することを目的と
するものである。
This invention was made in view of the above circumstances, and aims to generate an inert gas layer in just the right amount, improve the exhaust gas recovery rate, and eliminate the risk of explosion due to air being mixed in the recovered gas. The purpose of this invention is to provide a method for recovering exhaust gas that can be used.

すなわちこの発明は、溶銑の成分や温度等のデ
ータに基づいて脱炭酸素効率を予め算定するとと
もに、その脱炭酸素効率と吹込み酸素量や固体酸
素量等の操業条件とに基づいて可燃性ガス発生量
を予め算定し、排ガスの回収前後において不活性
ガス層を生成すべく前記算定された可燃性ガスの
一部を燃焼させるに必要な量の空気を煙道内に吸
入するものであつて、吸入酸素量をいわゆる先行
制御する排ガス回収方法である。
In other words, this invention calculates the decarburization oxygen efficiency in advance based on data such as the composition and temperature of hot metal, and also calculates flammability based on the decarburization oxygen efficiency and operating conditions such as the amount of blown oxygen and the amount of solid oxygen. The amount of gas generated is calculated in advance, and the amount of air necessary to burn a part of the calculated flammable gas is sucked into the flue in order to generate an inert gas layer before and after collecting the exhaust gas. This is an exhaust gas recovery method that performs so-called advance control of the intake oxygen amount.

以下、この発明の方法をより詳細に説明する。
なお、炉底羽口を有する転炉においては炉底羽口
冷却用に炭化水素を用いるため、排ガス中のH2
濃度がLD転炉の排ガスに比較して高くなり、し
たがつてこのような場合には不活性ガス層を生成
するに際し、H2の燃焼についても考慮する必要
があるが、通常はCOガスが排ガスの主成分とみ
なせるので、以下の説明においてはCOガスのみ
からなる排ガスを例として説明する。
The method of the present invention will be explained in more detail below.
In addition, in a converter with a bottom tuyere, hydrocarbons are used to cool the bottom tuyere, so H2 in the exhaust gas is
The concentration is higher than that of the exhaust gas of the LD converter, so in such cases it is necessary to consider the combustion of H 2 when creating an inert gas layer, but normally CO gas is Since it can be considered as the main component of exhaust gas, the following explanation will be given using exhaust gas consisting only of CO gas as an example.

まず、脱炭酸素効率ηc(%)は ηc≡脱炭に消費される酸素量/(吹錬酸素量+固
体酸素量)×100 で定義される。
First, the decarburization oxygen efficiency η c (%) is defined as η c ≡Amount of oxygen consumed for decarburization/(Amount of blowing oxygen + Amount of solid oxygen)×100.

一方、溶銑中の炭素は +O2→2CO のように反応するから、 Qcp=(Vp2+Sp2)×ηc/100×2 ……(1) となる。ここで、Qcpは炉内発生COガス量(N
m3/min)、Vp2は吹錬酸素量(Nm3/min),Sp2
は気体に換算した固体酸素量(Nm3/min)であ
る。(1)式中Vp2とSp2とは共に操業条件から知るこ
とができるから、ηcがわかればQcpを算出するこ
とができる。ところで、ηcは装入される溶銑の温
度(T)、成分(特にSi,Mn等)、溶銑比(HR)
などの関数であり、(2)式で表わされる。
On the other hand, since carbon in hot metal reacts as C + O 2 → 2CO, Q cp = (V p2 + S p2 ) x η c /100 x 2 (1). Here, Q cp is the amount of CO gas generated in the furnace (N
m 3 /min), V p2 is the blowing oxygen amount (Nm 3 /min), S p2
is the amount of solid oxygen (Nm 3 /min) converted into gas. Since both V p2 and S p2 in equation (1) can be known from the operating conditions, Q cp can be calculated if η c is known. By the way, η c is the temperature (T) of the charged hot metal, the components (especially Si, Mn, etc.), and the hot metal ratio (HR).
It is a function such as, and is expressed by equation (2).

ηc=ηc(T,SiMn,HR,…) ……(2) (2)式中Siは溶銑中のSi濃度、Mnは溶銑中のMn
濃度である。
η c = η c (T, Si , Mn , HR,...) ...(2) In the formula (2), Si is the Si concentration in the hot metal, and Mn is the Mn in the hot metal.
It is concentration.

したがつて、脱炭酸素効率ηcの経時変化は実操
業データを解析することにより容易に求めること
ができる。第2図はSiをパラメーターとし、Si
0.15%,0.30%,0.50%のときの脱炭酸素効率ηc
の経時変化を示すグラフである。
Therefore, the change over time in the decarburization oxygen efficiency η c can be easily determined by analyzing actual operation data. Figure 2 uses Si as a parameter, and Si is
Decarburization oxygen efficiency η c at 0.15%, 0.30%, 0.50%
It is a graph showing a change over time.

ところで、炉内発生ガスを完全燃焼させるのに
必要な吸入空気量Qairは、上記Qcpの量の炉内発
生COガスを完全燃焼させるのに必要な酸素量が
1/2Qcpであり、空気中の酸素濃度が20%であるこ とから、 Qair=5/2Qcp(Nm3/min) ……(3) となり、したがつて燃焼後の排ガス中のN2量,
CO2量はそれぞれ2Qcp,Qcp(Nm3/min)となり、
その結果排ガス流量QWGは QWG=2Qcp+Qcp=3Qcp(Nm3/min) となるから、この式に(1)式、(2)式を代入すれば、 となる。
By the way, the amount of intake air Q air required to completely burn the gas generated in the furnace is 1/2 Q cp , which is the amount of oxygen required to completely burn the amount of CO gas generated in the furnace in the amount of Q cp above. Since the oxygen concentration in the air is 20%, Q air = 5/2Q cp (Nm 3 /min) ...(3), and therefore the amount of N 2 in the exhaust gas after combustion,
The amount of CO 2 is 2Q cp and Q cp (Nm 3 /min), respectively.
As a result, the exhaust gas flow rate Q WG is Q WG = 2Q cp + Q cp = 3Q cp (Nm 3 /min), so by substituting equations (1) and (2) into this equation, we get becomes.

上述のように、吹錬開始前の溶銑の成分や温度
等の性状あるいは操業条件に基づいて脱炭酸素効
率ηcの経時変化を算定することができるので、そ
の算定結果に基づいて炉内発生ガスを完全燃焼さ
せた際に生じる排ガス量すなわち不活性ガス量を
算定することができる。したがつて、不活性ガス
量が煙道内の空気を置換するに必要な量となるよ
う(4)式に従つて排ガス流量の制御すなわち吸入空
気量の制御を行なえば、可燃性ガスを過不足なく
燃焼させて必要量の不活性ガス層を生成すること
ができる。
As mentioned above, it is possible to calculate the change over time in the decarburization oxygen efficiency η c based on the properties such as the composition and temperature of the hot metal before the start of blowing, or the operating conditions. It is possible to calculate the amount of exhaust gas, that is, the amount of inert gas produced when gas is completely combusted. Therefore, if the exhaust gas flow rate is controlled according to equation (4), that is, the intake air amount is controlled so that the amount of inert gas is the amount necessary to replace the air in the flue, there will be no excess or deficiency of flammable gas. The required amount of inert gas layer can be generated by combustion without any waste.

上述の脱炭酸素効率および排ガス流量につき、
溶銑中のSi濃度をパラメーターとした具体例を示
せば以下の通りである。まず、脱炭酸素効率ηc
吹錬開始から100秒経過するまでの間における経
時変化は前掲の第2図に示すようになるが、同様
の経時変化を多くのヒートに対して解析し、吹錬
開始後2秒,50秒,100秒の3点を代表点として
採ると、それぞれの時刻における脱炭酸素効率
η2 c,η50 c,η100 cはE−(1)〜(3)式で表わされる。
Regarding the decarburization oxygen efficiency and exhaust gas flow rate mentioned above,
A specific example using the Si concentration in hot metal as a parameter is as follows. First, the change over time in the decarburization oxygen efficiency η c from the start of blowing until 100 seconds has passed is shown in Figure 2 above, and similar changes over time were analyzed for many heats. If three points at 2 seconds, 50 seconds, and 100 seconds after the start of blowing are taken as representative points, the decarburization oxygen efficiency η 2 c , η 50 c , η 100 c at each time is E−(1) to (3 ) expression.

回帰式 寄与率 η2 c=39.37−42.63Si(%) ρ=0.7215
……E−(1) η50 c=75.57−65.56Si(%) ρ=0.7695
……E−(2) η100 c=86.38−69.19Si(%) ρ=0.6771
……E−(3) この3点における回帰式をもとにηcの経時変化
を2次曲線近似すると、E−(4)式が求められ、ηc
Siと時間tの関数で表わすことができる。
Regression formula Contribution rate η 2 c = 39.37−42.63 Si (%) ρ = 0.7215
...E-(1) η 50 c = 75.57-65.56 Si (%) ρ = 0.7695
...E-(2) η 100 c = 86.38-69.19 Si (%) ρ = 0.6771
……E-(3) By approximating the temporal change of η c with a quadratic curve based on the regression equation at these three points, equation E-(4) is obtained, and η c
can be expressed as a function of Si and time t.

t=0〜100秒において、 ηc=(−5.01×10-3+3.86×10-3 Si)t2 +(0.967−0.652Si)t +(39.7−42.6Si)(%) ……E−(4) 第3図にSi=0.25%のときのE−(4)で求めた排ガ
ス流量パターンを示す。第3図中斜線を施した領
域は不活性ガスの領域を示すが、ここで不活性ガ
スとはCO<12.5%,H2<4.0%,CO+H2<11.0
%,O2<5.5%である。したがつて、排ガス流量
が第3図に斜線を施して示した範囲内に入るよう
に流量制御すれば、すなわち、 (吸入空気量過少によるCO>12.5%、H2>4%
となる流量)<排ガス流量<(吸入空気量過多によ
るO2>5.5%となる流量) となるよう流量制御すれば、不活性ガスを得るこ
とができる。そして、不活性ガスの総量が煙道内
の空気を置換するのに十分となつた時点で外部か
らの空気の吸入を止めれば、不活性ガス層を過不
足なく生成することができる。
At t = 0 to 100 seconds, η c = (-5.01×10 -3 +3.86×10 -3 Si ) t 2 + (0.967-0.652 Si ) t + (39.7-42.6 Si ) (%)...E -(4) Figure 3 shows the exhaust gas flow rate pattern obtained in E-(4) when Si = 0.25%. The shaded area in Figure 3 indicates the inert gas area, where the inert gas is CO<12.5%, H 2 <4.0%, CO+H 2 <11.0.
%, O 2 <5.5%. Therefore, if the flow rate is controlled so that the exhaust gas flow rate falls within the shaded range in Figure 3, (CO > 12.5%, H 2 > 4% due to insufficient intake air amount)
Inert gas can be obtained by controlling the flow rate so that the following formula is satisfied: If the intake of air from the outside is stopped when the total amount of inert gas becomes sufficient to replace the air in the flue, the inert gas layer can be generated in just the right amount.

つぎに、吹錬末期における不活性ガス層の生成
について説明すると、まず、脱炭速度dc/dp2
その時点での鋼中炭素濃度、溶鋼重量WST、パ
ラメータαなどの関数となる。
Next, to explain the formation of an inert gas layer at the final stage of blowing, first, the decarburization rate d c /d p2 is a function of the carbon concentration in the steel C at that point, the molten steel weight W ST , the parameter α, etc. .

−dc/dp2=f(,WST,α,…) ……(5) ここで、αはサブランス測定による鋼中炭素濃
SL、溶鋼温度TSL等を要因として回帰により
求めたパラメータである。−dc/dp2の経時的な値
は、の初期値として SLを用いて計算を行な
い、例えば2秒後のを推定し、このを用いて
−dc/dp2を計算し、さらに2秒後のを推定す
ることを繰返すことによつて求めることができ
る。
−d c /d p2 = f ( C , W ST , α, …) ...(5) Here, α was determined by regression using the carbon concentration in steel C SL measured by sublance measurement, the molten steel temperature T SL, etc. as factors. It is a parameter. The value of -d c /d p2 over time is calculated using C SL as the initial value of C , for example, estimate C after 2 seconds, and use this C to calculate -d c /d p2 . It can be obtained by repeating the process of estimating C after 2 seconds.

また、脱炭酸素効率η′cは、脱炭速度、溶鋼重
量の関数で表わされ、dc/dp2の単位を(%C/
Nm3)とし、WSTの単位を(ton)とすると、 +1/2O2→CO であるから η′c=(WST+106×ΔC/100/12×0.0224/2/
ΔO2)×100(%)=933WST・ΔC/ΔO2(%) =−933WSTdc/dp2(%) ……(6) となり、したがつて脱炭酸素効率η′cの経時的な
変化を計算することができる。したがつて、可燃
性ガスを完全燃焼させた後の排ガス量Q′WGは、(6)
式から求まる脱炭酸素効率η′cに基づき(7)式によ
り算定することができる。
In addition, decarburization oxygen efficiency η' c is expressed as a function of decarburization rate and molten steel weight, and the unit of d c /d p2 is (%C/
Nm 3 ) and the unit of W ST is (ton). Since C + 1/2O 2 →CO, η′ c = (W ST +10 6 ×ΔC/100/12×0.0224/2/
ΔO 2 ) × 100 (%) = 933W ST・ΔC/ΔO 2 (%) = −933W ST d c /d p2 (%) ……(6) Therefore, the decarburization oxygen efficiency η′ c over time changes can be calculated. Therefore, the amount of exhaust gas Q′ WG after completely burning the combustible gas is (6)
It can be calculated using equation (7) based on the decarburization oxygen efficiency η′ c found from the equation.

Q′WG=3×(Vp2+Sp2)×η′c/100×2……(7) したがつて、吹錬末期においては、サブランス
測定によつて得られる溶鋼のデータ等に基づいて
脱炭酸素効率η′cを算定することができるので、
その算定結果に基づいて炉内発生ガスを完全燃焼
させた際に生じる排ガス流量すなわち不活性ガス
量を算定することができる。したがつて、不活性
ガス量が煙道内に充満するよう(7)式に従つて排ガ
ス流量の制御すなわち吸入空気量の制御を行なえ
ば、可燃性ガスを過不足なく燃焼させて必要量の
不活性ガス層を生成することができる。
Q' WG = 3 × (V p2 + S p2 ) × η' c /100 × 2... (7) Therefore, at the final stage of blowing, decomposition is Since the carbon-oxygen efficiency η′ c can be calculated,
Based on the calculation result, it is possible to calculate the exhaust gas flow rate, that is, the amount of inert gas generated when the gas generated in the furnace is completely combusted. Therefore, if the exhaust gas flow rate is controlled according to equation (7), that is, the amount of intake air is controlled so that the flue is filled with the amount of inert gas, the combustible gas can be burned in just the right amount and the necessary amount can be achieved. An active gas layer can be generated.

第4図はサブランス測定による鋼中炭素濃度
が0.2%、送酸素流量が670Nm3/min、溶鋼重量
が230tonの場合の吹錬末期における脱炭酸素効率
η′cの経時変化と不活性ガスとなる排ガス流量
Q′WGとの具体例を示すグラフである。したがつて
排ガス流量が第4図に斜線を施して示した不活性
ガス領域内に入るように流量制御すれば不活性ガ
スを得ることができ、そして外部から空気を吸入
し始めた時点から吹止め時までの間に生じる不活
性ガスの総量が、煙道内を充満するに十分な量と
なるように空気吸入開始時を設定すれば、不活性
ガス層を過不足なく生成することができる。
Figure 4 shows the carbon concentration C in steel measured by sublance measurements.
is 0.2%, the oxygen flow rate is 670Nm 3 /min, and the weight of molten steel is 230 tons. Changes in decarburization oxygen efficiency η′ c over time and the flow rate of exhaust gas that becomes inert gas at the final stage of blowing.
This is a graph showing a specific example with Q′ WG . Therefore, inert gas can be obtained by controlling the flow rate so that the exhaust gas flow rate falls within the inert gas region shown with diagonal lines in Fig. By setting the time to start air intake so that the total amount of inert gas generated up to the time of stopping is sufficient to fill the flue, it is possible to generate just the right amount of inert gas layer.

第5図はこの発明の回収方法による排ガス流量
を可燃性ガス発生量と共に示すグラフであつて、
吹錬開始と共に集塵器に設けたダンパを開いて排
ガス流量を(4)式で求まる流量に設定し、その結果
煙道内に外部から空気を吸入して可燃性ガスを燃
焼させることにより不活性ガスとし、そして不活
性ガスの総量が煙道内の空気を置換するのに十分
な量になる時点まで、すなわち不活性ガス層を煙
道内に生成する時点まで(′期)空気を吸入す
る。しかる後、ダンパを絞ることにより炉口部か
ら空気を吸入せずかつ可燃性ガスが噴出しないよ
うに排ガス流量を制御してCOガス濃度、O2ガス
濃度が所定の値になるまで待ち(′期)、その後
排ガスの回収を開始する。そして、サブランスに
よる測定を行なつた後は、サブランス測定により
得られたデータにより(7)式で求まる排ガス流量
Q′WGが不活性ガス層として十分な量となるよう吹
錬終了前所定時間(′期)ダンパを開いて空気
を吸入し、不活性ガス層を生成する。したがつ
て、排ガス回収は第5図の′期と′期の間行な
うことになる。
FIG. 5 is a graph showing the exhaust gas flow rate according to the recovery method of the present invention together with the amount of combustible gas generated,
At the start of blowing, the damper installed in the precipitator is opened and the exhaust gas flow rate is set to the flow rate determined by equation (4). As a result, air is drawn into the flue from the outside and the flammable gas is combusted, making it inert. gas and draw air in until the total amount of inert gas is sufficient to displace the air in the flue, i.e. to create an inert gas layer in the flue (period '). After that, the exhaust gas flow rate is controlled by restricting the damper so that air is not sucked in from the furnace mouth and flammable gas is not spewed out, and wait until the CO gas concentration and O 2 gas concentration reach the predetermined values (' period), then exhaust gas collection will begin. After measuring with the sublance, the exhaust gas flow rate is calculated using equation (7) using the data obtained from the sublance measurement.
In order to create a sufficient amount of Q' WG to form an inert gas layer, the damper is opened for a predetermined period (' period) before the end of blowing to suck in air and generate an inert gas layer. Therefore, exhaust gas recovery will be carried out between periods '' and '' in FIG.

しかして、上記の吹錬方法によれば、転炉から
発生する可燃性ガスを燃焼させて不活性ガスとす
るための排ガス流量が予め算定されて知られてお
り、その不活性ガス量が必要十分な量の不活性ガ
ス層となるように流量制御するものであるから、
第5図における′期および′期において回収可
能な可燃性ガスを過度に燃焼させることがなく、
したがつて回収ガス量を従来になく多くすること
ができる。
However, according to the above-mentioned blowing method, the exhaust gas flow rate for burning the flammable gas generated from the converter into inert gas is calculated and known in advance, and the amount of inert gas is required. Since the flow rate is controlled to create a sufficient amount of inert gas layer,
In periods '' and '' in Figure 5, recoverable combustible gas is not burned excessively;
Therefore, the amount of recovered gas can be increased more than ever before.

なお、上記の説明では可燃性ガスとしてCOガ
スのみが発生する場合について説明したが、炉底
羽口を冷却するために炭化水素を吹込んだ場合に
はH2ガスが転炉排ガスに含まれるようになるが、
その量は用いる炭化水素の種類や吹込み量によつ
て容易に算定することができ、したがつて炉底羽
口を冷却するために炭化水素を吹込む場合であつ
ても不活性ガス層を生成するための排ガスの流量
を算定し、過不足なく不活性ガス層を生成するこ
とができる。
Note that the above explanation deals with the case where only CO gas is generated as a combustible gas, but when hydrocarbons are injected to cool the bottom tuyeres, H2 gas is included in the converter exhaust gas. However,
The amount can be easily calculated depending on the type of hydrocarbon used and the amount of injection. Therefore, even when hydrocarbons are injected to cool the bottom tuyere, an inert gas layer is required. By calculating the flow rate of exhaust gas to be generated, it is possible to generate an inert gas layer with just the right amount.

以上の説明で明らかなようにこの発明の転炉排
ガス回収方法によれば、排ガス回収の前後におけ
る不活性ガス層の生成時に、可燃性ガスの発生量
に応じた量の空気を外部から導入し、もつて必要
十分な量の不活性ガス層を生成するものであるか
ら、回収可能な可燃性ガスを不必要に燃焼させて
しまうことがなく、換言すれば排ガスの回収量を
全可燃性ガス量の90%程度にまで向上させること
ができ、また可燃性ガスの発生量に応じた量の空
気を外部から吸入するものであるから、吹錬開始
前に固体酸素を含有する副原料を溶銑内に投入し
ておく場合のように多量の可燃性ガスが発生する
場合であつても、不活性ガス層を十分に生成させ
ることができ、回収ガスの爆発などの危険を確実
に防止することができる。
As is clear from the above explanation, according to the converter exhaust gas recovery method of the present invention, air is introduced from the outside in an amount corresponding to the amount of combustible gas generated when an inert gas layer is generated before and after exhaust gas recovery. Since it generates a necessary and sufficient amount of inert gas layer, the recoverable combustible gas is not burned unnecessarily, and in other words, the amount of recovered exhaust gas is reduced to the total amount of flammable gas. Since the amount of air can be increased to about 90% of the amount of flammable gas generated from the outside and the amount of air is sucked in from the outside according to the amount of flammable gas generated, an auxiliary material containing solid oxygen is added to the hot metal before the start of blowing. Even when a large amount of flammable gas is generated, such as when the collected gas is injected into the tank, a sufficient inert gas layer can be generated to reliably prevent dangers such as explosions of recovered gas. Can be done.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は従来の排ガス回収方法による排ガス流
量の経時変化を可燃性ガス発生量の経時変化と共
に示すグラフ、第2図は脱炭酸素効率の経時変化
を示すグラフ、第3図は溶銑内Si濃度が0.25%の
ときの脱炭酸素効率の経時変化と不活性な排ガス
の流量とを示すグラフ、第4図はサブランス測定
による鋼中炭素濃度が0.2%のときの脱炭酸素効
率の経時変化と不活性な排ガスの流量とを示すグ
ラフ、第5図はこの発明の排ガス回収方法の一例
による排ガス流量の経時変化を可燃性ガス発生量
の経時変化と共に示す第1図同様なグラフであ
る。
Figure 1 is a graph showing the change in exhaust gas flow rate over time due to the conventional exhaust gas recovery method along with the change in combustible gas generation amount over time, Figure 2 is a graph showing the change in decarburization oxygen efficiency over time, and Figure 3 is a graph showing the change in the amount of combustible gas generated over time. A graph showing the change in decarburization oxygen efficiency over time and the flow rate of inert exhaust gas when the concentration is 0.25%. Figure 4 shows the change in decarburization oxygen efficiency over time when the carbon concentration in steel is 0.2% by sublance measurement. FIG. 5 is a graph similar to FIG. 1 showing the change over time in the flow rate of exhaust gas according to an example of the exhaust gas recovery method of the present invention together with the change over time in the amount of combustible gas generated.

Claims (1)

【特許請求の範囲】[Claims] 1 転炉排ガスの回収前後において煙道内に外部
から空気を吸入して転炉排ガスを燃焼させること
により不活性ガス層を煙道内に生成させる転炉排
ガス回収方法において、脱炭酸素効率の経時変化
を溶銑についてのデータに基づいて予め算定する
とともに、算定された脱炭酸素効率と吹錬操業条
件に基づいて転炉内から発生する可燃性ガス量を
予め算定し、転炉排ガスの回収前後において前記
算定された量の可燃性ガスを前記不活性ガス層を
生成すべく燃焼させるに必要な量の空気を煙道内
に吸入することを特徴とする転炉排ガス回収方
法。
1 Changes in decarburization oxygen efficiency over time in a converter exhaust gas recovery method in which an inert gas layer is generated in the flue by sucking air from the outside into the flue and burning the converter exhaust gas before and after recovering the converter exhaust gas. is calculated in advance based on data about hot metal, and the amount of combustible gas generated from the converter is calculated in advance based on the calculated decarburization oxygen efficiency and blowing operating conditions, and the amount of flammable gas generated from the converter is calculated before and after recovering the converter exhaust gas A converter exhaust gas recovery method comprising sucking into a flue an amount of air necessary to combust the calculated amount of combustible gas to generate the inert gas layer.
JP15178580A 1980-10-29 1980-10-29 Recovery of exhaust gas at converter Granted JPS5776119A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP15178580A JPS5776119A (en) 1980-10-29 1980-10-29 Recovery of exhaust gas at converter

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP15178580A JPS5776119A (en) 1980-10-29 1980-10-29 Recovery of exhaust gas at converter

Publications (2)

Publication Number Publication Date
JPS5776119A JPS5776119A (en) 1982-05-13
JPS635449B2 true JPS635449B2 (en) 1988-02-03

Family

ID=15526235

Family Applications (1)

Application Number Title Priority Date Filing Date
JP15178580A Granted JPS5776119A (en) 1980-10-29 1980-10-29 Recovery of exhaust gas at converter

Country Status (1)

Country Link
JP (1) JPS5776119A (en)

Also Published As

Publication number Publication date
JPS5776119A (en) 1982-05-13

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