AU2002308827B2 - Recycling Method of Waste Material by Using of Coal Based Iron Making Process - Google Patents
Recycling Method of Waste Material by Using of Coal Based Iron Making ProcessInfo
- Publication number
- AU2002308827B2 AU2002308827B2 AU2002308827A AU2002308827A AU2002308827B2 AU 2002308827 B2 AU2002308827 B2 AU 2002308827B2 AU 2002308827 A AU2002308827 A AU 2002308827A AU 2002308827 A AU2002308827 A AU 2002308827A AU 2002308827 B2 AU2002308827 B2 AU 2002308827B2
- Authority
- AU
- Australia
- Prior art keywords
- waste material
- dust
- melter gasifier
- reduction
- recycling method
- 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.)
- Ceased
Links
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 title claims description 93
- 239000002699 waste material Substances 0.000 title claims description 49
- 229910052742 iron Inorganic materials 0.000 title claims description 45
- 238000000034 method Methods 0.000 title claims description 43
- 238000004064 recycling Methods 0.000 title claims description 23
- 239000003245 coal Substances 0.000 title claims description 18
- 239000000428 dust Substances 0.000 claims description 78
- 239000002245 particle Substances 0.000 claims description 24
- 239000002994 raw material Substances 0.000 claims description 21
- 238000002844 melting Methods 0.000 claims description 19
- 239000000203 mixture Substances 0.000 claims description 16
- 238000007664 blowing Methods 0.000 claims description 15
- 230000008018 melting Effects 0.000 claims description 12
- 229910052799 carbon Inorganic materials 0.000 claims description 11
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 10
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 claims description 10
- 238000009833 condensation Methods 0.000 claims description 7
- 230000005494 condensation Effects 0.000 claims description 7
- 239000002184 metal Substances 0.000 claims description 4
- 229910052751 metal Inorganic materials 0.000 claims description 4
- 238000001035 drying Methods 0.000 claims description 2
- 238000002156 mixing Methods 0.000 claims 1
- 239000010802 sludge Substances 0.000 description 35
- 239000007789 gas Substances 0.000 description 15
- 229910000831 Steel Inorganic materials 0.000 description 11
- 239000010959 steel Substances 0.000 description 11
- 239000002893 slag Substances 0.000 description 8
- 239000000446 fuel Substances 0.000 description 7
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 6
- 229910052760 oxygen Inorganic materials 0.000 description 6
- 239000001301 oxygen Substances 0.000 description 6
- 238000003860 storage Methods 0.000 description 6
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 229910000805 Pig iron Inorganic materials 0.000 description 3
- 239000006227 byproduct Substances 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 238000002474 experimental method Methods 0.000 description 3
- 229910052698 phosphorus Inorganic materials 0.000 description 3
- 229910052717 sulfur Inorganic materials 0.000 description 3
- 229910052725 zinc Inorganic materials 0.000 description 3
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- 239000003638 chemical reducing agent Substances 0.000 description 2
- 238000002485 combustion reaction Methods 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 238000013329 compounding Methods 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 239000006185 dispersion Substances 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000007800 oxidant agent Substances 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 230000035699 permeability Effects 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 238000003723 Smelting Methods 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 238000009933 burial Methods 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 230000003009 desulfurizing effect Effects 0.000 description 1
- 230000002542 deteriorative effect Effects 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 229910000514 dolomite Inorganic materials 0.000 description 1
- 239000010459 dolomite Substances 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 150000002736 metal compounds Chemical class 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000005245 sintering Methods 0.000 description 1
- 238000007711 solidification Methods 0.000 description 1
- 230000008023 solidification Effects 0.000 description 1
Description
RECYCLING METHOD OF WASTE MATERIAL BY USING OF COAL BASED IRON
MAKING PROCESS
TECHNICAL FIELD
The present invention relates to a recycling method of dust
and sludge produced in iron and steel works, and more particularly,
to a recycling method by which waste material such as dust and
sludge outputted in an iron and steel working process can be
recycled as fuel and raw material in a coal based iron making
process .
BACKGROUND ART
In general, by-products outputted in most iron and steel
works can be mainly discriminated into slag, dust and sludge.
Although dust and sludge can be recycled as raw material in some
iron and steel working, smelting or cement manufacturing
processes since they are abundant with Fe and C components, a
large portion of the by-products tend to be buried through
solidification without recycling. Therefore, treatment and
recycling of the by-products are gradually becoming important environmental problems in the ironworks .
The iron and steel works output dust and sludge in each
process. Dust and sludge are mainly comprises compounds of carbon component useful as both of heat source and reducing agent,
Fe component useful as raw material of iron and Ca, Mg and so
on useful as supplementary raw material. Although dust and
sludge have particles sizes of 1mm or less, occasionally the
particle sizes thereof reach up to 8mm. Moisture content is
remarkably different according to processes of outputting sludge
and dust, or between dust and sludge.
Recycling of the dust and sludge is greatly dependent upon
several conditions such as component difference, moisture
content, particle size and so on. Therefore, dust is recycled
by a large quantity since it has low moisture content and can
be simply treated, whereas outputted sludge is recycled by about
half only.
The COREX process, i.e. one of coal based iron making process, generally uses two reactors such as a melter gasifier
20 and a reduction furnace 10. In the iron making process, iron
ore used as raw material is charged together with supplementary
raw material into the top of the reduction furnace 10, where iron
ore and supplementary raw material undergo reduction and
sintering due to reducing gas blown through the bottom of the
reduction furnace 10. Reduced iron ore and sintered
supplementary raw material are fed into the melter gasifier 20,
where they are hot melted to yield pig iron. Coal is charged into the hot melter gasifier 20 to produce reducing gas, which
is fed into the reduction furnace 10, in which char of the
remaining coal is used as heat source as it reacts with oxygen
at the bottom of the melter gasifier 20. In the meantime,
reference numerals 12, 210 and 222 each indicate an ore-charging
duct, a dust-recycling duct and an exhaust gas duct.
In the coal based iron making process using the above two
reactors, a large quantity of reducing gas is fed into the upper reduction furnace 10 from the lower melter gasifier 20 so that
fine dust of coal, reduced ore and supplementary raw material
can be fed on reducing gas into the reduction furnace 10. Since
this is a major reason for deteriorating the internal status of
the reduction furnace, a cyclone 21 is installed between the
melter gasifier 20 and the reduction furnace 10 in order to remove
fine dust from gas.
Fine dust trapped by the cyclone 21 is blown again through
a two-stage charging vessel into the melter gasifier 20, in which
melting condensation is carried out with a dust burner 213 in
order to prevent blown fine dust from dispersing again. In such melting condensation, oxygen is fed together with the fine dust
into the dust burner to burn fine dust at the leading end of the
dust burner by using carbon contained in coal as fuel and blown
oxygen and oxygen contained in some of reduced ore as oxidizing agent .
This makes reduced ore melt and condense thereby
restricting re-dispersion. The dust burner blows again fine
dust outputted from the melter, and fine dust is
melting-condensed at the leading end thereof and thus restricted in its re-dispersion.
SUMMARY OF THE PRESENT INVENTION
It is therefore an object of the invention to provide a
recycling method in a coal based iron making process, which allows
recycling of waste material such as dust and sludge outputted from iron and steel works.
In order to obtain the above object, the invention provides
a recycling method of waste material in use for a coal based iron
making process by using a reduction-melting apparatus which includes a reduction furnace for reducing ore and supplementary
raw material, a melter gasifier for reduction-melting reduced iron fed from the reduction furnace into hot metal, a cyclone
for trapping fine dust in exhaust gas from the melter gasifier
to circulate trapped fine dust to the melter gasifier and to feed
exhaust gas cleared of fine dust to the reduction furnace as
reduction gas, and a dust burner with one end connected to the
cyclone and the other end connected to the melter gasifier and
for executing melting condensation to and then blowing fine dust
into the melting gasifier, in which the method comprises the
following steps of: collecting and drying waste material so that
the total composition of T.Fe, C, CaO and MgO reaches at least
50wt%; sorting dried waste material to have a particle size of
5mm or less; and blowing sorted waste material into the melter
gasifier with the dust burner.
BRIEF DESCRIPTION OF THE DRAWINGS
The above object and other advantages of the present
invention will become more apparent by describing in detail the
preferred embodiment of the present invention with reference to the attached drawings in which:
Fig. 1 schematically illustrates a general coal based iron
making process; and
Fig. 2 is a schematic view illustrating a recycling
apparatus of waste material in an iron making process according to the invention.
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENT
Hereinafter the present invention will be described in
detail.
As set forth above, it is a main feature of the present
invention that sludge and dust outputted from iron and steel works
are blown after adjusting composition and particle size thereof,
thereby recycling them in an iron making reduction-melting
process .
First, in the present invention, sludge and dust outputted in an iron and steel working process are collected for recycling
thereof. At this time, sludge and dust are required to contain
useful components in the iron working process such as Fe, C and
supplementary raw material (CaO, MgO) whose total composition
is at least 50wt%. It is because charging of waste material
cannot be effectuated as additional charging of fuel and raw
material unless the total composition of the useful components
reaches 50wt%.
If collected sludge and dust contain those components such
as alkaline metal compounds, Zn, S, and P by a large portion
dropping the total composition of the useful components under
50wt%, such sludge and dust are not suitably used in the iron
making process since those components would deposit within the
melter or act as heavy load in a hot metal pretreatment .
That is, if sludge and dust are mainly composed of those
elements including Si, Al, S, P, Cl, Zn, Na and K rather than
the above useful components, those elements may create severe
problems in the operation of the iron making process.
Specifically, Si and Al components removed as slag in the iron
making process directly affect properties of slag such as melting
point, viscosity, desulfurizing ability and so on. So there are
a number of difficulties in recycling sludge or dust containing
the Si and Al components by a large quantity. Further, in selection of fuel, raw material and supplementary raw material,
those components are strictly restricted since they otherwise
would yield low-grade pig iron and form deposits within the
furnace while creating environmental problems .
In this regard, the invention preferably restricts the
composition of waste material so that collected sludge and dust may contain Si and Al compounds each at 20wt% or less, Zn, Na
and K components each at 5wt% or less and S, P and Cl components
each at lwt% or less. The following Table 1 shows examples of
dust and sludge applicable to the invention.
Any waste material meeting the above composition standard
is collected and then dried. Where the moisture content is too
high, it is difficult to transport waste material on a belt or
via air, and waste material is unsuitable for the iron making
process.
The moisture content of dried waste material is controlled
with a drier, preferably, at 10% or less.
Above dried waste material is sorted to have a certain
particle size or less. Dried waste material is classified according to its particle size applicable to a dust burner, that
is, for example, about 70mm or less since a blowing portion of
the dust burner has an inside diameter of about 70mm.
Sludge and dust are necessarily melted and condensed in
flames of a dust burner for being recycled in the iron making
process, however, the present inventors found out through
researches that dust particles having a particle size of 5mm or
more hardly melt or condense in the dust burner based upon iron
ore regardless of their melting degrees which are varied
depending on their components. Further, the inventors found out
that in case where the iron ore particles have the large specific
gravity and a particle size of 5mm or more, it is required to
blow the air with a velocity of about at least 20m/s in order
to pneumatically carry them up to a charging bin which is
installed at least 50m high from the ground, thereby not ensuring
an efficient blowing.
Therefore, the invention restricts the particle size of
waste material at 5mm or less, and preferably, at 3mm or less
considering efficient blowing and melting.
And waste material having thus classified particle size is blown into the melter gasifier with the dust burner, and
therefore, the waste material outputted in the iron and works
can be efficiently recycled as fuel and raw material of the iron
making process.
Hereinafter the following detailed description will
discuss a detailed blowing method of the waste material prepared
as above.
Fig. 2 is a schematic view illustrating a coal based iron
making apparatus according to an embodiment of the invention, in which the apparatus generally comprises a reduction furnace
10 adapted for reducing ore and supplementary raw material, a
melter gasifier 20 adapted for manufacturing pig iron through
reduction-melting of reduced iron fed from the reduction furnace
10 and a cyclone 21 for trapping exhaust gas from the melter gasifier 20 to circulate fine dust in exhaust gas through a dust
recycling duct 210 to the melter gasifier 20 and feed exhaust
gas cleared of fine dust through a gas duct 22 to the reduction
furnace 10 as reduction gas.
Further, the reduction furnace 10 is connected through an ore-charging duct 12 to the melter gasifier 20 in an
ore-communicating relation, and includes a dust burner 213
having one end connected to the cyclone 21 and the other end
connected to the melter gasifier 10 and for executing melting
condensation to and then blowing the fine dust into the melter gasifier 20.
First, waste material such as sludge and dust produced from
processes in iron and steel works is collected in a storage 41.
The collected waste material is dried in a drier such as a rotary
kiln 42 for adjusting the moisture content suitable for recycling.
Dried waste material is adjusted in a sorting machine 43 to have
a particle size suitable for recycling. Coarse waste material
sorted in the sorting machine 43 is sent again to a grinding
machine 44, where coarse waste material is ground into a desired particle size.
In this manner, waste material having certain degrees of
moisture content and particle size is stored in a storage 31, and stored waste material is fed through a rotary feeder 34 and
a feeding line 35 to a temporary storage 36 which temporarily
stores waste material. Waste material in the temporary storage
36 is fed through a rotor feeder 37 under the storage 36 to a
storage 212 and then to the dust burner 213, by which waste material is blown into the melter gasifier 20.
In the meantime, the invention preferably mixes any
material such as ore or coal, which is used as fuel or raw material in the iron making process, into above prepared waste material
before feeding waste material to the dust burner 213 in order
to enhance the melting condensation efficiency of waste material
having the above composition and particle size distribution.
For the purpose of complete combustion of blown fine dust, at the leading end of the dust burner, the art examines the
oxidation states of carbon component (raw material) and ore
(regarding oxygen in metal oxide which is not completely
metalized as reducing agent) while adjusting the quantity of
oxygen which is blown in together with fine dust. Therefore,
the degree of compounding between coal and ore can be changed
into any value according to the carbon content and the oxidation
degree of iron oxide in waste material to be treated. The
compounding ratio is flexibly adjusted according to operating
situations, that is, oxidizing agent component can be overly
mixed to stop temperature elevation when the melter gasifier is
so heated to excessively elevate its temperature due to complete
combustion.
The following example will provide a more detailed
description of the invention without restricting the extent of the invention.
EXAMPLE
The following experiment was performed in order to know
whether sludge/dust can be recycled in the iron making process.
The composition of sludge/dust used in this experiment is
reported in the following Table 2. In Table 2, Inventive
examples 1 to 3 each contain T.Fe, C, CaO and MgO components whose
total composition is 50wt% or more, while Comparative examples
1 and 2 each contain the same components whose total composition
is under 50wt%. In the meantime, sludge/dust particles used in
this experiment are so sorted to have a particle size of 3mm or
less.
TABLE 2
Sludge/dust waste materials having the above composition
and sorted with their particle sizes were respectively blown into
the melter gasifier of the reduction-melting apparatus
configured as shown in Fig. 2 at a blowing speed of 5ton/hr for
3 days in order to make molten iron while evaluating any problems
in operation and facilities related to blowing of the waste
materials .
First, in order to determine the quantity of blown
sludge/dust which leaves on reduction gas out of the melter
gasifier 20 without melting condensation, it is measured the
quantity of dust circulating in the dust recycling duct 210 and
the air permeability of the reduction furnace 10 before and after
blowing. As a result, it can be seen that both of sludge and
dust waste materials have no effect on the air permeability of
the reduction furnace and the quantity of circulating dust has
no variation before and after blowing by the following reason.
That is, since both of the sludge and dust waste materials have
a particle size of 3mm or less within the inventive range, they
could be effectively melted and condensed when blown into the melter gasifier.
Then, the effects for the composition of the blown
sludge/dust are examined. As a result, in case where the waste
materials of Inventive examples 1 to 3 within the inventive range
are blown into the melter gasifier, there was almost no variation
in the operation while increasing the yield of molten iron.
On the contrary, in blowing the waste materials of the
Comparative examples 1 and 2 having composition beyond the
inventive range, it is required to additionally charge certain
quantities of lime and dolomite to adjust the basicity of slag
thereby increasing the output of slag. That is, when blown into
the melter gasifier, sludge and dust which contain a small amount
of useful components (e.g. T.Fe, C, CaO, MgO) and a large amount
of Si and Al increase the output of slag by itself because they
perform the same role as those components outputted as slag.
Also, it is needed to further charge supplementary raw material
to adjust the basicity of slag thereby dropping productivity.
As described above, in order to recycle sludge and dust
outputted in the iron and steel working process in the coal based
iron making process, it can be understood that sludge and dust
necessarily contain T.Fe, C, CaO and MgO whose total composition
is at least 50wt% as well as have particle sizes of 5mm or less
by taking account of the increasing hot metal output and reduction
in use of heat source and supplementary raw material.
According to the present invention as set forth above,
there is a useful effect that dust and sludge produced in the
iron and steel works and generally subject to burial are recycled
as fuel and raw material in the iron making process.
Claims
1. In a coal based iron making process by using a
reduction-melting apparatus which includes a reduction furnace
for reducing ore and supplementary raw material, a melter
gasifier for reduction-melting reduced iron fed from the
reduction furnace into hot metal, a cyclone for trapping fine
dust in exhaust gas from the melter gasifier to circulate trapped
fine dust to the melter gasifier and to feed exhaust gas cleared
of fine dust to the reduction furnace as reduction gas, and a dust burner with one end connected to the cyclone and the other
end connected to the melter gasifier and for executing melting
condensation to and then blowing fine dust into the melting
gasifier, a recycling method of waste materials comprising the following steps of:
collecting and drying waste material so that the total
composition of T.Fe, C, CaO and MgO reaches at least 50wt%;
sorting dried waste material to have a particle size of
5mm or less; and
blowing sorted waste material into the melter gasifier with
the dust burner.
2. The recycling method according to claim 1, wherein
waste material is dried to have a moisture content at 10% or less .
3. The recycling method according to claim 1, wherein
dried waste material is sorted to have a particle size of 3mm
or less.
4. The recycling method according to claim 1, wherein the
blowing step of sorted waste material comprises: mixing a proper
amount of ore or coal into sorted waste material.
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| KR2001/23113 | 2001-04-27 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| AU2002308827A1 AU2002308827A1 (en) | 2003-04-17 |
| AU2002308827B2 true AU2002308827B2 (en) | 2007-05-03 |
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